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; ; Municipal NPDES Permit Order No. 2001-01 Appendices; 2005-12-01
APPENDIX A Hydrographs Appendix A: Hydrographs Page 1 of 10 Agua Hedionda Creek February 11, 2005010203040506070801:40 2:40 3:40 4:40 5:40 6:40TimeFlow (cfs)FlowSampleAgua Hedionda Creek February 18, 20050501001502002503:50 4:50 5:50 6:50 7:50TimeFlow (cfs)FlowSample Agua Hedionda Creek October 17, 20040501001502002503003:25 4:25 5:25 6:25 7:25 8:25TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 2 of 10 Chollas Creek February 11, 2005010203040506070802:45 3:45 4:45 5:45 6:45TimeFlow (cfs)FlowSample Chollas Creek February 18 20050501001502002503:25 4:25 5:25 6:25 7:25 8:25 9:25TimeFlow (cfs)FlowSample Chollas Creek October 17, 2004010203040506:20 7:20 8:20 9:20 10:20TimeFlow (cfs)FlowSample Chollas Creek October 27, 200401002003004005006007003:45 4:45 5:45 6:45 7:45 8:45 9:45 10:45TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 3 of 10 Escondido Creek February 11, 2005101520253035400:05 1:05 2:05 3:05 4:05 5:05 6:05 7:05 8:05 9:05 10:05TimeFlow (cfs)FlowSample Escondido Creek February 18, 20051020304050607080903:45 4:45 5:45 6:45 7:45 8:45 9:45TimeFlow (cfs)FlowSample Escondido Creek October 17, 20040204060801004:05 5:05 6:05 7:05 8:05 9:05 10:05TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 4 of 10 Penasquitos River February 11, 2005697173757779812:003:004:005:006:007:008:00TimeFlow (cfs)FlowSample Penasquitos River February 18, 2005801301802302803304:50 5:50 6:50 7:50 8:50 9:50 10:50 11:50TimeFlow (cfs)FlowSample Penasquitos River October 17, 200581012141618203:05 4:05 5:05 6:05 7:05 8:05 9:05 10:05 11:05TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 5 of 10 San Dieguito River February 11, 200539.439.639.84040.240.440.62:05 3:05 4:05 5:05 6:05 7:05 8:05TimeFlow (cfs)Flow Sample San Dieguito River Febuary 18, 20054546474849504:40 5:40 6:40 7:40 8:40 9:40 10:40 11:40 12:40TimeFlow (cfs)FlowSample San Dieguito River October 17, 20042022242628303:15 4:15 5:15 6:15 7:15 8:15 9:15 10:15 11:15 12:15TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 6 of 10 San Diego RiverFebruary 11, 2005 0501001502002500:35 1:35 2:35 3:35 4:35 5:35 6:35 7:35TimeFlow (cfs)FlowSample San Diego River February 18, 2005501001502002503003504003:25 4:25 5:25 6:25 7:25 8:25 9:25 10:25TimeFlow (cfs)FlowSample San Diego River October 27, 200401002003004005006007003:15 4:15 5:15 6:15TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 7 of 10 San Luis Rey River February 11, 20056606706806907007101:30 2:30 3:30 4:30 5:30 6:30TimeFlow (cfs)FlowSample San Luis Rey River February 18, 20057908008108208308404:05 5:05 6:05 7:05 8:05 9:05 10:05 11:05TimeFlow (cfs)FlowSample San Luis Rey River October 27, 2004040801201602001:15 2:15 3:15 4:15 5:15 6:15 7:15TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 8 of 10 Sweetwater River Februay 11, 20059.29.49.69.81010.210.410.61:20 2:20 3:20 4:20 5:20 6:20TimeFlow (cfs)FlowSample Sweetwater River February 18, 200591215182124273:55 4:55 5:55 6:55 7:55 8:55 9:55 10:55 11:55TimeFlow (cfs)FlowSample Sweetwater River October 17, 200455.255.55.7566.253:10 4:10 5:10 6:10 7:10 8:10 9:10TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 9 of 10 Tecolote Creek February 11, 20050501001502002503003504002:50 3:18 3:47 4:16 4:45 5:14 5:42 6:11TimeFlow (cfs)FlowSample Tecolote Creek February 18, 20050501001502002503003504004:05 5:05 6:05 7:05 8:05 9:05 10:05TimeFlow (cfs)FlowSample Tecolote Creek October 27, 20040100002000030000400005000060000700003:25 4:25 5:25 6:25TimeFlow (cfs)FlowSample Appendix A: Hydrographs Page 10 of 10 Tijuana River February 11, 20050204060801001202:20 3:20 4:20 5:20 6:20 7:20 8:20 9:20TimeFlow (cfs)FlowSample Tijuana River February 18, 20050501001502002503005:40 6:40 7:40 8:40 9:40 10:40TimeFlow (cfs)FlowSample Tijuana River October 27, 2004050010001500200025003:30 4:30 5:30 6:30 7:30 8:30 9:30 10:30 11:30 12:30TimeFlow (cfs)FlowSample APPENDIX B Stream Bioassessment Data Appendix B.2-1: Taxonomic Listing of Benthic Macroinvertebrates Collected October 2004.TV FFG123123123123123123123123123123123123123PHYLUM ARTHROPODAInsectaEphemeropteraBaetidaeBaetis sp5cg 113100 1910393162010204514261901240Diphetor hageni5cgFallceon quilleri4cg331236100 937100142569211410210011629CaenidaeCaenis sp7cg100Heptageniidae 4 scIronodes sp3scLeptohyphidaeTricorythodes sp4cg011LeptophlebidaeParaleptophlebia sp4cgOdonataAeshindaeAeschnidae5pAnax sp8p001001Anisoptera p021CalopterygidaeHetaerina americana6p100CoenagrionidaeArgia sp7p 003577625320108701370532425119263331350111 28344Coenagrionidae9pIschnura sp9p021LibellulidaeBrechmorhoga mendax9pLibellula sp9p010Libellulidae9p 0100113PlecopteraCapniidaeCapniidae1shChloroperlidaeSweltsa1pNemouridaeMalenka sp2sh120122Zapada sp2shPerlodidae 2 pPlecopteraHemipteraBelostomatidaeAbedus sp8p001Belostomatidae8p100OdonataCoenagrionidaeEnallagma/Ischnura sp9p 010 200HemipteraCorixidae 8 pTrichocorixa sp8pTrichopteraBrachycentridaeMicrasema sp1mh62 29 93 66 42 45HelicopsychidaeHelicopsyche sp3sc103100HydropsychidaeCheumatopsyche sp5cf 00285 114 25 1 0 0 10 1 3 31 22 20 26 64 7 0 1 0Hydropsyche sp4cf519410100012645442627960100HydroptilidaeHydroptila sp6ph200 010 82128012881 100743161008240Ochrotrichia sp4phOxyethira sp3ph1000090183LepidostomatidaeLepidostoma sp1sh610LeptoceridaeLeptoceridae4om100Nectopsyche sp3om317LimnephilidaeHesperophylax3omLimnephilidae 4 sPsychomyiidaeTinodes sp2sc633 010RhyacophilidaeRhyacophila sp0pSericostomatidaeGumaga sp3shLepidopteraNepticulidaeNepticula sp5sh 031Nepticulidae sStigmella sp5shESC-HRB AHC_ECR AHC-MR CC-CSD-DDH SDR-1CCC-805 ESC-EF GVC-WB LPC-CCR(TV = Tolerance Value: range is 0-10; 0 is intolerant to impairment, 10 is highly tolerant to impairment. FFG = Functional Feeding Group: c=collector, cf=collector-filterer, cg=collector-gatherer, mh=macrophyte herbivore, om=omnivore, p=predator, pa= parasite, ph=piercer herbivore, sc=scraper, sh=shredder.)SDR-MTREF-DLC3 REF-SC2Page 1 of 6 Appendix B.2-1: Taxonomic Listing of Benthic Macroinvertebrates Collected October 2004.TV FFG123123123123123123123123123123123123123ESC-HRB AHC_ECR AHC-MR CC-CSD-DDH SDR-1CCC-805 ESC-EF GVC-WB LPC-CCRSDR-MTREF-DLC3 REF-SC2PyralidaeParaponyx sp5sh100Petrophila sp5sc009010LepidopteraColeopteraCurcADryopidaeHelichus sp5sh002101Postelichus5sh100DytiscidaeLiodessus sp5p210Sanfillipodytes spUvarus sp5p001ElmidaeHeterelmis sp4cg5 1 16 0 1 0Microcylloepus sp2cg20110236Narpus sp4cgZaitzevia sp4sc29 27 24 30 35 70HelophoridaeHelophorus spshHydraenidaeHydraena sp5pHydrophilidaeHelocharus spTropisternus sp5p010HydroscaphidaeHydroscapha natans7sc010PsephenidaeEubrianax edwardsi4sc4010Psephenus falli4sc001PtiliidaeScirtidaeCyphon spDipteraCeratopogonidaeBezzia/Palpomyia6p101 010 110081Stilobezzia sp6pAtrichopogon6cg 010040082011 001421063Ceratopogonidae6p001 10014 4 5Dasyhelea sp6cg011001100 005 571317ChaoboridaeChaoborus sp7p 110Chironomidae 6 cg 25 17 8 5 9 12 10 16 2 8 9 17 9 3 4 29 13 36 33 40 76 4 8 7 9 7 4 2 9 4 50 40 153 12 15 11 41 29 50CulicidaeAnopheles sp8cg 001Culex8cgDolichopodidae 4 pEmpididaeChelifera/Metachela sp6p010Hemerodromia sp6p110Ephydridae 6060200101299Muscidae 6 p 0 1 0 0 1 0100401PsychodidaeMaruina lanceolata2sc021141Pericoma/Telmatoscopus4cg110 0201 0 0 5 17 0Sciomyzidae 6 p001SimuliidaeSimulium sp6 cf 0 0 6 3 2 4 49 52 176 16 3 2 7 5 7 39 35 8 23 16 20 135 135 26 124 59 71StratiomyidaeCaloparyphus/Euparyphus7cg411010 1219451101301300230910 001Caloparyphus/Euparyphus8cgEuparyphus sp8cg15004413Myxosargus sp8cg001Nemotelus sp8cg 186 001 004301Syrphidae 10 cg 0 1 0TipulidaeDicranota sp3pHolorusia hespera5sh010 200Limonia sp6sh 010010 0012100324Molophilus sp4shOrmosia sp3cg001Tipula sp4om 020 020 002 010010 113Tipulidae 3 2 3 0BrachyceraDipteraPHYLUM CHELICERATAArachnidaAcariHygrobatidaeAtractides sp8p013LebertiidaeLebertia sp8p010010MideopsidaeMideopsis sp5pPage 2 of 6 Appendix B.2-1: Taxonomic Listing of Benthic Macroinvertebrates Collected October 2004.TV FFG123123123123123123123123123123123123123ESC-HRB AHC_ECR AHC-MR CC-CSD-DDH SDR-1CCC-805 ESC-EF GVC-WB LPC-CCRSDR-MTREF-DLC3 REF-SC2SperchonidaeSperchon sp8p 001161 81623500 006030100 24202TorrenticolidaeTorrenticola sp5p002Acari5p010PHYLUM ARTHROPODAMalacostracaAmphipodaCorophiidaeAmericorophium sp4cf0011CrangonyctidaeCrangonyx sp4cgHyalellidaeHyalella sp8cg1353758921181327067281970441640108150713105 461007117DecapodaCambaridae 6 sh031001 041Procambarus sp8sh 440 100 010100Decapoda6sh 010621210 001213600Ostracoda8 cg 70 78 78 0 4 0 10 4 2 62 90 128 87 97 107 2 1 100441907922PHYLUM PLATYHELMINTHESTurbelleria4 p 46 17 25 1 8 19 7 10 6 14 9 1 23 63 45 31 18 0 35 0 0 0 1 2 3 3 2 0 2 2 1 0 0 78 14 28 0 1 3PHYLUM CNIDARIAHydrozoaHydroidaHydridaeHydra sp5p1030PHYLUM NEMERTEAEnoplaHoplonemerteaTetrastemmatidaeProstoma sp8p 003942155161498494 1029 210 04425521501528PHYLUM ANNELIDAHirudinidaArynchobdellidaErpobdellidaeErpobdella sp8p010Mooreobdella sp8p010Helobdella sp6pa141Oligochaeta5 cg 3 141 129 6 68 15 30 2 13 80 2 21 3 2 6 0 29 34 9 5 38 1 8 3 2 17 6 0 0 20 0 29 4 0 12 43PHYLUM MOLLUSCAGastropodaPulmonataAncylidaeFerrissia sp6 sc 4 20 14200LymnaeidaeFossaria sp6sc 2122180100100 5121001200 001 122PhysidaePhysa sp8sc8460921456671976810012892014100001 31663117PlanorbidaeMenetus sp6sc011Planorbella sp6sc0140101ProsobranchiaThiaridaeTarebia granifera303BivalviaVeneroidaCorbiculidaeCorbicula fluminea10 cf 34 11 6 15 1 0030043 01614385411126018PelecypodaSphaeriidaePisidium sp8cfSphaeriidae 8 cf88 139 80210Page 3 of 6 Appendix B.2-1: Taxonomic Listing of Benthic Macroinvertebrates Collected October 2004.TV FFGPHYLUM ARTHROPODAInsectaEphemeropteraBaetidaeBaetis sp5cgDiphetor hageni5cgFallceon quilleri4cgCaenidaeCaenis sp7cgHeptageniidae 4 scIronodes sp3scLeptohyphidaeTricorythodes sp4cgLeptophlebidaeParaleptophlebia sp4cgOdonataAeshindaeAeschnidae5pAnax sp8pAnisoptera pCalopterygidaeHetaerina americana6pCoenagrionidaeArgia sp7pCoenagrionidae9pIschnura sp9pLibellulidaeBrechmorhoga mendax9pLibellula sp9pLibellulidae9pPlecopteraCapniidaeCapniidae1shChloroperlidaeSweltsa1pNemouridaeMalenka sp2shZapada sp2shPerlodidae 2 pPlecopteraHemipteraBelostomatidaeAbedus sp8pBelostomatidae8pOdonataCoenagrionidaeEnallagma/Ischnura sp9pHemipteraCorixidae 8 pTrichocorixa sp8pTrichopteraBrachycentridaeMicrasema sp1mhHelicopsychidaeHelicopsyche sp3scHydropsychidaeCheumatopsyche sp5cfHydropsyche sp4cfHydroptilidaeHydroptila sp6phOchrotrichia sp4phOxyethira sp3phLepidostomatidaeLepidostoma sp1shLeptoceridaeLeptoceridae4omNectopsyche sp3omLimnephilidaeHesperophylax3omLimnephilidae 4 sPsychomyiidaeTinodes sp2scRhyacophilidaeRhyacophila sp0pSericostomatidaeGumaga sp3shLepidopteraNepticulidaeNepticula sp5shNepticulidae sStigmella sp5sh12312312312312312312312312312312312 41 17 155 53 12 13 14 136 73 57 87 2 2 7 2 0 0 63 72 3527043 33 67 6 9 0 87 140 41 1 4 017 12 2140011 30 155012191001 100100110 0101002951194 24019143823 53 42 0 0 103201000243 53 6411 13 643 37 450 29 135007013109 9 096 1 00 1 0 29 8 107983151021591011157871511101010 042105712 8 7302200004155301422553900001100 100100SMR-CPMB-RC BVR-CB CC-FB REF-DC SLRR-BR SR-WS TC-TCNPSLRR-MR SMC-LCCC SMR-WGRPage 4 of 6 Appendix B.2-1: Taxonomic Listing of Benthic Macroinvertebrates Collected October 2004.TV FFGPyralidaeParaponyx sp5shPetrophila sp5scLepidopteraColeopteraCurcADryopidaeHelichus sp5shPostelichus5shDytiscidaeLiodessus sp5pSanfillipodytes spUvarus sp5pElmidaeHeterelmis sp4cgMicrocylloepus sp2cgNarpus sp4cgZaitzevia sp4scHelophoridaeHelophorus spshHydraenidaeHydraena sp5pHydrophilidaeHelocharus spTropisternus sp5pHydroscaphidaeHydroscapha natans7scPsephenidaeEubrianax edwardsi4scPsephenus falli4scPtiliidaeScirtidaeCyphon spDipteraCeratopogonidaeBezzia/Palpomyia6pStilobezzia sp6pAtrichopogon6cgCeratopogonidae6pDasyhelea sp6cgChaoboridaeChaoborus sp7pChironomidae 6 cgCulicidaeAnopheles sp8cgCulex8cgDolichopodidae 4 pEmpididaeChelifera/Metachela sp6pHemerodromia sp6pEphydridae 6Muscidae 6 pPsychodidaeMaruina lanceolata2scPericoma/Telmatoscopus4cgSciomyzidae 6 pSimuliidaeSimulium sp6cfStratiomyidaeCaloparyphus/Euparyphus7cgCaloparyphus/Euparyphus8cgEuparyphus sp8cgMyxosargus sp8cgNemotelus sp8cgSyrphidae 10 cgTipulidaeDicranota sp3pHolorusia hespera5shLimonia sp6shMolophilus sp4shOrmosia sp3cgTipula sp4omTipulidae 3BrachyceraDipteraPHYLUM CHELICERATAArachnidaAcariHygrobatidaeAtractides sp8pLebertiidaeLebertia sp8pMideopsidaeMideopsis sp5p123123123123123123123123123123123SMR-CPMB-RC BVR-CB CC-FB REF-DC SLRR-BR SR-WS TC-TCNPSLRR-MR SMC-LCCC SMR-WGR05001902002001000110001019 1 1010130301100 012124021001010 0012932141 1 0 0 0 0 11131121178 53 3606255197863403648120383619583917126172200163150105278042221645010010010010020200012030 141200 231 110102106010 142100319361445610145 0450219 127131158 158203198001272 194137222813001 001001211282101 100002 010 010011001010020924010001121001100500001444201Page 5 of 6 Appendix B.2-1: Taxonomic Listing of Benthic Macroinvertebrates Collected October 2004.TV FFGSperchonidaeSperchon sp8pTorrenticolidaeTorrenticola sp5pAcari5pPHYLUM ARTHROPODAMalacostracaAmphipodaCorophiidaeAmericorophium sp4cfCrangonyctidaeCrangonyx sp4cgHyalellidaeHyalella sp8cgDecapodaCambaridae 6 shProcambarus sp8shDecapoda6shOstracoda8cgPHYLUM PLATYHELMINTHESTurbelleria4pPHYLUM CNIDARIAHydrozoaHydroidaHydridaeHydra sp5pPHYLUM NEMERTEAEnoplaHoplonemerteaTetrastemmatidaeProstoma sp8pPHYLUM ANNELIDAHirudinidaArynchobdellidaErpobdellidaeErpobdella sp8pMooreobdella sp8pHelobdella sp6paOligochaeta5cgPHYLUM MOLLUSCAGastropodaPulmonataAncylidaeFerrissia sp6scLymnaeidaeFossaria sp6scPhysidaePhysa sp8scPlanorbidaeMenetus sp6scPlanorbella sp6scProsobranchiaThiaridaeTarebia graniferaBivalviaVeneroidaCorbiculidaeCorbicula fluminea10 cfPelecypodaSphaeriidaePisidium sp8cfSphaeriidae 8 cf123123123123123123123123123123123SMR-CPMB-RC BVR-CB CC-FB REF-DC SLRR-BR SR-WS TC-TCNPSLRR-MR SMC-LCCC SMR-WGR010 15001040421 12 1631578201111124 101096 2473101133431100101020231010001410 010002700 2001310 300010020 14555 4586 0 0 2 0 0 105 73 48 15 0 0 6 10 15 17 23 420200526142162 1600021423206112208491310041027202058132790172221100 0 4 16 159 1110014 19 1 73 102 110012002214357121421016 48 95020Page 6 of 6 Appendix B.2-2: Taxonomic Listing of Benthic Macroinvertebrates Collected May 2005.TV FFG123123123123123123123123123123123123123PHYLUM ARTHROPODAInsectaEphemeropteraBaetidaeBaetis sp5 cg 144 125 111 107 168 90 8 9 23 120 155 103 12 7 17 1 1 0 20 76 43 23 10 34 3 5 13 148 109 130 127 67 92 3 5 1 105 71 43Callibaetis sp9cg 100Centroptilum/Procleon sp3cgDiphetor hageni5cg542Fallceon quilleri4 cg 25 23 22 0 2 4 56 71 50 0 0 2 50 27 34 37 14 56 8 5 3 14 1 3 14 9 4 8 3 6HeptageniidaeIronodes sp3sc10 15 25LeptohyphidaeTricorythodes sp4cgParaleptophlebia sp4cg906SiphlonuridaeSiphlonurus sp7cg100OdonataCalopterygidaeHetaerina americana6pCoenagrionidaeArgia sp7p 100 514Ischnura sp9p100CordulegastridaeCordulegaster dorsalis3pPlecopteraCapniidae 1 sh060ChloroperlidaeHaploperla chilnualna sp1p201Sweltsa1p001NemouridaeMalenka sp2sh7248Nemouridae 2 sh58 39 39Neumoura spiniloba1sh110Zapada sp2sh18 46 19PerlodidaeIsoperla sp2p740Perlodinae 2 pTaeniopterygidaeTaenionema sp2omPlecoptera0109HemipteraBelostomatidaeAbedus sp8pBelostomatidae 8 pOdonataCoenagrionidaeEnallagma/Ischnura sp9p009310MegalopteraCorydalidaeNeohermes sp0pTrichopteraHydropsychidaeCheumatopsyche sp5cf1001216Hydropsyche sp4cf012Parapsyche sp0p100HydroptilidaeHydroptila sp6ph043 01000226310100241463279Oxyethira sp3ph 010LepidostomatidaeLepidostoma sp1shLimnephilidaeHesperophylax3om0311Psychoglypha sp2sh120PhilopotamidaeWormaldia sp3cfRhyacophilidaeRhyacophila sp0p0111SericostomatidaeGumaga sp3sh100LepidopteraNepticulidae sColeopteraDytiscidaeAgabinus sp5p201Agabus sp8p100Hydroporinae5p010Ilybius sp5p100Liodessus sp5p010Rhantus sp5p 100Sanfillipodytes sp(TV = Tolerance Value: range is 0-10; 0 is intolerant to impairment, 10 is highly tolerant to impairment. FFG = Functional Feeding Group: c=collector, cf=collector-filterer, cg=collector-gatherer, mh=macrophyte herbivore, om=omnivore, p=predator, pa= parasite, ph=piercer herbivore, sc=scraper, sh=shredder.)SGVC_WBSSR_WS SCCC_805 SESC_EF SESC_HRBSREF_DC SSDR_1 SSLRR_BR SSR_94SAHC_ECR SAHC_MR SCC_C SCC_FBPage 1 of 6 Appendix B.2-2: Taxonomic Listing of Benthic Macroinvertebrates Collected May 2005.TV FFG123123123123123123123123123123123123123SGVC_WBSSR_WS SCCC_805 SESC_EF SESC_HRBSREF_DC SSDR_1 SSLRR_BR SSR_94SAHC_ECR SAHC_MR SCC_C SCC_FBElmidaeMicrocylloepus sp2cgZaitzevia sp4scHaliplidaePeltodytes sp5mh010HydraenidaeHydraena sp5pHydrophilidaeBerosus sp5p100Tropisternus sp5pScirtidaeCyphon sp103DipteraCeratopogonidaBezzia/Palpomyia6p011010 120Stilobezzia sp6p100CeratopogonidaeCulicoides sp6p020Dasyhelea sp6cg001Chironomidae 6 cg 20 50 26 36 27 44 180 210 200 15 35 42 132 178 102 12 14 58 23 36 34 85 30 51 18 32 22 79 84 84 40 11 30 107 98 81 10 15 4CulicidaeCulex8cg001DixidaeDixa sp2cgDixella sp2cgDolichopodidae 4 p 0 0 1 0 0 2022EmpididaeChelifera/Metachela sp6p 100Clinocera sp6p 001 010Empididae 6 p001Ephydridae 6 0 0 1 2 0 0 0 1 0200Muscidae 6 p100231310 001001100001102 110100PsychodidaeMaruina lanceolata2scPericoma/Telmatoscopus4cg104010 001100200Psychoda sp10 cg100SimuliidaeSimulium sp6 cf 7 3 3 11 22 56 73 29 54 72 37 73 0 14 1 242 229 36 14 47 16 112 190 75 34 137 182 52 108 84 101 253 160 9 11 5 132 179 222StratiomyidaeCaloparyphus/Euparyphus8cg337010 100 010Euparyphus sp8cg230010TipulidaeDicranota sp3p117Holorusia hespera5sh100010Limonia sp6sh001Ormosia sp3cg010Tipula sp4om100010PHYLUM CHELICERATAArachnidaAcariHygrobatidaeAtractides sp8pLebertiidaeLebertia sp8p200SperchonidaeSperchon sp8p001001001001100202114TorrenticolidaeTorrenticola sp5pPHYLUM ARTHROPODAMalacostracaAmphipodaCorophiidaeAmericorophium sp4cf51316CrangonyctidaeCrangonyx sp4cgGammaridaeGammarus sp4cgHyalellidaeHyalella sp8cg108213110301300 47911313750 7035490101005191508Amphipodacg010310 400 020DecapodaCambaridaeProcambarus sp8sh020 101 100Decapoda6sh300001101 100010Ostracoda8cg641763198022330100242020031608633313 345131701Turbellaria4p13301002101029114013PHYLUM CNIDARIAHydrozoaHydroidaHydridaeHydra sp5p191421536010010303062001100100PHYLUM NEMERTEAEnoplaHoplonemerteaPage 2 of 6 Appendix B.2-2: Taxonomic Listing of Benthic Macroinvertebrates Collected May 2005.TV FFG123123123123123123123123123123123123123SGVC_WBSSR_WS SCCC_805 SESC_EF SESC_HRBSREF_DC SSDR_1 SSLRR_BR SSR_94SAHC_ECR SAHC_MR SCC_C SCC_FBTetrastemmatidaeProstoma sp8p012320100PHYLUM ANNELIDAOligochaeta5 cg 82 76 121 123 87 120 6 11 21 1 2 14 16 21 20 1 5 31 84 77 129 42 50 91 8 0 0 4 3 0 12 1 1 107 141 186 0 2 3PHYLUM MOLLUSCAGastropodaPulmonataAncylidaeFerrissia sp6sc004Fossaria sp6sc 100010Physa sp8sc020320221701068 1216200422 100 510BivalviaVeneroidaCorbiculidaeCorbicula fluminea10 cf110001SphaeriidaePisidium sp8cf16 1 0PHYLUM ANTHROPODAInsectaDipteraTipulidaeLimnophila sp100Page 3 of 6 Appendix B.2-2: Taxonomic Listing of Benthic Macroinvertebrates Collected May 2005.TV FFGPHYLUM ARTHROPODAInsectaEphemeropteraBaetidaeBaetis sp5cgCallibaetis sp9cgCentroptilum/Procleon sp3cgDiphetor hageni5cgFallceon quilleri4cgHeptageniidaeIronodes sp3scLeptohyphidaeTricorythodes sp4cgParaleptophlebia sp4cgSiphlonuridaeSiphlonurus sp7cgOdonataCalopterygidaeHetaerina americana6pCoenagrionidaeArgia sp7pIschnura sp9pCordulegastridaeCordulegaster dorsalis3pPlecopteraCapniidae 1 shChloroperlidaeHaploperla chilnualna sp1pSweltsa1pNemouridaeMalenka sp2shNemouridae 2 shNeumoura spiniloba1shZapada sp2shPerlodidaeIsoperla sp2pPerlodinae 2 pTaeniopterygidaeTaenionema sp2omPlecopteraHemipteraBelostomatidaeAbedus sp8pBelostomatidae 8 pOdonataCoenagrionidaeEnallagma/Ischnura sp9pMegalopteraCorydalidaeNeohermes sp0pTrichopteraHydropsychidaeCheumatopsyche sp5cfHydropsyche sp4cfParapsyche sp0pHydroptilidaeHydroptila sp6phOxyethira sp3phLepidostomatidaeLepidostoma sp1shLimnephilidaeHesperophylax3omPsychoglypha sp2shPhilopotamidaeWormaldia sp3cfRhyacophilidaeRhyacophila sp0pSericostomatidaeGumaga sp3shLepidopteraNepticulidae sColeopteraDytiscidaeAgabinus sp5pAgabus sp8pHydroporinae5pIlybius sp5pLiodessus sp5pRhantus sp5pSanfillipodytes sp12312312312312312312312312312312343 91 24 110 100 108 64 87 50 111 145 100 2 3 5 72 154 70 65 83 16 170 133 162 76 40 35 30 15 31010412101483525110 06113865149181331 410308011012115960030 001003 0010109107210001520100010469100321151220011 2103 2 8 31 78 36 2 0 0 7 10 3 0 1 0310 222 210210213 10010010001012 8 2001100110010SSMR_WGR STJ_DM SSD_DDH SREF_WCSSLRR_MR STC_TCNP SMB_RC SSMR_CPSLPC_CCR SREF_SC2 SSDR_MTPage 4 of 6 Appendix B.2-2: Taxonomic Listing of Benthic Macroinvertebrates Collected May 2005.TV FFGElmidaeMicrocylloepus sp2cgZaitzevia sp4scHaliplidaePeltodytes sp5mhHydraenidaeHydraena sp5pHydrophilidaeBerosus sp5pTropisternus sp5pScirtidaeCyphon spDipteraCeratopogonidaBezzia/Palpomyia6pStilobezzia sp6pCeratopogonidaeCulicoides sp6pDasyhelea sp6cgChironomidae 6 cgCulicidaeCulex8cgDixidaeDixa sp2cgDixella sp2cgDolichopodidae 4 pEmpididaeChelifera/Metachela sp6pClinocera sp6pEmpididae 6 pEphydridae 6Muscidae 6 pPsychodidaeMaruina lanceolata2scPericoma/Telmatoscopus4cgPsychoda sp10 cgSimuliidaeSimulium sp6cfStratiomyidaeCaloparyphus/Euparyphus8cgEuparyphus sp8cgTipulidaeDicranota sp3pHolorusia hespera5shLimonia sp6shOrmosia sp3cgTipula sp4omPHYLUM CHELICERATAArachnidaAcariHygrobatidaeAtractides sp8pLebertiidaeLebertia sp8pSperchonidaeSperchon sp8pTorrenticolidaeTorrenticola sp5pPHYLUM ARTHROPODAMalacostracaAmphipodaCorophiidaeAmericorophium sp4cfCrangonyctidaeCrangonyx sp4cgGammaridaeGammarus sp4cgHyalellidaeHyalella sp8cgAmphipodacgDecapodaCambaridaeProcambarus sp8shDecapoda6shOstracoda8cgTurbellaria4pPHYLUM CNIDARIAHydrozoaHydroidaHydridaeHydra sp5pPHYLUM NEMERTEAEnoplaHoplonemertea123123123123123123123123123123123SSMR_WGR STJ_DM SSD_DDH SREF_WCSSLRR_MR STC_TCNP SMB_RC SSMR_CPSLPC_CCR SREF_SC2 SSDR_MT0110011910031000044032200104 63 49 87 47 99 21 7 20 29 10 15 189 113 168 48 75 91 17 17 83 42 24 57 52 2 7 37 28 14 81 96 114001200010110101110 100006010100201 221 100301101 020020001001 002010402701243 119 196 39 39 20 164 169 210 139 142 181 92 197 69 102 26 74 58 138 29 67 125 24 203 237 269 166 170 119001001020100004 100001102001 002 11100120027002114580302238831011010010101022031 6055201651100114020001010Page 5 of 6 Appendix B.2-2: Taxonomic Listing of Benthic Macroinvertebrates Collected May 2005.TV FFGTetrastemmatidaeProstoma sp8pPHYLUM ANNELIDAOligochaeta5cgPHYLUM MOLLUSCAGastropodaPulmonataAncylidaeFerrissia sp6scFossaria sp6scPhysa sp8scBivalviaVeneroidaCorbiculidaeCorbicula fluminea10 cfSphaeriidaePisidium sp8cfPHYLUM ANTHROPODAInsectaDipteraTipulidaeLimnophila sp123123123123123123123123123123123SSMR_WGR STJ_DM SSD_DDH SREF_WCSSLRR_MR STC_TCNP SMB_RC SSMR_CPSLPC_CCR SREF_SC2 SSDR_MT010 001 002324428201173141160345536215171080200001008220 4680111001 010Page 6 of 6 Appendix B.3-1: Ranked Abundance of Benthic Macroinvertebrates Collected October 2004.Taxon AHC-ECR AHC-MR BVR-CB CC-C CCC-805 CC-FB ESC-EF ESC-HRB GVC-WB LPC-CCR MB-RC REF-DC REF-DLC3 REF-SC2Simulium sp 6 9 9 21 277 21 19 82 59Chironomidae 26 28 93 34 16 268 78 50 149 19 3 65 20 15Hyalella sp 48 269 15 54 8 20 230 33 20 2 6Ostracoda 4 16 280 291 226 226 4 2Oligochaeta 89 45 1 103 11 5 273 63 52 70 67 12 25Baetis sp 5 1 217 68 10 21 11 79 45Hydropsyche sp155 1 3 160 201Argia sp 3 158 6 5 25 71 4 60 31 46 99Fallceon quilleri 11 1 268 19 5 1 7 21 104 3 1Cheumatopsyche sp 2224 1 14 73Turbellaria 28 23 24 131 49 88 35 3 8 4Physa sp 11 25 32 21 186 1 18 139 5 34 1 1Prostoma sp 3 66 35 151 30 2 3Corbicula fluminea 51 1637Micrasema sp184 153Hydroptila sp 1 6 22 22 9 2 37 1Sphaeriidae 3073Caloparyphus/Euparyphus 1 97 76 63 12 6 4 3 1 5 10Fossaria sp 5 20 1 1 54 1 186 2Dasyhelea sp214 1Zaitzevia sp80 135Crangonyx spCapniidae160Pisidium sp159Decapoda1923 1 6 1Sperchon sp 1 8 47 5163CorixidaeTrichocorixa spMalenka sp84 3 5Zapada sp92Ceratopogonidae11 117Ironodes sp56Atrichopogon 1 410 2 1Euparyphus sp21 12 15Pericoma/Telmatoscopus 2 3 2 7 1Ephydridae 6 2 23Microcylloepus sp339Limonia sp 1 1 12 1 2Ferrissia sp 382Oxyethira sp1Sweltsa30Bezzia/Palpomyia 2132Nemotelus sp 15 1 1 4 1 4Procambarus sp 8 1 1 1Heterelmis sp22 1Cambaridae 4 15Paraleptophlebia sp22Hydraena sp21Tinodes sp12Petrophila sp91Plecoptera20Tipula sp 2 224 1Muscidae 1 162Planorbella spLibellulidae 1Eubrianax edwardsi14Lebertia sp 112 1Hydra sp13Rhyacophila sp13Americorophium spHesperophylax11Lepidostoma sp47Nectopsyche sp11Chaoborus sp 2Diphetor hageni9Gumaga sp9Page 1 of 4 Appendix B.3-1: Ranked Abundance of Benthic Macroinvertebrates Collected October 2004.Taxon AHC-ECR AHC-MR BVR-CB CC-C CCC-805 CC-FB ESC-EF ESC-HRB GVC-WB LPC-CCR MB-RC REF-DC REF-DLC3 REF-SC2Maruina lanceolata36Tricorythodes sp2Helobdella sp 6Paraponyx sp1Tarebia granifera6Brachycera5CoenagrionidaeHelicopsyche sp41Hetaerina americana 11Holorusia hespera11Nepticula sp 4Ochrotrichia spPerlodidae5Tipulidae 5Atractides sp4Cyphon sp4Helichus sp22Heptageniidae4Limnephilidae4Myxosargus spPtiliidae4Anax sp 11Anisoptera3Chelifera/Metachela sp1Enallagma/Ischnura sp 1 2Ischnura spLiodessus sp3Menetus sp2Mideopsis sp3Aeschnidae1Anopheles sp 1CulicidaeCurculionidae2Dicranota sp2DolichopodidaeHemerodromia sp2Lepidoptera2Nepticulidae1Ormosia sp11Sciomyzidae 11Torrenticola sp2Abedus sp1Acari1Belostomatidae1Brechmorhoga mendaxCaenis sp 1CulexDiptera1Erpobdella sp1Cymbiodyta1Helophorus sp1Hydroscapha natans1Leptoceridae1Libellula sp1Molophilus sp1Mooreobdella spNarpus sp1Postelichus1Psephenus falli 1Sanfillipodytes sp1Stigmella sp1Stilobezzia sp1Syrphidae 1Tropisternus sp1Uvarus sp1Grand Total 318 760 715 896 865 885 913 942 708 302 354 891 789 911Page 2 of 4 Appendix B.3-1: Ranked Abundance of Benthic Macroinvertebrates Collected October 2004.TaxonSimulium spChironomidaeHyalella spOstracodaOligochaetaBaetis spHydropsyche spArgia spFallceon quilleriCheumatopsyche spTurbellariaPhysa spProstoma spCorbicula flumineaMicrasema spHydroptila spSphaeriidaeCaloparyphus/EuparyphusFossaria spDasyhelea spZaitzevia spCrangonyx spCapniidaePisidium spDecapodaSperchon spCorixidaeTrichocorixa spMalenka spZapada spCeratopogonidaeIronodes spAtrichopogonEuparyphus spPericoma/TelmatoscopusEphydridaeMicrocylloepus spLimonia spFerrissia spOxyethira spSweltsaBezzia/PalpomyiaNemotelus spProcambarus spHeterelmis spCambaridaeParaleptophlebia spHydraena spTinodes spPetrophila spPlecopteraTipula spMuscidaePlanorbella spLibellulidaeEubrianax edwardsiLebertia spHydra spRhyacophila spAmericorophium spHesperophylaxLepidostoma spNectopsyche spChaoborus spDiphetor hageniGumaga spSD-DDH SDR-1 SDR-MT SLRR-BR SLRR-MR SMC-LCCC SMR-CP SMR-WGR SR-WS TC-TCNP Grand Total296 254 257 55 559 29 416 2369243 38 120 1 81 17 83 124 318 149 203820 124 13 185 146 4 178 13754 23 38 15 6 31 82 124820 33 55 98 57 8 4 129 13 123316 70 220 170 163 2 10981 15 2 7 264 80912 66 16 1 24 118 74546 143 50 15 69597 1 1 47 3 177 6401 120 4 2 7 22 54925 395388 92 43 9 7 44930 103 90 25 5 12 20 36233793 1 86 2 1 27 3103101 1 11 4 1 1 297154 1 281587167 2672151961961601596 74 14 3 17 1371 46 1 8 6 133118118979792922312569561 7 9 1 14 504822 174520 3 2 6 4442915 4140921233309137282281252728124612 211232221182110 202015 1 11915 218511 2181421714141313111111111181099Page 3 of 4 Appendix B.3-1: Ranked Abundance of Benthic Macroinvertebrates Collected October 2004.TaxonSi liMaruina lanceolataTricorythodes spHelobdella spParaponyx spTarebia graniferaBrachyceraCoenagrionidaeHelicopsyche spHetaerina americanaHolorusia hesperaNepticula spOchrotrichia spPerlodidaeTipulidaeAtractides spCyphon spHelichus spHeptageniidaeLimnephilidaeMyxosargus spPtiliidaeAnax spAnisopteraChelifera/Metachela spEnallagma/Ischnura spIschnura spLiodessus spMenetus spMideopsis spAeschnidaeAnopheles spCulicidaeCurculionidaeDicranota spDolichopodidaeHemerodromia spLepidopteraNepticulidaeOrmosia spSciomyzidaeTorrenticola spAbedus spAcariBelostomatidaeBrechmorhoga mendaxCaenis spCulexDipteraErpobdella spCymbiodytaHelophorus spHydroscapha natansLeptoceridaeLibellula spMolophilus spMooreobdella spNarpus spPostelichusPsephenus falliSanfillipodytes spStigmella spStilobezzia spSyrphidaeTropisternus spUvarus spGrand TotalSD-DDH SDR-1 SDR-MT SLRR-BR SLRR-MR SMC-LCCC SMR-CP SMR-WGR SR-WS TC-TCNP Grand Total9686566555512 52151555554444412 1 44133233333133121222221122212222111111111111111111111111111912 874 800 459 916 702 900 900 912 836 18460Page 4 of 4 Appendix B.3-2: Ranked Abundance of Benthic Macroinvertebrates Collected May 2005.Taxon AHC-ECR AHC-MR CC-C CCC-805 CC-FB ESC-EF ESC-HRB GVC-WB LPC-CCR MB-RC REF-DC REF-SC2 REF-WCSimulium sp 13 89 156 244 182 514 25 533 558 202 15 98 455Baetis sp 380 365 40 387 378 286 9 219 158 296 36 318 76Chironomidae 96 107 590 247 92 81 286 29 116 214 412 233 291Oligochaeta 279 330 38 7 17 14 434 5 31 93 57 30Fallceon quilleri 70 6 16 177 18 27 17 7 7 2Ostracoda 27 10 17 7 28 52 18 11 87 1 4Hyalella sp 20 15 3 1 13 1 25 13 17 3Hydropsyche sp3 13 145Hydra sp 11 7 14 11Physa sp 2 5 39 1 24 6 1 12 8Nemouridae136Hydroptila sp 7 2 1 2 24 48 4 3Zapada sp83 1Malenka sp39 26 3Turbellaria 16 1 3 3 24 4 6 2Ironodes sp50Argia sp 1 10 7 3 15Muscidae 1 6 3 4 2 12Plecoptera19 19Sperchon sp 1 1 1 4 1 613Americorophium spRhyacophila sp12 22Cheumatopsyche sp 1 194Pericoma/Telmatoscopus 5 1 1 2 1Isoperla sp11 7Pisidium sp17Caloparyphus/Euparyphus 13 1 1Paraleptophlebia sp15Hesperophylax14Bezzia/Palpomyia 21Enallagma/Ischnura sp4Prostoma sp11Tricorythodes spAmphipod, unid.21Dolichopodidae 1 4 22Diphetor hageni11Zaitzevia sp11Dicranota sp9Psychoda sp 1Clinocera sp 116Decapoda 3 1 1Crangonyx spEphydridae 1 2 2 1Euparyphus sp51Neohermes sp7Tipula sp14Belostomatidae6Capniidae6Culicoides spCorbicula fluminea11Procambarus sp1Agabinus sp31Chelifera/Metachela sp 12Cyphon sp4Ferrissia spGammarus spLimonia sp12Peltodytes sp3Tropisternus spAgabus sp12Haploperla chilnualna sp3Hetaerina americanaHolorusia hespera11Microcylloepus sp2Psychoglypha sp3Dasyhelea sp1Page 1 of 4 Appendix B.3-2: Ranked Abundance of Benthic Macroinvertebrates Collected May 2005.Taxon AHC-ECR AHC-MR CC-C CCC-805 CC-FB ESC-EF ESC-HRB GVC-WB LPC-CCR MB-RC REF-DC REF-SC2 REF-WCDixella sp2Empididae11Fossaria sp 1 1Lebertia sp2Maruina lanceolata2Neumoura spiniloba2Torrenticola sp2Wormaldia sp11Abedus sp1Atractides sp1Berosus sp1Callibaetis sp 1Centroptilum/Procleon sp1Cordulegaster dorsalis1Culex1Dixa sp1Gumaga sp1Hydraena sp1Hydroporinae1Ilybius sp1Ischnura sp 1Lepidostoma sp1Limnophila sp1Liodessus sp 1NepticulidaeOrmosia spOxyethira sp 1Parapsyche sp1Perlodinae1Rhantus sp 1Sanfillipodytes sp1Siphlonurus sp1Stilobezzia sp1Sweltsa1Taenionema sp1Grand Total 936 942 910 930 955 949 928 891 938 918 972 929 899Page 2 of 4 Appendix B.3-2: Ranked Abundance of Benthic Macroinvertebrates Collected May 2005.TaxonSimulium spBaetis spChironomidaeOligochaetaFallceon quilleriOstracodaHyalella spHydropsyche spHydra spPhysa spNemouridaeHydroptila spZapada spMalenka spTurbellariaIronodes spArgia spMuscidaePlecopteraSperchon spAmericorophium spRhyacophila spCheumatopsyche spPericoma/TelmatoscopusIsoperla spPisidium spCaloparyphus/EuparyphusParaleptophlebia spHesperophylaxBezzia/PalpomyiaEnallagma/Ischnura spProstoma spTricorythodes spAmphipod, unid.DolichopodidaeDiphetor hageniZaitzevia spDicranota spPsychoda spClinocera spDecapodaCrangonyx spEphydridaeEuparyphus spNeohermes spTipula spBelostomatidaeCapniidaeCulicoides spCorbicula flumineaProcambarus spAgabinus spChelifera/Metachela spCyphon spFerrissia spGammarus spLimonia spPeltodytes spTropisternus spAgabus spHaploperla chilnualna spHetaerina americanaHolorusia hesperaMicrocylloepus spPsychoglypha spDasyhelea spSD-DDH SDR-1 SDR-MT SLRR-BR SLRR-MR SMR-CP SMR-WGR SR-94 SR-WS TC-TCNP TJ-DM Grand Total709 507 543 77 462 225 216 377 353 358 6911151 2 201 139 356 164 465 67 21 10 452479 84 48 93 54 117 123 166 72 470 61 416137 21 290 31 23 18 183 8 7 2 19555 2 108 111 2 352 62 107 10966 4 4 1 3 279 61 6202 102 7 218 19 154 2 6152201184122 1 1 1 15919 4 2 8 18 1491361 6 6 2 11 3 120846811615031141131 14115238381123 2363434343229211 16211817116151473 1391313 5 2 1311 213144121212111198982187717177117662462152254144444414144433331313312Page 3 of 4 Appendix B.3-2: Ranked Abundance of Benthic Macroinvertebrates Collected May 2005.TaxonSi liDixella spEmpididaeFossaria spLebertia spMaruina lanceolataNeumoura spinilobaTorrenticola spWormaldia spAbedus spAtractides spBerosus spCallibaetis spCentroptilum/Procleon spCordulegaster dorsalisCulexDixa spGumaga spHydraena spHydroporinaeIlybius spIschnura spLepidostoma spLimnophila spLiodessus spNepticulidaeOrmosia spOxyethira spParapsyche spPerlodinaeRhantus spSanfillipodytes spSiphlonurus spStilobezzia spSweltsaTaenionema spGrand TotalSD-DDH SDR-1 SDR-MT SLRR-BR SLRR-MR SMR-CP SMR-WGR SR-94 SR-WS TC-TCNP TJ-DM Grand Total2222222211111111111111111111111111111950 932 953 948 936 957 899 926 910 942 84 21534Page 4 of 4 Appendix B.4-1: Top Five Most Abundant Taxa of Benthic Macroinvertebrates Collected October 2004. Station 1st 2nd 3rd 4th 5th Oligochaeta Corbicula fluminea Hyalella sp Turbellaria Chironomidae 28%16% 15%9% 8% Hyalella sp Argia sp Prostoma sp Oligochaeta Chironomidae 36%21%8%6% 5% Fallceon quilleri Baetis sp Caloparyphus/Euparyphus Chironomidae Hyalella sp 38% 31%14%12%2% Sphaeriidae Ostracoda Oligochaeta Hyalella sp Physa sp 35% 31%12%8% 4% Ostracoda Prostoma sp Turbellaria Caloparyphus/Euparyphus Sperchon sp 32% 17%17%9%7% Chironomidae Ostracoda Physa sp Caloparyphus/Euparyphus Argia sp 31%27% 20% 7%6% Simulium sp Cheumatopsyche sp Hydropsyche sp Chironomidae Baetis sp 30% 24% 17% 9% 7% Oligochaeta Hyalella sp Ostracoda Turbellaria Chironomidae 29%26% 24%9% 6% Chironomidae Physa sp Argia sp Oligochaeta Fossaria sp 22%19%9% 8%7% Fallceon quilleri Oligochaeta Argia sp Baetis sp Hyalella sp 34% 17% 10% 7%7% Fossaria sp Oligochaeta Physa sp Ceratopogonidae Muscidae 53%20%10%5% 2% Capniidae Pisidium sp Malenka sp Zapada sp Oligochaeta 20%18%9% 8%7% Micrasema sp Hydropsyche sp Zaitzevia sp Baetis sp Simulium sp 22%21% 12% 11% 10% Hydropsyche sp Micrasema sp Zaitzevia sp Argia sp Cheumatopsyche sp 22%18%14% 11% 8% Simulium sp Chironomidae Cheumatopsyche sp Hydroptila sp Fallceon quilleri 33% 25% 11% 11% 5% Simulium sp Turbellaria Hyalella sp Corbicula fluminea Prostoma sp 31% 14%13% 11% 10% Chironomidae Dasyhelea sp Hydroptila sp Corbicula fluminea Argia sp 17% 12% 10%10%8% Corixidae Oligochaeta Trichocorixa sp Decapoda Corbicula fluminea 26%21%21% 16% 5% Simulium sp Crangonyx sp Hyalella sp Chironomidae Oligochaeta 30% 21%20%9% 7% Baetis sp Hyalella sp Fallceon quilleri Cheumatopsyche sp Simulium sp 30%21%20% 8% 8% Simulium sp Baetis sp Chironomidae Fallceon quilleri Sperchon sp 62% 19% 8% 6% 1% Hydropsyche sp Cheumatopsyche sp Baetis sp Chironomidae Simulium sp 32% 18% 17% 15% 3% Simulium sp Chironomidae Oligochaeta Ostracoda Procambarus sp 43% 36% 15%3% 1% Hyalella sp Dasyhelea sp Chironomidae Argia sp Ostracoda 22%20% 19% 14%9% SR-WS TC-TCNP SDR-MT SLRR-BR SLRR-MR SMC-LCCC REF-SC2 SD-DDH SDR-1 SMR-WGR SMR-CP LPC-CCR MB-RC REF-DC REF-DLC3 Highly tolerant taxa (TV=8,9,10) are highlighted in red; Highly intolerant taxa (TV=0,1,2) are highlighted in blue AHC-ECR AHC-MR BVR-CB CC-C CCC-805 CC-FB ESC-EF ESC-HRB GVC-WB Page 1 of 1 Appendix B.4-2: Top Five Most Abundant Taxa of Benthic Macroinvertebrates Collected May 2005. Station 1st 2nd 3rd 4th 5th Baetis sp Oligochaeta Chironomidae Fallceon quilleri Ostracoda 40% 31% 9% 6%4% Baetis sp Oligochaeta Simulium sp Chironomidae Ostracoda 40% 33% 11% 11%1% Chironomidae Simulium sp Baetis sp Oligochaeta Physa sp 64% 18% 5% 5%4% Baetis sp Chironomidae Simulium sp Fallceon quilleri Oligochaeta 43% 26% 25% 2% 1% Baetis sp Fallceon quilleri Simulium sp Chironomidae Physa sp 40% 20% 18% 8%3% Simulium sp Baetis sp Chironomidae Cheumatopsyche Fallceon quilleri 57% 28% 8% 2% 2% Oligochaeta Chironomidae Ostracoda Hydroptila sp Simulium sp 48% 30%6%3% 3% Simulium sp Baetis sp Hydroptila sp Chironomidae Ostracoda 62% 23% 6% 3%2% Simulium sp Baetis sp Chironomidae Oligochaeta Hyalella sp 59% 16% 11% 4%2% Baetis sp Simulium sp Chironomidae Ostracoda Oligochaeta 32% 24% 22%10%10% Chironomidae Nemouridae Zapada sp Oligochaeta Ironodes sp 43%14% 8%6%5% Baetis sp Chironomidae Hydropsyche sp Simulium sp Oligochaeta 32% 26% 17% 10% 4% Simulium sp Chironomidae Baetis sp Rhyacophila sp Plecoptera 54% 31% 7%2% 2% Simulium sp Baetis sp Chironomidae Fallceon quilleri Cheumatopsyche sp 75% 16% 8% 1% 1% Simulium sp Hydra sp Chironomidae Hyalella sp Oligochaeta 52% 15% 10%10%4% Simulium sp Baetis sp Fallceon quilleri Chironomidae Oligochaeta 57% 21% 11% 6% 2% Oligochaeta Hyalella sp Baetis sp Fallceon quilleri Chironomidae 31%22%14% 12% 10% Simulium sp Baetis sp Chironomidae Oligochaeta Hyalella sp 49% 40% 5% 3%2% Fallceon quilleri Simulium sp Baetis sp Chironomidae Hydropsyche sp 37% 25% 16% 11% 2% Baetis sp Simulium sp Chironomidae Fallceon quilleri Oligochaeta 53% 22% 14% 7% 2% Simulium sp Oligochaeta Chironomidae Fallceon quilleri Baetis sp 38% 20% 20% 12% 7% Simulium sp Ostracoda Hyalella sp Chironomidae Baetis sp 38%30% 17%9% 2% Chironomidae Simulium sp Ostracoda Physa sp Baetis sp 51% 36%6% 2%1% Chironomidae Psychoda sp Pericoma/Telmatoscopu Culicoides sp Muscidae 73%10%7% 5% 2% Highly tolerant taxa (TV=8,9,10) are highlighted in red; Highly intolerant taxa (TV=0,1,2) are highlighted in blue TJ-DM SR-94 SR-WS TC-TCNP SLRR-BR SLRR-MR SMR-CP SMR-WGR REF-WC SD-DDH SDR-1 SDR-MT LPC-CCR MB-RC REF-DC REF-SC2 CC-FB ESC-EF ESC-HRB GVC-WB AHC-ECR AHC-MR CC-C CCC-805 Appendix B.5-1: Biological Metric Calculations for Benthic Macroinvertebrates Collected October 2004.Metric AHC-ECR AHC-MR BVR-CB CC-C CC-FB CCC-805 ESC-EF ESC-HRB GVC-WB LPC-CCR MB-RC REF-DC REF-DLC3 REF-SC2Taxa Richness 22 23 10 17 13 21 14 16 24 20 23 33 32 27Ephemeropteran Taxa21211121220531Plecopteran Taxa00000000000611Trichopteran Taxa11101131310575EPT Taxa3231225253016118Dipteran Taxa783467447912886Non Insect Taxa 10 12 3 103948978475% EPT 6% 0% 69% 0% 3% 4% 50% 1% 10% 42% 0% 60% 60% 54%Sensitive EPT % 0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 52% 27% 18%Shannon Diversity 2.3 2.2 1.5 1.8 1.7 2.1 1.9 1.8 2.5 2.2 1.7 2.6 2.4 2.4Margalef Diversity 3.6 3.8 1.5 2.7 1.9 3.3 2.1 2.3 4.0 3.5 3.9 5.1 5.1 4.1Tolerance Value 6.6 7.2 5.1 7.4 7.1 7.0 5.3 6.5 6.4 5.4 6.0 3.9 4.0 4.1% Dominant Taxa 28% 36% 38% 35% 30% 34% 31% 29% 21% 34% 53% 19% 23% 21%% Chironomidae 8% 4% 13% 4% 30% 2% 9% 5% 21% 6% 1% 7% 3% 2%% Intolerant Organisms 0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 44% 26% 23%% Tolerant Organisms 42% 54% 2% 80% 49% 64% 3% 52% 29% 12% 12% 20% 3% 1%% Grazer 0% 0% 1% 0% 3% 2% 2% 0% 6% 0% 0% 7% 36% 34%% Collector Gatherer 63% 49% 97% 53% 66% 52% 20% 86% 41% 75% 24% 21% 20% 15%% Collector Filterer 19% 2% 1% 34% 2% 1% 72% 0% 4% 10% 0% 18% 33% 37%% Predator 12% 34% 1% 8% 8% 42% 6% 11% 18% 12% 8% 10% 9% 12%% Shredder 2% 3% 0% 1% 0% 0% 0% 0% 4% 0% 1% 40% 1% 2%% Scraper 5% 11% 0% 4% 21% 3% 1% 2% 28% 3% 62% 7% 13% 17%% Other 0% 0% 1% 1% 3% 3% 1% 0% 6% 1% 1% 1% 25% 17%Estimated Total Abundance/ft218 65 50 267 806 64 360 913 171 17 21 127 56 73Page 1 of 2 Appendix B.5-1: Biological Metric Calculations for Benthic Macroinvertebrates Collected October 2004.MetricTaxa RichnessEphemeropteran TaxaPlecopteran TaxaTrichopteran TaxaEPT TaxaDipteran TaxaNon Insect Taxa% EPTSensitive EPT %Shannon DiversityMargalef DiversityTolerance Value% Dominant Taxa% Chironomidae% Intolerant Organisms% Tolerant Organisms% Grazer% Collector Gatherer% Collector Filterer% Predator% Shredder% Scraper% OtherEstimated Total Abundance/ft2SD-DDH SDR-1 SDR-MT SLRR-BR SLRR-MR SMR-CP SMC-LCCC SMR-WGR SR-WS TC-TCNP20 17 23 14 18 13 18 21 9 182000132210000000000041202236016120355811551166565310898582775430% 2% 11% 0% 9% 27% 60% 71% 0% 3%1% 2% 0% 0% 0% 0% 0% 1% 0% 0%2.0 2.2 2.7 1.9 2.0 1.2 2.0 2.0 1.2 2.13.0 2.5 3.6 2.6 3.0 2.0 2.8 3.4 1.5 2.85.9 6.7 6.8 7.1 5.9 5.7 5.7 5.0 6.0 6.832% 29% 15% 26% 27% 62% 31% 30% 45% 22%26% 5% 15% 0% 9% 8% 3% 14% 35% 18%0% 0% 0% 0% 0% 0% 0% 1% 0% 0%7% 42% 33% 59% 24% 2% 22% 4% 5% 32%12% 2% 11% 0% 0% 0% 0% 3% 0% 3%38% 26% 42% 28% 66% 34% 78% 34% 54% 73%47% 41% 11% 5% 30% 64% 17% 55% 45% 0%3% 25% 25% 47% 2% 1% 4% 7% 0% 19%0% 0% 2% 18% 3% 0% 0% 1% 1% 4%1% 4% 6% 0% 0% 0% 1% 2% 0% 0%12% 2% 12% 0% 0% 0% 0% 1% 0% 3%184 125 88 143 127 326 40 160 151 101Page 2 of 2 Appendix B.5-2: Biological Metric Calculations for Benthic Macroinvertebrates Collected May 2005.Metric AHC-ECR AHC-MR CC-C CC-FB CCC-805 ESC-EF ESC-HRB GVC-WB LPC-CCR MB-RC REF-DC REF-SC2 REF-WCTaxa Richness 17 13 12 16 14 11 16 12 14 9 29 24 19Ephemeropteran Taxa2212222222422Plecopteran Taxa0000000000823Trichopteran Taxa1010131121432EPT Taxa32223533431677Dipteran Taxa5447535442655Non Insect Taxa8765547553470% EPT 49% 39% 5% 59% 44% 35% 7% 31% 19% 33% 46% 54% 12%Sensitive EPT % 0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 38% 3% 4%Shannon Diversity 1.7 1.5 1.2 1.8 1.4 1.2 1.6 1.2 1.3 1.6 2.2 1.9 1.3Margalef Diversity 2.6 1.9 1.8 2.5 2.1 1.6 2.5 1.7 2.2 1.3 4.5 3.8 2.3Tolerance Value 5.2 5.3 6.0 5.4 5.6 5.6 5.6 5.8 5.8 5.8 4.4 5.2 5.6% Dominant Taxa 41% 39% 64% 40% 42% 54% 46% 60% 60% 32% 42% 34% 51%% Chironomidae 10% 12% 64% 10% 26% 9% 31% 3% 12% 22% 42% 25% 32%% Intolerant Organisms 0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 31% 4% 5%% Tolerant Organisms 5% 3% 7% 9% 2% 1% 10% 4% 3% 11% 2% 3% 0%% Grazer 1% 0% 0% 0% 0% 0% 3% 5% 0% 0% 5% 2% 0%% Collector Gatherer 94% 89% 75% 77% 72% 42% 90% 33% 36% 75% 54% 63% 41%% Collector Filterer 1% 9% 18% 19% 27% 56% 3% 61% 62% 23% 3% 27% 51%% Predator 4% 1% 3% 2% 1% 1% 3% 1% 2% 1% 5% 3% 6%% Shredder 0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 28% 3% 0%% Scraper 0% 1% 4% 3% 0% 0% 1% 0% 0% 1% 5% 3% 0%% Other 1% 0% 0% 0% 0% 0% 3% 5% 1% 0% 2% 0% 0%Estimated Total Abundance/ft2179 209 841 188 267 859 542 644 503 474 542 1433 271Page 1 of 2 Appendix B.5-2: Biological Metric Calculations for Benthic Macroinvertebrates Collected May 2005.MetricTaxa RichnessEphemeropteran TaxaPlecopteran TaxaTrichopteran TaxaEPT TaxaDipteran TaxaNon Insect Taxa% EPTSensitive EPT %Shannon DiversityMargalef DiversityTolerance Value% Dominant Taxa% Chironomidae% Intolerant Organisms% Tolerant Organisms% Grazer% Collector Gatherer% Collector Filterer% Predator% Shredder% Scraper% OtherEstimated Total Abundance/ft2SD-DDH SDR-1 SDR-MT SLRR-BR SLRR-MR SMR-CP SMR-WGRSR-94 SR-WS TC-TCNP TJ-DM7 12 14 11 9 17 11 12 11 13 721222332110000000000002010021111041322543220224336454561866432455116% 0% 33% 25% 39% 58% 59% 19% 3% 2% 0%0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 0%0.8 1.5 1.3 1.8 1.2 1.7 1.3 1.6 1.5 1.2 1.00.9 1.9 2.1 1.9 1.3 2.6 1.6 1.8 1.8 1.9 1.45.8 6.1 5.6 5.8 5.6 5.0 5.3 5.5 6.9 6.2 6.275% 55% 57% 31% 49% 37% 52% 41% 39% 50% 73%8% 9% 5% 10% 6% 12% 14% 18% 8% 50% 73%0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 0%0% 15% 2% 25% 2% 1% 0% 2% 48% 9% 10%0% 0% 1% 0% 0% 1% 0% 0% 1% 0% 0%24% 25% 40% 91% 50% 71% 75% 57% 59% 59% 92%76% 58% 57% 8% 49% 26% 24% 41% 39% 38% 0%0% 15% 1% 1% 0% 3% 1% 1% 0% 1% 7%0% 0% 0% 0% 0% 0% 0% 0% 0% 0% 0%0% 3% 1% 0% 0% 0% 0% 1% 0% 2% 0%0% 0% 1% 0% 0% 1% 0% 0% 1% 0% 0%4060 428 1028 252 501 499 1117 359 753 1043 5Page 2 of 2 Appendix B.6-1: Physical Habitat Quality Scores. October 2004.Measure SMR-WGR SMR-CP SLRR-MR SLRR-BR AHC-MR AHC-ECR ESC-HRB ESC-EF GVC-WB SD-DDH LPC-CCR CCC-8051. Instream Cover 16 1786847198617132. Embeddedness 15 17 3 4 15 2 9 19 14 11 18 123. Velocity / Depth Regimes 16 15 12 6 12 8 7 18 12 12 14 124. Sediment Deposition 17 13459291914171835. Channel Flow 17 17 13 4 8 17 19 19 6 16 18 156. Channel Alteration 20 16 19 19 18 10 11 17 14 20 17 137. Riffle Frequency 17 12718571612716158. Bank Stability 18 12 12 16 8 12 16 18 8 20 16 129. Vegetation Protection 20 18 20 18 6 12 16 19 10 18 14 1210. Riparian Vegetative Zone 20 18 18 20 16 12 12 18 11 19 12 12Total 176 155 116 99 108 84 113 182 109 146 160 119Measure MB-RC TC-TCNP SDR-MT SDR-1 CC-FB SR-WS SMC-LCCC CC-C REF-SC2 REF-DLC3 REF-DC1. Instream Cover 16 16 18 14 14 8 16 15 18 16 192. Embeddedness 18 16 17 6 18 7 19 5 16 17 173. Velocity / Depth Regimes 7 11 12 8 13 12 16 7 15 16 84. Sediment Deposition 16 13 12 8 16 9 18 3 15 13 185. Channel Flow 6 8 6 15 10 18 18 3 16 18 116. Channel Alteration 20 20 20 17 16 19 20 12 17 20 207. Riffle Frequency 8 8 14 2 17 8 14 6 19 18 188. Bank Stability 18 12 20 16 14 16 20 16 18 18 209. Vegetation Protection 18 18 20 19 14 12 6 16 14 18 2010. Riparian Vegetative Zone 19 18 19 15 15 18 16 10 18 19 20Total 146 140 158 120 147 127 163 93 166 173 171Page 1 of 1 Appendix B.6-2: Physical Habitat Quality Scores. May 2005.Measure SMR-WGR SMR-CP SLRR-MR SLRR-BR AHC-MR AHC-ECR ESC-HRB ESC-EF GVC-WB SD-DDH LPC-CCR CCC-8051. Instream Cover 16 18 12 8 12 3 3 17 15 17 16 142. Embeddedness 13 15 4 2 14 0 1 14 15 15 17 183. Velocity / Depth Regimes 18 17 16 10 13 10 6 19 13 18 15 144. Sediment Deposition 9 14 7 1 13 1 2 18 18 16 18 175. Channel Flow 19 17 17 18 11 19 18 19 16 19 16 96. Channel Alteration 20 17 18 19 19 15 8 19 14 19 16 137. Riffle Frequency 10 14 6 3 12 1 2 17 17 15 16 158. Bank Stability 18 10 14 6 12 6 15 12 9 18 16 89. Vegetation Protection 19 12 18 16 16 16 13 10 9 12 14 1410. Riparian Vegetative Zone 20 19 18 18 14 10 11 16 8 19 14 4Total 162 153 130 101 136 81 79 161 134 168 158 126Measure MB-RC TC-TCNP SDR-MT SDR-1 CC-FB SR-WS SR-94 CC-C TJ-DM REF-SC2 REF-WC REF-DC1. Instream Cover 18 18 19 14 15 8 4 14 12 19 16 162. Embeddedness 18 17 17 15 18 3 3 10 7 17 17 173. Velocity / Depth Regimes 14 15 18 11 14 9 11 12 11 16 14 114. Sediment Deposition 19 15 18 13 17 13 5 9 3 17 15 145. Channel Flow 15 15 18 19 10 13 15 10 17 16 11 176. Channel Alteration 15 16 19 17 11 20 14 15 17 16 17 207. Riffle Frequency 16 13 16 2 15 8 3 12 4 18 16 168. Bank Stability 15 14 18 18 14 15 16 16 8 16 18 169. Vegetation Protection 16 16 18 20 10 18 18 18 10 12 16 1810. Riparian Vegetative Zone 14 12 20 15 12 18 18 12 9 14 16 20Total 160 151 181 144 136 125 107 128 98 161 156 165Page 1 of 1 Appendix B.7-1: Water Quality Data. October 2004. Parameter pH Specific Conductance (mS/cm) Water Temperature (C) Chlorophyll (mg/l) Dissolved Oxygen (mg/l) Average Depth (In) Average Velocity (ft/sec) Elevation (ft above sea level) SMR-WGR 7.8 1.224 19.1 1.0 9.85 6.0 1.6 500 SMR-CP 7.7 1.461 12.6 1.1 12.33 5.0 1.9 110 SLRR-MR 7.7 2.918 17.9 3.1 8.06 8.0 1.4 70 SLRR-BR 7.3 2.822 18.0 22.2 4.13 8.0 0.1 10 AHC-MR 7.4 2.297 17.9 2.8 9.57 1.3 0.8 360 AHC-ECR 7.9 2.341 15.8 4.9 6.75 6.0 1.9 40 ESC-HRB 8.2 1.868 18.2 6.2 4.80 7.0 1.5 630 ESC-EF 8.4 1.938 17.6 6.1 6.71 5.0 3.6 360 GVC-WB 7.9 2.442 17.6 2.6 4.61 3.0 0.9 340 SD-DDH 8.0 3.059 20.1 3.0 6.90 4.0 1.8 170 LPC-CCR 7.4 1.636 15.1 6.2 9.12 6.0 2.7 440 CCC-805 8.2 3.738 23.7 6.2 9.96 4.0 1.6 80 MB-RC 8.1 3.651 19.8 5.7 6.22 2.0 0.9 65 TC-TCNP 7.4 7.992 18.4 2.3 3.77 2.0 0.9 55 SDR-MT 7.5 6.018 19.4 2.9 3.88 3.0 0.8 180 SDR-1 7.7 3.825 21.4 5.3 5.10 5.3 2.3 10 CC-FB 7.7 4.635 20.5 2.3 7.83 3.0 1.2 220 SR-WS 7.6 3.830 16.3 6.3 7.91 7.3 1.9 40 SMC-LCCC 7.5 0.994 14.6 6.6 6.94 7.3 2.4 320 CC-C 7.2 0.906 12.8 6.8 4.32 2.0 0.4 2550 REF-SC2 8.2 1.944 14.0 2.4 11.62 4.0 3.2 440 REF-DLC3 7.4 1.655 13.7 1.9 11.65 10.0 3.1 280 REF-DC 7.1 0.363 7.7 2.3 10.45 2.0 0.5 4950 Page 1 of 1 Appendix B.7-2: Water Quality Data. May 2005. Parameter pH Specific Conductance (mS/cm) Water Temperature (C) Chlorophyll (mg/l) Dissolved Oxygen (mg/l) Average Depth (cm) Average Velocity (ft/sec) Elevation (ft above sea level) SMR-WGR 8.4 0.952 24.6 2.0 13.48 9.3 2.8 500 SMR-CP 8.4 1.006 23.1 0.3 16.80 9.0 2.9 110 SLRR-MR 7.9 1.582 17.5 1.8 9.80 10.3 2.1 70 SLRR-BR 7.9 1.529 19.5 4.7 11.05 4.3 2.1 10 AHC-MR 7.9 1.733 18.0 3.6 9.85 3.3 2.6 360 AHC-ECR 8.0 2.622 25.0 1.3 9.43 3.7 1.6 40 ESC-HRB 8.4 1.891 29.7 2.8 13.15 6.0 0.8 630 ESC-EF 8.4 1.920 21.2 2.3 10.66 7.0 1.6 360 GVC-WB 7.9 2.038 18.9 3.1 9.22 5.0 1.2 340 SD-DDH 7.8 1.040 17.3 6.2 8.40 7.0 1.8 170 LPC-CCR 7.6 0.962 18.3 6.5 8.97 4.0 2.1 440 CCC-805 7.8 2.263 18.5 2.7 11.41 3.0 2.0 80 MB-RC 7.7 3.196 15.4 2.9 8.80 3.3 1.3 65 TC-TCNP 7.8 3.594 18.5 3.4 9.19 2.0 1.4 55 SDR-MT 8.2 1.691 18.8 4.9 10.59 8.7 1.6 180 SDR-1 7.4 1.547 20.8 8.2 7.84 5.3 1.8 10 CC-FB 7.6 2.382 22.5 0.2 10.10 3.2 1.0 220 SR-WS 7.8 3.523 19.4 10.0 8.91 5.3 1.6 40 SR-94 8.0 0.757 21.9 4.1 20.30 5.7 0.9 320 CC-C 7.6 1.190 14.6 6.1 18.01 3.3 1.0 2550 TJ-DM 7.1 1.584 17.8 4.7 8.65 4.0 1.3 25 REF-SC2 7.7 1.185 15.5 0.5 10.57 4.0 2.5 440 REF-WC 8.1 0.363 17.9 0.8 19.08 1.3 0.8 2200 REF-DC 7.7 0.178 10.7 2.2 10.87 5.0 1.4 4950 Page 1 of 1 Appendix B.8-1: Index of Biotic Integrity Scores for San Diego Bioassessment Monitoring Sites. October 2004.Metric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreREF-DC 59 Very Good39%1013%87%9588544%10169REF-DLC3 50 Good53%1023%619%6478526%10116REF-SC2 48 Good52%1019%714%7586323%984GVC-WB 21 Poor45%1040%224%400520%053MB-RC 21 Poor24%1035%326%324410%000SDR-MT 20 Poor53%1037%333%200740%021SMR-WGR 20 Poor89%232%415%700521%184TC-TCNP 20 Poor73%621%721%500520%010CCC-805 18 Poor53%1044%143%012740%021CC-FB 17 Poor68%723%628%300200%021BVR-CB 15 Poor98%025%610%800200%031ESC-EF 15 Poor92%231%419%600300%053SMC-LCCC 15 Poor94%136%316%700410%053SMR-CP 15 Poor98%015%823%400300%053AHC-MR 13 Very Poor51%1051%038%000520%021SD-DDH 13 Very Poor85%339%224%400410%063SLRR-BR 13 Very Poor34%1035%363%000300%000LPC-CCR 12 Very Poor85%335%320%500200%031AHC-ECR 10 Very Poor81%445%136%100630%031ESC-HRB 10 Very Poor86%349%034%124410%021SDR-1 8 Very Poor68%756%038%000410%010CC-C 6 Very Poor87%362%038%000630%010SLRR-MR 3 Very Poor96%148%040%000410%031SR-WS 1 Very Poor99%051%034%100000%010Monitoring ReachTotal IBI ScoreIBI Rating% CF+CG% Intolerant EPT Taxa% Non-Insect Taxa % Tolerant Taxa Coleoptera Taxa Predator TaxaPage 1 of 1 Appendix B.8-2: Index of Biotic Integrity Scores for San Diego Bioassessment Monitoring Sites. May 2005.Metric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreMetric scoreIBI scoreREF-DC 56 Very Good57%1015%811%82410731%10169REF-WC 36 Fair91%20%106%935855%263REF-SC2 25 Poor90%229%524%424744%274SMR-CP 24 Poor96%120%78%912520%053SD-DDH 17 Poor100%013%813%700000%042SMR-WGR 17 Poor99%018%79%800300%042TJ-DM 17 Poor92%214%814%700200%000AHC-ECR 12 Very Poor95%145%125%412630%031ESC-EF 12 Very Poor99%034%420%500200%053CC-FB 10 Very Poor95%132%438%012520%021MB-RC 10 Very Poor98%032%422%500200%031CCC-805 9 Very Poor98%037%325%400410%031LPC-CCR 9 Very Poor97%037%323%400300%042ESC-HRB 8 Very Poor93%142%230%212300%031SLRR-MR 8 Very Poor100%046%118%600100%021SR-94 8 Very Poor98%035%324%400300%031SDR-MT 6 Very Poor98%041%230%200410%031AHC-MR 5 Very Poor98%053%029%300410%021GVC-WB 5 Very Poor94%144%130%200200%031SR-WS 5 Very Poor98%044%128%300200%021CC-C 4 Very Poor93%151%033%200300%021SDR-1 4 Very Poor83%465%040%000200%010TC-TCNP 2 Very Poor97%043%138%000300%021SLRR-BR 1 Very Poor99%054%040%000200%021Monitoring ReachTotal IBI ScoreIBI Rating% CF+CG% Intolerant EPT Taxa% Non-Insect Taxa % Tolerant Taxa Coleoptera Taxa Predator TaxaPage 1 of 1 APPENDIX C Scatterplots and Trend Data Appendix C: Scatterplots and Trends Page 1 of 48 GENERAL CHEMISTRY Appendix C: Scatterplots and Trends Page 2 of 48 94 96 98 00 02 04 0 2,000 4,000 6,000 Conductivity (μmhos/cm)94 96 98 00 02 04 0 2,000 4,000 6,000 94 96 98 00 02 04 0 2,000 4,000 6,000 94 96 98 00 02 04 0 2,000 4,000 6,000 94 96 98 00 02 04 0 2,000 4,000 6,000 94 96 98 00 02 04 0 2,000 4,000 6,000 Conductivity (μmhos/cm)94 96 98 00 02 04 0 2,000 4,000 6,000 94 96 98 00 02 04 0 2,000 4,000 6,000 94 96 98 00 02 04 0 2,000 4,000 6,000 Conductivity (μmhos/cm)94 96 98 00 02 04 0 2,000 4,000 6,000 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 2,000 4,000 6,000 Conductivity (μmhos/cm)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 3 of 48 94 96 98 00 02 04 0 1 2 3 MBAS (mg/L)94 96 98 00 02 04 0 1 2 3 94 96 98 00 02 04 0 1 2 3 94 96 98 00 02 04 0 1 2 3 94 96 98 00 02 04 0 1 2 3 94 96 98 00 02 04 0 1 2 3 MBAS (mg/L)94 96 98 00 02 04 0 1 2 3 94 96 98 00 02 04 0 1 2 3 94 96 98 00 02 04 0 1 2 3 MBAS (mg/L)94 96 98 00 02 04 0 1 2 3 4 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 1 2 3 MBAS (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 4 of 48 94 96 98 00 02 04 0 4 8 12 16 Oil and Grease (mg/L)94 96 98 00 02 04 0 4 8 12 16 94 96 98 00 02 04 0 4 8 12 16 94 96 98 00 02 04 0 4 8 12 16 94 96 98 00 02 04 0 4 8 12 16 94 96 98 00 02 04 0 4 8 12 16 Oil and Grease (mg/L)94 96 98 00 02 04 0 4 8 12 16 94 96 98 00 02 04 0 4 8 12 16 94 96 98 00 02 04 0 4 8 12 16 Oil and Grease (mg/L)94 96 98 00 02 04 0 4 8 12 16 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 4 8 12 16 Oil and Grease (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 5 of 48 94 96 98 00 02 04 4 6 8 10 pH94 96 98 00 02 04 4 6 8 10 94 96 98 00 02 04 4 6 8 10 94 96 98 00 02 04 4 6 8 10 94 96 98 00 02 04 4 6 8 10 94 96 98 00 02 04 4 6 8 10 pH94 96 98 00 02 04 4 6 8 10 94 96 98 00 02 04 4 6 8 10 94 96 98 00 02 04 4 6 8 10 pH94 96 98 00 02 04 4 6 8 10 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 4 6 8 10 pHSignificant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 6 of 48 94 96 98 00 02 04 0 200 400 2,000 4,000 Turbidity (NTU)94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 Turbidity (NTU)94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 Turbidity (NTU)94 96 98 00 02 04 0 200 400 2,000 4,000 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 200 400 600 Turbidity (NTU)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 7 of 48 94 96 98 00 02 04 0 400 800 1,200 1,600 Total Hardness (mg/L)94 96 98 00 02 04 0 400 800 1,200 1,600 94 96 98 00 02 04 0 400 800 1,200 1,600 94 96 98 00 02 04 0 400 800 1,200 1,600 94 96 98 00 02 04 0 400 800 1,200 1,600 94 96 98 00 02 04 0 400 800 1,200 1,600 Total Hardness (mg/L)94 96 98 00 02 04 0 400 800 1,200 1,600 94 96 98 00 02 04 0 400 800 1,200 1,600 94 96 98 00 02 04 0 400 800 1,200 1,600 Total Hardness (mg/L)94 96 98 00 02 04 0 400 800 1,200 1,600 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 400 800 1,200 1,600 Total Hardness (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 8 of 48 94 96 98 00 02 04 0 40 80 120 160 Biological Oxygen Demand (mg/L)94 96 98 00 02 04 0 40 80 120 160 94 96 98 00 02 04 0 40 80 120 160 94 96 98 00 02 04 0 40 80 120 160 94 96 98 00 02 04 0 40 80 120 160 94 96 98 00 02 04 0 40 80 120 160 Biological Oxygen Demand (mg/L)94 96 98 00 02 04 0 40 80 120 160 94 96 98 00 02 04 0 40 80 120 160 94 96 98 00 02 04 0 40 80 120 160 Biological Oxygen Demand (mg/L)94 96 98 00 02 04 0 40 80 120 160 Santa Margarita River 94 96 98 00 02 04 0 40 80 120 160 Biological Oxygen Demand (mg/L)Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 9 of 48 94 96 98 00 02 04 0 200 400 600 Chemical Oxygen Demand (mg/L)94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 Chemical Oxygen Demand (mg/L)94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 94 96 98 00 02 04 0 200 400 600 Chemical Oxygen Demand (mg/L)94 96 98 00 02 04 0 200 400 600 800 1,000 Santa Margarita River 94 96 98 00 02 04 0 200 400 600 Chemical Oxygen Demand (mg/L)Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 10 of 48 94 96 98 00 02 04 0 20 40 60 80 100 Dissolved Organic Carbon (mg/L)94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 Dissolved Organic Carbon (mg/L)94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 160 94 96 98 00 02 04 0 20 40 60 80 100 Dissolved Organic Carbon (mg/L)94 96 98 00 02 04 0 20 40 60 80 100 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 20 40 60 80 100 Dissolved Organic Carbon (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 11 of 48 94 96 98 00 02 04 0 20 40 60 80 100 Total Organic Carbon (mg/L)94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 100 Total Organic Carbon (mg/L)94 96 98 00 02 04 0 20 40 60 80 100 94 96 98 00 02 04 0 20 40 60 80 160 94 96 98 00 02 04 0 20 40 60 80 100 Total Organic Carbon (mg/L)94 96 98 00 02 04 0 20 40 60 80 100 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 20 40 60 80 100 Total Organic Carbon (mg/L)Not Analyzed Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 12 of 48 94 96 98 00 02 04 0 1,000 2,000 3,000 Total Dissolved Solids (mg/L)94 96 98 00 02 04 0 1,000 2,000 3,000 94 96 98 00 02 04 0 1,000 2,000 3,000 94 96 98 00 02 04 0 1,000 2,000 3,000 94 96 98 00 02 04 0 1,000 2,000 3,000 94 96 98 00 02 04 0 1,000 2,000 3,000 Total Dissolved Solids (mg/L)94 96 98 00 02 04 0 1,000 2,000 3,000 94 96 98 00 02 04 0 1,000 2,000 3,000 94 96 98 00 02 04 0 1,000 2,000 3,000 Total Dissolved Solids (mg/L)94 96 98 00 02 04 0 1,000 2,000 3,000 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 1,000 2,000 3,000 Total Dissolved Solids (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 13 of 48 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 Total Suspended Solids (mg/L)94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 Total Suspended Solids (mg/L)94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 Total Suspended Solids (mg/L)94 96 98 00 02 04 0 1,000 2,000 3,0004,000 8,000 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 1,000 2,000 3,000 4,000 Total Suspended Solids (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 14 of 48 NUTRIENTS Appendix C: Scatterplots and Trends Page 15 of 48 94 96 98 00 02 04 0 4 8 12 Ammonia as N (mg/L)94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 Ammonia as N (mg/L)94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 Ammonia as N (mg/L)94 96 98 00 02 04 0 4 8 12 Santa Margarita River 94 96 98 00 02 04 0 4 8 12 Ammonia as N (mg/L)Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 16 of 48 94 96 98 00 02 04 0 4 8 12 Nitrate (mg/L)94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 Nitrate (mg/L)94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 94 96 98 00 02 04 0 4 8 12 Nitrate (mg/L)94 96 98 00 02 04 0 4 8 12 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 4 8 12 Nitrate (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 17 of 48 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 Nitrite (mg/L)94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 Nitrite (mg/L)94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 Nitrite (mg/L)94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.4 0.8 1.2 1.6 Nitrite (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 18 of 48 94 96 98 00 02 04 0 5 10 15 20 25 Total Kjeldahl Nitrogen (mg/L)94 96 98 00 02 04 0 5 10 15 20 25 94 96 98 00 02 04 0 5 10 15 20 25 94 96 98 00 02 04 0 5 10 15 20 25 94 96 98 00 02 04 0 5 10 15 20 25 94 96 98 00 02 04 0 5 10 15 20 25 Total Kjeldahl Nitrogen (mg/L)94 96 98 00 02 04 0 5 10 15 20 25 94 96 98 00 02 04 0 5 10 15 20 25 94 96 98 00 02 04 0 5 10 15 20 25 Total Kjeldahl Nitrogen (mg/L)94 96 98 00 02 04 0 5 10 15 20 25 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 5 10 15 20 25 Total Kjeldahl Nitrogen (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 19 of 48 94 96 98 00 02 04 0 1 2 3 4 Dissolved Phosphorus (mg/L)94 96 98 00 02 04 0 1 2 3 4 94 96 98 00 02 04 0 1 2 3 4 94 96 98 00 02 04 0 1 2 3 4 94 96 98 00 02 04 0 1 2 3 4 94 96 98 00 02 04 0 1 2 3 4 Dissolved Phosphorus (mg/L)94 96 98 00 02 04 0 1 2 3 4 94 96 98 00 02 04 0 1 2 3 4 94 96 98 00 02 04 0 1 2 3 4 Dissolved Phosphorus (mg/L)94 96 98 00 02 04 0 1 2 3 4 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 1 2 3 4 Dissolved Phosphorus (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 20 of 48 94 96 98 00 02 04 0 1 2 3 4 5 Total Phosphorus (mg/L)94 96 98 00 02 04 0 1 2 3 4 5 94 96 98 00 02 04 0 1 2 3 4 5 94 96 98 00 02 04 0 1 2 3 4 5 94 96 98 00 02 04 0 1 2 3 4 5 94 96 98 00 02 04 0 1 2 3 4 5 Total Phosphorus (mg/L)94 96 98 00 02 04 0 1 2 3 4 5 94 96 98 00 02 04 0 1 2 3 4 5 94 96 98 00 02 04 0 1 2 3 4 5 Total Phosphorus (mg/L)94 96 98 00 02 04 0 1 2 3 4 5 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 1 2 3 4 5 Total Phosphorus (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 21 of 48 BACTERIOLOGICAL MEASURES Appendix C: Scatterplots and Trends Page 22 of 48 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 Enterococci (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 94 96 98 00 02 04 1,000 10,000 100,000 1,000,000 10,000,000 94 96 98 00 02 04 100 1,000 10,000 100,000 1,000,000 10,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 Enterococci (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 Enterococci (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 Santa Margarita River 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 Enterococci (MPN/100ml)Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San DieguitoRiver San Diego River Tijuana River Agua HediondaCreek PenasquitosCreek Chollas Creek Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 23 of 48 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Fecal Coliform (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Fecal Coliform (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Fecal Coliform (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Santa Margarita River 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Fecal Coliform (MPN/100ml)Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 24 of 48 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Total Coliform (MPN/100ml)94 96 98 00 02 04 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Total Coliform (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Total Coliform (MPN/100ml)94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Santa MargaritaRiver 94 96 98 00 02 04 10 100 1,000 10,000 100,000 1,000,000 10,000,000 100,000,000 Total Coliform (MPN/100ml)Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 25 of 48 PESTICIDES Appendix C: Scatterplots and Trends Page 26 of 48 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Chloropyrifos (μg/L)94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Chlorpyrifos (μg/L)94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Chlorpyrifos (μg/L)94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 0.2 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Chlorpyrifos (μg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 27 of 48 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Diazinon (μg/L)94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Diazinon (μg/L)94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Diazinon (μg/L)94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Diazinon (μg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 28 of 48 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Malathion (μg/L)94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Malathion (μg/L)94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Malathion (μg/L)94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1.6 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.2 0.4 0.6 0.8 1 Malathion (μg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 29 of 48 TOTAL METALS Appendix C: Scatterplots and Trends Page 30 of 48 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Total Antimony (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Total Antimony (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Total Antimony (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Total Antimony (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 31 of 48 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Arsenic (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Arsenic (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Arsenic (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Arsenic (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 32 of 48 94 96 98 00 02 04 0 0.001 0.002 0.003 Total Cadmium (mg/L)94 96 98 00 02 04 0 0.001 0.002 0.003 94 96 98 00 02 04 0 0.001 0.002 0.003 94 96 98 00 02 04 0 0.001 0.002 0.003 94 96 98 00 02 04 0 0.001 0.002 0.003 94 96 98 00 02 04 0 0.001 0.002 0.003 Total Cadmium (mg/L)94 96 98 00 02 04 0 0.001 0.002 0.003 94 96 98 00 02 04 0 0.001 0.002 0.003 94 96 98 00 02 04 0 0.001 0.002 0.003 Total Cadmium (mg/L)94 96 98 00 02 04 0 0.001 0.002 0.003 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.001 0.002 0.003 Total Cadmium (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 33 of 48 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Chromium (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.08 0.16 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Chromium (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Chromium (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.08 0.16 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua HediondaCreek PenasquitosCreek Chollas Creek 94 96 98 00 02 04 0 0.02 0.04 0.06 Total Chromium (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 34 of 48 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Total Copper (mg/L)94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Total Copper (mg/L)94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Total Copper (mg/L)94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.04 0.08 0.12 0.16 Total Copper (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 35 of 48 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 Total Lead (mg/L)94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 Total Lead (mg/L)94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 Total Lead (mg/L)94 96 98 00 02 04 0 0.05 0.1 0.2 0.3 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.05 0.1 0.15 0.2 Total Lead (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 36 of 48 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 Total Nickel (mg/L)94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 Total Nickel (mg/L)94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 Total Nickel (mg/L)94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.08 0.12 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 0.05 Total Nickel (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 37 of 48 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 Total Selenium (mg/L)94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 Total Selenium (mg/L)94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 Total Selenium (mg/L)94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San DieguitoRiver San Diego River Tijuana River Agua HediondaCreek PenasquitosCreek Chollas Creek 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 0.025 Total Selenium (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 38 of 48 94 96 98 00 02 04 0 0.4 0.8 1.2 Total Zinc (mg/L)94 96 98 00 02 04 0 0.4 0.8 1.2 94 96 98 00 02 04 0 0.4 0.8 1.2 94 96 98 00 02 04 0 0.4 0.8 1.2 94 96 98 00 02 04 0 0.4 0.8 1.2 94 96 98 00 02 04 0 0.4 0.8 1.2 Total Zinc (mg/L)94 96 98 00 02 04 0 0.4 0.8 1.2 94 96 98 00 02 04 0 0.4 0.8 1.2 94 96 98 00 02 04 0 0.4 0.8 1.2 Total Zinc (mg/L)94 96 98 00 02 04 0 0.4 0.8 1.2 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek PenasquitosCreek Chollas Creek 94 96 98 00 02 04 0 0.4 0.8 1.2 Total Zinc (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 39 of 48 DISSOLVED METALS Appendix C: Scatterplots and Trends Page 40 of 48 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Antimony (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Antimony (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Antimony (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Antimony (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 41 of 48 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Arsenic (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Arsenic (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Arsenic (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua HediondaCreek PenasquitosCreek Chollas Creek 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Arsenic (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 42 of 48 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 Dissolved Cadmium (mg/L)94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 Dissolved Cadmium (mg/L)94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 Dissolved Cadmium (mg/L)94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.0004 0.0008 0.0012 0.0016 0.002 Dissolved Cadmium (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 43 of 48 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Chromium (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Chromium (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Chromium (mg/L)94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San Dieguito River San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.002 0.004 0.006 0.008 0.01 Dissolved Chromium (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 44 of 48 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Copper (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Copper (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Copper (mg/L)94 96 98 00 02 04 0 0.02 0.04 0.06 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San Dieguito River San Diego River Tijuana River Agua HediondaCreek PenasquitosCreek Chollas Creek 94 96 98 00 02 04 0 0.02 0.04 0.06 Dissolved Copper (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 45 of 48 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 Dissolved Lead (mg/L)94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 Dissolved Lead (mg/L)94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 Dissolved Lead (mg/L)94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San DieguitoRiver San Diego River Tijuana River Agua HediondaCreek PenasquitosCreek Chollas Creek 94 96 98 00 02 04 0 0.004 0.008 0.012 0.016 0.02 Dissolved Lead (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 46 of 48 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 Dissolved Nickel (mg/L)94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 Dissolved Nickel (mg/L)94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 Dissolved Nickel (mg/L)94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis ReyRiver San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek PenasquitosCreek Chollas Creek 94 96 98 00 02 04 0 0.01 0.02 0.03 0.04 Dissolved Nickel (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 47 of 48 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 Dissolved Selenium (mg/L)94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 Dissolved Selenium (mg/L)94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 Dissolved Selenium (mg/L)94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 Santa MargaritaRiver Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San DieguitoRiver San Diego River Tijuana River Agua HediondaCreek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.005 0.01 0.015 0.02 Dissolved Selenium (mg/L)Significant Trend Water Quality Objective Appendix C: Scatterplots and Trends Page 48 of 48 94 96 98 00 02 04 0 0.1 0.2 0.3 Dissolved Zinc (mg/L)94 96 98 00 02 04 0 0.1 0.2 0.3 94 96 98 00 02 04 0 0.1 0.2 0.3 94 96 98 00 02 04 0 0.1 0.2 0.3 94 96 98 00 02 04 0 0.1 0.2 0.3 94 96 98 00 02 04 0 0.1 0.2 0.3 Dissolved Zinc (mg/L)94 96 98 00 02 04 0 0.1 0.2 0.3 94 96 98 00 02 04 0 0.1 0.2 0.3 94 96 98 00 02 04 0 0.1 0.2 0.3 Dissolved Zinc (mg/L)94 96 98 00 02 04 0 0.1 0.2 0.3 Santa Margarita River Escondido Creek Tecolote Creek Sweetwater River San Luis Rey River San DieguitoRiver San Diego River Tijuana River Agua Hedionda Creek Penasquitos Creek Chollas Creek 94 96 98 00 02 04 0 0.1 0.2 0.3 Dissolved Zinc (mg/L)Significant Trend Water Quality Objective APPENDIX D Dry Weather Data Land Use and MS4 Type by Watershed Appendix D.1. Dry Weather Criteria Exccedances by Land Use Type for Each Watershed Management Area. Watershed Primary Landuse Number of SitespHTurbidityConductivityAmmonia (NH3-N)Nitrate (NO3-N)Orthophosphate (PO4-P)MBASOil & GreaseCadmium, DissCopper, DissLead, DissZinc, DissChlorpyrifosDiazinonEnterococcusFecal ColiformTotal ColiformSanta Margarita Agriculture 6 6 1 Open 4 1 Residential 1 San Luis Rey Agriculture 11 1 3 2 4 2 1 4 Commercial 1 1 Open 4 1 Parks 2 1 Residential 5 4 2 Rural Residential 4 1 Carlsbad Agriculture 1 1 Commercial 33 241682 1539 Industrial 5 3 Open 6 Parks 3 2 1 Residential 59 29471471 8620 Rural Residential 5 2 1 San Dieguito Commercial 2 1 1 1 Open 2 Parks 5 3 1 1 1 1 1 Residential 21 8 5 2 6 1 1 2 2 6 Penasquitos Commercial 3 1 1 2 1 Industrial 33111 1 23 Open 1 1 Parks 1 Residential 14 3 2 3 3 1 5 1 6 Mission Bay Commercial 8 1 2 1 3 1 2 Residential 8 3 2 1 2 1 2 San Diego River Agriculture 1 1 Commercial 9 1 2 2 1 2 4 6 Industrial 5 1 1 2 Residential 37 2 7 6261 2 29212 Rural Residential 2 Pueblo San Diego Commercial 13 8 1 3 62111 1626 Parks 3 1 1 Residential 75242 1556 Sweetwater Commercial 6 1 2 1 3 Open 4 1 2 Parks 3 1 1 1 1 2 Residential 12 1 1 1 2 6 Rural Residential 5 1 3 Otay Commercial 5 2 1 2 1 1 2 3 Industrial 2 1 1 1 1 1 1 Open 1 1 Residential 9 1 1 2 1 1 3 1 4 Tijuana Agriculture 2 1 Commercial 1 1 Open 1 Residential 2 Appendix D.2. Dry Weather Criteria Exceedances by Conveyance Type for Each Watershed Management Area. Watershed Conveyance Type Number of SitespHTurbidityConductivityAmmonia (NH3-N)Nitrate (NO3-N)Orthophosphate (PO4-P)MBASOil & GreaseCadmium, DissCopper, DissLead, DissZinc, DissChlorpyrifosDiazinonEnterococcusFecal ColiformTotal ColiformSanta Margarita Earthen Channel 2 Natural Creek 11 1 6 1 San Luis Rey Concrete Channel 2 2 1 Earthen Channel 4 1 1 1 1 3 Natural Creek 19 3 1 5 1 1 2 Outlet 5 3 1 Carlsbad Catch Basin 2 1 1 Concrete Channel 14 2 2 4 1 1 Earthen Channel 5 1 1 Manhole 3 2 2 1 2 Natural Creek 36 5 3 9 1 1 Open Channel 20 2 6 3 3 1 15 Outlet 37 14371061 10615 San Dieguito Catch Basin 1 1 1 1 1 1 Concrete Channel 2 2 2 1 Earthen Channel 1 Natural Creek 6 2 Open Channel 14 6 2 1 2 Outlet 8 3 3 1 4 1 1 3 1 4 Penasquitos Concrete Channel 3 1 Natural Creek 4111 11 Outlet 14 6 2 3 1 5 1 8 1 9 Mission Bay Concrete Channel Earthen Channel 2 1 1 1 Outlet 8 4 2 1 3 3 1 4 San Diego River Catch Basin 1 1 Concrete Channel 15 3 1 1 4 1 7 Earthen Channel 2 Manhole 2 1 1 1 1 2 Natural Creek 7 1 1 2 Outlet 27 7 7 6 2 3 1 7 4 9 Pueblo San Diego Catch Basin 2 1 1 Concrete Channel 1 1 1 1 1 Manhole 5414 1 323 Outlet 15 9 1 3 5 4 2 1 1 1 7 4 8 Sweetwater Concrete Channel 6 2 1 1 2 Earthen Channel 6 2 Natural Creek 12 1 1 3 1 Outlet 10 4 1 1 1 1 1 8 Otay Catch Basin 3 2 2 2 2 Concrete Channel 2 1 1 Gutter 1 1 1 1 1 Manhole 3 2 1 1 1 Natural Creek 1 1 Outlet 6 1 2 1 1 3 1 4 Tijuana Natural Creek 4 1 Outlet 3 1 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report TABLE OF CONTENTS 1 .0 Introduction………………………………………………………….. 1 1.1 Program Goals and Objectives 2 1.2 Program Design 2 1.2.1 Prescriptive Sampling Program 2 1.2.2 Adaptive Sampling Program 3 1.3 Exceedance Criteria 3 1.3.1 Coastal Receiving Water Exceedance Criteria 3 1.3.2 Lagoon Receiving Water Exceedance Criteria 4 1.3.3 Storm Drain Exceedance Criteria 5 1.4 Sampling Frequency Reduction 7 1.5 Data Management 8 2 .0 Methods……………………………………………………………… 9 2.1 Site Selection 9 2.1.1 Coastal Site Selection 9 2.1.2 Lagoon Site Selection 10 2.2 Sampling Frequency 11 2.3 Sampling Procedures 11 2.3.1 Sample Collection 12 2.4 Laboratory Analysis 12 2.5 Data Analysis 13 2.5.1 Lab Data 13 2.5.2 Visual Observations 13 2.5.3 Data Transfer Templates 14 2.6 Follow-up Activities 14 3.0 Results………………………………………………………………… 15 3.1 Coastal Storm Drains Discharging to Ocean or Bay 15 3.1.1 Coastal Receiving Water Storm Drain Exceedances 19 3.1.2 Coastal Storm Drain Exceedances 22 3.2 Storm Drains Discharging to Lagoons 28 3.2.1 Lagoon Receiving Water Exceedances 30 3.2.2 Lagoon Storm Drain Exceedances 34 3.3 95th Percentile Storm Drain Exceedance Criteria 37 3.4 2003-2004 Sampling Frequency Reduction Calculation 37 4 .0 Discussion……………………………………………………………. 39 4.1 Coastal Storm Drains and Receiving Water 39 4.2 Lagoon Storm Drains and Receiving Water 40 4.2.1 Lagoon Frequency of Use Matrix 41 4.3 Adaptive Sampling Diagrams 45 4.3.1 Coastal Adaptive Diagrams 47 4.3.2 Lagoon Adaptive Diagrams 47 4.4 General Trends and Seasonal Variations 55 4.5 95th Percentile Storm Drain Action Levels 56 4.5 Sampling Frequency Reduction 57 4.6 Source Investigations 57 5 .0 Conclusions and Recommendations………………………………. 72 5.1 Program Achievements 72 5.2 Program Recommendations 73 6.0 References……………………………………………………………. 76 Appendix A Adaptive Monitoring Proposal Appendix B Map of 2004-2005 CSDM Monitoring Locations Appendix C Sample Collection Standard Operating Procedures Appendix D 2004-2005 CSDM Field Data Sheet Appendix E CSDM Data Transfer Template Appendix F 2004-2005 CSDM Coastal Data Appendix G 2004-2005 CSDM Lagoon Data Appendix H Data Screening Protocol Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report SECTION 1 - INTRODUCTION 1.0 Introduction The Municipal Stormwater Permit (Order 2001-01, Attachment B.II.C), requires that the San Diego Copermittees (Copermittees) establish a Coastal Storm Drain Outfall Monitoring Program to determine the impacts that storm drains have on coastal receiving waters. Development of such a program must meet the following conditions: 1. The program must include rationale and criteria for selecting the storm drain outfalls to be monitored. 2. The program must include the collection and analysis of total and fecal coliform and enterococci bacterial indicators. 3. Samples must be collected at both the storm drain outfall and in the receiving water in ankle to knee-deep water. 4. Samples must be collected during both the dry and wet weather seasons. 5. The Copermittees must report exceedances of public health standards for bacteria in coastal receiving waters to the County Department of Environmental Health as soon as possible after discovery. Seven coastal cities in San Diego County implemented the 2004-2005 CSDM Program. The Copermittees include the cities of Oceanside, Carlsbad, Encinitas, Solana Beach, Del Mar, San Diego, and the San Diego Unified Port District1. The following discussion of the Coastal Storm Drain Monitoring Program will use the term Copermittees to refer specifically to the above entities and will not include the non-coastal stormwater copermittees. The Copermittees’ Coastal Storm Drain Monitoring (CSDM) program was designed to meet the Permit requirements by monitoring bacteria levels in urban runoff from coastal and lagoon outfalls, and evaluating the relationship between storm drain discharges and exceedances of bacteriological water quality standards in the coastal receiving waters. This program included sampling of both storm drains and adjacent receiving waters at coastal beaches and in lagoons. 1 The cities of Coronado and Imperial Beach do not currently conduct coastal storm drain monitoring as identified in this program. The City of Coronado monitors beach bacteriological water quality on a weekly basis as part of a different sampling program. Imperial Beach has not observed storm drain discharges during dry weather within their jurisdiction. These cities will continue to assess the flow status of their coastal storm drains and participate in this program if conditions change. Section 1 - Introduction 1 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report This 2004-2005 CSDM Annual Report discusses the progress made in meeting the above stated requirements and will further identify how the Copermittees implementing the CSDM Program are remaining in compliance with the Permit. 1.1 Program Goals and Objectives The objectives of the Coastal Storm Drain Outfall Monitoring Program are the following: 1. Evaluate the impacts of coastal storm drains on the recreational beneficial uses in coastal receiving waters. 2. Determine if bacteriological water quality improves or declines seasonally and over time. 3. Develop a coastal water quality database. The CSDM Workgroup made notable progress on each of the goals during the reporting period. Many of the Workgroup’s efforts were aimed at improving consistency in both the program design and reporting. Copermittees developed a methodology to refine lagoon monitoring compared to Water Quality Objectives (WQO), standardized data sheets and databases were established, reporting limits were increased, and improved participation in meetings allowed for buy-in on all of the workgroup deliverables. The progress on each of the above stated objectives will be further discussed in Section 5 of this 2004-2005 Annual Report. 1.2 Program Design Until recently, there was very little data collected related to paired samples taken at both the storm drain and adjacent receiving waters. As such, Copermittees were unsure at what point elevated storm drain flows impacted the receiving waters. The first years of the CSDM Program were aimed at understanding that relationship and determining when or if the storm drain flows impacted the beaches. Additionally, the Municipal Stormwater Permit required bacteria sampling throughout the entire year, which is somewhat different than the public health related bacteria monitoring programs being conducted in the region today, which generally only occur during the summer months (April – October). As such, the CSDM program needed to be designed appropriately to address these issues. To address the data gaps in a reasonable yet cost-effective manner, the CSDM program utilized a two-phased approach to meet the requirements of Order 2001-01. During 2001-2002, Phase I consisted of the Copermittees monitoring the coastal receiving waters and storm drain outfalls using the prescriptive protocol defined in the original CSDM program (San Diego County Municipal Copermittees, 2001). After the initial year of the program, Phase II consisted of Section 1 - Introduction 2 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report the Copermittees moving to an adaptive sampling protocol. These protocols are discussed further below. 1.2.1 Prescriptive Sampling Program The prescriptive program design, initiated in November 2001, was based on elements of the AB 411 Recreational Water Monitoring Program conducted by the County of San Diego Department of Environmental Health (DEH). The prescriptive protocol included the collection of paired samples at flowing storm drain outlets and in corresponding coastal or lagoon receiving water. Samples were collected monthly during the non-AB 411 period (November 1 – March 31), and every other week during the AB 411 period (April 1 – October 31). Lagoons were incorporated into the program in November 2002. All samples were analyzed for total and fecal coliform, and Enterococcus indicators. 1.2.2 Adaptive Sampling Program The Coastal Storm Drain Monitoring Workgroup developed the Adaptive Sampling Program in 2002 and began implementation of the program on April 1, 2003. (The final Adaptive Monitoring Proposal is included as Appendix A). It is designed to address the storm drains that pose the greatest threat to recreational receiving waters most aggressively, while allocating a lower monitoring intensity to locations that exhibit consistently low bacterial levels. Thus, the adaptive strategy is intended to make efficient use of Copermittee resources by identifying and addressing high priority storm drains first and reducing sampling intensity at low priority sampling locations. 1.3 Exceedance Criteria The establishment of exceedance criteria provides a means by which Copermittees can evaluate the condition of the receiving waters and storm drains and determine whether a problem exists. It also allows copermittees the means to report issues of public health, conduct resampling, and/or initiate source investigations. Coastal receiving water, lagoon receiving water and storm drain exceedance criteria are discussed next. 1.3.1 Coastal Receiving Water Exceedance Criteria The coastal receiving water criteria was used to evaluate water quality on open coastal beaches in the San Diego Region. These criteria were established by Assembly Bill 411 (AB411) for the protection of public health. They include an evaluation of a single sample standard to assess conditions presently occurring at each site, rather than solely relying on a geometric mean. The single sample criteria are listed in Table 1-1. Section 1 - Introduction 3 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 1-1. AB 411 Criteria for Open Coastal Receiving Waters Indicator Single Sample Maximum (MPN or CFU/100 ml) Total Coliform 10,000 Fecal Coliform 400 Enterococcus 104 If any one of the three standards indicates that bacteria levels are greater than the AB411 standards, the beaches are posted with advisory signs. Sites are reported to DEH upon notification that the receiving water single sample criteria have been exceeded. Resampling of the receiving waters occurs as required through the AB 411 program. 1.3.2 Lagoon Receiving Water Exceedance Criteria The criteria used to evaluate water quality in enclosed bays and estuaries have been established in the San Diego Basin Plan (1994). These criteria will be used to identify exceedances of lagoon receiving water quality, and are identified in Table 1-2. Table 1-2 Basin Plan Water Quality Objectives for Bays and Estuaries Indicator Single Sample Objective (MPN or CFU/100 ml) Frequency of Use Total Coliform 10,000 All Fecal Coliform 400 All Enterococcus 104 Designated Beach Enterococcus 276 Light to Moderate Enterococcus 500 Infrequent As indicated, the criteria for evaluating total and fecal coliform are the AB411 criteria applied in coastal waters. The criteria for Enterococcus has been subcategorized according to frequency of use in the Basin Plan taken from United States Environmental Protection Agency Bacteriological Criteria for Water Contact Recreation. (San Diego Basin Plan, 1994) Contrary to the procedure used for reporting exceedances of ocean waters, the lagoons are not included as part of the AB 411 program and County DEH does not post the lagoon sites if they exceed the AB 411 standards. The lagoon waters, in general, are not used for recreational body contact, although they are considered REC-1 waters. It is proposed that with less parking, less amenities, less lifeguard services, beach substrate, and accessibility, there is less public Section 1 - Introduction 4 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report contact with water. This led the CSDM workgroup to justify comparing their Enterococcus monitoring results to the basin plan WQO based on frequency of use. This would then enable the Copermittees to base their source investigations and resampling efforts on the Basin Plan’s Frequency of Use numbers. Prior to the first year of sample collection in lagoons, the Coastal Copermittees stated that the water quality evaluation would be based on the AB411 standards for total and fecal coliform and the subcategories for Enterococcus may be implemented to varying extents. After one year of lagoon data collection, the data was evaluated based on the established objectives with narrative descriptions of the frequencies of use considered to implement (or not) the subcategories for Enterococcus. An explanation as to the specific frequency of use and associated criteria selected for each lagoon was included in the 2002- 2003 Coastal Storm Drain Monitoring Annual Report. During the previous (2003-2004) reporting period, the Copermittees researched the Basin Plan criteria for justification of the Frequency of Use criteria and could not find relevant support to determine when such listings may apply. Therefore, the CSDM workgroup developed a matrix by which to assess each lagoon monitoring site’s frequency of use. A complete discussion of the development of the matrix is identified in Section 4.2.1 of this report. A list of sites and their respective associated frequency of use designations for the terms of triggering resamples or investigations, is presented in Section 2. The associated Frequency of Use designation for each lagoon monitoring site is identified in Table 4-2. 1.3.3 Storm Drain Exceedance Criteria Prior to the onset of the CSDM Program, water quality criteria with which to evaluate storm drain discharges were not available. Copermittees then worked to provide a rationale for selecting storm drains to investigate. Two separate sets of storm drain criteria or action levels were developed for initiating storm drain investigations: 1) action levels triggering a storm drain investigation when the receiving water exceeds any of the three bacteria indicators and, 2) action levels that trigger storm drain investigations in the absence of a receiving water exceedance (CSDM Adaptive Sampling Program, 2003). 95th Percentile Storm Drain Action Level Criteria In the instances where there were no receiving water exceedances, Copermittees reviewed the data and made the decision to investigate the upper 5 percent of storm drains. Several reasons exist for pursuing highly contaminated drains, including the likelihood that they are sources of bacterial pollution during Section 1 - Introduction 5 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report storms and/or dry weather flows when the contents of the storm drain are flushed into the receiving water. In these circumstances, the potential detrimental impacts exist because of the high bacteria levels and source investigations will proceed accordingly. These storm drain action level criteria are applied in the circumstances identified in Table 1-3. Each year, the previous year’s data are reviewed and the 95th percentile is recalculated. The 95th percentile action levels used for the 2004-2005 reporting period are as follows: • Total Coliform 160,000 MPN/ 100 mls • Fecal Coliform 27,600 MPN/ 100 mls • Enterococcus 18,400 MPN/ 100 mls Table 1-3 Storm Drain Investigation Criteria Receiving Water Concentration Storm Drain Concentration Action < AB 411 or Basin Plan < AB 411 or Basin Plan Both the storm drain and receiving water are below the receiving water standard. No follow up action necessary. Continue sampling at Base Frequency unless Sampling Frequency Reduction Criteria are met. If met, sample at ½ Base Frequency. < AB 411or Basin Plan > AB 411 or Basin Plan and < 95th percentile Storm drain is above the receiving water regulatory standard but the receiving water is below. Storm drain is also below the 95th percentile criteria. No action necessary. Continue sampling at Base Frequency unless Sampling Frequency Reduction Criteria are met. If met, sample at ½ Base Frequency. > AB 411 or Basin Plan < AB 411 or Basin Plan Receiving water is above standard but storm drain is below. Unlikely that storm drain contamination caused the receiving water exceedance. Non-storm drain sources are likely present. Resample ASAP to confirm scenario and address potential non-storm drain sources. > AB 411 or Basin Plan > AB 411 or Basin Plan Both the storm drain and receiving water are above the receiving water standard but RW level is greater than storm drain level. This indicates that storm drain contamination may contribute to exceedance but that non-storm drain sources may predominate. Resample ASAP to confirm scenario and address both storm drain and non-storm drain sources. > AB 411 or Basin Plan > AB 411 or Basin Plan Both the storm drain and receiving water are above the receiving water standard. Storm drain appears to be a dominant contributor. Resample ASAP to confirm scenario and conduct IC/ID investigation. < AB 411 or Basin Plan > AB 411 or Basin Plan and > 95th percentile Receiving water is below the standard however; the storm drain is highly contaminated. Resample and conduct IC/ID investigation. Section 1 - Introduction 6 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report 1.4 Sampling Frequency Reduction The adaptive sampling protocol allows for reduced sampling at locations having storm drains that exhibit consistently low bacteria levels (CSDM Adaptive Sampling Program, 2003). As part of the sampling reduction protocol, minimum requirements for this reporting year were established and storm drains were reviewed, ensuring that only those storm drains having low bacteria levels would be eligible (Table 1-4). Two factors are annually assessed to determine locations where reduced sampling is appropriate: 1) a comparison of the analytical results of the three most recent paired sampling events to the numeric sampling reduction criteria and, 2) a simple analysis of the previous one year (April – March) of paired sampling data. Those storm drains where samples satisfactorily meet these requirements can be collected at ½ the base frequency (once every four weeks in the summer, once every two months in the winter) as long as they continue to meet these requirements. Table 1-4 Sampling Frequency Reduction Eligibility Requirements Minimum Eligibility Requirements for Sample Reduction* 1 3 consecutive storm drain samples with all bacterial indicators below the numeric Sampling Frequency Reduction Criteria (Table 1) 2 The three consecutive samples must be paired with receiving water samples that do not exceed AB 411 or Basin Plan standards unless the receiving water exceedance can be reasonably attributed to a non-storm drain source. 3 If > 20% of a location’s storm drain samples were above any of the Sampling Frequency Reduction Criteria during the previous year then that location is not eligible for a lower sampling frequency until the following year. * Storm drains must meet all of the requirements to be eligible for reduced sampling. Copermittee review their data annually to assess the eligibility of their locations for sampling frequency reduction. Those locations eligible for reduced sampling are submitted to the RWQCB prior to April 1 of each year. The 2004-2005 calculation of the numeric sampling frequency reduction criteria is discussed in Section 3.4 of this report. Eligible sites for the 2004-2005 reporting period are discussed in Section 4 of this report. Section 1 - Introduction 7 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report 1.5 Data Management Copermittees have made significant efforts to improve data and reporting consistency this year. Standardized field sheets have been developed (in 2002) and are being used by all coastal copermittees. The field sheets ensure similar data recording methods, and common units for data entry and statistical analysis purposes. Additionally, the field sheets utilize a format that can be easily transferable electronically, providing future efforts to move toward electronic data capture in the field. The use of standardized field sheets also influenced the creation of standard data transfer templates that have dramatically improved sharing data and manipulating data. Two Data Transfer Templates were developed; one for laboratory results, and one for visual observations. A third data transfer template is under development for static site information. These Data Transfer Templates were modeled after the Stormwater Monitoring Coalition (SMC) Guidance Document to remain consistent with other database efforts in the state. Section 1 - Introduction 8 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Section 2 - Methods 9 SECTION 2 - METHODS 2.0 Methods The CSDM program is designed primarily to assess the bacterial effects of storm drains on coastal and lagoon beaches and receiving waters, and secondarily to investigate potential sources of bacteria that may be impacting the waters. Coastal storm drain monitoring began in November 2001 with the lagoon monitoring being incorporated in November 2002. This report provides information on monitoring performed from November 1, 2004 through October 31, 2005 by the Copermittees. The methodologies used for the 2004-2005 CSDM program are discussed below, and include site selection, sampling frequency, sampling procedures, laboratory analysis, data analysis, and follow up activities. 2.1 Site Selection Site selection focused on storm drains having the greatest potential to adversely affect the bacterial water quality of coastal and lagoon receiving waters. The coastal ocean sites were established in 2001, at the onset of the CSDM program. Per correspondence with the RWQCB, Copermittees were required to begin lagoon monitoring in November 2002. Thus lagoon sites were established in the second year of the CSDM Program. It should be noted that the Coastal Storm Drain Monitoring Program was designed to assess the bacteriological water quality of local stormwater conveyances and therefore, does not include rivers and creeks. Maps of all of the coastal and lagoons sites are included as Appendix B. The adaptive sampling approach, which started in 2003, allowed for reduced sampling at locations with consistently low bacteria levels. Sites are evaluated annually for determination of sampling reduction based on the criteria identified in Section 1.4 of this report. Furthermore, each Copermittee conducts wet and dry season storm drain evaluations of inactive sites to assess whether there are additional flowing storm drains that should be included in the program. 2.1.1 Coastal Site Selection The CSDM program used the County DEH AB 411 monitoring program locations for the coastal sites. Appendix B identifies the complete list of the 2004-2005 CSDM coastal monitoring sites. The determination to use the AB411 sites was made during program development because both programs have similar criteria. The AB 411 site selection criteria were based on three principal factors: 1) the number of people using the coastal area, 2) the presence of flowing storm drains, Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report creeks, and rivers, and 3) accessibility. Sites included storm drains discharging to San Diego Bay and the Pacific Ocean. Storm drains discharging to Mission Bay have been diverted to the sanitary sewer and are not sampled as part of this CSDM program. All coastal sites were evaluated during the reporting period to determine whether the sampling reduction frequency would apply. Two Copermittees provided updates to their coastal sites during the 2004-2005 reporting period. The City of Oceanside added three sites (20-1, 20-2 and 20-3) and updated the name of one site. The City of Del Mar provided new site identification numbers for all of their sites. 2.1.2 Lagoon Site Selection Prior to the onset of lagoon sampling, Copermittees inventoried storm drains discharging into coastal lagoons and identified flowing storm drains using storm drain maps and GPS units (if available). Once inventoried, Copermittees then noted the accessibility and flow characteristics of the storm drains, and also identified locations having sensitive lagoon habitat in and around the storm drain discharge points. Storm drains were included in the program if they exhibited or had evidence of flow or a large catchment area with potential to convey urban runoff. It was noted that many of the storm drains discharging to the lagoons had very small catchment areas unlikely to convey water under dry, non-storm event conditions. These drains generally captured water from a road curbside with adjacent open space. Consistent with the AB411 beach site selection criteria, drains having little catchment area and no flow would remain in the inventory but not be monitored on a routine basis. Additionally, any sites that could potentially damage or require passing in, through, or over sensitive habitat to monitor were designated exempt from the monitoring requirements per the Regional Board staff. Appendix B identifies the complete list of the 2004-2005 CSDM lagoon monitoring sites. All lagoon sites were evaluated during this reporting period to determine whether the sampling reduction frequency would apply. Only one Copermittee provided updates to their lagoon sites during the 2004-2005 reporting period. The City of Carlsbad deleted four stations because they determined that they were either (1) not within the city’s stormwater conveyance system, (2) currently inaccessible, or (3) historically experiencing no flow and are immediately adjacent to another active site. Section 2 - Methods 10 Attachment A Coastal Storm Drain and Lagoon Monitoring 2003-2004 Annual Report 2.2 Sampling Frequency Implementation of the Coastal Storm Drain Monitoring Program was divided into two phases coinciding with non-AB 411 (November 1 – March 31) and AB 411 (April 1 – October 31) sampling periods. These intervals are referred to as the wet season and dry season periods, respectively. Paired samples were collected monthly during the wet season and every two weeks during the dry season at the coastal storm drains and lagoon sites. During the wet season, if a scheduled sample time fell within 72 hours after the completion of a rainstorm, sampling was deferred to another time during the same calendar month. If rain events occurred on a staggered basis such that there was no time during one calendar month to complete monitoring, the event was deferred to the next regularly scheduled event. If this circumstance occurred during the dry season, paired sampling was deferred until the following week. 2.3 Sampling Procedures The CSDM program developed and implemented standardized sampling procedures during the reporting period. This ensured that all Copermittees were collecting information in a manner consistent with the CSDM program objectives and in compliance with the permit. Samples were collected at all identified flowing storm drain outlets even if the discharge did not come into immediate contact with the receiving water. For example, samples were collected even if ponding occurred between the drain and the receiving water, or the storm drain discharge infiltrated into the sand before reaching the receiving water. Copermittees used their best professional judgment to determine when to collect ponded water samples. These samples were generally collected because Copermittees elected to act conservatively rather than dismiss the possibility that the ponded water could potentially (through tidal fluctuation or infiltration) affect the receiving water. Samples were not collected at the storm drain outlet and/or in the receiving water if, to get to the monitoring site, it would require the disturbance of freshwater wetland, freshwater marsh, or salt marsh habitat, or if unsafe conditions restricted sampling accessibility. Samples were not collected at either the outlet or in the receiving water if the outlet was not flowing. Additionally, samplers recorded whether the storm drain flows reached the receiving water. For coastal sites, samples were collected at the storm drain outlet and 25 yards down current in the receiving water unless unsafe conditions existed. A distance of 25 yards was used to maintain consistency with current AB411 standard sampling protocol for coastal bacteriological monitoring in California. It was necessary to collect the receiving water samples at a distance other than 25 Section 2 - Methods 11 Attachment A Coastal Storm Drain and Lagoon Monitoring 2003-2004 Annual Report yards at several locations due to accessibility factors. Lagoon sites were sampled in the receiving water mixing zone directly in front of the storm drain whenever possible. 2.3.1 Sample Collection Paired samples were collected by the cities of Oceanside, Carlsbad, Encinitas, Solana Beach, Del Mar, and San Diego and the San Diego Unified Port District or their contractor during the 2004 – 2005 reporting period. Trained field personnel employing standard bacteriological sampling procedures collected the paired coastal samples at the specified frequency. A detailed description of the sampling protocol used by the CSDM program is included in Appendix C, “Standard Operating Procedures (SOP) For The Collection Of Bacteria Samples From Storm Drains And Receiving Waters (Creeks, Lagoons, Bays, And Ocean)”. Upon collection, samples were placed in a cooler with blue ice for transport to the laboratory for analysis. A six-hour holding time as recommended by ASTM and USEPA methods was strictly observed for all samples. 2.4 Laboratory Analysis Paired samples were analyzed for total and fecal coliform, and Enterococcus indicators. The Copermittees used laboratories certified by the Environmental Laboratory Accreditation Program (ELAP) Division of the California Department of Health Services. Only methods approved by the ELAP Division were used to analyze the samples. Common methods for analysis included multi-tube fermentation, membrane filtration and IDEXX (for Enterococcus analyses only). IDEXX methodology that enumerates for E coli instead of fecal coliform is not currently permitted under the Municipal Storm Water Permit and was not used to enumerate bacterial concentrations. During the initial months of the program, the number of laboratory dilutions necessary to analyze the storm drain and surf zone samples had not been established. As the Copermittees began receiving data and it became apparent that a small number of the storm drain samples were being reported above the range of the highest laboratory dilution, the Monitoring Workgroup established program guidelines to ensure that the storm drain samples were enumerated from 20 – 1,600,000 MPN/100 mls. Section 2 - Methods 12 Attachment A Coastal Storm Drain and Lagoon Monitoring 2003-2004 Annual Report 2.5 Data Analysis Data from the coastal monitoring program was used to characterize the sites (at the time of sampling), identify receiving water exceedances, and determine source investigations. Data was compiled to provide an overall assessment of the receiving water and storm drain conditions (both in lagoons and oceans). The methodology for the various data analyses is discussed below. Seasonal variation in receiving water and storm drain conditions was also evaluated during this reporting period. 2.5.1 Lab Data Laboratory results were compared to the following standards. These standards are identified in the basin plan for REC-1 waters. The minimum protective bacteriological standards for waters adjacent to public beaches and public water- contact sports areas are listed in Title 17 of the California Code of Regulations, Section 7958. These single sample standards are: • 1,000 total coliform bacteria per 100 mls, if the ratio of fecal/total coliform bacteria exceeds 0.1; or • 10,000 total coliform bacteria per 100 mls; or • 400 fecal coliform bacteria per 100 mls; or • 104 Enterococcus bacteria per 100 mls. (for designated beaches and lagoons) • 276 Enterococcus bacteria per 100mls (moderately used lagoons) • 500 Enterococcus bacteria per 100mls (infrequently used lagoons) If there were exceedances to any of these criteria, investigations followed according to the Adaptive Plan protocol. This is further discussed in Section 2.6 of this report. 2.5.2 Visual Observations Copermittees recorded visual observations of the storm drains and beaches during each sampling effort regardless of whether samples were collected. These observations were designed to determine whether there may be outside sources causing or contributing to elevated bacteria levels. Field data sheets were developed to standardize the visual observations criteria to facilitate use, and provide consistency (i.e. similar data recording methods, common data entry, etc.) for statistical purposes (Appendix D). All copermittees were required to use these standardized field sheets. Section 2 - Methods 13 Attachment A Coastal Storm Drain and Lagoon Monitoring 2003-2004 Annual Report 2.5.3 Data Transfer Templates The CSDM Copermittees developed standardized data transfer templates during the reporting period in effort to improve consistency. These templates were designed using the SMC guidance. During this reporting period, all CSDM copermittees were required to submit data using these templates. Templates were designed for both visual and laboratory data. The final templates are included as Appendix E. 2.6 Follow-up Activities All investigations from exceedances are conducted according to the Adaptive Plan protocol. Coastal receiving water exceedances receive the highest priority. Contaminated storm drain discharges with sufficient flow to reach the receiving water were assigned the next highest priority for additional investigation and source elimination. Receiving water bacteriological results that identified an exceedance of any one of the three bacteria standards were immediately reported to the County DEH for coastal sites. This allowed the County to take appropriated public health protection measures (i.e. posting the beach). In some instances the County Department of Environmental Health would direct the Copermittee to resample the receiving water where bacterial standards were exceeded. Lagoon sites were not posted by DEH. DEH had elected, prior to the start of the Lagoon Monitoring (in 2002) not to review and/or post lagoons. Therefore, Copermittees resampled these locations based on the Adaptive Plan criteria. Storm drain outfall data that showed unusually high levels of bacteria on a repeated basis were reviewed by each Copermittee to determine the need for source identification by the city’s IC/ ID program or inclusion into the Dry Weather Monitoring Program. Section 2 - Methods 14 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report SECTION 3 - RESULTS 3.0 Results The following description of bacterial indicator analytical results is a summary of the data collected from November 1, 2004 through October 31, 2005 in accordance with Coastal Monitoring Program protocols. Paired samples were collected at all coastal and bay sites; and at all lagoon sites, where possible. At lagoon sites where paired sampling was not possible due to access limitations or sensitive habitat, efforts were made to collect an unpaired storm drain sample. While conducting sampling, field staff performed visual observations and noted flow conditions, including whether storm drain flow directly discharged to the receiving water. With the exception of this flow characteristic, all other qualitative data will not be discussed in this report. To streamline the data compilation and assessment process, a standardized data transfer template was developed and used by the Copermittees to produce a complete dataset. A copy of the data transfer template is included as Appendix D. The raw data is contained in Appendix F (coastal) and G (lagoon). Data includes both routine and follow-up samples (denoted in the appendices as R and F, respectively). In addition, the raw data was screened and standardized for assessment purposes. The protocol used to screen the data was agreed upon by participating Copermittees is included as Appendix H. The screened dataset was used for further analysis in this report. The data has been separated into a coastal section, which includes coastal storm drains (identified as CSDO) and associated receiving waters (CRW), and a lagoon section which includes storm drains discharging into lagoons (LSDO) and associated lagoon receiving waters (LRW). As such, the results of coastal and lagoon monitoring will be discussed independently in the following sections. Relevant information on exceedances will also be included in the appropriate sections below. 3.1 Coastal Storm Drains Discharging to Ocean or Bay The Copermittees monitored 59 storm drains discharging to coastal oceans or bays during the 2004-2005 Coastal Monitoring Program. 339 paired samples and 8 unpaired samples were collected for each analyte at 39 of the 59 coastal sites during the period. Of the total, 92 samples were collected during the wet season, and 247 samples were collected during the dry seasons. The greater number of dry season samples is a reflection of the higher sampling frequency during the dry season (once every two weeks versus once per month) and its longer duration (7 months versus 5 months). Most sites were sampled at less Section 3 – Results 15 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report than the maximum frequency due to an absence of storm drain flow. The intermittent flows at many of the coastal storm drains may have been caused by the generally ephemeral character of the region’s coastal storm drain discharges. Flow observations made by Copermittees while conducting sampling further support the notion that many coastal storm drains do not regularly have sufficient flow to discharge to the receiving water. Of the 39 sites sampled, only 16 locations had flow that regularly reached the receiving water, 13 sites had occasional flow, and ten sites had flow from the outfall that did not reach the receiving water. In addition to the paired samples, a total of eight unpaired samples were collected from the coastal storm drain outfalls during the reporting period. With the exception of Coast-9 (Oceanside), all of the unpaired samples were follow-up samples, taken in response to exceedances discovered during routine monitoring. Two of the unpaired samples were collected during the wet season and six were collected during the dry season. Table 3-1 summarizes the paired and unpaired samples collected at each site, beginning with samples collected by the City of Oceanside and moving south. Also included is a characterization of whether the storm drain flows to the receiving water at each site. Provided below is a more detailed description of the sampling results for each jurisdiction. Of the 20 coastal sites routinely monitored by Oceanside, only five sites were observed to have intermittent flow during the reporting period. Of these five sites, a total of 26 paired samples were collected, including five during the wet season and 21 during the dry season. Five unpaired samples were collected as part of follow-up investigations, including two during the wet season and three during the dry season. Four of the storm drains were observed to be flowing to the receiving water during sampling events, and the remaining storm drain was not observed flowing to the receiving water. Carlsbad conducts routine monitoring at six coastal sites, of which five were observed to be flowing on an intermittent basis during the reporting period. Between these five sites, a total of nine paired sample were collected, including three during the wet season and six during the dry season. No unpaired samples were collected. None of the storm drains monitored by Carlsbad were observed to be directly flowing to the receiving water. Section 3 – Results 16 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 3-1 2004-2005 Paired and Unpaired Samples. # Paired Samples Collected # Unpaired Samples Collected Station ID Wet Dry Total Wet Dry Total Storm Drain Flows to Receiving Water Oceanside Coast 8 5* 15 20 0 2 (SD) 2 Yes Coast 9 0 0 0 1 (SD) 0 1 Yes Coast 14 0 2 2 0 0 0 Yes Coast 18 0 2 2 1 (SD) 1 (SD) 2 Yes Coast 21 0 2 2 0 0 0 No Carlsbad EH-460 0 1 1 0 0 0 No EH-470 0 1 1 0 0 0 No EH-475 1 3 4 0 0 0 No EH-476 1 1 2 0 0 0 No EH-477 1 0 1 0 0 0 No Encinitas EH-403 5 9 14 0 0 0 Yes EH-405 1 3 4 0 0 0 Yes EH-410 5 7 12 0 0 0 Yes EH-420 12 25* 37 0 2 (RW) 2 Yes Solana Beach EH-390 5 13 18 0 0 0 Occasional1 Del Mar S-03 2 0 2 0 0 0 No S-04 2 6 8 0 1 (RW) 1 Occasional S-05 2 10 12 0 0 0 Yes S-06 2 10 12 0 0 0 Occasional S-07 0 9 9 0 0 0 Occasional S-10 2 0 2 0 0 0 Occasional S-12 0 10 10 0 0 0 Occasional San Diego EH-250 5 16 21 0 0 0 Occasional EH-255 5 16 21 0 0 0 Yes EH-280 5 16 21 0 0 0 Occasional EH-290 2 2 4 0 0 0 Yes EH-300 4 7 11 0 0 0 Yes EH-320 2 2 4 0 0 0 Yes EH-330 2 9 11 0 0 0 Occasional EH-340 4 15 19 0 0 0 Occasional FM-030 2 5 7 0 0 0 Occasional FM-050 4 1 5 0 0 0 Occasional FM-060 5 15 20 0 0 0 Yes FM-080 3 8 11 0 0 0 Yes Section 3 – Results 17 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report # Paired Samples Collected # Unpaired Samples Collected Station ID Wet Dry Total Wet Dry Total Storm Drain Flows to Receiving Water Port EH-070 1 0 1 0 0 0 No EH-120 1 1 2 0 0 0 Occasional EH-160 0 1 1 0 0 0 No EH-205 0 3 3 0 0 0 Yes EH-210 1 1 2 0 0 0 No TOTAL 92 247 339 2 6 8 * One of the pairs was a follow-up sample, taken in response to an exceedance during routine monitoring. 1. Occasional flow is based on an observed condition of “yes” during < 50% of sampling events. SD = Storm Drain RW = Receiving Water Samples were collected at all four of the coastal sites routinely monitored by Encinitas. A total of 67 paired samples were collected, of which 23 were collected during the wet season and 44 were collected during the dry season. Two unpaired follow-up samples were collected during the dry season as part of a follow-up investigation. All of the storm drains sampled by Encinitas were observed to be directly flowing to the receiving water. Solana Beach routinely monitors one coastal site, which had consistent flow during the reporting period. A total of 18 paired samples were collected at this site, including five collected during the wet season and 13 during the dry season. No unpaired or follow-up samples were collected. The flow from the storm drain only reached the receiving water on a single occasion. Flow was observed at all seven coastal locations routinely monitored by Del Mar during the reporting period. Between these seven sites, a total of 55 paired samples were collected, including ten during the wet season and 45 during the dry season. No unpaired samples were collected. Five of the storm drains monitored by Del Mar were observed to occasionally flow into the receiving water, one storm drain was observed to regularly flow into the receiving water, and the remaining flow was not observed flowing into the receiving water. Samples were collected at all 12 of the coastal sites routinely monitored by San Diego for a total of 155 paired samples. Of these, 43 samples were collected during the wet season and 112 were collected during the dry season. There were no unpaired or follow-up samples collected during the reporting period. Six sites had flow that occasionally reached the receiving water and six sites frequently flowed to the receiving water. Samples were collected at five of the six coastal sites routinely monitored by the Port. A total of nine paired samples were collected, of which three were collected during the wet season and six were collected during the dry season. There were Section 3 – Results 18 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report no follow-up samples or unpaired samples. One site had flow that occasionally reached the receiving water, one site frequently flowed to the receiving water, and three sites did not have flow that reached the receiving water. 3.1.1 Coastal Receiving Water Exceedances Results of coastal receiving water monitoring were evaluated to determine exceedances of AB411 standards for total coliform, fecal coliform, and Enterococcus. During the reporting period, receiving water samples were collected at a total of 39 sites. Of these, 31 sites (79%) never exceeded the water quality objectives for any indicators. Eight locations had bacteria concentrations in the receiving water exceeding the AB411 water quality objectives for at least one indicator during at least one sampling event. As shown in Table 3-2 below, there were a total of 28 single sample exceedances, including seven for total coliform, six for fecal coliform, and 15 for Enterococcus. With a total of 339 paired samples and 3 unpaired receiving water samples collected, bringing the total to 342, the exceedance rates for total coliform, fecal coliform, and Enterococcus in the coastal receiving water are 2.0%, 1.7%, and 4.4%, respectively. Finally, it should be noted that, as indicated in the tables below, the majority of the single sample exceedances were for Enterococcus. According to the Coastal Monitoring Program protocols, all results of paired sampling that exceed relevant water quality criteria (AB411 standards for receiving water and the 95% action levels for storm drains) require further source identification investigation. Of particular concern are sites with exceedances of a single indicator on multiple dates, and those with multiple indicator exceedances on the same date. All source investigations will be discussed in Section 4.6. Table 3-2 Coastal receiving water exceedances Site Total Number of Exceedances Total Coliform Fecal Coliform Enterococcus Oceanside Coast 8 5 4 5 Encinitas EH-420 0 0 1 Del Mar S-04 0 0 2 S-12 1 0 1 San Diego EH-255 1 2 3 EH-280 0 0 1 EH-320 0 0 1 FM-060 0 0 1 TOTAL 7 6 15 Section 3 – Results 19 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report There were a total of seven total coliform coastal receiving water exceedances. Two sites exceeded on single occasions, the highest of which was 240,000 MPN/100mL at S-12 on October 5, 2005. Coast 8 in Oceanside had five exceedances, the highest of which was 900,000 MPN/100mL on November 16, 2004. These results are provided in Table 3-3. Table 3-3 Total Coliform Receiving Water Exceedances Station ID Date Result Unit Oceanside Coast 8 11/16/04 900,000 MPN/100mL Coast 8 12/14/04 50,000 MPN/100mL Coast 8 02/10/05 80,000 MPN/100mL Coast 8 03/08/05 130,000 MPN/100mL Coast 8 07/05/05 30,000 MPN/100mL Del Mar S-12 10/05/05 240,000 MPN/100mL San Diego EH-255 08/22/05 16,000 CFU/100mL There were a total of six fecal coliform receiving water exceedances. Coast 8 had four exceedances of the single sample standard, with the highest result of 17,000 MPN/100mL on November 16, 2004. EH-255 had two fecal coliform exceedances, with the highest result of 12,000 CFU/100mL on August 22, 2005. These results are provided in Table 3-4. Table 3-4 Fecal Coliform Receiving Water Exceedances Station ID Date Result Unit Oceanside Coast 8 11/16/04 17,000 MPN/100mL Coast 8 12/14/04 3,000 MPN/100mL Coast 8 07/05/05 500 MPN/100mL Coast 8 08/02/05 500 MPN/100mL San Diego EH-255 06/13/05 440 CFU/100mL EH-255 08/22/05 12,000 CFU/100mL 15 coastal receiving water sites had exceedances of the Enterococcus water quality objective, with the maximum result of 5,600 CFU/100mL at EH-255 on August 22, 2005. It should be noted that EH-255 also had high total coliform and fecal coliform values on the same date. Three of the eight sites had Enterococcus exceedances on multiple dates, including Coast 8, EH-255, and S-04. These results are provided in Table 3-5. Section 3 – Results 20 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 3-5 Enterococcus receiving water exceedances Station ID Date Result Unit Oceanside Coast 8 11/16/04 1,000 MPN/100mL Coast 8 02/10/05 260 MPN/100mL Coast 8 03/08/05 602 MPN/100mL Coast 8 05/10/05 190 MPN/100mL Coast 8 07/05/05 120 MPN/100mL Encinitas EH-420 04/19/05 128 CFU/100mL Del Mar S-04 03/08/05 170 MPN/100mL S-04 10/05/05 110 MPN/100mL S-12 10/05/05 220 MPN/100mL San Diego EH-255 07/11/05 160 CFU/100mL EH-255 08/22/05 5,600 CFU/100mL EH-255 10/17/05 540 CFU/100mL EH-280 12/13/04 1,200 CFU/100mL EH-320 03/01/05 660 CFU/100mL FM-060 02/01/05 140 CFU/100mL There were only seven of the 342 coastal receiving water samples (or 2.0%) collected during the reporting period that had multiple indicator exceedances during a single sampling event. Furthermore, these multiple indicator exceedances only occurred at three of the 39 sites sampled. During each of these occurrences, Enterococcus was one of the indicators included. Table 3-6 indicates the sites and dates when exceedances of more than one indicator occurred. Table 3-6 Multiple indicator receiving water exceedances Site ID Date Total Coliform Fecal Coliform Enterococcus Unit Oceanside Coast 8 11/16/04 900,000 17,000 1,000 MPN/100mL Coast 8 12/14/04 50,000 3,000 NE MPN/100mL Coast 8 02/10/05 80,000 NE 260 MPN/100mL Coast 8 03/08/05 130,000 NE 602 MPN/100mL Coast 8 07/05/05 30,000 500 120 MPN/100mL Del Mar S-12 10/05/05 240,000 NE 220 MPN/100mL San Diego EH-255 08/22/05 16,000 12,000 5,600 CFU/100mL NE = No Exceedance of this indicator Section 3 – Results 21 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report 3.1.2 Coastal Storm Drain Exceedances Results of coastal storm drain monitoring were evaluated to determine exceedances of the 95% percentile action level criteria for total coliform, fecal coliform, and Enterococcus. The 95th-percentile action levels used to assess storm drain exceedances during this reporting period are identified in Table 3-7. Data from both coastal and lagoon stations were used for this assessment. Table 3-7 95th-percentile storm drain criteria for 2004-2005 Indicator 95th-Percentile Storm Drain Criteria Total Coliform 160,000 MPN/ 100mL Fecal Coliform 27,600 MPN/ 100mL Enterococcus 18,400 MPN/ 100mL During the reporting period, coastal storm drain samples were collected at a total of 39 sites. Of these locations, 15 sites (38%) never exceeded the 95% action levels. 24 locations had bacteria concentrations in the storm drain effluent exceeding the action levels for at least one indicator during at least one sampling event. As shown in Table 3-8 below, there were a total of 104 coastal storm drain exceedances, including 55 for total coliform, 23 for fecal coliform, and 26 for Enterococcus. With 339 paired samples and five unpaired storm drain samples collected for a total of 344 storm drain samples, the exceedance rates for total coliform, fecal coliform, and Enterococcus in the storm drain effluent are 16.0%, 6.7%, and 7.6%, respectively. Table 3-8 Coastal Exceedances of the 95% Storm Drain Action Levels. Site Number of Exceedances Total Coliform Fecal Coliform Enterococcus Oceanside Coast 8 10 6 0 Coast 14 1 0 0 Coast 18 2 0 2 Carlsbad EH-475 0 0 1 EH-476 0 1 0 EH-477 0 0 1 Solana Beach EH-390 14 5 2 Del Mar S-03 1 0 0 S-05 1 0 0 S-06 3 0 0 Section 3 – Results 22 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Del Mar (con’t) S-07 4 0 1 S-12 3 0 2 San Diego EH-250 1 0 1 EH-255 3 1 2 EH-280 0 0 1 EH-290 1 1 2 EH-300 0 1 1 EH-330 2 1 1 EH-340 5 2 5 FM-030 1 1 1 FM-060 1 1 0 FM-080 0 1 0 Port EH-070 0 0 1 EH-205 2 2 2 TOTAL 55 23 26 There were a total of 55 exceedances of the total coliform storm drain action level. 17 sites had at least one exceedance for total coliform, of which ten had a total coliform exceedance on more than one date. The highest result of 16,000,000 MPN/100mL was reported from EH-390 on July 28, 2005 in Solana Beach. However, several locations had results equal to or greater than 1,600,000 MPN/100mL, including Coast 8, S-07 and EH-340. These results are provided in Table 3-9. Table 3-9 Total Coliform coastal storm drain exceedances Prefix Station ID Date Result Unit SD REACH RW Oceanside R Coast 8 11/16/04 >1,600,000 MPN/100mL Yes F Coast 8 02/10/05 900,000 MPN/100mL Yes R Coast 8 03/08/05 >1,600,000 MPN/100mL Yes F Coast 8 04/19/05 300,000 MPN/100mL Yes R Coast 8 04/26/05 900,000 MPN/100mL Yes R Coast 8 06/21/05 300,000 MPN/100mL Yes R Coast 8 07/05/05 >1,600,000 MPN/100mL Yes R Coast 8 07/19/05 500,000 MPN/100mL Yes R Coast 8 08/02/05 220,000 MPN/100mL Yes R Coast 8 10/25/05 170,000 MPN/100mL Yes R Coast 14 10/11/05 500,000 MPN/100mL Yes R Coast 18 04/12/05 500,000 MPN/100mL No R Coast 18 04/26/05 240,000 MPN/100mL No Section 3 – Results 23 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Prefix Station ID Date Result Unit SD REACH RW Solana Beach R EH-390 12/16/04 2,400,000 MPN/100mL No R EH-390 02/28/05 230,000 MPN/100mL No R EH-390 03/31/05 220,000 MPN/100mL No R EH-390 04/15/05 800,000 MPN/100mL No R EH-390 05/18/05 700,000 MPN/100mL No R EH-390 06/16/05 1,100,000 MPN/100mL No R EH-390 06/30/05 5,000,000 MPN/100mL No R EH-390 07/14/05 800,000 MPN/100mL No R EH-390 07/28/05 16,000,000 MPN/100mL No R EH-390 08/18/05 500,000 MPN/100mL No R EH-390 08/31/05 2,400,000 MPN/100mL No R EH-390 09/16/05 500,000 MPN/100mL No R EH-390 09/27/05 2,200,000 MPN/100mL No R EH-390 10/28/05 3,000,000 MPN/100mL No Del Mar R S-03 11/23/03 240,000 MPN/100mL No R S-05 07/26/05 160,000 MPN/100mL Yes R S-06 07/26/05 160,000 MPN/100mL No R S-06 07/27/05 900,000 MPN/100mL Yes R S-06 10/05/05 160,000 MPN/100mL Yes R S-07 06/16/05 240,000 MPN/100mL No R S-07 07/26/05 160,000 MPN/100mL No R S-07 07/27/05 900,000 MPN/100mL No R S-07 09/21/05 1,600,000 MPN/100mL No R S-12 07/26/05 500,000 MPN/100mL No R S-12 08/16/05 220,000 MPN/100mL Unknown R S-12 09/21/05 240,000 MPN/100mL No San Diego R EH-250 05/17/05 170,000 MPN/100mL No R EH-255 05/31/05 900,000 MPN/100mL No R EH-255 06/13/05 240,000 MPN/100mL No R EH-255 07/25/05 220,000 MPN/100mL No R EH-290 03/01/05 240,000 MPN/100mL No R EH-330 05/31/05 220,000 MPN/100mL No R EH-330 08/09/05 500,000 MPN/100mL No R EH-340 05/17/05 300,000 MPN/100mL No R EH-340 08/22/05 170,000 MPN/100mL No R EH-340 09/06/05 1,600,000 MPN/100mL No R EH-340 10/17/05 170,000 MPN/100mL Yes R EH-340 10/31/05 170,000 MPN/100mL No R FM-030 10/17/05 240,000 CFU/100mL No Section 3 – Results 24 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Prefix Station ID Date Result Unit SD REACH RW San Diego (con’t) R FM-060 07/11/05 500,000 CFU/100mL No Port R EH-205 08/09/05 900,000 MPN/100mL Yes R EH-205 09/06/05 500,000 MPN/100mL Yes There were a total of 23 exceedances of the fecal coliform storm drain action level. 12 sites had at least one exceedance on at least one date, with four of these locations having exceedances on more than one date. The highest value of 2,200,000 MPN/100mL was reported from EH-390 on July 28, 2005. Table 3- 10 presents this data. Table 3-10 Fecal Coliform coastal storm drain exceedances Prefix Station ID Date Result Unit SD REACH RW Oceanside R Coast 8 11/16/04 1,600,000 MPN/100mL Yes R Coast 8 05/24/05 30,000 MPN/100mL No R Coast 8 06/07/05 50,000 MPN/100mL No R Coast 8 07/05/05 50,000 MPN/100mL No R Coast 8 08/02/05 130,000 MPN/100mL No R Coast 8 09/27/05 80,000 MPN/100mL No Carlsbad R EH-476 4/18/05 35,050 CFU/100mL No Solana Beach R EH-390 06/30/05 500,000 MPN/100mL No R EH-390 07/28/05 2,200,000 MPN/100mL No R EH-390 08/31/05 50,000 MPN/100mL No R EH-390 09/27/05 230,000 MPN/100mL No R EH-390 10/28/05 700,000 MPN/100mL No San Diego R EH-255 05/31/05 900,000 MPN/100mL Yes R EH-290 03/01/05 80,000 MPN/100mL No R EH-300 06/13/05 50,000 MPN/100mL No R EH-330 05/31/05 220,000 MPN/100mL No R EH-340 09/06/05 >1,600,000 MPN/100mL No R EH-340 10/31/05 80,000 MPN/100mL No R FM-030 06/13/05 80,000 MPN/100mL No R FM-060 12/13/04 110,000 MPN/100mL Yes R FM-080 10/17/05 50,000 MPN/100mL Unknown Section 3 – Results 25 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Prefix Station ID Date Result Unit SD REACH RW Port R EH-205 08/09/05 80,000 MPN/100mL No R EH-205 09/06/05 30,000 MPN/100mL Yes There were a total of 26 exceedances of the Enterococcus storm drain action level. There were 16 sites with exceedances of Enterococcus, seven of which had exceedances on multiple dates. The highest value of 170,000 CFU/100mL was reported at S-12 on May 19, 2005. This data is presented in Table 3-11. Table 3-11 Enterococcus coastal storm drain exceedances Prefix Station ID Date Result Unit SD REACH RW Oceanside R Coast 18 04/12/05 155,000 MPN/100mL Yes R Coast 18 04/26/05 21,800 MPN/100mL Yes Carlsbad R EH-477 03/17/05 23,800 CFU/100mL No R EH-475 06/13/05 24,700 CFU/100mL No Solana Beach R EH-390 09/27/05 27,551 MPN/100mL No R EH-390 10/28/05 111,987 MPN/100mL No Del Mar R S-07 04/13/05 30,000 MPN/100mL No R S-12 05/19/05 170,000 MPN/100mL No R S-12 05/27/05 160,000 MPN/100mL No San Diego R EH-250 10/31/05 44,000 CFU/100mL No R EH-255 05/31/05 20,000 CFU/100mL Yes R EH-255 06/13/05 32,000 CFU/100mL No R EH-280 10/03/05 50,000 CFU/100mL No R EH-290 03/01/05 30,000 CFU/100mL No R EH-290 07/11/05 36,000 CFU/100mL Yes R EH-300 06/13/05 38,000 CFU/100mL Unknown R EH-330 08/09/05 46,000 CFU/100mL No R EH-340 05/17/05 32,000 CFU/100mL No R EH-340 07/11/05 32,000 CFU/100mL No R EH-340 08/09/05 28,000 CFU/100mL No R EH-340 08/22/05 38,000 CFU/100mL No R EH-340 09/06/05 120,000 CFU/100mL No R FM-030 04/04/05 20,000 CFU/100mL No Section 3 – Results 26 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Prefix Station ID Date Result Unit SD REACH RW Port R EH-070 03/08/05 24,196 MPN/100mL No R EH-205 08/09/05 98,039 MPN/100mL No R EH-205 09/06/05 120,333 MPN/100mL Yes As indicated in Tables 3-9 through 3-11, the majority of the single sample exceedances in storm drain effluent were for total coliform. Of the 55 samples that had a total coliform exceedance, 21 samples (38%) also exceeded for fecal coliform or Enterococcus. However, only 6.1% of the 344 total storm drain samples collected during the reporting period had multiple indicator exceedances. Table 3-12 indicates the sites and dates of multiple indicator exceedances in the storm drain effluent. Table 3-12 Multiple indicator exceedances in storm drains Site ID Date Total Coliform Fecal Coliform Enterococcus Unit Oceanside Coast 8 11/16/04 >1,600,000 1,600,000 NE MPN/100mL Coast 8 07/05/05 >1,600,000 50,000 NE MPN/100mL Coast 8 08/02/05 220,000 130,000 NE MPN/100mL Coast 18 04/12/05 500,000 NE 155,000 MPN/100mL Coast 18 04/26/05 240,000 NE 21,800 MPN/100mL Solana Beach EH-390 06/30/05 5,000,000 500,000 NE MPN/100mL EH-390 07/28/05 16,000,000 2,200,000 NE MPN/100mL EH-390 09/27/05 2,200,000 230,000 NE MPN/100mL EH-390 10/28/05 3,000,000 700,000 NE MPN/100mL San Diego EH-255 05/31/05 900,000 900,000 20,000 MPN/100mL EH-255 06/13/05 240,000 NE 32,000 MPN/100mL EH-290 03/01/05 240,000 80,000 30,000 MPN/100mL EH-300 06/13/05 NE 50,000 38,000 MPN/100mL EH-330 05/31/05 220,000 220,000 NE MPN/100mL EH-330 08/09/05 500,000 NE 46,000 MPN/100mL EH-340 05/17/05 300,000 NE 32,000 MPN/100mL EH-340 08/22/05 170,000 NE 28,000 MPN/100mL EH-340 09/06/05 1,600,000 >1,600,000 120,000 CFU/100mL EH-340 10/31/05 170,000 80,000 NE CFU/100mL Port EH-205 08/09/05 900,000 80,000 98,039 MPN/100mL EH-205 09/06/05 500,000 30,000 120,333 MPN/100mL NE = No Exceedance of this indicator Section 3 – Results 27 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report As stated above, this section identified all sites having a storm drain action level exceedance during the reporting period. According to the Coastal Monitoring Program protocols, all results of paired sampling that exceed relevant water quality criteria (AB411 standards for receiving water and the 95% action levels for storm drains) require further source identification investigation. Of particular concern are sites with exceedances of a single indicator on multiple dates, and those with multiple indicator exceedances on the same date. All source investigations are discussed in Section 4.6. 3.2 Storm Drains Discharging to Lagoons The Copermittees monitored 28 storm drains discharging to lagoons during the 2004-2005 Coastal Monitoring Program. The five lagoons monitored include Los Penasquitos, San Elijo, Batiquitos, Agua Hedionda, and Buena Vista. A total of 128 paired samples were collected at 11 of the 28 lagoon monitoring sites during the period. Of the 11 sites where paired samples were collected, nine had flows reaching receiving waters. Of the total, 33 and 95 paired samples were collected during the wet and dry seasons, respectively. In addition to the paired samples collected, the design of the lagoon program specified that samples are to be collected at flowing storm drains. In some cases Copermittees used their best professional judgment to determine when to sample ponded water. Some Copermittees elected to act conservatively rather than dismiss the possibility that elevated bacteria levels in the ponded water could potentially affect receiving water. In many instances where the storm drains were sampled, the receiving water sample was unable to be collected due to inaccessibility and/or safety issues. This resulted in the collection of 170 storm drain samples without a receiving water sample. Of the single samples collected, 46 were collected during the wet season and 124 were collected during the dry season. The greater number of dry season samples is a reflection of the higher sampling frequency during the dry season (once every two weeks versus once per month) and its longer duration (7 months versus 5 months). Table 3-13 summarizes the paired and unpaired samples on a site-by-site basis, beginning with samples collected by the City of Oceanside and moving south. Also included is a characterization of whether the storm drain flows reach the receiving water at each site. Provided below is a more detailed description of the sampling results for each jurisdiction. Section 3 – Results 28 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 3-13 Summary of Lagoon Samples, November 2004-October 2005 Station ID # Paired Samples Collected # Unpaired Samples Collected Storm Drain Flows to Receiving Water Wet Dry Total Wet Dry Total Oceanside Coast 20-1 5 15 20 0 0 0 Yes Coast 20-2 0 0 0 5 13 18 Yes Carlsbad AH-006 5 14 19 0 0 0 Yes AH-011 2 0 2 0 0 0 Yes AH-025 4 14 18 0 0 0 Yes AH-19A 4 14 18 0 0 0 Yes AH-017 0 0 0 0 2 2 No AH-020 0 0 0 0 1 1 No AH-022 0 0 0 2 1 3 No AH-023 0 0 0 5 0 5 No AH-025 0 0 0 1 0 1 Yes BA-001 0 0 0 1 14 15 Occasional* BA-014 0 0 0 1 2 3 No BA-017 0 0 0 5 15 20 No BA-018 0 0 0 2 0 2 No BA-021 1 0 1 4 15 19 Occasional BA-022 0 0 0 5 0 5 No BV-002 0 0 0 0 11 11 No Encinitas CBS-1 5 15 20 0 0 0 No CBS-2 6 16 22 0 0 0 Yes CBS-5 0 1 1 0 0 0 Yes SEL-1 1 5 6 0 0 0 Yes SEL-2 0 0 0 5 15 20 No SEL-3 0 0 0 5 15 20 No San Diego PENA08 0 1 1 0 0 0 No PENA03 0 0 0 5 14 19 No PENA10 0 0 0 0 1 1 Yes PENA11 0 0 0 0 5 5 Occasional PENA06 0 0 0 0 0 0 N/A TOTAL 33 95 128 46 124 170 * Occasional flow is based on the observed condition of “yes” during ≤50% of the sampling events. Section 3 – Results 29 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report 3.2.1 Lagoon Receiving Water Exceedances Results of lagoon receiving water monitoring were evaluated to determine exceedances of AB411 standards for total coliform and fecal coliform. Enterococcus standards are based on criteria established in the San Diego Basin Plan for REC-1 waters and account for frequencies of use at lagoon sites. A detailed discussion of the Frequency of Use follows in Section 4. During the reporting period, receiving water samples were collected at 11 sites. Of these locations, 7 sites (64%) had bacteria concentrations in the receiving water exceeding the single sample standards for at least one indicator during at least one sampling event. As shown in Table 3-14 below, there were a total of 65 single sample indicator exceedances, including 16 for total coliform, 31 for fecal coliform, and 18 for Enterococcus. With a total of 128 paired samples collected, the exceedance rates for total coliform, fecal coliform, and Enterococcus in the receiving water are 13%, 24%, and 14%, respectively. However, Coast 20 represented the majority of these exceedances, significantly influencing the calculation of the exceedance rates for the other lagoons. And, it should be noted that receiving water samples at Coast 20 are collected in a freshwater lagoon that is not open to tidal flushing. Coast 20 had 20 paired samples collected, leaving 108 collected in other lagoons. Without Coast 20 exceedances in the rate calculation, the exceedance rates were only 0% for total coliform, 14% for fecal coliform, and 4.6% for Enterococcus. Table 3-14 Single Sample Lagoon Receiving Water Exceedances Site Total Coliform Fecal Coliform Enterococcus Oceanside Coast 20-1 16 16 13 Carlsbad AH-006 0 2 2 AH-19A 0 3 0 Encinitas CBS-1 0 1 1 CBS-2 0 7 1 SEL-1 0 1 0 San Diego PENA08 0 1 1 TOTAL 16 31 18 Section 3 – Results 30 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Only a single site had receiving water exceedances for total coliform, Coast 20. The highest total coliform result was 920,000 MPN/100mL. These results are provided in Table 3-15. Table 3-15 Total Coliform Lagoon Receiving Water Exceedances Station ID Date Result Unit Oceanside COAST 20-1 12/14/04 30,000 MPN/100 ml COAST 20-1 1/18/05 50,000 MPN/100 ml COAST 20-1 2/8/05 17,000 MPN/100 ml COAST 20-1 4/12/05 13,000 MPN/100 ml COAST 20-1 4/26/05 30,000 MPN/100 ml COAST 20-1 5/10/05 29,000 MPN/100 ml COAST 20-1 5/24/05 12,000 MPN/100 ml COAST 20-1 6/7/05 65,000 MPN/100 ml COAST 20-1 6/21/05 90,000 MPN/100 ml COAST 20-1 7/5/05 15,000 MPN/100 ml COAST 20-1 7/19/05 13,000 MPN/100 ml COAST 20-1 8/2/05 13,000 MPN/100 ml COAST 20-1 8/16/05 13,000 MPN/100 ml COAST 20-1 9/27/05 22,000 MPN/100 ml COAST 20-1 10/11/05 50,000 MPN/100 ml COAST 20-1 10/25/05 920,000 MPN/100 ml COAST 20-1 12/14/04 30,000 MPN/100 ml Seven sites had exceedances of the single sample standard for fecal coliform, with the highest result of 23,000 MPN/100mL at Coast 20. Four of the seven sites exceeded standards on more than one sampling event. These results are provided in Table 3-16. Table 3-16 Fecal Coliform Lagoon Receiving Water Exceedances Station ID Date Result Unit Oceanside COAST 20-1 11/16/04 500 MPN/100 ml COAST 20-1 1/18/05 800 MPN/100 ml COAST 20-1 2/8/05 500 MPN/100 ml COAST 20-1 3/8/05 2,300 MPN/100 ml COAST 20-1 4/12/05 500 MPN/100 ml COAST 20-1 4/26/05 1,700 MPN/100 ml COAST 20-1 5/24/05 2,000 MPN/100 ml COAST 20-1 6/7/05 6,500 MPN/100 ml COAST 20-1 6/21/05 4,000 MPN/100 ml COAST 20-1 7/5/05 1,100 MPN/100 ml Section 3 – Results 31 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Station ID Date Result Unit Oceanside (con’t) COAST 20-1 7/19/05 3,000 MPN/100 ml COAST 20-1 8/2/05 3,000 MPN/100 ml COAST 20-1 8/16/05 1,300 MPN/100 ml COAST 20-1 9/27/05 8,000 MPN/100 ml COAST 20-1 10/11/05 17,000 MPN/100 ml COAST 20-1 10/25/05 23,000 MPN/100 ml Carlsbad AH-006 6/27/05 4,550 CFU/100 ml AH-006 10/5/05 960 CFU/100 ml AH-19A 5/31/05 508 CFU/100 ml AH-19A 7/26/05 440 CFU/100 ml AH-19A 8/23/05 1,880 CFU/100 ml Encinitas CBS-1 3/9/05 530 CFU/100 ml CBS-2 1/19/05 690 CFU/100 ml CBS-2 2/2/05 660 CFU/100 ml CBS-2 5/3/05 490 CFU/100 ml CBS-2 6/2/05 420 CFU/100 ml CBS-2 6/16/05 660 CFU/100 ml CBS-2 8/29/05 3,300 CFU/100 ml CBS-2 9/28/05 520 CFU/100 ml SEL-1 5/3/05 920 CFU/100 ml San Diego PENA08 7/11/05 500 MPN/100 ml For Enterococcus, five sites had exceedances, with the maximum result of 5,200 MPN/100mL at Coast 20. Two of the five had exceedances on more than one sampling event. These results are provided in Table 3-17. Table 3-17. Enterococcus Lagoon Receiving Water Exceedances Station ID Date Result Unit Oceanside COAST 20-1 11/16/04 800 MPN/100 ml COAST 20-1 12/14/04 640 MPN/100 ml COAST 20-1 3/8/05 2,100 MPN/100 ml COAST 20-1 4/26/05 550 MPN/100 ml COAST 20-1 6/7/05 1,000 MPN/100 ml COAST 20-1 6/21/05 5,200 MPN/100 ml COAST 20-1 7/5/05 1,800 MPN/100 ml COAST 20-1 7/19/05 860 MPN/100 ml Section 3 – Results 32 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Station ID Date Result Unit Oceanside (con’t) COAST 20-1 8/2/05 1,270 MPN/100 ml COAST 20-1 8/16/05 500 MPN/100 ml COAST 20-1 9/27/05 500 MPN/100 ml COAST 20-1 10/11/05 740 MPN/100 ml COAST 20-1 10/25/05 2,700 MPN/100 ml Carlsbad AH-006 6/27/05 1,300 CFU/100 ml AH-006 10/5/05 430 CFU/100 ml Encinitas CBS-1 3/9/05 590 CFU/100 ml CBS-2 1/19/05 520 CFU/100 ml San Diego PENA08 7/11/05 3,800 MPN/100 ml As indicated in Tables 3-14 through 3-17, the majority of the single sample exceedances were for fecal coliform. Of the 31 samples that had fecal coliform exceedances, 21 samples (68%) also exceeded for total coliform or Enterococcus. However, of the 16 samples with total coliform exceedances, 15 samples (94%) also exceeded for fecal coliform or Enterococcus bacteria. Of the 33 samples with exceedances, 22 samples (67%) had exceedances for multiple indicators. A total of 17% of the 128 total paired samples collected during the reporting period had multiple indicator exceedances in the lagoon receiving water. Excluding Coast 20, the multiple indicator exceedance rate drops to 4.6%. Table 3-18 indicates the sites and dates of multiple indicator exceedances. Table 3-18 Lagoon Receiving Waters with Multiple Indicator Exceedances Site ID Date Total Coliform Fecal Coliform Enterococcus Unit Oceanside COAST 20-1 11/16/04 NE 500 800 MPN/100 ml COAST 20-1 12/14/04 30000 230 640 MPN/100 ml COAST 20-1 1/18/05 50000 800 170 MPN/100 ml COAST 20-1 2/8/05 17000 500 183 MPN/100 ml COAST 20-1 3/8/05 NE 2300 2100 MPN/100 ml COAST 20-1 4/12/05 13000 500 170 MPN/100 ml COAST 20-1 4/26/05 30000 1700 550 MPN/100 ml COAST 20-1 5/24/05 12000 2000 340 MPN/100 ml COAST 20-1 6/7/05 65000 6500 1000 MPN/100 ml COAST 20-1 6/21/05 90000 4000 5200 MPN/100 ml Section 3 – Results 33 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Site ID Date Total Coliform Fecal Coliform Enterococcus Unit Oceanside COAST 20-1 7/5/05 15000 1100 1800 MPN/100 ml COAST 20-1 7/19/05 13000 3000 860 MPN/100 ml COAST 20-1 8/2/05 13000 3000 1270 MPN/100 ml COAST 20-1 8/16/05 13000 1300 500 MPN/100 ml COAST 20-1 9/27/05 22000 8000 500 MPN/100 ml COAST 20-1 10/11/05 50000 17000 740 MPN/100 ml COAST 20-1 10/25/05 920000 23000 2700 MPN/100 ml Carlsbad AH-006 6/27/05 NE 4,550 1300 CFU/100 ml AH-006 10/5/05 NE 960 430 CFU/100 ml Encinitas CBS-1 3/9/05 NE 530 590 CFU/100 ml CBS-2 1/19/05 NE 660 520 CFU/100 ml San Diego PENA08 7/11/05 NE 500 3800 MPN/100 ml NE – No exceedance of this indicator. Presented in this section were all sites with a lagoon receiving water exceedance during the reporting period. According to the Coastal and Lagoon Monitoring Program protocols, all results of paired sampling that exceed relevant water quality criteria (AB411 standards for receiving water and the 95% action levels for storm drains) require further source identification investigation. Of particular concern are sites with exceedances of a single indicator on multiple dates, and those with multiple indicator exceedances on the same date. All source investigations are discussed in Section 4.6 3.2.2 Lagoon Storm Drain Exceedances Results of coastal and lagoon storm drain monitoring were evaluated to determine exceedances of the 95% action levels for total coliform, fecal coliform, and Enterococcus. During the reporting period, paired lagoon storm drain samples were collected at a total of 11 sites, of which the flow reached the receiving water at nine. Of these 11 locations, nine sites (82%) never exceeded the 95% action levels. In addition to the paired samples, there were 17 sites where only storm drain samples (unpaired) were collected (i.e. no receiving water sample. Of these unpaired sites, three had bacteria concentrations in the storm drain effluent exceeding the action levels for at least one indicator during at least one sampling event. Two of the unpaired sites had exceedances during multiple sampling events, totaling five storm drain samples having action level exceedances. As shown in Table 3-19 below, there were a total of 14 single sample exceedances in storm drains, including four for total coliform, five for Section 3 – Results 34 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report fecal coliform, and five for Enterococcus. With 298 total storm drain samples collected (paired & unpaired), the exceedance rates for total coliform, fecal coliform, and Enterococcus in the storm drain effluent are 1.3%, 1.7%, and 1.7%, respectively. Table 3-19 Lagoon Exceedances of the 95% Storm Drain Action Levels Site Number of Exceedances Total Coliform Fecal Coliform Enterococcus Oceanside Coast 20-1 2 0 0 Carlsbad AH-017 0 1 1 BV-002 1 3 2 Encinitas CBS-5 0 0 1 San Diego PENA10 1 1 1 TOTAL 4 5 5 Three sites had at least one exceedance for total coliform, of which only Coast 20 had an exceedance of total coliform on more than one date. The highest result of 500,000 MPN/100mL was reported at PENA10 on July 25, 2005. Only a single sample was collected at this location (no receiving water sample). Of the paired samples collected where the storm drain reached the receiving water, Coast 20 had the highest total coliform concentration at 180,000 MPN/100 ml. The total coliform exceedance results are provided in Table 3-20. Table 3-20 Total Coliform Lagoon Storm Drain Exceedances Station ID Date Result Unit SD REACH RW Oceanside COAST 20-1 8/2/05 180,000 MPN/100 ml Yes COAST 20-1 9/13/05 180,000 MPN/100 ml Yes Carlsbad BV-002 05/02/05 269,000 CFU/100 ml No San Diego PENA10 07/25/05 500,000 MPN/100 ml Yes Section 3 – Results 35 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report For fecal coliform, three sites had exceedances. The highest value of 130,000 MPN/100mL was reported from PENA10 on July 25, 2005 respectively. Table 3-21 presents this data. Table 3-21 Fecal Coliform Lagoon Storm Drain Exceedances Station ID Date Result Unit SD REACH RW Carlsbad AH-017 06/29/05 34,150 CFU/100 ml No BV-002 05/02/05 39,000 CFU/100 ml no BV-002 07/26/05 33,800 CFU/100 ml No BV-002 10/03/05 44,000 CFU/100 ml No San Diego PENA10 07/25/05 130,000 MPN/100 ml Yes There were four sites with exceedances of Enterococcus. The highest value of 74,000 MPN/100mL was reported at PENA10 on July 25, 2005. This data is presented in Table 3-22. Table 3-22 Enterococcus Lagoon Storm Drain Exceedances Station ID Date Result Unit SD REACH RW Carlsbad AH-017 06/29/05 22,050 CFU/100 ml No BV-002 07/26/05 32,600 CFU/100 ml No BV-002 08/22/05 21,600 CFU/100 ml No Encinitas CBS-5 06/07/05 30,450 CFU/100 ml Yes San Diego PENA10 07/25/05 74,000 MPN/100 ml Yes Only four of the 18 sampling events with storm drain exceedances had exceedances for multiple indicators (22%). Table 3-23 indicates the sites and dates of multiple indicator exceedances in the storm drain effluent. Table 3-23 Lagoon Storm Drains with Multiple Indicator Exceedances Site ID Date Total Coliform Fecal Coliform Enterococcus Unit Carlsbad AH-017 06/29/05 AE 34,150 22,050CFU/100 ml BV-002 05/02/05 269,000 39,000 NECFU/100 ml BV-002 07/26/05 NE 33,800 32,600CFU/100 ml San Diego PENA10 07/25/05 500,000 130,000 74,000MPN/100 ml AE – Analyst Error NE – No exceedances of this indicator. Section 3 – Results 36 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Presented in this section were all sites with a storm drain exceedance during the reporting period. According to the Coastal Monitoring Program protocols, all results of paired sampling that exceed relevant water quality criteria (AB411 standards for receiving water and the 95% confidence interval values for storm drains) require further source identification investigation. Of particular concern are sites with exceedances of a single indicator on multiple dates, and those with multiple indicator exceedances on the same date. Additionally, sampling events in which storm drain samples and receiving water samples exceed standards are significant and must be further assessed. This assessment is presented in Section 4. All source investigations will be discussed in Section 4.6 3.3 Calculation of 95th Percentile Storm Drain Action Levels The 95th percentile storm drain action levels, from which to initiate investigations, are revised each year to reflect current storm drain conditions (Adaptive Sampling Program, 2003). Storm drain data from both coastal and lagoon stations are used to set the action levels. New 95th-percentiles were calculated with the data collected during the 2004-2005 sampling season (Table 3-24). Data was carefully reviewed and screened prior to calculating the 95th percentile criteria. The screening was used to remove outliers and/or blank data fields and provide a consistent data set from which to perform statistical analyses. The screening process and data used to calculate the 2006 95th percentile storm drain action levels are included in Appendix H. Table 3-24 95th-Percentile Storm Drain Action Levels for 2006 Indicator 95th-Percentile Storm Drain Action Levels Total Coliform 160,000 MPN/ 100 mls* Fecal Coliform 18,755 MPN/ 100 mls Enterococcus 17,820 MPN/ 100 mls *Actual 95th percentile is 289,150 MPN/100 mls. Copermittees will continue to use 160,000 MPN/100 mls to initiate resampling and investigations. It should be noted that the 95th percentile storm drain action levels for all indicators decreased from the previous reporting period. 3.4 2004-2005 Sampling Frequency Reduction Calculation The initial sampling reduction frequency criteria were established during the first year of the adaptive program in April of 2003 (using the 2001-2002 data set). Refinements to the methodology were made during 2003 because, 1) stormdrain results for total coliform were set too low (TC results greater than 160,000MPN/100mL were estimated), and 2) it was unknown if storm drain flow reached the receiving waters (at several monitoring locations). These pieces of Section 3 – Results 37 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report information are necessary if a relationship between the storm drains and receiving waters is to be understood. Currently, the methodology used to determine the Sampling Frequency Reduction Criteria involves calculating the storm drain-to-receiving water dilution factor using the slope of the regression line for each indicator’s annual data set. The slope of the paired sampling data regression line is an approximation of the dilution that occurs on a regional basis. A safety factor of 10:1 was applied to the calculated dilution factors to account for the possibility of lesser dilution rates between the storm drain and receiving water sampling points than is indicated by the slope of the regression line. Additionally, rules for data processing were established to ensure consistency in reporting and are as follows: 1. Data was screened prior to performing analysis. 2. The regression line was forced to have a zero intercept. 3. The resulting slope (in log10) was back transformed and is identified as the slope of regression line. 4. The new slope is then multiplied by the indicator’s receiving water action level. The data screening process is included in Appendix H. The rules and refinements stated above will improve reporting consistency and ensure that results can be reproduced in the future. Table 3-25 presents the numeric criteria from which to determine eligibility for sample reduction beginning in 2006. Table 3-25 Revised Sampling Reduction Frequency Criteria for 2006 Indicator Receiving Water Standard (MPN/100mL) Slope of Regression Line Reduction Standard without Safety Factor (MPN/100mL) Slope/Safety Factor Sampling Frequency Reduction Criteria (MPN/100mL) Total Coliform 10,000 44 441,774 10:1 44,177 Fecal Coliform 400 31 12,510 10:1 1,251 Enterococcus 104 42 4,377 10:1 437 Program modifications were made (beginning April 2004) to increase the total coliform lab analysis limits in stormdrains to 1,600,000 MPN/100 mls, and to ensure that all Copermittees identify whether stormdrain flows are reaching the receiving water. These criteria will be used to identify sites that are eligible for reduced sampling in the 2006 season. Future assessments will follow the refined methodology and will utilize the most recent year’s data set. Section 3 – Results 38 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report SECTION 4 - DISCUSSION 4.0 Discussion The following discussion of the CSDM Program is an evaluation of the data collected from November 1, 2004 through October 31, 2005. The results of the CSDM Program were assessed to determine the impacts that storm drains have on the receiving waters at coastal beaches and lagoons. The assessment was achieved by evaluating 2004-2005 results against the AB411 standards for receiving waters, and the ninety-five percent action levels for storm drains. An exceedance of either limit warranted further source identification investigation, however, specific attention was given to paired samples with an exceedance of both storm drain and receiving water standards during the same sampling event. These paired exceedances were considered indicative of a correlation between storm drain and receiving water quality, and are further discussed under Section 4.3, Adaptive Sampling Diagrams. Where analytical results exceeded action levels in either the storm drain or receiving water, investigative efforts and follow- up actions are described on a site-by-site basis under Section 4.6, Source Investigations. This discussion is divided into separate sub-sections for coastal (ocean and bay) beach receiving waters and associated storm drain outfalls, and lagoon receiving waters and associated storm drain outfalls. 4.1 Coastal Storm Drains and Receiving Water A comparison of the 2004-2005 data with the results collected during the previous years (2003-2004 and 2002-2003) indicated that overall conditions at sites were similar. The majority of the paired samples were collected during the dry season, which is likely due to the longer sampling period and the increased sampling frequency. The ratio of wet to dry season samples from the each of the three reporting periods is nearly identical. During each of the three sampling years, the wet season samples comprised approximately 27% of the total paired samples collected, whereas dry season samples accounted for 73% of the total. Furthermore, the percentage of sites having zero exceedances in the receiving water increased slightly (79%), but remained comparable to 2002-2003 (72%) and 2003-2004) (73%). This indicates that nearly three quarters of the sites sampled by the copermittees have consistently low bacteria concentrations. Section 4 – Discussion 39 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Bacterial indicator exceedance rates in the coastal receiving water were comparable between the previous and current reporting periods (Table 4-1). Results suggest that elevated Enterococcus levels account for many of the reported receiving water exceedances, whereas the total coliform standard is rarely exceeded in the receiving water. Table 4-1 Coastal Receiving Water Exceedance Percentages Reporting Period Exceedance Percentages Total Coliform Fecal Coliform Enterococcus 2002-2003 0.0% 2.3% 3.6% 2003-2004 0.6% 1.8% 5.0% 2004-2005 2.0% 1.7% 4.4% Coastal storm drain results showed trends similar to the receiving water (Table 4-2). As identified, total coliform accounted for the majority of the storm drain action level exceedances. Table 4-2 Coastal Storm Drain Exceedance Percentages Reporting Period Exceedance Percentages Total Coliform Fecal Coliform Enterococcus 2002-2003 14.8% 7.4% 6.9% 2003-2004 19.5% 7.7% 6.2% 2004-2005 16.0% 6.7% 7.6% Overall, the data collected during the last two reporting periods of the CSDM program indicates comparable results, with no significant increase or decrease in bacteria levels. 4.2 Lagoon Storm Drains and Receiving Water The focus of the Coastal Storm Drain Monitoring Program is to assess the impacts of the coastal storm drain outfalls on lagoon receiving waters. The analyses discussed herein are based only on paired sample data in which the storm drain flows reach the receiving water. It should be noted that there are instances in which paired samples cannot be collected from lagoon sampling locations. As such, the non-paired samples were not used in receiving water assessments. Furthermore, no correlation between an elevated storm drain Section 4 – Discussion 40 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report sample and adjacent lagoon waters was made if a paired sample was not collected. This assessment is based on the data collected from November 2004 through October 2005. 4.2.1 Lagoon Frequency of Use Matrix With the inclusion of lagoon monitoring in the CSDM Program, the criteria used to identify bacterial exceedances in lagoon receiving waters has been based on the water quality objectives established in the California Basin Plan (Table 1-2). Prior to the first year of sample collection in lagoons, the Coastal Copermittees stated that the water quality evaluations would be based on the AB411 standards for total and fecal coliform and the subcategories for Enterococcus (established by USEPA) to varying extents. During the first year of data collection in the lagoons (2002-2003), data was evaluated based on the Basin Plan’s narrative descriptions of the frequencies of use. The supporting documentation establishing the subcategories (Cabelli, 1983; USEPA, 1986) were studied and found to provide only qualitative descriptions of the use intensities and did not adequately define the frequency of use designations identified in the Basin Plan. CSDM Copermittees individually evaluated their lagoon sites and considered when to apply the additional Enterococcus standards to determine exceedances and initiate resampling and/or source investigations. A narrative explanation as to the specific frequency of use and associated criteria selected for each lagoon was included in the 2002- 2003 CSDM Annual Report. Epidemiology studies performed by Cabelli and Dufour provide the justification for having multiple Enterococcus frequency of use subcategories (Cabelli, 1983; Dufour, 1984). The Cabelli study focused on marine waters and the Dufour study focused on fresh waters. The studies were intended to establish a correlation between bacterial indicators and health risks associated with water contact. The findings of these two studies led to the USEPA’s Ambient Water Quality Criteria for Bacteria – 1986. The 1986 document established qualitative use criteria based on confidence intervals associated with an acceptable swimming associated gastro-enteritis rate per person (USEPA, 1986). A smaller confidence level corresponds with a more stringent single sample maximum. This document sub-categorizes the Enterococcus standards for marine waters, establishing objectives based on frequencies of use. The four categories recommended in the 1986 document are summarized in Table 4-3. Section 4 – Discussion 41 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 4-3 Frequency of Use Sub-categories for Enterococcus* Frequency of Use Associated Confidence Level Recommended Criteria (MPN or CFU/100 ml) Designated Beach Upper 75% C.L. 104 Moderate Full Body Contact Recreation Upper 82% C.L. 158 Lightly Used Full Body Contact Recreation Upper 90% C.L. 275 Infrequently Used Full Body Contact Recreation Upper 95% C.L. 500 *USEPA, 1986, Table 4 Of these four categories, no criteria for when and/or how to apply these standards were explicitly defined in the 1986 recommendations. The designated beaches were described as “frequently lifeguard protected, provide(ing) parking and other public access and are heavily used by the public” (USEPA, 1986, p. 7). The Basin Plan for the San Diego Region includes three of these four sub- categories, omitting the moderate use, conservatively including this in the designated beach category. There is a lack of established criteria or definitions for using the Enterococcus subcategories. The CSDM Copermittees recognized the need for a prescriptive process to apply the subcategories to lagoon monitoring sites and data gathered at these sites for source investigation and resampling purposes. As such, the CSDM Copermittees have developed a set of criteria contained in the Lagoon Frequency of Use Matrix (Table 4-4) to further classify lagoon sampling location areas based on use. The lagoon classification matrix criteria applies only to lagoon sampling locations and does not attempt to define uses at coastal beaches, because the coastal beaches have designated criteria established through AB 411 standards. The matrix does not attempt to change the Beneficial Uses of the lagoons, rather, it provides guidance in determining the most appropriate instances to initiate resampling and/or source identification investigations based on lagoon receiving water exceedances. The frequency of use matrix developed by the CSDM Copermittees assigns point totals to each sampling location based on five attributes (Table 4-5). These attributes were extrapolated from the designated beach description in the USEPA 1986 document. Each sampling location is evaluated separately and point totals are assigned based on the attributes of that location, adequate, moderate, limited, or none. The overall score is the sum of the point totals from each attribute. This number is then used to establish a frequency of use category for that location, the higher the point total, the more stringent the Enterococcus objective (Table 4-6). Section 4 – Discussion 42 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 4-4 Frequency of Lagoon Use Matrix Decision Matrix for Determination of Frequency of Use for Lagoons Attribute Adequate (3) Moderate (2) Limited (1) None (0) Total Parking1 Designated parking Area with >50 spaces Designated parking with <50 spaces On-street parking No parking available Swimming Recreation Area Pets Fire Rings Picnic Tables Restrooms Visitor Center/Snackshop Tidepooling Fishing Nature Trails/Hiking Jet Skis Number of Amendities/Activities2 Boat Ramp >5 3-51-20 Lifeguard Services3 Year Round Seasonal Patrolled None Beach Substrate4 Sand Cobbles/Narrow Beach Tidal Beach None Accessibility5 Designated water contact likely Water contact possible, use unlikely due to accessibility Limited water contact (i.e. boating or fishing only) Water contact prohibited Total Points (Designated beach=11-15, Light to Moderate Use=6-10, Infrequent Use=0-5) Each qualitative attribute (i.e. parking, amenities, lifeguard services, beach substrate) is ranked as adequate, moderate, limited, or none, with each ranking carrying an assigned number of points as indicated (3,2,1,0). 1Parking is assigned a point total based on number of parking spaces (adequate=designated parking with greater than 50 spaces; moderate=designated parking area with less than or equal to 50 parking spaces; limited=on-street parking only; none=no parking). 2Amendities are assigned a point total based on the number of available features, one point each (adequate=5+; moderate=3-5; limited=1-2; none=0). 3Lifeguard services are assigned a point total based on the services provided at the location (adequate=year round; moderate=seasonal; limited=patrolled only; none=none). 4Beach substrate is assigned a point total based on the quality of the beach for recreation (adequate=sandy; moderate=cobbles/narrow beach; limited=tidal beach with sandy bottom only; none=none). 5Accessibility is defined as accessibility for body contact recreation with head immersion (adequate=designated water contact likely - common, many people; moderate=designated for body contact but due to conditions, unlikely head immersion; limited=swim). The sum of the totals of the five attributes with then fall into an assigned frequency of use category. Section 4 – Discussion 43 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 4-5 Frequency of Use Categories based on Matrix Scores Score Frequency of Use 11-15 Designated Beach 6-10 Light to Moderate Use 0-5 Infrequent Use Using this matrix, the Copermittees have calculated scores and assigned the associated frequency of use for each lagoon sampling location in their jurisdiction. These scores, associated frequency of use, and relevant Enterococcus criteria are presented in Table 4-4. The appropriate Enterococcus criteria will be used to evaluate the bacteria levels in lagoon receiving water. Table 4-6 Frequency of Use Scores for Lagoon Monitoring Sites Lagoon Jurisdiction Site ID Score Frequency of Use Enterococcus Objective (MPN or CFU/100 ml) Buena Vista Oceanside Coast20 3 Infrequent 500 Buena Vista Oceanside Coast22 3 Infrequent 500 Buena Vista Carlsbad BV-002 2 Infrequent 500 Buena Vista Carlsbad BV-010 4 Infrequent 500 Agua Hedionda Carlsbad AH-005 1 Infrequent 500 Agua Hedionda Carlsbad AH-006 10 Moderate 276 Agua Hedionda Carlsbad AH-007 1 Infrequent 500 Agua Hedionda Carlsbad AH-008 3 Infrequent 500 Agua Hedionda Carlsbad AH-011 4 Infrequent 500 Agua Hedionda Carlsbad AH-017 6 Moderate 276 Agua Hedionda Carlsbad AH-18A 2 Infrequent 500 Agua Hedionda Carlsbad AH-019 5 Infrequent 500 Agua Hedionda Carlsbad AH-019A 5 Infrequent 500 Agua Hedionda Carlsbad AH-020 2 Infrequent 500 Agua Hedionda Carlsbad AH-021 2 Infrequent 500 Agua Hedionda Carlsbad AH-022 2 Infrequent 500 Agua Hedionda Carlsbad AH-023 2 Infrequent 500 Agua Hedionda Carlsbad AH-024 2 Infrequent 500 Agua Hedionda Carlsbad AH-025 2 Infrequent 500 Batiquitos Carlsbad BA-001 0 Infrequent 500 Batiquitos Carlsbad BA-004 0 Infrequent 500 Batiquitos Carlsbad BA-008 0 Infrequent 500 Batiquitos Carlsbad BA-009 0 Infrequent 500 Batiquitos Carlsbad BA-012 0 Infrequent 500 Batiquitos Carlsbad BA-013 0 Infrequent 500 Batiquitos Carlsbad BA-014 0 Infrequent 500 Batiquitos Carlsbad BA-015 0 Infrequent 500 Batiquitos Carlsbad BA-017 2 Infrequent 500 Batiquitos Carlsbad BA-018 2 Infrequent 500 Section 4 – Discussion 44 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Lagoon Jurisdiction Site ID Score Frequency of Use Enterococcus Objective (MPN or CFU/100 ml) Batiquitos Carlsbad BA-019 2 Infrequent 500 Batiquitos Carlsbad BA-020 4 Infrequent 500 Batiquitos Carlsbad BA-021 1 Infrequent 500 Batiquitos Carlsbad BA-022 2 Infrequent 500 Batiquitos Carlsbad BA-08-9 0 Infrequent 500 San Elijo Lagoon Encinitas CBS-1 5 Infrequent 500 San Elijo Lagoon Encinitas CBS-2 5 Infrequent 500 San Elijo Lagoon Encinitas CBS-5 2 Infrequent 500 San Elijo Lagoon Encinitas SEL-1 0 Infrequent 500 San Elijo Lagoon Encinitas SEL-2 1 Infrequent 500 San Elijo Lagoon Encinitas SEL-3 4 Infrequent 500 San Elijo Lagoon Solana Beach SE1 0 Infrequent 500 San Elijo Lagoon Solana Beach SE2 0 Infrequent 500 San Elijo Lagoon Solana Beach SE3 0 Infrequent 500 San Elijo Lagoon Solana Beach SE4 3 Infrequent 500 San Elijo Lagoon Solana Beach SE5 2 Infrequent 500 San Elijo Lagoon Solana Beach SE6 2 Infrequent 500 San Elijo Lagoon Solana Beach SE7 2 Infrequent 500 San Elijo Lagoon Solana Beach SE8 0 Infrequent 500 Los Penasquitos San Diego PENA03 1 Infrequent 500 Los Penasquitos San Diego PENA06 1 Infrequent 500 Los Penasquitos San Diego PENA08 1 Infrequent 500 Los Penasquitos San Diego PENA10 3 Infrequent 500 Los Penasquitos San Diego PENA11 3 Infrequent 500 4.3 Adaptive Sampling Diagrams A series of scatter plots, referred to as adaptive monitoring diagrams, were developed to illustrate the relationships between receiving water and storm drain bacteria levels, potential contamination sources, the AB 411 and Basin Plan regulatory drivers, and the storm drain criteria developed by the CSDM Workgroup. The adaptive monitoring diagrams stratify the paired sampling data into categories, or quadrants, for management purposes and are essential tools in the implementation of the current adaptive monitoring Program. Figures 4-1 through 4-6 summarize the results of total coliform, fecal coliform, and Enterococcus paired samples for coastal and lagoon sites. The scatter plots are divided into five quadrants that are formed by superimposing a line of slope = 1 and two perpendicular lines that delineate the AB 411 standard for the indicator of interest. For example, the five quadrants in Section 4 – Discussion 45 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figures 4-1 through 4-6 are formed by the 1:1 slope line and two lines delineating the AB 411 standard line for total coliform (10,000 MPN/ 100 mls). Receiving water bacteria levels in samples falling within quadrants above the 1:1 slope line (Quadrants II and III, and the upper part of Quadrant I) are higher in bacteria than the corresponding storm drain sample and are therefore, probably influenced by sources in addition to the storm drain discharge. Possible sources include birds, other marine wildlife, discharges from watercraft, and ocean bathers. Quadrant IV of the scatter plots includes the paired samples where elevated storm drain bacteria are likely to have caused or contributed significantly to the AB 411 exceedance. Quadrant V includes the elevated storm drain samples that did not result in an AB 411 exceedance. Table 4-7 describes the relationships associated with paired sample data falling into each quadrant and resulting management actions, where appropriate. Table 4-7 Adaptive Monitoring Description Quadrant Area Relationship/Possible Action Lower Left I Storm drain and receiving water levels are below receiving water standards. No action necessary. IA Storm drain concentration is above receiving water criteria but below 95th Percentile action level, receiving water is below receiving water criteria. No action necessary. Lower Right V Storm drain concentration above 95th Percentile action level while receiving water concentration is below receiving water criteria. Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain. Upper Left II Storm drain less than receiving water standards, while criteria is exceeded in receiving water sample. Resample LRW as soon as possible and eliminate non-storm drain sources. III Storm drain and receiving water samples are above receiving water criteria, and storm drain concentration < receiving water concentration. Storm drain contamination may contribute to receiving water exceedance, other sources are likely, resample ASAP and investigate. Upper Right IV Storm drain and receiving water samples are above receiving water criteria, and storm drain concentration > receiving water concentration. Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP and investigate. Section 4 – Discussion 46 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report 4.3.1 Coastal Adaptive Diagrams The coastal adaptive monitoring diagrams (Figures 4-1 – 4-3) clearly show all of the above-mentioned exceedances for the routine paired receiving water and storm drain samples. Of particular interest are those samples falling into Quadrants III and IV of the diagrams. All samples in these quadrants were investigated and details of those investigations are provided in Section 4.6, Source Investigations. For total coliform, there are no samples in Quadrant III and only four samples in Quadrant IV). Three of these samples were collected at Coast 8. For fecal coliform, there was a single sample falling into Quadrant III (EH-255 on August 22, 2005) and a single sample falling into Quadrant IV (Coast 8 on November 16, 2004). Enterococcus results identify a single sample falling into Quadrant III (EH-320 on March 1, 2005), and nine in Quadrant IV. The highest Enterococcus samples in Quadrant IV were both from EH-255 (August 22, 2005 and October 17, 2005). Four other samples in this quadrant were collected from Coast 8, one of which coincided with the high fecal sample on November 16, 2004. The other Enterococcus exceedances in Quadrant IV occurred at FM-060 (February 1, 2005) and EH-420 (April 19, 2005). 4.3.2 Lagoon Adaptive Diagrams The lagoon adaptive monitoring diagrams (Figures 4-4 – 4-6) show the relationship of paired storm drain and receiving water samples during 2004-2005. Figure 4-4 illustrates the Total Coliform paired sample data, Figure 4-5 illustrates the Fecal Coliform paired sample data, and the Enterococcus data is shown in Figure 4-6. The lagoon adaptive diagrams identify that the majority of the data falls below receiving water criteria and below 95th Percentile action levels for the storm drain. Table 4-8 shows the numbers and percentages of samples falling in each quadrant by lagoon. It should be noted that there were no paired samples collected within Los Penasquitos Lagoon during the reporting period, only unpaired storm drain samples. As such, this data is not applicable for the Adaptive Diagram Plots since a comparison between the storm drain and receiving water cannot be made. Section 4 – Discussion 47 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figure 4-1 2004-2005 Total Coliform Adaptive Monitoring Diagram - Coastal 1101001,00010,000100,0001,000,00010,000,0001101001,00010,000100,0001,000,00010,000,000Storm Drain (MPN/ 100 mls)Receiving Water (MPN/ 100 mlTC Standard10,000 MPN/ 100 mlsStorm drain and receiving water levels are below receiving water standards. No action necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.Storm drain concentration below 95th percentile criteria - no action necessaryUnlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.95th percentile criteria160,000 MPN/ 100 mlsStorm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary. Section 4 – Discussion 48 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figure 4-2 2004-2005 Fecal Coliform Adaptive Monitoring Diagram - Coastal1101001,00010,000100,0001,000,0001101001,00010,000100,0001,000,00010,000,000Storm Drain (MPN/ 100 mls)Receiving Water (MPN/ 100 mls)FC Standard - 400 MPN/ 100 mlsHighly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm Storm drain concentration below 95th percentile criteria - no action necessary95th percentile criteria27,600 MPN/ 100 mls FCStorm drain and receiving water levels are below receiving water standards. No action necessary.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms.Unlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.Section 4 – Discussion 49 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figure 4-3 2004-2005 Enterococcus Adaptive Monitoring Diagram - Coastal1101001,00010,000100,0001,000,0001101001,00010,000100,0001,000,000Storm Drain (MPN/ 100 mls)Receiving Water (MPN/ 100 mls)Storm drain concentration below 95th percentile criteria - no action necessaryEntero Standard (Ocean)- 104 MPN/ 100 mlsStorm drain and receiving water levels are below receiving water standards. No action necessary.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.95th percentile criteria18,400 MPN/ 100 Unlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms. Section 4 – Discussion 50 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figure 4.4 Adaptive Monitoring Diagram for Total Coliform - Lagoon Data 2004-20051101001,00010,000100,0001,000,00010,000,0001101001,00010,000100,0001,000,00010,000,000Lagoon Storm Drain Outfall (LSDO) (MPN/ 100 mls)Lagoon Receiving Water (LRW) (MPN/ 100 mls)Aqua HediondaBatiquitosSan ElijoBuena VistaStorm drain and receiving water levels are below receiving water standards. No action necessary.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.Storm drain concentration below 95th percentile criteria - no action Unlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.95th percentile criteria160,000 MPN/ 100 mls Section 4 – Discussion 51 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figure 4.5 Adaptive Monitoring Diagram For Fecal Coliform - Lagoon Data 2004-20051101001,00010,000100,0001,000,0001101001,00010,000100,0001,000,000Lagoon Storm Drain Outfall (LSDO) (MPN/ 100 mls)Lagoon Receiving Water (LRW) (MPN/ 100 mls)Agua HediondaBatiquitosSan ElijoBuena VistaHighly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.Storm drain concentration below 95th percentile criteria - no action necessary95th percentile criteria27,600 MPN/ 100 mls FCStorm drain and receiving water levels are below receiving water standards. No action necessary.Unlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms. Section 4 – Discussion 52 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figure 4.6 Adaptive Monitoring Diagram For Enterococcus Lagoon Data 2004-2005 1101001,00010,000100,0001,000,0001101001,00010,000100,000Lagoon Storm Drain Outfall (LSDO) (MPN/ 100 mls)Lagoon Receiving Water (LRW) (MPN/ 100 mls)Agua HediondaBatiquitosSan ElijoBuena VistaStorm drain and receiving water levels are below receiving water standards. No action necessary.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.95th percentile criteria 18,400 MPN/ 100 mls Ent.Storm drain concentration below 95th percentile criteria - no action necessaryUnlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms.Infrequent Use Moderate/Light Use Section 4 – Discussion 53 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Table 4-8 Lagoon Adaptive Diagram Quadrants (Percent of Observations in Quadrant Sets) Lagoon Indicator N* I IA V II III IV Total Coliform 52 5 0 0 0 0 52 Fecal Coliform 21 31 0 3 0 2 21 Agua Hedionda Enterococcus 25 30 0 1 0 1 25 Percentages per Quadrant 117 57% 39% 0% 2% 0% 2% Total Coliform 1 1 0 0 0 0 0 Fecal Coliform 1 0 1 0 0 0 0 Batiquitos Enterococcus 1 0 1 0 0 0 0 Percentages per Quadrant 3 33% 67% 0% 0% 0% 0% Total Coliform 27 26 1 0 0 0 0 Fecal Coliform 28 11 9 0 4 1 3 San Elijo Enterococcus 28 17 9 1 0 0 1 Percentages per Quadrant 83 65% 23% 1% 5% 1% 5% Total Coliform 20 1 2 1 4 7 5 Fecal Coliform 20 0 4 0 3 7 6 Buena Vista Enterococcus 20 2 5 0 0 6 7 Percentages per Quadrant 60 5% 18% 2% 12% 33% 30% *Number of paired samples collected per indicator The Quadrants I, IA, and V in each adaptive diagram identify receiving water bacteria levels below established receiving water criteria. In these instances, the data supports the finding that the storm drains are not negatively impacting the receiving waters. Samples collected in Agua Hedionda, Batiquitos, and San Elijo, Lagoons fell into quadrants I, IA, or V 96%, 100%, and 89% of the time, respectively. On the contrary, Buena Vista Lagoon had indicators falling into these quadrants only 25% of the time. Quadrants III and IV identify samples where elevated bacteria levels from the storm drains may be impacting adjacent receiving waters. The majority of the samples collected in Buena Vista Lagoon (63%) fell into Quadrants III or IV, indicating elevated storm drain concentrations and elevated receiving water concentrations. This suggests that the receiving waters adjacent to the Buena Vista sampling locations may be impacted from bacteria contributions originating from the storm drains. It should be noted however, that paired samples were only taken at one location in the lagoon and that Buena Vista Lagoon is a freshwater lagoon with no tidal flushing. Consequently, mixing, bacterial die-off rates, and inputs from natural sources have not been assessed. As such, conclusions cannot be made about overall water quality in Buena Vista lagoon. Section 4 – Discussion 54 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report During the reporting period, there were a total of 61 bacterial indicator exceedances in the receiving water, of which 16 were for total coliform, 29 were for fecal coliform, and 16 were for Enterococcus. For the storm drains, a total of 14 bacterial indicators exceeded, with 4 for total coliform, 5 for fecal coliform, and 5 for Enterococcus. Of the 128 total paired samples collected, however, only one sampling event resulted in an exceedance of both the receiving water and the storm drain criteria, Coast 20-1 on August 2, 2005. This one sampling event comprised less than 1% of the total paired samples collected during the reporting period. 4.4 General Trends and Seasonal Variations The information collected during this reporting period provided some interesting trend and seasonal information for both storm drains and receiving waters. Figures 4-7 and 4-8 show seasonal variation and indicator trends for storm drains, while Figures 4-9 and 4-10 show these observations for receiving waters. Please note, that these trends are based on the complete paired data set using both lagoon and coastal locations. Figure 4-7 Total Storm Drain Exceedances per Month 0 2 4 6 8 10 12 14 16 18 20 Nov Dec Jan Feb Mar Apr May Jun Jul Aug Sept Oct Month Exceedances Figure 4-8 Storm Drain Exceedances by Indicator 0 2 4 6 8 10 12 Nov Dec Jan Feb Mar Apr May Jun Jul Aug Sept Oct Month Exceedances enterococci fecal coliforms total coliforms As noted, the number of storm drain exceedances is higher in the dry (summer) months with very few exceedances occurring during the wet (winter) months (Nov-Feb). This finding could be attributed to two possible reasons. First, the dry season (April – October) sampling frequency is double that of the wet season. As such there would be a greater chance of finding an exceedance. Second, the regular flushing of storm drains that occurs with each rain event prevents a build-up or regrowth of bacteria. Another interesting finding is that total coliform dominates the storm drain exceedances. Additionally, there were no exceedances of the Enterococcus storm drain action level between November and February. Section 4 – Discussion 55 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Figure 4-10 Receiving Water Exceedances by Indicator 0 2 4 6 8 10 Nov Dec Jan Feb Mar Apr May Jun Jul Aug Sept Oct Month Exceedances Total Fecal Entero Figure 4-9 Total Receiving Water Exceedances per Month 0 2 4 6 8 10 12 14 16 18 Nov Dec Jan Feb Mar Apr May Jun Jul Aug Sept Oct Month Exceedances Similar to the storm drains, the number of receiving water exceedances is also higher in the dry (summer) months. However, there tend to be more receiving water exceedances in the wet (winter) months when compared to storm drains. This could be a result of the storm drain flushing that occurs during each rain event, which would carry the bacteria into the receiving water. The indicators themselves also exhibit slightly different trends with Enterococcus having more indicator exceedances than either total or fecal coliform. 4.5 Revised 95th Percentile Storm Drain Action Levels As stated in Section 3 of this report, the 95th percentile storm drain action levels are used to initiate investigations based on storm drain bacteria concentrations. These action levels are re-calculated annually. The 95th percentile storm drain action levels used for assessments during this current reporting period are presented in Table 3-7. New 95th-percentile criteria have been re-calculated with the data collected during the current (2004-2005) sampling season to reflect current storm drain conditions and are presented in Table 3-24 of this report. These criteria will be used to initiate IC/ID investigations at storm drain sites starting with samples collected in 2006. It should be noted that 95th percentile action levels for total coliform, fecal coliform and Enterococcus decreased from the previous reporting period. Both total coliform and fecal coliform were greatly decreased, with total coliform decreasing from 500,000 MPN/mls to 289,150 MPN/mls and fecal coliform decreasing from 27,600 MPN/mls to 18,755 MPN/mls. Such decreases are to be expected as Copermittees continue to investigate and eliminate discharges each year. It is anticipated that this downward trend in storm drain bacteria levels will continue as more BMPs are implemented annually. Section 4 – Discussion 56 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report 4.6 Sampling Frequency Reduction Data collected from all sample sites was reviewed prior to April 1, 2004 to determine the sites eligible for reduced sampling using the criteria identified in Section 1.4 of this report. Sites meeting the criteria at both storm drain and receiving water locations were identified. The sampling frequency reduction was calculated for the upcoming year and is presented in Table 3-25. During this reporting period, the City of Encinitas continued to utilize the SFRC for three sites and the recent data indicates that these sites will remain on a reduced sampling schedule. 4.7 Source Investigations Source identification investigations were initiated when sampling indicated that bacteria levels exceeded receiving water criteria or 95th percentile action levels (for storm drains). The source investigations conducted by the Coastal Copermittees during the 2004-2005 reporting period are discussed below by City. It is worth noting that a success of the program this year is evident from some of the IC/ID investigations listed below. For example, locations having repeated flows were traced upstream to identify several different sources. The IC/ID investigations successfully identified and eliminated problems such as improper washing activities, over-irrigation, potential issues with the homeless, leaking water lines and illicit connections. The investigations led to corrective actions being implemented and improved compliance in each situation. All of the investigations are further detailed in the tables below. Section 4 – Discussion 57 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Oceanside Location Coast 8 Original Sample Date Ongoing Investigation Original Sample Results Various exceedances spanning the reporting period. Investigation Date Ongoing Investigation Investigation Results: Routine sampling at the Harbor Boat Wash outfall has revealed consistently high levels of bacteria in the runoff. Since February 2004 the City of Oceanside has been conducting an ongoing investigation to locate the source of the contamination. The outfall drains a public boat wash area, and is located next to a sewage dump for recreational vehicles. The Harbor and Clean Water Program staff hired Ace Pipeline Inspection and Cleaning Service to clean the storm drain line in April 2005. The CDS boxes were jet cleaned/vacuumed and the 6” PVC line was jet cleaned. Sampling following cleaning continued to show intermittent exceedances. In October 2005, Harbor and Clean Water staff hired Attitude Technology to investigate and clean the system. Conclusions from the investigation included: 1. The grate for vault 1 collects significant amounts of debris that aid in breeding bacteria; 2. Vault 1 is handling a certain amount of raw sewage runoff and has a large amount of solids; 3. Piping from vault 1 to vault 2 is loaded with solids, hydrocarbons and bacteria; 4. The building near the service island is dripping fecal matter from bird droppings; 5. Vault 2 is handling a quantity of raw sewage runoff from vault 1 and a quantity of solids; 6. The outfall from vault 2 has standing animal fecal matter. Both vault 1 and 2 were serviced and completely cleaned out. Samples were taken following cleaning to determine baseline bacteria levels. Attitude Technology installed anti-microbial devices in the marina vault following Oceanside City staff taking regular samples and also took water samples directly from the vault. Attitude Technology plans to take follow-up samples from the boat wash outfall, the vault closest to the outfall and the connecting vault near the service island. Location Coast 14 Original Sample Date 10/11/05 Original Sample Results: TC = 500,000 MPN/100mL Investigation Date 10/15/05 Investigation Results: Most probable sources are large amount of sand in storm drain and squirrel population. Next routine sample came back within acceptable limits. Section 4 – Discussion 58 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Location Coast 18 Original Sample Date 4/12/05, 4/26/05 Original Sample Results (for storm drain): 4/12/05 - TC = 500,000 MPN/100mL, E = 155,000 MPN/100mL; 4/26/05 – TC = 240,000 MPN/100mL, E = 21,800 MPN/100mL Investigation Date 4/25/05 – 5/03/05 Investigation Results: Intermittently high results have been seen at this site. Resampling is often not possible due to absence of flow. On one site visit Oceanside staff found the guard at the gate of the St. Malo community excessively watering plants with a garden hose. Oceanside staff spoke with the guard regarding conserving water and minimizing the amount of water being applied to the street and subsequently running into the storm drain. The guard agreed and also informed staff of water flows coming from neighbors across the street and around the immediate neighborhood. Possible sources of contamination in addition to over irrigation include debris in the storm drain, a dead animal or animals living in storm drain, or pet waste. No flow at next regular sampling round. Investigation closed. Location Coast 20-1 Original Date Sampled 6/1/05, 8/2/05, 9/13/05 Original Sample Results (for storm drain): 6/1/05 - TC = 240,000 MPN/100mL, FC = 35,000 MPN/100mL; 8/2/05 – TC = 180,000 MPN/100mL; 9/13/05 – TC = 180,000 MPN/100mL Investigation Date Ongoing Investigation Investigation Results: Routine sampling revealed consistently high bacteria levels draining Buena Vista Lagoon. Since May 2004, the City of Oceanside has been actively investigating this nebulous source of contamination. The Coast 20-1 outfall lies south of Highway 78 and the Pacific Plaza Shopping Center, east of Interstate 5 and west of Jefferson St. The outfall drains 32 homes from a residential neighborhood called Fire Mountain, north of the Pacific Plaza Shopping Center. In December 2004, Oceanside City staff tested the storm drain further upstream to see if the source of contamination could be isolated. No samples identified elevated levels of fecal coliform or Enterococcus. On 11 May 2005, Ace Pipeline Inspection and Cleaning Service conducted a CCTV inspection of the storm drain. On 12 May 2005, Ace Pipeline Inspection and Cleaning Service jet cleaned and vacuumed the 56” RCP storm drain. In August 2005, Oceanside City staff retested the storm drain further upstream and found elevated fecal coliform in one of the samples. Oceanside City staff also noticed bats living in the storm drain and concluded that the bat guano could be one possible source of contamination. Section 4 – Discussion 59 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Carlsbad Location OC-002 Original Sample Date 4/18/05 Original Sample Results (for storm drain): TC = 73,600 CFU/100mL, FC = 35,050 CFU/100mL, E = 3,400 CFU/100mL Investigation Date 5/3/05 Investigation Results: No flow to receiving water. Rain delayed investigation until the next regularly scheduled event. When we arrived to resample, there was no flow and no evidence upstream on the street. Location BV-002 Original Sample Date 5/2/05, 7/26/05, 10/3/05 Original Sample Results (for storm drain): 5/2/05 - TC = 269,000 CFU/100mL, FC = 39,000 CFU/100mL; 7/26/05 – TC = 71,000 CFU/100mL, FC = 33,800 CFU/100mL, E = 32,600 CFU/100mL; 10/3/05 – TC = 98,000 CFU/100mL, FC = 44,000 CFU/100mL, E = 15,200 CFU/100mL Investigation Date 5/16/05, 8/9/05, 10/24/05 Investigation Results: Rain delayed investigations, and resamples are within limits. The flow tracked upstream to SDG&E vault pump that is pumping out groundwater. There is also a homeless population in area, making human waste a likely source. Location AH-19A Original Sample Date 5/31/05, 7/26/05, 8/23/05 Original Sample Results (for receiving water): 5/31/05 - FC = 400 CFU/100mL; 7/26/05 – FC = 440 CFU/100mL, E = 280 CFU/100mL; 8/23/05 – FC = 1,880 CFU/100mL, E = 380 CFU/100mL Investigation Date 6/2/05, 8/3/05, 8/25/05 Investigation Results: Nothing on the street upstream of marina to contribute to receiving water, only possibility is bird waste and dead crabs on rocks near the water due to red tide, and a few outdoor showers as possible contributors. Location 0C-007 Original Sample Date 6/13/05 Original Sample Results (for storm drain): TC = 29,800 CFU/100mL, FC = 2,400 CFU/100mL, E = 24,700 CFU/100mL Investigation Date 6/27/05 Investigation Results: Did not have knowledge of exceedances until time for next regular monitoring event on 6/27/05. Resample results within limits. Section 4 – Discussion 60 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Location AH-017 Original Sample Date 6/29/06 Original Sample Results (for storm drain): FC = 34,150 CFU/100mL, E = 22,050 CFU/100mL Investigation Date 7/7/05 Investigation Results: No flow during investigation to resample. Investigation at time of original sample showed possible source a nearby overflowing outdoor fountain. Location AH-006 Original Sample Date 10/5/05 Original Sample Results (for receiving water): FC = 960 CFU/100mL, E = 430 CFU/100mL Investigation Date 10/11/05 Investigation Results: Resample results are all within limits. Previous investigations shown to be groundwater. Investigation at time of original sample found a possible contributor of flow to be sump pumped groundwater from a nearby underground garage. Encinitas Location EH-420 75L Original Sample Date 4/19/05 Original Sample Results (for receiving water): Enterococcus=128 cfu/100 ml (see table below for paired data) Investigation Date 4/20/05 Investigation Results: See discussion below. Prefix Station ID Station Type Date Time Analyte Qualifier Result R EH-420 CSDO 4/19/2005 11:20 Total Coliform None 2,800 R EH-420 CSDO 4/19/2005 11:20 Fecal Coliform None 1750 R EH-420 CSDO 4/19/2005 11:20 Enterococcus None 420 R EH-420 CRW (75L) 4/19/2005 11:15 Total Coliform None 78 R EH-420 CRW (75L) 4/19/2005 11:15 Fecal Coliform None 79 R EH-420 CRW (75L) 4/19/2005 11:15 Enterococcus None 128 Routine samples were collected on April 19, 2005 at the mouth of Cottonwood Creek and in the receiving water 75 feet left of the creek mouth. Results indicated that water quality in the receiving water exceeded the State AB 411 standard for Enterococcus of 104 cfu/100 ml. None of the corresponding storm drain samples were above established action levels. Conditions noted during sample collection included heavy kelp, organics, Section 4 – Discussion 61 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report and arundo at the creek mouth and on the beach. The mouth of Cottonwood Creek is pictured on the previous page in a photograph from April 21, two days after the initial sample was collected. Upon receipt of the results, City staff immediately resampled at the mouth of Cottonwood Creek and at three locations in the receiving water. These follow-up samples were collected on April 20, 2005. The conditions noted on April 19 had not changed, as noted in the visual observations database. Data collected from the follow-up sample is presented in the table below. Prefix Station ID Station Type Date Time Analyte Qualifier Result F EH-420 CSDO 4/20/2005 11:25 Total Coliform None 3,000 F EH-420 CSDO 4/20/2005 11:25 Fecal Coliform None 1750 F EH-420 CSDO 4/20/2005 11:25 Enterococcus None 240 F EH-420 CRW (75L) 4/20/2005 11:20 Total Coliform None 75 F EH-420 CRW (75L) 4/20/2005 11:20 Fecal Coliform None 43 F EH-420 CRW (75L) 4/20/2005 11:20 Enterococcus None 5 F EH-420 CRW (0M) 4/20/2005 11:22 Total Coliform None 64 F EH-420 CRW (0M) 4/20/2005 11:22 Fecal Coliform None 12 F EH-420 CRW (0M) 4/20/2005 11:22 Enterococcus < 4 F EH-420 CRW (75R) 4/20/2005 11:23 Total Coliform None 5 F EH-420 CRW (75R) 4/20/2005 11:23 Fecal Coliform None 2 F EH-420 CRW (75R) 4/20/2005 11:23 Enterococcus None 1 Follow-up samples were collected at three locations in the receiving water, 75 feet right and left of the creek mouth and at point 0 in the mixing zone. All data collected on April 20 indicated that receiving water bacteria concentrations were below State AB411 standards. The sample collected at the mouth of Cottonwood Creek was also below action levels. The cause of the exceedance was likely the kelp, organic debris, and arundo concentrated at the creek mouth. All water from the creek was flowing through the heavy wrackline prior to entering the receiving water. It has been well documented that the heavy wrackline may contribute to increases in bacteria concentrations. In order to reduce the occurrence of future bacteria exceedances, the City contracted to have the debris accumulation on the beach at the creek mouth removed on April 21. The picture below is of the beach at Cottonwood Creek after the debris was removed. Section 4 – Discussion 62 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Location CBS-1 Lagoon Receiving Water Original Sample Date 3/9/05 Original Sample Results (for receiving water): Fecal Coliform=530 cfu/100 ml; Enterococcus=590 cfu/100 ml (see table below for paired data) Investigation Date 3/10/05 Investigation Results: See discussion below. Prefix Station ID Station_Type Date Time Analyte Qualifier Result R CBS-1 LSDO 3/9/2005 12:08 Total Coliform None 180 R CBS-1 LSDO 3/9/2005 12:08 Fecal Coliform None 60 R CBS-1 LSDO 3/9/2005 12:08 Enterococcus None 60 R CBS-1 LRW 3/9/2005 12:04 Total Coliform None 360 R CBS-1 LRW 3/9/2005 12:04 Fecal Coliform None 530 R CBS-1 LRW 3/9/2005 12:04 Enterococcus None 590 Routine samples collected on March 9, 2005 at CBS-1 exceeded Basin Plan standards in the receiving water for fecal coliform and enterococcus. At this monitoring location, there is no connection between the storm drain flow and the receiving water. Since the storm drain results were low and there is no flow from the storm drain entering the receiving water on the surface, it is unlikely that the exceedances in the receiving water were related to the storm drain. Although the samples were collected during a dry weather period, with a minimum of 72 hours since the last rainfall, the previous storm event may have contributed to the elevated bacteria concentrations in the lagoon. A storm on March 4-5 generated 0.44” of rain in Encinitas which would cause significant amounts of runoff to enter San Elijo Lagoon. Due to muted tidal flushing in the lagoon, bacteria concentrations in enclosed estuaries may not recover as quickly as bacteria concentrations in open coastal receiving waters. Samples were collected approximately 96 hours after the end of the rain event, however bacteria concentrations remained elevated. Since the storm drain was not considered a source of the bacteria for the dry weather exceedance, the site was not resampled immediately but was kept on a routine monitoring schedule. Bacteria concentrations in routine samples collected in April were below applicable standards. Location CBS-5 Lagoon Storm Drain Outfall Original Sample Date 6/7/05 Original Sample Results (for storm drain): Enterococcus=30,450 cfu/100 ml (see table below for paired data) Investigation Date 6/16/05, 6/20/05, 6/30/05, on-going Investigation Results: See discussion below. Prefix Station ID Station_Type Date Time Analyte Qualifier Result R CBS-5 LSDO 6/7/2005 9:58 AM Total Coliform None 25700 R CBS-5 LSDO 6/7/2005 9:58 AM Fecal Coliform None 6700 R CBS-5 LSDO 6/7/2005 9:58 AM Enterococcus None 30450 R CBS-5 LRW 6/7/2005 10:02 AM Total Coliform None 280 R CBS-5 LRW 6/7/2005 10:02 AM Fecal Coliform None 360 R CBS-5 LRW 6/7/2005 10:02 AM Enterococcus None 240 Section 4 – Discussion 63 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report The dry weather monitoring program in August 2003 detected bacteria exceedances at this location. After an extensive ICID investigation, staff concluded that the bacteria were originating from a restaurant in the immediate area. Wash water and other waste was bypassing a trench drain connected to the sanitary sewer and was instead mixing with irrigation water in the area. This provided the conveyance mechanism for the bacteria to enter the lagoon. Upon correction of the problem, flows were not detected at the location any longer. Dry weather monitoring in 2004 confirmed the lack of flow at the location and samples were not collected. In 2005, routine dry weather monitoring found flows at the location and bacteria concentrations were found to be elevated at the storm drain, although only a fraction of concentrations in 2003. Samples were also collected in the receiving water at this time, where no exceedances were found. The flow was approximately 1 gallon per minute at the site. There were no unusual visual observations noted that would contribute to increased bacteria in the storm drain. Because of the elevated bacteria, the site is now monitored more frequently in the CSDM program. Following the sample on June 7, staff visited the site weekly though the end of June and continually found the storm drain dry with no flow to sample. Following these site visits, the site was put on the routine monitoring schedule with the other sites in San Elijo Lagoon. This location has been monitored since and no flows have been present to sample. Bacteria sources in this location are transient and the site will continue to be monitored regularly. Additionally, staff remains vigilant with the restaurants in the area. These are all high priority commercial facilities and are inspected annually by the Clean Water Program in an effort to ensure compliance and educate businesses and workers. Location SEL-1 Lagoon Receiving Water Original Sample Date 5/3/05 Original Sample Results (for receiving water): Fecal Coliform=920 cfu/100 ml (see table below for paired data) Investigation Date 5/11/05 Investigation Results: See table and discussion below. Prefix Station ID Station_Type Date Time Analyte Qualifier Result R SEL-1 LSDO 5/3/2005 12:18 PM Total Coliform None 60 R SEL-1 LSDO 5/3/2005 12:18 PM Fecal Coliform None 20 R SEL-1 LSDO 5/3/2005 12:18 PM Enterococcus None 60 R SEL-1 LRW 5/3/2005 12:23 PM Total Coliform < 20 R SEL-1 LRW 5/3/2005 12:23 PM Fecal Coliform None 920 R SEL-1 LRW 5/3/2005 12:23 PM Enterococcus None 140 F SEL-1 LSDO 05/11/05 2:28 PM Total Coliform None 100 F SEL-1 LSDO 05/11/05 2:28 PM Fecal Coliform < 20 F SEL-1 LSDO 05/11/05 2:28 PM Enterococcus None 20 F SEL-1 LRW 05/11/05 2:30 PM Total Coliform < 20 F SEL-1 LRW 05/11/05 2:30 PM Fecal Coliform None 100 F SEL-1 LRW 05/11/05 2:30 PM Enterococcus None 10 Section 4 – Discussion 64 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Routine samples collected on May 3, 2005 at SEL-1 exceeded Basin Plan standards in the receiving water for fecal coliform. At this monitoring location, there is no direct connection between the storm drain flow and the receiving water, although during high tides the flows likely enter the lagoon. Flows here are typically only trickles of water, noted as <0.5 gallons per minute on the field sheets. Since the storm drain results were very low and the flows are minimal, it is unlikely that the exceedances in the receiving water were related to the storm drain. Follow-up samples contained low concentrations of bacteria in the storm drain and in the receiving water. Although the samples were collected during a dry weather period, with a minimum of 72 hours since the last rainfall, the previous storm event may have contributed to the elevated bacteria concentrations in the lagoon. A storm on April 28-29 generated 0.58” of rain in Encinitas which would cause significant amounts of runoff to enter San Elijo Lagoon. Due to muted tidal flushing in the lagoon, bacteria concentrations in enclosed estuaries may not recover as quickly as bacteria concentrations in open coastal receiving waters. Samples were collected approximately 120 hours after the end of the rain event, however bacteria concentrations remained elevated. All other bacteria samples collected at this location throughout the monitoring period were below standards. Location CBS-2 Lagoon Receiving Water Original Sample Date 1/19/05, 2/2/05, 5/3/05, 6/2/05, 6/16/05, 8/29/05, 9/28/05 Original Sample Results (for receiving water): See tables below Investigation Date On-going Investigation Results: See table and discussion below. Through the reporting period, CBS-2 receiving water samples contained bacteria concentrations higher than Basin Plan Rec-1 standards regularly. The site is located near the mouth of San Elijo Lagoon, just east of Highway 101. Of 25 total paired samples collected, there were 8 exceedances in the receiving water. One of the samples exceeded for fecal and enterococcus while six exceeded the fecal standard only. This equates to 7 of 25 receiving water samples exceeding standards, or 28%. In three of the samples with receiving water exceedances, the storm drain bacteria concentrations were low. These samples fall into Quadrant II (QII) of the adaptive monitoring diagram. Four of the samples with receiving water exceedances also had storm drain bacteria concentrations above Basin Plan standards, although well below 95th percentile action levels established by this program. These samples fall within Quadrant III (QIII) or IV (QIV) of the adaptive monitoring diagrams and warrant much more attention. The table below separates the samples according to the relationship between the storm drain and receiving water bacteria concentrations. CBS-2 Exceedances According to the Adaptive Monitoring Strategy, Nov 2004-Oct 2005 Quadrant II Quadrant III, IV February 2 January 19 May 3 June 16 June 2 August 29 September 28 Section 4 – Discussion 65 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Quadrant II Exceedances at CBS-2 Paired samples falling within QII are characterized by receiving water concentrations over Basin Plan Rec-1 standards and storm drain concentrations that are less than Basin Plan Rec-1 standards. On each occasion, QII samples had receiving water fecal coliform concentrations above the standard of 400 cfu/100 ml. Paired bacteria data for these exceedances is listed below. Quadrant II Fecal Coliform Exceedances for CBS-2 Prefix Station ID Station_Type Date Time Result R CBS-2 LSDO 2/2/2005 10:43 100 R CBS-2 LRW 2/2/2005 10:41 660 R CBS-2 LSDO 5/3/2005 12:05 250 R CBS-2 LRW 5/3/2005 12:04 490 R CBS-2 LSDO 6/2/2005 13:55 100 R CBS-2 LRW 6/2/2005 13:53 420 In each case, the storm drain fecal coliform concentrations are well below Basin Plan standards. This supports the theory that the exceedances in the receiving water were caused by non-storm drain sources. These non-storm drain sources in the lagoon include wildlife, birds, bacterial regrowth, and others. In each instance, confirmation/follow-up samples were collected in the storm drain and in the receiving water and results for both were below Basin Plan standards. Data collected for follow-up samples is shown below. Follow-up Sample Data for QII Exceedances at CBS-2 Prefix Station ID Station_Type Date Time Analyte Qualifier Result F CBS-2 LSDO 2/9/2005 11:19 Total Coliform None 3720 F CBS-2 LSDO 2/9/2005 11:19 Fecal Coliform None 60 F CBS-2 LSDO 2/9/2005 11:19 Enterococcus None 300 F CBS-2 LRW 2/9/2005 11:18 Total Coliform None 130 F CBS-2 LRW 2/9/2005 11:18 Fecal Coliform None 20 F CBS-2 LRW 2/9/2005 11:18 Enterococcus None 60 F CBS-2 LSDO 05/11/05 11:30 Total Coliform < 20 F CBS-2 LSDO 05/11/05 11:30 Fecal Coliform None 100 F CBS-2 LSDO 05/11/05 11:30 Enterococcus None 380 F CBS-2 LRW 05/11/05 11:35 Total Coliform < 20 F CBS-2 LRW 05/11/05 11:35 Fecal Coliform < 10 F CBS-2 LRW 05/11/05 11:35 Enterococcus None 10 F CBS-2 LSDO 6/8/2005 10:29 Total Coliform < 20 F CBS-2 LSDO 6/8/2005 10:29 Fecal Coliform None 240 F CBS-2 LSDO 6/8/2005 10:29 Enterococcus None 520 F CBS-2 LRW 6/8/2005 10:28 Total Coliform < 20 F CBS-2 LRW 6/8/2005 10:28 Fecal Coliform None 10 F CBS-2 LRW 6/8/2005 10:28 Enterococcus < 10 Section 4 – Discussion 66 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report To better understand the possible causes for these receiving water exceedances, the observations and conditions at the time of sampling were assessed. Common factors to the initial sampling events included tidal flow and recent rainfall. In each case, samples were collected while the lagoon was flushing during the peak low tides for the day. This would cause less saline water from the east basin of the lagoon to flow to the sea. It is reasonable that this water, originating from freshwater sources such as Escondido Creek, would contain higher concentrations of bacteria than other water in the lagoon. Tidal mixing is muted in the east basins of the lagoon, prohibiting dilution and attenuation of bacteria concentrations here. In addition, two of the three samples were collected after significant rain events. Samples are not collected within 72 hours of a rain event in order to characterize the samples as collected under dry weather conditions. This 72 hour time period is generally long enough for bacteria concentrations in open coastal receiving waters to return within Rec-1 standards. However, this may not be the case in enclosed estuaries where tidal flushing is restricted and attenuation of the rain water may take longer than 72 hours. Samples in February and May were collected approximately 96 and 120 hours after rain events of 0.20” and 0.58” respectively. Collection within several days after a rain event coupled with low tides and flushing of the lagoon may account for elevated bacteria concentrations. Quadrant III and Quadrant IV Exceedances at CBS-2 QIII and QIV exceedances are of greater concern as these include elevated bacteria concentrations in the receiving water and in the storm drain. In both quadrants the receiving water sample exceeded Basin Plan Rec-1 standards. In QIII samples, the storm drain bacteria concentration was also above the Rec-1 standard but less than the concentration in the receiving water. In QIV samples, the storm drain bacteria concentration was above Rec-1 standards and is greater than the concentration in the receiving water. Although all storm drain data is well below 95th percentile action levels, the concentrations are high enough (above Rec-1) that there may be contributions to the receiving water exceedances by the storm drain flows. Dilution and safety factors are disregarded when these types of exceedances occur. Four routine paired samples had bacteria concentrations falling into QIII or QIV. The paired sample data is presented below. QIII and QIV Paired Sampling Exceedances at CBS-2 Prefix Station ID Station_Type Date Time Analyte Qualifier Result R CBS-2 LSDO 1/19/2005 13:50 Total Coliform None 3000 R CBS-2 LSDO 1/19/2005 13:50 Fecal Coliform None 440 R CBS-2 LSDO 1/19/2005 13:50 Enterococcus None 540 R CBS-2 LRW 1/19/2005 14:00 Total Coliform None 300 R CBS-2 LRW 1/19/2005 14:00 Fecal Coliform None 690 R CBS-2 LRW 1/19/2005 14:00 Enterococcus None 520 R CBS-2 LSDO 06/16/05 11:19 Total Coliform < 20 R CBS-2 LSDO 06/16/05 11:19 Fecal Coliform None 1980 R CBS-2 LSDO 06/16/05 11:19 Enterococcus None 2200 R CBS-2 LRW 06/16/05 11:17 Total Coliform < 20 R CBS-2 LRW 06/16/05 11:17 Fecal Coliform None 660 R CBS-2 LRW 06/16/05 11:17 Enterococcus None 160 R CBS-2 LSDO 08/29/05 11:34 Total Coliform None 840 Section 4 – Discussion 67 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report R CBS-2 LSDO 08/29/05 11:34 Fecal Coliform None 10920 R CBS-2 LSDO 08/29/05 11:34 Enterococcus None 3100 R CBS-2 LRW 08/29/05 11:33 Total Coliform None 40 R CBS-2 LRW 08/29/05 11:33 Fecal Coliform None 3300 R CBS-2 LRW 08/29/05 11:33 Enterococcus None 420 R CBS-2 LSDO 9/28/2005 10:57 Total Coliform None 100 R CBS-2 LSDO 9/28/2005 10:57 Fecal Coliform None 2350 R CBS-2 LSDO 9/28/2005 10:57 Enterococcus None 450 R CBS-2 LRW 9/28/2005 10:55 Total Coliform None 120 R CBS-2 LRW 9/28/2005 10:55 Fecal Coliform None 520 R CBS-2 LRW 9/28/2005 10:55 Enterococcus None 100 Paired samples collected on January 19 had exceedances in the receiving water for fecal coliform and enterococcus. Storm drain concentrations were similar for both indicators on the initial samples. A rain event totaling 0.17” occurred the following week preventing the collection of confirmation samples. The confirmation sample was collected on February 2. This pair of samples had one exceedance for fecal coliform in the receiving water. There was no correlating storm drain exceedance. February 2 samples were collected on an outgoing tide approximately 96 hours following the rain event, accounting for the increase in bacteria in the receiving water. Samples collected the following week, after a significant dry period, contained no exceedances in the receiving water or in the storm drain. Although bacteria counts in the initial storm drain sample, January 19, were higher than Rec-1 standards, the bacteria concentrations are very low in comparison to storm drain bacteria concentrations in general. Without confirmation and considering the relatively low concentrations of bacteria in the storm drain on the initial exceedance, further investigation was not performed. Paired samples collected on June 16 had fecal coliform concentrations above Rec-1 standards in the lagoon. This exceedance was accompanied by a storm drain concentration also above Rec-1 standards for the receiving water, suggesting a possible cause and effect relationship between the two. Follow-up samples collected on June 20 and June 30 had no elevated bacteria concentrations in the storm drain or in the receiving water. With no confirmation of the bacteria exceedances, and due to the relatively low concentrations of bacteria in the storm drain, further upstream source investigations were not performed. Paired samples collected on August 29 contained elevated fecal coliform concentrations in the receiving water and in the storm drain. These concentrations were significantly higher than usual for both samples. Confirmation samples were collected on August 31 and on September 6. Neither of the paired confirmation samples contained bacteria concentrations above standards. However, due to the initial concentrations, upstream source investigations were performed with additional upstream samples collected on August 31 and on September 6. On August 25 a construction project began to pump uncontaminated groundwater into the storm drain upstream of CBS-2. The dewatering project generates groundwater in quantities less than that requiring regulation by Regional Water Quality Control Board under Order 2001-96, provided the groundwater is free of pollutants. Since the operation does not fall under RWQCB regulation, the City of Encinitas has chosen to regulate the discharge. The dewatering utilizes multiple types of filtration and reverse Section 4 – Discussion 68 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report osmosis to remove all sediment, nitrates, and bacteria from the groundwater. Samples collected on August 31 confirmed that the water is free of bacteria. The construction site is generating between 6,000 and 20,000 gallons of groundwater per day and discharges into the storm drain above CBS-2. Although the water has proven to be free of pollutants, staff suspects that the initial pumping of groundwater into the system may have re-suspended some sediment and associated bacteria already present in the channel. With clean follow-up samples at the storm drain and in the receiving water, it seems that this first flush was the case and is no longer a problem. This potential for bacteria discharge associated with re-suspension will be evaluated more rigorously with future dewatering projects and appropriate BMPs will be implemented to prevent these types of discharges. Paired samples collected on September 28 had fecal coliform concentrations above Rec-1 standards in the lagoon. This exceedance was accompanied by a storm drain concentration also above Rec-1 standards for the receiving water, suggesting a possible cause and effect relationship between the two. Follow-up samples collected on October 6 and 24 had no elevated bacteria concentrations in the storm drain or in the receiving water. With no confirmation of the bacteria exceedances, and due to the relatively low concentrations of bacteria in the storm drain, further upstream source investigations were not performed. Best professional judgment and experience indicate that because of the relatively low concentrations of bacteria entering the lagoon, upstream ICID investigation is difficult. Since the fecal concentrations are low relative to potential sewage sources, sewage is not a likely source of the bacteria problems at CBS-2. However, due to the persistent exceedances at CBS-2, source investigations in the area are on-going. Staff suspects that the major factor contributing to bacteria exceedances in the drainage area is a commercial shopping center in Cardiff. Several restaurants operate within a small area just upstream of the sample location. With relatively low bacteria counts and persistent exceedances, the cause is likely urban runoff from these commercial operations. Restaurants such as Yogi’s and Jack in the Box continue to generate complaints from the public. These restaurants are inspected and educated regularly. However, staff suspects that washing continues at these locations, most often after hours when the businesses close. Staff will continue to focus on commercial inspections, complaint response, and education in this area in an effort to reduce pollutants. Sources of bacteria outside of the storm drain regularly contribute to exceedances in water quality at CBS-2. In addition, urban runoff and commercial activities upstream of the sample location also contribute to the bacteria exceedances at this location. Staff will continue to monitor and attempt to source bacteria exceedances at this location. Section 4 – Discussion 69 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Solana Beach Location EH-390 Original Date Sampled Ongoing Investigation Original Sample Results: Storm drain consistently exceeds effluent limits Investigation Date Ongoing Investigation Investigation Results: Routine sampling revealed consistently high bacteria levels at Seascape Sur Outfall. Since May 2003, the City of Solana Beach has been actively investigating this mysterious source of contamination. The Seascape Sur Outfall lies west of Coast Highway 101 and the Beachwalk Shopping Center, adjacent to the Seascape Sur beach access. The outfall drains a large area of high-density residential units as well as a small shopping center with a few restaurants and office spaces. In 2004, City staff thoroughly cleaned the pipe with high pressure water and a bleach concentrate to remove the bacteria, which helped for a short time before the bacteria levels spiked once again. The City is currently conducting a pilot study with their lab to distinguish if the bacterial contamination is coming from human or animal origins. One test result has been positive for human contamination; however the samples continually reveal bacterial levels higher than water quality objectives for the storm drain. The City is committed to resolving this problem and will continue to track the source of the bacteria. Educational campaigns are in place for the neighboring residential complexes and upstream businesses are inspected. Storm drain lines are televised to investigate the existence of illicit connections or illegal discharges. Del Mar The City of Del Mar did not conduct any investigations during the reporting period. San Diego The City of San Diego did not conduct any investigations during the reporting period. Section 4 – Discussion 70 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report Port Location EH-070 Original Sample Date 3/8/05 Original Sample Results: E = 24,196 MPN/100mL Investigation Date 4/5/05 Investigation Results: We were not able to access this storm drain to resample due to the challenge of low tides. By the time we resampled the storm drain on the next round of monitoring on 4/5, there were no exceedances and the investigation was closed and attributed to a transient flow. Location EH-205 Original Sample Date 8/9/05 Original Sample Results: TC = 900,000 MPN/100mL, FC = 80,000 MPN/100mL, E = 98,039 MPN/100mL Investigation Date N/A Investigation Results: This storm drain was flowing due to runoff from sprinklers in the neighborhood behind the beach. The runoff was flowing from City of San Diego property, and therefore the City was notified because the problem originated outside of the Port’s jurisdiction. Location EH-205 Original Sample Date 9/6/05 Original Sample Results: TC = 500,000 MPN/100mL, FC = 30,000 MPN/100mL, E = 120,33 MPN/100mL Investigation Date N/A Investigation Results: This storm drain was flowing again due to the sprinkler runoff, and the City of San Diego was notified. Section 4 – Discussion 71 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report SECTION 5 - CONCLUSIONS 5.0 Conclusions The CSDM Copermittees made notable progress on the program goals identified in Section 1. Overall, the CSDM program was effective in evaluating urban runoff impacts on coastal beaches and lagoons. The CSDM Copermittees have successfully completed the 2004-2005 monitoring requirements, and have demonstrated compliance with the requirements identified in Attachment B, Section II.C of the Municipal Stormwater Permit. 5.1 Program Achievements The sampling efforts occurring during the reporting period were effective at evaluating the impacts of storm drains on the recreational beneficial uses in coastal and lagoon receiving waters. Only 4 samples of the paired sample results (<1%) showed both a storm drain action level exceedance and a receiving water exceedance at coastal locations. Similarly, only 1 of 128 paired lagoon samples (<1.0%) exceeded criteria for lagoon receiving water and storm drains. Furthermore, the sampling data also enabled CSDM Copermittees to assess whether bacteriological water quality is improving over time and/or assess seasonal trends. The data collected during the last three reporting periods indicates that conditions have been quite consistent. There has been little variation of any of the indicator exceedances over the last three reporting periods. Similarly, while there has not been a demonstrated decrease in bacteria levels from the 2002-2003 and 2003-2004 programs, overall bacteria levels at the majority of the sites are currently below action levels. Approximately 75% of all the coastal locations had zero exceedances in the receiving water. Seasonal variations show both the storm drains and receiving waters tend to have more exceedances in the summer months. This may be a result of increased sampling frequency in the summer or possibly a result of the storm drain flushing that occurs with every rain event in the winter. Additionally, the receiving water had more winter exceedances than the storm drains. Other trends of note were that total coliform dominated the storm drain exceedances, while Enterococcus dominated the receiving water exceedances. Based on the analyses performed on the paired sample data collected in the lagoons during this reporting period, it does not appear that receiving water exceedances occur regularly in Agua Hedionda, San Elijo, Batiquitos, or Los Penasquitos Lagoons. Furthermore, it appears that the storm drains, which are relatively low in bacteria, do not have a negative impact on associated Section 5 – Conclusions 72 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report bacteria concentrations in those lagoon receiving waters. In further support of this finding, in paired samples where receiving water exceedances are present, seldom (<1.0%) are these exceedances accompanied by exceedances of storm drain 95% action levels. In Buena Vista Lagoon, which is freshwater and is not open to tidal flushing, the receiving water exceedances are often accompanied by storm drain exceedances indicating that there may be a relationship between the storm drain exceedance and receiving water exceedances. However, paired sampling data was only collected from a single location in Buena Vista Lagoon, therefore conclusions about overall water quality of the lagoon can not be made. The CSDM Copermittees continued using the coastal water quality database and improving consistency in program design and reporting. Meetings were scheduled regularly, providing a means for information transfer and ensuring improved participation and agreement on all of the workgroup deliverables. The upper end of the reporting range for total coliform provided a better assessment of storm drain data and allowed Copermittees to see the makings of a downward trend for total coliform (in storm drains). Use of standardized data submittals continued and greatly facilitated data assessments. The CSDM Copermittees also increased efforts to use GIS capabilities to map and display information from sampling efforts. The efforts to integrate GIS and the data transfer templates will continue into the next reporting period. Finally, during this reporting year, a significant portion of the CSDM Copermittees’ efforts were directed toward preparing a program assessment for the Report of Waste Discharge (ROWD), which was submitted to the RWQCB in August 2005. The assessment evaluated the CSDM program and identified ways for improvement. The recommendations from the ROWD assessment are consistent with the findings from this year’s data, and as such, are identified in the recommendations below. 5.2 Program Recommendations Based on the efforts of the CSDM Copermittees during 2004-2005, the following recommendations have been identified. These recommendations are consistent with the recommendations submitted with the ROWD to improve the CSDM Program during the next Permit cycle. It is believed that incorporating these recommendations into future monitoring will provide a more enhanced understanding of bacteria issues within the San Diego region. 1. Reduce the sampling frequency to monthly at all sites Supporting Evidence The CSDM Program results have shown that dry weather flows from storm drains tend to be intermittent and often do not impact the recreational Section 5 – Conclusions 73 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report beneficial uses of the coastal receiving waters. As supported by paired sample bacteria data presented in the Adaptive Diagrams, very few paired samples (four at coastal locations and only one in the lagoons) show both a receiving water and storm drain action level exceedance. It is widely accepted that sources other than urban runoff may impact receiving water quality (Mission Bay Bacterial Source Identification Study, 2005). While the CSDM Copermittees agree that monitoring is necessary at all the CSDM Program locations, it is recommended, and supported by over three years of monitoring data, that monthly sampling of both coastal and lagoon sites, during both the dry and wet seasons would adequately meet Permit requirements and the CSDM Program objectives. 2. Define the monitoring season to span from Oct 1st through September 30th. The dry season would begin May 1st and continue through September 30th while the wet season would start October 1st through April 30th. Supporting Evidence The Permit requires that the monitoring season starts on October 1 and ends Sept 30. It is recommended that the CSDM sampling and reporting period begin and end in accordance with this timeframe. As such, the wet weather season would begin on October 1 and end on April 30, while the dry weather season would occur May 1 through September 30. Storm drain action levels will continue to be reassessed annually and the new action levels would start on October 1 of each year. 3. Continue to standardize data. Supporting Evidence The CSDM Copermittees will continue efforts to standardize data. Additionally, efforts to use GIS to assess and plot CSDM data will be increased over the next reporting period. It is expected that these efforts will continue into the future. 4. Continue to collect and analyze visual observations data to provide a full data record and determine the most effective way to use and/or interpret this information. Supporting Evidence The analysis of visual data has not yet shown significant links between exceedance rates and the presence of visual triggers. However, collection of these data provide a compete record which will prove useful should environmental conditions at sampling sites change. Section 5 – Conclusions 74 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report 5. Align TMDL implementation plans with permit sampling. Supporting Evidence As more data continues to be collected for bacteria, both in receiving waters and storm drains, and as receiving waters are being placed on the CWA Section 303(d) List for bacteria impairments, the need for aligning Permit required sampling with TMDL implementation plans becomes critical. Many sites in the coastal monitoring program are also identified on the 303(d) List, creating the potential for duplicative monitoring to occur at these sites. The CSDM Copermittees recommend that the RWQCB take into account the bacteria TMDL efforts that are occurring in the region and utilize cost effective monitoring strategies that can meet both Permit and TMDL compliance objectives. The development of an appropriate monitoring program best addressing both Permit and TMDL objectives is beneficial and an effective approach to allocating resources. Therefore, it is recommended that RWQCB allow the Copermittees flexibility to work together with both Stormwater and TMDL staff to develop and/or modify the Coastal Monitoring Program to create such a monitoring strategy once TMDLs are approved at the state and/or EPA level. Section 5 – Conclusions 75 Attachment A Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report SECTION 6 - REFERENCES Cabelli, V.J. (1983) “Health Effects Criteria for Marine Recreational Waters.” USEPA Office of Research and Development. EPA-600/1-80-031. California Regional Water Quality Control Board, San Diego Region. “Water Quality Control Plan for the San Diego Basin (9)”. September 8, 1994 California Regional Water Quality Control Board, San Diego Region (RWQCB). 2001. Order No.2001-01. California State Water Resources Control Board (CSWRCB). 2003. 2002 CWA Section 303(d) List of Water Quality Limited Segments. California State Assembly Bill 411 – Title 17 of the California Code of Federal Regulations, Section 7958. Dufour, A.P. (1984) “Health Effects Criteria for Fresh Recreational Waters.” UPEPA Office of Research and Development. EPA-600/1-84-004. MEC Analytical Systems, Inc. 2003. San Diego County Municipal Copermittees 2002-2003 Urban Runoff Monitoring Report. Prepared for the County of San Diego. January, 2004. MEC Analytical Systems, Inc. 2004. San Diego County Municipal Copermittees 2003-2004 Urban Runoff Monitoring Report, Draft Report. Prepared for the County of San Diego. November, 2004. USEPA (1986) “Ambient Water Quality Criteria for Bacteria – 1986.” Office of Water. EPA440/5-84-002. Zar, J.H. (1974) “Biostatistical Analysis.” Prentice-Hall, Inc. Englewood Cliffs, N.J. 620pp San Diego County Municipal Copermittees, 2001b. San Diego Stormwater Copermittees. Coastal Storm Drain Outfall Monitoring Program, October 19, 2001. Revisions to August 20, 2001 Submittal. San Diego County Municipal Copermittees, 2001b. San Diego Stormwater Copermittees.Coastal Storm Drain Outfall Monitoring Program, Adaptive Monitoring Program, March 20, 2003. Section 6 – References 76 APPENDIX A Adaptive Monitoring Proposal Due to the number of pages in this document, this information is submitted electronically only. Please refer to the enclosed CD for the electronic version of Attachment A: Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report. CSDM Adaptive Program (3/20/03) 1 San Diego County Stormwater Copermittees Coastal Storm Drain Monitoring Program Adaptive Monitoring Proposal March 20, 2003 1.0 CURRENT PROGRAM The Copermittees initiated the Coastal Storm Drain Monitoring Program in November 2001. The current program design is a prescriptive approach that is based on elements of the AB 411 Recreational Water Monitoring Program and involves the collection of paired samples at flowing storm drain outlets and in the corresponding coastal or lagoon receiving water. Coastal receiving water samples are collected 25 yards downcurrent of the mixing zone, while lagoon samples are collected immediately in front of the storm drain outlet. Samples are collected monthly during the non-AB 411 period (November 1 – March 31), and every other week during the AB 411 period (April 1 – October 31), and are analyzed for total and fecal coliform, and enterococcus indicators (San Diego County Municipal Copermittees, 2001). Lagoons were incorporated into the program beginning November 2002. The Revised Sampling Plan (San Diego County Municipal Copermittees, 2001b) states that, after one year of data collection the Copermittees will: ‘…. review the complete database to determine the appropriateness and applicability of an Adaptive Shoreline Monitoring matrix or any other available tools. Recommendations may include modifications to monitoring frequencies and locations in subsequent years.’ The Coastal Storm Drain Monitoring Workgroup began development of an adaptive strategy for the Coastal Storm Drain Monitoring Program in August 2002. The Workgroup decided not to follow the adaptive models developed by the State Water Resources Control Board or the USEPA. These guidance documents are designed to address recreational waters alone and do not necessarily accommodate paired sampling designs. The Workgroup discussed various adaptive approaches, conducted a comprehensive analysis of the paired sampling data collected from November 2001 to October 2002, and developed procedures to guide the implementation of an adaptive strategy. 2.0 COASTAL STORM DRAIN MONITORING RESULTS (NOV 2001 – OCT 2002) The complete results of the data analysis are included in the San Diego Municipal Copermittees 2001 – 2002 Urban Runoff Monitoring Final Report, Attachment A, submitted to the San Diego RWQCB on January 31, 2003. The analysis included the development of a Coastal Storm Drain Monitoring database, plotting the data distributions for the 332 paired samples, identifying the samples that exceeded the receiving water AB 411 standards, calculating statistical values for the receiving water and storm drain data sets, and regression analyses. The total and fecal coliform, and enterococcus bacterial indicators exceeded AB 411 standards 3, 5, and 15 times, respectively (23 total exceedances in 15 samples) (Table 1). This corresponds to overall exceedance rates of 0.9%, 1.5%, and 4.6% for the respective indicators. The higher rate of enterococci exceedance may be related to its ability to survive for comparatively longer periods in marine environments. CSDM Adaptive Program (3/20/03) 2 Table 1: Summary of Samples Exceeding AB 411 Receiving Water Standards (Nov 01 – Oct 02) # of Paired Samples Collected AB 411 Exceedances Site ID Location Name Wet Dry Total % of Sampling Attempts With Flowing Storm Drain Storm Drain Flows To Ocean During Sampling? TC FC Ent Oceanside Hayes 1 0 1 5 no 0 0 0 Oceanside Blvd 1 1 2 10 no 0 0 0 EH-490 Wisconsin 0 1 1 5 no 0 0 0 OC-090 Surfrider 0 1 1 5 no 0 0 0 Carlsbad EH-470 Pine Ave 0 8 8 40 no 0 0 0 #2 Ocean St. 1 0 1 5 no 0 0 0 #3 Cypress Street 2 0 2 10 no 0 0 0 #5 Christiansen PBA 2 0 2 10 no 0 0 0 EH-475 Carlsbad Village Dr 1 2 3 15 no 0 0 0 Encinitas EH-403 North San Elijo SB 5 15 20 100 usually 0 0 0 EH-405 Swami's mid beach 5 15 20 100 yes 0 0 0 EH-410 Swami's Beach 5 15 20 100 yes 0 0 0 EH-420 Cottonwood Creek 5 15 20 100 yes 0 0 0 Solana Beach EH-390 Seascape Beach Park 5 12 17 85 no 0 0 0 SE-010 Fletcher Cove 5 10 15 75 sometimes 0 0 0 Del Mar EH-355 12th Street 4 15 19 95 yes 0 0 0 EH-360 15th Street 5 15 20 100 rarely 0 0 0 EH-370 17th Street 5 15 20 100 no 0 0 0 San Diego EH-250 Grand Ave 5 15 20 100 usually 0 0 0 FM-030 Tourmaline 4 4 8 40 sometimes 0 0 0 EH-255 PB Point 5 15 20 100 yes 1 1 4 EH-280 Playa Del Norte 5 15 20 100 yes 0 0 0 FM-050 Bonair 1 2 3 15 usually 0 0 0 EH-300 Ravina/ Horseshoes 2 9 11 55 yes 0 0 0 FM-060 Coast Blvd. 1 9 10 50 usually 0 0 0 EH-340 El Paseo Grande 3 8 11 55 sometimes 0 0 0 FM-080 Avenida De La Playa 0 1 1 5 yes 0 0 0 San Diego Unified Port District EH-070 Tidelands (bayside) 1 2 3 15 no 0 0 1 EH-120 Bayside Park (J St.) 4 6 10 50 at low tide 1 2 3 EH-160 Spanish Landing 1 3 4 20 sometimes 0 0 1 EH-200 Shelter Island 5 5 10 50 yes 1 2 4 EH-205 Bessemer Street 0 2 2 10 no 0 0 1 EH-210 Kellogg Street 5 2 7 35 usually 0 0 1 TOTALS: 33 Sites 94 238 332 50.3% 3 5 15 CSDM Adaptive Program (3/20/03) 3 Approximately 37% of the storm drain samples had total coliform levels above the 10,000 MPN/ 100 mls receiving water standard. Similarly, approximately 35% and 62% of the storm drain samples exceeded the fecal coliform and enterococcus AB 411 standards, respectively. Dilution, filtration, and natural UV disinfection between the storm drain outlet and the receiving water sampling location contributed to the low number of AB 411 violations during the period of record. One of the key findings of the data analysis was that storm drains that did not discharge directly to the receiving water (soaked into beach or ponded) typically had much higher bacteria levels than conveyances that flowed across the beach and directly into the ocean. Not surprisingly, storm drains that did not reach the receiving water had comparatively lower discharge rates than storm drains that conveyed runoff directly to the receiving water. The apparent difference in storm drain bacteria levels may be related to one or more characteristics of these two categories of storm drains. Low-flow storm drains may be characterized by a lack of flushing and dilution of bacterial contaminants, stagnation of runoff in the drain pipes due to ponding behind debris blockages, and the relative predominance of urban runoff over ground water discharge. Conversely, storm drain discharges that reach the receiving water typically originate from drains that are less stagnant than low-flow conveyances. The 2001 – 2002 data also demonstrated that although storm drain flows that did not reach the ocean had comparatively higher bacteria levels, they were rarely associated with elevated concentrations in the receiving water. Several factors may contribute to the apparent absence of negative impacts of the low-flow storm drains. 1. Effective bacteria filtration of the storm drain discharge by beach sand and other substrate before it reaches the receiving water. 2. Bacteria mortality caused by exposure to UV radiation after the flow emerges from the drain outlet. 3. Comparatively low bacterial loadings from high concentration, low flow storm drains. 4. Dilution of storm drain discharges between the mixing zone and the site of receiving water sample collection (usually 25 downcurrent of the storm drain). Elevated receiving water results that were paired with a low-flow storm drain sample were at least partially attributable to sources within the receiving water itself. For example, bird populations, which are significant natural sources of bacteria, were often observed in the vicinity of the receiving water sampling locations. A regression analysis was performed on the log-transformed data to assess the relationship between the storm drain (independent variable) and receiving water (dependent variable) concentrations. The relationship between the two variables was statistically significant for all three indicators when the storm drain flow reached the receiving water and was essentially non- existent when the storm drain did not discharge directly to the receiving water. This supported the conclusion that storm drain flows that do not reach the receiving water do not negatively impact the receiving water, regardless of their bacteria concentrations. In summary, there is very little evidence linking high bacteria levels in storm drains that do not discharge directly to the receiving water and elevated bacteria in the corresponding receiving water sample. The adaptive program incorporates into its design the observation that storm drains that do not discharge directly to the receiving water pose a minimal threat to receiving CSDM Adaptive Program (3/20/03) 4 water quality. Conversely, storm drains that discharge directly to the receiving water have a greater potential to cause or contribute to elevated bacteria levels in the receiving water although this effect is moderated by the generally lower bacteria levels in these discharges. CSDM Adaptive Program (3/20/03) 5 3.0 ADAPTIVE MONITORING PROGRAM The proposed adaptive program will pursue the following objectives: 1. Evaluate the impacts of ocean and lagoon storm drains on the recreational beneficial uses in coastal receiving waters 2. Identify and eliminate sources of highly elevated bacteria from coastal storm drains In addition, the trend assessment and database development program objectives identified in the original Coastal Storm Drain Monitoring Program will continue to be pursued. 3.1 Program Design The adaptive strategy is designed to address the storm drains that pose the greatest threat to recreational receiving waters most aggressively, while allocating a lower monitoring intensity to locations that exhibit consistently low bacterial levels. Thus, the adaptive strategy is intended to make efficient use of Copermittee resources by identifying and addressing high priority storm drains first and reducing sampling intensity at low priority paired sampling locations. The Copermittees will perform follow up procedures and management actions depending on the results of the paired samples. Existing water quality criteria and other action levels developed by the Coastal Storm Drain Monitoring Workgroup will be used to trigger these sets of follow up procedures and actions. Contaminated storm drain discharges with sufficient flow to reach the receiving water will be assigned the highest priority for additional investigation and source elimination. Established water quality objectives that can be employed as exceedance criteria are available for the ocean and lagoon receiving waters of coastal San Diego County. Established water quality criteria applicable to storm drain discharges are not available and have been developed as outlined below. Two other criteria were developed based on an analysis of the November 2001 – October 2002 paired sampling data: 1) action levels for each bacterial indicator that trigger storm drain investigations in the absence of a receiving water exceedance and, 2) a criteria that allows for a reduction in sampling frequency when bacteria results are consistently low. The development of these criteria are described in Section 3.1.2 and Section 3.1.3, respectively. 3.1.1 Receiving Water Exceedance Criteria The ocean receiving water exceedance criteria are the AB 411 standards established for the protection of public health. The lagoon criteria are established in the San Diego Basin Plan (1994). Coastal Lagoon Total Coliform (MPN/ 100 mls) 10,000 10,000 Fecal Coliform (MPN/ 100 mls) 400 400 (for REC-1areas) Enterococcus (MPN/ 100 mls) 104 104 (designated beach); 276 (light-mod. used area); 500 (infrequently used area) Each of the currently monitored coastal lagoons is designated with the REC-1 beneficial use; however the actual contact recreational activity within these lagoons varies considerably with location. Copermittees that are conducting coastal storm drain monitoring in lagoons will assess beach usage at each of the lagoon paired sampling locations to determine which of the CSDM Adaptive Program (3/20/03) 6 three enterococci standards are applicable. Most of the lagoon areas monitored by the Copermittees are in infrequently used areas and will probably be subject to the 500 MPN/ 1000 mls standard. Selected lagoon areas may be categorized as designated beach and will be subject to the most stringent of the three enterococci criteria (104 MPN/ 100 mls). 3.1.2 Storm Drain Exceedance Criteria Two separate sets of storm drain criteria or action levels were developed. These criteria are applied in the following circumstances: 1. When a receiving water bacteria concentration exceeds AB 411 or Basin Plan criteria given in Section 3.1.1, the storm drain criteria is identical to the receiving water criteria. This represents a conservative approach because it ignores the potential dilution of storm drain discharges as they mix with the receiving water however; this approach will provide assurance that storm drains that may have caused or contributed to a receiving water exceedance will be investigated. 2. When the receiving water does not exceed AB 411 or Basin Plan guidelines a different set of storm drain criteria are applied. The vast majority of the receiving water samples did not exceed the ocean AB 411 standards during 2001 – 2002. This included numerous receiving water samples that were paired with highly elevated storm drain samples. Despite the generally low threat to the receiving water posed by many high-bacteria storm drains, the Coastal Storm Drain Monitoring Workgroup agreed that a certain percentage of the high- bacteria drains should be investigated. Accordingly, the Workgroup established action levels for further storm drain investigation when highly elevated storm drain results are paired with compliant receiving water samples. There are several reasons for pursuing these highly contaminated drains, including the likelihood that they are sources of bacterial pollution during storms when the contents of the storm drain are flushed into the receiving water, the potential health effects of these discharges if they become ponded in accessible coastal areas, and the possibility that ongoing sources of pollution can be eliminated from coastal sub-watersheds by investigating these conveyances. The exceedance criteria for storm drains that are not paired with a receiving water sample that exceeded the AB 411 or Basin Plan criteria are based on the 95th -percentile observations of the 2001 – 2002 total and fecal coliform, and enterococcus data. Storm drains that are not paired with a receiving water exceedance but exceed any of the following three 95th-percentile action levels are subject to additional investigation. Indicator 95th-Percentile Storm Drain Criteria Total Coliform 160,000 MPN/ 100 mls Fecal Coliform 24,000 MPN/ 100 mls Enterococcus 20,000 MPN/ 100 mls Over time, addressing these highly contaminated storm drains will allow the Copermittees to identify and eliminate significant bacterial sources. As sources are eliminated, the 95th- percentile concentrations will decrease (the 95th-percentile concentration will be re- calculated on an annual basis) and the Copermittees will be tasked with investigating less and less contaminated storm drains. 3.1.3 Sampling Frequency CSDM Adaptive Program (3/20/03) 7 Paired sampling at all identified locations will typically be initiated at the base frequency. The base frequency is identical to the sampling frequency implemented in the current Coastal Storm Drain Monitoring Program. Time Period Base Frequency Nov 1 – March 31 once per month April 1 – Oct 31 once every two weeks An important characteristic of the adaptive sampling approach is an allowance for reduced sampling at locations with consistently low bacteria levels. Two factors will be assessed to determine locations where reduced sampling is appropriate: 1) a comparison of the analytical results of the three most recent paired sampling events to the sampling reduction criteria described below and, 2) a simple analysis of the previous one year (April – March) of paired sampling data. Storm drains whose samples satisfactorily meet these requirements can be collected at ½ the base frequency (once every four weeks in the summer, once every two months in the winter) as long as they continue to meet these requirements. Sampling Frequency Reduction Criteria As storm drain flows enter receiving waters, the discharge is quickly diluted by diffusion and wave action between the mixing zone and the sampling point 25 yards downcurrent. The method used to determine the Sampling Frequency Reduction Criteria (SFRC) involved calculating the storm drain-to-receiving water dilution factor using the slope of the regression line for each indicator’s 2001-2002 data set. The slope of the paired sampling data regression line is an approximation of the dilution that occurs on a regional basis. A safety factor of 10:1 was applied to the calculated dilution factors to account for the possibility of lesser dilution rates between the storm drain and receiving water sampling points than is indicated by the slope of the regression line. The numerical storm drain criteria for reducing the base sampling frequency are provided in Table 2. Table 2: Sampling Frequency Reduction Criteria Indicator Receiving Water Standard (MPN/ 100 mls) Slope of Regression Line Reduction Standard Without Safety Factor (MPN/ 100 mls) Slope/Safety Factor Sampling Frequency Reduction Criteria (MPN/ 100 mls) TC 10,000 42 420,000 10:1 42,000 FC 400 18 7,200 10:1 720 Entero 104 165 17,160 10:1 1,716 Annual Data AssessmentPrior to April 1 of each sampling year, each municipality is required to review the previous year’s data to assess the eligibility of their locations for sampling frequency reduction. If > 20% of a location’s storm drain samples were above any of the three Sampling Frequency Reduction Criteria during the previous year then that location is not eligible for a lower sampling frequency until the following year. For example, if there were 15 samples collected at a paired sampling site during the April 2002 – March 2003 period, then no more than three of the 15 storm drain samples may exceed any of the three Sampling Frequency Reduction Criteria provided in Table 2. If > 20% of the samples have at least one exceedance of an SFRC then sampling must be conducted at the base frequency during the entire sampling year. CSDM Adaptive Program (3/20/03) 8 The results of this annual assessment of April 1, 2002 – March 31, 2003 storm drain data will be a list of paired sampling locations that are eligible for sampling frequency reduction during that April – March sampling year. Each jurisdiction will provide that information to the chair of the Coastal Storm Drain Monitoring Workgroup who will subsequently provide that list of eligible locations to the RWQCB prior to the beginning of the sampling year. At all storm drains that are determined eligible for sampling frequency reduction, a minimum of three consecutive storm drain samples with bacteria levels below the Sampling Frequency Reduction Criteria (Table 2) for each bacterial indicator are required to reduce sampling to one- half base frequency. The three consecutive samples must be paired with receiving water samples that do not exceed AB 411 or Basin Plan standards unless the receiving water exceedance can be reasonably attributed to a non-storm drain source or sources. Samples collected immediately prior to the implementation of the program can be applied toward reducing sampling frequency. For example, if the Adaptive Program is implemented beginning April 2003, the January, February, and March 2003 samples may be applied to reducing sampling frequency if the results meet the Sampling Frequency Reduction Criteria in Table 2. Additional Reduction of Sampling Frequency The sampling frequency for storm drains that are confirmed to consistently discharge low bacteria levels may be further reduced to quarterly frequency pending additional supporting information collected by the municipality. This information may include existing or future storm drain source flow studies and detailed comparisons between storm drain and local groundwater bacteria levels. The San Diego RWQCB will evaluate the appropriateness of this additional sampling frequency reduction on a case-by-case basis. The municipality must submit the relevant paired sampling results and corroborating information to the RWQCB prior to April 1 of each sampling year to have that location considered for quarterly sampling during the April – March sampling year. If a location sampled at ½ base frequency or quarterly experiences a receiving water bacteria result above the receiving water standard, and that exceedance cannot be reasonably attributed to a non-storm drain source(s) then the municipality must return to sampling that location at the base frequency. Likewise, if a location sampled at a reduced frequency experiences a storm drain bacteria result above the Sampling Frequency Reduction Criteria, a return to sampling at the base frequency is required. 3.1.4 Adaptive Monitoring Diagrams A series of scatter plots, referred to as adaptive monitoring diagrams, were developed to illustrate the relationships between receiving water and storm drain bacteria levels, AB 411 and Basin Plan regulatory drivers, the storm drain criteria developed by the Coastal Storm Drain Monitoring Workgroup, and potential contamination sources. The adaptive monitoring diagrams stratify the paired sampling data into categories, or Regions, for management purposes and are essential tools in the implementation of the proposed Adaptive Monitoring Program. The diagrams are also extremely useful visual tools for summarizing the results of the 2001 – 2002 paired sampling program. The adaptive monitoring diagrams for total and fecal coliform for both coastal and lagoon sampling are presented in Figures 1 and 2. The adaptive monitoring diagram for enterococcus for coastal and designated beach areas within lagoons is presented in Figure 3. The diagrams CSDM Adaptive Program (3/20/03) 9 for enterococcus in light to moderate and infrequently used lagoon areas are provided in Figures 4 and 5. Each adaptive monitoring diagram is divided into five regions and one subregion that are formed by superimposing a line of slope = 1 (indicative of equal receiving water and storm drain bacteria concentration), two perpendicular lines that delineate the receiving water regulatory standards summarized in Section 3.1.1, and the 95th percentile storm drain criteria outlined in Section 3.1.2. Table 3 describes the regions of the scatter plots as they relate to the applicable bacterial standards and criteria and the required follow up actions. The regions of the adaptive monitoring diagrams are color shaded to indicate the level of risk associated with the storm drain discharge. Green shaded areas (Regions I and II) are associated with the lowest storm drain bacteria concentrations and represent the lowest risk. Paired samples falling within Region II exceed the receiving water standard but are probably dominated by non-storm drain sources. The paired samples within this region are characterized by receiving water results that are higher than the corresponding storm drain results. Very few paired samples collected during 2001 – 2002 fall within Region II. Table 3: Adaptive Monitoring Diagram Regions Region Receiving Water Concentration Storm Drain Concentration Description: I < AB 411 or Basin Plan < AB 411 or Basin Plan Both the storm drain and receiving water are below the receiving water standard. No follow up action necessary. Continue sampling at BF unless Sampling Frequency Reduction Criteria are met. If met, sample at ½ BF. I-A < AB 411 or Basin Plan > AB 411 or Basin Plan and < 95th percentile Storm drain is above the receiving water regulatory standard but the receiving water is below. Storm drain is also below the 95th percentile criteria. No action necessary. Continue sampling at BF unless Sampling Frequency Reduction Criteria are met. If met, sample at ½ BF. II > AB 411 or Basin Plan < AB 411 or Basin Plan Receiving water is above standard but storm drain is below. Unlikely that storm drain contamination caused the receiving water exceedance. Non-storm drain sources are likely present. Resample ASAP to confirm scenario and address potential non-storm drain sources. III > AB 411 or Basin Plan > AB 411 or Basin Plan Both the storm drain and receiving water are above the receiving water standard but RW level is greater than storm drain level. This indicates that storm drain contamination may contribute to exceedance but that non-storm drain sources may predominate. Resample ASAP to confirm scenario and address both storm drain and non-storm drain sources. IV > AB 411 or Basin Plan > AB 411 or Basin Plan Both the storm drain and receiving water are above the receiving water standard. Storm drain appears to be a dominant contributor. Resample ASAP to confirm scenario and conduct IC/ID investigation. V < AB 411 or Basin Plan > AB 411 or Basin Plan and > 95th percentile Receiving water is below the standard however; the storm drain is highly contaminated. Resample and conduct IC/ID investigation. Region I-A is yellow shaded to indicate a moderately high storm drain concentration that is paired with a receiving water sample within regulatory limits. Follow up action is not required in response to paired samples within Region I-A however; the high between-sample variability that characterizes storm drain samples suggests that these storm drains have a reasonable probability of exceeding the 95th percentile criteria at some point. Region III is pink shaded to indicate that both the storm drain and receiving water samples are above receiving water criteria however; Region III lies above the slope = 1 (equal concentration) line indicating that non-storm drain sources likely predominate. Possible sources include birds, CSDM Adaptive Program (3/20/03) 10 other marine wildlife, discharges from watercraft, and ocean bathers. It is important to consider these sources and their potential contribution to observed receiving water bacteria levels to avoid wasted effort when the paired sampling results fall within Regions II or III. Bacteriological analyses of coastal and storm drain water samples are often characterized by high variability, a factor that should be considered when the paired sampling results are within Regions II and III and slightly above the slope = 1 line. In this situation, the bacterial contribution from the storm drain cannot be assumed to be insignificant. Municipal staff must use their Best Professional Judgment to assess the follow up actions that are appropriate to identify and address potential storm drain and non-storm drain sources. This is especially important when the paired sample results fall slightly above the slope = 1 line within Region III. If the storm drain discharges directly to the receiving water a more conservative approach, similar to the procedures followed in Region IV is appropriate. This would involve an immediate resample and follow up investigation of the storm drain. If the flow does not reach the receiving water a storm drain investigation is the proper course of action if the storm drain concentration exceeds the 95th percentile criteria. Region IV is red shaded to indicate that the combination of elevated receiving water and storm drain bacteria levels is most likely a result of storm drain contributions. The extent of the storm drain’s contribution depends largely on whether the storm drain flow reaches the receiving water. This scenario represents the highest priority for follow up action according to the adaptive monitoring approach. The storm drain’s influence is expected to decrease significantly if the discharge does not reach the receiving water. Regardless of the flow conditions, an immediate follow up investigation is warranted to further assess the situation. Region V is pink shaded to delineate that the storm drain concentration is above the 95th percentile criteria. Although the paired receiving water sample is within regulatory limits, the storm drain is discharging highly elevated bacteria levels and must be investigated. In summary, additional sampling and/or investigation is required when the results of paired samples fall within one of three categories: 1. The storm drain sample is below and the receiving water is above the receiving water AB 411 or Basin Plan standard for the indicator in question (Region II). Follow up actions other than prompt resampling, if necessary, are likely to focus on controllable non-storm drain sources (boat discharges, pet waste on beach, etc.). 2. The storm drain and receiving water samples both exceed the receiving water AB 411 or Basin Plan standard for the indicator in question (Regions III and IV). The Region IV scenario is considered the highest priority especially if the storm drain discharge reaches the receiving water. Follow up actions may include resampling, source identification and elimination, and BMP implementation. Follow up actions for the Region III scenario may focus on eliminating both storm drain and controllable non-storm drain sources. 3. The receiving water sample is below the AB 411 or Basin Plan standard and the storm drain sample is above the 95-percentile action level (Region V). Follow up actions may include resampling, source identification and elimination, and BMP implementation. CSDM Adaptive Program (3/20/03) 11 4.0 IMPLEMENTATION The Copermittees will begin implementing the Adaptive Program on April 1, 2003. Samples will continue to be collected and analyzed in accordance with the procedures described in the prescriptive Coastal Storm Drain Monitoring Program (San Diego County Municipal Copermittees, 2001). Paired samples will be collected at frequencies outlined in Section 3.1.3. Upon receipt of the analytical results, staff will promptly refer to the respective adaptive monitoring diagrams for the three bacterial indicators to determine the status of each of the paired samples. Appropriate management actions will be implemented based on the guidelines provided on the adaptive monitoring diagram and the Coastal Storm Drain Adaptive Monitoring Matrix (Table 4). The management strategies in Table 4 are intended to be general instructions in the event that receiving water and /or storm drain results exceed the established criteria. The Coastal Storm Drain Monitoring Workgroup believes that the individual jurisdictions must retain a sufficient degree of flexibility to develop specific follow up approaches to address the situation at hand. The Copermittees are encouraged to employ their Best Professional Judgment and field experience when developing the details of their follow up actions. 4.1 Field Observations The Coastal Storm Drain Monitoring Workgroup has worked closely with the Copermittees’ Dry Weather Monitoring Workgroup to develop consistent guidelines for collecting and recording qualitative and quantitative field observations. These data collection standards are designed to ensure that important measurements and observations are collected during all field visits. Additional required data collection includes bird and bather counts, storm drain flow measurements, and tidal information (Figure 6). Copermittee staff may initiate an investigation based solely on field observations, prior to obtaining analytical results. This approach is similar to investigating a problem observed during dry weather field screening. Field staff does not need the validation of high bacteria results to pursue an immediate source investigation if observations of abnormally high flows, sewage releases, restaurant discharges, excessive foam, or other evidence of potential bacterial contamination or illicit discharge is present. One of the most important field observations recorded during paired sampling and investigative work is whether or not the storm drain discharges directly to the corresponding receiving water. Municipal staff should also be aware of the storm drains within their jurisdiction that flow intermittently and may actually reach the receiving water for short periods of time. Field staff will record any evidence of intermittent flows and act accordingly when conducting follow up investigations. Qualitative observations of debris, trash, flow lines, or local knowledge may be helpful when assessing the threat that a storm drain poses to the receiving water. Certain storm drains may represent a potential health risk to children because of their accessibility and tendency to pond on the beach. Staff will record observations of coastal visitors contacting storm drain discharges and will consider these special circumstances when assessing the urgency of follow up action. Receiving water exceedances and elevated bacteria levels discharging from these storm drains will be considered high priority events and aggressively investigated. CSDM Adaptive Program (3/20/03) 12 4.2 Resampling After Receiving Water Criteria Are Exceeded The first management action to follow any exceedance of the receiving water criteria outlined in Section 3.1.1 is prompt resampling of the paired sampling location. The resample must be collected as soon as possible after the results are received and must not be delayed until the next regularly scheduled sampling event. The Coastal Storm Drain Monitoring Workgroup believes that the follow up confirmation sample is very important tool to assess whether the initial contamination is a transient event or a chronic condition. A repeatable exceedance suggests that the problem should be considered a high priority and addressed immediately and aggressively. The experience of Workgroup members with IC/ID investigations has shown that unless the contamination is either followed upstream immediately or confirmed by resampling, there is little chance of identifying sources. Investigating these transient discharges often leads to wasted effort that could be better used elsewhere. Nevertheless, a certain amount of judgment must be employed when interpreting the resampling results. For example, if a regularly scheduled sample exceeds the receiving water criteria and the corresponding resample is within limits, it is reasonable to attribute the initial receiving water exceedance to a transient occurrence. However, if this pattern repeats then a more detailed follow up investigation is warranted to address an intermittent discharge of bacteria from the storm drain in question. 4.3 Exceedance of 95th Percentile Storm Drain Criteria Some storm drains may regularly exceed the 95th percentile storm drain criteria (Region V), despite ongoing efforts to identify and eliminate causative bacterial sources. If a chronically contaminated storm drain is already under investigation it is not necessary to immediately resample the storm drain if a high result occurs. The fact that the IC/ID investigation is underway and moving ahead is sufficient to demonstrate progress and action. In contrast, receiving water exceedances should always be resampled in a timely manner. These chronically contaminated storm drains may be addressed using a range of investigative tools as determined by the jurisdiction until the source(s) of contamination is identified. The methods of eliminating identified discharges or the appropriateness of eliminating such discharges will be left to the discretion of the jurisdiction involved. 4.4 Program Evaluation The Coastal Storm Drain Monitoring Workgroup will re-evaluate the Adaptive Coastal Storm Drain Monitoring Program on an ongoing basis. At a minimum, the following issues will be reviewed: 1. Changes in regulatory requirements and applicable water quality criteria for bacterial indicators. 2. Sharing of successful source identification techniques and procedures. 3. Results of other relevant bacteriological studies in local waters. The Workgroup may also discuss necessary changes and clarifications to the program. The Copermittees will also recalculate the Sampling Frequency Reduction Criteria and 95th Percentile Storm Drain Criteria on an annual basis. These calculations should be based on the most recently tabulated year of paired sampling data. CSDM Adaptive Program (3/20/03) 13 5.0 REFERENCES San Diego County Municipal Copermittees, 2003. San Diego County Municipal Copermittees 2001 – 2002 Urban Runoff Monitoring Report, Final Report, Attachment A, January 31, 2003. San Diego County Municipal Copermittees, 2001. San Diego Region: Previous Monitoring and Future Recommendations, Final Report, August 20, 2001. San Diego County Municipal Copermittees, 2001b. San Diego Stormwater Copermittees Coastal Storm Drain Outfall Monitoring Program, October 19, 2001. Revisions to August 20, 2001 Submittal. Water Quality Control Plan for the San Diego Region (9), 1994. California Regional Water Quality Control Board, San Diego Region. APPENDIX B 2004-2005 Coastal Storm Drain Monitoring Locations CSDM Coastal Monitoring Station Information Lat Long Type Construction Dimensions Coast 1 Marina Inn 33.20955 117.39703 outlet pipe concrete 18" Coast 2 Camp Pendleton Outfall 33.21303 117.39474 outlet pipe concrete 2 x 48" Coast 3 Harbor Administration 33.20977 117.39463 outlet pipe concrete 18" Coast 4 Monterey Bay Canners 33.20645 117.39185 outlet pipe concrete 18" Coast 5 Joe's Crab Shack 33.20559 117.38927 outlet pipe concrete 24" Coast 6 Harbor Fish&Chips 33.20514 117.38941 outlet pipe concrete 36" Coast 7 Outfall West of Retail Spaces 33.20486 117.38985 outlet pipe concrete 36" Coast 8 Harbor Boat Wash Outfall 33.20555 117.39331 outlet pipe concrete 36" Coast 9 Surfrider Street 33.19686 117.38658 outlet pipe concrete 36" Coast 10 Civic Center Drive 33.19504 117.38502 outlet pipe concrete 18" Coast 11 Pier Outfall 33.19444 117.38453 outlet pipe concrete 12" Coast 12 Seagaze Drive 33.19228 117.38255 outlet pipe metal 18" Coast 13 Tyson Street 33.19073 117.38123 outlet pipe concrete 18" Coast 14 Wisconsin Street 33.18591 117.37716 outlet pipe concrete 38" Coast 15 Hayes Street 33.18491 117.37608 outlet pipe metal/conc. 24" Coast 16 Forster Street 33.18257 117.37410 outlet pipe concrete 18" Coast 21 Oceanside Blvd 33.18139 117.37325 outlet pipe concrete 48" Coast 17 Cassidy Street 33.17315 117.36575 outlet pipe plastic 18" Coast 18 St. Malo North 33.16809 117.36158 outlet pipe metal/conc. 18" Coast 19 St. Malo South 33.36152 117.36152 outlet pipe metal/conc. 18" Carlsbad EH-470 Pine Ave 33.15509 117.35123 outlet pipe concrete 20" EH-477 Cypress Street 33.16154 117.35659 outlet pipe metal 17.5" EH-479 Ocean St 33.16352 117.35791 outlet box concrete 10 x 26.5" OC-007 Carlsbad Village Dr 33.15720 117.35283 outlet pipes (2) concrete 2 @ 6.5" OC-002 Christiansen PBA 33.15882 117.35427 outlet pipe concrete 18" OC-005 Tamarack PBA 33.08741 117.20671 outlet pipe concrete 48" Encinitas EH-403 N San Elijo CG 33.02808 117.28828 outlet pipe metal 12" EH-405 Swami's Mid 33.03112 117.28985 outlet pipe metal 8" EH-410 Swami's 33.03482 117.29291 outlet pipe plastic 4" EH-420 Cottonwood Creek 33.04838 117.29827 outlet pipes (3) metal/conc. 3 @ 72" EH-390 Seascape Beach Park 32.98554 117.27333 outlet pipe metal 24" S-02 End of 8th Street (cliffside) 32.95152 117.26608 open channel concrete 48" S-03 End of Sea Orbit Lane 32.95580 117.26743 twin outlet pipes concrete 2 @ 36" S-04 End of 12th Street 32.95514 117.26735 open channel concrete 48" S-05 Between 13th & 15th St (cliffside) 32.95783 117.26767 outlet pipe concrete 24" S-06 Powerhouse Park (Cliffside) 32.96250 117.26824 outlet pipe concrete 32" S-07 17th St 32.96250 117.26829 open channel concrete 36" S-12 Anderson Canyon 32.94252 117.26258 culvert concrete 48" Oceanside Solana Beach Del Mar Site ID Location Name Coordinates Conveyance Information CSDM Coastal Monitoring Station Information Lat Long Type Construction DimensionsSite ID Location Name Coordinates Conveyance Information EH-250 Grand Ave 32.79449 117.25624 outlet pipe concrete 24" EH-255 PB Point 32.80810 117.26534 outlet pipe concrete 4' EH-280 Playa Del Norte 32.82939 117.28062 outlet pipe concrete 26" EH-290 Vista De La Playa 32.83430 117.28150 outlet pipe concrete 36" EH-300 Ravina/ Horseshoes 32.83934 117.28179 outlet pipe concrete 64" EH-320 Vallecitos 32.85560 117.25820 outlet box concrete 24" x 48" EH-330 Camino Del Oro 32.85910 117.25600 outlet pipe concrete 18" EH-340 El Paseo Grande 32.86291 117.25492 outlet pipe concrete 46" FM-030 Tourmaline 32.80544 117.26243 open channel concrete 15.5' FM-050 Bonair 32.82994 117.28082 outlet pipe concrete 46" FM-060 Coast Blvd. 32.84099 117.28162 outlet box concrete 36" x 36" FM-080 Avenida De La Playa 32.85470 117.25905 outlet box concrete 96" x 48" EH-070 Tidelands (bayside) 32.69047 117.16454 outlet pipe concrete 18" EH-120 Bayside Park (J St.) 32.62959 117.10858 outlet pipe concrete 36" EH-160 Spanish Landing 32.72826 117.21144 outlet pipe concrete 24" EH-200 Shelter Island 32.71477 117.22430 outlet pipe concrete 18" EH-205 Bessemer Street 32.71803 117.23344 outlet pipe concrete 20" EH-210 Kellogg Street 32.70923 117.23678 outlet pipe concrete 20" San Diego San Diego Unified Port District CSDM Lagoon Monitoring Station Information Site ID Location Name Coordinates Conveyance Information Lat Long Type Construction Dimensions Oceanside Coast 20-1 Buena Vista #1 33.18063 117.34251 outlet pipe concrete 48" Coast 20-2 Buena Vista #2 33.18058 117.34250 outlet pipe metal 12" Coast 20-3 Buena Vista Lagoon Outfall Mixing Zone 33.18046 117.34246 open water n/a open Carlsbad BV-002 SE State St & Carlsbad Bl 33.09940 117.21246 outlet pipe concrete 48" BV-010 N of jefferson St, Inside Buena Vista Ecological Reserve 33.10743 117.20454 outlet pipe metal 18" AH-006 S of Aguila St, E of RR tracks, N of Agua Hedionda Lagoon 33.08761 117.20285 outlet pipe concrete 6' AH-011 S end of Hoover St, 30' W of the cul-de-sac 33.08842 117.19848 outlet pipe metal 17" AH-017 S end of Bayshore Dr 33.08555 117.19264 manhole cement 36" AH-019A E of 4607 Park Dr outfall on N side of Agua Hedionda Lagoon 33.08785 117.19460 outlet pipe concrete 20" AH-020 S of Park Dr , E of Valencia Av 33.08584 117.18937 outlet pipe concrete 42" AH-022 S of Kelly Dr and Park Dr 33.08781 117.18640 outlet boxes concrete 6' x 12' AH-023 10' W of cannon Rd and Legoland Dr, N of Cannon Rd 33.08101 117.19064 outlet pipe concrete 17.5" AH-025 Encina Power Stn 100' E of plant tower 33.08267 117.20104 outlet pipe concrete 6' BA-001 N of La Costa Av 100' W of El Camino Real 33.05127 117.16171 outlet boxes concrete 4 - 10' x 12' BA-008 E Pipe N of La Costa Av 100' E of Saxony Rd 33.05242 117.17116 manhole concrete 36" BA-009 W Pipe N of La Costa Av 100' E of Saxony Rd 33.05242 117.17117 manhole concrete 36" BA-014 N of La Costa Av 300' E of I-5 Freeway 33.05134 117.17710 manhole concrete 24" BA-015 S of Arenal, W of El Camino Real 33.05664 117.16171 debris basin concrete BA-017 S of Batiquitos Dr 200' E of Spoonbill Dr 33.05550 117.16910 outlet pipe concrete 72" BA-018 S of Batiquitos Dr and Aviara Dr, SE of Aviara Golf Club Parking Lot 33.05545 117.17158 outlet pipe concrete 48" BA-021 50' E of Carlsbad Bl Bridge at N end of Batiquitos Lagoon 33.05345 117.18714 manhole concrete 24" BA-022 In Sediment Basin SW of Navigator Cr and Windrose Cr 33.05458 117.18481 outlet pipe concrete 72" & 36" CSDM Lagoon Monitoring Station Information Encinitas CBS-1 SEJPA 33.01361 117.27306 outlet channel concrete 2 4'x6' boxes CBS-2 Cardiff 101 Channel 33.01667 117.28139 outlet channel concrete 60" wide trapezoidal channel SEL-1 SE Storm Drain 33.01472 117.27639 outlet pipe concrete 12" SEL-2 MacKinnon Ranch 33.01333 117.27167 outlet pipe concrete undetermined SEL-3 Mira Costa 33.01639 117.25694 detention basin natural undetermined Solana Beach SE1 Highway 101 North Outfall Outfall Pipe Metal 24" SE2 East Side Railroad Tracks Open Channel Concrete SE3 Rios Access Rd Outfall Outfall Pipe Metal 12" SE4 Rios Rd Outfall Outfall Pipe Metal 24" SE5 Santa Inez Outfall Outfall Pipe Metal 24" SE6 Santa Carina Outfall Outfall Pipe Metal 24" SE7 Santa Helena Outlet Catch Basin Concrete Open SE8 Santa Luisa Outlet Catch Basin Concrete Open San Diego PENA03 Portofina Drive 32.55846 117.14822 outlet pipe concrete 24" PENA06 Via Esperia 32.55940 117.15112 outlet pipe concrete 24" PENA08 Between Via Aprilla & Del Mar Scenic Pkwy 32.56076 117.15377 outlet pipe concrete 48" PENA10 Del Mar Scenic Pkwy North 32.56141 117.15447 outlet pipe concrete 21" PENA11 Del Mar Scenic Pkwy South 32.56140 117.15443 outlet pipes concrete 24",24" I NTERSTATE 5HIGH WAY 78 V I A D E L A V A L L EMISSION AVH IG HW A Y 565 78S-10 S-06S-05S-04S-03S-02 S-01 SEL-3SEL-2SEL-1CBS-2 CBS-1 EH-390 EH-420 EH-410 EH-405EH-403 EH-477EH-479 EH-475EH-470 EH-476 BA-022BA-021 BA-019BA-018 BA-017 BA-015 BA-014BA-013 BA-009BA-008 BA-001 AH-025 AH-023 AH-022AH-020 AH-019 AH-017 AH-011AH-006 BV-010 BV-002 AH-019A Coast 9 Coast 8Coast 7Coast 6 Coast 3 Coast 22 Coast 20 Coast 19Coast 18 Coast 17 Coast 21Coast 16 Coast 14 Coast 13Coast 12 Legend City, Sampling Type Oceanside, Coastal Oceanside, Lagoon Carlsbad, Coastal Carlsbad, Lagoon Encinitas, Coastal Encinitas, Lagoon Solana Beach, Coastal Del Mar, Coastal Freeways Streams Other Jurisdictions Oceanside Carlsbad Encinitas Solana Beach Del Mar Water Northern Coastal Storm Drain Monitoring Locations 0 1 20.5 Miles Buena Vista Lagoon Batiquitos Lagoon Agua Hedidonda Lagoon San Dieguito Lagoon San Elijo Lagoon INTERSTATE 5I N T E R S T A T E 8 0 5 INTERSTATE 15HIGHWAY 52 HIGHWAY 163HI GHWA Y 7 5INTERSTATE 8 B A L B O A A V H IGH WAY 94 H IG H W A Y 56CATALI NA BLVDROSECRANS ST40TH STHIGHWAY 75INTERSTATE 1558 0 5 158 1516352 759456 5475 S-10 S-01 EH-210 EH-205EH-200 EH-160 EH-120 EH-070 EH-330EH-320 EH-300 EH-290 FM-080 EH-340 FM-060 EH-300 FM-050EH-280 EH-255FM-030 EH-250 PENA11PENA10PENA08PENA06 Legend City, Sampling Type San Diego, Coastal San Diego, Lagoon San Diego Unified Port District, Coastal Streams Freeways Other Jurisdictions San Diego Port of San Diego Water Southern Coastal Storm Drain Monitoring Locations 0 1 20.5 Miles Los Penasquitos Lagoon Mission Bay San Diego Bay APPENDIX C Sample Collection Standard Operating Procedures Due to the number of pages in this document, this information is submitted electronically only. Please refer to the enclosed CD for the electronic version of Attachment A: Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report. STANDARD OPERATING PROCEDURES (S.O.P.) FOR THE COLLECTION OF BACTERIA SAMPLES FROM STORM DRAINS AND RECEIVING WATERS (CREEKS, LAGOONS, BAYS, AND OCEAN). I Introduction: This SOP describes the proper sampling technique for the collection of bacteria samples from receiving waters and storm drains. These sampling techniques are approved for both permit compliance monitoring and recreational beach monitoring for human health concerns. To accurately assess bacteria concentrations in urban runoff and receiving waters, field and laboratory staff must collect and analyze samples in accordance with the following guidance documents: · Standard Operating Procedures for the Collection of Bacteria Samples from Storm Drains and Receiving Waters (Creeks, Lagoons, Bays, and Ocean). · Most Current Version of Standard Methods for Wastewater Analysis II General Standard Sampling Procedures: Care should be taken to avoid direct, indirect, and cross contamination of the water, sample containers, coolers, and other tools used to collect water samples. Do’s · Store / transport unused sample bottles in a clean bag or cooler. · Always wear nitrile or latex gloves when handling samples. · Use EPA approved unopened autoclaved / sterilized clear plastic bottles. · Immediately place samples into coolers. · Clearly distinguish between receiving water and storm drain samples during storage and transfer. A suggested method could be to place them in separate coolers. Do Not’s · Do not remove the sample bottle cap until immediately prior to sampling. · Do not touch the inside of the bottle or cap. · Do not place the cap on the ground or in a pocket. · Do not rinse the bottle. · Do not reuse sample bottles or syringes. · Do not carry samples in pockets or under arms Equipment List 1. Rubber Gloves 2. Coolers (2) 3. Blue Ice 4. Sample Bottles 5. 4’-8’ Sample Pole 6. Sampling Syringes 7. Sample Bottle Labels 8. Rubber Waders/Boots 9. Sharpie© Permanent Marker 10. Ballpoint Pen 11. Mechanical Pencil 12. Clipboard 13. Field Data Sheets 14. GPS Unit 15. Stop Watch 16. Flashlight 17. Tape Measure 18. Digital Camera 19. Site Maps 20. City Identification 21. Personal Business Cards 22. Lab Chain of Custody Sheets 23. Cellular Phone STANDARD OPERATING PROCEDURES (S.O.P.) FOR THE COLLECTION OF BACTERIA SAMPLES FROM STORM DRAINS AND RECEIVING WATERS (CREEKS, LAGOONS, BAYS, AND OCEAN). Page 2 of 6 S:\Watershed Project\WATER QUALITY\SCIENCE AND MONITORING\copermiteemonitoringcom\Coastal Monitoring\2002-2003 report\Final CD\8_Microbiology Sampling SOP 032803.doc Last Updated: 03-28-03 III Sample Bottles and Bottle Labeling: The following pertinent information shall be recorded on all sample bottles prior to sample collection. Be sure that sample bottle information matches the chain of custody. Information shall be written using an indelible ink pen and in ones best handwriting. All information must also match field monitoring sheet. i Location of Sample – Record Station ID and Source information (ie:Storm Drain or Receiving Water sample) ii Sampler – Record sampler’s initials iii Date – Record date in the MM-DD-YY format iv Time – Record using 24-hour clock v Project Title (optional) vi Remarks – Record general comments (optional). IV Sample Collection: Direct Fall – This collection method is used for water samples collected from flowing storm drains where water can be easily collected by placing a sample bottle under the flow. (i.e. similar to a low flowing garden hose) i Using indelible ink, clearly label the sample bottle prior to collecting sample with the appropriate information as described section III, “Sample Bottle Labeling”. ii Put on gloves. iii Remove the screw cap, holding the open side of the cap facing the ground. DO NOT PLACE THE CAP ON THE GROUND OR IN A POCKET iv Place the opened sample bottle under the stream of water . Fill the sample bottle to the shoulder of the bottle by. Be sure to leave a small amount of air in the sample container prior to capping the bottle. v Replace the cap tightly. vi Place the sample on ice (blue ice) in the dark from the time of collection until delivery to the analytical laboratory. Syringe Collection – This collection method is used for water samples collected from low flowing storm drains, gutters, and shallow puddles. i Using indelible ink, clearly label the sample bottle prior to collecting sample with the appropriate information as listed in section III, “Sample Bottle Labeling” of this S.O.P. ii Put on gloves. iii Loosen the screw cap, but do not remove the cap from the sample bottle. While keeping the cap on the bottle, you may place the sample bottle upright on the ground/sand while working with syringe. iv Remove the syringe from its sterile packaging. v Position for sample. STANDARD OPERATING PROCEDURES (S.O.P.) FOR THE COLLECTION OF BACTERIA SAMPLES FROM STORM DRAINS AND RECEIVING WATERS (CREEKS, LAGOONS, BAYS, AND OCEAN). Page 3 of 6 S:\Watershed Project\WATER QUALITY\SCIENCE AND MONITORING\copermiteemonitoringcom\Coastal Monitoring\2002-2003 report\Final CD\8_Microbiology Sampling SOP 032803.doc Last Updated: 03-28-03 vi Remove small protective cap from point of syringe. vii Place the tip of the syringe below the water’s surface to prevent the suction of surface scum, yet far enough away from the bottom to prevent the suction of soil, silt, and organic matter. viii Draw back the plunger in a controlled and slow manner, monitoring the syringe for organic matter, silt, sand, and scum. IF ACCIDENTAL COLLECTION OF BOTTOM SEDIMENTS AND/OR ORGANICS OCCURS, DISCARD THE SYRINGE AND RESAMPLE using a clean syringe AND sample bottle. Naturally occurring suspended solids in the sample is permitted. ix Remove the screw cap, holding the open side of the cap facing the ground. DO NOT PLACE THE CAP ON THE GROUND OR IN A POCKET. x Dispense the water inside the syringe into the sample bottle by pressing slowly on the plunger. DO NOT CONTACT THE INSIDE OF THE BOTTLE WITH ANY PART OF THE SYRINGE. xi Replace the cap loosely onto the sample bottle. vii Repeat steps vi-ix until the water level reaches the shoulder of the bottle. Be sure to leave a small amount of air in the sample container prior to capping the bottle. xii Replace the cap tightly. xiii Place the sample into the cooler and keep them on ice (blue ice) in the dark from the time of sample collection until delivery to the analytical laboratory. xiv Syringes are for single use only. Discard used syringe after collection of each sample. Plunge Sample – This collection method is used for samples collected from deep, ponded areas or ocean, bay, and lagoon samples. i Using indelible ink, clearly label the sample bottle prior to collecting sample with the appropriate information as listed in section III, “Sample Bottle Labeling” of this S.O.P. ii Put on gloves. iii Place the bottle into the sampling pole, if necessary. iv Loosen the screw cap. v Remove the screw cap, holding the open side of the cap facing the ground and turn the bottle so the opening is facing the ground. DO NOT PLACE THE CAP ON THE GROUND OR IN A POCKET vi (This step for bay and lagoon samples) The sampler will wade slowly into the water to a depth of about 12 inches (middle of the shinbone) being careful not to stir bottom sediments and sand. The sampler shall reach far out in front to ensure water collected does not contain Too Too Deep Correct Shallow Wade into the water approximately 1 foot deep, incoming wave, sweeping motion 4- 8 inches beneath the water. STANDARD OPERATING PROCEDURES (S.O.P.) FOR THE COLLECTION OF BACTERIA SAMPLES FROM STORM DRAINS AND RECEIVING WATERS (CREEKS, LAGOONS, BAYS, AND OCEAN). Page 4 of 6 S:\Watershed Project\WATER QUALITY\SCIENCE AND MONITORING\copermiteemonitoringcom\Coastal Monitoring\2002-2003 report\Final CD\8_Microbiology Sampling SOP 032803.doc Last Updated: 03-28-03 sediment/sand that is stirred-up while sampler wading into the water. vii (This step for ocean samples only) a. Visually determine the direction of the ocean swell. b. Record the swell direction and note sample location while standing at the storm drain and looking at the ocean, see below. i. If swell is out of the northwest (swell pushes south), grab sample 25 yards left of the storm drain outlet. ii. If swell is out of the southwest (swell pushes north), grab sample 25 yards right from storm drain outlet. c. The sampler will wade into the water to a depth of about 12 inches (middle of the shinbone). On an incoming wave (not outgoing wave), the sampler shall use the sample pole to reach the bottle far out in front of him/her to ensure water collected does not contain sediment suspended while wading out to depth. viii Collect the sample from below the water surface being careful not to collect surface scum or bottom sediments. a. Plunge the bottle into the water with the bottle opening facing downwards to a depth of approximately 4”-8” b. Turn the bottle such that the mouth of the bottle opening points slightly upwards, while slowly moving the bottle horizontally through the water (this eliminates cross contamination from sampling equipment or hands). c. When the bottle is nearly full tilt the bottle upwards while removing the bottle from the water. ix Decant as necessary to lower the water level to the shoulder of the bottle assuring that a small amount of air is left in the sample container prior to capping. x Do not allow surface residue, sediment, or debris to enter the sample bottle. If debris or sediment is evident in the bottle, discard the sample and re-sample the site with a new, sterile bottle. xi Replace the cap tightly. xii Place the samples into the cooler and keep them on ice (blue ice) in the dark from the time of sample collection until delivery to the analytical laboratory. YES NO Water should be filled to the shoulder of the bottle; however, sediment shall not be present in samples. In this case, the water sample shall be discarded and a new sample bottle used to recollect a sample. Yes No STANDARD OPERATING PROCEDURES (S.O.P.) FOR THE COLLECTION OF BACTERIA SAMPLES FROM STORM DRAINS AND RECEIVING WATERS (CREEKS, LAGOONS, BAYS, AND OCEAN). Page 5 of 6 S:\Watershed Project\WATER QUALITY\SCIENCE AND MONITORING\copermiteemonitoringcom\Coastal Monitoring\2002-2003 report\Final CD\8_Microbiology Sampling SOP 032803.doc Last Updated: 03-28-03 V Laboratory Procedures: Sample Preservation – All samples shall be stored on Blue Ice in sample cooler and delivered to the laboratory within 6 hours of sample collection. Analytical Methods – All samples shall be analyzed using the methods approved in Standard Methods for the Examination of Water and Wastewater, 18th Edition 1992. In addition, all samples shall be analyzed using the detection ranges listed below unless directed otherwise by a Storm Water Program Biologist. · Receiving Waters (Beaches, Bays, Lagoons) – All receiving water samples shall be analyzed for Total Coliform, Fecal Coliform), and Enterococci using only EPA approved methods. Receiving waters analysis should be analyzed using detection ranges between 2- 16,000 MPN/100mL. [I do not think we should be specifying a method since this SOP is being designed to be used by all in SD Region] · Storm Drain Samples – All storm drain samples shall be analyzed for Total Coliform, Fecal Coliform, and Enterococci using only EPA approved methods. Storm drain samples should be analyzed using detection ranges between 20-160,000 MPN/100mL or CFU/100mL. Sampling Report and Chain of Custody Procedures – An official Sampling Report and Chain of Custody Record shall be completed for all samples submitted to the laboratory. i Record the appropriate sample information in the correct sections. Be sure to include collection time and verify that bottle numbers are correctly listed. ii Fill in any appropriate comments or special instructions to the laboratory staff. iii Relinquish samples to the laboratory by legibly printing, signing, and dating the chain of custody section. iv Retain copies of the Sampling Report and Chain of Custody Record for filing. Cooler/Blue Ice Clean-up – All coolers and Blue Ice shall be cleaned after delivery of the samples to the laboratory. i Wear laboratory latex or nitrile gloves when washing equipment. ii With a soapy sponge and warm water, wash and rinse the cooler and Blue Ice. STANDARD OPERATING PROCEDURES (S.O.P.) FOR THE COLLECTION OF BACTERIA SAMPLES FROM STORM DRAINS AND RECEIVING WATERS (CREEKS, LAGOONS, BAYS, AND OCEAN). Page 6 of 6 S:\Watershed Project\WATER QUALITY\SCIENCE AND MONITORING\copermiteemonitoringcom\Coastal Monitoring\2002-2003 report\Final CD\8_Microbiology Sampling SOP 032803.doc Last Updated: 03-28-03 iii Dry the cooler and Blue Ice completely by wiping with paper towels. iv Wipe down with a 1% benzylchronium chloride saturated towel to decontaminate. Material Resupply – All material stocks should be assessed upon completion of sampling activity. Replace any used materials immediately so that adequate materials are available for future sampling. i Place Blue Ice into the freezer for future use. ii Obtain additional Sampling Report and Chain of Custody Records. iii Obtain additional sample bottles as necessary. APPENDIX D 2004-2005 Coastal Storm Drain Monitoring Field Data Sheet Insert City Seal and Address *See formula and conversions on back of page COASTAL STORM DRAIN MONITORING Routine Investigation Resample IC/ID Follow-Up (Select One) GENERAL SITE DESCRIPTION Site ID: Latitude: (GPS coordinates recorded in NAD 83 decimal deg) Location: Longitude: Date/Time: Watershed: (Watershed Management Area as defined in Permit) Observer: TB Page: ATMOSPHERIC CONDITIONS Weather Sunny Partly Cloudy Overcast Fog Tide N/A Low Incoming High Outgoing Tide Height: ______ft. Last Rain > 72 hours < 72 hours Rainfall None < 0.1” > 0.1” BEACH APPEARANCE Composition: Sandy Rocky/Gravel Clean Trash Kelp/Grasses Organic Matter Other: ___________ RUNOFF CHARACTERISTICS Odor None Musty Rotten Eggs Chemical Sewage Other Color None Yellow Brown White Gray Other Clarity Clear Slightly Cloudy Opaque Other Floatables None Trash Bubbles/Foam Sheen Fecal Matter Other Deposits None Sediment/Gravel Fine Particulates Stains Oily Deposit Other Vegetation None Limited Normal Excessive Other Biology None Insects Algae Snails/Fish Mussels/barnacles Other Flow Observed Yes No Ponded Tidal (If yes, record conductivity below) Flow Rate:__________ gpm (*See worksheets below) __________mS/cm or mhos/cm Does the storm drain flow reach the Receiving Water? Yes No N/A Evidence of Overland Flow? Yes No Irrigation Runoff Other: ________________________ Photo Taken Yes No Picture # __________ Stormdrain Sample Collected Yes No Bottle ID# __________ Collection Time __________ Storm Drain T. Coliform F. Coliform Enterococcus Receiving Water Sample Collected Yes No Bottle ID# __________ Collection Time __________ Sample Location (From storm drain, facing receiving water) 75’ Left 75’ Right Mixing Zone Other Receiving Water T. Coliform F. Coliform Enterococcus * FLOW ESTIMATION WORKSHEETS Flowing Creek or Box Culvert* Filling a Bottle or Known Volume* Flowing Pipe* Width ft Volume mL Diameter ft Depth ft Time to Fill sec Depth ft Velocity ft/sec Flow gpm Velocity ft/sec Flow gpm Flow gpm COMMENTS: Observed Land Use: Residential Commercial Industrial Agricultural Parks Open (check all applicable) Conveyance Type: Manhole Catch Basin Outlet Open Channel Other Construction: Concrete Steel Plastic Natural Potential Fecal Sources Within 75 ft. Wildlife: # Pets: #______ Birds: #______ Children (Diapers): _____ Other Bathers: # Encampments: # Insert City Seal and Address *See formula and conversions on back of page SAE / Metric Unit Conversion 0.083 ft = 1 in = 2.54 cm 0.1337 ft3 3,785 mL = 1 gal = = 128 oz 3.785 L 1ft3/S = 448.8 gal/min 0.0078 gal = 1 oz = .0011 ft3 1mL/S = 0.0159 gal/min 1000 cm3 = 1 L = 1000 mL 1728 in3 = 1ft3 ppt = g/L ppm = mg/L ppb = µg/L AREA x VELOCITY (CREEK/CHANNEL METHOD) TIME REQUIRED TO FILL A KNOWN VOLUME (FILL A BOTTLE METHOD) AREA x VELOCITY (PARTIALLY FILLED PIPE) 1. Measure the width, depth, and velocity of the water. 2. Convert each value to a common unit (i.e. all measurements converted to cm, ft, or in.) 3. Multiply the width * depth * velocity to determine flow. 4. Multiply the flow by 0.8 for creek measurements –or-- 0.9 for concrete channel measurements to account for channel roughness. 5. The results if measured in Ft = Ft3/sec cm = cm3/sec (mL/sec) in = in3/sec 6. Convert to desired value. 1. Determine volume/capacity of the sample bottle. 2. Measure time required to fill the bottle. 3. Divide time by seconds 4. Flow will be determined by initial volume units: mL/s oz/s 5. Convert to desired value 1. All measurement must be converted to a common unit before calculation (ft, in, or cm). 2. Let D = water depth 3. Let d = inside pipe diameter 4. Calculate D/d 5. Find the tabulated (Ta) value on the partially filled pipe formula chart above using the D/d value. (i.e. if D/d = 0.263 then Ta . 0.1623) 6. Find the area using the formula a = Ta*d2. 7. Multiply area (a) by the water velocity. 8. Convert to desired value D = Depth of water a = area of water in partially filled pipe d = diameter of the pipe Ta = Tabulated Value Then a = Ta*d2 D/d 0.00 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.0 0.0000 0.0013 0.0037 0.0069 0.0105 0.0147 0.0192 0.0242 0.0294 0.0350 0.1 0.0409 0.0470 0.0534 0.0600 0.0668 0.0739 0.0817 0.0885 0.0951 0.1039 0.2 0.1118 0.1199 0.1281 0.1365 0.1440 0.1535 0.1623 0.1711 0.1800 0.1890 0.3 0.1982 0.2074 0.2187 0.2280 0.2355 0.2450 0.2540 0.2642 0.2780 0.2836 0.4 0.2934 0.3032 0.3130 0.3220 0.3328 0.3428 0.3527 0.3627 0.3727 0.3827 0.5 0.3980 0.4030 0.4130 0.4230 0.4330 0.4430 0.4520 0.4620 0.4720 0.4820 0.6 0.4920 0.5020 0.5120 0.5210 0.5310 0.5400 0.5500 0.5590 0.5690 0.5780 0.7 0.5870 0.5960 0.6050 0.6140 0.6230 0.6320 0.6400 0.6490 0.6570 0.6660 0.8 0.6740 0.6810 0.6890 0.6970 0.7040 0.7120 0.7190 0.7250 0.7320 0.7360 0.9 0.7450 0.7500 0.7560 0.7610 0.7660 0.7710 0.7750 0.7790 0.7820 0.7840 Calculating the Area (a) of the Cross Section of a Circular Pipe Flowing Partially Full Insert City Seal and Address *See formula and conversions on back of page APPENDIX E Coastal Storm Drain Monitoring Data Transfer Templates Coastal Stormdrain Monitoring WorkgroupData Transfer Template GuidelinesforAnalytical (Lab) DataField NamePrefix Station_ID Location Station_Type Date Time Station_Owner Analyte MethodField DescriptionA qualifier code identifying why the sample was collected. All samples collected during the course of normal sampling should be labeled routine, samples collected due to action level exceedances are follow-up.The name or number identifying the geographical location where the sample was collected. This ID will be unique to the the geographical location.The name of the beach or general area where the sample site is located. The location name should be a common name used to identify the location in general terms (i.e. Moonlight Beach, etc) A three or four letter text value identifiying the type of sample collected. For purposes of this data template, locations should typically have two station types associated with each - a receiving water and a stormdrain.The date the sample was collected. Use the format presented below. If a month or day is a single number it should be preceded by a zero (ie 01/01/04). The time the sample was collected. Use the format presented below. e time should use the 24-hr clock (military time). If the hour is a single digit, it should be preceded by a zero (ie Two O'clock AM should read 02:00).The jurisdiction in which the station is located. This may or may not be the same as the collecting agency (a City may elect to contract sample collection to an outside consultant).The parameter or constituent being analyzed. The codes identifed below should be used for each constituent. In terms of data sharing consistency, a list of constituent codes should be established by the regional monitoring group.The analytical method used to perform the analysis. Use the appropriate code from the list.Required Field TypeText - use codes listed below Text Text Text - use codes listed below Date TimeText - use codes listed belowText - use codes listed below Text - use codes listed belowR - RoutineCoastal Sites - DEH IDsCRW- coastal receiving waterMM/DD/YYHH:MMCA - Carlsbad Total Coliform SM 9221B- MTF Total ColiformF - Follow up CSDO- coastal stormdrain outfallCO - CoronadoFecal Coliform SM 9221E- MTF Fecal ColiformS - Sewage Spill ResponseLagoon Sites - use a similar patternLRW - lagoon receiving waterDM - Del MarEnterococcusSM 9223- Chromogenic substrate (ie IDEXX)(ie 2 letters - 3 numbers)LSDO - lagoon stormdrain outfallEN - EncinitasSM 9222B - MF Total ColiformIB - Imperial BeachSM 9222D - MF Fecal ColiformOC - OceansideSM 9230B- MTF for Fecal Strep and Enterococci PT - Port of San DiegoSM 9230C- MF for Fecal Strep and EnterococciSD - City of San DiegoSB - Solana Beach* Valid field codes for each field having a predetermined set of allowable values are identified in BOLD print. Each valid code is followed by a definition of the value. Valid Field Code*The development of this table and associated field names are derived from the Stormwater Monitoring Coalition (SMC) Standardized Data Transfer Guidance Document and the County of San Diego Department of Environmental Health (DEH) Beach Water Quality Database. Every effort has been made to remain consistent with field names and valid value lists within the aforementioned data transfer formats.CSDM Laboratory Data Transfer Template (Final) 7/20/041 of 2 Coastal Stormdrain Monitoring WorkgroupData Transfer Template GuidelinesforAnalytical (Lab) DataSample_Type Qualifier Result Unit Reporting_Limit Lab Distance Direction SD_Reach_RWThe type of sample being analyzed. This field differentiates laboratory and field QA samples from normal field collected samples. All samples that are collected as part of a normal field study should be identified as "Result".An identification of what the reported result for the analyzed sample represents. This field MUST to be formatted as a text field. Actual results from either QA samples or field samples should use the qualifier "None". If the qualifiers "NA", "NS", or "AE" are entered, the result MUST be reported as "-99"The numerical result obtained from the lab (whether an estimate from MTF or IDEXX) or plate count (MF). If "NA", "NS", or "AE" are entered as qualifiers, the result MUST be reported as "-99". A unit of measurement appropriate to the analysis and analytical method. A complete list of units should be established for the group. The reporting limit is the minimum value that the specified method (and dilution) can give readable results. This value will be a numeric value only. The lab used to perform the analysis. Analytical Labs will be identified and assigned a lab code for purposes of data transfer consistency.This field identifies the distance in feet from the stormdrain to the receiving water collection site. This field is for receiving water samples only ("CRW" "LRW"). Samples collected from stormdrain outfalls ("CSDO" "LSDO") should leave this field blank.This field identifies the direction from the stormdrain, when facing the water, to the receiving water collection site. This field is for receiving water samples only ("CRW" "LRW"). Samples collected from stormdrain outfalls ("CSDO" "LSDO") should leave this field blank.This field identifies whether the stormdrain flow reaches the receiving water. This field is for stormdrain samples only. Enter "yes" if flow is observed entering receiving water. Enter "no" if the water is ponded, or the flow is infiltrating and not entering the receiving water.Text - use codes listed below Text - use codes listed below NumberText - use codes listed belowNumber Text - use codes listed below NumberText - use codes listed belowText - use codes listed belowFDUP - Field DuplicateNone - True sampling resultMPN/100mlAJL- Alvarado Joint LabR- Right Yes FBLK - Field Blank< - less thanCFU/100mlEWW- Encina Wastewater L- LeftNoLBLK - Laboratory Blank> - greater thanEMX - EnviromatrixM - Mixing ZoneLDUP - Laboratory DuplicateNA - Not AnalyzedEEL- Environmental Engineering LabsLCM - Laboratory Control MaterialNS - Not SampledPHL- County Public Health LabLREP - Laboratory ReplicateAE - Analyst ErrorMEC - MEC/WestonMS - Matrix SpikeMML- EMTS Marine Microbiology LabRESULT - Normal Field SampleSLR- San Luis Rey Wastewater DeptSRM - Standard Reference MaterialCSDM Laboratory Data Transfer Template (Final) 7/20/042 of 2 Coastal Stormdrain Monitoring WorkgroupData Transfer Template Guidelines for Visual Observations Field NamePrefix Station_ID Station_Owner Date Time Weather Rainfall Tide Tide_Height Wildlife Pets BirdsField DescriptionA qualifier code identifying why the sample was collected. All samples collected initially should be labeled routine, samples collected due to action level exceedances are follow-up.The name or number identifying the geographical location where the sample was collected. This ID will be unique to the geographical location.The jurisdiction in which the station is located. This may or may not be the same as the collecting agency (a City may elect to contract sample collection to an outside consultant).The date the sample was collected. Use the format presented below. If a month or day is a single number it should be preceded by a zero (ie 01/01/04). The time the sample was collected. Use the format presented below. e time should use the 24-hr clock (military time). If the hour is a single digit, it should be preceded by a zero (ie Two O'clock AM should read 02:00).A general description of the atmospheric conditions while on site. Values are limited to the list identified below.The amount of rain that fell within the last 72 hours. Values are limited to the codes listed below.An observation of the tidal stage at the time of the visual observations. Values are limited to the codes listed below.A numerical value quantifying the tide height (in feet) at the time of visual observations. Tide Heights should be based on local tide charts referring to MMLW depths. Negative tide should be identified with a "minus" sign.A numeric value quantifying the wildlife (excluding birds) either on the beach or in the water within a 75ft. radius of the sample site. If no wildlife is present, a zero should be recorded.A numeric value quantifying the number of pets either on the beach or in the water within a 75ft. radius of the sample site. If no pets are present, a zero should be recorded.A numeric value quantifying the number of birds either on the beach or in the water within a 75ft. radius of the sample site. If no birds are present, a zero should be recorded.Required Field TypeText - use codes listed belowTextText - use codes listed belowDate Time Text Text Text Number Number Number NumberR - RoutineCoastal Sites - DEH IDsCA - Carlsbad MM/DD/YY HH:MMSunnyNone N/A####F - Follow upLagoon Sites - CO - CoronadoPartly Cloudy<0.1" LowS - Sewage Spill Responuse a similar patternDM - Del MarOvercast >0.1" Incoming(ie 2 letters - 3 numbers)EN - EncinitasFog HighIB - Imperial BeachOutgoingOC - OceansidePT - Port of San DiegoSD - City of San DiegoSB - Solana Beach* Valid field codes for each field having a predetermined set of allowable values are identified in BOLDprint. Each valid code is followed by a definition of the value. Valid Field CodeThe development of this table and associated field names are derived from the Stormwater Monitoring Coalition (SMC) Standardized Data Transfer Guidance Document and the County of San Diego Department of Environmental Health (DEH) Beach Water Quality Database. Every effort has been made to remain consistent with field names and valid value lists within the aforementioned data transfer formats.CSDM Visual Observations Data Transfer Template (Final) 7/21/041 of 3 Coastal Stormdrain Monitoring WorkgroupData Transfer Template Guidelines for Visual Observations Field NameField DescriptionRequired Field TypeValid Field CodeChildren Other_Bathers Encampments Beach_Clean Beach_Trash Beach_Kelp Beach_Organic Other Odor Color ClarityA numeric value quantifying the number of children either on the beach or in the water within a 75ft. radius of the sample site. If no children are present, a zero should be recorded.A numeric value quantifying the number of bathers either on the beach or in the water within a 75ft. radius of the sample site. If no bathers are present, a zero should be recorded.A numeric value quantifying the number of encampments within a 75ft. radius of the sample site. If no encampments are present, a zero should be recorded.This field identifies whether or not the beach is clean. Values are limited to Yes/No. If Beach_Clean is "No" then one of the next four fields must be "Yes".This field identifies whether or not there is trash on the beach. Values are limited to Yes/No. If Beach_Clean is "Yes" then this field must be "No".This field identifies whether or not there is kelp present on the beach. Values are limited to Yes/No. If Beach_Clean is "Yes" then this field must be "No".This field identifies whether or not there is organic material on the beach. Values are limited to Yes/No. If Beach_Clean is "Yes" then this field must be "No".This field identifies materials on the beach that are not covered in the previous categories. Values are limited to Yes/No. If Beach_Clean is "Yes" then this field must be "No". If this field is "yes" then additional descriptions of these materials should be included the comments field.A general description of the storm drain discharge odor. If the odor is typical of seawater or freshwater, it should be identified as "None". The code "Other" should only be used in the case where an abnormal odor is apparent and it does not fit the existing codes. In this instance, further description should be included the comments field.A general description of the storm drain discharge color. If the clarity is typical of seawater or freshwater, it should be identified as "None". The code "Other" should only be used in the case where an abnormal color is apparent and it does not fit the existing codes. In this instance, further description should be included the comments field.A general description of the storm drain discharge clarity. Values are limited to the codes listed below.Number Number Number Text Text Text Text Text Text - use codes listed below Text - use codes listed below Text## #Yes Yes Yes Yes Yes None None ClearNo No No No No MustyYellow Slightly CloudyRotten Eggs Brown OpaqueChemical WhiteSewage GrayOther OtherCSDM Visual Observations Data Transfer Template (Final) 7/21/042 of 3 Coastal Stormdrain Monitoring WorkgroupData Transfer Template Guidelines for Visual Observations Field NameField DescriptionRequired Field TypeValid Field CodeFloatables Vegetation Deposits Biology Flow_Observed Flow_Rate SD_Reach_RW Overland_Flow CommentsA general description of floating materials found in the discharge. If no floatables are present, "None" should be entered in this field. The code "Other" should only be used when materials are present that do not fit the existing codes. In this instance, further description should be included the comments field.An observation of the vegetation found in the discharge area at the time of the visual observations. Values are limited to the codes listed below.A general description of the deposits found in the storm drain. If there are no deposits present, "None" should be entered in this field. The code "Other" should only be used in instances where deposits are present that do not fit the existing codes. In this instance, further description should be included the comments field.A general description of the biota present in the stormdrain. If there are no organisms present, it should be identified as none. The code "Other" should only be used in the case where organisms are present that do not fit the existing codes. In this instance, further description should be included the comments field.This field identifies whether flow is observed from the stormdrain. Values are limited to those listed below. If the water is present but not flowing, the value "Ponded" should be used. A numerical value quantifying the flow rate (in gallons per minute) at the time of visual observations.This field identifies whether storm drain discharges reach the receiving water. If the "Flow_Observed" field has a "Yes" value, this field must have a "Yes" or "No" value. If the flow observed is "No" or "Ponded", then "N/A" must be entered.This field identifies the presence of any overland flow or discharges. If the "Flow_Observed" field has a "Yes" value, this field must have a Yes/No values. If the flow observed is no, then N/A must be entered.This field is for further explainations of the entered data. If additional site information is needed, it should be added here. Text - use codes listed below Text Text - use codes listed below Text - use codes listed below Text Number Text Text TextNone None None None Yes#Yes YesTrash Limited Sediment/Gravel Insects No No NoBubbles/Foam Normal Fine ParticlesAlgae Ponded N/AIrrigationSheen Excessive Stains Snails/Fish Tidal N/AFecal Matter Oily Deposits Mussels/BarnaclesOther Other OtherCSDM Visual Observations Data Transfer Template (Final) 7/21/043 of 3 APPENDIX F & G 2004-2005 Coastal and Lagoon Bacteria Data Due to the extreme size of the data set, this information is submitted electronically only. Please refer to the enclosed CD for the electronic version of Attachment A: Coastal Storm Drain and Lagoon Monitoring 2004-2005 Annual Report. Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 8 CSDO 11/16/04 8:44 EnterococcusSM 9223Result None 1400 10 YesR COAST 8 CRW 11/16/04 8:45 EnterococcusSM 9223Result None 1000 10 0 MR COAST 8 CSDO 11/16/04 8:44 Fecal ColiformSM 9221EResult None 1600000 20 YesR COAST 8 CRW 11/16/04 8:45 Fecal ColiformSM 9221EResult None 17000 20 0 MR COAST 8 CSDO 11/16/04 8:44 Total ColiformSM 9221BResult > 1600000 20 YesR COAST 8 CRW 11/16/04 8:45 Total ColiformSM 9221BResult None 900000 20 0 MR COAST 8 CSDO 12/14/04 9:00 EnterococcusSM 9223Result None 17100 10 YesR COAST 8 CRW 12/14/04 9:01 EnterococcusSM 9223Result None 85 10 0 MR COAST 8 CSDO 12/14/04 9:00 Fecal ColiformSM 9221EResult None 20 20 YesR COAST 8 CRW 12/14/04 9:01 Fecal ColiformSM 9221EResult None 3000 20 0 MR COAST 8 CSDO 12/14/04 9:00 Total ColiformSM 9221BResult None 500 20 YesR COAST 8 CRW 12/14/04 9:01 Total ColiformSM 9221BResult None 50000 20 0 MR COAST 8 CSDO 01/18/05 8:45 EnterococcusSM 9223Result None 460 10 YesR COAST 8 CRW 01/18/05 8:46 EnterococcusSM 9223Result None 20 10 0 MR COAST 8 CSDO 01/18/05 8:45 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 8 CRW 01/18/05 8:46 Fecal ColiformSM 9221EResult None 40 20 0 MR COAST 8 CSDO 01/18/05 8:45 Total ColiformSM 9221BResult None 130000 20 YesR COAST 8 CRW 01/18/05 8:46 Total ColiformSM 9221BResult None 1700 20 0 MF COAST 8 CSDO 02/10/05 12:30 EnterococcusSM 9223Result None 2250 10 YesF COAST 8 CRW 02/10/05 12:32 EnterococcusSM 9223Result None 260 10 0 MF COAST 8 CSDO 02/10/05 12:30 Fecal ColiformSM 9221EResult None 500 20 YesF COAST 8 CRW 02/10/05 12:32 Fecal ColiformSM 9221EResult None 40 20 0 MF COAST 8 CSDO 02/10/05 12:30 Total ColiformSM 9221BResult None 900000 20 YesF COAST 8 CRW 02/10/05 12:32 Total ColiformSM 9221BResult None 80000 20 0 MR COAST 18 CSDO 03/08/05 9:35 EnterococcusSM 9223Result < 10 10 NoR COAST 18 CSDO 03/08/05 9:35 Fecal ColiformSM 9221EResult < 20 20 NoR COAST 18 CSDO 03/08/05 9:35 Total ColiformSM 9221BResult None 40 20 NoR COAST 8 CSDO 03/08/05 8:36 EnterococcusSM 9223Result None 602 10 YesR COAST 8 CRW 03/08/05 8:37 EnterococcusSM 9223Result None 602 10 0 MR COAST 8 CSDO 03/08/05 8:36 Fecal ColiformSM 9221EResult None 8000 20 YesR COAST 8 CRW 03/08/05 8:37 Fecal ColiformSM 9221EResult None 230 20 0 MR COAST 8 CSDO 03/08/05 8:36 Total ColiformSM 9221BResult > 1600000 20 YesR COAST 8 CRW 03/08/05 8:37 Total ColiformSM 9221BResult None 130000 20 0 MR COAST 9 CSDO 03/08/05 8:55 EnterococcusSM 9223Result < 10 10 YesR COAST 9 CSDO 03/08/05 8:55 Fecal ColiformSM 9221EResult < 20 20 YesR COAST 9 CSDO 03/08/05 8:55 Total ColiformSM 9221BResult < 20 20 YesR COAST 18 CSDO 04/12/05 11:20 EnterococcusSM 9223Result None 155000 10 YesOC04-05 DataPage 1 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 18 CSDO 04/12/05 11:20 Fecal ColiformSM 9221EResult None 3000 20 YesR COAST 18 CSDO 04/12/05 11:20 Total ColiformSM 9221BResult None 500000 20 YesR COAST 8 CSDO 04/12/05 10:20 EnterococcusSM 9223Result None 130 10 YesR COAST 8 CRW 04/12/05 10:21 EnterococcusSM 9223Result < 10 10 0 MR COAST 8 CSDO 04/12/05 10:20 Fecal ColiformSM 9221EResult None 400 20 YesR COAST 8 CRW 04/12/05 10:21 Fecal ColiformSM 9221EResult None 20 20 0 MR COAST 8 CSDO 04/12/05 10:20 Total ColiformSM 9221BResult None 8000 20 YesR COAST 8 CRW 04/12/05 10:21 Total ColiformSM 9221BResult None 40 20 0 MF COAST 8 CSDO 04/19/05 8:15 EnterococcusSM 9223Result None 580 10 YesF COAST 8 CSDO 04/19/05 8:15 Fecal ColiformSM 9221EResult None 1100 20 YesF COAST 8 CSDO 04/19/05 8:15 Total ColiformSM 9221BResult None 300000 20 YesR COAST 18 CSDO 04/26/05 10:00 EnterococcusSM 9223Result None 21800 10 YesR COAST 18 CRW 04/26/05 10:01 EnterococcusSM 9223Result < 10 10 0 MR COAST 18 CSDO 04/26/05 10:00 Fecal ColiformSM 9221EResult None 800 20 YesR COAST 18 CRW 04/26/05 10:01 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 18 CSDO 04/26/05 10:00 Total ColiformSM 9221BResult None 240000 20 YesR COAST 18 CRW 04/26/05 10:01 Total ColiformSM 9221BResult < 20 20 0 MR COAST 8 CSDO 04/26/05 8:55 EnterococcusSM 9223Result None 130 10 YesR COAST 8 CRW 04/26/05 9:00 EnterococcusSM 9223Result None 52 10 0 MR COAST 8 CSDO 04/26/05 8:55 Fecal ColiformSM 9221EResult None 3000 20 YesR COAST 8 CRW 04/26/05 9:00 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 8 CSDO 04/26/05 8:55 Total ColiformSM 9221BResult None 900000 20 YesR COAST 8 CRW 04/26/05 9:00 Total ColiformSM 9221BResult None 500 20 0 MF COAST 8 CSDO 05/03/05 8:20 EnterococcusSM 9223Result None 8220 10 YesF COAST 8 CSDO 05/03/05 8:20 Fecal ColiformSM 9221EResult None 300 20 YesF COAST 8 CSDO 05/03/05 8:20 Total ColiformSM 9221BResult None 80000 20 YesR COAST 21 CSDO 05/10/05 10:05 EnterococcusSM 9223Result None 41 10 NoR COAST 21 CRW 05/10/05 10:06 EnterococcusSM 9223Result < 10 10 0 MR COAST 21 CSDO 05/10/05 10:05 Fecal ColiformSM 9221EResult None 270 20 NoR COAST 21 CRW 05/10/05 10:06 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 21 CSDO 05/10/05 10:05 Total ColiformSM 9221BResult None 3000 20 NoR COAST 21 CRW 05/10/05 10:06 Total ColiformSM 9221BResult None 80 20 0 MR COAST 8 CSDO 05/10/05 9:13 EnterococcusSM 9223Result None 2340 10 YesR COAST 8 CRW 05/10/05 9:14 EnterococcusSM 9223Result None 190 10 0 MR COAST 8 CSDO 05/10/05 9:13 Fecal ColiformSM 9221EResult None 3000 20 YesR COAST 8 CRW 05/10/05 9:14 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 8 CSDO 05/10/05 9:13 Total ColiformSM 9221BResult None 110000 20 YesOC04-05 DataPage 2 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 8 CRW 05/10/05 9:14 Total ColiformSM 9221BResult None 500 20 0 MR COAST 21 CSDO 05/24/05 10:40 EnterococcusSM 9223Result None 20 10 NoR COAST 21 CRW 05/24/05 10:41 EnterococcusSM 9223Result < 10 10 0 MR COAST 21 CSDO 05/24/05 10:40 Fecal ColiformSM 9221EResult None 500 20 NoR COAST 21 CRW 05/24/05 10:41 Fecal ColiformSM 9221EResult None 20 20 0 MR COAST 21 CSDO 05/24/05 10:40 Total ColiformSM 9221BResult None 800 20 NoR COAST 21 CRW 05/24/05 10:41 Total ColiformSM 9221BResult None 20 20 0 MR COAST 8 CSDO 05/24/05 9:35 EnterococcusSM 9223Result None 210 10 YesR COAST 8 CRW 05/24/05 9:36 EnterococcusSM 9223Result None 10 10 0 MR COAST 8 CSDO 05/24/05 9:35 Fecal ColiformSM 9221EResult None 30000 20 YesR COAST 8 CRW 05/24/05 9:36 Fecal ColiformSM 9221EResult None 220 20 0 MR COAST 8 CSDO 05/24/05 9:35 Total ColiformSM 9221BResult None 50000 20 YesR COAST 8 CRW 05/24/05 9:36 Total ColiformSM 9221BResult None 500 20 0 MR COAST 8 CSDO 06/07/05 9:10 EnterococcusSM 9223Result None 210 10 YesR COAST 8 CRW 06/07/05 9:11 EnterococcusSM 9223Result None 10 10 0 MR COAST 8 CSDO 06/07/05 9:10 Fecal ColiformSM 9221EResult None 50000 20 YesR COAST 8 CRW 06/07/05 9:11 Fecal ColiformSM 9221EResult None 170 20 0 MR COAST 8 CSDO 06/07/05 9:10 Total ColiformSM 9221BResult None 130000 20 YesR COAST 8 CRW 06/07/05 9:11 Total ColiformSM 9221BResult None 300 20 0 MR COAST 8 CSDO 06/21/05 9:18 EnterococcusSM 9223Result None 290 10 YesR COAST 8 CRW 06/21/05 9:19 EnterococcusSM 9223Result < 10 10 0 MR COAST 8 CSDO 06/21/05 9:18 Fecal ColiformSM 9221EResult None 7000 20 YesR COAST 8 CRW 06/21/05 9:19 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 8 CSDO 06/21/05 9:18 Total ColiformSM 9221BResult None 300000 20 YesR COAST 8 CRW 06/21/05 9:19 Total ColiformSM 9221BResult None 230 20 0 MR COAST 8 CSDO 07/05/05 9:35 EnterococcusSM 9223Result None 6520 10 YesR COAST 8 CRW 07/05/05 9:36 EnterococcusSM 9223Result None 120 10 0 MR COAST 8 CSDO 07/05/05 9:35 Fecal ColiformSM 9221EResult None 50000 20 YesR COAST 8 CRW 07/05/05 9:36 Fecal ColiformSM 9221EResult None 500 20 0 MR COAST 8 CSDO 07/05/05 9:35 Total ColiformSM 9221BResult > 1600000 20 YesR COAST 8 CRW 07/05/05 9:36 Total ColiformSM 9221BResult None 30000 20 0 MR COAST 8 CSDO 07/19/05 9:22 EnterococcusSM 9223Result None 210 10 YesR COAST 8 CRW 07/19/05 9:28 EnterococcusSM 9223Result None 70 10 0 MR COAST 8 CSDO 07/19/05 9:22 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 8 CRW 07/19/05 9:28 Fecal ColiformSM 9221EResult None 170 20 0 MR COAST 8 CSDO 07/19/05 9:22 Total ColiformSM 9221BResult None 500000 20 YesR COAST 8 CRW 07/19/05 9:28 Total ColiformSM 9221BResult None 5000 20 0 MOC04-05 DataPage 3 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 8 CSDO 08/02/05 9:40 EnterococcusSM 9223Result None 590 10 YesR COAST 8 CRW 08/02/05 9:42 EnterococcusSM 9223Result None 31 10 0 MR COAST 8 CSDO 08/02/05 9:40 Fecal ColiformSM 9221EResult None 130000 20 YesR COAST 8 CRW 08/02/05 9:42 Fecal ColiformSM 9221EResult None 500 20 0 MR COAST 8 CSDO 08/02/05 9:40 Total ColiformSM 9221BResult None 220000 20 YesR COAST 8 CRW 08/02/05 9:42 Total ColiformSM 9221BResult None 800 20 0 MR COAST 8 CSDO 08/16/05 9:50 EnterococcusSM 9223Result None 340 10 YesR COAST 8 CRW 08/16/05 9:51 EnterococcusSM 9223Result None 10 10 0 MR COAST 8 CSDO 08/16/05 9:50 Fecal ColiformSM 9221EResult None 8000 20 YesR COAST 8 CRW 08/16/05 9:51 Fecal ColiformSM 9221EResult None 140 20 0 MR COAST 8 CSDO 08/16/05 9:50 Total ColiformSM 9221BResult None 130000 20 YesR COAST 8 CRW 08/16/05 9:51 Total ColiformSM 9221BResult None 2300 20 0 MR COAST 8 CSDO 08/30/05 10:08 EnterococcusSM 9223Result None 270 10 YesR COAST 8 CRW 08/30/05 10:10 EnterococcusSM 9223Result None 10 10 0 MR COAST 8 CSDO 08/30/05 10:08 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 8 CRW 08/30/05 10:10 Fecal ColiformSM 9221EResult None 40 20 0 MR COAST 8 CSDO 08/30/05 10:08 Total ColiformSM 9221BResult None 50000 20 YesR COAST 8 CRW 08/30/05 10:10 Total ColiformSM 9221BResult None 80 20 0 MR COAST 8 CSDO 09/13/05 9:38 EnterococcusSM 9223Result None 240 10 YesR COAST 8 CRW 09/13/05 9:39 EnterococcusSM 9223Result None 10 10 0 MR COAST 8 CSDO 09/13/05 9:38 Fecal ColiformSM 9221EResult None 17000 20 YesR COAST 8 CRW 09/13/05 9:39 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 8 CSDO 09/13/05 9:38 Total ColiformSM 9221BResult None 140000 20 YesR COAST 8 CRW 09/13/05 9:39 Total ColiformSM 9221BResult None 230 20 0 MR COAST 8 CSDO 09/27/05 11:05 EnterococcusSM 9223Result None 51 10 YesR COAST 8 CRW 09/27/05 11:06 EnterococcusSM 9223Result < 10 10 0 MR COAST 8 CSDO 09/27/05 11:05 Fecal ColiformSM 9221EResult None 80000 20 YesR COAST 8 CRW 09/27/05 11:06 Fecal ColiformSM 9221EResult None 20 20 0 MR COAST 8 CSDO 09/27/05 11:05 Total ColiformSM 9221BResult None 80000 20 YesR COAST 8 CRW 09/27/05 11:06 Total ColiformSM 9221BResult None 230 20 0 MR COAST 14 CSDO 10/11/05 9:55 EnterococcusSM 9223Result None 2170 10 YesR COAST 14 CRW 10/11/05 9:56 EnterococcusSM 9223Result < 10 10 0 MR COAST 14 CSDO 10/11/05 9:55 Fecal ColiformSM 9221EResult None 7000 20 YesR COAST 14 CRW 10/11/05 9:56 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 14 CSDO 10/11/05 9:55 Total ColiformSM 9221BResult None 500000 20 YesR COAST 14 CRW 10/11/05 9:56 Total ColiformSM 9221BResult None 20 20 0 MR COAST 8 CSDO 10/11/05 9:15 EnterococcusSM 9223Result None 75 10 YesOC04-05 DataPage 4 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 8 CRW 10/11/05 9:16 EnterococcusSM 9223Result < 10 10 0 MR COAST 8 CSDO 10/11/05 9:15 Fecal ColiformSM 9221EResult None 17000 20 YesR COAST 8 CRW 10/11/05 9:16 Fecal ColiformSM 9221EResult None 130 20 0 MR COAST 8 CSDO 10/11/05 9:15 Total ColiformSM 9221BResult None 50000 20 YesR COAST 8 CRW 10/11/05 9:16 Total ColiformSM 9221BResult None 2300 20 0 MR COAST 14 CSDO 10/25/05 11:05 EnterococcusSM 9223Result None 10400 10 YesR COAST 14 CRW 10/25/05 11:06 EnterococcusSM 9223Result < 10 10 0 MR COAST 14 CSDO 10/25/05 11:05 Fecal ColiformSM 9221EResult None 11000 20 YesR COAST 14 CRW 10/25/05 11:06 Fecal ColiformSM 9221EResult None 90 20 0 MR COAST 14 CSDO 10/25/05 11:05 Total ColiformSM 9221BResult None 80000 20 YesR COAST 14 CRW 10/25/05 11:06 Total ColiformSM 9221BResult None 90 20 0 MR COAST 18 CSDO 10/25/05 12:11 EnterococcusSM 9223Result None 1060 10 YesR COAST 18 CRW 10/25/05 12:34 EnterococcusSM 9223Result < 10 10 0 MR COAST 18 CSDO 10/25/05 12:11 Fecal ColiformSM 9221EResult None 1300 20 YesR COAST 18 CRW 10/25/05 12:34 Fecal ColiformSM 9221EResult < 20 20 0 MR COAST 18 CSDO 10/25/05 12:11 Total ColiformSM 9221BResult None 13000 20 YesR COAST 18 CRW 10/25/05 12:34 Total ColiformSM 9221BResult < 20 20 0 MR COAST 8 CSDO 10/25/05 10:10 EnterococcusSM 9223Result None 1000 10 YesR COAST 8 CRW 10/25/05 10:15 EnterococcusSM 9223Result None 20 10 0 MR COAST 8 CSDO 10/25/05 10:10 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 8 CRW 10/25/05 10:15 Fecal ColiformSM 9221EResult None 40 20 0 MR COAST 8 CSDO 10/25/05 10:10 Total ColiformSM 9221BResult None 170000 20 YesR COAST 8 CRW 10/25/05 10:15 Total ColiformSM 9221BResult None 300 20 0 MOC04-05 DataPage 5 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 20-1 LSDO 11/16/04 10:22 EnterococcusSM 9223Result None 1790 10 YesR COAST 20-1 LSDO 11/16/04 10:22 Fecal ColiformSM 9221EResult None 70 20 YesR COAST 20-1 LSDO 11/16/04 10:22 Total ColiformSM 9221BResult None 30000 20 YesR COAST 20-2 LSDO 11/16/04 10:25 EnterococcusSM 9223Result None 3600 10 YesR COAST 20-2 LSDO 11/16/04 10:25 Fecal ColiformSM 9221EResult None 20 20 YesR COAST 20-2 LSDO 11/16/04 10:25 Total ColiformSM 9221BResult None 3600 20 YesR COAST 20-3 LRW 11/16/04 10:30 EnterococcusSM 9223Result None 800 10 0 MR COAST 20-3 LRW 11/16/04 10:30 Fecal ColiformSM 9221EResult None 500 20 0 MR COAST 20-3 LRW 11/16/04 10:30 Total ColiformSM 9221BResult None 8000 20 0 MR COAST 20-1 LSDO 12/14/04 10:39 EnterococcusSM 9223Result None 720 10 YesR COAST 20-1 LSDO 12/14/04 10:39 Fecal ColiformSM 9221EResult None 400 20 YesR COAST 20-1 LSDO 12/14/04 10:39 Total ColiformSM 9221BResult None 46000 20 YesR COAST 20-2 LSDO 12/14/04 10:41 EnterococcusSM 9223Result None 88 10 YesR COAST 20-2 LSDO 12/14/04 10:41 Fecal ColiformSM 9221EResult None 40 20 YesR COAST 20-2 LSDO 12/14/04 10:41 Total ColiformSM 9221BResult None 1700 20 YesR COAST 20-3 LRW 12/14/04 10:43 EnterococcusSM 9223Result None 640 10 0 MR COAST 20-3 LRW 12/14/04 10:43 Fecal ColiformSM 9221EResult None 230 20 0 MR COAST 20-3 LRW 12/14/04 10:43 Total ColiformSM 9221BResult None 30000 20 0 MR COAST 20-1 LSDO 01/18/05 10:44 EnterococcusSM 9223Result None 280 10 YesR COAST 20-1 LSDO 01/18/05 10:44 Fecal ColiformSM 9221EResult None 110 20 YesR COAST 20-1 LSDO 01/18/05 10:44 Total ColiformSM 9221BResult None 17500 20 YesR COAST 20-2 LSDO 01/18/05 10:45 EnterococcusSM 9223Result None 10 10 YesR COAST 20-2 LSDO 01/18/05 10:45 Fecal ColiformSM 9221EResult None 170 20 YesR COAST 20-2 LSDO 01/18/05 10:45 Total ColiformSM 9221BResult None 2300 20 YesR COAST 20-3 LRW 01/18/05 10:50 EnterococcusSM 9223Result None 170 10 0 MR COAST 20-3 LRW 01/18/05 10:50 Fecal ColiformSM 9221EResult None 800 20 0 MR COAST 20-3 LRW 01/18/05 10:50 Total ColiformSM 9221BResult None 50000 20 0 MR COAST 20-1 LSDO 02/08/05 10:10 EnterococcusSM 9223Result None 200 10 YesR COAST 20-1 LSDO 02/08/05 10:10 Fecal ColiformSM 9221EResult None 800 20 YesR COAST 20-1 LSDO 02/08/05 10:10 Total ColiformSM 9221BResult None 15000 20 YesR COAST 20-2 LSDO 02/08/05 10:12 EnterococcusSM 9223Result None 31 10 YesR COAST 20-2 LSDO 02/08/05 10:12 Fecal ColiformSM 9221EResult None 40 20 YesR COAST 20-2 LSDO 02/08/05 10:12 Total ColiformSM 9221BResult None 2200 20 YesR COAST 20-3 LRW 02/08/05 10:15 EnterococcusSM 9223Result None 183 10 0 MR COAST 20-3 LRW 02/08/05 10:15 Fecal ColiformSM 9221EResult None 500 20 0 MR COAST 20-3 LRW 02/08/05 10:15 Total ColiformSM 9221BResult None 17000 20 0 MR COAST 20-1 LSDO 03/08/05 9:58 EnterococcusSM 9223Result None 1590 10 YesOC04-05 DataPage 6 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 20-1 LSDO 03/08/05 9:58 Fecal ColiformSM 9221EResult None 170 20 YesR COAST 20-1 LSDO 03/08/05 9:58 Total ColiformSM 9221BResult None 23000 20 YesR COAST 20-2 LSDO 03/08/05 10:01 EnterococcusSM 9223Result < 10 10 YesR COAST 20-2 LSDO 03/08/05 10:01 Fecal ColiformSM 9221EResult < 20 20 YesR COAST 20-2 LSDO 03/08/05 10:01 Total ColiformSM 9221BResult None 1300 20 YesR COAST 20-3 LRW 03/08/05 10:10 EnterococcusSM 9223Result None 2100 10 0 MR COAST 20-3 LRW 03/08/05 10:10 Fecal ColiformSM 9221EResult None 2300 20 0 MR COAST 20-3 LRW 03/08/05 10:10 Total ColiformSM 9221BResult None 2300 20 0 MR COAST 20-1 LSDO 04/12/05 11:40 EnterococcusSM 9223Result None 1000 10 YesR COAST 20-1 LSDO 04/12/05 11:40 Fecal ColiformSM 9221EResult None 800 20 YesR COAST 20-1 LSDO 04/12/05 11:40 Total ColiformSM 9221BResult None 14000 20 YesR COAST 20-2 LSDO 04/12/05 11:41 EnterococcusSM 9223Result None 10 10 YesR COAST 20-2 LSDO 04/12/05 11:41 Fecal ColiformSM 9221EResult None 40 20 YesR COAST 20-2 LSDO 04/12/05 11:41 Total ColiformSM 9221BResult None 3000 20 YesR COAST 20-3 LRW 04/12/05 11:59 EnterococcusSM 9223Result None 170 10 0 MR COAST 20-3 LRW 04/12/05 11:59 Fecal ColiformSM 9221EResult None 500 20 0 MR COAST 20-3 LRW 04/12/05 11:59 Total ColiformSM 9221BResult None 13000 20 0 MR COAST 20-1 LSDO 04/26/05 11:08 EnterococcusSM 9223Result None 680 10 YesR COAST 20-1 LSDO 04/26/05 11:08 Fecal ColiformSM 9221EResult None 650 20 YesR COAST 20-1 LSDO 04/26/05 11:08 Total ColiformSM 9221BResult None 15000 20 YesR COAST 20-3 LRW 04/26/05 11:15 EnterococcusSM 9223Result None 550 10 0 MR COAST 20-3 LRW 04/26/05 11:15 Fecal ColiformSM 9221EResult None 1700 20 0 MR COAST 20-3 LRW 04/26/05 11:15 Total ColiformSM 9221BResult None 30000 20 0 MR COAST 20-1 LSDO 05/10/05 10:55 EnterococcusSM 9223Result None 980 10 YesR COAST 20-1 LSDO 05/10/05 10:55 Fecal ColiformSM 9221EResult None 1700 20 YesR COAST 20-1 LSDO 05/10/05 10:55 Total ColiformSM 9221BResult None 22000 20 YesR COAST 20-3 LRW 05/10/05 11:05 EnterococcusSM 9223Result None 370 10 0 MR COAST 20-3 LRW 05/10/05 11:05 Fecal ColiformSM 9221EResult None 300 20 0 MR COAST 20-3 LRW 05/10/05 11:05 Total ColiformSM 9221BResult None 29000 20 0 MF COAST 20-1 LSDO 05/17/05 9:19 EnterococcusSM 9223Result None 390 10 YesF COAST 20-1 LSDO 05/17/05 9:19 Fecal ColiformSM 9221EResult None 5000 20 YesF COAST 20-1 LSDO 05/17/05 9:19 Total ColiformSM 9221BResult None 50000 20 YesR COAST 20-1 LSDO 05/24/05 11:43 EnterococcusSM 9223Result None 640 10 YesR COAST 20-1 LSDO 05/24/05 11:43 Fecal ColiformSM 9221EResult None 4000 20 YesR COAST 20-1 LSDO 05/24/05 11:43 Total ColiformSM 9221BResult None 9000 20 YesR COAST 20-2 LSDO 05/24/05 11:44 EnterococcusSM 9223Result < 10 10 YesR COAST 20-2 LSDO 05/24/05 11:44 Fecal ColiformSM 9221EResult None 300 20 YesOC04-05 DataPage 7 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 20-2 LSDO 05/24/05 11:44 Total ColiformSM 9221BResult None 4300 20 YesR COAST 20-3 LRW 05/24/05 11:55 EnterococcusSM 9223Result None 340 10 0 MR COAST 20-3 LRW 05/24/05 11:55 Fecal ColiformSM 9221EResult None 2000 20 0 MR COAST 20-3 LRW 05/24/05 11:55 Total ColiformSM 9221BResult None 12000 20 0 MF COAST 20-1 LSDO 06/01/05 9:15 EnterococcusSM 9223Result None 8850 10 YesF COAST 20-1 LSDO 06/01/05 9:15 Fecal ColiformSM 9221EResult None 35000 20 YesF COAST 20-1 LSDO 06/01/05 9:15 Total ColiformSM 9221BResult None 240000 20 YesR COAST 20-1 LSDO 06/07/05 10:40 EnterococcusSM 9223Result None 2620 10 YesR COAST 20-1 LSDO 06/07/05 10:40 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 20-1 LSDO 06/07/05 10:40 Total ColiformSM 9221BResult None 30000 20 YesR COAST 20-2 LSDO 06/07/05 10:41 EnterococcusSM 9223Result None 92 10 YesR COAST 20-2 LSDO 06/07/05 10:41 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 20-2 LSDO 06/07/05 10:41 Total ColiformSM 9221BResult None 7000 20 YesR COAST 20-3 LRW 06/07/05 10:55 EnterococcusSM 9223Result None 1000 10 0 MR COAST 20-3 LRW 06/07/05 10:55 Fecal ColiformSM 9221EResult None 6500 20 0 MR COAST 20-3 LRW 06/07/05 10:55 Total ColiformSM 9221BResult None 65000 20 0 MR COAST 20-1 LSDO 06/21/05 10:50 EnterococcusSM 9223Result None 790 10 YesR COAST 20-1 LSDO 06/21/05 10:50 Fecal ColiformSM 9221EResult None 700 20 YesR COAST 20-1 LSDO 06/21/05 10:50 Total ColiformSM 9221BResult None 21000 20 YesR COAST 20-2 LSDO 06/21/05 10:51 EnterococcusSM 9223Result None 960 10 YesR COAST 20-2 LSDO 06/21/05 10:51 Fecal ColiformSM 9221EResult None 2300 20 YesR COAST 20-2 LSDO 06/21/05 10:51 Total ColiformSM 9221BResult None 2300 20 YesR COAST 20-3 LRW 06/21/05 10:58 EnterococcusSM 9223Result None 5200 10 0 MR COAST 20-3 LRW 06/21/05 10:58 Fecal ColiformSM 9221EResult None 4000 20 0 MR COAST 20-3 LRW 06/21/05 10:58 Total ColiformSM 9221BResult None 90000 20 0 MR COAST 20-1 LSDO 07/05/05 11:15 EnterococcusSM 9223Result None 1460 10 YesR COAST 20-1 LSDO 07/05/05 11:15 Fecal ColiformSM 9221EResult None 1100 20 YesR COAST 20-1 LSDO 07/05/05 11:15 Total ColiformSM 9221BResult None 8000 20 YesR COAST 20-2 LSDO 07/05/05 11:16 EnterococcusSM 9223Result None 290 10 YesR COAST 20-2 LSDO 07/05/05 11:16 Fecal ColiformSM 9221EResult None 230 20 YesR COAST 20-2 LSDO 07/05/05 11:16 Total ColiformSM 9221BResult None 800 20 YesR COAST 20-3 LRW 07/05/05 11:25 EnterococcusSM 9223Result None 1800 10 0 MR COAST 20-3 LRW 07/05/05 11:25 Fecal ColiformSM 9221EResult None 1100 20 0 MR COAST 20-3 LRW 07/05/05 11:25 Total ColiformSM 9221BResult None 15000 20 0 MR COAST 20-1 LSDO 07/19/05 11:05 EnterococcusSM 9223Result None 800 10 YesR COAST 20-1 LSDO 07/19/05 11:05 Fecal ColiformSM 9221EResult None 2300 20 YesR COAST 20-1 LSDO 07/19/05 11:05 Total ColiformSM 9221BResult None 30000 20 YesOC04-05 DataPage 8 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 20-2 LSDO 07/19/05 11:06 EnterococcusSM 9223Result None 70 10 YesR COAST 20-2 LSDO 07/19/05 11:06 Fecal ColiformSM 9221EResult None 900 20 YesR COAST 20-2 LSDO 07/19/05 11:06 Total ColiformSM 9221BResult None 6500 20 YesR COAST 20-3 LRW 07/19/05 11:15 EnterococcusSM 9223Result None 860 10 0 MR COAST 20-3 LRW 07/19/05 11:15 Fecal ColiformSM 9221EResult None 3000 20 0 MR COAST 20-3 LRW 07/19/05 11:15 Total ColiformSM 9221BResult None 13000 20 0 MR COAST 20-1 LSDO 08/02/05 11:11 EnterococcusSM 9223Result None 3270 10 YesR COAST 20-1 LSDO 08/02/05 11:11 Fecal ColiformSM 9221EResult None 9500 20 YesR COAST 20-1 LSDO 08/02/05 11:11 Total ColiformSM 9221BResult None 180000 20 YesR COAST 20-2 LSDO 08/02/05 11:12 EnterococcusSM 9223Result None 146 10 YesR COAST 20-2 LSDO 08/02/05 11:12 Fecal ColiformSM 9221EResult None 40 20 YesR COAST 20-2 LSDO 08/02/05 11:12 Total ColiformSM 9221BResult None 3000 20 YesR COAST 20-3 LRW 08/02/05 11:20 EnterococcusSM 9223Result None 1270 10 0 MR COAST 20-3 LRW 08/02/05 11:20 Fecal ColiformSM 9221EResult None 3000 20 0 MR COAST 20-3 LRW 08/02/05 11:20 Total ColiformSM 9221BResult None 13000 20 0 MR COAST 20-1 LSDO 08/16/05 11:44 EnterococcusSM 9223Result None 1520 10 YesR COAST 20-1 LSDO 08/16/05 11:44 Fecal ColiformSM 9221EResult None 2000 20 YesR COAST 20-1 LSDO 08/16/05 11:44 Total ColiformSM 9221BResult None 6500 20 YesR COAST 20-2 LSDO 08/16/05 11:45 EnterococcusSM 9223Result None 580 10 YesR COAST 20-2 LSDO 08/16/05 11:45 Fecal ColiformSM 9221EResult None 1300 20 YesR COAST 20-2 LSDO 08/16/05 11:45 Total ColiformSM 9221BResult None 23000 20 YesR COAST 20-3 LRW 08/16/05 11:52 EnterococcusSM 9223Result None 500 10 0 MR COAST 20-3 LRW 08/16/05 11:52 Fecal ColiformSM 9221EResult None 1300 20 0 MR COAST 20-3 LRW 08/16/05 11:52 Total ColiformSM 9221BResult None 13000 20 0 MR COAST 20-1 LSDO 08/30/05 11:44 EnterococcusSM 9223Result None 4200 10 YesR COAST 20-1 LSDO 08/30/05 11:44 Fecal ColiformSM 9221EResult None 1500 20 YesR COAST 20-1 LSDO 08/30/05 11:44 Total ColiformSM 9221BResult None 5200 20 YesR COAST 20-2 LSDO 08/30/05 11:45 EnterococcusSM 9223Result None 250 10 YesR COAST 20-2 LSDO 08/30/05 11:45 Fecal ColiformSM 9221EResult None 300 20 YesR COAST 20-2 LSDO 08/30/05 11:45 Total ColiformSM 9221BResult None 5000 20 YesR COAST 20-3 LRW 08/30/05 11:55 EnterococcusSM 9223Result None 480 10 0 MR COAST 20-3 LRW 08/30/05 11:55 Fecal ColiformSM 9221EResult None 300 20 0 MR COAST 20-3 LRW 08/30/05 11:55 Total ColiformSM 9221BResult None 3000 20 0 MR COAST 20-1 LSDO 09/13/05 11:04 EnterococcusSM 9223Result None 1700 10 YesR COAST 20-1 LSDO 09/13/05 11:04 Fecal ColiformSM 9221EResult None 4000 20 YesR COAST 20-1 LSDO 09/13/05 11:04 Total ColiformSM 9221BResult None 180000 20 YesR COAST 20-2 LSDO 09/13/05 11:05 EnterococcusSM 9223Result None 82 10 YesOC04-05 DataPage 9 of 133 Analytical Laboratory: San Luis ReyAnalytical Units: MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of OceansidePrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR COAST 20-2 LSDO 09/13/05 11:05 Fecal ColiformSM 9221EResult None 500 20 YesR COAST 20-2 LSDO 09/13/05 11:05 Total ColiformSM 9221BResult None 5000 20 YesR COAST 20-3 LRW 09/13/05 11:15 EnterococcusSM 9223Result None 160 10 0 MR COAST 20-3 LRW 09/13/05 11:15 Fecal ColiformSM 9221EResult None 300 20 0 MR COAST 20-3 LRW 09/13/05 11:15 Total ColiformSM 9221BResult None 1100 20 0 MR COAST 20-1 LSDO 09/27/05 12:25 EnterococcusSM 9223Result None 2300 10 YesR COAST 20-1 LSDO 09/27/05 12:25 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 20-1 LSDO 09/27/05 12:25 Total ColiformSM 9221BResult None 50000 20 YesR COAST 20-2 LSDO 09/27/05 12:26 EnterococcusSM 9223Result None 26 10 YesR COAST 20-2 LSDO 09/27/05 12:26 Fecal ColiformSM 9221EResult None 200 20 YesR COAST 20-2 LSDO 09/27/05 12:26 Total ColiformSM 9221BResult None 4000 20 YesR COAST 20-3 LRW 09/27/05 12:35 EnterococcusSM 9223Result None 500 10 0 MR COAST 20-3 LRW 09/27/05 12:35 Fecal ColiformSM 9221EResult None 8000 20 0 MR COAST 20-3 LRW 09/27/05 12:35 Total ColiformSM 9221BResult None 22000 20 0 MR COAST 20-1 LSDO 10/11/05 10:50 EnterococcusSM 9223Result None 550 10 YesR COAST 20-1 LSDO 10/11/05 10:50 Fecal ColiformSM 9221EResult None 800 20 YesR COAST 20-1 LSDO 10/11/05 10:50 Total ColiformSM 9221BResult None 5000 20 YesR COAST 20-2 LSDO 10/11/05 10:51 EnterococcusSM 9223Result None 72 10 YesR COAST 20-2 LSDO 10/11/05 10:51 Fecal ColiformSM 9221EResult None 850 20 YesR COAST 20-2 LSDO 10/11/05 10:51 Total ColiformSM 9221BResult None 5200 20 YesR COAST 20-3 LRW 10/11/05 11:00 EnterococcusSM 9223Result None 740 10 0 MR COAST 20-3 LRW 10/11/05 11:00 Fecal ColiformSM 9221EResult None 17000 20 0 MR COAST 20-3 LRW 10/11/05 11:00 Total ColiformSM 9221BResult None 50000 20 0 MR COAST 20-1 LSDO 10/25/05 13:01 EnterococcusSM 9223Result None 882 10 YesR COAST 20-1 LSDO 10/25/05 13:01 Fecal ColiformSM 9221EResult None 5000 20 YesR COAST 20-1 LSDO 10/25/05 13:01 Total ColiformSM 9221BResult None 23000 20 YesR COAST 20-2 LSDO 10/25/05 13:02 EnterococcusSM 9223Result None 470 10 YesR COAST 20-2 LSDO 10/25/05 13:02 Fecal ColiformSM 9221EResult None 300 20 YesR COAST 20-2 LSDO 10/25/05 13:02 Total ColiformSM 9221BResult None 3000 20 YesR COAST 20-3 LRW 10/25/05 13:11 EnterococcusSM 9223Result None 2700 10 0 MR COAST 20-3 LRW 10/25/05 13:11 Fecal ColiformSM 9221EResult None 23000 20 0 MR COAST 20-3 LRW 10/25/05 13:11 Total ColiformSM 9221BResult None 920000 20 0 MOC04-05 DataPage 10 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-475 CSDO11/01/0412:55 Enterococcus SM9230C Result None 1,000 20NoREH-475 CRW11/01/0413:00 Enterococcus SM9230C Result < 4475 LREH-475 CSDO11/01/0412:55 Fecal Coliform SM9222D Result None 6,000 20NoREH-475 CRW11/01/0413:00 Fecal Coliform SM9222D Result None 4475 LREH-475 CSDO11/01/0412:55 Total Coliform SM9222B Result None 30,000 20NoREH-475 CRW11/01/0413:00 Total Coliform SM9222B Result None 4475 LR EH-476CSDO03/17/05 10:15Total Coliform SM9222B Result None 33,800 20NoR EH-476CSDO03/17/05 10:15Fecal Coliform SM9222D Result None 19,000 20NoR EH-476CSDO03/17/05 10:15Enterococcus SM9230C Result None 3,850 20NoR EH-476CRW03/17/05 10:25Total Coliform SM9222B Result None 20475 LR EH-476CRW03/17/05 10:25Fecal Coliform SM9222D Result None 10475 LR EH-476CRW03/17/05 10:25Enterococcus SM9230C Result None 10475 LR EH-477CSDO03/17/05 10:40Total Coliform SM9222B Result None 17,000 20NoR EH-477CSDO03/17/05 10:40Fecal Coliform SM9222D Result None 12,450 20NoR EH-477CSDO03/17/05 10:40Enterococcus SM9230C Result None 23,800 20NoR EH-477CRW03/17/05 10:45Total Coliform SM9222B Result None 20475 LR EH-477CRW03/17/05 10:45Fecal Coliform SM9222D Result None 10475 LR EH-477CRW03/17/05 10:45Enterococcus SM9230C Result None 10475 LR EH-460 CRW 04/18/05 10:45Enterococcus SM9230C Result < 1010 75 LR EH-460 CSDO 04/18/05 10:35Enterococcus SM9230C Result None 1,800 20NoR EH-460 CRW 04/18/05 10:45Fecal Coliform SM9222D Result < 1010 75 LR EH-460 CSDO 04/18/05 10:35Fecal Coliform SM9222D Result None 3,350 20NoR EH-460 CRW 04/18/05 10:45Total Coliform SM9222B Result < 2020 75 LR EH-460 CSDO 04/18/05 10:35Total Coliform SM9222B Result None 16,900 20NoR EH-476 CRW 04/18/05 10:05Enterococcus SM9230C Result < 1010 75 LR EH-476 CSDO 04/18/05 9:50Enterococcus SM9230C Result None 3,400 20NoR EH-476 CSDO 04/18/05 9:50Fecal Coliform SM9222D Result None 35,050 20NoR EH-476 CRW 04/18/05 10:05Fecal Coliform SM9222D Result None 20475 LR EH-476 CSDO 04/18/05 9:50Total Coliform SM9222B Result None 73,600 20NoR EH-476 CRW 04/18/05 10:05Total Coliform SM9222B Result None 40475 LREH-475CRW 06/13/05 11:10Enterococcus SM9230C Result <101075 LREH-475CSDO 06/13/05 11:00Enterococcus SM9230C Result None 24,700 20NoREH-475CRW 06/13/05 11:10Fecal Coliform SM9222D Result <202075 LREH-475CSDO 06/13/05 11:00Fecal Coliform SM9222D Result None 2,400 20NoREH-475CSDO 06/13/05 11:00Total Coliform SM9222B Result None 29,800 20NoREH-475CRW 06/13/05 11:10Total Coliform SM9222B Result None60475 LREH-475CRW 06/27/05 10:40Enterococcus SM9230C Result <101075 LCA04-05 DataPage 11 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-475CSDO 06/27/05 10:35Enterococcus SM9230C Result None 12,800 20NoREH-475CRW 06/27/05 10:40Fecal Coliform SM9222D Result <202075 LREH-475CSDO 06/27/05 10:35Fecal Coliform SM9222D Result None 2,400 20NoREH-475CRW 06/27/05 10:40Total Coliform SM9222B Result <202075 LREH-475CSDO 06/27/05 10:35Total Coliform SM9222B Result None 48,200 20NoREH-475CRW 07/12/05 9:40Enterococcus SM9230C Result <101075 LREH-475CSDO 07/12/05 9:34Enterococcus SM9230C Result None 15,200 20NoREH-475CRW 07/12/05 9:40Fecal Coliform SM9222D Result <202075 LREH-475CSDO 07/12/05 9:34Fecal Coliform SM9222D Result None 1,800 20NoREH-475CRW 07/12/05 9:40Total Coliform SM9222B Result <202075 LREH-475CSDO 07/12/05 9:34Total Coliform SM9222B Result None 22,000 20NoR EH-470 CSDO 10/05/05 10:35Total Coliform SM9222B Result None23,400 20 NoR EH-470 CSDO 10/05/05 10:35Fecal Coliform SM9222D Result None12,800 20 NoR EH-470 CSDO 10/05/05 10:35Enterococcus SM9230C Result None7,800 20 NoR EH-470 CRW 10/05/05 10:45Total Coliform SM9222B Result None16 4 75 LR EH-470 CRW 10/05/05 10:45Fecal Coliform SM9222D Result <4 4 75 LR EH-470 CRW 10/05/05 10:45Enterococcus SM9230C Result <4 4 75 LCA04-05 DataPage 12 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-017LSDO11/01/0409:55 Total Coliform SM9222B Result None 3,600 20NoR BA-017LSDO11/01/0409:55 Fecal Coliform SM9222D Result None 750 20NoR BA-017LSDO11/01/0409:55 Enterococcus SM9230C Result None 350 20NoRAH-023 LSDO 11/02/04 09:00 Enterococcus SM9230C Result None 2,000 20 NoRAH-023 LSDO 11/02/04 09:00 Fecal Coliform SM9222D Result None 8,000 20 NoRAH-023 LSDO 11/02/04 09:00 Total Coliform SM9222B Result None 25,000 20 NoR BA-021LSDO 11/02/0409:40Enterococcus SM9230C Result None25020YesR BA-021LSDO 11/02/0409:40Fecal Coliform SM9222D Result None95020YesR BA-021LSDO 11/02/0409:40Total Coliform SM9222B Result None12,50020YesR BA-022LSDO 11/02/0410:05Enterococcus SM9230C Result None1,550 20 NoR BA-022LSDO 11/02/0410:05Fecal Coliform SM9222D Result None2,100 20 NoR BA-022LSDO 11/02/0410:05Total Coliform SM9222B Result None6,100 20 NoRAH-006 LSDO11/03/04 11:40Enterococcus SM9230C Result None9,90020YesRAH-006 LRW11/03/04 11:45Enterococcus SM9230C Result None14040MRAH-006 LSDO11/03/04 11:40Fecal Coliform SM9222D Result None10,70020YesRAH-006 LRW11/03/04 11:45Fecal Coliform SM9222D Result None24440MRAH-006 LSDO11/03/04 11:40Total Coliform SM9222B Result None27,00020YesRAH-006 LRW11/03/04 11:45Total Coliform SM9222B Result None40040MR AH-025LSDO11/03/0411:25 Enterococcus SM9230C Result None 950 20YesR AH-025LRW11/03/0411:30 Enterococcus SM9230C Result None 40 40MR AH-025LSDO11/03/0411:25 Fecal Coliform SM9222D Result None 2,800 20YesR AH-025LRW11/03/0411:30 Fecal Coliform SM9222D Result None 114 40MR AH-025LSDO11/03/0411:25 Total Coliform SM9222B Result None 4,500 20YesR AH-025LRW11/03/0411:30 Total Coliform SM9222B Result None 186 40MR BA-017LSDO12/13/0409:15 Enterococcus SM9230C Result None 50 20NoR BA-017LSDO12/13/0409:15 Fecal Coliform SM9222D Result None 150 20NoR BA-017LSDO12/13/0409:15 Total Coliform SM9222B Result None 1,000 20NoR BA-021 LSDO12/13/04 10:10 Enterococcus SM9230C Result None 5,500 20 YesR BA-021LRW 12/13/04 10:00 Enterococcus SM9230C Result None 116 4 0 MR BA-021 LSDO12/13/04 10:10 Fecal Coliform SM9222D Result None 4,900 20 YesR BA-021LRW 12/13/04 10:00 Fecal Coliform SM9222D Result None 140 4 0 MR BA-021 LSDO12/13/04 10:10 Total Coliform SM9222B Result None 5,800 20 YesR BA-021LRW 12/13/04 10:00 Total Coliform SM9222B Result None 248 4 0 MR BA-022LSDO 12/13/0410:30Enterococcus SM9230C Result None200 20 NoR BA-022LSDO 12/13/0410:30Fecal Coliform SM9222D Result None1,000 20 NoR BA-022LSDO 12/13/0410:30Total Coliform SM9222B Result None6,000 20 NoRAH-006 LSDO12/14/04 12:00Enterococcus SM9230C Result None70020YesCA04-05 DataPage 13 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterRAH-006 LRW12/14/04 12:05Enterococcus SM9230C Result None4840MRAH-006 LSDO12/14/04 12:00Fecal Coliform SM9222D Result None30020YesRAH-006 LRW12/14/04 12:05Fecal Coliform SM9222D Result None19640MRAH-006 LSDO12/14/04 12:00Total Coliform SM9222B Result None5,65020YesRAH-006 LRW12/14/04 12:05Total Coliform SM9222B Result None67640MR AH-025LSDO12/14/0411:10 Enterococcus SM9230C Result None 950 20YesR AH-025LRW12/14/0411:15 Enterococcus SM9230C Result None 40 40MR AH-025LSDO12/14/0411:10 Fecal Coliform SM9222D Result None 2,800 20YesR AH-025LRW12/14/0411:15 Fecal Coliform SM9222D Result None 114 40MR AH-025LSDO12/14/0411:10 Total Coliform SM9222B Result None 4,500 20YesR AH-025LRW12/14/0411:15 Total Coliform SM9222B Result None 186 40MRAH-023 LSDO 12/15/04 09:25 Enterococcus SM9230C Result None 200 20 NoRAH-023 LSDO 12/15/04 09:25 Fecal Coliform SM9222D Result None 400 20 NoRAH-023 LSDO 12/15/04 09:25 Total Coliform SM9222B Result None 4,000 20 NoRAH-19A LSDO 12/15/04 14:10 Enterococcus SM9230C Result None 150 20 YesR AH-19ALRW 12/15/04 14:15 Enterococcus SM9230C Result None 16 4 0 MRAH-19A LSDO 12/15/04 14:10 Fecal Coliform SM9222D Result None 250 20 YesR AH-19ALRW 12/15/04 14:15 Fecal Coliform SM9222D Result None 16 4 0 MR AH-19ALSDO 12/15/04 14:10 Total Coliform SM9222B Result None 800 20 YesR AH-19ALRW 12/15/04 14:15 Total Coliform SM9222B Result None 24 4 0 MRAH-006 LSDO01/19/05 10:15Enterococcus SM9230C Result None3,20020YesRAH-006 LRW01/19/05 10:05Enterococcus SM9230C Result None13240MRAH-006 LSDO01/19/05 10:15Fecal Coliform SM9222D Result None18,30020YesRAH-006 LRW01/19/05 10:05Fecal Coliform SM9222D Result None24040MRAH-006 LSDO01/19/05 10:15Total Coliform SM9222B Result None47,60020YesRAH-006 LRW01/19/05 10:05Total Coliform SM9222B Result None3,85040MR AH-011LSDO01/20/05 11:20Enterococcus SM9230C Result None1,250 20YesR AH-011LRW01/20/0511:25 Enterococcus SM9230C Result None 48 4 0 MR AH-011LSDO01/20/05 11:20Fecal Coliform SM9222D Result None500 20YesR AH-011LRW01/20/0511:25 Fecal Coliform SM9222D Result None 84 4 0 MR AH-011LSDO01/20/05 11:20Total Coliform SM9222B Result None3,500 20YesR AH-011LRW01/20/0511:25 Total Coliform SM9222B Result None 330 4 0 MR AH-022 LSDO01/20/05 10:51 Enterococcus SM9230C Result None 2,320 20 NoR AH-022 LSDO01/20/05 10:51 Fecal Coliform SM9222D Result None 2,500 20 NoR AH-022 LSDO01/20/05 10:51 Total Coliform SM9222B Result None 6,800 20 NoRAH-19A LSDO 01/20/05 11:05 Enterococcus SM9230C Result None 100 20 YesR AH-19ALRW 01/20/05 11:10 Enterococcus SM9230C Result None 48 4 0 MCA04-05 DataPage 14 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterRAH-19A LSDO 01/20/05 11:05 Fecal Coliform SM9222D Result None 250 20 YesR AH-19ALRW 01/20/05 11:10 Fecal Coliform SM9222D Result None 88 4 0 MR AH-19ALSDO 01/20/05 11:05 Total Coliform SM9222B Result None 2,300 20 YesR AH-19ALRW 01/20/05 11:10 Total Coliform SM9222B Result None 340 4 0 MRBA-001 LSDO 01/20/05 9:40 Enterococcus SM9230C Result None 50 20 NoRBA-001 LSDO 01/20/05 9:40 Fecal Coliform SM9222D Result None 700 20 NoRBA-001 LSDO 01/20/05 9:40 Total Coliform SM9222B Result None 3,500 20 NoR BA-017LSDO01/20/059:00 Enterococcus SM9230C Result None 50 20NoR BA-017LSDO01/20/059:00 Fecal Coliform SM9222D Result None 500 20NoR BA-017LSDO01/20/059:00 Total Coliform SM9222B Result None 3,900 20NoRBA-018 LSDO01/20/059:10 Enterococcus SM9230C Result None 2,000 20NoRBA-018 LSDO01/20/059:10 Fecal Coliform SM9222D Result None 10,000 20NoRBA-018 LSDO01/20/059:10 Total Coliform SM9222B Result None 17,400 20NoR BA-021 LSDO01/20/05 10:20 Enterococcus SM9230C Result None 40 20 NoR BA-021 LSDO01/20/05 10:20 Fecal Coliform SM9222D Result None 1,100 20 NoR BA-021 LSDO01/20/05 10:20 Total Coliform SM9222B Result None 1,800 20 NoR BA-022LSDO 01/20/0510:10Enterococcus SM9230C Result None100 20 NoR BA-022LSDO 01/20/0510:10Fecal Coliform SM9222D Result None400 20 NoR BA-022LSDO 01/20/0510:10Total Coliform SM9222B Result None8,400 20 NoRAH-023 LSDO 01/25/05 8:40 Enterococcus SM9230C Result None 650 20 NoRAH-023 LSDO 01/25/05 8:40 Fecal Coliform SM9222D Result None 2,000 20 NoRAH-023 LSDO 01/25/05 8:40 Total Coliform SM9222B Result None 3,200 20 NoR AH-025LSDO 01/25/05 9:40 Enterococcus SM9230C Result None 1,500 20YesR AH-025LRW 01/25/05 9:45 Enterococcus SM9230C Result None 68 40MR AH-025LSDO 01/25/05 9:40 Fecal Coliform SM9222D Result None 100 20YesR AH-025LRW 01/25/05 9:45 Fecal Coliform SM9222D Result None 82 40MR AH-025LSDO 01/25/05 9:40 Total Coliform SM9222B Result None 7,700 20YesR AH-025LRW 01/25/05 9:45 Total Coliform SM9222B Result None 166 40MR AH-022 LSDO02/03/05 10:30 Enterococcus SM9230C Result None 360 20 NoR AH-022 LSDO02/03/05 10:30 Fecal Coliform SM9222D Result None 1,100 20 NoR AH-022 LSDO02/03/05 10:30 Total Coliform SM9222B Result None 1,600 20 NoRAH-19A LSDO 02/03/05 10:10 Enterococcus SM9230C Result None 50 20 YesR AH-19ALRW 02/03/05 10:15 Enterococcus SM9230C Result None 192 4 0 MRAH-19A LSDO 02/03/05 10:10 Fecal Coliform SM9222D Result None 70 20 YesR AH-19ALRW 02/03/05 10:15 Fecal Coliform SM9222D Result None 80 4 0 MR AH-19ALSDO 02/03/05 10:10 Total Coliform SM9222B Result None 1,160 20 YesR AH-19ALRW 02/03/05 10:15 Total Coliform SM9222B Result None 292 4 0 MCA04-05 DataPage 15 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-021 LSDO02/03/059:30Enterococcus SM9230C Result None 560 20 NoR BA-021 LSDO02/03/059:30Fecal Coliform SM9222D Result None 360 20 NoR BA-021 LSDO02/03/059:30Total Coliform SM9222B Result None 1,100 20 NoR BA-022LSDO 02/03/059:15Enterococcus SM9230C Result None250 20 NoR BA-022LSDO 02/03/059:15Fecal Coliform SM9222D Result None1,400 20 NoR BA-022LSDO 02/03/059:15Total Coliform SM9222B Result None6,400 20 NoRAH-006 LSDO02/10/05 9:45Enterococcus SM9230C Result None90020YesRAH-006 LRW02/10/05 9:48Enterococcus SM9230C Result None5640MRAH-006 LSDO02/10/05 9:45Fecal Coliform SM9222D Result None50020YesRAH-006 LRW02/10/05 9:48Fecal Coliform SM9222D Result None10040MRAH-006 LSDO02/10/05 9:45Total Coliform SM9222B Result None80020YesRAH-006 LRW02/10/05 9:48Total Coliform SM9222B Result None32040MRAH-023 LSDO 02/10/05 11:30 Enterococcus SM9230C Result None 50 20 NoRAH-023 LSDO 02/10/05 11:30 Fecal Coliform SM9222D Result None 200 20 NoRAH-023 LSDO 02/10/05 11:30 Total Coliform SM9222B Result None 200 20 NoR AH-025LSDO 02/10/05 10:15 Enterococcus SM9230C Result None 200 20YesR AH-025LSDO 02/10/05 10:15 Fecal Coliform SM9222D Result None 50 20YesR AH-025LSDO 02/10/05 10:15 Total Coliform SM9222B Result None 1,700 20YesR BA-017LSDO02/10/05 12:00Enterococcus SM9230C Result None 20 20NoR BA-017LSDO02/10/05 12:00Fecal Coliform SM9222D Result < 20 20NoR BA-017LSDO02/10/05 12:00Total Coliform SM9222B Result None 200 20NoR AH-011LSDO03/10/05 10:45Enterococcus SM9230C Result None350 20YesR AH-011LRW03/10/0510:50 Enterococcus SM9230C Result None 40 4 0 MR AH-011LSDO03/10/05 10:45Fecal Coliform SM9222D Result None1,100 20YesR AH-011LRW03/10/0510:50 Fecal Coliform SM9222D Result None 80 4 0 MR AH-011LSDO03/10/05 10:45Total Coliform SM9222B Result None1,300 20YesR AH-011LRW03/10/0510:50 Total Coliform SM9222B Result None 300 4 0 MRAH-023 LSDO03/10/0511:25 Enterococcus SM9230C Result None 150 20 NoRAH-023 LSDO03/10/0511:25 Fecal Coliform SM9222D Result None 250 20 NoRAH-023 LSDO03/10/0511:25 Total Coliform SM9222B Result None 1,400 20 NoR BA-014 LSDO 03/10/05 9:25Enterococcus SM9230C Result None8020NoR BA-014 LSDO 03/10/05 9:25Fecal Coliform SM9222D Result None2020NoR BA-014 LSDO 03/10/05 9:25Total Coliform SM9222B Result None25020NoR BA-021 LSDO 03/10/05 10:10Enterococcus SM9230C Result None 180 20 NoR BA-021 LSDO 03/10/05 10:10Fecal Coliform SM9222D Result None 600 20 NoR BA-021 LSDO 03/10/05 10:10Total Coliform SM9222B Result None 500 20 NoR BA-022LSDO03/10/05 9:50Enterococcus SM9230C Result None380 20 NoCA04-05 DataPage 16 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-022LSDO03/10/05 9:50Fecal Coliform SM9222D Result None1,050 20 NoR BA-022LSDO03/10/05 9:50Total Coliform SM9222B Result None1,800 20 NoR AH-025LSDO03/16/0510:35 Enterococcus SM9230C Result None 60 20YesR AH-025LRW03/16/0510:45 Enterococcus SM9230C Result None 32 40MR AH-025LSDO03/16/0510:35 Fecal Coliform SM9222D Result None 1,660 20YesR AH-025LRW03/16/0510:45 Fecal Coliform SM9222D Result None 52 40MR AH-025LSDO03/16/0510:35 Total Coliform SM9222B Result None 850 20YesR AH-025LRW03/16/0510:45 Total Coliform SM9222B Result None 112 40MRAH-19A LSDO03/16/0510:10 Enterococcus SM9230C Result None 710 20 YesR AH-19ALRW03/16/0510:15 Enterococcus SM9230C Result None 16 4 0 MRAH-19A LSDO03/16/0510:10 Fecal Coliform SM9222D Result None 190 20 YesR AH-19ALRW03/16/0510:15 Fecal Coliform SM9222D Result None 16 4 0 MR AH-19ALSDO03/16/0510:10 Total Coliform SM9222B Result None 400 20 YesR AH-19ALRW03/16/0510:15 Total Coliform SM9222B Result None 52 4 0 MR BA-017LSDO03/16/05 8:50Enterococcus SM9230C Result None 140 20NoR BA-017LSDO03/16/05 8:50Fecal Coliform SM9222D Result None 70 20NoR BA-017LSDO03/16/05 8:50Total Coliform SM9222B Result None 350 20NoRBA-018 LSDO03/16/059:00 Enterococcus SM9230C Result None 100 20NoRBA-018 LSDO03/16/059:00 Fecal Coliform SM9222D Result None 200 20NoRBA-018 LSDO03/16/059:00 Total Coliform SM9222B Result None 200 20NoRAH-006 LSDO03/17/05 13:45Enterococcus SM9230C Result None60020YesRAH-006 LRW03/17/05 13:35Enterococcus SM9230C Result None5640MRAH-006 LSDO03/17/05 13:45Fecal Coliform SM9222D Result None80020YesRAH-006 LRW03/17/05 13:35Fecal Coliform SM9222D Result None440MRAH-006 LSDO03/17/05 13:45Total Coliform SM9222B Result None1,80020YesRAH-006 LRW03/17/05 13:35Total Coliform SM9222B Result None2040MRBA-001 LSDO 04/04/05 8:50 Enterococcus SM9230C Result None 150 20 NoRBA-001 LSDO 04/04/05 8:50 Fecal Coliform SM9222D Result None 100 20 NoRBA-001 LSDO 04/04/05 8:50 Total Coliform SM9222B Result None 2,000 20 NoR BA-014 LSDO04/04/059:10Enterococcus SM9230C Result None1020NoR BA-014 LSDO04/04/059:10Fecal Coliform SM9222D Result <2020NoR BA-014 LSDO04/04/059:10Total Coliform SM9222B Result None2020NoR BA-017LSDO04/05/05 9:40Enterococcus SM9230C Result None 10 20NoR BA-017LSDO04/05/05 9:40Fecal Coliform SM9222D Result None 10 20NoR BA-017LSDO04/05/05 9:40Total Coliform SM9222B Result None 240 20NoR BA-021 LSDO 04/05/0510:05 Enterococcus SM9230C Result None 310 20 NoR BA-021 LSDO 04/05/0510:05 Fecal Coliform SM9222D Result None 100 20 NoCA04-05 DataPage 17 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-021 LSDO 04/05/0510:05 Total Coliform SM9222B Result None 420 20 NoR BV-002 LSDO 04/05/05 10:25Enterococcus SM9230C Result None9,80020 NoR BV-002 LSDO 04/05/05 10:25Fecal Coliform SM9222D Result None22,80020 NoR BV-002 LSDO 04/05/05 10:25Total Coliform SM9222B Result None51,80020 NoRAH-006 LSDO04/14/05 8:50Enterococcus SM9230C Result None60020YesRAH-006 LRW04/14/05 8:55Enterococcus SM9230C Result None5240MRAH-006 LSDO04/14/05 8:50Fecal Coliform SM9222D Result None55020YesRAH-006 LRW04/14/05 8:55Fecal Coliform SM9222D Result None4440MRAH-006 LSDO04/14/05 8:50Total Coliform SM9222B Result None4,50020YesRAH-006 LRW04/14/05 8:55Total Coliform SM9222B Result None14040MR AH-025LSDO04/14/059:15 Enterococcus SM9230C Result None 40 20YesR AH-025LRW04/14/059:20 Enterococcus SM9230C Result None 4 40MR AH-025LSDO04/14/059:15 Fecal Coliform SM9222D Result None 30 20YesR AH-025LRW04/14/059:20 Fecal Coliform SM9222D Result None 60 40MR AH-025LSDO04/14/059:15 Total Coliform SM9222B Result None 700 20YesR AH-025LRW04/14/059:20 Total Coliform SM9222B Result None 80 40MRAH-19A LSDO04/14/058:00 Enterococcus SM9230C Result None 180 20 YesR AH-19ALRW04/14/058:05 Enterococcus SM9230C Result None 72 4 0 MRAH-19A LSDO04/14/058:00 Fecal Coliform SM9222D Result None 120 20 YesR AH-19ALRW04/14/058:05 Fecal Coliform SM9222D Result None 80 4 0 MR AH-19ALSDO04/14/058:00 Total Coliform SM9222B Result None 520 20 YesR AH-19ALRW04/14/058:05 Total Coliform SM9222B Result None 308 4 0 MR BV-002 LSDO 04/18/05 11:15Enterococcus SM9230C Result None5,80020 NoR BV-002 LSDO 04/18/05 11:15Fecal Coliform SM9222D Result None8,00020 NoR BV-002 LSDO 04/18/05 11:15Total Coliform SM9222B Result None54,60020 NoR AH-025LRW 04/19/05 14:10 Enterococcus SM9230C Result < 4 40MR AH-025LSDO 04/19/05 14:00 Enterococcus SM9230C Result None 20 20YesR AH-025LSDO 04/19/05 14:00 Fecal Coliform SM9222D Result None 180 20YesR AH-025LRW 04/19/05 14:10 Fecal Coliform SM9222D Result None 28 40MR AH-025LSDO 04/19/05 14:00 Total Coliform SM9222B Result None 740 20YesR AH-025LRW 04/19/05 14:10 Total Coliform SM9222B Result None 20 40MRAH-19A LSDO 04/19/05 13:40 Enterococcus SM9230C Result None 360 20 YesR AH-19ALRW 04/19/05 13:45 Enterococcus SM9230C Result None 4 4 0 MRAH-19A LSDO 04/19/05 13:40 Fecal Coliform SM9222D Result None 380 20 YesR AH-19ALRW 04/19/05 13:45 Fecal Coliform SM9222D Result None 40 4 0 MR AH-19ALSDO 04/19/05 13:40 Total Coliform SM9222B Result None 460 20 YesR AH-19ALRW 04/19/05 13:45 Total Coliform SM9222B Result None 16 4 0 MCA04-05 DataPage 18 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-014 LSDO04/19/0510:35Enterococcus SM9230C Result <2020NoR BA-014 LSDO04/19/0510:35Fecal Coliform SM9222D Result None1020NoR BA-014 LSDO04/19/0510:35Total Coliform SM9222B Result None8020NoR BA-017LSDO 04/19/0511:55Enterococcus SM9230C Result None 70 20NoR BA-017LSDO 04/19/0511:55Fecal Coliform SM9222D Result None 170 20NoR BA-017LSDO 04/19/0511:55Total Coliform SM9222B Result None 960 20NoR BA-021 LSDO04/19/05 11:30 Enterococcus SM9230C Result None 590 20 NoR BA-021 LSDO04/19/05 11:30 Fecal Coliform SM9222D Result None 510 20 NoR BA-021 LSDO04/19/05 11:30 Total Coliform SM9222B Result None 1,060 20 NoRAH-006 LSDO04/20/05 10:15Enterococcus SM9230C Result None1,06020YesRAH-006 LRW04/20/05 10:20Enterococcus SM9230C Result None3240MRAH-006 LSDO04/20/05 10:15Fecal Coliform SM9222D Result None1,82020YesRAH-006 LRW04/20/05 10:20Fecal Coliform SM9222D Result None7240MRAH-006 LSDO04/20/05 10:15Total Coliform SM9222B Result None3,65020YesRAH-006 LRW04/20/05 10:20Total Coliform SM9222B Result None12040MRAH-19A LSDO 05/02/05 11:15 Enterococcus SM9230C Result None 90 20 YesR AH-19ALRW 05/02/0511:20Enterococcus SM9230C Result None 4 4 0 MRAH-19A LSDO 05/02/05 11:15 Fecal Coliform SM9222D Result None 260 20 YesR AH-19ALRW 05/02/0511:20Fecal Coliform SM9222D Result None 100 4 0 MR AH-19ALSDO 05/02/05 11:15 Total Coliform SM9222B Result None 280 20 YesR AH-19ALRW 05/02/0511:20Total Coliform SM9222B Result None 12 4 0 MRBA-001 LSDO 05/02/05 10:15 Enterococcus SM9230C Result None 400 20 NoRBA-001 LSDO 05/02/05 10:15 Fecal Coliform SM9222D Result None 350 20 NoRBA-001 LSDO 05/02/05 10:15 Total Coliform SM9222B Result None 900 20 NoR BA-017LSDO 05/02/059:55Enterococcus SM9230C Result None 680 20NoR BA-017LSDO 05/02/059:55Fecal Coliform SM9222D Result None 770 20NoR BA-017LSDO 05/02/059:55Total Coliform SM9222B Result None 1,300 20NoR BA-021 LSDO05/02/05 10:35 Enterococcus SM9230C Result None 510 20 NoR BA-021 LSDO05/02/05 10:35 Fecal Coliform SM9222D Result None 300 20 NoR BA-021 LSDO05/02/05 10:35 Total Coliform SM9222B Result None 380 20 NoR BV-002 LSDO05/02/0511:55Enterococcus SM9230C Result None4,80020 NoR BV-002 LSDO05/02/0511:55Fecal Coliform SM9222D Result None39,00020 NoR BV-002 LSDO05/02/0511:55Total Coliform SM9222B Result None269,00020 NoRAH-006 LSDO05/03/05 9:20Enterococcus SM9230C Result None2,18020YesRAH-006 LRW05/03/05 9:25Enterococcus SM9230C Result None15240MRAH-006 LSDO05/03/05 9:20Fecal Coliform SM9222D Result None5,36020YesRAH-006 LRW05/03/05 9:25Fecal Coliform SM9222D Result None20040MCA04-05 DataPage 19 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterRAH-006 LSDO05/03/05 9:20Total Coliform SM9222B Result None9,90020YesRAH-006 LRW05/03/05 9:25Total Coliform SM9222B Result None35040MR AH-025LSDO05/03/059:55 Enterococcus SM9230C Result None 1,160 20YesR AH-025LRW05/03/0510:00 Enterococcus SM9230C Result None 8 40MR AH-025LSDO05/03/059:55 Fecal Coliform SM9222D Result None 1,250 20YesR AH-025LRW05/03/0510:00 Fecal Coliform SM9222D Result None 24 40MR AH-025LSDO05/03/059:55 Total Coliform SM9222B Result None 20 20YesR AH-025LRW05/03/0510:00 Total Coliform SM9222B Result None 12 40MRAH-19A LSDO 05/16/05 10:30 Enterococcus SM9230C Result None 60 20 YesR AH-19ALRW 05/16/05 10:35 Enterococcus SM9230C Result None 20 4 0 MRAH-19A LSDO 05/16/05 10:30 Fecal Coliform SM9222D Result None 120 20 YesR AH-19ALRW 05/16/05 10:35 Fecal Coliform SM9222D Result None 20 4 0 MR AH-19ALRW 05/16/05 10:35 Total Coliform SM9222B Result < 4 4 0 MR AH-19ALSDO 05/16/05 10:30 Total Coliform SM9222B Result None 10 20 YesRBA-001 LSDO 05/16/05 13:15 Enterococcus SM9230C Result None 100 20 NoRBA-001 LSDO 05/16/05 13:15 Fecal Coliform SM9222D Result None 200 20 NoRBA-001 LSDO 05/16/05 13:15 Total Coliform SM9222B Result None 2,400 20 NoR BA-021 LSDO05/16/05 13:30 Enterococcus SM9230C Result None 260 20 NoR BA-021 LSDO05/16/05 13:30 Fecal Coliform SM9222D Result None 200 20 NoR BA-021 LSDO05/16/05 13:30 Total Coliform SM9222B Result None 960 20 NoR BV-002 LSDO05/16/0511:00Enterococcus SM9230C Result None5,40020 NoR BV-002 LSDO05/16/0511:00Fecal Coliform SM9222D Result None3,80020 NoR BV-002 LSDO05/16/0511:00Total Coliform SM9222B Result None128,00020 NoR AH-022 LSDO05/31/05 10:30 Enterococcus SM9230C Result None 660 20 NoR AH-022 LSDO05/31/05 10:30 Fecal Coliform SM9222D Result None 1,080 20 NoR AH-022 LSDO05/31/05 10:30 Total Coliform SM9222B Result < 20 20 NoRAH-19A LSDO 05/31/05 10:15 Enterococcus SM9230C Result None 30 20 YesR AH-19ALRW 05/31/05 10:20 Enterococcus SM9230C Result None 80 4 0 MRAH-19A LSDO 05/31/05 10:15 Fecal Coliform SM9222D Result None 260 20 YesR AH-19ALRW 05/31/05 10:20 Fecal Coliform SM9222D Result None 508 4 0 MR AH-19ALSDO 05/31/05 10:15 Total Coliform SM9222B Result None 540 20 YesR AH-19ALRW 05/31/05 10:20 Total Coliform SM9222B Result None 204 4 0 MRBA-001 LSDO 05/31/05 8:45 Enterococcus SM9230C Result None 250 20 NoRBA-001 LSDO 05/31/05 8:45 Fecal Coliform SM9222D Result None 850 20 NoRBA-001 LSDO 05/31/05 8:45 Total Coliform SM9222B Result None 2,200 20 NoR BA-017LSDO 05/31/059:20Enterococcus SM9230C Result None 200 20NoR BA-017LSDO 05/31/059:20Fecal Coliform SM9222D Result None 1,220 20NoCA04-05 DataPage 20 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-017LSDO 05/31/059:20Total Coliform SM9222B Result None 960 20NoR BA-021 LSDO05/31/05 9:00 Enterococcus SM9230C Result None 370 20 NoR BA-021 LSDO05/31/05 9:00 Fecal Coliform SM9222D Result None 1,090 20 NoR BA-021 LSDO05/31/05 9:00 Total Coliform SM9222B Result None 1,100 20 NoR BV-002 LSDO05/31/0510:50Enterococcus SM9230C Result None4,20020 NoR BV-002 LSDO05/31/0510:50Fecal Coliform SM9222D Result None25,40020 NoR BV-002 LSDO05/31/0510:50Total Coliform SM9222B Result None86,00020 NoRAH-006 LSDO06/02/05 9:30Enterococcus SM9230C Result None2,14020YesRAH-006 LRW06/02/05 9:35Enterococcus SM9230C Result None19240MRAH-006 LSDO06/02/05 9:30Fecal Coliform SM9222D Result None84020YesRAH-006 LRW06/02/05 9:35Fecal Coliform SM9222D Result None18440MRAH-006 LSDO06/02/05 9:30Total Coliform SM9222B Result None9,70020YesRAH-006 LRW06/02/05 9:35Total Coliform SM9222B Result None25040MR AH-025LSDO06/02/059:05 Enterococcus SM9230C Result None 40 20YesR AH-025LRW06/02/059:10 Enterococcus SM9230C Result None 80 40MR AH-025LSDO06/02/059:05 Fecal Coliform SM9222D Result None 280 20YesR AH-025LRW06/02/059:10 Fecal Coliform SM9222D Result None 80 40MR AH-025LSDO06/02/059:05 Total Coliform SM9222B Result None 2,700 20YesR AH-025LRW06/02/059:10 Total Coliform SM9222B Result None 100 40MFAH-19A LSDO06/02/0511:50 Fecal Coliform SM9222D Result None 120 20 YesF AH-19ALRW06/02/0511:55 Fecal Coliform SM9222D Result None 620 4 0 MR AH-19A LSDO 06/14/05 8:55Enterococcus SM9230C Result None17020YesR AH-19A LRW 06/14/05 9:00Enterococcus SM9230C Result None4040MR AH-19A LRW 06/14/05 9:00Fecal Coliform SM9222D Result <20200MR AH-19A LSDO 06/14/05 8:55Fecal Coliform SM9222D Result None8020YesR AH-19A LSDO 06/14/05 8:55Total Coliform SM9222B Result <2020YesR AH-19A LRW 06/14/05 9:00Total Coliform SM9222B Result <20200MR BA-001 LSDO 06/14/05 10:40Enterococcus SM9230C Result None20020YesR BA-001 LSDO 06/14/05 10:40Fecal Coliform SM9222D Result None1,55020YesR BA-001 LSDO 06/14/05 10:40Total Coliform SM9222B Result None1,10020YesR BA-017LSDO06/14/05 9:55Enterococcus SM9230C Result None 1,220 20NoR BA-017LSDO06/14/05 9:55Fecal Coliform SM9222D Result None 3,220 20NoR BA-017LSDO06/14/05 9:55Total Coliform SM9222B Result None 1,880 20NoR BA-021 LSDO 06/14/05 11:05Enterococcus SM9230C Result None 2,160 20YesR BA-021 LSDO 06/14/05 11:05Fecal Coliform SM9222D Result None 1,240 20YesR BA-021 LSDO 06/14/05 11:05Total Coliform SM9222B Result None 2,200 20YesR AH-006 LRW 06/15/05 11:15Enterococcus SM9230C Result None2040MCA04-05 DataPage 21 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR AH-006 LSDO 06/15/05 11:10Enterococcus SM9230C Result None 3,600 20YesR AH-006 LRW 06/15/05 11:15Fecal Coliform SM9222D Result None1040MR AH-006 LSDO 06/15/05 11:10Fecal Coliform SM9222D Result None 10,550 20YesR AH-006 LRW 06/15/05 11:15Total Coliform SM9222B Result None5040MR AH-006 LSDO 06/15/05 11:10Total Coliform SM9222B Result None 10,900 20YesR AH-025 LSDO 06/15/05 1:20Enterococcus SM9230C Result None 160 20YesR AH-025 LRW 06/15/05 1:30Enterococcus SM9230C Result None440MR AH-025 LSDO 06/15/05 1:20Fecal Coliform SM9222D Result None 300 20YesR AH-025 LRW 06/15/05 1:30Fecal Coliform SM9222D Result None10040MR AH-025 LSDO 06/15/05 1:20Total Coliform SM9222B Result None 200 20YesR AH-025 LRW 06/15/05 1:30Total Coliform SM9222B Result None8840MR AH-006 LRW 06/27/05 13:45Enterococcus SM9230C Result None130040MR AH-006 LSDO 06/27/05 13:50Enterococcus SM9230C Result None 10 20YesR AH-006 LRW 06/27/05 13:45Fecal Coliform SM9222D Result None4,55040MR AH-006 LSDO 06/27/05 13:50Fecal Coliform SM9222D Result None 10 20YesR AH-006 LSDO 06/27/05 13:50Total Coliform SM9222B Result < 20 20YesR AH-006 LRW 06/27/05 13:45Total Coliform SM9222B Result None5,10040MR BA-001 LSDO 06/27/05 9:15Enterococcus SM9230C Result None 220 20YesR BA-001 LSDO 06/27/05 9:15Fecal Coliform SM9222D Result None 1,750 20YesR BA-001 LSDO 06/27/05 9:15Total Coliform SM9222B Result None 1,100 20YesR AH-017 LSDO 06/29/05 11:00Enterococcus SM9230C Result None 22,050 20NoR AH-017 LSDO 06/29/05 11:00Fecal Coliform SM9222D Result None 34,150 20NoR AH-017 LSDO 06/29/05 11:00Total Coliform SM9222B Result NA -99 20NoR AH-025 LSDO 06/29/05 10:15Enterococcus SM9230C Result None 420 20YesR AH-025 LRW 06/29/05 10:20Enterococcus SM9230C Result None7240MR AH-025 LSDO 06/29/05 10:15Fecal Coliform SM9222D Result None 1,070 20YesR AH-025 LRW 06/29/05 10:20Fecal Coliform SM9222D Result None4440MR AH-025 LRW 06/29/05 10:20Total Coliform SM9222B Result <440MR AH-025 LSDO 06/29/05 10:15Total Coliform SM9222B Result None 2,020 20YesR AH-19A LSDO 06/29/05 10:45Enterococcus SM9230C Result None3020YesR AH-19A LRW 06/29/05 10:50Enterococcus SM9230C Result None1040MR AH-19A LSDO 06/29/05 10:45Fecal Coliform SM9222D Result None4020YesR AH-19A LRW 06/29/05 10:50Fecal Coliform SM9222D Result None2040MR AH-19A LSDO 06/29/05 10:45Total Coliform SM9222B Result None8020YesR AH-19A LRW 06/29/05 10:50Total Coliform SM9222B Result None2040MR BA-017LSDO06/29/05 9:30Enterococcus SM9230C Result None 60 20NoR BA-017LSDO06/29/05 9:30Fecal Coliform SM9222D Result None 350 20NoCA04-05 DataPage 22 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-017LSDO06/29/05 9:30Total Coliform SM9222B Result None 780 20NoR BA-021 LSDO 06/29/05 10:00Enterococcus SM9230C Result None 4,850 20YesR BA-021 LSDO 06/29/05 10:00Fecal Coliform SM9222D Result None 3,850 20YesR BA-021 LSDO 06/29/05 10:00Total Coliform SM9222B Result None 4,500 20YesR BA-001 LSDO 07/12/05 11:40Enterococcus SM9230C Result None 420 20YesR BA-001 LSDO 07/12/05 11:40Fecal Coliform SM9222D Result None 440 20YesR BA-001 LSDO 07/12/05 11:40Total Coliform SM9222B Result None 950 20YesR BA-017LSDO07/12/05 14:05Enterococcus SM9230C Result None 380 20NoR BA-017LSDO07/12/05 14:05Fecal Coliform SM9222D Result None 150 20NoR BA-017LSDO07/12/05 14:05Total Coliform SM9222B Result None 1,450 20NoR BV-002 LSDO 07/12/05 10:50Enterococcus SM9230C Result None3,60020 NoR BV-002 LSDO 07/12/05 10:50Fecal Coliform SM9222D Result None1,40020 NoR BV-002 LSDO 07/12/05 10:50Total Coliform SM9222B Result None54,00020 NoR AH-006 LRW 07/13/05 13:50Enterococcus SM9230C Result <10100MR AH-006 LSDO 07/13/05 13:45Enterococcus SM9230C Result None 200 20YesR AH-006 LRW 07/13/05 13:50Fecal Coliform SM9222D Result <10100MR AH-006 LSDO 07/13/05 13:45Fecal Coliform SM9222D Result None 250 20YesR AH-006 LSDO 07/13/05 13:45Total Coliform SM9222B Result None 1,000 20YesR AH-006 LRW 07/13/05 13:50Total Coliform SM9222B Result None6040MR AH-017 LSDO 07/13/05 9:50Enterococcus SM9230C Result None 10,200 20NoR AH-017 LSDO 07/13/05 9:50Fecal Coliform SM9222D Result None 10,000 20NoR AH-017 LSDO 07/13/05 9:50Total Coliform SM9222B Result None 18,000 20NoR AH-020 LSDO 07/13/05 9:05Enterococcus SM9230C Result None 8,800 20NoR AH-020 LSDO 07/13/05 9:05Fecal Coliform SM9222D Result None 9,950 20NoR AH-020 LSDO 07/13/05 9:05Total Coliform SM9222B Result None 7,500 20NoR AH-19A LSDO 07/13/05 10:00Enterococcus SM9230C Result None15020YesR AH-19A LRW 07/13/05 10:00Enterococcus SM9230C Result None1040MR AH-19A LRW 07/13/05 10:00Fecal Coliform SM9222D Result <20200MR AH-19A LSDO 07/13/05 10:00Fecal Coliform SM9222D Result None22020YesR AH-19A LRW 07/13/05 10:00Total Coliform SM9222B Result <20200MR AH-19A LSDO 07/13/05 10:00Total Coliform SM9222B Result None30020YesR AH-025 LRW 07/14/05 11:05Enterococcus SM9230C Result <10100MR AH-025 LSDO 07/14/05 10:55Enterococcus SM9230C Result None 610 20YesR AH-025 LRW 07/14/05 11:05Fecal Coliform SM9222D Result <10100MR AH-025 LSDO 07/14/05 10:55Fecal Coliform SM9222D Result None 750 20YesR AH-025 LRW 07/14/05 11:05Total Coliform SM9222B Result None3040MR AH-025 LSDO 07/14/05 10:55Total Coliform SM9222B Result None 1,800 20YesCA04-05 DataPage 23 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-017LSDO07/14/05 9:56Enterococcus SM9230C Result None 700 20NoR BA-017LSDO07/14/05 9:56Fecal Coliform SM9222D Result None 960 20NoR BA-017LSDO07/14/05 9:56Total Coliform SM9222B Result None 2,100 20NoR BA-021 LSDO 07/14/05 10:30Enterococcus SM9230C Result None 2,300 20YesR BA-021 LSDO 07/14/05 10:30Fecal Coliform SM9222D Result None 4,900 20YesR BA-021 LSDO 07/14/05 10:30Total Coliform SM9222B Result None 3,900 20YesR AH-19A LSDO 07/26/05 9:55Enterococcus SM9230C Result None295020YesR AH-19A LRW 07/26/05 10:00Enterococcus SM9230C Result None28040MR AH-19A LSDO 07/26/05 9:55Fecal Coliform SM9222D Result None3,48020YesR AH-19A LRW 07/26/05 10:00Fecal Coliform SM9222D Result None44040MR AH-19A LSDO 07/26/05 9:55Total Coliform SM9222B Result <2020YesR AH-19A LRW 07/26/05 10:00Total Coliform SM9222B Result <20200MR BA-001 LSDO 07/26/05 9:10Enterococcus SM9230C Result None 920 20NoR BA-001 LSDO 07/26/05 9:10Fecal Coliform SM9222D Result None 1,160 20NoR BA-001 LSDO 07/26/05 9:10Total Coliform SM9222B Result None 600 20NoR BA-017LSDO07/26/05 8:45Enterococcus SM9230C Result None 350 20NoR BA-017LSDO07/26/05 8:45Fecal Coliform SM9222D Result None 1,220 20NoR BA-017LSDO07/26/05 8:45Total Coliform SM9222B Result None 1,750 20NoR BV-002 LSDO 07/26/05 10:50Enterococcus SM9230C Result None32,60020 NoR BV-002 LSDO 07/26/05 10:50Fecal Coliform SM9222D Result None33,80020 NoR BV-002 LSDO 07/26/05 10:50Total Coliform SM9222B Result None71,00020 NoR AH-006 LRW 07/27/05 14:20Enterococcus SM9230C Result None2040MR AH-006 LSDO 07/27/05 14:10Enterococcus SM9230C Result None 1,100 20YesR AH-006 LRW 07/27/05 14:20Fecal Coliform SM9222D Result None2040MR AH-006 LSDO 07/27/05 14:10Fecal Coliform SM9222D Result None 200 20YesR AH-006 LSDO 07/27/05 14:10Total Coliform SM9222B Result None 1,980 20YesR AH-006 LRW 07/27/05 14:20Total Coliform SM9222B Result None13040MR AH-025 LRW 07/27/05 10:00Enterococcus SM9230C Result <10100MR AH-025 LSDO 07/27/05 9:50Enterococcus SM9230C Result None 300 20YesR AH-025 LSDO 07/27/05 9:50Fecal Coliform SM9222D Result None 200 20YesR AH-025 LRW 07/27/05 10:00Fecal Coliform SM9222D Result None7040MR AH-025 LRW 07/27/05 10:00Total Coliform SM9222B Result <10100MR AH-025 LSDO 07/27/05 9:50Total Coliform SM9222B Result None 2,450 20YesR BA-021 LSDO 07/27/05 14:55Enterococcus SM9230C Result None 450 20YesR BA-021 LSDO 07/27/05 14:55Fecal Coliform SM9222D Result None 500 20YesR BA-021 LSDO 07/27/05 14:55Total Coliform SM9222B Result None 700 20YesR AH-025 LRW 08/08/05 14:45Enterococcus SM9230C Result <20200MCA04-05 DataPage 24 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR AH-025 LSDO 08/08/05 14:30Enterococcus SM9230C Result None 480 20YesR AH-025 LSDO 08/08/05 14:30Fecal Coliform SM9222D Result None 900 20YesR AH-025 LRW 08/08/05 14:45Fecal Coliform SM9222D Result None2040MR AH-025 LRW 08/08/05 14:45Total Coliform SM9222B Result <20200MR AH-025 LSDO 08/08/05 14:30Total Coliform SM9222B Result None 3,350 20YesR AH-19A LRW 08/08/05 8:35Enterococcus SM9230C Result <20200MR AH-19A LSDO 08/08/05 8:30Enterococcus SM9230C Result None294020YesR AH-19A LSDO 08/08/05 8:30Fecal Coliform SM9222D Result None78020YesR AH-19A LRW 08/08/05 8:35Fecal Coliform SM9222D Result None2040MR AH-19A LSDO 08/08/05 8:30Total Coliform SM9222B Result <2020YesR AH-19A LRW 08/08/05 8:35Total Coliform SM9222B Result None2040MR BA-001 LSDO 08/08/05 13:00Enterococcus SM9230C Result None 20 20NoR BA-001 LSDO 08/08/05 13:00Fecal Coliform SM9222D Result None 380 20NoR BA-001 LSDO 08/08/05 13:00Total Coliform SM9222B Result None 1,900 20NoR BA-017LSDO08/08/05 11:50Enterococcus SM9230C Result None 740 20NoR BA-017LSDO08/08/05 11:50Fecal Coliform SM9222D Result None 2,120 20NoR BA-017LSDO08/08/05 11:50Total Coliform SM9222B Result None 2,150 20NoR BA-021 LSDO 08/09/05 11:30Enterococcus SM9230C Result None 2,200 20YesR BA-021 LSDO 08/09/05 11:30Fecal Coliform SM9222D Result None 10,250 20YesR BA-021 LSDO 08/09/05 11:30Total Coliform SM9222B Result None 19,400 20YesR BV-002 LSDO 08/09/05 12:25Enterococcus SM9230C Result None4,60020 NoR BV-002 LSDO 08/09/05 12:25Fecal Coliform SM9222D Result None5,00020 NoR BV-002 LSDO 08/09/05 12:25Total Coliform SM9222B Result None38,60020 NoR AH-006 LRW 08/11/05 14:10Enterococcus SM9230C Result <20200MR AH-006 LSDO 08/11/05 14:05Enterococcus SM9230C Result None 2,200 20YesR AH-006 LRW 08/11/05 14:10Fecal Coliform SM9222D Result None2040MR AH-006 LSDO 08/11/05 14:05Fecal Coliform SM9222D Result None 1,250 20YesR AH-006 LRW 08/11/05 14:10Total Coliform SM9222B Result None2040MR AH-006 LSDO 08/11/05 14:05Total Coliform SM9222B Result None 5,600 20YesR AH-006 LRW 08/22/05 9:45Enterococcus SM9230C Result None8040MR AH-006 LSDO 08/22/05 9:40Enterococcus SM9230C Result None 2,000 20YesR AH-006 LRW 08/22/05 9:45Fecal Coliform SM9222D Result None8040MR AH-006 LSDO 08/22/05 9:40Fecal Coliform SM9222D Result None 3,250 20YesR AH-006 LRW 08/22/05 9:45Total Coliform SM9222B Result None22040MR AH-006 LSDO 08/22/05 9:40Total Coliform SM9222B Result None 3,700 20YesR BV-002 LSDO 08/22/05 9:20Enterococcus SM9230C Result None 21,600 20 NoR BV-002 LSDO 08/22/05 9:20Fecal Coliform SM9222D Result None 12,700 20 NoCA04-05 DataPage 25 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BV-002 LSDO 08/22/05 9:20Total Coliform SM9222B Result None 15,400 20 NoR AH-025 LRW 08/23/05 9:30Enterococcus SM9230C Result <10100MR AH-025 LSDO 08/23/05 9:20Enterococcus SM9230C Result None 1,000 20YesR AH-025 LRW 08/23/05 9:30Fecal Coliform SM9222D Result <10100MR AH-025 LSDO 08/23/05 9:20Fecal Coliform SM9222D Result None 420 20YesR AH-025 LSDO 08/23/05 9:20Total Coliform SM9222B Result None 1,500 20YesR AH-025 LRW 08/23/05 9:30Total Coliform SM9222B Result None3040MR AH-19A LSDO 08/23/05 8:18Enterococcus SM9230C Result None26020YesR AH-19A LRW 08/23/05 8:20Enterococcus SM9230C Result None38040MR AH-19A LSDO 08/23/05 8:18Fecal Coliform SM9222D Result None32020YesR AH-19A LRW 08/23/05 8:20Fecal Coliform SM9222D Result None1,88040MR AH-19A LSDO 08/23/05 8:18Total Coliform SM9222B Result <2020YesR AH-19A LRW 08/23/05 8:20Total Coliform SM9222B Result None20040MR BA-001 LSDO 08/23/05 8:50Enterococcus SM9230C Result None 220 20NoR BA-001 LSDO 08/23/05 8:50Fecal Coliform SM9222D Result None 200 20NoR BA-001 LSDO 08/23/05 8:50Total Coliform SM9222B Result None 3,100 20NoR BA-017LSDO08/23/05 10:00Enterococcus SM9230C Result None 340 20NoR BA-017LSDO08/23/05 10:00Fecal Coliform SM9222D Result None 1,180 20NoR BA-017LSDO08/23/05 10:00Total Coliform SM9222B Result None 400 20NoR BA-021 LSDO 08/23/05 9:05Enterococcus SM9230C Result None 3,450 20YesR BA-021 LSDO 08/23/05 9:05Fecal Coliform SM9222D Result None 5,250 20YesR BA-021 LSDO 08/23/05 9:05Total Coliform SM9222B Result None 5,700 20YesF AH-19A LSDO 08/25/05 8:10Enterococcus SM9230C Result None10020YesF AH-19A LRW 08/25/05 8:00Enterococcus SM9230C Result None25040MF AH-19A LSDO 08/25/05 8:10Fecal Coliform SM9222D Result None14020YesF AH-19A LRW 08/25/05 8:00Fecal Coliform SM9222D Result None30040MF AH-19A LSDO 08/25/05 8:10Total Coliform SM9222B Result <2020YesF AH-19A LRW 08/25/05 8:00Total Coliform SM9222B Result <20200MR BA-001 LSDO 09/06/05 8:45Enterococcus SM9230C Result None 180 20NoR BA-001 LSDO 09/06/05 8:45Fecal Coliform SM9222D Result None 140 20NoR BA-001 LSDO 09/06/05 8:45Total Coliform SM9222B Result None 1,200 20NoR BA-021 LSDO 09/06/05 9:10Enterococcus SM9230C Result None 2,700 20YesR BA-021 LSDO 09/06/05 9:10Fecal Coliform SM9222D Result None 1,950 20YesR BA-021 LSDO 09/06/05 9:10Total Coliform SM9222B Result None 4,700 20YesR BV-002 LSDO 09/06/05 11:00Enterococcus SM9230C Result None 7,000 20 NoR BV-002 LSDO 09/06/05 11:00Fecal Coliform SM9222D Result None 3,800 20 NoR BV-002 LSDO 09/06/05 11:00Total Coliform SM9222B Result None 29,000 20 NoCA04-05 DataPage 26 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR AH-025 LSDO 09/07/05 9:35Enterococcus SM9230C Result None 580 20YesR AH-025 LRW 09/07/05 9:45Enterococcus SM9230C Result None1040MR AH-025 LSDO 09/07/05 9:35Fecal Coliform SM9222D Result None 2,420 20YesR AH-025 LRW 09/07/05 9:45Fecal Coliform SM9222D Result None3040MR AH-025 LSDO 09/07/05 9:35Total Coliform SM9222B Result None 4,800 20YesR AH-025 LRW 09/07/05 9:45Total Coliform SM9222B Result None2040MR AH-19A LRW 09/07/05 9:15Enterococcus SM9230C Result <10100MR AH-19A LSDO 09/07/05 9:15Enterococcus SM9230C Result None18020YesR AH-19A LRW 09/07/05 9:15Fecal Coliform SM9222D Result <20200MR AH-19A LSDO 09/07/05 9:15Fecal Coliform SM9222D Result None30020YesR AH-19A LRW 09/07/05 9:15Total Coliform SM9222B Result <20200MR AH-19A LSDO 09/07/05 9:15Total Coliform SM9222B Result None10020YesR BA-017LSDO09/07/05 8:40Enterococcus SM9230C Result None 100 20NoR BA-017LSDO09/07/05 8:40Fecal Coliform SM9222D Result None 1,160 20NoR BA-017LSDO09/07/05 8:40Total Coliform SM9222B Result None 1,900 20NoR AH-006 LRW 09/08/05 11:35Enterococcus SM9230C Result None2040MR AH-006 LSDO 09/08/05 11:30Enterococcus SM9230C Result None 2,150 20YesR AH-006 LRW 09/08/05 11:35Fecal Coliform SM9222D Result <10100MR AH-006 LSDO 09/08/05 11:30Fecal Coliform SM9222D Result None 700 20YesR AH-006 LRW 09/08/05 11:35Total Coliform SM9222B Result None7040MR AH-006 LSDO 09/08/05 11:30Total Coliform SM9222B Result None 5,200 20YesR AH-006 LRW 09/28/05 11:40Enterococcus SM9230C Result None16040MR AH-006 LSDO 09/28/05 11:35Enterococcus SM9230C Result None 5,100 20YesR AH-006 LRW 09/28/05 11:40Fecal Coliform SM9222D Result None24040MR AH-006 LSDO 09/28/05 11:35Fecal Coliform SM9222D Result None 7,400 20YesR AH-006 LRW 09/28/05 11:40Total Coliform SM9222B Result None52040MR AH-006 LSDO 09/28/05 11:35Total Coliform SM9222B Result None 14,500 20YesR AH-025 LSDO 09/28/05 11:10Enterococcus SM9230C Result None 660 20YesR AH-025 LRW 09/28/05 11:20Enterococcus SM9230C Result None1040MR AH-025 LSDO 09/28/05 11:10Fecal Coliform SM9222D Result None 4,600 20YesR AH-025 LRW 09/28/05 11:20Fecal Coliform SM9222D Result None4040MR AH-025 LRW 09/28/05 11:20Total Coliform SM9222B Result <20200MR AH-025 LSDO 09/28/05 11:10Total Coliform SM9222B Result None 3,475 20YesR BA-001 LSDO 09/28/05 9:40Enterococcus SM9230C Result None 1,125 20NoR BA-001 LSDO 09/28/05 9:40Fecal Coliform SM9222D Result None 1,950 20NoR BA-001 LSDO 09/28/05 9:40Total Coliform SM9222B Result None 2,650 20NoR BA-017LSDO09/28/05 9:05Enterococcus SM9230C Result None 120 20NoCA04-05 DataPage 27 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR BA-017LSDO09/28/05 9:05Fecal Coliform SM9222D Result None 1,660 20NoR BA-017LSDO09/28/05 9:05Total Coliform SM9222B Result None 3,000 20NoR BA-021 LSDO 09/28/05 10:05Enterococcus SM9230C Result None 1,125 20YesR BA-021 LSDO 09/28/05 10:05Fecal Coliform SM9222D Result None 1,950 20YesR BA-021 LSDO 09/28/05 10:05Total Coliform SM9222B Result None 2,450 20YesR AH-19A LRW 10/03/05 2:45Enterococcus SM9230C Result <20200MR AH-19A LSDO 10/03/05 14:30Enterococcus SM9230C Result None14020YesR AH-19A LSDO 10/03/05 14:30Fecal Coliform SM9222D Result None46020YesR AH-19A LRW 10/03/05 2:45Fecal Coliform SM9222D Result None2040MR AH-19A LSDO 10/03/05 14:30Total Coliform SM9222B Result <2020YesR AH-19A LRW 10/03/05 2:45Total Coliform SM9222B Result None2040MR BA-001 LSDO 10/03/05 9:40Enterococcus SM9230C Result None 220 20YesR BA-001 LSDO 10/03/05 9:40Fecal Coliform SM9222D Result None 480 20YesR BA-001 LSDO 10/03/05 9:40Total Coliform SM9222B Result None 1,450 20YesR BA-017LSDO10/03/05 9:10Enterococcus SM9230C Result None 160 20NoR BA-017LSDO10/03/05 9:10Fecal Coliform SM9222D Result None 1,960 20NoR BA-017LSDO10/03/05 9:10Total Coliform SM9222B Result None 3,250 20NoR BA-021 LSDO 10/03/05 10:00Enterococcus SM9230C Result None 2,250 20YesR BA-021 LSDO 10/03/05 10:00Fecal Coliform SM9222D Result None 4,900 20YesR BA-021 LSDO 10/03/05 10:00Total Coliform SM9222B Result None 4,600 20YesR BV-002 LSDO 10/03/05 10:55Enterococcus SM9230C Result None15,20020 NoR BV-002 LSDO 10/03/05 10:55Fecal Coliform SM9222D Result None44,00020 NoR BV-002 LSDO 10/03/05 10:55Total Coliform SM9222B Result None98,00020 NoR AH-025 LRW 10/04/05 11:20Enterococcus SM9230C Result <10100MR AH-025 LSDO 10/04/05 11:08Enterococcus SM9230C Result None 1,340 20YesR AH-025 LRW 10/04/05 11:20Fecal Coliform SM9222D Result <20200MR AH-025 LSDO 10/04/05 11:08Fecal Coliform SM9222D Result None 550 20YesR AH-025 LSDO 10/04/05 11:08Total Coliform SM9222B Result None 200 20YesR AH-025 LRW 10/04/05 11:20Total Coliform SM9222B Result None4040MR AH-006 LRW 10/05/05 11:45Enterococcus SM9230C Result None43040MR AH-006 LSDO 10/05/05 11:50Enterococcus SM9230C Result None 3,100 20YesR AH-006 LRW 10/05/05 11:45Fecal Coliform SM9222D Result None96040MR AH-006 LSDO 10/05/05 11:50Fecal Coliform SM9222D Result None 5,000 20YesR AH-006 LRW 10/05/05 11:45Total Coliform SM9222B Result None1,52040MR AH-006 LSDO 10/05/05 11:50Total Coliform SM9222B Result None 6,500 20YesF AH-006 LRW 10/11/05 1:35Enterococcus SM9230C Result None1040MF AH-006 LSDO 10/11/05 1:40Enterococcus SM9230C Result None 800 20YesCA04-05 DataPage 28 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of CarlsbadPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterF AH-006 LRW 10/11/05 1:35Fecal Coliform SM9222D Result None2040MF AH-006 LSDO 10/11/05 1:40Fecal Coliform SM9222D Result None 100 20YesF AH-006 LRW 10/11/05 1:35Total Coliform SM9222B Result <20200MF AH-006 LSDO 10/11/05 1:40Total Coliform SM9222B Result < 200 200YesR BA-001 LSDO 10/24/05 11:40Enterococcus SM9230C Result None 460 20YesR BA-001 LSDO 10/24/05 11:40Fecal Coliform SM9222D Result None 220 20YesR BA-001 LSDO 10/24/05 11:40Total Coliform SM9222B Result None 1,100 20YesR AH-006 LRW 10/26/05 10:40Enterococcus SM9230C Result None18040MR AH-006 LSDO 10/26/05 10:35Enterococcus SM9230C Result None 2,100 20YesR AH-006 LRW 10/26/05 10:40Fecal Coliform SM9222D Result None18040MR AH-006 LSDO 10/26/05 10:35Fecal Coliform SM9222D Result None 2,150 20YesR AH-006 LRW 10/26/05 10:40Total Coliform SM9222B Result None32040MR AH-006 LSDO 10/26/05 10:35Total Coliform SM9222B Result None 6,700 20YesR AH-025 LRW 10/26/05 10:20Enterococcus SM9230C Result <10100MR AH-025 LSDO 10/26/05 10:10Enterococcus SM9230C Result None 2,000 20YesR AH-025 LSDO 10/26/05 10:10Fecal Coliform SM9222D Result None 8,350 20YesR AH-025 LRW 10/26/05 10:20Fecal Coliform SM9222D Result None10040MR AH-025 LSDO 10/26/05 10:10Total Coliform SM9222B Result None 28,600 20YesR AH-025 LRW 10/26/05 10:20Total Coliform SM9222B Result None30040MR AH-19A LRW 10/26/05 12:23Enterococcus SM9230C Result <10100MR AH-19A LSDO 10/26/05 12:20Enterococcus SM9230C Result None22020YesR AH-19A LRW 10/26/05 12:23Fecal Coliform SM9222D Result <20200MR AH-19A LSDO 10/26/05 12:20Fecal Coliform SM9222D Result None46020YesR AH-19A LRW 10/26/05 12:23Total Coliform SM9222B Result <20200MR AH-19A LSDO 10/26/05 12:20Total Coliform SM9222B Result None10020YesR BA-017LSDO10/26/05 9:20Enterococcus SM9230C Result None 2,080 20NoR BA-017LSDO10/26/05 9:20Fecal Coliform SM9222D Result None 960 20NoR BA-017LSDO10/26/05 9:20Total Coliform SM9222B Result None 1,700 20NoR BA-021 LSDO 10/26/05 9:55Enterococcus SM9230C Result None 1,650 20YesR BA-021 LSDO 10/26/05 9:55Fecal Coliform SM9222D Result None 1,100 20YesR BA-021 LSDO 10/26/05 9:55Total Coliform SM9222B Result None 4,000 20YesCA04-05 DataPage 29 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-03 CSDO 11/23/04 11:30 Enterococcus SM 9230 A, B RESULT NONE 270 20 NOR S-03 CRW 11/23/04 11:40 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-03 CSDO 11/23/04 11:30 Fecal Coliform SM 9221 E RESULT NONE 900 20 NOR S-03 CRW 11/23/04 11:40 Fecal Coliform SM 9221 E RESULT < 20 20 75 LR S-03 CSDO 11/23/04 11:30 Total Coliform SM 9221 B RESULT NONE 240,000 2,000 NOR S-03 CRW 11/23/04 11:40 Total Coliform SM 9221 B RESULT NONE 9 2 75 LR S-04 CSDO 11/23/04 11:15 Enterococcus SM 9230 A, B RESULT NONE 300 20 NOR S-04 CRW 11/23/04 11:25 Enterococcus SM 9230 A, B RESULT NONE 2 2 0 MR S-04 CSDO 11/23/04 11:15 Fecal Coliform SM 9221 E RESULT NONE 270 20 NOR S-04 CRW 11/23/04 11:25 Fecal Coliform SM 9221 E RESULT NONE 4 2 0 MR S-04 CSDO 11/23/04 11:15 Total Coliform SM 9221 B RESULT NONE 30,000 2,000 NOR S-04 CRW 11/23/04 11:25 Total Coliform SM 9221 B RESULT NONE 17 2 0 MR S-05 CSDO 11/23/04 11:00 Enterococcus SM 9230 A, B RESULT NONE 140 20 NOR S-05 CRW 11/23/04 11:10 Enterococcus SM 9230 A, B RESULT NONE 2 2 75 LR S-05 CSDO 11/23/04 11:00 Fecal Coliform SM 9221 E RESULT NONE 2,200 20 NOR S-05 CRW 11/23/04 11:10 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 LR S-05 CSDO 11/23/04 11:00 Total Coliform SM 9221 B RESULT NONE 23,000 2,000 NOR S-05 CRW 11/23/04 11:10 Total Coliform SM 9221 B RESULT NONE 13 2 75 LR S-06 CSDO 11/23/04 10:44 Enterococcus SM 9230 A, B RESULT NONE 170 20 NOR S-06 CRW 11/23/04 10:55 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-06 CSDO 11/23/04 10:44 Fecal Coliform SM 9221 E RESULT NONE 300 20 NOR S-06 CRW 11/23/04 10:55 Fecal Coliform SM 9221 E RESULT NONE 20 2 0 MR S-06 CSDO 11/23/04 10:44 Total Coliform SM 9221 B RESULT NONE 23,000 2,000 NOR S-06 CRW 11/23/04 10:55 Total Coliform SM 9221 B RESULT NONE 20 2 0 MR S-10 CSDO 11/23/04 12:30 Enterococcus SM 9230 A, B RESULT NONE 130 20 NOR S-10 CRW 11/23/04 12:40 Enterococcus SM 9230 A, B RESULT NONE 4 2 0 MR S-10 CSDO 11/23/04 12:30 Fecal Coliform SM 9221 E RESULT NONE 500 20 NOR S-10 CRW 11/23/04 12:40 Fecal Coliform SM 9221 E RESULT NONE 50 2 0 MR S-10 CSDO 11/23/04 12:30 Total Coliform SM 9221 B RESULT NONE 23,000 2,000 NOR S-10 CRW 11/23/04 12:40 Total Coliform SM 9221 B RESULT > 1,600 2 0 MR S-03 CSDO 3/8/05 10:00 Enterococcus SM 9230 A, B RESULT NONE 700 20 NOR S-03 CRW 3/8/05 10:10 Enterococcus SM 9230 A, B RESULT NONE 34 2 0 MR S-03 CSDO 3/8/05 10:00 Fecal Coliform SM 9221 E RESULT NONE 800 20 NOR S-03 CRW 3/8/05 10:10 Fecal Coliform SM 9221 E RESULT NONE 13 2 0 MR S-03 CSDO 3/8/05 10:00 Total Coliform SM 9221 B RESULT NONE 17,000 200 NOR S-03 CRW 3/8/05 10:10 Total Coliform SM 9221 B RESULT NONE 220 2 0 MR S-04 CSDO 3/8/05 9:45 Enterococcus SM 9230 A, B RESULT NONE 40 20 YESDM04-05 DataPage 30 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-04 CRW 3/8/05 9:55 Enterococcus SM 9230 A, B RESULT NONE 170 2 75 LR S-04 CSDO 3/8/05 9:45 Fecal Coliform SM 9221 E RESULT < 20 20 YESR S-04 CRW 3/8/05 9:55 Fecal Coliform SM 9221 E RESULT NONE 170 2 75 LR S-04 CSDO 3/8/05 9:45 Total Coliform SM 9221 B RESULT NONE 1,400 20 YESR S-04 CRW 3/8/05 9:55 Total Coliform SM 9221 B RESULT NONE 30 2 75 LR S-05 CSDO 3/8/05 9:30 Enterococcus SM 9230 A, B RESULT NONE 500 20 NOR S-05 CRW 3/8/05 9:35 Enterococcus SM 9230 A, B RESULT NONE 20 2 75 LR S-05 CSDO 3/8/05 9:30 Fecal Coliform SM 9221 E RESULT NONE 130 20 NOR S-05 CRW 3/8/05 9:35 Fecal Coliform SM 9221 E RESULT NONE 8 2 75 LR S-05 CSDO 3/8/05 9:30 Total Coliform SM 9221 B RESULT NONE 700 20 NOR S-05 CRW 3/8/05 9:35 Total Coliform SM 9221 B RESULT NONE 170 2 75 LR S-06 CSDO 3/8/05 9:00 Enterococcus SM 9230 A, B RESULT NONE 1,300 20 NOR S-06 CRW 3/8/05 9:10 Enterococcus SM 9230 A, B RESULT NONE 8 2 75 LR S-06 CSDO 3/8/05 9:00 Fecal Coliform SM 9221 E RESULT NONE 300 20 NOR S-06 CRW 3/8/05 9:10 Fecal Coliform SM 9221 E RESULT NONE 4 2 75 LR S-06 CSDO 3/8/05 9:00 Total Coliform SM 9221 B RESULT NONE 28,000 200 NOR S-06 CRW 3/8/05 9:10 Total Coliform SM 9221 B RESULT NONE 140 2 75 LR S-10 CSDO 3/8/05 10:45 Enterococcus SM 9230 A, B RESULT < 20 20 YESR S-10 CRW 3/8/05 10:55 Enterococcus SM 9230 A, B RESULT NONE 50 2 75 LR S-10 CSDO 3/8/05 10:45 Fecal Coliform SM 9221 E RESULT < 20 20 YESR S-10 CRW 3/8/05 10:55 Fecal Coliform SM 9221 E RESULT NONE 4 2 75 LR S-10 CSDO 3/8/05 10:45 Total Coliform SM 9221 B RESULT NONE 300 20 YESR S-10 CRW 3/8/05 10:55 Total Coliform SM 9221 B RESULT NONE 130 2 75 LR S-04 CSDO 4/13/05 15:02 Enterococcus SM 9230 A, B RESULT NONE 300 20 YESR S-04 CRW 4/13/05 15:02 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-04 CSDO 4/13/05 15:02 Fecal Coliform SM 9221 E RESULT NONE 130 20 YESR S-04 CRW 4/13/05 15:02 Fecal Coliform SM 9221 E RESULT < 2 2 75 LR S-04 CSDO 4/13/05 15:02 Total Coliform SM 9221 B RESULT NONE 3500 20 YESR S-04 CRW 4/13/05 15:02 Total Coliform SM 9221 B RESULT NONE 2 2 75 LR S-05 CSDO 4/13/05 14:50 Enterococcus SM 9230 A, B RESULT NONE 20 20 YESR S-05 CRW 4/13/05 14:50 Enterococcus SM 9230 A, B RESULT < 20 20 0 MR S-05 CSDO 4/13/05 14:50 Fecal Coliform SM 9221 E RESULT < 20 20 YESR S-05 CRW 4/13/05 14:50 Fecal Coliform SM 9221 E RESULT NONE 2 2 0 MR S-05 CSDO 4/13/05 14:50 Total Coliform SM 9221 B RESULT NONE 1400 20 YESR S-05 CRW 4/13/05 14:50 Total Coliform SM 9221 B RESULT NONE 2 2 0 MR S-06 CSDO 4/13/05 14:35 Enterococcus SM 9230 A, B RESULT NONE 300 20 YESR S-06 CRW 4/13/05 14:35 Enterococcus SM 9230 A, B RESULT < 2 2 75 LDM04-05 DataPage 31 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-06 CSDO 4/13/05 14:35 Fecal Coliform SM 9221 E RESULT NONE 80 20 YESR S-06 CRW 4/13/05 14:35 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 LR S-06 CSDO 4/13/05 14:35 Total Coliform SM 9221 B RESULT NONE 7000 200 YESR S-06 CRW 4/13/05 14:35 Total Coliform SM 9221 B RESULT NONE 2 2 75 LR S-07 CSDO 4/13/05 14:20 Enterococcus SM 9230 A, B RESULT NONE 30000 2000 NOR S-07 CRW 4/13/05 14:20 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-07 CSDO 4/13/05 14:20 Fecal Coliform SM 9221 E RESULT NONE 170 20 NOR S-07 CRW 4/13/05 14:20 Fecal Coliform SM 9221 E RESULT < 2 2 75 LR S-07 CSDO 4/13/05 14:20 Total Coliform SM 9221 B RESULT NONE 3000 200 NOR S-07 CRW 4/13/05 14:20 Total Coliform SM 9221 B RESULT < 2 2 75 LR S-12 CSDO 4/13/05 16:03 Enterococcus SM 9230 A, B RESULT NONE 7000 200 YESR S-12 CRW 4/13/05 16:03 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-12 CSDO 4/13/05 16:03 Fecal Coliform SM 9221 E RESULT < 20 20 YESR S-12 CRW 4/13/05 16:03 Fecal Coliform SM 9221 E RESULT < 2 2 0 MR S-12 CSDO 4/13/05 16:03 Total Coliform SM 9221 B RESULT NONE 2200 20 YESR S-12 CRW 4/13/05 16:03 Total Coliform SM 9221 B RESULT < 2 2 0 MR S-05 CSDO 5/19/05 11:25 Enterococcus SM 9230 A, B RESULT NONE 110 20 NOR S-05 CRW 5/19/05 11:25 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-05 CSDO 5/19/05 11:25 Fecal Coliform SM 9221 E RESULT NONE 80 20 NOR S-05 CRW 5/19/05 11:25 Fecal Coliform SM 9221 E RESULT < 2 2 0 MR S-05 CSDO 5/19/05 11:25 Total Coliform SM 9221 B RESULT NONE 3000 200 NOR S-05 CRW 5/19/05 11:25 Total Coliform SM 9221 B RESULT NONE 2 2 0 MR S-06 CSDO 5/19/05 11:15 Enterococcus SM 9230 A, B RESULT NONE 1300 20 NOR S-06 CRW 5/19/05 11:15 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-06 CSDO 5/19/05 11:15 Fecal Coliform SM 9221 E RESULT NONE 80 20 NOR S-06 CRW 5/19/05 11:15 Fecal Coliform SM 9221 E RESULT < 2 2 75 LR S-06 CSDO 5/19/05 11:15 Total Coliform SM 9221 B RESULT NONE 13000 200 NOR S-06 CRW 5/19/05 11:15 Total Coliform SM 9221 B RESULT NONE 2 2 75 LR S-07 CSDO 5/19/05 11:00 Enterococcus SM 9230 A, B RESULT NONE 3000 200 NOR S-07 CRW 5/19/05 11:00 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-07 CSDO 5/19/05 11:00 Fecal Coliform SM 9221 E RESULT NONE 230 20 NOR S-07 CRW 5/19/05 11:00 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 LR S-07 CSDO 5/19/05 11:00 Total Coliform SM 9221 B RESULT NONE 5000 200 NOR S-07 CRW 5/19/05 11:00 Total Coliform SM 9221 B RESULT NONE 30 2 75 LR S-12 CSDO 5/19/05 12:20 Enterococcus SM 9230 A, B RESULT NONE 170000 2000 NOR S-12 CRW 5/19/05 12:20 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-12 CSDO 5/19/05 12:20 Fecal Coliform SM 9221 E RESULT NONE 20 20 NODM04-05 DataPage 32 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-12 CRW 5/19/05 12:20 Fecal Coliform SM 9221 E RESULT < 2 2 0 MR S-12 CSDO 5/19/05 12:20 Total Coliform SM 9221 B RESULT NONE 8000 200 NOR S-12 CRW 5/19/05 12:20 Total Coliform SM 9221 B RESULT NONE 2 2 0 MR S-04 CSDO 5/27/05 11:20 Enterococcus SM 9230 A, B RESULT NONE 500 20 NOR S-04 CRW 5/27/05 11:20 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-04 CSDO 5/27/05 11:20 Fecal Coliform SM 9221 E RESULT NONE 20 20 NOR S-04 CRW 5/27/05 11:20 Fecal Coliform SM 9221 E RESULT < 2 2 0 MR S-04 CSDO 5/27/05 11:20 Total Coliform SM 9221 B RESULT NONE 2300 200 NOR S-04 CRW 5/27/05 11:20 Total Coliform SM 9221 B RESULT < 2 2 0 MR S-05 CSDO 5/27/05 11:00 Enterococcus SM 9230 A, B RESULT NONE 20 20 NOR S-05 CRW 5/27/05 11:00 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-05 CSDO 5/27/05 11:00 Fecal Coliform SM 9221 E RESULT NONE 20 20 NOR S-05 CRW 5/27/05 11:00 Fecal Coliform SM 9221 E RESULT < 2 2 75 LR S-05 CSDO 5/27/05 11:00 Total Coliform SM 9221 B RESULT NONE 24000 200 NOR S-05 CRW 5/27/05 11:00 Total Coliform SM 9221 B RESULT NONE 4 2 75 LR S-06 CSDO 5/27/05 10:50 Enterococcus SM 9230 A, B RESULT NONE 800 20 NOR S-06 CRW 5/27/05 10:50 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-06 CSDO 5/27/05 10:50 Fecal Coliform SM 9221 E RESULT NONE 500 20 NOR S-06 CRW 5/27/05 10:50 Fecal Coliform SM 9221 E RESULT < 2 2 0 MR S-06 CSDO 5/27/05 10:50 Total Coliform SM 9221 B RESULT NONE 24000 200 NOR S-06 CRW 5/27/05 10:50 Total Coliform SM 9221 B RESULT NONE 2 2 0 MR S-07 CSDO 5/27/05 10:40 Enterococcus SM 9230 A, B RESULT < 2 2 NOR S-07 CRW 5/27/05 10:40 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-07 CSDO 5/27/05 10:40 Fecal Coliform SM 9221 E RESULT < 2 2 NOR S-07 CRW 5/27/05 10:40 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 LR S-07 CSDO 5/27/05 10:40 Total Coliform SM 9221 B RESULT < 2 2 NOR S-07 CRW 5/27/05 10:40 Total Coliform SM 9221 B RESULT NONE 7 2 75 LR S-12 CSDO 5/27/05 11:58 Enterococcus SM 9230 A, B RESULT NONE 160000 200 NOR S-12 CRW 5/27/05 11:58 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-12 CSDO 5/27/05 11:58 Fecal Coliform SM 9221 E RESULT < 20 20 NOR S-12 CRW 5/27/05 11:58 Fecal Coliform SM 9221 E RESULT NONE 7 2 0 MR S-12 CSDO 5/27/05 11:58 Total Coliform SM 9221 B RESULT NONE 30000 200 NOR S-12 CRW 5/27/05 11:58 Total Coliform SM 9221 B RESULT NONE 7 2 0 MR S-05 CSDO 6/16/05 10:55 Enterococcus SM 9230 A, B RESULT NONE 40 20 NOR S-05 CRW 6/16/05 10:55 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-05 CSDO 6/16/05 10:55 Fecal Coliform SM 9221 E RESULT NONE 40 20 NOR S-05 CRW 6/16/05 10:55 Fecal Coliform SM 9221 E RESULT < 2 2 0 MDM04-05 DataPage 33 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-05 CSDO 6/16/05 10:55 Total Coliform SM 9221 B RESULT NONE 8000 200 NOR S-05 CRW 6/16/05 10:55 Total Coliform SM 9221 B RESULT < 2 2 0 MR S-06 CSDO 6/16/05 10:45 Enterococcus SM 9230 A, B RESULT NONE 230 20 NOR S-06 CRW 6/16/05 10:45 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-06 CSDO 6/16/05 10:45 Fecal Coliform SM 9221 E RESULT NONE 2800 20 NOR S-06 CRW 6/16/05 10:45 Fecal Coliform SM 9221 E RESULT < 2 2 75 LR S-06 CSDO 6/16/05 10:45 Total Coliform SM 9221 B RESULT NONE 30000 2000 NOR S-06 CRW 6/16/05 10:45 Total Coliform SM 9221 B RESULT NONE 7 2 75 LR S-07 CSDO 6/16/05 10:30 Enterococcus SM 9230 A, B RESULT NONE 300 20 NOR S-07 CRW 6/16/05 10:30 Enterococcus SM 9230 A, B RESULT NONE 2 2 75 LR S-07 CSDO 6/16/05 10:30 Fecal Coliform SM 9221 E RESULT NONE 130 20 NOR S-07 CRW 6/16/05 10:30 Fecal Coliform SM 9221 E RESULT < 2 2 75 LR S-07 CSDO 6/16/05 10:30 Total Coliform SM 9221 B RESULT NONE 240000 2000 NOR S-07 CRW 6/16/05 10:30 Total Coliform SM 9221 B RESULT NONE 4 2 75 LR S-12 CSDO 6/16/05 11:30 Enterococcus SM 9230 A, B RESULT < 2 2 NOR S-12 CRW 6/16/05 11:30 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-12 CSDO 6/16/05 11:30 Fecal Coliform SM 9221 E RESULT < 2 2 NOR S-12 CRW 6/16/05 11:30 Fecal Coliform SM 9221 E RESULT < 2 2 0 MR S-12 CSDO 6/16/05 11:30 Total Coliform SM 9221 B RESULT NONE 3000 200 NOR S-12 CRW 6/16/05 11:30 Total Coliform SM 9221 B RESULT NONE 4 2 0 MR S-04 CSDO 7/1/05 9:00 Enterococcus SM 9230 A, B RESULT NONE 130 20 NOR S-04 CRW 7/1/05 9:00 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-04 CSDO 7/1/05 9:00 Fecal Coliform SM 9221 E RESULT NONE 40 20 NOR S-04 CRW 7/1/05 9:00 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 RR S-04 CSDO 7/1/05 9:00 Total Coliform SM 9221 B RESULT NONE 2800 20 NOR S-04 CRW 7/1/05 9:00 Total Coliform SM 9221 B RESULT NONE 2 2 75 RR S-05 CSDO 7/1/05 8:40 Enterococcus SM 9230 A, B RESULT NONE 130 20 YESR S-05 CRW 7/1/05 8:40 Enterococcus SM 9230 A, B RESULT < 2 2 75 LR S-05 CSDO 7/1/05 8:40 Fecal Coliform SM 9221 E RESULT < 20 20 YESR S-05 CRW 7/1/05 8:40 Fecal Coliform SM 9221 E RESULT < 2 2 75 LR S-05 CSDO 7/1/05 8:40 Total Coliform SM 9221 B RESULT NONE 1300 20 YESR S-05 CRW 7/1/05 8:40 Total Coliform SM 9221 B RESULT NONE 4 2 75 LR S-06 CSDO 7/1/05 8:20 Enterococcus SM 9230 A, B RESULT NONE 2800 20 NOR S-06 CRW 7/1/05 8:20 Enterococcus SM 9230 A, B RESULT < 2 2 0 MR S-06 CSDO 7/1/05 8:20 Fecal Coliform SM 9221 E RESULT NONE 7000 200 NOR S-06 CRW 7/1/05 8:20 Fecal Coliform SM 9221 E RESULT NONE 2 2 0 MR S-06 CSDO 7/1/05 8:20 Total Coliform SM 9221 B RESULT NONE 50000 2000 NODM04-05 DataPage 34 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-06 CRW 7/1/05 8:20 Total Coliform SM 9221 B RESULT NONE 7 2 0 MR S-12 CSDO 7/1/05 11:52 Enterococcus SM 9230 A, B RESULT < 20 20 YESR S-12 CRW 7/1/05 11:52 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-12 CSDO 7/1/05 11:52 Fecal Coliform SM 9221 E RESULT < 20 20 YESR S-12 CRW 7/1/05 11:52 Fecal Coliform SM 9221 E RESULT < 2 2 75 RR S-12 CSDO 7/1/05 11:52 Total Coliform SM 9221 B RESULT NONE 20 20 YESR S-12 CRW 7/1/05 11:52 Total Coliform SM 9221 B RESULT < 2 2 75 RR S-04 CSDO 7/26/05 10:35 Enterococcus SM 9230 A, B RESULT NONE 300 20 NOR S-04 CRW 7/26/05 10:35 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-04 CSDO 7/26/05 10:35 Fecal Coliform SM 9221 E RESULT NONE 220 20 NOR S-04 CRW 7/26/05 10:35 Fecal Coliform SM 9221 E RESULT < 2 2 75 RR S-04 CSDO 7/26/05 10:35 Total Coliform SM 9221 B RESULT NONE 30000 2000 NOR S-04 CRW 7/26/05 10:35 Total Coliform SM 9221 B RESULT NONE 2 2 75 RR S-05 CSDO 7/26/05 10:10 Enterococcus SM 9230 A, B RESULT NONE 5000 200 YESR S-05 CRW 7/26/05 10:10 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-05 CSDO 7/26/05 10:10 Fecal Coliform SM 9221 E RESULT NONE 13000 200 YESR S-05 CRW 7/26/05 10:10 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 RR S-05 CSDO 7/26/05 10:10 Total Coliform SM 9221 B RESULT NONE 160000 200 YESR S-05 CRW 7/26/05 10:10 Total Coliform SM 9221 B RESULT NONE 8 2 75 RR S-06 CSDO 7/26/05 9:55 Enterococcus SM 9230 A, B RESULT NONE 2200 20 NOR S-06 CRW 7/26/05 9:55 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-06 CSDO 7/26/05 9:55 Fecal Coliform SM 9221 E RESULT NONE 1400 20 NOR S-06 CRW 7/26/05 9:55 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 RR S-06 CSDO 7/26/05 9:55 Total Coliform SM 9221 B RESULT NONE 160000 200 NOR S-06 CRW 7/26/05 9:55 Total Coliform SM 9221 B RESULT NONE 4 2 75 RR S-07 CSDO 7/26/05 9:32 Enterococcus SM 9230 A, B RESULT NONE 2300 20 NOR S-07 CRW 7/26/05 9:32 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-07 CSDO 7/26/05 9:32 Fecal Coliform SM 9221 E RESULT NONE 1700 20 NOR S-07 CRW 7/26/05 9:32 Fecal Coliform SM 9221 E RESULT < 2 2 75 RR S-07 CSDO 7/26/05 9:32 Total Coliform SM 9221 B RESULT NONE 160000 200 NOR S-07 CRW 7/26/05 9:32 Total Coliform SM 9221 B RESULT NONE 4 2 75 RR S-12 CSDO 7/26/05 11:15 Enterococcus SM 9230 A, B RESULT NONE 800 20 NOR S-12 CRW 7/26/05 11:15 Enterococcus SM 9230 A, B RESULT NONE 2 2 0 MR S-12 CSDO 7/26/05 11:15 Fecal Coliform SM 9221 E RESULT NONE 220 20 NOR S-12 CRW 7/26/05 11:15 Fecal Coliform SM 9221 E RESULT NONE 4 2 0 MR S-12 CSDO 7/26/05 11:15 Total Coliform SM 9221 B RESULT NONE 500000 2000 NOR S-12 CRW 7/26/05 11:15 Total Coliform SM 9221 B RESULT NONE 240 2 0 MDM04-05 DataPage 35 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-04 CSDO 7/27/05 15:26 Enterococcus SM 9230 A, B RESULT NONE 80 20 YESR S-04 CRW 7/27/05 15:26 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-04 CSDO 7/27/05 15:26 Fecal Coliform SM 9221 E RESULT NONE 40 20 YESR S-04 CRW 7/27/05 15:26 Fecal Coliform SM 9221 E RESULT NONE 11 2 75 RR S-04 CSDO 7/27/05 15:26 Total Coliform SM 9221 B RESULT NONE 50000 2000 YESR S-04 CRW 7/27/05 15:26 Total Coliform SM 9221 B RESULT NONE 80 2 75 RR S-05 CSDO 7/27/05 15:17 Enterococcus SM 9230 A, B RESULT < 2 2 YESR S-05 CRW 7/27/05 15:17 Enterococcus SM 9230 A, B RESULT NONE 2 2 75 RR S-05 CSDO 7/27/05 15:17 Fecal Coliform SM 9221 E RESULT < 2 2 YESR S-05 CRW 7/27/05 15:17 Fecal Coliform SM 9221 E RESULT NONE 17 2 75 RR S-05 CSDO 7/27/05 15:17 Total Coliform SM 9221 B RESULT NONE 17000 200 YESR S-05 CRW 7/27/05 15:17 Total Coliform SM 9221 B RESULT NONE 110 2 75 RR S-06 CSDO 7/27/05 15:05 Enterococcus SM 9230 A, B RESULT NONE 340 20 YESR S-06 CRW 7/27/05 15:05 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-06 CSDO 7/27/05 15:05 Fecal Coliform SM 9221 E RESULT NONE 9000 200 YESR S-06 CRW 7/27/05 15:05 Fecal Coliform SM 9221 E RESULT NONE 20 20 75 RR S-06 CSDO 7/27/05 15:05 Total Coliform SM 9221 B RESULT NONE 900000 2000 YESR S-06 CRW 7/27/05 15:05 Total Coliform SM 9221 B RESULT NONE 240 2 75 RR S-07 CSDO 7/27/05 14:43 Enterococcus SM 9230 A, B RESULT NONE 1100 20 NOR S-07 CRW 7/27/05 14:43 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-07 CSDO 7/27/05 14:43 Fecal Coliform SM 9221 E RESULT NONE 2200 20 NOR S-07 CRW 7/27/05 14:43 Fecal Coliform SM 9221 E RESULT NONE 40 20 75 RR S-07 CSDO 7/27/05 14:43 Total Coliform SM 9221 B RESULT NONE 900000 2000 NOR S-07 CRW 7/27/05 14:43 Total Coliform SM 9221 B RESULT NONE 9 2 75 RR S-12 CSDO 7/27/05 16:08 Enterococcus SM 9230 A, B RESULT NONE 270 20 NOR S-12 CRW 7/27/05 16:08 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-12 CSDO 7/27/05 16:08 Fecal Coliform SM 9221 E RESULT NONE 40 20 NOR S-12 CRW 7/27/05 16:08 Fecal Coliform SM 9221 E RESULT NONE 2 2 75 RR S-12 CSDO 7/27/05 16:08 Total Coliform SM 9221 B RESULT NONE 1400 20 NOR S-12 CRW 7/27/05 16:08 Total Coliform SM 9221 B RESULT NONE 4 2 75 RR S-06 CSDO 8/16/05 12:30 Enterococcus SM 9230 A, B RESULT NONE 300 20R S-06 CRW 8/16/05 12:30 Enterococcus SM 9230 A, B RESULT < 2 2R S-06 CSDO 8/16/05 12:30 Fecal Coliform SM 9221 E RESULT NONE 2200 20R S-06 CRW 8/16/05 12:30 Fecal Coliform SM 9221 E RESULT < 20 20R S-06 CSDO 8/16/05 12:30 Total Coliform SM 9221 B RESULT NONE 80000 2000R S-06 CRW 8/16/05 12:30 Total Coliform SM 9221 B RESULT < 20 20R S-07 CSDO 8/16/0512:15Enterococcus SM 9230 A, B RESULT NONE110 20DM04-05 DataPage 36 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-07 CRW 8/16/0512:15Enterococcus SM 9230 A, B RESULT NONE 20 20R S-07 CSDO 8/16/0512:15Fecal Coliform SM 9221 E RESULT NONE500 20R S-07 CRW 8/16/0512:15Fecal Coliform SM 9221 E RESULT < 20 20R S-07 CSDO 8/16/0512:15Total Coliform SM 9221 B RESULT NONE2300 2000R S-07 CRW 8/16/0512:15Total Coliform SM 9221 B RESULT < 20 20R S-12 CSDO 8/16/05 13:30 Enterococcus SM 9230 A, B RESULT NONE 130 20R S-12 CRW 8/16/05 13:30 Enterococcus SM 9230 A, B RESULT <22R S-12 CSDO 8/16/05 13:30 Fecal Coliform SM 9221 E RESULT NONE 80 20R S-12 CRW 8/16/05 13:30 Fecal Coliform SM 9221 E RESULT <20 20R S-12 CSDO 8/16/05 13:30 Total Coliform SM 9221 B RESULT NONE 220000 2000R S-12 CRW 8/16/05 13:30 Total Coliform SM 9221 B RESULT <20 20R S-04 CSDO 8/24/05 12:20 Enterococcus SM 9230 A, B RESULT NONE 800 20 YESR S-04 CRW 8/24/05 12:20 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-04 CSDO 8/24/05 12:20 Fecal Coliform SM 9221 E RESULT NONE 1400 20 YESR S-04 CRW 8/24/05 12:20 Fecal Coliform SM 9221 E RESULT NONE 110 20 75 RR S-04 CSDO 8/24/05 12:20 Total Coliform SM 9221 B RESULT NONE 30000 2000 YESR S-04 CRW 8/24/05 12:20 Total Coliform SM 9221 B RESULT NONE 140 20 75 RR S-05 CSDO 8/24/05 12:50 Enterococcus SM 9230 A, B RESULT NONE 20 20 YESR S-05 CRW 8/24/05 12:50 Enterococcus SM 9230 A, B RESULT < 2 2 75 RR S-05 CSDO 8/24/05 12:50 Fecal Coliform SM 9221 E RESULT NONE 130 20 YESR S-05 CRW 8/24/05 12:50 Fecal Coliform SM 9221 E RESULT < 20 20 75 RR S-05 CSDO 8/24/05 12:50 Total Coliform SM 9221 B RESULT NONE 13000 200 YESR S-05 CRW 8/24/05 12:50 Total Coliform SM 9221 B RESULT < 20 20 75 RR S-05 CSDO 9/21/05 8:30 Enterococcus SM 9230 A, B RESULT NONE 110 20 YESR S-05 CRW 9/21/05 8:30 Enterococcus SM 9230 A, B RESULT < 20 20 75 RR S-05 CSDO 9/21/05 8:30 Fecal Coliform SM 9221 E RESULT NONE 270 20 YESR S-05 CRW 9/21/05 8:30 Fecal Coliform SM 9221 E RESULT NONE 40 20 75 RR S-05 CSDO 9/21/05 8:30 Total Coliform SM 9221 B RESULT NONE 110000 2000 YESR S-05 CRW 9/21/05 8:30 Total Coliform SM 9221 B RESULT NONE 300 20 75 RR S-06 CSDO 9/21/05 8:20 Enterococcus SM 9230 A, B RESULT NONE 2300 200 YESR S-06 CRW 9/21/05 8:20 Enterococcus SM 9230 A, B RESULT NONE 20 20 75 RR S-06 CSDO 9/21/05 8:20 Fecal Coliform SM 9221 E RESULT NONE 500 20 YESR S-06 CRW 9/21/05 8:20 Fecal Coliform SM 9221 E RESULT NONE 40 20 75 RR S-06 CSDO 9/21/05 8:20 Total Coliform SM 9221 B RESULT NONE 50000 2000 YESR S-06 CRW 9/21/05 8:20 Total Coliform SM 9221 B RESULT NONE 1300 20 75 RR S-07 CSDO 9/21/05 8:10 Enterococcus SM 9230 A, B RESULT NONE 3000 200 NOR S-07 CRW 9/21/05 8:10 Enterococcus SM 9230 A, B RESULT < 20 20 75 RDM04-05 DataPage 37 of 133 Analytical Lab: Enviromatrix (EEL for Nov 2003)Analytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Del MarPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR S-07 CSDO 9/21/05 8:10 Fecal Coliform SM 9221 E RESULT NONE 3000 200 NOR S-07 CRW 9/21/05 8:10 Fecal Coliform SM 9221 E RESULT < 20 20 75 RR S-07 CSDO 9/21/05 8:10 Total Coliform SM 9221 B RESULT NONE 1600000 2000 NOR S-07 CRW 9/21/05 8:10 Total Coliform SM 9221 B RESULT NONE 170 20 75 RR S-12 CSDO 9/21/05 8:45 Enterococcus SM 9230 A, B RESULT NONE 1300 20 NOR S-12 CRW 9/21/05 8:45 Enterococcus SM 9230 A, B RESULT < 20 20 75 RR S-12 CSDO 9/21/05 8:45 Fecal Coliform SM 9221 E RESULT NONE 3000 200 NOR S-12 CRW 9/21/05 8:45 Fecal Coliform SM 9221 E RESULT NONE 20 20 75 RR S-12 CSDO 9/21/05 8:45 Total Coliform SM 9221 B RESULT NONE 240000 2000 NOR S-12 CRW 9/21/05 8:45 Total Coliform SM 9221 B RESULT NONE 300 20 75 RR S-04 CRW 10/5/05 10:45 Enterococcus SM 9230 A, B RESULT NONE 110 2 75 LR S-04 CRW 10/5/05 10:45 Fecal Coliform SM 9221 E RESULT NONE 240 2 75 LR S-04 CRW 10/5/05 10:45 Total Coliform SM 9221 B RESULT > 1600 2 75 LR S-05 CRW 10/5/05 10:10 Enterococcus SM 9230 A, B RESULT NONE 4 2 75 LR S-05 CSDO 10/5/05 10:10 Enterococcus SM 9230 A, B RESULT NONE 20 20 YESR S-05 CRW 10/5/05 10:10 Fecal Coliform SM 9221 E RESULT NONE 8 2 75 LR S-05 CSDO 10/5/05 10:10 Fecal Coliform SM 9221 E RESULT < 20 20 YESR S-05 CRW 10/5/05 10:10 Total Coliform SM 9221 B RESULT > 1600 2 75 LR S-05 CSDO 10/5/05 10:10 Total Coliform SM 9221 B RESULT NONE 13000 200 YESR S-06 CSDO 10/5/05 10:25 Enterococcus SM 9230 A, B RESULT NONE 500 20 YESR S-06 CRW 10/5/05 10:25 Enterococcus SM 9230 A, B RESULT NONE 22 2 75 LR S-06 CSDO 10/5/05 10:25 Fecal Coliform SM 9221 E RESULT NONE 11000 200 YESR S-06 CRW 10/5/05 10:25 Fecal Coliform SM 9221 E RESULT NONE 50 2 75 LR S-06 CSDO 10/5/05 10:25 Total Coliform SM 9221 B RESULT > 160000 2000 YESR S-06 CRW 10/5/05 10:25 Total Coliform SM 9221 B RESULT NONE 500 2 75 LR S-07 CSDO 10/5/05 9:10 Enterococcus SM 9230 A, B RESULT NONE 1300 20 YESR S-07 CRW 10/5/05 9:10 Enterococcus SM 9230 A, B RESULT NONE 11 2 75 RR S-07 CSDO 10/5/05 9:10 Fecal Coliform SM 9221 E RESULT NONE 230 20 YESR S-07 CRW 10/5/05 9:10 Fecal Coliform SM 9221 E RESULT NONE 8 2 75 RR S-07 CSDO 10/5/05 9:10 Total Coliform SM 9221 B RESULT NONE 17000 200 YESR S-07 CRW 10/5/05 9:10 Total Coliform SM 9221 B RESULT NONE 80 20 75 RR S-12 CSDO 10/5/05 10:55 Enterococcus SM 9230 A, B RESULT NONE 4 2 NOR S-12 CRW 10/5/05 10:55 Enterococcus SM 9230 A, B RESULT NONE 220 20 75 LR S-12 CSDO 10/5/05 10:55 Fecal Coliform SM 9221 E RESULT NONE 4 2 NOR S-12 CRW 10/5/05 10:55 Fecal Coliform SM 9221 E RESULT NONE 70 20 75 LR S-12 CSDO 10/5/05 10:55 Total Coliform SM 9221 B RESULT NONE 220 2 NOR S-12 CRW 10/5/05 10:55 Total Coliform SM 9221 B RESULT NONE 240000 2000 75 LDM04-05 DataPage 38 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-420 CSDO 11/1/2004 10:40 Enterococcus SM 9230C RESULT None 500 50 YesR EH-420 CRW 11/1/2004 10:45 Enterococcus SM 9230C RESULT None 6 1 75 RR EH-420 CSDO 11/1/2004 10:40 Fecal Coliform SM 9222D RESULT None 1950 50 YesR EH-420 CRW 11/1/2004 10:45 Fecal Coliform SM 9222D RESULT None 3 1 75 RR EH-420 CSDO 11/1/2004 10:40 Total Coliform SM 9222B RESULT None 8200 200 YesR EH-420 CRW 11/1/2004 10:45 Total Coliform SM 9222B RESULT None 12 1 75 RR EH-403 CSDO 11/3/2004 12:07 Enterococcus SM 9230C RESULT None 50 50 YesR EH-403 CRW 11/3/2004 12:05 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-403 CSDO 11/3/2004 12:07 Fecal Coliform SM 9222D RESULT None 250 50 YesR EH-403 CRW 11/3/2004 12:05 Fecal Coliform SM 9222D RESULT None 1 1 75 LR EH-403 CSDO 11/3/2004 12:07 Total Coliform SM 9222B RESULT None 1400 100 YesR EH-403 CRW 11/3/2004 12:05 Total Coliform SM 9222B RESULT None 9 1 75 LR EH-410 CSDO 11/3/2004 11:53 Enterococcus SM 9230C RESULT < 50 50 YesR EH-410 CRW 11/3/2004 11:50 Enterococcus SM 9230C RESULT None 5 1 75 LR EH-410 CSDO 11/3/2004 11:53 Fecal Coliform SM 9222D RESULT None 50 50 YesR EH-410 CRW 11/3/2004 11:50 Fecal Coliform SM 9222D RESULT None 11 4 75 LR EH-410 CSDO 11/3/2004 11:53 Total Coliform SM 9222B RESULT None 100 100 YesR EH-410 CRW 11/3/2004 11:50 Total Coliform SM 9222B RESULT None 20 4 75 LR EH-420 CSDO 11/15/2004 11:10 Enterococcus SM 9230C RESULT < 50 50 YesR EH-420 CRW 11/15/2004 11:03 Enterococcus SM 9230C RESULT None 12 4 75 LR EH-420 CSDO 11/15/2004 11:10 Fecal Coliform SM 9222D RESULT None 400 50 YesR EH-420 CRW 11/15/2004 11:03 Fecal Coliform SM 9222D RESULT None 4 4 75 LR EH-420 CSDO 11/15/2004 11:10 Total Coliform SM 9222B RESULT None 1,200 200 YesR EH-420 CRW 11/15/2004 11:03 Total Coliform SM 9222B RESULT None 20 4 75 LR EH-420 CSDO 11/24/2004 10:18 Enterococcus SM 9230C RESULT None 200 50 YesR EH-420 CRW 11/24/2004 10:23 Enterococcus SM 9230C RESULT None 1 1 75 LR EH-420 CSDO 11/24/2004 10:18 Fecal Coliform SM 9222D RESULT None 300 50 YesR EH-420 CRW 11/24/2004 10:23 Fecal Coliform SM 9222D RESULT None 10 1 75 LR EH-420 CSDO 11/24/2004 10:18 Total Coliform SM 9222B RESULT None 5,400 100 YesR EH-420 CRW 11/24/2004 10:23 Total Coliform SM 9222B RESULT None 24 1 75 LR EH-420 CSDO 12/2/2004 11:20 Enterococcus SM 9230C RESULT < 50 50 YesR EH-420 CRW 12/2/2004 11:10 Enterococcus SM 9230C RESULT None 16 1 75 LR EH-420 CSDO 12/2/2004 11:20 Fecal Coliform SM 9222D RESULT None 200 50 YesR EH-420 CRW 12/2/2004 11:10 Fecal Coliform SM 9222D RESULT None 43 1 75 LR EH-420 CSDO 12/2/2004 11:20 Total Coliform SM 9222B RESULT None 1,400 100 YesR EH-420 CRW 12/2/2004 11:10 Total Coliform SM 9222B RESULT None 44 1 75 LR EH-420 CSDO 12/15/2004 9:43 Enterococcus SM 9230C RESULT None 400 50 YesEN04-05 DataPage 39 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-420 CRW 12/15/2004 9:35 Enterococcus SM 9230C RESULT None 29 1 75 LR EH-420 CSDO 12/15/2004 9:43 Fecal Coliform SM 9222D RESULT None 50 50 YesR EH-420 CRW 12/15/2004 9:35 Fecal Coliform SM 9222D RESULT None 21 1 75 LR EH-420 CSDO 12/15/2004 9:43 Total Coliform SM 9222B RESULT None 2,000 100 YesR EH-420 CRW 12/15/2004 9:35 Total Coliform SM 9222B RESULT None 126 1 75 LR EH-403 CSDO 12/16/2004 10:42 Enterococcus SM 9230C RESULT None 20 20 YesR EH-403 CRW 12/16/2004 10:40 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-403 CSDO 12/16/2004 10:42 Fecal Coliform SM 9222D RESULT < 20 20 YesR EH-403 CRW 12/16/2004 10:40 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-403 CSDO 12/16/2004 10:42 Total Coliform SM 9222B RESULT None 100 50 YesR EH-403 CRW 12/16/2004 10:40 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-410 CSDO 12/16/2004 10:14 Enterococcus SM 9230C RESULT < 20 20 YesR EH-410 CRW 12/16/2004 10:10 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-410 CSDO 12/16/2004 10:14 Fecal Coliform SM 9222D RESULT < 20 20 YesR EH-410 CRW 12/16/2004 10:10 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-410 CSDO 12/16/2004 10:14 Total Coliform SM 9222B RESULT < 50 50 YesR EH-410 CRW 12/16/2004 10:10 Total Coliform SM 9222B RESULT None 10 1 75 LR EH-420 CSDO 12/20/2004 9:35 Enterococcus SM 9230C RESULT None 300 50 YesR EH-420 CRW 12/20/2004 9:43 Enterococcus SM 9230C RESULT None 19 1 75 LR EH-420 CSDO 12/20/2004 9:35 Fecal Coliform SM 9222D RESULT None 200 100 YesR EH-420 CRW 12/20/2004 9:43 Fecal Coliform SM 9222D RESULT None 54 2 75 LR EH-420 CSDO 12/20/2004 9:35 Total Coliform SM 9222B RESULT None 8,200 200 YesR EH-420 CRW 12/20/2004 9:43 Total Coliform SM 9222B RESULT None 84 2 75 LR EH-403 CSDO 1/19/2005 11:40 Enterococcus SM 9230C RESULT None 450 10 YesR EH-403 CRW 1/19/2005 11:45 Enterococcus SM 9230C RESULT None 6 1 75 LR EH-403 CSDO 1/19/2005 11:40 Fecal Coliform SM 9222D RESULT None 200 10 YesR EH-403 CRW 1/19/2005 11:45 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-403 CSDO 1/19/2005 11:40 Total Coliform SM 9222B RESULT None 1020 20 YesR EH-403 CRW 1/19/2005 11:45 Total Coliform SM 9222B RESULT None 3 1 75 LR EH-405 CSDO 1/19/2005 11:55 Enterococcus SM 9230C RESULT < 20 20 YesR EH-405 CRW 1/19/2005 11:50 Enterococcus SM 9230C RESULT None 4 1 75 LR EH-405 CSDO 1/19/2005 11:55 Fecal Coliform SM 9222D RESULT < 20 20 YesR EH-405 CRW 1/19/2005 11:50 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-405 CSDO 1/19/2005 11:55 Total Coliform SM 9222B RESULT < 50 50 YesR EH-405 CRW 1/19/2005 11:50 Total Coliform SM 9222B RESULT None 1 1 75 LR EH-410 CSDO 1/19/2005 12:05 Enterococcus SM 9230C RESULT < 20 20 YesR EH-410 CRW 1/19/2005 12:10 Enterococcus SM 9230C RESULT < 1 1 75 LEN04-05 DataPage 40 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-410 CSDO 1/19/2005 12:05 Fecal Coliform SM 9222D RESULT < 20 20 YesR EH-410 CRW 1/19/2005 12:10 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-410 CSDO 1/19/2005 12:05 Total Coliform SM 9222B RESULT < 50 50 YesR EH-410 CRW 1/19/2005 12:10 Total Coliform SM 9222B RESULT < 1 1 75 LR EH-420 CSDO 1/19/2005 10:55 Enterococcus SM 9230C RESULT None 360 20 YesR EH-420 CRW 1/19/2005 11:00 Enterococcus SM 9230C RESULT None 50 1 75 LR EH-420 CSDO 1/19/2005 10:55 Fecal Coliform SM 9222D RESULT None 120 20 YesR EH-420 CRW 1/19/2005 11:00 Fecal Coliform SM 9222D RESULT None 19 1 75 LR EH-420 CSDO 1/19/2005 10:55 Total Coliform SM 9222B RESULT None 8,400 100 YesR EH-420 CRW 1/19/2005 11:00 Total Coliform SM 9222B RESULT None 111 1 75 LR EH-403 CSDO 2/2/2005 9:18 Enterococcus SM 9230C RESULT None 40 10 YesR EH-403 CRW 2/2/2005 9:15 Enterococcus SM 9230C RESULT None 3 1 75 LR EH-403 CSDO 2/2/2005 9:18 Fecal Coliform SM 9222D RESULT < 10 10 YesR EH-403 CRW 2/2/2005 9:15 Fecal Coliform SM 9222D RESULT None 3 1 75 LR EH-403 CSDO 2/2/2005 9:18 Total Coliform SM 9222B RESULT None 20 20 YesR EH-403 CRW 2/2/2005 9:15 Total Coliform SM 9222B RESULT None 5 1 75 LR EH-410 CSDO 2/2/2005 9:38 Enterococcus SM 9230C RESULT < 10 10 YesR EH-410 CRW 2/2/2005 9:35 Enterococcus SM 9230C RESULT None 4 1 75 LR EH-410 CSDO 2/2/2005 9:38 Fecal Coliform SM 9222D RESULT < 10 10 YesR EH-410 CRW 2/2/2005 9:35 Fecal Coliform SM 9222D RESULT None 2 1 75 LR EH-410 CSDO 2/2/2005 9:38 Total Coliform SM 9222B RESULT None 20 20 YesR EH-410 CRW 2/2/2005 9:35 Total Coliform SM 9222B RESULT None 14 1 75 LR EH-420 CSDO 2/2/2005 9:59 Enterococcus SM 9230C RESULT None 160 20 YesR EH-420 CRW 2/2/2005 9:57 Enterococcus SM 9230C RESULT None 19 1 75 LR EH-420 CSDO 2/2/2005 9:59 Fecal Coliform SM 9222D RESULT None 1260 20 YesR EH-420 CRW 2/2/2005 9:57 Fecal Coliform SM 9222D RESULT None 58 1 75 LR EH-420 CSDO 2/2/2005 9:59 Total Coliform SM 9222B RESULT None 4,000 100 YesR EH-420 CRW 2/2/2005 9:57 Total Coliform SM 9222B RESULT None 75 1 75 LR EH-420 CSDO 2/9/2005 10:54 Enterococcus SM 9230C RESULT None 60 20 YesR EH-420 CRW 2/9/2005 10:52 Enterococcus SM 9230C RESULT None 11 1 75 LR EH-420 CSDO 2/9/2005 10:54 Fecal Coliform SM 9222D RESULT None 60 20 YesR EH-420 CRW 2/9/2005 10:52 Fecal Coliform SM 9222D RESULT None 2 1 75 LR EH-420 CSDO 2/9/2005 10:54 Total Coliform SM 9222B RESULT None 2,500 100 YesR EH-420 CRW 2/9/2005 10:52 Total Coliform SM 9222B RESULT None 34 1 75 LR EH-420 CSDO 3/2/2005 9:15 Enterococcus SM 9230C RESULT None 100 20 YesR EH-420 CRW 3/2/2005 9:18 Enterococcus SM 9230C RESULT None 12 1 75 LR EH-420 CSDO 3/2/2005 9:15 Fecal Coliform SM 9222D RESULT None 320 20 YesEN04-05 DataPage 41 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-420 CRW 3/2/2005 9:18 Fecal Coliform SM 9222D RESULT None 28 1 75 LR EH-420 CSDO 3/2/2005 9:15 Total Coliform SM 9222B RESULT None 11,800 100 YesR EH-420 CRW 3/2/2005 9:18 Total Coliform SM 9222B RESULT None 104 1 75 LR EH-403 CSDO 3/17/2005 11:27 Enterococcus SM 9230C RESULT None 370 10 YesR EH-403 CRW 3/17/2005 11:25 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-403 CSDO 3/17/2005 11:27 Fecal Coliform SM 9222D RESULT None 1200 10 YesR EH-403 CRW 3/17/2005 11:25 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-403 CSDO 3/17/2005 11:27 Total Coliform SM 9222B RESULT None 1700 20 YesR EH-403 CRW 3/17/2005 11:25 Total Coliform SM 9222B RESULT None 1 1 75 LR EH-410 CSDO 3/17/2005 11:00 Enterococcus SM 9230C RESULT < 10 10 YesR EH-410 CRW 3/17/2005 10:58 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-410 CSDO 3/17/2005 11:00 Fecal Coliform SM 9222D RESULT < 10 10 YesR EH-410 CRW 3/17/2005 10:58 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-410 CSDO 3/17/2005 11:00 Total Coliform SM 9222B RESULT < 20 20 YesR EH-410 CRW 3/17/2005 10:58 Total Coliform SM 9222B RESULT < 1 1 75 LR EH-420 CSDO 3/17/2005 10:39 Enterococcus SM 9230C RESULT None 190 10 YesR EH-420 CRW 3/17/2005 10:37 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-420 CSDO 3/17/2005 10:39 Fecal Coliform SM 9222D RESULT None 1460 20 YesR EH-420 CRW 3/17/2005 10:37 Fecal Coliform SM 9222D RESULT None 2 1 75 LR EH-420 CSDO 3/17/2005 10:39 Total Coliform SM 9222B RESULT None 1,100 100 YesR EH-420 CRW 3/17/2005 10:37 Total Coliform SM 9222B RESULT < 1 1 75 LR EH-420 CSDO 3/30/2005 11:03 Enterococcus SM 9230C RESULT None 840 20 YesR EH-420 CRW 3/30/2005 11:00 Enterococcus SM 9230C RESULT None 18 1 75 LR EH-420 CSDO 3/30/2005 11:03 Fecal Coliform SM 9222D RESULT None 480 20 YesR EH-420 CRW 3/30/2005 11:00 Fecal Coliform SM 9222D RESULT None 19 1 75 LR EH-420 CSDO 3/30/2005 11:03 Total Coliform SM 9222B RESULT None 150 50 YesR EH-420 CRW 3/30/2005 11:00 Total Coliform SM 9222B RESULT < 1 1 75 LR EH-403 CSDO 4/6/2005 11:20 Enterococcus SM 9230C RESULT None 20 10 YesR EH-403 CRW 4/6/2005 11:17 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-403 CSDO 4/6/2005 11:20 Fecal Coliform SM 9222D RESULT None 20 10 YesR EH-403 CRW 4/6/2005 11:17 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-403 CSDO 4/6/2005 11:20 Total Coliform SM 9222B RESULT None 960 20 YesR EH-403 CRW 4/6/2005 11:17 Total Coliform SM 9222B RESULT None 1 1 75 LR EH-405 CSDO 4/6/2005 11:08 Enterococcus SM 9230C RESULT < 20 20 YesR EH-405 CRW 4/6/2005 11:05 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-405 CSDO 4/6/2005 11:08 Fecal Coliform SM 9222D RESULT None 100 20 YesR EH-405 CRW 4/6/2005 11:05 Fecal Coliform SM 9222D RESULT < 1 1 75 LEN04-05 DataPage 42 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-405 CSDO 4/6/2005 11:08 Total Coliform SM 9222B RESULT None 960 20 YesR EH-405 CRW 4/6/2005 11:05 Total Coliform SM 9222B RESULT None 1 1 75 LR EH-410 CSDO 4/6/2005 10:43 Enterococcus SM 9230C RESULT < 20 20 YesR EH-410 CRW 4/6/2005 10:40 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-410 CSDO 4/6/2005 10:43 Fecal Coliform SM 9222D RESULT < 20 20 YesR EH-410 CRW 4/6/2005 10:40 Fecal Coliform SM 9222D RESULT None 2 1 75 LR EH-410 CSDO 4/6/2005 10:43 Total Coliform SM 9222B RESULT < 20 20 YesR EH-410 CRW 4/6/2005 10:40 Total Coliform SM 9222B RESULT None 3 1 75 LR EH-420 CSDO 4/6/2005 10:07 Enterococcus SM 9230C RESULT None 400 20 YesR EH-420 CRW 4/6/2005 10:05 Enterococcus SM 9230C RESULT None 6 1 75 LR EH-420 CSDO 4/6/2005 10:07 Fecal Coliform SM 9222D RESULT None 900 20 YesR EH-420 CRW 4/6/2005 10:05 Fecal Coliform SM 9222D RESULT None 18 1 75 LR EH-420 CSDO 4/6/2005 10:07 Total Coliform SM 9222B RESULT None 6,700 20 YesR EH-420 CRW 4/6/2005 10:05 Total Coliform SM 9222B RESULT None 89 1 75 LR EH-420 CSDO 4/12/2005 10:10 Enterococcus SM 9230C RESULT None 650 20 YesR EH-420 CRW 4/12/2005 10:07 Enterococcus SM 9230C RESULT None 64 1 75 LR EH-420 CSDO 4/12/2005 10:10 Fecal Coliform SM 9222D RESULT None 3300 20 YesR EH-420 CRW 4/12/2005 10:07 Fecal Coliform SM 9222D RESULT None 35 1 75 LR EH-420 CSDO 4/12/2005 10:10 Total Coliform SM 9222B RESULT None 4,700 20 YesR EH-420 CRW 4/12/2005 10:07 Total Coliform SM 9222B RESULT None 56 1 75 LR EH-420 CSDO 4/19/2005 11:20 Enterococcus SM 9230C RESULT None 420 20 YesR EH-420 CRW 4/19/2005 11:15 Enterococcus SM 9230C RESULT None 128 1 75 LR EH-420 CSDO 4/19/2005 11:20 Fecal Coliform SM 9222D RESULT None 1750 20 YesR EH-420 CRW 4/19/2005 11:15 Fecal Coliform SM 9222D RESULT None 79 1 75 LR EH-420 CSDO 4/19/2005 11:20 Total Coliform SM 9222B RESULT None 2,800 20 YesR EH-420 CRW 4/19/2005 11:15 Total Coliform SM 9222B RESULT None 78 1 75 LR EH-403 CSDO 4/20/2005 10:35 Enterococcus SM 9230C RESULT < 20 20 YesR EH-403 CRW 4/20/2005 10:33 Enterococcus SM 9230C RESULT < 1 1 75 LR EH-403 CSDO 4/20/2005 10:35 Fecal Coliform SM 9222D RESULT None 40 20 YesR EH-403 CRW 4/20/2005 10:33 Fecal Coliform SM 9222D RESULT < 1 1 75 LR EH-403 CSDO 4/20/2005 10:35 Total Coliform SM 9222B RESULT None 140 20 YesR EH-403 CRW 4/20/2005 10:33 Total Coliform SM 9222B RESULT < 1 1 75 LF EH-420 CSDO 4/20/2005 11:25 Enterococcus SM 9230C RESULT None 240 20 YesF EH-420 CRW 4/20/2005 11:20 Enterococcus SM 9230C RESULT None 5 1 75 LF EH-420 CRW 4/20/2005 11:22 Enterococcus SM 9230C RESULT < 4 4 0 MF EH-420 CRW 4/20/2005 11:23 Enterococcus SM 9230C RESULT None 1 1 75 RF EH-420 CSDO 4/20/2005 11:25 Fecal Coliform SM 9222D RESULT None 1750 20 YesEN04-05 DataPage 43 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterF EH-420 CRW 4/20/2005 11:20 Fecal Coliform SM 9222D RESULT None 43 1 75 LF EH-420 CRW 4/20/2005 11:22 Fecal Coliform SM 9222D RESULT None 12 1 0 MF EH-420 CRW 4/20/2005 11:23 Fecal Coliform SM 9222D RESULT None 2 1 75 RF EH-420 CSDO 4/20/2005 11:25 Total Coliform SM 9222B RESULT None 3,000 20 YesF EH-420 CRW 4/20/2005 11:20 Total Coliform SM 9222B RESULT None 75 1 75 LF EH-420 CRW 4/20/2005 11:22 Total Coliform SM 9222B RESULT None 64 1 0 MF EH-420 CRW 4/20/2005 11:23 Total Coliform SM 9222B RESULT None 5 1 75 RREH-403CSDO5/2/200511:55 Enterococcus SM 9230C RESULT None 60 10 YesREH-403CRW5/2/200511:57 Enterococcus SM 9230C RESULT < 1 1 75 R REH-403CSDO5/2/200511:55 Fecal Coliform SM 9222D RESULT None 80 10 YesREH-403CRW5/2/200511:57 Fecal Coliform SM 9222D RESULT < 1 1 75 R REH-403CSDO5/2/200511:55 Total Coliform SM 9222B RESULT None 800 10 YesREH-403CRW5/2/200511:57 Total Coliform SM 9222B RESULT < 1 1 75 R REH-410CSDO5/2/200511:39 Enterococcus SM 9230C RESULT < 20 20 YesREH-410CRW5/2/200511:35 Enterococcus SM 9230C RESULT none 1 1 75 R REH-410CSDO5/2/200511:39 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-410CRW5/2/200511:35 Fecal Coliform SM 9222D RESULT < 1 1 75 R REH-410CSDO5/2/200511:39 Total Coliform SM 9222B RESULT < 20 20 YesREH-410CRW5/2/200511:35 Total Coliform SM 9222B RESULT < 1 1 75 R REH-420CSDO5/2/200510:54 Enterococcus SM 9230C RESULT none 200 100 YesREH-420CRW5/2/200510:59 Enterococcus SM 9230C RESULT None 3 1 75 R REH-420CSDO5/2/200510:54 Fecal Coliform SM 9222D RESULT none 1600 100 YesREH-420CRW5/2/200510:59 Fecal Coliform SM 9222D RESULT < 1 1 75 R REH-420CSDO5/2/200510:54 Total Coliform SM 9222B RESULT none 4300 100 YesREH-420CRW5/2/200510:59 Total Coliform SM 9222B RESULT None 3 1 75 R REH-420CSDO 05/11/05 10:48 Enterococcus SM 9230C RESULT None 120 20 YesREH-420CRW 05/11/05 10:40 Enterococcus SM 9230C RESULT None 8 1 75 LREH-420CSDO 05/11/05 10:48 Fecal Coliform SM 9222D RESULT None 250 20 YesREH-420CRW 05/11/05 10:40 Fecal Coliform SM 9222D RESULT None 5 1 75 LREH-420CSDO 05/11/05 10:48 Total Coliform SM 9222B RESULT None 3400 20 YesREH-420CRW 05/11/05 10:40 Total Coliform SM 9222B RESULT None 33 1 75 LREH-420CSDO 5/16/2005 10:57 Enterococcus SM 9230C RESULT None 160 100 YesREH-420CRW 5/16/2005 11:00 Enterococcus SM 9230C RESULT < 1 1 75 RREH-420CSDO 5/16/2005 10:57 Fecal Coliform SM 9222D RESULT None 1200 100 YesREH-420CRW 5/16/2005 11:00 Fecal Coliform SM 9222D RESULT None 1 1 75 RREH-420CSDO 5/16/2005 10:57 Total Coliform SM 9222B RESULT None 14300 100 YesREH-420CRW 5/16/2005 11:00 Total Coliform SM 9222B RESULT None 11 1 75 REN04-05 DataPage 44 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-420CSDO 05/25/05 10:57 Enterococcus SM 9230C RESULT None 240 100 YesREH-420CRW 05/25/05 11:00 Enterococcus SM 9230C RESULT None 13 1 75 LREH-420CSDO 05/25/05 10:57 Fecal Coliform SM 9222D RESULT None 800 100 YesREH-420CRW 05/25/05 11:00 Fecal Coliform SM 9222D RESULT None 17 1 75 LREH-420CSDO 05/25/05 10:57 Total Coliform SM 9222B RESULT None 4400 100 YesREH-420CRW 05/25/05 11:00 Total Coliform SM 9222B RESULT None 4 1 75 LREH-403CSDO 06/01/05 9:53 Enterococcus SM 9230C RESULT < 20 20 YesREH-403CRW 06/01/05 9:55 Enterococcus SM 9230C RESULT < 1 1 75 LREH-403CSDO 06/01/05 9:53 Fecal Coliform SM 9222D RESULT None 140 10 YesREH-403CRW 06/01/05 9:55 Fecal Coliform SM 9222D RESULT None 1 1 75 LREH-403CSDO 06/01/05 9:53 Total Coliform SM 9222B RESULT None 200 10 YesREH-403CRW 06/01/05 9:55 Total Coliform SM 9222B RESULT < 1 1 75 LREH-410CSDO 06/01/05 9:35 Enterococcus SM 9230C RESULT None 20 10 YesREH-410CRW 06/01/05 9:40 Enterococcus SM 9230C RESULT < 1 1 75 LREH-410CSDO 06/01/05 9:35 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-410CRW 06/01/05 9:40 Fecal Coliform SM 9222D RESULT < 1 1 75 LREH-410CSDO 06/01/05 9:35 Total Coliform SM 9222B RESULT None 20 10 YesREH-410CRW 06/01/05 9:40 Total Coliform SM 9222B RESULT < 1 1 75 LREH-420CSDO 06/01/05 10:32 Enterococcus SM 9230C RESULT None 1620 100 YesREH-420CRW 06/01/05 10:35 Enterococcus SM 9230C RESULT None 3 1 75 LREH-420CSDO 06/01/05 10:32 Fecal Coliform SM 9222D RESULT None 1950 100 YesREH-420CRW 06/01/05 10:35 Fecal Coliform SM 9222D RESULT None 1 1 75 LREH-420CSDO 06/01/05 10:32 Total Coliform SM 9222B RESULT None 1400 100 YesREH-420CRW 06/01/05 10:35 Total Coliform SM 9222B RESULT None 9 1 75 LREH-420CSDO 06/16/05 10:55 Enterococcus SM 9230C RESULT None 220 100 YesREH-420CRW 06/16/05 10:59 Enterococcus SM 9230C RESULT None 29 1 75 RREH-420CSDO 06/16/05 10:55 Fecal Coliform SM 9222D RESULT None 250 100 YesREH-420CRW 06/16/05 10:59 Fecal Coliform SM 9222D RESULT None 11 1 75 RREH-420CSDO 06/16/05 10:55 Total Coliform SM 9222B RESULT None 2800 100 YesREH-420CRW 06/16/05 10:59 Total Coliform SM 9222B RESULT None 20 1 75 RREH-420CSDO 06/22/05 11:05 Enterococcus SM 9230C RESULT None 400 100 YesREH-420CRW 06/22/05 11:00 Enterococcus SM 9230C RESULT None 2 1 75 LREH-420CSDO 06/22/05 11:05 Fecal Coliform SM 9222D RESULT None 950 100 YesREH-420CRW 06/22/05 11:00 Fecal Coliform SM 9222D RESULT None 14 1 75 LREH-420CSDO 06/22/05 11:05 Total Coliform SM 9222B RESULT None 2800 100 YesREH-420CRW 06/22/05 11:00 Total Coliform SM 9222B RESULT None 16 1 75 LREH-403CSDO 06/29/05 11:36 Enterococcus SM 9230C RESULT None 140 10 YesEN04-05 DataPage 45 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-403CRW 06/29/05 11:33 Enterococcus SM 9230C RESULT < 2 2 75 RREH-403CSDO 06/29/05 11:36 Fecal Coliform SM 9222D RESULT None 40 10 YesREH-403CRW 06/29/05 11:33 Fecal Coliform SM 9222D RESULT < 2 2 75 RREH-403CSDO 06/29/05 11:36 Total Coliform SM 9222B RESULT None 60 10 YesREH-403CRW 06/29/05 11:33 Total Coliform SM 9222B RESULT < 2 2 75 RREH-420CSDO 06/29/05 11:07 Enterococcus SM 9230C RESULT None 160 100 YesREH-420CRW 06/29/05 10:56 Enterococcus SM 9230C RESULT None 4 1 75 RREH-420CSDO 06/29/05 11:07 Fecal Coliform SM 9222D RESULT None 560 100 YesREH-420CRW 06/29/05 10:56 Fecal Coliform SM 9222D RESULT None 10 1 75 RREH-420CSDO 06/29/05 11:07 Total Coliform SM 9222B RESULT None 2900 100 YesREH-420CRW 06/29/05 10:56 Total Coliform SM 9222B RESULT None 10 1 75 RREH-420CSDO 07/06/05 11:01 Enterococcus SM 9230C RESULT None 170 100 YesREH-420CRW 07/06/05 10:57 Enterococcus SM 9230C RESULT < 2 2 75 LREH-420CSDO 07/06/05 11:01 Fecal Coliform SM 9222D RESULT None 150 100 YesREH-420CRW 07/06/05 10:57 Fecal Coliform SM 9222D RESULT None 24 1 75 LREH-420CSDO 07/06/05 11:01 Total Coliform SM 9222B RESULT None 3300 100 YesREH-420CRW 07/06/05 10:57 Total Coliform SM 9222B RESULT None 2 1 75 LREH-420CSDO 07/12/05 10:05 Enterococcus SM 9230C RESULT None 240 100 YesREH-420CRW 07/12/05 10:00 Enterococcus SM 9230C RESULT < 4 4 75 RREH-420CSDO 07/12/05 10:05 Fecal Coliform SM 9222D RESULT None 260 100 YesREH-420CRW 07/12/05 10:00 Fecal Coliform SM 9222D RESULT < 4 4 75 RREH-420CSDO 07/12/05 10:05 Total Coliform SM 9222B RESULT None 3500 100 YesREH-420CRW 07/12/05 10:00 Total Coliform SM 9222B RESULT None 8 1 75 RREH-403CSDO 07/14/05 10:54 Enterococcus SM 9230C RESULT None 60 20 YesREH-403CRW 07/14/05 10:45 Enterococcus SM 9230C RESULT < 4 4 75 LREH-403CSDO 07/14/05 10:54 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-403CRW 07/14/05 10:45 Fecal Coliform SM 9222D RESULT < 4 4 75 LREH-403CSDO 07/14/05 10:54 Total Coliform SM 9222B RESULT None 1440 20 YesREH-403CRW 07/14/05 10:45 Total Coliform SM 9222B RESULT < 4 4 75 LREH-405CSDO 07/14/05 10:38 Enterococcus SM 9230C RESULT < 20 20 YesREH-405CRW 07/14/05 10:35 Enterococcus SM 9230C RESULT < 4 4 75 LREH-405CSDO 07/14/05 10:38 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-405CRW 07/14/05 10:35 Fecal Coliform SM 9222D RESULT < 4 4 75 LREH-405CSDO 07/14/05 10:38 Total Coliform SM 9222B RESULT < 20 20 YesREH-405CRW 07/14/05 10:35 Total Coliform SM 9222B RESULT < 4 4 75 LREH-410CSDO 07/14/05 10:18 Enterococcus SM 9230C RESULT None 200 20 YesREH-410CRW 07/14/05 10:15 Enterococcus SM 9230C RESULT None 4 4 75 REN04-05 DataPage 46 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-410CSDO 07/14/05 10:18 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-410CRW 07/14/05 10:15 Fecal Coliform SM 9222D RESULT None 12 4 75 RREH-410CSDO 07/14/05 10:18 Total Coliform SM 9222B RESULT < 20 20 YesREH-410CRW 07/14/05 10:15 Total Coliform SM 9222B RESULT None 20 4 75 RREH-420CSDO 07/20/05 10:53 Enterococcus SM 9230C RESULT None 340 20 YesREH-420CRW 07/20/05 10:48 Enterococcus SM 9230C RESULT None 3 1 75 LREH-420CSDO 07/20/05 10:53 Fecal Coliform SM 9222D RESULT None 250 50 YesREH-420CRW 07/20/05 10:48 Fecal Coliform SM 9222D RESULT None 10 1 75 LREH-420CSDO 07/20/05 10:53 Total Coliform SM 9222B RESULT None 4200 100 YesREH-420CRW 07/20/05 10:48 Total Coliform SM 9222B RESULT None 44 1 75 LREH-420CSDO 07/27/05 10:54 Enterococcus SM 9230C RESULT None 160 20 YesREH-420CRW 07/27/05 10:40 Enterococcus SM 9230C RESULT < 1 1 75 RREH-420CSDO 07/27/05 10:54 Fecal Coliform SM 9222D RESULT None 3000 50 YesREH-420CRW 07/27/05 10:40 Fecal Coliform SM 9222D RESULT None 3 1 75 RREH-420CSDO 07/27/05 10:54 Total Coliform SM 9222B RESULT None 3000 100 YesREH-420CRW 07/27/05 10:40 Total Coliform SM 9222B RESULT < 1 1 75 RREH-420CSDO 08/03/05 11:03 Enterococcus SM 9230C RESULT None 240 20 YesREH-420CRW 08/03/05 10:58 Enterococcus SM 9230C RESULT None 1 1 75 RREH-420CSDO 08/03/05 11:03 Fecal Coliform SM 9222D RESULT None 150 50 YesREH-420CRW 08/03/05 10:58 Fecal Coliform SM 9222D RESULT None 1 1 75 RREH-420CSDO 08/03/05 11:03 Total Coliform SM 9222B RESULT None 3600 100 YesREH-420CRW 08/03/05 10:58 Total Coliform SM 9222B RESULT None 11 1 75 RREH-403CSDO 08/10/05 11:46 Enterococcus SM 9230C RESULT < 20 20 YesREH-403CRW 08/10/05 11:44 Enterococcus SM 9230C RESULT < 20 20 75 RREH-403CSDO 08/10/05 11:46 Fecal Coliform SM 9222D RESULT None 100 20 YesREH-403CRW 08/10/05 11:44 Fecal Coliform SM 9222D RESULT < 20 20 75 RREH-403CSDO 08/10/05 11:46 Total Coliform SM 9222B RESULT None 360 20 YesREH-403CRW 08/10/05 11:44 Total Coliform SM 9222B RESULT None 20 20 75 RREH-410CSDO 08/10/05 11:10 Enterococcus SM 9230C RESULT < 20 20 YesREH-410CRW 08/10/05 11:06 Enterococcus SM 9230C RESULT < 4 4 75 RREH-410CSDO 08/10/05 11:10 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-410CRW 08/10/05 11:06 Fecal Coliform SM 9222D RESULT < 4 4 75 RREH-410CSDO 08/10/05 11:10 Total Coliform SM 9222B RESULT < 20 20 YesREH-410CRW 08/10/05 11:06 Total Coliform SM 9222B RESULT < 4 4 75 RREH-420CSDO 08/10/05 10:47 Enterococcus SM 9230C RESULT None 320 20 YesREH-420CRW 08/10/05 10:42 Enterococcus SM 9230C RESULT None 10 1 75 RREH-420CSDO 08/10/05 10:47 Fecal Coliform SM 9222D RESULT None 6600 50 YesEN04-05 DataPage 47 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-420CRW 08/10/05 10:42 Fecal Coliform SM 9222D RESULT None 60 1 75 RREH-420CSDO 08/10/05 10:47 Total Coliform SM 9222B RESULT None 8100 100 YesREH-420CRW 08/10/05 10:42 Total Coliform SM 9222B RESULT None 110 1 75 RREH-420CSDO 08/24/05 10:51 Enterococcus SM 9230C RESULT None 620 20 YesREH-420CRW 08/24/05 10:45 Enterococcus SM 9230C RESULT None 23 1 75 RREH-420CSDO 08/24/05 10:51 Fecal Coliform SM 9222D RESULT None 2500 50 YesREH-420CRW 08/24/05 10:45 Fecal Coliform SM 9222D RESULT None 31 1 75 RREH-420CSDO 08/24/05 10:51 Total Coliform SM 9222B RESULT None 4800 100 YesREH-420CRW 08/24/05 10:45 Total Coliform SM 9222B RESULT None 33 1 75 RREH-420CSDO 08/31/05 10:38 Enterococcus SM 9230C RESULT None 1880 20 YesREH-420CRW 08/31/05 10:37 Enterococcus SM 9230C RESULT None 6 1 75 RREH-420CSDO 08/31/05 10:38 Fecal Coliform SM 9222D RESULT None 800 50 YesREH-420CRW 08/31/05 10:37 Fecal Coliform SM 9222D RESULT None 2 1 75 RREH-420CSDO 08/31/05 10:38 Total Coliform SM 9222B RESULT None 13400 100 YesREH-420CRW 08/31/05 10:37 Total Coliform SM 9222B RESULT None 2 1 75 RREH-403CSDO 09/07/05 11:10 Enterococcus SM 9230C RESULT None 20 20 YesREH-403CRW 09/07/05 11:08 Enterococcus SM 9230C RESULT None 4 20 75 LREH-403CSDO 09/07/05 11:10 Fecal Coliform SM 9222D RESULT None 20 20 YesREH-403CRW 09/07/05 11:08 Fecal Coliform SM 9222D RESULT None 1 20 75 LREH-403CSDO 09/07/05 11:10 Total Coliform SM 9222B RESULT None 260 20 YesREH-403CRW 09/07/05 11:08 Total Coliform SM 9222B RESULT None 1 20 75 LREH-410CSDO 09/07/05 11:33 Enterococcus SM 9230C RESULT < 20 20 YesREH-410CRW 09/07/05 11:30 Enterococcus SM 9230C RESULT None 13 4 75 LREH-410CSDO 09/07/05 11:33 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-410CRW 09/07/05 11:30 Fecal Coliform SM 9222D RESULT None 4 4 75 LREH-410CSDO 09/07/05 11:33 Total Coliform SM 9222B RESULT None 40 20 YesREH-410CRW 09/07/05 11:30 Total Coliform SM 9222B RESULT < 1 1 75 LREH-420CSDO 09/07/05 10:43 Enterococcus SM 9230C RESULT None 940 20 YesREH-420CRW 09/07/05 10:50 Enterococcus SM 9230C RESULT None 2 1 75 RREH-420CSDO 09/07/05 10:43 Fecal Coliform SM 9222D RESULT None 200 50 YesREH-420CRW 09/07/05 10:50 Fecal Coliform SM 9222D RESULT None 1 1 75 RREH-420CSDO 09/07/05 10:43 Total Coliform SM 9222B RESULT None 8400 100 YesREH-420CRW 09/07/05 10:50 Total Coliform SM 9222B RESULT < 1 1 75 RREH-420CSDO 09/14/05 11:02 Enterococcus SM 9230C RESULT None 1460 20 YesREH-420CRW 09/14/05 10:58 Enterococcus SM 9230C RESULT None 23 1 75 LREH-420CSDO 09/14/05 11:02 Fecal Coliform SM 9222D RESULT None 5100 50 YesREH-420CRW 09/14/05 10:58 Fecal Coliform SM 9222D RESULT None 62 1 75 LEN04-05 DataPage 48 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-420CSDO 09/14/05 11:02 Total Coliform SM 9222B RESULT None 7500 100 YesREH-420CRW 09/14/05 10:58 Total Coliform SM 9222B RESULT None 27 1 75 LREH-420CSDO 09/28/05 10:27 Enterococcus SM 9230C RESULT None 750 20 YesREH-420CRW 09/28/05 10:18 Enterococcus SM 9230C RESULT None 84 1 75 LREH-420CSDO 09/28/05 10:27 Fecal Coliform SM 9222D RESULT None 2900 50 YesREH-420CRW 09/28/05 10:18 Fecal Coliform SM 9222D RESULT None 141 1 75 LREH-420CSDO 09/28/05 10:27 Total Coliform SM 9222B RESULT None 13200 100 YesREH-420CRW 09/28/05 10:18 Total Coliform SM 9222B RESULT None 27 1 75 LREH-403CSDO 10/12/05 11:42 Enterococcus SM 9230C RESULT None 40 20 YesREH-403CRW 10/12/05 11:40 Enterococcus SM 9230C RESULT < 1 1 75 LREH-403CSDO 10/12/05 11:42 Fecal Coliform SM 9222D RESULT None 60 20 YesREH-403CRW 10/12/05 11:40 Fecal Coliform SM 9222D RESULT < 1 1 75 LREH-403CSDO 10/12/05 11:42 Total Coliform SM 9222B RESULT None 160 20 YesREH-403CRW 10/12/05 11:40 Total Coliform SM 9222B RESULT < 1 1 75 LREH-405CSDO 10/12/05 11:32 Enterococcus SM 9230C RESULT < 20 20 YesREH-405CRW 10/12/05 11:30 Enterococcus SM 9230C RESULT < 1 1 75 LREH-405CSDO 10/12/05 11:32 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-405CRW 10/12/05 11:30 Fecal Coliform SM 9222D RESULT < 1 1 75 LREH-405CSDO 10/12/05 11:32 Total Coliform SM 9222B RESULT None 80 20 YesREH-405CRW 10/12/05 11:30 Total Coliform SM 9222B RESULT < 1 1 75 LREH-410CSDO 10/12/05 11:22 Enterococcus SM 9230C RESULT < 20 20 YesREH-410CRW 10/12/05 11:18 Enterococcus SM 9230C RESULT < 1 1 75 LREH-410CSDO 10/12/05 11:22 Fecal Coliform SM 9222D RESULT < 20 20 YesREH-410CRW 10/12/05 11:18 Fecal Coliform SM 9222D RESULT < 1 1 75 LREH-410CSDO 10/12/05 11:22 Total Coliform SM 9222B RESULT < 20 20 YesREH-410CRW 10/12/05 11:18 Total Coliform SM 9222B RESULT None 2 1 75 LREH-420CSDO 10/12/05 10:50 Enterococcus SM 9230C RESULT None 680 20 YesREH-420CRW 10/12/05 10:57 Enterococcus SM 9230C RESULT None 13 1 75 LREH-420CSDO 10/12/05 10:50 Fecal Coliform SM 9222D RESULT None 1350 50 YesREH-420CRW 10/12/05 10:57 Fecal Coliform SM 9222D RESULT None 69 1 75 LREH-420CSDO 10/12/05 10:50 Total Coliform SM 9222B RESULT None 14500 100 YesREH-420CRW 10/12/05 10:57 Total Coliform SM 9222B RESULT None 79 1 75 LREH-420CSDO 10/24/05 10:42 Enterococcus SM 9230C RESULT None 200 20 YesREH-420CRW 10/24/05 10:48 Enterococcus SM 9230C RESULT < 1 1 75 LREH-420CSDO 10/24/05 10:42 Fecal Coliform SM 9222D RESULT None 300 50 YesREH-420CRW 10/24/05 10:48 Fecal Coliform SM 9222D RESULT < 1 1 75 LREH-420CSDO 10/24/05 10:42 Total Coliform SM 9222B RESULT None 5900 100 YesEN04-05 DataPage 49 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterREH-420CRW 10/24/05 10:48 Total Coliform SM 9222B RESULT None 7 1 75 LEN04-05 DataPage 50 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-1 LSDO 11/3/2004 12:35 Enterococcus SM 9230C RESULT None 100 50 NoR CBS-1 LRW 11/3/2004 12:30 Enterococcus SM 9230C RESULT None 88 4 0 MR CBS-1 LSDO 11/3/2004 12:35 Fecal Coliform SM 9222D RESULT None 1000 50 NoR CBS-1 LRW 11/3/2004 12:30 Fecal Coliform SM 9222D RESULT None 270 10 0 MR CBS-1 LSDO 11/3/2004 12:35 Total Coliform SM 9222B RESULT None 4100 100 NoR CBS-1 LRW 11/3/2004 12:30 Total Coliform SM 9222B RESULT None 230 10 0 MR CBS-2 LSDO 11/3/2004 12:18 Enterococcus SM 9230C RESULT None 300 50 YesR CBS-2 LRW 11/3/2004 12:17 Enterococcus SM 9230C RESULT None 20 4 0 MR CBS-2 LSDO 11/3/2004 12:18 Fecal Coliform SM 9222D RESULT None 2050 50 YesR CBS-2 LRW 11/3/2004 12:17 Fecal Coliform SM 9222D RESULT None 70 10 0 MR CBS-2 LSDO 11/3/2004 12:18 Total Coliform SM 9222B RESULT None 5500 100 YesR CBS-2 LRW 11/3/2004 12:17 Total Coliform SM 9222B RESULT None 200 10 0 MR SEL-1 LSDO 11/3/2004 12:25 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 11/3/2004 12:25 Enterococcus SM 9230C RESULT NS -99R SEL-1 LSDO 11/3/2004 12:25 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 11/3/2004 12:25 Fecal Coliform SM 9222D RESULT NS -99R SEL-1 LSDO 11/3/2004 12:25 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 11/3/2004 12:25 Total Coliform SM 9222B RESULT NS -99R SEL-2 LSDO 11/3/2004 12:40 Enterococcus SM 9230C RESULT None 400 50 NoR SEL-2 LRW 11/3/2004 12:40 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 11/3/2004 12:40 Fecal Coliform SM 9222D RESULT None 850 50 NoR SEL-2 LRW 11/3/2004 12:40 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 11/3/2004 12:40 Total Coliform SM 9222B RESULT None 1400 100 NoR SEL-2 LRW 11/3/2004 12:40 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 11/3/2004 12:48 Enterococcus SM 9230C RESULT None 300 50 NoR SEL-3 LRW 11/3/2004 12:48 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 11/3/2004 12:48 Fecal Coliform SM 9222D RESULT None 1400 50 NoR SEL-3 LRW 11/3/2004 12:48 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 11/3/2004 12:48 Total Coliform SM 9222B RESULT None 2,200 100 NoR SEL-3 LRW 11/3/2004 12:48 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 12/16/2004 11:20 Enterococcus SM 9230C RESULT None 650 50 NoR CBS-1 LRW 12/16/2004 11:15 Enterococcus SM 9230C RESULT None 64 4 0 MR CBS-1 LSDO 12/16/2004 11:20 Fecal Coliform SM 9222D RESULT None 550 50 NoR CBS-1 LRW 12/16/2004 11:15 Fecal Coliform SM 9222D RESULT None 110 10 0 MR CBS-1 LSDO 12/16/2004 11:20 Total Coliform SM 9222B RESULT None 1900 100 NoR CBS-1 LRW 12/16/2004 11:15 Total Coliform SM 9222B RESULT None 310 10 0 MR CBS-2 LSDO 12/16/2004 12:34 Enterococcus SM 9230C RESULT None 400 50 YesEN04-05 DataPage 51 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-2 LRW 12/16/2004 12:35 Enterococcus SM 9230C RESULT None 4 4 0 MR CBS-2 LSDO 12/16/2004 12:34 Fecal Coliform SM 9222D RESULT < 50 50 YesR CBS-2 LRW 12/16/2004 12:35 Fecal Coliform SM 9222D RESULT None 20 10 0 MR CBS-2 LSDO 12/16/2004 12:34 Total Coliform SM 9222B RESULT None 100 100 YesR CBS-2 LRW 12/16/2004 12:35 Total Coliform SM 9222B RESULT None 10 10 0 MR SEL-1 LSDO 12/16/2004 11:10 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 12/16/2004 11:10 Enterococcus SM 9230C RESULT NS -99R SEL-1 LSDO 12/16/2004 11:10 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 12/16/2004 11:10 Fecal Coliform SM 9222D RESULT NS -99R SEL-1 LSDO 12/16/2004 11:10 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 12/16/2004 11:10 Total Coliform SM 9222B RESULT NS -99R SEL-2 LSDO 12/16/2004 11:27 Enterococcus SM 9230C RESULT None 100 50 NoR SEL-2 LRW 12/16/2004 11:27 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 12/16/2004 11:27 Fecal Coliform SM 9222D RESULT None 250 50 NoR SEL-2 LRW 12/16/2004 11:27 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 12/16/2004 11:27 Total Coliform SM 9222B RESULT None 1400 100 NoR SEL-2 LRW 12/16/2004 11:27 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 12/16/2004 11:35 Enterococcus SM 9230C RESULT < 50 50 NoR SEL-3 LRW 12/16/2004 11:35 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 12/16/2004 11:35 Fecal Coliform SM 9222D RESULT None 100 50 NoR SEL-3 LRW 12/16/2004 11:35 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 12/16/2004 11:35 Total Coliform SM 9222B RESULT None 400 100 NoR SEL-3 LRW 12/16/2004 11:35 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 1/19/2005 13:15 Enterococcus SM 9230C RESULT None 480 20 NoR CBS-1 LRW 1/19/2005 13:20 Enterococcus SM 9230C RESULT None 190 10 0 MR CBS-1 LSDO 1/19/2005 13:15 Fecal Coliform SM 9222D RESULT None 420 20 NoR CBS-1 LRW 1/19/2005 13:20 Fecal Coliform SM 9222D RESULT None 340 10 0 MR CBS-1 LSDO 1/19/2005 13:15 Total Coliform SM 9222B RESULT None 1600 100 NoR CBS-1 LRW 1/19/2005 13:20 Total Coliform SM 9222B RESULT None 440 10 0 MR CBS-2 LSDO 1/19/2005 13:50 Enterococcus SM 9230C RESULT None 540 20 YesR CBS-2 LRW 1/19/2005 14:00 Enterococcus SM 9230C RESULT None 520 10 0 MR CBS-2 LSDO 1/19/2005 13:50 Fecal Coliform SM 9222D RESULT None 440 20 YesR CBS-2 LRW 1/19/2005 14:00 Fecal Coliform SM 9222D RESULT None 690 10 0 MR CBS-2 LSDO 1/19/2005 13:50 Total Coliform SM 9222B RESULT None 3000 20 YesR CBS-2 LRW 1/19/2005 14:00 Total Coliform SM 9222B RESULT None 300 10 0 MR SEL-2 LSDO 1/19/2005 13:10 Enterococcus SM 9230C RESULT None 140 20 NoR SEL-2 LRW 1/19/2005 13:10 Enterococcus SM 9230C RESULT NS -99EN04-05 DataPage 52 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-2 LSDO 1/19/2005 13:10 Fecal Coliform SM 9222D RESULT None 80 20 NoR SEL-2 LRW 1/19/2005 13:10 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 1/19/2005 13:10 Total Coliform SM 9222B RESULT None 650 50 NoR SEL-2 LRW 1/19/2005 13:10 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 1/19/2005 13:00 Enterococcus SM 9230C RESULT None 40 20 NoR SEL-3 LRW 1/19/2005 13:00 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 1/19/2005 13:00 Fecal Coliform SM 9222D RESULT None 240 20 NoR SEL-3 LRW 1/19/2005 13:00 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 1/19/2005 13:00 Total Coliform SM 9222B RESULT None 780 20 NoR SEL-3 LRW 1/19/2005 13:00 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 2/2/2005 11:00 Enterococcus SM 9230C RESULT None 120 20 NoR CBS-1 LRW 2/2/2005 10:55 Enterococcus SM 9230C RESULT None 100 10 0 MR CBS-1 LSDO 2/2/2005 11:00 Fecal Coliform SM 9222D RESULT None 1220 20 NoR CBS-1 LRW 2/2/2005 10:55 Fecal Coliform SM 9222D RESULT None 370 10 0 MR CBS-1 LSDO 2/2/2005 11:00 Total Coliform SM 9222B RESULT None 8400 100 NoR CBS-1 LRW 2/2/2005 10:55 Total Coliform SM 9222B RESULT None 120 10 0 MR CBS-2 LSDO 2/2/2005 10:43 Enterococcus SM 9230C RESULT None 200 20 YesR CBS-2 LRW 2/2/2005 10:41 Enterococcus SM 9230C RESULT None 80 10 0 MR CBS-2 LSDO 2/2/2005 10:43 Fecal Coliform SM 9222D RESULT None 100 20 YesR CBS-2 LRW 2/2/2005 10:41 Fecal Coliform SM 9222D RESULT None 660 10 0 MR CBS-2 LSDO 2/2/2005 10:43 Total Coliform SM 9222B RESULT None 9460 20 YesR CBS-2 LRW 2/2/2005 10:41 Total Coliform SM 9222B RESULT None 710 10 0 MR SEL-1 LSDO 2/2/2005 10:50 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 2/2/2005 10:50 Enterococcus SM 9230C RESULT NS -99R SEL-1 LSDO 2/2/2005 10:50 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 2/2/2005 10:50 Fecal Coliform SM 9222D RESULT NS -99R SEL-1 LSDO 2/2/2005 10:50 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 2/2/2005 10:50 Total Coliform SM 9222B RESULT NS -99R SEL-2 LSDO 2/2/2005 11:04 Enterococcus SM 9230C RESULT None 160 20 NoR SEL-2 LRW 2/2/2005 11:04 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 2/2/2005 11:04 Fecal Coliform SM 9222D RESULT None 140 20 NoR SEL-2 LRW 2/2/2005 11:04 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 2/2/2005 11:04 Total Coliform SM 9222B RESULT None 4600 50 NoR SEL-2 LRW 2/2/2005 11:04 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 2/2/2005 11:10 Enterococcus SM 9230C RESULT < 20 20 NoR SEL-3 LRW 2/2/2005 11:10 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 2/2/2005 11:10 Fecal Coliform SM 9222D RESULT None 140 20 NoEN04-05 DataPage 53 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-3 LRW 2/2/2005 11:10 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 2/2/2005 11:10 Total Coliform SM 9222B RESULT None 220 20 NoR SEL-3 LRW 2/2/2005 11:10 Total Coliform SM 9222B RESULT NS -99R CBS-2 LSDO 2/9/2005 11:19 Enterococcus SM 9230C RESULT None 300 20 YesR CBS-2 LRW 2/9/2005 11:18 Enterococcus SM 9230C RESULT None 60 10 0 MR CBS-2 LSDO 2/9/2005 11:19 Fecal Coliform SM 9222D RESULT None 60 20 YesR CBS-2 LRW 2/9/2005 11:18 Fecal Coliform SM 9222D RESULT None 20 10 0 MR CBS-2 LSDO 2/9/2005 11:19 Total Coliform SM 9222B RESULT None 3720 20 YesR CBS-2 LRW 2/9/2005 11:18 Total Coliform SM 9222B RESULT None 130 10 0 MR CBS-1 LSDO 3/9/2005 12:08 Enterococcus SM 9230C RESULT None 60 20 NoR CBS-1 LRW 3/9/2005 12:04 Enterococcus SM 9230C RESULT None 590 10 0 MR CBS-1 LSDO 3/9/2005 12:08 Fecal Coliform SM 9222D RESULT None 60 20 NoR CBS-1 LRW 3/9/2005 12:04 Fecal Coliform SM 9222D RESULT None 530 10 0 MR CBS-1 LSDO 3/9/2005 12:08 Total Coliform SM 9222B RESULT None 180 100 NoR CBS-1 LRW 3/9/2005 12:04 Total Coliform SM 9222B RESULT None 360 10 0 MR CBS-2 LSDO 3/9/2005 11:27 Enterococcus SM 9230C RESULT None 200 20 YesR CBS-2 LRW 3/9/2005 11:25 Enterococcus SM 9230C RESULT None 100 10 0 MR CBS-2 LSDO 3/9/2005 11:27 Fecal Coliform SM 9222D RESULT None 1040 20 YesR CBS-2 LRW 3/9/2005 11:25 Fecal Coliform SM 9222D RESULT None 130 10 0 MR CBS-2 LSDO 3/9/2005 11:27 Total Coliform SM 9222B RESULT None 2620 20 YesR CBS-2 LRW 3/9/2005 11:25 Total Coliform SM 9222B RESULT None 660 10 0 MR SEL-1 LSDO 3/9/2005 11:48 Enterococcus SM 9230C RESULT < 20 20 YesR SEL-1 LRW 3/9/2005 11:52 Enterococcus SM 9230C RESULT None 60 4 0 MR SEL-1 LSDO 3/9/2005 11:48 Fecal Coliform SM 9222D RESULT None 40 20 YesR SEL-1 LRW 3/9/2005 11:52 Fecal Coliform SM 9222D RESULT None 192 4 0 MR SEL-1 LSDO 3/9/2005 11:48 Total Coliform SM 9222B RESULT < 100 100 YesR SEL-1 LRW 3/9/2005 11:52 Total Coliform SM 9222B RESULT None 232 4 0 MR SEL-2 LSDO 3/9/2005 12:14 Enterococcus SM 9230C RESULT None 80 20 NoR SEL-2 LRW 3/9/2005 12:14 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 3/9/2005 12:14 Fecal Coliform SM 9222D RESULT None 20 20 NoR SEL-2 LRW 3/9/2005 12:14 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 3/9/2005 12:14 Total Coliform SM 9222B RESULT None 50 50 NoR SEL-2 LRW 3/9/2005 12:14 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 3/9/2005 12:20 Enterococcus SM 9230C RESULT None 20 20 NoR SEL-3 LRW 3/9/2005 12:20 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 3/9/2005 12:20 Fecal Coliform SM 9222D RESULT None 40 20 NoR SEL-3 LRW 3/9/2005 12:20 Fecal Coliform SM 9222D RESULT NS -99EN04-05 DataPage 54 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-3 LSDO 3/9/2005 12:20 Total Coliform SM 9222B RESULT None 1,140 20 NoR SEL-3 LRW 3/9/2005 12:20 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 4/6/2005 12:30 Enterococcus SM 9230C RESULT None 200 20 NoR CBS-1 LRW 4/6/2005 12:25 Enterococcus SM 9230C RESULT < 10 10 0 MR CBS-1 LSDO 4/6/2005 12:30 Fecal Coliform SM 9222D RESULT None 120 20 NoR CBS-1 LRW 4/6/2005 12:25 Fecal Coliform SM 9222D RESULT None 150 10 0 MR CBS-1 LSDO 4/6/2005 12:30 Total Coliform SM 9222B RESULT None 220 20 NoR CBS-1 LRW 4/6/2005 12:25 Total Coliform SM 9222B RESULT None 50 10 0 MR CBS-2 LSDO 4/6/2005 11:50 Enterococcus SM 9230C RESULT None 760 20 YesR CBS-2 LRW 4/6/2005 11:49 Enterococcus SM 9230C RESULT < 20 20 0 MR CBS-2 LSDO 4/6/2005 11:50 Fecal Coliform SM 9222D RESULT None 480 20 YesR CBS-2 LRW 4/6/2005 11:49 Fecal Coliform SM 9222D RESULT None 20 20 0 MR CBS-2 LSDO 4/6/2005 11:50 Total Coliform SM 9222B RESULT None 340 20 YesR CBS-2 LRW 4/6/2005 11:49 Total Coliform SM 9222B RESULT None 20 20 0 MR SEL-1 LSDO 4/6/2005 12:06 Enterococcus SM 9230C RESULT None 20 20 YesR SEL-1 LRW 4/6/2005 12:12 Enterococcus SM 9230C RESULT None 40 10 0 MR SEL-1 LSDO 4/6/2005 12:06 Fecal Coliform SM 9222D RESULT None 140 20 YesR SEL-1 LRW 4/6/2005 12:12 Fecal Coliform SM 9222D RESULT None 70 10 0 MR SEL-1 LSDO 4/6/2005 12:06 Total Coliform SM 9222B RESULT None 180 20 YesR SEL-1 LRW 4/6/2005 12:12 Total Coliform SM 9222B RESULT None 80 10 0 MR SEL-2 LSDO 4/6/2005 12:35 Enterococcus SM 9230C RESULT None 80 20 NoR SEL-2 LRW 4/6/2005 12:35 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 4/6/2005 12:35 Fecal Coliform SM 9222D RESULT < 20 20 NoR SEL-2 LRW 4/6/2005 12:35 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 4/6/2005 12:35 Total Coliform SM 9222B RESULT None 100 20 NoR SEL-2 LRW 4/6/2005 12:35 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 4/6/2005 12:40 Enterococcus SM 9230C RESULT None 1100 20 NoR SEL-3 LRW 4/6/2005 12:40 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 4/6/2005 12:40 Fecal Coliform SM 9222D RESULT None 1620 20 NoR SEL-3 LRW 4/6/2005 12:40 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 4/6/2005 12:40 Total Coliform SM 9222B RESULT None 2,660 20 NoR SEL-3 LRW 4/6/2005 12:40 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 4/20/2005 12:17 Enterococcus SM 9230C RESULT None 2360 20 NoR CBS-1 LRW 4/20/2005 12:10 Enterococcus SM 9230C RESULT None 20 10 0 MR CBS-1 LSDO 4/20/2005 12:17 Fecal Coliform SM 9222D RESULT None 1300 20 NoR CBS-1 LRW 4/20/2005 12:10 Fecal Coliform SM 9222D RESULT None 320 10 0 MR CBS-1 LSDO 4/20/2005 12:17 Total Coliform SM 9222B RESULT None 1400 20 NoEN04-05 DataPage 55 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-1 LRW 4/20/2005 12:10 Total Coliform SM 9222B RESULT None 380 10 0 MR CBS-2 LSDO 4/20/2005 10:55 Enterococcus SM 9230C RESULT None 1700 20 YesR CBS-2 LRW 4/20/2005 10:53 Enterococcus SM 9230C RESULT None 20 20 0 MR CBS-2 LSDO 4/20/2005 10:55 Fecal Coliform SM 9222D RESULT None 550 20 YesR CBS-2 LRW 4/20/2005 10:53 Fecal Coliform SM 9222D RESULT None 60 20 0 MR CBS-2 LSDO 4/20/2005 10:55 Total Coliform SM 9222B RESULT None 1700 20 YesR CBS-2 LRW 4/20/2005 10:53 Total Coliform SM 9222B RESULT None 120 20 0 MR SEL-1 LSDO 4/20/2005 11:03 Enterococcus SM 9230C RESULT None 100 20 YesR SEL-1 LRW 4/20/2005 11:05 Enterococcus SM 9230C RESULT < 10 10 0 MR SEL-1 LSDO 4/20/2005 11:03 Fecal Coliform SM 9222D RESULT None 80 20 YesR SEL-1 LRW 4/20/2005 11:05 Fecal Coliform SM 9222D RESULT None 160 10 0 MR SEL-1 LSDO 4/20/2005 11:03 Total Coliform SM 9222B RESULT None 240 20 YesR SEL-1 LRW 4/20/2005 11:05 Total Coliform SM 9222B RESULT None 180 10 0 MR SEL-2 LSDO 4/20/2005 12:20 Enterococcus SM 9230C RESULT None 80 20 NoR SEL-2 LRW 4/20/2005 12:20 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 4/20/2005 12:20 Fecal Coliform SM 9222D RESULT None 60 20 NoR SEL-2 LRW 4/20/2005 12:20 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 4/20/2005 12:20 Total Coliform SM 9222B RESULT None 260 20 NoR SEL-2 LRW 4/20/2005 12:20 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 4/20/2005 12:30 Enterococcus SM 9230C RESULT None 60 20 NoR SEL-3 LRW 4/20/2005 12:30 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 4/20/2005 12:30 Fecal Coliform SM 9222D RESULT None 1480 20 NoR SEL-3 LRW 4/20/2005 12:30 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 4/20/2005 12:30 Total Coliform SM 9222B RESULT None 2,520 20 NoR SEL-3 LRW 4/20/2005 12:30 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 5/3/2005 12:56 Enterococcus SM 9230C RESULT None 460 50 NoR CBS-1 LRW 5/3/2005 12:39 Enterococcus SM 9230C RESULT None 240 10 0 MR CBS-1 LSDO 5/3/2005 12:56 Fecal Coliform SM 9222D RESULT None 700 100 NoR CBS-1 LRW 5/3/2005 12:39 Fecal Coliform SM 9222D RESULT None 180 10 0 MR CBS-1 LSDO 5/3/2005 12:56 Total Coliform SM 9222B RESULT None 950 100 NoR CBS-1 LRW 5/3/2005 12:39 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-2 LSDO 5/3/2005 12:05 Enterococcus SM 9230C RESULT None 880 100 YesR CBS-2 LRW 5/3/2005 12:04 Enterococcus SM 9230C RESULT None 130 20 0 MR CBS-2 LSDO 5/3/2005 12:05 Fecal Coliform SM 9222D RESULT None 250 100 YesR CBS-2 LRW 5/3/2005 12:04 Fecal Coliform SM 9222D RESULT None 490 20 0 MR CBS-2 LSDO 5/3/2005 12:05 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 5/3/2005 12:04 Total Coliform SM 9222B RESULT None 40 20 0 MEN04-05 DataPage 56 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-1 LSDO 5/3/2005 12:18 Enterococcus SM 9230C RESULT None 60 20 YesR SEL-1 LRW 5/3/2005 12:23 Enterococcus SM 9230C RESULT None 140 20 0 MR SEL-1 LSDO 5/3/2005 12:18 Fecal Coliform SM 9222D RESULT None 20 20 YesR SEL-1 LRW 5/3/2005 12:23 Fecal Coliform SM 9222D RESULT None 920 20 0 MR SEL-1 LSDO 5/3/2005 12:18 Total Coliform SM 9222B RESULT None 60 20 YesR SEL-1 LRW 5/3/2005 12:23 Total Coliform SM 9222B RESULT < 20 20 0 MR SEL-2 LSDO 5/3/2005 13:00 Enterococcus SM 9230C RESULT None 60 20 NoR SEL-2 LRW 5/3/2005 13:00 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 5/3/2005 13:00 Fecal Coliform SM 9222D RESULT None 40 20 NoR SEL-2 LRW 5/3/2005 13:00 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 5/3/2005 13:00 Total Coliform SM 9222B RESULT None 80 20 NoR SEL-2 LRW 5/3/2005 13:00 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 5/3/2005 13:10 Enterococcus SM 9230C RESULT None 650 20 NoR SEL-3 LRW 5/3/2005 13:10 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 5/3/2005 13:10 Fecal Coliform SM 9222D RESULT None 6400 20 NoR SEL-3 LRW 5/3/2005 13:10 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 5/3/2005 13:10 Total Coliform SM 9222B RESULT None 12800 20 NoR SEL-3 LRW 5/3/2005 13:10 Total Coliform SM 9222B RESULT NS -99R CBS-2 LSDO 05/11/05 11:30 Enterococcus SM 9230C RESULT None 380 20 YesR CBS-2 LRW 05/11/05 11:35 Enterococcus SM 9230C RESULT None 10 20 75 LR CBS-2 LSDO 05/11/05 11:30 Fecal Coliform SM 9222D RESULT None 100 20 YesR CBS-2 LRW 05/11/05 11:35 Fecal Coliform SM 9222D RESULT < 10 10 75 LR CBS-2 LSDO 05/11/05 11:30 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 05/11/05 11:35 Total Coliform SM 9222B RESULT < 20 20 75 LR SEL-1 LSDO 05/11/05 14:28 Enterococcus SM 9230C RESULT None 20 20 YesR SEL-1 LRW 05/11/05 14:30 Enterococcus SM 9230C RESULT None 10 20 0 MR SEL-1 LSDO 05/11/05 14:28 Fecal Coliform SM 9222D RESULT < 20 20 YesR SEL-1 LRW 05/11/05 14:30 Fecal Coliform SM 9222D RESULT None 100 20 0 MR SEL-1 LSDO 05/11/05 14:28 Total Coliform SM 9222B RESULT None 100 20 YesR SEL-1 LRW 05/11/05 14:30 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-1 LSDO 5/16/2005 12:05 Enterococcus SM 9230C RESULT None 1860 50 NoR CBS-1 LRW 5/16/2005 12:00 Enterococcus SM 9230C RESULT None 40 10 0 MR CBS-1 LSDO 5/16/2005 12:05 Fecal Coliform SM 9222D RESULT None 160 100 NoR CBS-1 LRW 5/16/2005 12:00 Fecal Coliform SM 9222D RESULT None 20 10 0 MR CBS-1 LSDO 5/16/2005 12:05 Total Coliform SM 9222B RESULT < 20 20 NoR CBS-1 LRW 5/16/2005 12:00 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-2 LSDO 5/16/2005 11:32 Enterococcus SM 9230C RESULT None 1600 100 YesEN04-05 DataPage 57 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-2 LRW 5/16/2005 11:30 Enterococcus SM 9230C RESULT None 60 20 75 R R CBS-2 LSDO 5/16/2005 11:32 Fecal Coliform SM 9222D RESULT None 1280 100 YesR CBS-2 LRW 5/16/2005 11:30 Fecal Coliform SM 9222D RESULT None 170 20 75 R R CBS-2 LSDO 5/16/2005 11:32 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 5/16/2005 11:30 Total Coliform SM 9222B RESULT < 20 20 75 R R SEL-1 LSDO 5/16/2005 11:39 Enterococcus SM 9230C RESULT None 20 20 YesR SEL-1 LRW 5/16/2005 11:44 Enterococcus SM 9230C RESULT None 40 20 0 MR SEL-1 LSDO 5/16/2005 11:39 Fecal Coliform SM 9222D RESULT < 20 20 YesR SEL-1 LRW 5/16/2005 11:44 Fecal Coliform SM 9222D RESULT None 120 20 0 MR SEL-1 LSDO 5/16/2005 11:39 Total Coliform SM 9222B RESULT None 1140 20 YesR SEL-1 LRW 5/16/2005 11:44 Total Coliform SM 9222B RESULT < 20 20 0 MR SEL-2 LSDO 5/16/2005 12:11 Enterococcus SM 9230C RESULT None 140 20 NoR SEL-2 LRW 5/16/2005 12:11 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 5/16/2005 12:11 Fecal Coliform SM 9222D RESULT None 420 20 NoR SEL-2 LRW 5/16/2005 12:11 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 5/16/2005 12:11 Total Coliform SM 9222B RESULT None 540 20 NoR SEL-2 LRW 5/16/2005 12:11 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 5/16/2005 12:18 Enterococcus SM 9230C RESULT None 300 20 NoR SEL-3 LRW 5/16/2005 12:18 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 5/16/2005 12:18 Fecal Coliform SM 9222D RESULT None 50 20 NoR SEL-3 LRW 5/16/2005 12:18 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 5/16/2005 12:18 Total Coliform SM 9222B RESULT None 15200 20 NoR SEL-3 LRW 5/16/2005 12:18 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 6/2/2005 14:35 Enterococcus SM 9230C RESULT None 1390 50 NoR CBS-1 LRW 6/2/2005 14:27 Enterococcus SM 9230C RESULT < 20 20 0 MR CBS-1 LSDO 6/2/2005 14:35 Fecal Coliform SM 9222D RESULT None 540 100 NoR CBS-1 LRW 6/2/2005 14:27 Fecal Coliform SM 9222D RESULT None 20 10 0 MR CBS-1 LSDO 6/2/2005 14:35 Total Coliform SM 9222B RESULT < 20 20 NoR CBS-1 LRW 6/2/2005 14:27 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-2 LSDO 6/2/2005 13:55 Enterococcus SM 9230C RESULT None 460 100 YesR CBS-2 LRW 6/2/2005 13:53 Enterococcus SM 9230C RESULT None 60 20 75 R R CBS-2 LSDO 6/2/2005 13:55 Fecal Coliform SM 9222D RESULT None 100 100 YesR CBS-2 LRW 6/2/2005 13:53 Fecal Coliform SM 9222D RESULT None 420 20 75 R R CBS-2 LSDO 6/2/2005 13:55 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 6/2/2005 13:53 Total Coliform SM 9222B RESULT < 20 20 75 R R SEL-1 LSDO 6/2/2005 Enterococcus SM 9230C RESULT NS -99 20 YesR SEL-1 LRW 6/2/2005 Enterococcus SM 9230C RESULT NS -99 20 0 MEN04-05 DataPage 58 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-1 LSDO 6/2/2005 Fecal Coliform SM 9222D RESULT NS -99 20 YesR SEL-1 LRW 6/2/2005 Fecal Coliform SM 9222D RESULT NS -99 20 0 MR SEL-1 LSDO 6/2/2005 Total Coliform SM 9222B RESULT NS -99 20 YesR SEL-1 LRW 6/2/2005 Total Coliform SM 9222B RESULT NS -99 20 0 MR SEL-2 LSDO 6/2/2005 14:42 Enterococcus SM 9230C RESULT None 80 20 NoR SEL-2 LRW 6/2/2005 14:42 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 6/2/2005 14:42 Fecal Coliform SM 9222D RESULT None 220 20 NoR SEL-2 LRW 6/2/2005 14:42 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 6/2/2005 14:42 Total Coliform SM 9222B RESULT None 120 20 NoR SEL-2 LRW 6/2/2005 14:42 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 6/2/2005 14:57 Enterococcus SM 9230C RESULT None 350 20 NoR SEL-3 LRW 6/2/2005 14:57 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 6/2/2005 14:57 Fecal Coliform SM 9222D RESULT None 500 20 NoR SEL-3 LRW 6/2/2005 14:57 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 6/2/2005 14:57 Total Coliform SM 9222B RESULT None 17200 20 NoR SEL-3 LRW 6/2/2005 14:57 Total Coliform SM 9222B RESULT NS -99R CBS-5 LSDO 6/7/2005 9:58 Enterococcus SM 9230C RESULT None 30450 50 YesR CBS-5 LRW 6/7/2005 10:02 Enterococcus SM 9230C RESULT None 240 10 0 MR CBS-5 LSDO 6/7/2005 9:58 Fecal Coliform SM 9222D RESULT None 6700 100 YesR CBS-5 LRW 6/7/2005 10:02 Fecal Coliform SM 9222D RESULT None 360 10 0 MR CBS-5 LSDO 6/7/2005 9:58 Total Coliform SM 9222B RESULT None 25700 100 YesR CBS-5 LRW 6/7/2005 10:02 Total Coliform SM 9222B RESULT None 280 10 0 MR CBS-2 LSDO 6/8/2005 10:29 Enterococcus SM 9230C RESULT None 520 100 YesR CBS-2 LRW 6/8/2005 10:28 Enterococcus SM 9230C RESULT < 10 10 0 MR CBS-2 LSDO 6/8/2005 10:29 Fecal Coliform SM 9222D RESULT None 240 100 YesR CBS-2 LRW 6/8/2005 10:28 Fecal Coliform SM 9222D RESULT None 10 20 0 MR CBS-2 LSDO 6/8/2005 10:29 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 6/8/2005 10:28 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-1 LSDO 06/16/05 12:00 Enterococcus SM 9230C RESULT None 4060 50 NoR CBS-1 LRW 06/16/05 11:50 Enterococcus SM 9230C RESULT None 140 10 0 MR CBS-1 LSDO 06/16/05 12:00 Fecal Coliform SM 9222D RESULT None 1680 100 NoR CBS-1 LRW 06/16/05 11:50 Fecal Coliform SM 9222D RESULT None 360 10 0 MR CBS-1 LSDO 06/16/05 12:00 Total Coliform SM 9222B RESULT None 740 100 NoR CBS-1 LRW 06/16/05 11:50 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-2 LSDO 06/16/05 11:19 Enterococcus SM 9230C RESULT None 2200 100 YesR CBS-2 LRW 06/16/05 11:17 Enterococcus SM 9230C RESULT None 160 20 0 MR CBS-2 LSDO 06/16/05 11:19 Fecal Coliform SM 9222D RESULT None 1980 100 YesEN04-05 DataPage 59 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-2 LRW 06/16/05 11:17 Fecal Coliform SM 9222D RESULT None 660 20 0 MR CBS-2 LSDO 06/16/05 11:19 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 06/16/05 11:17 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-5 LSDO 06/16/05 11:14 Enterococcus SM 9230C RESULT NS -99 50 NoR CBS-5 LRW 06/16/05 11:14 Enterococcus SM 9230C RESULT NS -99 10 0 MR CBS-5 LSDO 06/16/05 11:14 Fecal Coliform SM 9222D RESULT NS -99 100 NoR CBS-5 LRW 06/16/05 11:14 Fecal Coliform SM 9222D RESULT NS -99 10 0 MR CBS-5 LSDO 06/16/05 11:14 Total Coliform SM 9222B RESULT NS -99 100 NoR CBS-5 LRW 06/16/05 11:14 Total Coliform SM 9222B RESULT NS -99 10 0 MR SEL-1 LSDO 06/16/05 11:30 Enterococcus SM 9230C RESULT NS -99 20 NoR SEL-1 LRW 06/16/05 11:30 Enterococcus SM 9230C RESULT NS -99 20 0 MR SEL-1 LSDO 06/16/05 11:30 Fecal Coliform SM 9222D RESULT NS -99 20 NoR SEL-1 LRW 06/16/05 11:30 Fecal Coliform SM 9222D RESULT NS -99 20 0 MR SEL-1 LSDO 06/16/05 11:30 Total Coliform SM 9222B RESULT NS -99 20 NoR SEL-1 LRW 06/16/05 11:30 Total Coliform SM 9222B RESULT NS -99 20 0 MR SEL-2 LSDO 06/16/05 12:05 Enterococcus SM 9230C RESULT None 140 20 NoR SEL-2 LRW 06/16/05 12:05 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 06/16/05 12:05 Fecal Coliform SM 9222D RESULT None 340 20 NoR SEL-2 LRW 06/16/05 12:05 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 06/16/05 12:05 Total Coliform SM 9222B RESULT < 20 20 NoR SEL-2 LRW 06/16/05 12:05 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 06/16/05 12:17 Enterococcus SM 9230C RESULT None 160 20 NoR SEL-3 LRW 06/16/05 12:17 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 06/16/05 12:17 Fecal Coliform SM 9222D RESULT None 50 20 NoR SEL-3 LRW 06/16/05 12:17 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 06/16/05 12:17 Total Coliform SM 9222B RESULT None 16700 20 NoR SEL-3 LRW 06/16/05 12:17 Total Coliform SM 9222B RESULT NS -99F CBS-2 LSDO 06/20/05 13:27 Enterococcus SM 9230C RESULT None 100 100 YesF CBS-2 LRW 06/20/05 13:25 Enterococcus SM 9230C RESULT None 10 20 0 MF CBS-2 LSDO 06/20/05 13:27 Fecal Coliform SM 9222D RESULT < 20 20 YesF CBS-2 LRW 06/20/05 13:25 Fecal Coliform SM 9222D RESULT None 160 20 0 MF CBS-2 LSDO 06/20/05 13:27 Total Coliform SM 9222B RESULT < 20 20 YesF CBS-2 LRW 06/20/05 13:25 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-1 LSDO 06/30/05 14:45 Enterococcus SM 9230C RESULT None 760 50 NoR CBS-1 LRW 06/30/05 14:38 Enterococcus SM 9230C RESULT None 40 10 0 MR CBS-1 LSDO 06/30/05 14:45 Fecal Coliform SM 9222D RESULT None 620 100 NoR CBS-1 LRW 06/30/05 14:38 Fecal Coliform SM 9222D RESULT None 20 10 0 MEN04-05 DataPage 60 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-1 LSDO 06/30/05 14:45 Total Coliform SM 9222B RESULT None 20 100 NoR CBS-1 LRW 06/30/05 14:38 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-2 LSDO 06/30/05 14:23 Enterococcus SM 9230C RESULT None 40 100 YesR CBS-2 LRW 06/30/05 14:18 Enterococcus SM 9230C RESULT None 20 20 0 MR CBS-2 LSDO 06/30/05 14:23 Fecal Coliform SM 9222D RESULT None 20 100 YesR CBS-2 LRW 06/30/05 14:18 Fecal Coliform SM 9222D RESULT < 20 20 0 MR CBS-2 LSDO 06/30/05 14:23 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 06/30/05 14:18 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-5 LSDO 06/30/05 14:15 Enterococcus SM 9230C RESULT NS -99 50 NoR CBS-5 LRW 06/30/05 14:15 Enterococcus SM 9230C RESULT NS -99 10 0 MR CBS-5 LSDO 06/30/05 14:15 Fecal Coliform SM 9222D RESULT NS -99 100 NoR CBS-5 LRW 06/30/05 14:15 Fecal Coliform SM 9222D RESULT NS -99 10 0 MR CBS-5 LSDO 06/30/05 14:15 Total Coliform SM 9222B RESULT NS -99 100 NoR CBS-5 LRW 06/30/05 14:15 Total Coliform SM 9222B RESULT NS -99 10 0 MR SEL-1 LSDO 06/30/05 14:30 Enterococcus SM 9230C RESULT NS -99 20 NoR SEL-1 LRW 06/30/05 14:30 Enterococcus SM 9230C RESULT NS -99 20 0 MR SEL-1 LSDO 06/30/05 14:30 Fecal Coliform SM 9222D RESULT NS -99 20 NoR SEL-1 LRW 06/30/05 14:30 Fecal Coliform SM 9222D RESULT NS -99 20 0 MR SEL-1 LSDO 06/30/05 14:30 Total Coliform SM 9222B RESULT NS -99 20 NoR SEL-1 LRW 06/30/05 14:30 Total Coliform SM 9222B RESULT NS -99 20 0 MR SEL-2 LSDO 06/30/05 14:50 Enterococcus SM 9230C RESULT None 60 20 NoR SEL-2 LRW 06/30/05 14:50 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 06/30/05 14:50 Fecal Coliform SM 9222D RESULT None 200 20 NoR SEL-2 LRW 06/30/05 14:50 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 06/30/05 14:50 Total Coliform SM 9222B RESULT None 20 20 NoR SEL-2 LRW 06/30/05 14:50 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 06/30/05 14:56 Enterococcus SM 9230C RESULT None 20 20 NoR SEL-3 LRW 06/30/05 14:56 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 06/30/05 14:56 Fecal Coliform SM 9222D RESULT None 550 20 NoR SEL-3 LRW 06/30/05 14:56 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 06/30/05 14:56 Total Coliform SM 9222B RESULT None 1800 20 NoR SEL-3 LRW 06/30/05 14:56 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 07/14/05 14:25 Enterococcus SM 9230C RESULT None 1140 20 NoR CBS-1 LRW 07/14/05 14:12 Enterococcus SM 9230C RESULT None 40 20 0 MR CBS-1 LSDO 07/14/05 14:25 Fecal Coliform SM 9222D RESULT None 220 20 NoR CBS-1 LRW 07/14/05 14:12 Fecal Coliform SM 9222D RESULT < 20 20 0 MR CBS-1 LSDO 07/14/05 14:25 Total Coliform SM 9222B RESULT < 20 20 NoEN04-05 DataPage 61 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-1 LRW 07/14/05 14:12 Total Coliform SM 9222B RESULT None 40 20 0 MR CBS-2 LSDO 07/14/05 11:16 Enterococcus SM 9230C RESULT None 20 20 YesR CBS-2 LRW 07/14/05 11:14 Enterococcus SM 9230C RESULT < 20 20 0 MR CBS-2 LSDO 07/14/05 11:16 Fecal Coliform SM 9222D RESULT None 200 20 YesR CBS-2 LRW 07/14/05 11:14 Fecal Coliform SM 9222D RESULT < 20 20 0 MR CBS-2 LSDO 07/14/05 11:16 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 07/14/05 11:14 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-5 LSDO 07/14/05 11:05 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 07/14/05 11:05 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 07/14/05 11:05 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 07/14/05 11:05 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 07/14/05 11:05 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 07/14/05 11:05 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 07/14/05 11:30 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 07/14/05 11:30 Enterococcus SM 9230C RESULT NS -99 0 MR SEL-1 LSDO 07/14/05 11:30 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 07/14/05 11:30 Fecal Coliform SM 9222D RESULT NS -99 0 MR SEL-1 LSDO 07/14/05 11:30 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 07/14/05 11:30 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-2 LSDO 07/14/05 14:30 Enterococcus SM 9230C RESULT None 360 20 NoR SEL-2 LRW 07/14/05 14:30 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 07/14/05 14:30 Fecal Coliform SM 9222D RESULT None 360 20 NoR SEL-2 LRW 07/14/05 14:30 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 07/14/05 14:30 Total Coliform SM 9222B RESULT None 1000 20 NoR SEL-2 LRW 07/14/05 14:30 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 07/14/05 14:35 Enterococcus SM 9230C RESULT < 20 20 NoR SEL-3 LRW 07/14/05 14:35 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 07/14/05 14:35 Fecal Coliform SM 9222D RESULT None 20 20 NoR SEL-3 LRW 07/14/05 14:35 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 07/14/05 14:35 Total Coliform SM 9222B RESULT None 900 20 NoR SEL-3 LRW 07/14/05 14:35 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 07/28/05 12:35 Enterococcus SM 9230C RESULT None 2000 20 NoR CBS-1 LRW 07/28/05 12:25 Enterococcus SM 9230C RESULT None 400 20 0 MR CBS-1 LSDO 07/28/05 12:35 Fecal Coliform SM 9222D RESULT None 540 20 NoR CBS-1 LRW 07/28/05 12:25 Fecal Coliform SM 9222D RESULT < 20 20 0 MR CBS-1 LSDO 07/28/05 12:35 Total Coliform SM 9222B RESULT < 20 20 NoR CBS-1 LRW 07/28/05 12:25 Total Coliform SM 9222B RESULT None 20 20 0 MEN04-05 DataPage 62 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-2 LSDO 07/28/05 12:10 Enterococcus SM 9230C RESULT None 80 20 YesR CBS-2 LRW 07/28/05 12:08 Enterococcus SM 9230C RESULT None 20 20 0 MR CBS-2 LSDO 07/28/05 12:10 Fecal Coliform SM 9222D RESULT None 540 20 YesR CBS-2 LRW 07/28/05 12:08 Fecal Coliform SM 9222D RESULT None 80 20 0 MR CBS-2 LSDO 07/28/05 12:10 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 07/28/05 12:08 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-5 LSDO 07/28/05 12:03 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 07/28/05 12:03 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 07/28/05 12:03 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 07/28/05 12:03 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 07/28/05 12:03 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 07/28/05 12:03 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 07/28/05 12:17 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 07/28/05 12:17 Enterococcus SM 9230C RESULT NS -99 0 MR SEL-1 LSDO 07/28/05 12:17 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 07/28/05 12:17 Fecal Coliform SM 9222D RESULT NS -99 0 MR SEL-1 LSDO 07/28/05 12:17 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 07/28/05 12:17 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-2 LSDO 07/28/05 12:40 Enterococcus SM 9230C RESULT None 160 20 NoR SEL-2 LRW 07/28/05 12:40 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 07/28/05 12:40 Fecal Coliform SM 9222D RESULT None 1840 20 NoR SEL-2 LRW 07/28/05 12:40 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 07/28/05 12:40 Total Coliform SM 9222B RESULT None 2900 20 NoR SEL-2 LRW 07/28/05 12:40 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 07/28/05 13:00 Enterococcus SM 9230C RESULT None 80 20 NoR SEL-3 LRW 07/28/05 13:00 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 07/28/05 13:00 Fecal Coliform SM 9222D RESULT None 20 20 NoR SEL-3 LRW 07/28/05 13:00 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 07/28/05 13:00 Total Coliform SM 9222B RESULT None 2500 20 NoR SEL-3 LRW 07/28/05 13:00 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 08/11/05 11:25 Enterococcus SM 9230C RESULT None 2040 20 NoR CBS-1 LRW 08/11/05 11:17 Enterococcus SM 9230C RESULT None 380 20 0 MR CBS-1 LSDO 08/11/05 11:25 Fecal Coliform SM 9222D RESULT None 260 20 NoR CBS-1 LRW 08/11/05 11:17 Fecal Coliform SM 9222D RESULT None 80 20 0 MR CBS-1 LSDO 08/11/05 11:25 Total Coliform SM 9222B RESULT < 20 20 NoR CBS-1 LRW 08/11/05 11:17 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-2 LSDO 08/11/05 11:03 Enterococcus SM 9230C RESULT None 440 20 YesEN04-05 DataPage 63 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-2 LRW 08/11/05 11:01 Enterococcus SM 9230C RESULT None 40 20 0 MR CBS-2 LSDO 08/11/05 11:03 Fecal Coliform SM 9222D RESULT None 1040 20 YesR CBS-2 LRW 08/11/05 11:01 Fecal Coliform SM 9222D RESULT < 20 20 0 MR CBS-2 LSDO 08/11/05 11:03 Total Coliform SM 9222B RESULT < 20 20 YesR CBS-2 LRW 08/11/05 11:01 Total Coliform SM 9222B RESULT None 20 20 0 MR CBS-5 LSDO 08/11/05 10:50 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 08/11/05 10:50 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 08/11/05 10:50 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 08/11/05 10:50 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 08/11/05 10:50 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 08/11/05 10:50 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 08/11/05 11:10 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 08/11/05 11:10 Enterococcus SM 9230C RESULT NS -99 0 MR SEL-1 LSDO 08/11/05 11:10 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 08/11/05 11:10 Fecal Coliform SM 9222D RESULT NS -99 0 MR SEL-1 LSDO 08/11/05 11:10 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 08/11/05 11:10 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-2 LSDO 08/11/05 11:32 Enterococcus SM 9230C RESULT None 380 20 NoR SEL-2 LRW 08/11/05 11:32 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 08/11/05 11:32 Fecal Coliform SM 9222D RESULT None 1000 20 NoR SEL-2 LRW 08/11/05 11:32 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 08/11/05 11:32 Total Coliform SM 9222B RESULT None 1600 20 NoR SEL-2 LRW 08/11/05 11:32 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 08/11/05 11:55 Enterococcus SM 9230C RESULT < 20 20 NoR SEL-3 LRW 08/11/05 11:55 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 08/11/05 11:55 Fecal Coliform SM 9222D RESULT None 3120 20 NoR SEL-3 LRW 08/11/05 11:55 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 08/11/05 11:55 Total Coliform SM 9222B RESULT None 1600 20 NoR SEL-3 LRW 08/11/05 11:55 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 08/29/05 12:05 Enterococcus SM 9230C RESULT None 2900 20 NoR CBS-1 LRW 08/29/05 11:55 Enterococcus SM 9230C RESULT < 20 20 0 MR CBS-1 LSDO 08/29/05 12:05 Fecal Coliform SM 9222D RESULT None 440 20 NoR CBS-1 LRW 08/29/05 11:55 Fecal Coliform SM 9222D RESULT None 20 20 0 MR CBS-1 LSDO 08/29/05 12:05 Total Coliform SM 9222B RESULT < 20 20 NoR CBS-1 LRW 08/29/05 11:55 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-2 LSDO 08/29/05 11:34 Enterococcus SM 9230C RESULT None 3100 20 YesR CBS-2 LRW 08/29/05 11:33 Enterococcus SM 9230C RESULT None 420 20 0 MEN04-05 DataPage 64 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR CBS-2 LSDO 08/29/05 11:34 Fecal Coliform SM 9222D RESULT None 10920 20 YesR CBS-2 LRW 08/29/05 11:33 Fecal Coliform SM 9222D RESULT None 3300 20 0 MR CBS-2 LSDO 08/29/05 11:34 Total Coliform SM 9222B RESULT None 840 20 YesR CBS-2 LRW 08/29/05 11:33 Total Coliform SM 9222B RESULT None 40 20 0 MR CBS-5 LSDO 08/29/05 11:28 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 08/29/05 11:28 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 08/29/05 11:28 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 08/29/05 11:28 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 08/29/05 11:28 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 08/29/05 11:28 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 08/29/05 11:45 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 08/29/05 11:45 Enterococcus SM 9230C RESULT NS -99 0 MR SEL-1 LSDO 08/29/05 11:45 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 08/29/05 11:45 Fecal Coliform SM 9222D RESULT NS -99 0 MR SEL-1 LSDO 08/29/05 11:45 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 08/29/05 11:45 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-2 LSDO 08/29/05 12:10 Enterococcus SM 9230C RESULT None 550 20 NoR SEL-2 LRW 08/29/05 12:10 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 08/29/05 12:10 Fecal Coliform SM 9222D RESULT None 1650 20 NoR SEL-2 LRW 08/29/05 12:10 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 08/29/05 12:10 Total Coliform SM 9222B RESULT None 4000 20 NoR SEL-2 LRW 08/29/05 12:10 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 08/29/05 14:14 Enterococcus SM 9230C RESULT None 20 20 NoR SEL-3 LRW 08/29/05 14:14 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 08/29/05 14:14 Fecal Coliform SM 9222D RESULT < 20 20 NoR SEL-3 LRW 08/29/05 14:14 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 08/29/05 14:14 Total Coliform SM 9222B RESULT None 1660 20 NoR SEL-3 LRW 08/29/05 14:14 Total Coliform SM 9222B RESULT NS -99F CBS-2 LSDO 08/31/05 11:05 Enterococcus SM 9230C RESULT None 1800 20 YesF CBS-2 LRW 08/31/05 11:03 Enterococcus SM 9230C RESULT None 180 20 0 MF CBS-2 LSDO 08/31/05 11:35 Enterococcus SM 9230C RESULT < 20 20 YesF CBS-2 LSDO 08/31/05 11:05 Fecal Coliform SM 9222D RESULT None 2500 20 YesF CBS-2 LRW 08/31/05 11:03 Fecal Coliform SM 9222D RESULT None 150 20 0 MF CBS-2 LSDO 08/31/05 11:35 Fecal Coliform SM 9222D RESULT None 20 20 YesF CBS-2 LSDO 08/31/05 11:05 Total Coliform SM 9222B RESULT None 11400 20 YesF CBS-2 LRW 08/31/05 11:03 Total Coliform SM 9222B RESULT None 580 20 0 MF CBS-2 LSDO 08/31/05 11:35 Total Coliform SM 9222B RESULT < 20 20 YesEN04-05 DataPage 65 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterF CBS-2A LSDO 08/31/05 11:23 Enterococcus SM 9230C RESULT None 8650 20F CBS-2A LSDO 08/31/05 11:23 Fecal Coliform SM 9222D RESULT None 5050 20F CBS-2A LSDO 08/31/05 11:23 Total Coliform SM 9222B RESULT None 12900 20F CBS-2B LSDO 08/31/05 11:32 Enterococcus SM 9230C RESULT None 4950 20 YesF CBS-2B LSDO 08/31/05 11:32 Fecal Coliform SM 9222D RESULT None 3350 20 YesF CBS-2B LSDO 08/31/05 11:32 Total Coliform SM 9222B RESULT None 6600 20 YesF CBS-2C LSDO 08/31/05 11:37 Enterococcus SM 9230C RESULT None 2380 20 YesF CBS-2C LSDO 08/31/05 11:37 Fecal Coliform SM 9222D RESULT None 2120 20 YesF CBS-2C LSDO 08/31/05 11:37 Total Coliform SM 9222B RESULT None 9300 20 YesF CBS-2 LSDO 09/06/05 13:07 Enterococcus SM 9230C RESULT None 450 20 YesF CBS-2 LRW 09/06/05 13:05 Enterococcus SM 9230C RESULT < 20 20 0 MF CBS-2 LSDO 09/06/05 13:07 Fecal Coliform SM 9222D RESULT None 1300 20 YesF CBS-2 LRW 09/06/05 13:05 Fecal Coliform SM 9222D RESULT < 20 20 0 MF CBS-2 LSDO 09/06/05 13:07 Total Coliform SM 9222B RESULT None 200 20 YesF CBS-2 LRW 09/06/05 13:05 Total Coliform SM 9222B RESULT None 100 20 0 MF CBS-2A LSDO 09/06/05 13:15 Enterococcus SM 9230C RESULT None 1260 20F CBS-2A LSDO 09/06/05 13:15 Fecal Coliform SM 9222D RESULT None 540 20F CBS-2A LSDO 09/06/05 13:15 Total Coliform SM 9222B RESULT None 2760 20F CBS-2B LSDO 09/06/05 13:25 Enterococcus SM 9230C RESULT None 5950 20 YesF CBS-2B LSDO 09/06/05 13:25 Fecal Coliform SM 9222D RESULT None 1770 20 YesF CBS-2B LSDO 09/06/05 13:25 Total Coliform SM 9222B RESULT None 10000 20 YesF CBS-2C LSDO 09/06/05 13:30 Enterococcus SM 9230C RESULT None 1640 20 YesF CBS-2C LSDO 09/06/05 13:30 Fecal Coliform SM 9222D RESULT None 940 20 YesF CBS-2C LSDO 09/06/05 13:30 Total Coliform SM 9222B RESULT None 2420 20 YesR CBS-1 LSDO 09/08/05 11:00 Enterococcus SM 9230C RESULT None 5340 20 NoR CBS-1 LRW 09/08/05 10:45 Enterococcus SM 9230C RESULT None 20 20 0 MR CBS-1 LSDO 09/08/05 11:00 Fecal Coliform SM 9222D RESULT None 250 20 NoR CBS-1 LRW 09/08/05 10:45 Fecal Coliform SM 9222D RESULT < 20 20 0 MR CBS-1 LSDO 09/08/05 11:00 Total Coliform SM 9222B RESULT None 360 20 NoR CBS-1 LRW 09/08/05 10:45 Total Coliform SM 9222B RESULT < 20 20 0 MR CBS-5 LSDO 09/08/05 10:25 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 09/08/05 10:25 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 09/08/05 10:25 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 09/08/05 10:25 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 09/08/05 10:25 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 09/08/05 10:25 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 09/08/05 10:30 Enterococcus SM 9230C RESULT NS -99 NoEN04-05 DataPage 66 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-1 LRW 09/08/05 10:30 Enterococcus SM 9230C RESULT NS -99 0 MR SEL-1 LSDO 09/08/05 10:30 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 09/08/05 10:30 Fecal Coliform SM 9222D RESULT NS -99 0 MR SEL-1 LSDO 09/08/05 10:30 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 09/08/05 10:30 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-2 LSDO 09/08/05 11:05 Enterococcus SM 9230C RESULT None 735 20 NoR SEL-2 LRW 09/08/05 11:05 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 09/08/05 11:05 Fecal Coliform SM 9222D RESULT None 780 20 NoR SEL-2 LRW 09/08/05 11:05 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 09/08/05 11:05 Total Coliform SM 9222B RESULT None 1100 20 NoR SEL-2 LRW 09/08/05 11:05 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 09/08/05 11:15 Enterococcus SM 9230C RESULT None 20 20 NoR SEL-3 LRW 09/08/05 11:15 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 09/08/05 11:15 Fecal Coliform SM 9222D RESULT None 480 20 NoR SEL-3 LRW 09/08/05 11:15 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 09/08/05 11:15 Total Coliform SM 9222B RESULT None 1480 20 NoR SEL-3 LRW 09/08/05 11:15 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 9/28/2005 11:25 Enterococcus SM 9230C RESULT None 1480 20 NoR CBS-1 LRW 9/28/2005 11:20 Enterococcus SM 9230C RESULT < 20 20 0 MR CBS-1 LSDO 9/28/2005 11:25 Fecal Coliform SM 9222D RESULT None 1760 20 NoR CBS-1 LRW 9/28/2005 11:20 Fecal Coliform SM 9222D RESULT None 40 20 0 MR CBS-1 LSDO 9/28/2005 11:25 Total Coliform SM 9222B RESULT None 2240 20 NoR CBS-1 LRW 9/28/2005 11:20 Total Coliform SM 9222B RESULT None 80 20 0 MR CBS-2 LSDO 9/28/2005 10:57 Enterococcus SM 9230C RESULT None 450 20 YesR CBS-2 LRW 9/28/2005 10:55 Enterococcus SM 9230C RESULT None 100 20 75 R R CBS-2 LSDO 9/28/2005 10:57 Fecal Coliform SM 9222D RESULT None 2350 20 YesR CBS-2 LRW 9/28/2005 10:55 Fecal Coliform SM 9222D RESULT None 520 20 75 R R CBS-2 LSDO 9/28/2005 10:57 Total Coliform SM 9222B RESULT None 100 20 YesR CBS-2 LRW 9/28/2005 10:55 Total Coliform SM 9222B RESULT None 120 20 75 R R CBS-5 LSDO 09/28/05 10:45 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 09/28/05 10:45 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 09/28/05 10:45 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 09/28/05 10:45 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 09/28/05 10:45 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 09/28/05 10:45 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 09/28/05 11:02 Enterococcus SM 9230C RESULT NS -99 20 NoR SEL-1 LRW 09/28/05 11:02 Enterococcus SM 9230C RESULT NS -99 20 0 MEN04-05 DataPage 67 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-1 LSDO 09/28/05 11:02 Fecal Coliform SM 9222D RESULT NS -99 20 NoR SEL-1 LRW 09/28/05 11:02 Fecal Coliform SM 9222D RESULT NS -99 20 0 MR SEL-1 LSDO 09/28/05 11:02 Total Coliform SM 9222B RESULT NS -99 20 NoR SEL-1 LRW 09/28/05 11:02 Total Coliform SM 9222B RESULT NS -99 20 0 MR SEL-2 LSDO 09/28/05 11:30 Enterococcus SM 9230C RESULT None 300 20 NoR SEL-2 LRW 09/28/05 11:30 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 09/28/05 11:30 Fecal Coliform SM 9222D RESULT None 800 20 NoR SEL-2 LRW 09/28/05 11:30 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 09/28/05 11:30 Total Coliform SM 9222B RESULT None 2400 20 NoR SEL-2 LRW 09/28/05 11:30 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 09/28/05 11:38 Enterococcus SM 9230C RESULT None 180 20 NoR SEL-3 LRW 09/28/05 11:38 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 09/28/05 11:38 Fecal Coliform SM 9222D RESULT None 4520 20 NoR SEL-3 LRW 09/28/05 11:38 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 09/28/05 11:38 Total Coliform SM 9222B RESULT None 7300 20 NoR SEL-3 LRW 09/28/05 11:38 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 10/06/05 14:57 Enterococcus SM 9230C RESULT None 6500 20 NoR CBS-1 LRW 10/06/05 14:50 Enterococcus SM 9230C RESULT None 220 20 0 MR CBS-1 LSDO 10/06/05 14:57 Fecal Coliform SM 9222D RESULT None 4100 20 NoR CBS-1 LRW 10/06/05 14:50 Fecal Coliform SM 9222D RESULT None 200 20 0 MR CBS-1 LSDO 10/06/05 14:57 Total Coliform SM 9222B RESULT None 1860 20 NoR CBS-1 LRW 10/06/05 14:50 Total Coliform SM 9222B RESULT None 260 20 0 MR CBS-2 LSDO 10/06/05 14:42 Enterococcus SM 9230C RESULT None 1600 20 YesR CBS-2 LRW 10/06/05 14:40 Enterococcus SM 9230C RESULT None 140 20 0 MR CBS-2 LSDO 10/06/05 14:42 Fecal Coliform SM 9222D RESULT None 2550 20 YesR CBS-2 LRW 10/06/05 14:40 Fecal Coliform SM 9222D RESULT None 60 20 0 MR CBS-2 LSDO 10/06/05 14:42 Total Coliform SM 9222B RESULT < 100 100 YesR CBS-2 LRW 10/06/05 14:40 Total Coliform SM 9222B RESULT None 40 20 0 MR CBS-5 LSDO 10/06/05 14:34 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 10/06/05 14:34 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 10/06/05 14:34 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 10/06/05 14:34 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 10/06/05 14:34 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 10/06/05 14:34 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 10/06/05 14:46 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 10/06/05 14:46 Enterococcus SM 9230C RESULT NS -99 0 MR SEL-1 LSDO 10/06/05 14:46 Fecal Coliform SM 9222D RESULT NS -99 NoEN04-05 DataPage 68 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-1 LRW 10/06/05 14:46 Fecal Coliform SM 9222D RESULT NS -99 0 MR SEL-1 LSDO 10/06/05 14:46 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 10/06/05 14:46 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-2 LSDO 10/06/05 15:02 Enterococcus SM 9230C RESULT None 300 20 NoR SEL-2 LRW 10/06/05 15:02 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 10/06/05 15:02 Fecal Coliform SM 9222D RESULT None 650 20 NoR SEL-2 LRW 10/06/05 15:02 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 10/06/05 15:02 Total Coliform SM 9222B RESULT None 1200 20 NoR SEL-2 LRW 10/06/05 15:02 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 10/06/05 15:08 Enterococcus SM 9230C RESULT None 50 20 NoR SEL-3 LRW 10/06/05 15:08 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 10/06/05 15:08 Fecal Coliform SM 9222D RESULT None 1450 20 NoR SEL-3 LRW 10/06/05 15:08 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 10/06/05 15:08 Total Coliform SM 9222B RESULT None 3400 20 NoR SEL-3 LRW 10/06/05 15:08 Total Coliform SM 9222B RESULT NS -99R CBS-1 LSDO 10/24/05 10:07 Enterococcus SM 9230C RESULT None 600 20 NoR CBS-1 LRW 10/24/05 9:58 Enterococcus SM 9230C RESULT None 40 20 0 MR CBS-1 LSDO 10/24/05 10:07 Fecal Coliform SM 9222D RESULT None 260 20 NoR CBS-1 LRW 10/24/05 9:58 Fecal Coliform SM 9222D RESULT None 220 20 0 MR CBS-1 LSDO 10/24/05 10:07 Total Coliform SM 9222B RESULT None 700 20 NoR CBS-1 LRW 10/24/05 9:58 Total Coliform SM 9222B RESULT None 280 20 0 MR CBS-2 LSDO 10/24/05 9:40 Enterococcus SM 9230C RESULT None 1450 20 YesR CBS-2 LRW 10/24/05 9:38 Enterococcus SM 9230C RESULT None 60 20 0 MR CBS-2 LSDO 10/24/05 9:40 Fecal Coliform SM 9222D RESULT None 350 20 YesR CBS-2 LRW 10/24/05 9:38 Fecal Coliform SM 9222D RESULT < 20 20 0 MR CBS-2 LSDO 10/24/05 9:40 Total Coliform SM 9222B RESULT None 1400 20 YesR CBS-2 LRW 10/24/05 9:38 Total Coliform SM 9222B RESULT None 280 20 0 MR CBS-5 LSDO 10/24/05 9:30 Enterococcus SM 9230C RESULT NS -99 NoR CBS-5 LRW 10/24/05 9:30 Enterococcus SM 9230C RESULT NS -99 0 MR CBS-5 LSDO 10/24/05 9:30 Fecal Coliform SM 9222D RESULT NS -99 NoR CBS-5 LRW 10/24/05 9:30 Fecal Coliform SM 9222D RESULT NS -99 0 MR CBS-5 LSDO 10/24/05 9:30 Total Coliform SM 9222B RESULT NS -99 NoR CBS-5 LRW 10/24/05 9:30 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-1 LSDO 10/24/05 9:50 Enterococcus SM 9230C RESULT NS -99 NoR SEL-1 LRW 10/24/05 9:50 Enterococcus SM 9230C RESULT NS -99 0 MR SEL-1 LSDO 10/24/05 9:50 Fecal Coliform SM 9222D RESULT NS -99 NoR SEL-1 LRW 10/24/05 9:50 Fecal Coliform SM 9222D RESULT NS -99 0 MEN04-05 DataPage 69 of 133 Analytical Laboratory: Encina Wastewater PlantAnalytical Units: CFU/100mlCSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of Encinitas Prefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR SEL-1 LSDO 10/24/05 9:50 Total Coliform SM 9222B RESULT NS -99 NoR SEL-1 LRW 10/24/05 9:50 Total Coliform SM 9222B RESULT NS -99 0 MR SEL-2 LSDO 10/24/05 10:11 Enterococcus SM 9230C RESULT None 160 20 NoR SEL-2 LRW 10/24/05 10:11 Enterococcus SM 9230C RESULT NS -99R SEL-2 LSDO 10/24/05 10:11 Fecal Coliform SM 9222D RESULT None 1450 20 NoR SEL-2 LRW 10/24/05 10:11 Fecal Coliform SM 9222D RESULT NS -99R SEL-2 LSDO 10/24/05 10:11 Total Coliform SM 9222B RESULT None 2500 20 NoR SEL-2 LRW 10/24/05 10:11 Total Coliform SM 9222B RESULT NS -99R SEL-3 LSDO 10/24/05 10:17 Enterococcus SM 9230C RESULT None 100 20 NoR SEL-3 LRW 10/24/05 10:17 Enterococcus SM 9230C RESULT NS -99R SEL-3 LSDO 10/24/05 10:17 Fecal Coliform SM 9222D RESULT None 350 20 NoR SEL-3 LRW 10/24/05 10:17 Fecal Coliform SM 9222D RESULT NS -99R SEL-3 LSDO 10/24/05 10:17 Total Coliform SM 9222B RESULT None 9400 20 NoR SEL-3 LRW 10/24/05 10:17 Total Coliform SM 9222B RESULT NS -99EN04-05 DataPage 70 of 133 Analytical Laboratory: MECAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005Port of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-120 CSDO 02/09/05 16:40Enterococcus SM 9223 RESULT None41 10 NoR EH-120 CRW 02/09/05 16:40Enterococcus SM 9223 RESULT <10 10 75 LR EH-120 CSDO 02/09/05 16:40Fecal Coliform SM 9221E RESULT None230 20 NoR EH-120 CRW 02/09/05 16:40Fecal Coliform SM 9221E RESULT None40 20 75 LR EH-120 CSDO 02/09/05 16:40Total Coliform SM 9221B RESULT None500 20 NoR EH-120 CRW 02/09/05 16:40Total Coliform SM 9221B RESULT None80 20 75 LR EH-210 CSDO 02/09/05 14:20Enterococcus SM 9223 RESULT None135 10 NoR EH-210 CRW 02/09/05 14:20Enterococcus SM 9223 RESULT <10 10 50 RR EH-210 CSDO 02/09/05 14:20Fecal Coliform SM 9221E RESULT None300 20 NoR EH-210 CRW 02/09/05 14:20Fecal Coliform SM 9221E RESULT None40 20 50 RR EH-210 CSDO 02/09/05 14:20Total Coliform SM 9221B RESULT None2,200 20 NoR EH-210 CRW 02/09/05 14:20Total Coliform SM 9221B RESULT None40 20 50 RR EH-070 CSDO 03/08/05 15:10Enterococcus SM 9223 RESULT None24,196 10 NoR EH-070 CRW 03/08/05 15:15Enterococcus SM 9223 RESULT None20 10 75 LR EH-070 CSDO 03/08/05 15:10Fecal Coliform SM 9221E RESULT None140 20 NoR EH-070 CRW 03/08/05 15:15Fecal Coliform SM 9221E RESULT None40 20 75 LR EH-070 CSDO 03/08/05 15:10Total Coliform SM 9221B RESULT None140,000 20 NoR EH-070 CRW 03/08/05 15:15Total Coliform SM 9221B RESULT None130 20 75 LR EH-160 CSDO 04/05/05 14:10Enterococcus SM 9223 RESULT None1,610 10 NoR EH-160 CRW 04/05/05 14:15Enterococcus SM 9223 RESULT <10 10 200 LR EH-160 CSDO 04/05/05 14:10Fecal Coliform SM 9221E RESULT None1,400 20 NoR EH-160 CRW 04/05/05 14:15Fecal Coliform SM 9221E RESULT <20 20 200 LR EH-160 CSDO 04/05/05 14:10Total Coliform SM 9221B RESULT None80,000 20 NoR EH-160 CRW 04/05/05 14:15Total Coliform SM 9221B RESULT <20 20 200 LR EH-205 CSDO 08/09/05 6:55Enterococcus SM9223 RESULT None98,039 10 NoR EH-205 CRW 08/09/05 6:50Enterococcus SM9224 RESULT <10 10 75 LR EH-205 CSDO 08/09/05 6:55Fecal Coliform SM9221E RESULT None80,000 20 NoR EH-205 CRW 08/09/05 6:50Fecal Coliform SM9221E RESULT <20 20 75 LR EH-205 CSDO 08/09/05 6:55Total Coliform SM9221B RESULT None900,000 20 NoR EH-205 CRW 08/09/05 6:50Total Coliform SM9221B RESULT None20 20 75 LR EH-205 CSDO 09/06/05 6:50 Enterococcus SM 9223 RESULT None 120,333 10 YesR EH-205 CRW 09/06/05 6:50 Enterococcus SM 9223 RESULT None 20 10 75 LR EH-205 CSDO 09/06/05 6:50 Fecal Coliform SM 9221E RESULT None 30,000 20 YesR EH-205 CRW 09/06/05 6:50 Fecal Coliform SM 9221E RESULT None 130 20 75 LR EH-205 CSDO 09/06/05 6:50 Total Coliform SM 9221B RESULT None 500,000 20 YesR EH-205 CRW 09/06/05 6:50 Total Coliform SM 9221B RESULT None 170 20 75 LR EH-120 CRW 09/19/05 17:30Enterococcus SM 9223 RESULT< 10 10 YesPort04-05 DataPage 71 of 133 Analytical Laboratory: MECAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005Port of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-120 CSDO 09/19/05 17:30Enterococcus SM 9223 RESULTNone 171 10 75 LR EH-120 CRW 09/19/05 17:30Fecal Coliform SM 9221E RESULT< 20 20 YesR EH-120 CSDO 09/19/05 17:30Fecal Coliform SM 9221E RESULT<202075LR EH-120 CRW 09/19/05 17:30Total Coliform SM 9221B RESULT< 20 20 YesR EH-120 CSDO 09/19/05 17:30Total Coliform SM 9221B RESULTNone 110 20 75 LR EH-205 CRW 09/19/05 15:35Enterococcus SM 9223 RESULT< 10 10 YesR EH-205 CSDO 09/19/05 15:35Enterococcus SM 9223 RESULTNone 14,549 10 50 RR EH-205 CRW 09/19/05 15:35Fecal Coliform SM 9221E RESULTNone 20 20 YesR EH-205 CSDO 09/19/05 15:35Fecal Coliform SM 9221E RESULTNone 500 20 50 RR EH-205 CRW 09/19/05 15:35Total Coliform SM 9221B RESULTNone 40 20 YesR EH-205 CSDO 09/19/05 15:35Total Coliform SM 9221B RESULTNone 140,000 20 50 RR EH-210 CRW 09/19/05 15:25Enterococcus SM 9223 RESULT <10 10 NoR EH-210 CSDO 09/19/05 15:25Enterococcus SM 9223 RESULT None3,499 10 50 RR EH-210 CRW 09/19/05 15:25Fecal Coliform SM 9221E RESULT <20 20 NoR EH-210 CSDO 09/19/05 15:25Fecal Coliform SM 9221E RESULT None3,000 20 50 RR EH-210 CRW 09/19/05 15:25Total Coliform SM 9221B RESULT None20 20 NoR EH-210 CSDO 09/19/05 15:25Total Coliform SM 9221B RESULT None80,000 20 50 RPort04-05 DataPage 72 of 133 Analytical Laboratory: MECAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Solana BeachPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-390 CSDO 11/30/04 9:00EnterococcusSM 9223RESULTNone 3,441 10 YesR EH-390 CRW 11/30/04 9:10EnterococcusSM 9223RESULTNone 75 10 75 LR EH-390 CSDO 11/30/04 9:00Fecal ColiformSM 9221ERESULTNone 5,000 20 YesR EH-390 CRW 11/30/04 9:10Fecal ColiformSM 9221ERESULTNone 40 20 75 LR EH-390 CSDO 11/30/04 9:00Total ColiformSM 9221BRESULTNone 130,000 20 YesR EH-390 CRW 11/30/04 9:10Total ColiformSM 9221BRESULTNone 1,300 20 75 LR EH-390 CSDO 12/16/04 9:15EnterococcusSM 9223RESULTNone 1,212 10 NoR EH-390 CRW 12/16/04 9:30EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 12/16/04 9:15Fecal ColiformSM 9221ERESULTNone 5,000 20 NoR EH-390 CRW 12/16/04 9:30Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 12/16/04 9:15Total ColiformSM 9221BRESULTNone 2,400,000 20 NoR EH-390 CRW 12/16/04 9:30Total ColiformSM 9221BRESULTNone 20 20 75 LR EH-390 CSDO 01/31/05 10:00EnterococcusSM 9223RESULT<1010 NoR EH-390 CRW 01/31/05 10:15EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 01/31/05 10:00Fecal ColiformSM 9221ERESULTNone 500 20 NoR EH-390 CRW 01/31/05 10:15Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 01/31/05 10:00Total ColiformSM 9221BRESULTNone 14,000 20 NoR EH-390 CRW 01/31/05 10:15Total ColiformSM 9221BRESULTNone 20 20 75 LR EH-390 CSDO 02/28/05 9:45EnterococcusSM 9223RESULTNone 10 10 NoR EH-390 CRW 02/28/05 10:45EnterococcusSM 9223RESULTNone 10 10 75 LR EH-390 CSDO 02/28/05 9:45Fecal ColiformSM 9221ERESULTNone 800 20 NoR EH-390 CRW 02/28/05 10:45Fecal ColiformSM 9221ERESULTNone 20 20 75 LR EH-390 CSDO 02/28/05 9:45Total ColiformSM 9221BRESULTNone 230,000 20 NoR EH-390 CRW 02/28/05 10:45Total ColiformSM 9221BRESULTNone 40 20 75 LR EH-390 CSDO 03/31/05 9:00EnterococcusSM 9223RESULTNone 41 10 NoR EH-390 CRW 03/31/05 9:15EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 03/31/05 9:00Fecal ColiformSM 9221ERESULTNone 5,000 20 NoR EH-390 CRW 03/31/05 9:15Fecal ColiformSM 9221ERESULTAE -99 20 75 LR EH-390 CSDO 03/31/05 9:00Total ColiformSM 9221BRESULTNone 220,000 20 NoR EH-390 CRW 03/31/05 9:15Total ColiformSM 9221BRESULTNone 40 20 75 LR EH-390 CSDO 04/15/05 9:45EnterococcusSM 9223RESULTNone 1,439 10 NoR EH-390 CRW 04/15/05 10:00EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 04/15/05 9:45Fecal ColiformSM 9221ERESULTNone 8,000 20 NoR EH-390 CRW 04/15/05 10:00Fecal ColiformSM 9221ERESULTNone 20 20 75 LR EH-390 CSDO 04/15/05 9:45Total ColiformSM 9221BRESULTNone 800,000 20 NoR EH-390 CRW 04/15/05 10:00Total ColiformSM 9221BRESULTNone 20 20 75 LR EH-390 CSDO 04/27/05 10:00EnterococcusSM 9223RESULTNone 12,997 10 NoSB04-05 DataPage 73 of 133 Analytical Laboratory: MECAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Solana BeachPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-390 CRW 04/27/05 10:15EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 04/27/05 10:00Fecal ColiformSM 9221ERESULTNone 8,000 20 NoR EH-390 CRW 04/27/05 10:15Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 04/27/05 10:00Total ColiformSM 9221BRESULTNone 80,000 20 NoR EH-390 CRW 04/27/05 10:15Total ColiformSM 9221BRESULTNone 20 20 75 LR EH-390 CSDO 05/18/05 9:30EnterococcusSM 9223RESULTNone 4,568 10 NoR EH-390 CRW 05/18/05 9:45EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 05/18/05 9:30Fecal ColiformSM 9221ERESULTNone 8,000 20 NoR EH-390 CRW 05/18/05 9:45Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 05/18/05 9:30Total ColiformSM 9221BRESULTNone 700,000 20 NoR EH-390 CRW 05/18/05 9:45Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 06/02/05 9:30EnterococcusSM 9223RESULT10 NoR EH-390 CRW 06/02/05 9:45EnterococcusSM 9223RESULT10 75 LR EH-390 CSDO 06/02/05 9:30Fecal ColiformSM 9221ERESULT20 NoR EH-390 CRW 06/02/05 9:45Fecal ColiformSM 9221ERESULT20 75 LR EH-390 CSDO 06/02/05 9:30Total ColiformSM 9221BRESULT20 NoR EH-390 CRW 06/02/05 9:45Total ColiformSM 9221BRESULT20 75 LR EH-390 CSDO 06/16/05 10:15EnterococcusSM 9223RESULTNone 2,378 10 NoR EH-390 CRW 06/16/05 10:30EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 06/16/05 10:15Fecal ColiformSM 9221ERESULTNone 11,000 20 NoR EH-390 CRW 06/16/05 10:30Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 06/16/05 10:15Total ColiformSM 9221BRESULTNone 1,100,000 20 NoR EH-390 CRW 06/16/05 10:30Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 06/30/05 11:30EnterococcusSM 9223RESULTNone 1,281 10 NoR EH-390 CRW 06/30/05 11:45EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 06/30/05 11:30Fecal ColiformSM 9221ERESULTNone 500,000 20 NoR EH-390 CRW 06/30/05 11:45Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 06/30/05 11:30Total ColiformSM 9221BRESULTNone 5,000,000 20 NoR EH-390 CRW 06/30/05 11:45Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 07/14/05 10:45EnterococcusSM 9223RESULTNone 3,784 10 NoR EH-390 CRW 07/14/05 11:00EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 07/14/05 10:45Fecal ColiformSM 9221ERESULTNone 3,000 20 NoR EH-390 CRW 07/14/05 11:00Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 07/14/05 10:45Total ColiformSM 9221BRESULTNone 800,000 20 NoR EH-390 CRW 07/14/05 11:00Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 07/28/05 9:30EnterococcusSM 9223RESULTNone 7,279 10 NoR EH-390 CRW 07/28/05 9:45EnterococcusSM 9223RESULT<101075LSB04-05 DataPage 74 of 133 Analytical Laboratory: MECAnalytical Units: MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of Solana BeachPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-390 CSDO 07/28/05 9:30Fecal ColiformSM 9221ERESULTNone 2,200,000 20 NoR EH-390 CRW 07/28/05 9:45Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 07/28/05 9:30Total ColiformSM 9221BRESULT> 16,000,000 20 NoR EH-390 CRW 07/28/05 9:45Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 08/18/05 9:15EnterococcusSM 9223RESULTNone 1,782 10 NoR EH-390 CRW 08/18/05 9:30EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 08/18/05 9:15Fecal ColiformSM 9221ERESULTNone 7,000 20 NoR EH-390 CRW 08/18/05 9:30Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 08/18/05 9:15Total ColiformSM 9221BRESULTNone 500,000 20 NoR EH-390 CRW 08/18/05 9:30Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 08/31/05 9:30EnterococcusSM 9223RESULTNone 5,371 10 NoR EH-390 CRW 08/31/05 9:45EnterococcusSM 9223RESULTNone 10 10 75 LR EH-390 CSDO 08/31/05 9:30Fecal ColiformSM 9221ERESULTNone 50,000 20 NoR EH-390 CRW 08/31/05 9:45Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 08/31/05 9:30Total ColiformSM 9221BRESULTNone 2,400,000 20 NoR EH-390 CRW 08/31/05 9:45Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 09/16/05 10:30EnterococcusSM 9223RESULTNone 388 10 NoR EH-390 CRW 09/16/05 10:45EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 09/16/05 10:30Fecal ColiformSM 9221ERESULTNone 3,000 20 NoR EH-390 CRW 09/16/05 10:45Fecal ColiformSM 9221ERESULTNone 20 20 75 LR EH-390 CSDO 09/16/05 10:30Total ColiformSM 9221BRESULTNone 500,000 20 NoR EH-390 CRW 09/16/05 10:45Total ColiformSM 9221BRESULTNone 20 20 75 LR EH-390 CSDO 09/27/05 9:30EnterococcusSM 9223RESULTNone 27,551 10 NoR EH-390 CRW 09/27/05 9:30EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 09/27/05 9:30Fecal ColiformSM 9221ERESULTNone 230,000 20 NoR EH-390 CRW 09/27/05 9:30Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 09/27/05 9:30Total ColiformSM 9221BRESULTNone 2,200,000 20 NoR EH-390 CRW 09/27/05 9:30Total ColiformSM 9221BRESULT<202075LR EH-390 CSDO 10/28/05 9:30EnterococcusSM 9223RESULTNone 111,987 10 NoR EH-390 CRW 10/28/05 9:45EnterococcusSM 9223RESULT<101075LR EH-390 CSDO 10/28/05 9:30Fecal ColiformSM 9221ERESULTNone 700,000 20 NoR EH-390 CRW 10/28/05 9:45Fecal ColiformSM 9221ERESULT<202075LR EH-390 CSDO 10/28/05 9:30Total ColiformSM 9221BRESULTNone 3,000,000 20 NoR EH-390 CRW 10/28/05 9:45Total ColiformSM 9221BRESULT<202075LSB04-05 DataPage 75 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-250 CRW 11/02/04 14:00 Enterococcus EPA 1600 RESULT None 18 2 75 RR EH-250 CSDO 11/02/04 14:00 Enterococcus EPA 1600 RESULT None 280 20 NoR EH-250 CRW 11/02/04 14:00 Fecal Coliform SM 9222D RESULT None 6 2 75 RR EH-250 CSDO 11/02/04 14:00 Fecal Coliform SM 9221E RESULT None 300 20 NoR EH-250 CRW 11/02/04 14:00 Total Coliform SM 9222B RESULT None 52 2 75 RR EH-250 CSDO 11/02/04 14:00 Total Coliform SM 9221B RESULT None 2200 20 NoR EH-255 CRW 11/02/04 12:45 Enterococcus EPA 1600 RESULT None 8 2 75 LR EH-255 CSDO 11/02/04 12:45 Enterococcus EPA 1600 RESULT None 11000 20 N/AR EH-255 CRW 11/02/04 12:45 Fecal Coliform SM 9222D RESULT None 120 2 75 LR EH-255 CSDO 11/02/04 12:45 Fecal Coliform SM 9221E RESULT None 1700 20 N/AR EH-255 CRW 11/02/04 12:45 Total Coliform SM 9222B RESULT None 120 2 75 LR EH-255 CSDO 11/02/04 12:45 Total Coliform SM 9221B RESULT None 50000 20 N/AR EH-280 CRW 11/02/04 12:25 Enterococcus EPA 1600 RESULT None 2 2 75 LR EH-280 CSDO 11/02/04 12:25 Enterococcus EPA 1600 RESULT < 20 20 NoR EH-280 CRW 11/02/04 12:25 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-280 CSDO 11/02/04 12:25 Fecal Coliform SM 9221E RESULT None 20 20 NoR EH-280 CRW 11/02/04 12:25 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-280 CSDO 11/02/04 12:25 Total Coliform SM 9221B RESULT None 40 20 NoR EH-290 CRW 11/02/04 12:10 Enterococcus EPA 1600 RESULT None 16 2 0 MR EH-290 CSDO 11/02/04 12:10 Enterococcus EPA 1600 RESULT None 1000 20 YesR EH-290 CRW 11/02/04 12:10 Fecal Coliform SM 9222D RESULT < 2 2 0 MR EH-290 CSDO 11/02/04 12:10 Fecal Coliform SM 9221E RESULT None 1100 20 YesR EH-290 CRW 11/02/04 12:10 Total Coliform SM 9222B RESULT None 60 2 0 MR EH-290 CSDO 11/02/04 12:10 Total Coliform SM 9221B RESULT None 50000 20 YesR EH-300 CRW 11/02/04 12:00 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-300 CSDO 11/02/04 12:00 Enterococcus EPA 1600 RESULT None 200 20 NoR EH-300 CRW 11/02/04 12:00 Fecal Coliform SM 9222D RESULT None 4 2 75 LR EH-300 CSDO 11/02/04 12:00 Fecal Coliform SM 9221E RESULT None 80 20 NoR EH-300 CRW 11/02/04 12:00 Total Coliform SM 9222B RESULT None 8 2 75 LR EH-300 CSDO 11/02/04 12:00 Total Coliform SM 9221B RESULT None 5000 20 NoR EH-320 CRW 11/02/04 10:59 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 11/02/04 10:59 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 11/02/04 10:59 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 11/02/04 10:59 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 11/02/04 10:59 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 11/02/04 10:59 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 11/02/04 10:50 Enterococcus EPA 1600 RESULT None 2 2 75 LSD04-05 DataPage 76 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-330 CSDO 11/02/04 10:50 Enterococcus EPA 1600 RESULT None 2400 20 YesR EH-330 CRW 11/02/04 10:50 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-330 CSDO 11/02/04 10:50 Fecal Coliform SM 9221E RESULT None 80 20 YesR EH-330 CRW 11/02/04 10:50 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-330 CSDO 11/02/04 10:50 Total Coliform SM 9221B RESULT None 17000 20 YesR EH-340 CRW 11/02/04 10:00 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-340 CSDO 11/02/04 10:00 Enterococcus EPA 1600 RESULT None 1400 20 YesR EH-340 CRW 11/02/04 10:00 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-340 CSDO 11/02/04 10:00 Fecal Coliform SM 9221E RESULT None 2300 20 YesR EH-340 CRW 11/02/04 10:00 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-340 CSDO 11/02/04 10:00 Total Coliform SM 9221B RESULT None 8000 20 YesR FM-030 CRW 11/02/04 12:40 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 11/02/04 12:40 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 11/02/04 12:40 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 11/02/04 12:40 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 11/02/04 12:40 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 11/02/04 12:40 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 11/02/04 12:20 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 11/02/04 12:20 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 11/02/04 12:20 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 11/02/04 12:20 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 11/02/04 12:20 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 11/02/04 12:20 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 11/02/04 11:45 Enterococcus EPA 1600 RESULT None 6 2 0 MR FM-060 CSDO 11/02/04 11:45 Enterococcus EPA 1600 RESULT None 2200 20 YesR FM-060 CRW 11/02/04 11:45 Fecal Coliform SM 9222D RESULT None 2 2 0 MR FM-060 CSDO 11/02/04 11:45 Fecal Coliform SM 9221E RESULT None 300 20 YesR FM-060 CRW 11/02/04 11:45 Total Coliform SM 9222B RESULT None 18 2 0 MR FM-060 CSDO 11/02/04 11:45 Total Coliform SM 9221B RESULT None 14000 20 YesR FM-080 CRW 11/02/04 11:00 Enterococcus EPA 1600 RESULT None 2 2 75 RR FM-080 CSDO 11/02/04 11:00 Enterococcus EPA 1600 RESULT None 20 20 YesR FM-080 CRW 11/02/04 11:00 Fecal Coliform SM 9222D RESULT None 4 2 75 RR FM-080 CSDO 11/02/04 11:00 Fecal Coliform SM 9221E RESULT None 300 20 YesR FM-080 CRW 11/02/04 11:00 Total Coliform SM 9222B RESULT None 180 2 75 RR FM-080 CSDO 11/02/04 11:00 Total Coliform SM 9221B RESULT None 30000 20 YesR EH-250 CRW 12/13/04 11:55 Enterococcus EPA 1600 RESULT None 8 2 75 RR EH-250 CSDO 12/13/04 11:55 Enterococcus EPA 1600 RESULT None 4000 20 YesSD04-05 DataPage 77 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-250 CRW 12/13/04 11:55 Fecal Coliform SM 9222D RESULT None 12 2 75 RR EH-250 CSDO 12/13/04 11:55 Fecal Coliform SM 9221E RESULT None 20 20 YesR EH-250 CRW 12/13/04 11:55 Total Coliform SM 9222B RESULT None 140 2 75 RR EH-250 CSDO 12/13/04 11:55 Total Coliform SM 9221B RESULT None 14000 20 YesR EH-255 CRW 12/13/04 11:45 Enterococcus EPA 1600 RESULT None 4 2 75 LR EH-255 CSDO 12/13/04 11:45 Enterococcus EPA 1600 RESULT None 780 20 NoR EH-255 CRW 12/13/04 11:45 Fecal Coliform SM 9222D RESULT None 8 2 75 LR EH-255 CSDO 12/13/04 11:45 Fecal Coliform SM 9221E RESULT None 130 20 NoR EH-255 CRW 12/13/04 11:45 Total Coliform SM 9222B RESULT None 20 2 75 LR EH-255 CSDO 12/13/04 11:45 Total Coliform SM 9221B RESULT None 1100 20 NoR EH-280 CRW 12/13/04 11:00 Enterococcus EPA 1600 RESULT None 1200 2 75 LR EH-280 CSDO 12/13/04 11:00 Enterococcus EPA 1600 RESULT < 20 20 NoR EH-280 CRW 12/13/04 11:00 Fecal Coliform SM 9222D RESULT None 76 2 75 LR EH-280 CSDO 12/13/04 11:00 Fecal Coliform SM 9221E RESULT < 20 20 NoR EH-280 CRW 12/13/04 11:00 Total Coliform SM 9222B RESULT None 82 2 75 LR EH-280 CSDO 12/13/04 11:00 Total Coliform SM 9221B RESULT None 20 20 NoR EH-290 CRW 12/13/04 10:45 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 12/13/04 10:45 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 12/13/04 10:45 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 12/13/04 10:45 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 12/13/04 10:45 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 12/13/04 10:45 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 12/13/04 10:36 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 12/13/04 10:36 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 12/13/04 10:36 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 12/13/04 10:36 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 12/13/04 10:36 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 12/13/04 10:36 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 12/13/04 10:15 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 12/13/04 10:15 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 12/13/04 10:15 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 12/13/04 10:15 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 12/13/04 10:15 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 12/13/04 10:15 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 12/13/04 10:10 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 12/13/04 10:10 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 12/13/04 10:10 Fecal Coliform SM 9222D RESULT NS -99 2SD04-05 DataPage 78 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-330 CSDO 12/13/04 10:10 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 12/13/04 10:10 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 12/13/04 10:10 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 12/13/04 10:02 Enterococcus EPA 1600 RESULT NS -99 2R EH-340 CSDO 12/13/04 10:02 Enterococcus EPA 1600 RESULT NS -99 20R EH-340 CRW 12/13/04 10:02 Fecal Coliform SM 9222D RESULT NS -99 2R EH-340 CSDO 12/13/04 10:02 Fecal Coliform SM 9221E RESULT NS -99 20R EH-340 CRW 12/13/04 10:02 Total Coliform SM 9222B RESULT NS -99 2R EH-340 CSDO 12/13/04 10:02 Total Coliform SM 9221B RESULT NS -99 20R FM-030 CRW 12/13/04 11:20 Enterococcus EPA 1600 RESULT None 6 2 75 LR FM-030 CSDO 12/13/04 11:20 Enterococcus EPA 1600 RESULT None 5600 20 NoR FM-030 CRW 12/13/04 11:20 Fecal Coliform SM 9222D RESULT None 18 2 75 LR FM-030 CSDO 12/13/04 11:20 Fecal Coliform SM 9221E RESULT None 7000 20 NoR FM-030 CRW 12/13/04 11:20 Total Coliform SM 9222B RESULT < 20 2 75 LR FM-030 CSDO 12/13/04 11:20 Total Coliform SM 9221B RESULT None 17000 20 NoR FM-050 CRW 12/13/04 10:52 Enterococcus EPA 1600 RESULT None 6 2 0 MR FM-050 CSDO 12/13/04 10:52 Enterococcus EPA 1600 RESULT < 20 20 YesR FM-050 CRW 12/13/04 10:52 Fecal Coliform SM 9222D RESULT None 8 2 0 MR FM-050 CSDO 12/13/04 10:52 Fecal Coliform SM 9221E RESULT < 20 20 YesR FM-050 CRW 12/13/04 10:52 Total Coliform SM 9222B RESULT None 40 2 0 MR FM-050 CSDO 12/13/04 10:52 Total Coliform SM 9221B RESULT < 20 20 YesR FM-060 CRW 12/13/04 10:25 Enterococcus EPA 1600 RESULT None 8 2 75 RR FM-060 CSDO 12/13/04 10:25 Enterococcus EPA 1600 RESULT None 3200 20 YesR FM-060 CRW 12/13/04 10:25 Fecal Coliform SM 9222D RESULT None 14 2 75 RR FM-060 CSDO 12/13/04 10:25 Fecal Coliform SM 9221E RESULT None 110000 20 YesR FM-060 CRW 12/13/04 10:25 Total Coliform SM 9222B RESULT < 200 200 75 RR FM-060 CSDO 12/13/04 10:25 Total Coliform SM 9221B RESULT None 50000 20 YesR FM-080 CRW 12/13/04 10:18 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 12/13/04 10:18 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 12/13/04 10:18 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 12/13/04 10:18 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 12/13/04 10:18 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 12/13/04 10:18 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 01/18/05 8:50 Enterococcus EPA 1600 RESULT None 2 2 0 MR EH-300 CSDO 01/18/05 8:50 Enterococcus EPA 1600 RESULT None 4000 20 YesR EH-300 CRW 01/18/05 8:50 Fecal Coliform SM 9222D RESULT None 14 2 0 MR EH-300 CSDO 01/18/05 8:50 Fecal Coliform SM 9221E RESULT None 80 20 YesSD04-05 DataPage 79 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-300 CRW 01/18/05 8:50 Total Coliform SM 9222B RESULT None 18 2 0 MR EH-300 CSDO 01/18/05 8:50 Total Coliform SM 9221B RESULT None 23000 20 YesR EH-320 CRW 01/18/05 8:17 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 01/18/05 8:17 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 01/18/05 8:17 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 01/18/05 8:17 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 01/18/05 8:17 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 01/18/05 8:17 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 01/18/05 8:15 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 01/18/05 8:15 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 01/18/05 8:15 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 01/18/05 8:15 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 01/18/05 8:15 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 01/18/05 8:15 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 01/18/05 8:05 Enterococcus EPA 1600 RESULT None 10 2 75 RR EH-340 CSDO 01/18/05 8:05 Enterococcus EPA 1600 RESULT None 600 20 YesR EH-340 CRW 01/18/05 8:05 Fecal Coliform SM 9222D RESULT None 2 2 75 RR EH-340 CSDO 01/18/05 8:05 Fecal Coliform SM 9221E RESULT None 2300 20 YesR EH-340 CRW 01/18/05 8:05 Total Coliform SM 9222B RESULT None 22 2 75 RR EH-340 CSDO 01/18/05 8:05 Total Coliform SM 9221B RESULT None 2800 20 YesR FM-060 CRW 01/18/05 8:40 Enterococcus EPA 1600 RESULT None 14 2 75 RR FM-060 CSDO 01/18/05 8:40 Enterococcus EPA 1600 RESULT None 660 20 YesR FM-060 CRW 01/18/05 8:40 Fecal Coliform SM 9222D RESULT None 14 2 75 RR FM-060 CSDO 01/18/05 8:40 Fecal Coliform SM 9221E RESULT None 300 20 YesR FM-060 CRW 01/18/05 8:40 Total Coliform SM 9222B RESULT None 34 2 75 RR FM-060 CSDO 01/18/05 8:40 Total Coliform SM 9221B RESULT None 5000 20 YesR FM-080 CRW 01/18/05 8:31 Enterococcus EPA 1600 RESULT None 6 2 75 LR FM-080 CSDO 01/18/05 8:31 Enterococcus EPA 1600 RESULT None 500 20 YesR FM-080 CRW 01/18/05 8:31 Fecal Coliform SM 9222D RESULT None 4 2 75 LR FM-080 CSDO 01/18/05 8:31 Fecal Coliform SM 9221E RESULT None 1700 20 YesR FM-080 CRW 01/18/05 8:31 Total Coliform SM 9222B RESULT None 18 2 75 LR FM-080 CSDO 01/18/05 8:31 Total Coliform SM 9221B RESULT None 140000 20 YesR EH-250 CRW 01/20/05 10:10 Enterococcus EPA 1600 RESULT NS -99 2R EH-250 CSDO 01/20/05 10:10 Enterococcus EPA 1600 RESULT NS -99 20R EH-250 CRW 01/20/05 10:10 Fecal Coliform SM 9222D RESULT NS -99 2R EH-250 CSDO 01/20/05 10:10 Fecal Coliform SM 9221E RESULT NS -99 20R EH-250 CRW 01/20/05 10:10 Total Coliform SM 9222B RESULT NS -99 2SD04-05 DataPage 80 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-250 CSDO 01/20/05 10:10 Total Coliform SM 9221B RESULT NS -99 20R EH-255 CRW 01/20/05 10:02 Enterococcus EPA 1600 RESULT None 16 2 75 LR EH-255 CSDO 01/20/05 10:02 Enterococcus EPA 1600 RESULT None 1400 20 YesR EH-255 CRW 01/20/05 10:02 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-255 CSDO 01/20/05 10:02 Fecal Coliform SM 9221E RESULT None 70 20 YesR EH-255 CRW 01/20/05 10:02 Total Coliform SM 9222B RESULT None 200 2 75 LR EH-255 CSDO 01/20/05 10:02 Total Coliform SM 9221B RESULT None 13000 20 YesR EH-280 CRW 01/20/05 9:38 Enterococcus EPA 1600 RESULT None 16 2 75 LR EH-280 CSDO 01/20/05 9:38 Enterococcus EPA 1600 RESULT None 20 20 YesR EH-280 CRW 01/20/05 9:38 Fecal Coliform SM 9222D RESULT None 12 2 75 LR EH-280 CSDO 01/20/05 9:38 Fecal Coliform SM 9221E RESULT < 20 20 YesR EH-280 CRW 01/20/05 9:38 Total Coliform SM 9222B RESULT None 60 2 75 LR EH-280 CSDO 01/20/05 9:38 Total Coliform SM 9221B RESULT None 40 20 YesR EH-290 CRW 01/20/05 9:05 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 01/20/05 9:05 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 01/20/05 9:05 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 01/20/05 9:05 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 01/20/05 9:05 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 01/20/05 9:05 Total Coliform SM 9221B RESULT NS -99 20R FM-030 CRW 01/20/05 9:48 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 01/20/05 9:48 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 01/20/05 9:48 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 01/20/05 9:48 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 01/20/05 9:48 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 01/20/05 9:48 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 01/20/05 9:32 Enterococcus EPA 1600 RESULT None 10 2 75 LR FM-050 CSDO 01/20/05 9:32 Enterococcus EPA 1600 RESULT None 460 20 NoR FM-050 CRW 01/20/05 9:32 Fecal Coliform SM 9222D RESULT None 6 2 75 LR FM-050 CSDO 01/20/05 9:32 Fecal Coliform SM 9221E RESULT < 20 20 NoR FM-050 CRW 01/20/05 9:32 Total Coliform SM 9222B RESULT None 44 2 75 LR FM-050 CSDO 01/20/05 9:32 Total Coliform SM 9221B RESULT None 7000 20 NoR EH-250 CRW 02/01/05 11:37 Enterococcus EPA 1600 RESULT None 2 2 75 LR EH-250 CSDO 02/01/05 11:37 Enterococcus EPA 1600 RESULT None 520 20 NoR EH-250 CRW 02/01/05 11:37 Fecal Coliform SM 9222D RESULT None 4 2 75 LR EH-250 CSDO 02/01/05 11:37 Fecal Coliform SM 9221E RESULT < 20 20 NoR EH-250 CRW 02/01/05 11:37 Total Coliform SM 9222B RESULT None 18 2 75 LR EH-250 CSDO 02/01/05 11:37 Total Coliform SM 9221B RESULT None 5000 20 NoSD04-05 DataPage 81 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-255 CRW 02/01/05 11:05 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-255 CSDO 02/01/05 11:05 Enterococcus EPA 1600 RESULT None 4200 20 YesR EH-255 CRW 02/01/05 11:05 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-255 CSDO 02/01/05 11:05 Fecal Coliform SM 9221E RESULT None 300 20 YesR EH-255 CRW 02/01/05 11:05 Total Coliform SM 9222B RESULT None 10 2 75 LR EH-255 CSDO 02/01/05 11:05 Total Coliform SM 9221B RESULT None 8000 20 YesR EH-280 CRW 02/01/05 10:40 Enterococcus EPA 1600 RESULT None 2 2 75 LR EH-280 CSDO 02/01/05 10:40 Enterococcus EPA 1600 RESULT None 100 20 YesR EH-280 CRW 02/01/05 10:40 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-280 CSDO 02/01/05 10:40 Fecal Coliform SM 9221E RESULT < 20 20 YesR EH-280 CRW 02/01/05 10:40 Total Coliform SM 9222B RESULT None 38 2 75 LR EH-280 CSDO 02/01/05 10:40 Total Coliform SM 9221B RESULT None 300 20 YesR EH-290 CRW 02/01/05 10:25 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 02/01/05 10:25 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 02/01/05 10:25 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 02/01/05 10:25 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 02/01/05 10:25 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 02/01/05 10:25 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 02/01/05 10:16 Enterococcus EPA 1600 RESULT < 2 2 0 MR EH-300 CSDO 02/01/05 10:16 Enterococcus EPA 1600 RESULT None 300 20 YesR EH-300 CRW 02/01/05 10:16 Fecal Coliform SM 9222D RESULT None 4 2 0 MR EH-300 CSDO 02/01/05 10:16 Fecal Coliform SM 9221E RESULT < 20 20 YesR EH-300 CRW 02/01/05 10:16 Total Coliform SM 9222B RESULT None 18 2 0 MR EH-300 CSDO 02/01/05 10:16 Total Coliform SM 9221B RESULT None 800 20 YesR EH-320 CRW 02/01/05 9:43 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-320 CSDO 02/01/05 9:43 Enterococcus EPA 1600 RESULT None 1400 20 YesR EH-320 CRW 02/01/05 9:43 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-320 CSDO 02/01/05 9:43 Fecal Coliform SM 9221E RESULT < 20 20 YesR EH-320 CRW 02/01/05 9:43 Total Coliform SM 9222B RESULT None 2 2 75 RR EH-320 CSDO 02/01/05 9:43 Total Coliform SM 9221B RESULT None 1700 20 YesR EH-330 CRW 02/01/05 9:39 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 02/01/05 9:39 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 02/01/05 9:39 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 02/01/05 9:39 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 02/01/05 9:39 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 02/01/05 9:39 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 02/01/05 9:30 Enterococcus EPA 1600 RESULT < 2 2 75 LSD04-05 DataPage 82 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-340 CSDO 02/01/05 9:30 Enterococcus EPA 1600 RESULT None 400 20 NoR EH-340 CRW 02/01/05 9:30 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-340 CSDO 02/01/05 9:30 Fecal Coliform SM 9221E RESULT None 110 20 NoR EH-340 CRW 02/01/05 9:30 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-340 CSDO 02/01/05 9:30 Total Coliform SM 9221B RESULT None 440 20 NoR FM-030 CRW 02/01/05 10:58 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 02/01/05 10:58 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 02/01/05 10:58 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 02/01/05 10:58 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 02/01/05 10:58 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 02/01/05 10:58 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 02/01/05 10:35 Enterococcus EPA 1600 RESULT None 10 2 0 MR FM-050 CSDO 02/01/05 10:35 Enterococcus EPA 1600 RESULT None 760 20 YesR FM-050 CRW 02/01/05 10:35 Fecal Coliform SM 9222D RESULT < 200 200 0 MR FM-050 CSDO 02/01/05 10:35 Fecal Coliform SM 9221E RESULT None 500 20 YesR FM-050 CRW 02/01/05 10:35 Total Coliform SM 9222B RESULT None 600 2 0 MR FM-050 CSDO 02/01/05 10:35 Total Coliform SM 9221B RESULT None 130000 20 YesR FM-060 CRW 02/01/05 9:55 Enterococcus EPA 1600 RESULT None 140 2 75 RR FM-060 CSDO 02/01/05 9:55 Enterococcus EPA 1600 RESULT None 140 20 YesR FM-060 CRW 02/01/05 9:55 Fecal Coliform SM 9222D RESULT None 46 2 75 RR FM-060 CSDO 02/01/05 9:55 Fecal Coliform SM 9221E RESULT None 110 20 YesR FM-060 CRW 02/01/05 9:55 Total Coliform SM 9222B RESULT None 700 2 75 RR FM-060 CSDO 02/01/05 9:55 Total Coliform SM 9221B RESULT None 2800 20 YesR FM-080 CRW 02/01/05 9:45 Enterococcus EPA 1600 RESULT NS < 2 75 LR FM-080 CSDO 02/01/05 9:45 Enterococcus EPA 1600 RESULT NS None 20 YesR FM-080 CRW 02/01/05 9:45 Fecal Coliform SM 9222D RESULT NS < 2 75 LR FM-080 CSDO 02/01/05 9:45 Fecal Coliform SM 9221E RESULT NS None 20 YesR FM-080 CRW 02/01/05 9:45 Total Coliform SM 9222B RESULT NS None 2 75 LR FM-080 CSDO 02/01/05 9:45 Total Coliform SM 9221B RESULT NS None 20 YesR EH-250 CRW 03/01/05 8:20 Enterococcus EPA 1600 RESULT None 2 2 75 LR EH-250 CSDO 03/01/05 8:20 Enterococcus EPA 1600 RESULT None 220 20 NoR EH-250 CRW 03/01/05 8:20 Fecal Coliform SM 9222D RESULT None 6 2 75 LR EH-250 CSDO 03/01/05 8:20 Fecal Coliform SM 9221E RESULT None 20 20 NoR EH-250 CRW 03/01/05 8:20 Total Coliform SM 9222B RESULT None 20 2 75 LR EH-250 CSDO 03/01/05 8:20 Total Coliform SM 9221B RESULT None 1100 20 NoR EH-255 CRW 03/01/05 8:45 Enterococcus EPA 1600 RESULT None 4 2 75 LR EH-255 CSDO 03/01/05 8:45 Enterococcus EPA 1600 RESULT None 500 20 YesSD04-05 DataPage 83 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-255 CRW 03/01/05 8:45 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-255 CSDO 03/01/05 8:45 Fecal Coliform SM 9221E RESULT None 40 20 YesR EH-255 CRW 03/01/05 8:45 Total Coliform SM 9222B RESULT None 8 2 75 LR EH-255 CSDO 03/01/05 8:45 Total Coliform SM 9221B RESULT None 4000 20 YesR EH-280 CRW 03/01/05 9:17 Enterococcus EPA 1600 RESULT None 2 2 75 LR EH-280 CSDO 03/01/05 9:17 Enterococcus EPA 1600 RESULT None 20 20 YesR EH-280 CRW 03/01/05 9:17 Fecal Coliform SM 9222D RESULT None 6 2 75 LR EH-280 CSDO 03/01/05 9:17 Fecal Coliform SM 9221E RESULT None 20 20 YesR EH-280 CRW 03/01/05 9:17 Total Coliform SM 9222B RESULT None 22 2 75 LR EH-280 CSDO 03/01/05 9:17 Total Coliform SM 9221B RESULT None 300 20 YesR EH-290 CRW 03/01/05 9:30 Enterococcus EPA 1600 RESULT None 10 2 0 MR EH-290 CSDO 03/01/05 9:30 Enterococcus EPA 1600 RESULT None 30000 20 NoR EH-290 CRW 03/01/05 9:30 Fecal Coliform SM 9222D RESULT None 8 2 0 MR EH-290 CSDO 03/01/05 9:30 Fecal Coliform SM 9221E RESULT None 80000 20 NoR EH-290 CRW 03/01/05 9:30 Total Coliform SM 9222B RESULT None 160 2 0 MR EH-290 CSDO 03/01/05 9:30 Total Coliform SM 9221B RESULT None 240000 20 NoR EH-300 CRW 03/01/05 9:54 Enterococcus EPA 1600 RESULT None 2 2 0 MR EH-300 CSDO 03/01/05 9:54 Enterococcus EPA 1600 RESULT None 1400 20 YesR EH-300 CRW 03/01/05 9:54 Fecal Coliform SM 9222D RESULT None 4 2 0 MR EH-300 CSDO 03/01/05 9:54 Fecal Coliform SM 9221E RESULT None 8000 20 YesR EH-300 CRW 03/01/05 9:54 Total Coliform SM 9222B RESULT None 6 2 0 MR EH-300 CSDO 03/01/05 9:54 Total Coliform SM 9221B RESULT None 22000 20 YesR EH-320 CRW 03/01/05 10:25 Enterococcus EPA 1600 RESULT None 660 2 75 RR EH-320 CSDO 03/01/05 10:25 Enterococcus EPA 1600 RESULT None 160 20 YesR EH-320 CRW 03/01/05 10:25 Fecal Coliform SM 9222D RESULT None 140 2 75 RR EH-320 CSDO 03/01/05 10:25 Fecal Coliform SM 9221E RESULT None 110 20 YesR EH-320 CRW 03/01/05 10:25 Total Coliform SM 9222B RESULT None 1800 2 75 RR EH-320 CSDO 03/01/05 10:25 Total Coliform SM 9221B RESULT None 17000 20 YesR EH-330 CRW 03/01/05 10:54 Enterococcus EPA 1600 RESULT None 4 2 75 LR EH-330 CSDO 03/01/05 10:54 Enterococcus EPA 1600 RESULT None 7000 20 YesR EH-330 CRW 03/01/05 10:54 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-330 CSDO 03/01/05 10:54 Fecal Coliform SM 9221E RESULT None 3000 20 YesR EH-330 CRW 03/01/05 10:54 Total Coliform SM 9222B RESULT None 4 2 75 LR EH-330 CSDO 03/01/05 10:54 Total Coliform SM 9221B RESULT None 50000 20 YesR EH-340 CRW 03/01/05 11:03 Enterococcus EPA 1600 RESULT None 4 2 75 RR EH-340 CSDO 03/01/05 11:03 Enterococcus EPA 1600 RESULT None 2800 20 YesR EH-340 CRW 03/01/05 11:03 Fecal Coliform SM 9222D RESULT < 2 2 75 RSD04-05 DataPage 84 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-340 CSDO 03/01/05 11:03 Fecal Coliform SM 9221E RESULT None 3000 20 YesR EH-340 CRW 03/01/05 11:03 Total Coliform SM 9222B RESULT None 16 2 75 RR EH-340 CSDO 03/01/05 11:03 Total Coliform SM 9221B RESULT None 13000 20 YesR FM-030 CRW 03/01/05 8:35 Enterococcus EPA 1600 RESULT None 8 2 75 LR FM-030 CSDO 03/01/05 8:35 Enterococcus EPA 1600 RESULT None 980 20 YesR FM-030 CRW 03/01/05 8:35 Fecal Coliform SM 9222D RESULT None 6 2 75 LR FM-030 CSDO 03/01/05 8:35 Fecal Coliform SM 9221E RESULT None 1100 20 YesR FM-030 CRW 03/01/05 8:35 Total Coliform SM 9222B RESULT None 60 2 75 LR FM-030 CSDO 03/01/05 8:35 Total Coliform SM 9221B RESULT None 17000 20 YesR FM-050 CRW 03/01/05 9:12 Enterococcus EPA 1600 RESULT None 6 2 0 MR FM-050 CSDO 03/01/05 9:12 Enterococcus EPA 1600 RESULT < 20 20 NoR FM-050 CRW 03/01/05 9:12 Fecal Coliform SM 9222D RESULT None 4 2 0 MR FM-050 CSDO 03/01/05 9:12 Fecal Coliform SM 9221E RESULT < 20 20 NoR FM-050 CRW 03/01/05 9:12 Total Coliform SM 9222B RESULT None 20 2 0 MR FM-050 CSDO 03/01/05 9:12 Total Coliform SM 9221B RESULT None 20 20 NoR FM-060 CRW 03/01/05 9:48 Enterococcus EPA 1600 RESULT None 2 2 75 RR FM-060 CSDO 03/01/05 9:48 Enterococcus EPA 1600 RESULT None 660 20 YesR FM-060 CRW 03/01/05 9:48 Fecal Coliform SM 9222D RESULT None 6 2 75 RR FM-060 CSDO 03/01/05 9:48 Fecal Coliform SM 9221E RESULT None 170 20 YesR FM-060 CRW 03/01/05 9:48 Total Coliform SM 9222B RESULT None 40 2 75 RR FM-060 CSDO 03/01/05 9:48 Total Coliform SM 9221B RESULT None 5000 20 YesR FM-080 CRW 03/01/05 10:13 Enterococcus EPA 1600 RESULT None 6 2 75 RR FM-080 CSDO 03/01/05 10:13 Enterococcus EPA 1600 RESULT None 360 20 YesR FM-080 CRW 03/01/05 10:13 Fecal Coliform SM 9222D RESULT None 8 2 75 RR FM-080 CSDO 03/01/05 10:13 Fecal Coliform SM 9221E RESULT None 300 20 YesR FM-080 CRW 03/01/05 10:13 Total Coliform SM 9222B RESULT None 12 2 75 RR FM-080 CSDO 03/01/05 10:13 Total Coliform SM 9221B RESULT None 13000 20 YesR EH-250 CRW 04/04/05 13:15 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-250 CSDO 04/04/05 13:15 Enterococcus EPA 1600 RESULT None 160 20 YesR EH-250 CRW 04/04/05 13:15 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-250 CSDO 04/04/05 13:15 Fecal Coliform SM 9221E RESULT None 20 20 YesR EH-250 CRW 04/04/05 13:15 Total Coliform SM 9222B RESULT None 4 2 75 RR EH-250 CSDO 04/04/05 13:15 Total Coliform SM 9221B RESULT None 5000 20 YesR EH-255 CRW 04/04/05 12:49 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-255 CSDO 04/04/05 12:49 Enterococcus EPA 1600 RESULT None 12000 20 YesR EH-255 CRW 04/04/05 12:49 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-255 CSDO 04/04/05 12:49 Fecal Coliform SM 9221E RESULT None 110 20 YesSD04-05 DataPage 85 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-255 CRW 04/04/05 12:49 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-255 CSDO 04/04/05 12:49 Total Coliform SM 9221B RESULT None 24000 20 YesR EH-280 CRW 04/04/05 12:33 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-280 CSDO 04/04/05 12:33 Enterococcus EPA 1600 RESULT None 40 20 YesR EH-280 CRW 04/04/05 12:33 Fecal Coliform SM 9222D RESULT None 4 2 75 RR EH-280 CSDO 04/04/05 12:33 Fecal Coliform SM 9221E RESULT None 20 20 YesR EH-280 CRW 04/04/05 12:33 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-280 CSDO 04/04/05 12:33 Total Coliform SM 9221B RESULT None 40 20 YesR EH-290 CRW 04/04/05 12:21 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-290 CSDO 04/04/05 12:21 Enterococcus EPA 1600 RESULT None 5600 20 YesR EH-290 CRW 04/04/05 12:21 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-290 CSDO 04/04/05 12:21 Fecal Coliform SM 9221E RESULT None 1100 20 YesR EH-290 CRW 04/04/05 12:21 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-290 CSDO 04/04/05 12:21 Total Coliform SM 9221B RESULT None 8000 20 YesR EH-300 CRW 04/04/05 12:03 Enterococcus EPA 1600 RESULT < 2 2 0 MR EH-300 CSDO 04/04/05 12:03 Enterococcus EPA 1600 RESULT None 200 20 YesR EH-300 CRW 04/04/05 12:03 Fecal Coliform SM 9222D RESULT None 4 2 0 MR EH-300 CSDO 04/04/05 12:03 Fecal Coliform SM 9221E RESULT None 20 20 YesR EH-300 CRW 04/04/05 12:03 Total Coliform SM 9222B RESULT None 2 2 0 MR EH-300 CSDO 04/04/05 12:03 Total Coliform SM 9221B RESULT None 1700 20 YesR EH-320 CRW 04/04/05 11:17 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 04/04/05 11:17 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 04/04/05 11:17 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 04/04/05 11:17 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 04/04/05 11:17 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 04/04/05 11:17 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 04/04/05 11:23 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-330 CSDO 04/04/05 11:23 Enterococcus EPA 1600 RESULT None 480 20 NoR EH-330 CRW 04/04/05 11:23 Fecal Coliform SM 9222D RESULT None 2 2 75 RR EH-330 CSDO 04/04/05 11:23 Fecal Coliform SM 9221E RESULT None 130 20 NoR EH-330 CRW 04/04/05 11:23 Total Coliform SM 9222B RESULT None 2 2 75 RR EH-330 CSDO 04/04/05 11:23 Total Coliform SM 9221B RESULT None 13000 20 NoR EH-340 CRW 04/04/05 11:10 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-340 CSDO 04/04/05 11:10 Enterococcus EPA 1600 RESULT None 1800 20 NoR EH-340 CRW 04/04/05 11:10 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-340 CSDO 04/04/05 11:10 Fecal Coliform SM 9221E RESULT None 500 20 NoR EH-340 CRW 04/04/05 11:10 Total Coliform SM 9222B RESULT None 4 2 75 LSD04-05 DataPage 86 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-340 CSDO 04/04/05 11:10 Total Coliform SM 9221B RESULT None 13000 20 NoR FM-030 CRW 04/04/05 13:00 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-030 CSDO 04/04/05 13:00 Enterococcus EPA 1600 RESULT None 20000 20 NoR FM-030 CRW 04/04/05 13:00 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-030 CSDO 04/04/05 13:00 Fecal Coliform SM 9221E RESULT None 3000 20 NoR FM-030 CRW 04/04/05 13:00 Total Coliform SM 9222B RESULT < 2 2 75 RR FM-030 CSDO 04/04/05 13:00 Total Coliform SM 9221B RESULT None 5000 20 NoR FM-050 CRW 04/04/05 12:31 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 04/04/05 12:31 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 04/04/05 12:31 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 04/04/05 12:31 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 04/04/05 12:31 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 04/04/05 12:31 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 04/04/05 11:55 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-060 CSDO 04/04/05 11:55 Enterococcus EPA 1600 RESULT None 600 20 NoR FM-060 CRW 04/04/05 11:55 Fecal Coliform SM 9222D RESULT None 4 2 75 RR FM-060 CSDO 04/04/05 11:55 Fecal Coliform SM 9221E RESULT None 36 20 NoR FM-060 CRW 04/04/05 11:55 Total Coliform SM 9222B RESULT None 6 2 75 RR FM-060 CSDO 04/04/05 11:55 Total Coliform SM 9221B RESULT None 500 20 NoR FM-080 CRW 04/04/05 11:34 Enterococcus EPA 1600 RESULT None 2 2 75 RR FM-080 CSDO 04/04/05 11:34 Enterococcus EPA 1600 RESULT None 400 20 YesR FM-080 CRW 04/04/05 11:34 Fecal Coliform SM 9222D RESULT None 20 2 75 RR FM-080 CSDO 04/04/05 11:34 Fecal Coliform SM 9221E RESULT None 20 20 YesR FM-080 CRW 04/04/05 11:34 Total Coliform SM 9222B RESULT None 260 2 75 RR FM-080 CSDO 04/04/05 11:34 Total Coliform SM 9221B RESULT None 5000 20 YesR EH-340 CRW 04/18/05 9:13 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-340 CSDO 04/18/05 9:13 Enterococcus EPA 1600 RESULT None 3200 20 NoR EH-340 CRW 04/18/05 9:13 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-340 CSDO 04/18/05 9:13 Fecal Coliform SM 9221E RESULT None 300 20 NoR EH-340 CRW 04/18/05 9:13 Total Coliform SM 9222B RESULT None 8 2 75 RR EH-340 CSDO 04/18/05 9:13 Total Coliform SM 9221B RESULT None 3000 20 NoR FM-080 CRW 04/18/05 9:34 Enterococcus EPA 1600 RESULT None 4 2 75 RR FM-080 CSDO 04/18/05 9:34 Enterococcus EPA 1600 RESULT None 3200 20 YesR FM-080 CRW 04/18/05 9:34 Fecal Coliform SM 9222D RESULT None 4 2 75 RR FM-080 CSDO 04/18/05 9:34 Fecal Coliform SM 9221E RESULT None 400 20 YesR FM-080 CRW 04/18/05 9:34 Total Coliform SM 9222B RESULT None 34 2 75 RR FM-080 CSDO 04/18/05 9:34 Total Coliform SM 9221B RESULT None 80000 20 YesSD04-05 DataPage 87 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-250 CRW 04/19/05 10:24 Enterococcus EPA 1600 RESULT None 18 2 75 RR EH-250 CSDO 04/19/05 10:24 Enterococcus EPA 1600 RESULT < 20 20 YesR EH-250 CRW 04/19/05 10:24 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-250 CSDO 04/19/05 10:24 Fecal Coliform SM 9221E RESULT < 20 20 YesR EH-250 CRW 04/19/05 10:24 Total Coliform SM 9222B RESULT None 8600 2 75 RR EH-250 CSDO 04/19/05 10:24 Total Coliform SM 9221B RESULT < 20 20 YesR EH-255 CRW 04/19/05 9:53 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-255 CSDO 04/19/05 9:53 Enterococcus EPA 1600 RESULT None 13000 20 NoR EH-255 CRW 04/19/05 9:53 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-255 CSDO 04/19/05 9:53 Fecal Coliform SM 9221E RESULT None 3000 20 NoR EH-255 CRW 04/19/05 9:53 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-255 CSDO 04/19/05 9:53 Total Coliform SM 9221B RESULT None 23000 20 NoR EH-280 CRW 04/19/05 9:27 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-280 CSDO 04/19/05 9:27 Enterococcus EPA 1600 RESULT < 20 20 YesR EH-280 CRW 04/19/05 9:27 Fecal Coliform SM 9222D RESULT None 4 2 75 LR EH-280 CSDO 04/19/05 9:27 Fecal Coliform SM 9221E RESULT None 20 20 YesR EH-280 CRW 04/19/05 9:27 Total Coliform SM 9222B RESULT None 26 2 75 LR EH-280 CSDO 04/19/05 9:27 Total Coliform SM 9221B RESULT None 80 20 YesR EH-300 CRW 04/19/05 8:47 Enterococcus EPA 1600 RESULT None 100 2 0 MR EH-300 CSDO 04/19/05 8:47 Enterococcus EPA 1600 RESULT None 4200 20 YesR EH-300 CRW 04/19/05 8:47 Fecal Coliform SM 9222D RESULT None 16 2 0 MR EH-300 CSDO 04/19/05 8:47 Fecal Coliform SM 9221E RESULT None 300 20 YesR EH-300 CRW 04/19/05 8:47 Total Coliform SM 9222B RESULT None 1000 2 0 MR EH-300 CSDO 04/19/05 8:47 Total Coliform SM 9221B RESULT None 7000 20 YesR FM-060 CRW 04/19/05 9:00 Enterococcus EPA 1600 RESULT None 2 2 75 RR FM-060 CSDO 04/19/05 9:00 Enterococcus EPA 1600 RESULT None 420 20 NoR FM-060 CRW 04/19/05 9:00 Fecal Coliform SM 9222D RESULT None 4 2 75 RR FM-060 CSDO 04/19/05 9:00 Fecal Coliform SM 9221E RESULT None 1100 20 NoR FM-060 CRW 04/19/05 9:00 Total Coliform SM 9222B RESULT < 200 200 75 RR FM-060 CSDO 04/19/05 9:00 Total Coliform SM 9221B RESULT None 1400 20 NoR EH-250 CRW 05/02/05 12:25 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-250 CSDO 05/02/05 12:25 Enterococcus EPA 1600 RESULT None 10000 20 NoR EH-250 CRW 05/02/05 12:25 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-250 CSDO 05/02/05 12:25 Fecal Coliform SM 9221E RESULT None 5000 20 NoR EH-250 CRW 05/02/05 12:25 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-250 CSDO 05/02/05 12:25 Total Coliform SM 9221B RESULT None 30000 20 NoR EH-255 CRW 05/02/05 12:10 Enterococcus EPA 1600 RESULT None 4 2 75 LSD04-05 DataPage 88 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-255 CSDO 05/02/05 12:10 Enterococcus EPA 1600 RESULT None 16000 20 YesR EH-255 CRW 05/02/05 12:10 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-255 CSDO 05/02/05 12:10 Fecal Coliform SM 9221E RESULT None 1700 20 YesR EH-255 CRW 05/02/05 12:10 Total Coliform SM 9222B RESULT < 20 2 75 LR EH-255 CSDO 05/02/05 12:10 Total Coliform SM 9221B RESULT None 22000 20 YesR EH-280 CRW 05/02/05 11:40 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-280 CSDO 05/02/05 11:40 Enterococcus EPA 1600 RESULT None 700 20 NoR EH-280 CRW 05/02/05 11:40 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-280 CSDO 05/02/05 11:40 Fecal Coliform SM 9221E RESULT None 230 20 NoR EH-280 CRW 05/02/05 11:40 Total Coliform SM 9222B RESULT None 2 2 75 RR EH-280 CSDO 05/02/05 11:40 Total Coliform SM 9221B RESULT None 17000 20 NoR EH-290 CRW 05/02/05 11:30 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 05/02/05 11:30 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 05/02/05 11:30 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 05/02/05 11:30 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 05/02/05 11:30 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 05/02/05 11:30 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 05/02/05 11:15 Enterococcus EPA 1600 RESULT None 10 2 0 MR EH-300 CSDO 05/02/05 11:15 Enterococcus EPA 1600 RESULT None 60 20 NoR EH-300 CRW 05/02/05 11:15 Fecal Coliform SM 9222D RESULT < 2 2 0 MR EH-300 CSDO 05/02/05 11:15 Fecal Coliform SM 9221E RESULT None 20 20 NoR EH-300 CRW 05/02/05 11:15 Total Coliform SM 9222B RESULT None 32 2 0 MR EH-300 CSDO 05/02/05 11:15 Total Coliform SM 9221B RESULT None 1700 20 NoR EH-320 CRW 05/02/05 10:40 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 05/02/05 10:40 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 05/02/05 10:40 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 05/02/05 10:40 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 05/02/05 10:40 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 05/02/05 10:40 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 05/02/05 10:35 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 05/02/05 10:35 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 05/02/05 10:35 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 05/02/05 10:35 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 05/02/05 10:35 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 05/02/05 10:35 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 05/02/05 10:15 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-340 CSDO 05/02/05 10:15 Enterococcus EPA 1600 RESULT None 1800 20 NoSD04-05 DataPage 89 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-340 CRW 05/02/05 10:15 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-340 CSDO 05/02/05 10:15 Fecal Coliform SM 9221E RESULT None 1700 20 NoR EH-340 CRW 05/02/05 10:15 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-340 CSDO 05/02/05 10:15 Total Coliform SM 9221B RESULT None 50000 20 NoR FM-030 CRW 05/02/05 12:00 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 05/02/05 12:00 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 05/02/05 12:00 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 05/02/05 12:00 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 05/02/05 12:00 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 05/02/05 12:00 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 05/02/05 11:35 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 05/02/05 11:35 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 05/02/05 11:35 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 05/02/05 11:35 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 05/02/05 11:35 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 05/02/05 11:35 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 05/02/05 11:05 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-060 CSDO 05/02/05 11:05 Enterococcus EPA 1600 RESULT None 16000 20 YesR FM-060 CRW 05/02/05 11:05 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-060 CSDO 05/02/05 11:05 Fecal Coliform SM 9221E RESULT None 110 20 YesR FM-060 CRW 05/02/05 11:05 Total Coliform SM 9222B RESULT < 2 2 75 RR FM-060 CSDO 05/02/05 11:05 Total Coliform SM 9221B RESULT None 13000 20 YesR FM-080 CRW 05/02/05 10:45 Enterococcus EPA 1600 RESULT None 2 2 75 RR FM-080 CSDO 05/02/05 10:45 Enterococcus EPA 1600 RESULT None 1100 20 YesR FM-080 CRW 05/02/05 10:45 Fecal Coliform SM 9222D RESULT None 2 2 75 RR FM-080 CSDO 05/02/05 10:45 Fecal Coliform SM 9221E RESULT None 800 20 YesR FM-080 CRW 05/02/05 10:45 Total Coliform SM 9222B RESULT None 14 2 75 RR FM-080 CSDO 05/02/05 10:45 Total Coliform SM 9221B RESULT None 17000 20 YesR EH-250 CRW 05/17/05 12:19 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-250 CSDO 05/17/05 12:19 Enterococcus EPA 1600 RESULT None 2400 20 NoR EH-250 CRW 05/17/05 12:19 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-250 CSDO 05/17/05 12:19 Fecal Coliform SM 9221E RESULT None 1100 20 NoR EH-250 CRW 05/17/05 12:19 Total Coliform SM 9222B RESULT None 8 2 75 LR EH-250 CSDO 05/17/05 12:19 Total Coliform SM 9221B RESULT None 170000 20 NoR EH-255 CRW 05/17/05 11:58 Enterococcus EPA 1600 RESULT None 60 2 75 LR EH-255 CSDO 05/17/05 11:58 Enterococcus EPA 1600 RESULT None 2200 20 NoR EH-255 CRW 05/17/05 11:58 Fecal Coliform SM 9222D RESULT None 120 2 75 LSD04-05 DataPage 90 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-255 CSDO 05/17/05 11:58 Fecal Coliform SM 9221E RESULT None 500 20 NoR EH-255 CRW 05/17/05 11:58 Total Coliform SM 9222B RESULT None 540 2 75 LR EH-255 CSDO 05/17/05 11:58 Total Coliform SM 9221B RESULT None 5000 20 NoR EH-280 CRW 05/17/05 11:38 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-280 CSDO 05/17/05 11:38 Enterococcus EPA 1600 RESULT None 40 20 NoR EH-280 CRW 05/17/05 11:38 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-280 CSDO 05/17/05 11:38 Fecal Coliform SM 9221E RESULT None 20 20 NoR EH-280 CRW 05/17/05 11:38 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-280 CSDO 05/17/05 11:38 Total Coliform SM 9221B RESULT None 1700 20 NoR EH-290 CRW 05/17/05 11:22 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 05/17/05 11:22 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 05/17/05 11:22 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 05/17/05 11:22 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 05/17/05 11:22 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 05/17/05 11:22 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 05/17/05 11:10 Enterococcus EPA 1600 RESULT None 2 2 0 MR EH-300 CSDO 05/17/05 11:10 Enterococcus EPA 1600 RESULT None 3800 20 NoR EH-300 CRW 05/17/05 11:10 Fecal Coliform SM 9222D RESULT < 2 2 0 MR EH-300 CSDO 05/17/05 11:10 Fecal Coliform SM 9221E RESULT None 3000 20 NoR EH-300 CRW 05/17/05 11:10 Total Coliform SM 9222B RESULT None 16 2 0 MR EH-300 CSDO 05/17/05 11:10 Total Coliform SM 9221B RESULT None 13000 20 NoR EH-320 CRW 05/17/05 10:23 Enterococcus EPA 1600 RESULT None 6 2 75 RR EH-320 CSDO 05/17/05 10:23 Enterococcus EPA 1600 RESULT None 280 20 NoR EH-320 CRW 05/17/05 10:23 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-320 CSDO 05/17/05 10:23 Fecal Coliform SM 9221E RESULT None 700 20 NoR EH-320 CRW 05/17/05 10:23 Total Coliform SM 9222B RESULT None 2 2 75 RR EH-320 CSDO 05/17/05 10:23 Total Coliform SM 9221B RESULT None 700 20 NoR EH-330 CRW 05/17/05 10:15 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-330 CSDO 05/17/05 10:15 Enterococcus EPA 1600 RESULT None 1100 20 NoR EH-330 CRW 05/17/05 10:15 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-330 CSDO 05/17/05 10:15 Fecal Coliform SM 9221E RESULT None 300 20 NoR EH-330 CRW 05/17/05 10:15 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-330 CSDO 05/17/05 10:15 Total Coliform SM 9221B RESULT None 7000 20 NoR EH-340 CRW 05/17/05 10:03 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-340 CSDO 05/17/05 10:03 Enterococcus EPA 1600 RESULT None 32000 20 NoR EH-340 CRW 05/17/05 10:03 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-340 CSDO 05/17/05 10:03 Fecal Coliform SM 9221E RESULT None 5000 20 NoSD04-05 DataPage 91 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-340 CRW 05/17/05 10:03 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-340 CSDO 05/17/05 10:03 Total Coliform SM 9221B RESULT None 300000 20 NoR FM-030 CRW 05/17/05 11:48 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 05/17/05 11:48 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 05/17/05 11:48 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 05/17/05 11:48 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 05/17/05 11:48 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 05/17/05 11:48 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 05/17/05 11:35 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 05/17/05 11:35 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 05/17/05 11:35 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 05/17/05 11:35 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 05/17/05 11:35 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 05/17/05 11:35 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 05/17/05 11:01 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-060 CSDO 05/17/05 11:01 Enterococcus EPA 1600 RESULT None 4200 20 NoR FM-060 CRW 05/17/05 11:01 Fecal Coliform SM 9222D RESULT None 4 2 75 RR FM-060 CSDO 05/17/05 11:01 Fecal Coliform SM 9221E RESULT None 2300 20 NoR FM-060 CRW 05/17/05 11:01 Total Coliform SM 9222B RESULT < 2 2 75 RR FM-060 CSDO 05/17/05 11:01 Total Coliform SM 9221B RESULT None 5000 20 NoR FM-080 CRW 05/17/05 10:32 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-080 CSDO 05/17/05 10:32 Enterococcus EPA 1600 RESULT None 60 20 NoR FM-080 CRW 05/17/05 10:32 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-080 CSDO 05/17/05 10:32 Fecal Coliform SM 9221E RESULT None 300 20 NoR FM-080 CRW 05/17/05 10:32 Total Coliform SM 9222B RESULT < 2 2 75 RR FM-080 CSDO 05/17/05 10:32 Total Coliform SM 9221B RESULT None 22000 20 NoR EH-250 CRW 05/31/05 9:05 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-250 CSDO 05/31/05 9:05 Enterococcus EPA 1600 RESULT None 360 20 NoR EH-250 CRW 05/31/05 9:05 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-250 CSDO 05/31/05 9:05 Fecal Coliform SM 9221E RESULT None 170 20 NoR EH-250 CRW 05/31/05 9:05 Total Coliform SM 9222B RESULT None 4 2 75 LR EH-250 CSDO 05/31/05 9:05 Total Coliform SM 9221B RESULT None 5000 20 NoR EH-255 CRW 05/31/05 9:40 Enterococcus EPA 1600 RESULT None 20 2 75 LR EH-255 CSDO 05/31/05 9:40 Enterococcus EPA 1600 RESULT None 20000 20 YesR EH-255 CRW 05/31/05 9:40 Fecal Coliform SM 9222D RESULT None 8 2 75 LR EH-255 CSDO 05/31/05 9:40 Fecal Coliform SM 9221E RESULT None 900000 20 YesR EH-255 CRW 05/31/05 9:40 Total Coliform SM 9222B RESULT < 20 20 75 LSD04-05 DataPage 92 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-255 CSDO 05/31/05 9:40 Total Coliform SM 9221B RESULT None 900000 20 YesR EH-280 CRW 05/31/05 10:15 Enterococcus EPA 1600 RESULT None 8 2 75 LR EH-280 CSDO 05/31/05 10:15 Enterococcus EPA 1600 RESULT None 60 20 NoR EH-280 CRW 05/31/05 10:15 Fecal Coliform SM 9222D RESULT None 68 2 75 LR EH-280 CSDO 05/31/05 10:15 Fecal Coliform SM 9221E RESULT < 20 20 NoR EH-280 CRW 05/31/05 10:15 Total Coliform SM 9222B RESULT None 600 2 75 LR EH-280 CSDO 05/31/05 10:15 Total Coliform SM 9221B RESULT None 800 20 NoR EH-290 CRW 05/31/05 10:00 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 05/31/05 10:00 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 05/31/05 10:00 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 05/31/05 10:00 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 05/31/05 10:00 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 05/31/05 10:00 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 05/31/05 10:50 Enterococcus EPA 1600 RESULT < 2 2 0 MR EH-300 CSDO 05/31/05 10:50 Enterococcus EPA 1600 RESULT < 20 20 YesR EH-300 CRW 05/31/05 10:50 Fecal Coliform SM 9222D RESULT None 2 2 0 MR EH-300 CSDO 05/31/05 10:50 Fecal Coliform SM 9221E RESULT < 20 20 YesR EH-300 CRW 05/31/05 10:50 Total Coliform SM 9222B RESULT < 200 200 0 MR EH-300 CSDO 05/31/05 10:50 Total Coliform SM 9221B RESULT None 20 20 YesR EH-320 CRW 05/31/05 12:00 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 05/31/05 12:00 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 05/31/05 12:00 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 05/31/05 12:00 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 05/31/05 12:00 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 05/31/05 12:00 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 05/31/05 12:05 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-330 CSDO 05/31/05 12:05 Enterococcus EPA 1600 RESULT None 10000 20 NoR EH-330 CRW 05/31/05 12:05 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-330 CSDO 05/31/05 12:05 Fecal Coliform SM 9221E RESULT None 220000 20 NoR EH-330 CRW 05/31/05 12:05 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-330 CSDO 05/31/05 12:05 Total Coliform SM 9221B RESULT None 220000 20 NoR EH-340 CRW 05/31/05 12:30 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-340 CSDO 05/31/05 12:30 Enterococcus EPA 1600 RESULT None 4900 20 NoR EH-340 CRW 05/31/05 12:30 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-340 CSDO 05/31/05 12:30 Fecal Coliform SM 9221E RESULT None 2300 20 NoR EH-340 CRW 05/31/05 12:30 Total Coliform SM 9222B RESULT < 20 20 75 RR EH-340 CSDO 05/31/05 12:30 Total Coliform SM 9221B RESULT None 110000 20 NoSD04-05 DataPage 93 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-030 CRW 05/31/05 9:30 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 05/31/05 9:30 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 05/31/05 9:30 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 05/31/05 9:30 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 05/31/05 9:30 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 05/31/05 9:30 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 05/31/05 10:10 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 05/31/05 10:10 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 05/31/05 10:10 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 05/31/05 10:10 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 05/31/05 10:10 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 05/31/05 10:10 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 05/31/05 11:10 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-060 CSDO 05/31/05 11:10 Enterococcus EPA 1600 RESULT None 2900 20 NoR FM-060 CRW 05/31/05 11:10 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-060 CSDO 05/31/05 11:10 Fecal Coliform SM 9221E RESULT None 1700 20 NoR FM-060 CRW 05/31/05 11:10 Total Coliform SM 9222B RESULT < 2 2 75 RR FM-060 CSDO 05/31/05 11:10 Total Coliform SM 9221B RESULT None 13000 20 NoR FM-080 CRW 05/31/05 11:55 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-080 CSDO 05/31/05 11:55 Enterococcus EPA 1600 RESULT None 940 20 NoR FM-080 CRW 05/31/05 11:55 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-080 CSDO 05/31/05 11:55 Fecal Coliform SM 9221E RESULT None 2300 20 NoR FM-080 CRW 05/31/05 11:55 Total Coliform SM 9222B RESULT None 4 2 75 RR FM-080 CSDO 05/31/05 11:55 Total Coliform SM 9221B RESULT None 80000 20 NoR EH-250 CRW 06/13/05 13:15 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-250 CSDO 06/13/05 13:15 Enterococcus EPA 1600 RESULT None 640 20 NoR EH-250 CRW 06/13/05 13:15 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-250 CSDO 06/13/05 13:15 Fecal Coliform SM 9221E RESULT None 800 20 NoR EH-250 CRW 06/13/05 13:15 Total Coliform SM 9222B RESULT < 20 20 75 RR EH-250 CSDO 06/13/05 13:15 Total Coliform SM 9221B RESULT None 17000 20 NoR EH-255 CRW 06/13/05 12:30 Enterococcus EPA 1600 RESULT None 24 2 unknown unknownR EH-255 CSDO 06/13/05 12:30 Enterococcus EPA 1600 RESULT None 32000 20 NoR EH-255 CRW 06/13/05 12:30 Fecal Coliform SM 9222D RESULT None 440 2 unknown unknownR EH-255 CSDO 06/13/05 12:30 Fecal Coliform SM 9221E RESULT None 22000 20 NoR EH-255 CRW 06/13/05 12:30 Total Coliform SM 9222B RESULT None 1000 2 unknown unknownR EH-255 CSDO 06/13/05 12:30 Total Coliform SM 9221B RESULT None 240000 20 NoR EH-280 CRW 06/13/05 12:10 Enterococcus EPA 1600 RESULT None 4 2 unknown unknownSD04-05 DataPage 94 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-280 CSDO 06/13/05 12:10 Enterococcus EPA 1600 RESULT None 1200 20 NoR EH-280 CRW 06/13/05 12:10 Fecal Coliform SM 9222D RESULT < 2 2 unknown unknownR EH-280 CSDO 06/13/05 12:10 Fecal Coliform SM 9221E RESULT None 5000 20 NoR EH-280 CRW 06/13/05 12:10 Total Coliform SM 9222B RESULT None 80 2 unknown unknownR EH-280 CSDO 06/13/05 12:10 Total Coliform SM 9221B RESULT None 5000 20 NoR EH-290 CRW 06/13/05 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 06/13/05 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 06/13/05 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 06/13/05 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 06/13/05 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 06/13/05 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 06/13/05 11:30 Enterococcus EPA 1600 RESULT None 20 2 unknown unknownR EH-300 CSDO 06/13/05 11:30 Enterococcus EPA 1600 RESULT None 38000 20 unknown unknownR EH-300 CSDO 06/13/05 11:30 Fecal Coliform SM 9221E RESULT None 50000 20 NoR EH-300 CRW 06/13/05 11:30 Fecal Coliform SM 9222D RESULT None 4 2 NoR EH-300 CRW 06/13/05 11:30 Total Coliform SM 9222B RESULT None 1000 2 unknown unknownR EH-300 CSDO 06/13/05 11:30 Total Coliform SM 9221B RESULT None 70000 20 NoR EH-320 CRW 06/13/05 10:50 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 06/13/05 10:50 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 06/13/05 10:50 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 06/13/05 10:50 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 06/13/05 10:50 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 06/13/05 10:50 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 06/13/05 10:45 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 06/13/05 10:45 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 06/13/05 10:45 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 06/13/05 10:45 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 06/13/05 10:45 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 06/13/05 10:45 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 06/13/05 10:30 Enterococcus EPA 1600 RESULT None 32 2 75 RR EH-340 CSDO 06/13/05 10:30 Enterococcus EPA 1600 RESULT None 9800 20 NoR EH-340 CRW 06/13/05 10:30 Fecal Coliform SM 9222D RESULT None 4 2 75 RR EH-340 CSDO 06/13/05 10:30 Fecal Coliform SM 9221E RESULT None 3000 20 NoR EH-340 CRW 06/13/05 10:30 Total Coliform SM 9222B RESULT None 800 2 75 RR EH-340 CSDO 06/13/05 10:30 Total Coliform SM 9221B RESULT None 50000 20 NoR FM-030 CRW 06/13/05 12:45 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-030 CSDO 06/13/05 12:45 Enterococcus EPA 1600 RESULT None 10000 20 NoSD04-05 DataPage 95 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-030 CRW 06/13/05 12:45 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-030 CSDO 06/13/05 12:45 Fecal Coliform SM 9221E RESULT None 80000 20 NoR FM-030 CRW 06/13/05 12:45 Total Coliform SM 9222B RESULT < 20 20 75 RR FM-030 CSDO 06/13/05 12:45 Total Coliform SM 9221B RESULT None 130000 20 NoR FM-050 CRW 06/13/05 12:00 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 06/13/05 12:00 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 06/13/05 12:00 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 06/13/05 12:00 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 06/13/05 12:00 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 06/13/05 12:00 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 06/13/05 11:20 Enterococcus EPA 1600 RESULT None 2 2 0 MR FM-060 CSDO 06/13/05 11:20 Enterococcus EPA 1600 RESULT None 1600 20 NoR FM-060 CRW 06/13/05 11:20 Fecal Coliform SM 9222D RESULT None 6 2 0 MR FM-060 CSDO 06/13/05 11:20 Fecal Coliform SM 9221E RESULT None 3000 20 NoR FM-060 CRW 06/13/05 11:20 Total Coliform SM 9222B RESULT None 200 2 0 MR FM-060 CSDO 06/13/05 11:20 Total Coliform SM 9221B RESULT None 30000 20 NoR FM-080 CRW 06/13/05 11:05 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-080 CSDO 06/13/05 11:05 Enterococcus EPA 1600 RESULT None 1400 20 NoR FM-080 CRW 06/13/05 11:05 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-080 CSDO 06/13/05 11:05 Fecal Coliform SM 9221E RESULT None 3000 20 NoR FM-080 CRW 06/13/05 11:05 Total Coliform SM 9222B RESULT None 20 2 75 RR FM-080 CSDO 06/13/05 11:05 Total Coliform SM 9221B RESULT None 30000 20 NoR EH-250 CRW 06/27/05 11:00 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-250 CSDO 06/27/05 11:00 Enterococcus EPA 1600 RESULT None 440 20 NoR EH-250 CRW 06/27/05 11:00 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-250 CSDO 06/27/05 11:00 Fecal Coliform SM 9221E RESULT None 1300 20 NoR EH-250 CRW 06/27/05 11:00 Total Coliform SM 9222B RESULT None 4 2 75 RR EH-250 CSDO 06/27/05 11:00 Total Coliform SM 9221B RESULT None 2300 20 NoR EH-255 CRW 06/27/05 10:30 Enterococcus EPA 1600 RESULT None 6 2 75 RR EH-255 CSDO 06/27/05 10:30 Enterococcus EPA 1600 RESULT None 4800 20 NoR EH-255 CRW 06/27/05 10:30 Fecal Coliform SM 9222D RESULT None 84 2 75 RR EH-255 CSDO 06/27/05 10:30 Fecal Coliform SM 9221E RESULT None 800 20 NoR EH-255 CRW 06/27/05 10:30 Total Coliform SM 9222B RESULT None 160 2 75 RR EH-255 CSDO 06/27/05 10:30 Total Coliform SM 9221B RESULT None 80000 20 NoR EH-280 CRW 06/27/05 10:05 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-280 CSDO 06/27/05 10:05 Enterococcus EPA 1600 RESULT None 120 20 NoR EH-280 CRW 06/27/05 10:05 Fecal Coliform SM 9222D RESULT None 2 2 75 RSD04-05 DataPage 96 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-280 CSDO 06/27/05 10:05 Fecal Coliform SM 9221E RESULT None 110 20 NoR EH-280 CRW 06/27/05 10:05 Total Coliform SM 9222B RESULT None 6 2 75 RR EH-280 CSDO 06/27/05 10:05 Total Coliform SM 9221B RESULT None 700 20 NoR EH-290 CRW 06/27/05 9:40 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 06/27/05 9:40 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 06/27/05 9:40 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 06/27/05 9:40 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 06/27/05 9:40 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 06/27/05 9:40 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 06/27/05 9:15 Enterococcus EPA 1600 RESULT < 2 2 0 MR EH-300 CSDO 06/27/05 9:15 Enterococcus EPA 1600 RESULT None 60 20 NoR EH-300 CRW 06/27/05 9:15 Fecal Coliform SM 9222D RESULT < 2 2 0 MR EH-300 CSDO 06/27/05 9:15 Fecal Coliform SM 9221E RESULT None 80 20 NoR EH-300 CRW 06/27/05 9:15 Total Coliform SM 9222B RESULT < 2 2 0 MR EH-300 CSDO 06/27/05 9:15 Total Coliform SM 9221B RESULT None 7000 20 NoR EH-320 CRW 06/27/05 8:50 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 06/27/05 8:50 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 06/27/05 8:50 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 06/27/05 8:50 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 06/27/05 8:50 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 06/27/05 8:50 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 06/27/05 8:40 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 06/27/05 8:40 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 06/27/05 8:40 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 06/27/05 8:40 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 06/27/05 8:40 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 06/27/05 8:40 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 06/27/05 8:25 Enterococcus EPA 1600 RESULT NS -99 2R EH-340 CSDO 06/27/05 8:25 Enterococcus EPA 1600 RESULT NS -99 20R EH-340 CRW 06/27/05 8:25 Fecal Coliform SM 9222D RESULT NS -99 2R EH-340 CSDO 06/27/05 8:25 Fecal Coliform SM 9221E RESULT NS -99 20R EH-340 CRW 06/27/05 8:25 Total Coliform SM 9222B RESULT NS -99 2R EH-340 CSDO 06/27/05 8:25 Total Coliform SM 9221B RESULT NS -99 20R FM-030 CRW 06/27/05 10:40 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 06/27/05 10:40 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 06/27/05 10:40 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 06/27/05 10:40 Fecal Coliform SM 9221E RESULT NS -99 20SD04-05 DataPage 97 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-030 CRW 06/27/05 10:40 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 06/27/05 10:40 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 06/27/05 9:55 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 06/27/05 9:55 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 06/27/05 9:55 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 06/27/05 9:55 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 06/27/05 9:55 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 06/27/05 9:55 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 06/27/05 9:05 Enterococcus EPA 1600 RESULT < 2 2 0 MR FM-060 CSDO 06/27/05 9:05 Enterococcus EPA 1600 RESULT None 1600 20 YesR FM-060 CRW 06/27/05 9:05 Fecal Coliform SM 9222D RESULT < 2 2 0 MR FM-060 CSDO 06/27/05 9:05 Fecal Coliform SM 9221E RESULT None 800 20 YesR FM-060 CRW 06/27/05 9:05 Total Coliform SM 9222B RESULT < 2 2 0 MR FM-060 CSDO 06/27/05 9:05 Total Coliform SM 9221B RESULT None 2300 20 YesR FM-080 CRW 06/27/05 8:45 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 06/27/05 8:45 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 06/27/05 8:45 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 06/27/05 8:45 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 06/27/05 8:45 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 06/27/05 8:45 Total Coliform SM 9221B RESULT NS -99 20R EH-250 CRW 07/11/05 12:23 Enterococcus EPA 1600 RESULT None 2 2 75 RR EH-250 CSDO 07/11/05 12:23 Enterococcus EPA 1600 RESULT None 1000 20 NoR EH-250 CRW 07/11/05 12:23 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-250 CSDO 07/11/05 12:23 Fecal Coliform SM 9221E RESULT None 1300 20 NoR EH-250 CRW 07/11/05 12:23 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-250 CSDO 07/11/05 12:23 Total Coliform SM 9221B RESULT None 50000 20 NoR EH-255 CRW 07/11/05 11:55 Enterococcus EPA 1600 RESULT None 160 2 75 RR EH-255 CSDO 07/11/05 11:55 Enterococcus EPA 1600 RESULT None 7400 20 NoR EH-255 CRW 07/11/05 11:55 Fecal Coliform SM 9222D RESULT None 140 2 75 RR EH-255 CSDO 07/11/05 11:55 Fecal Coliform SM 9221E RESULT None 14000 20 NoR EH-255 CRW 07/11/05 11:55 Total Coliform SM 9222B RESULT None 600 2 75 RR EH-255 CSDO 07/11/05 11:55 Total Coliform SM 9221B RESULT None 50000 20 NoR EH-280 CRW 07/11/05 11:31 Enterococcus EPA 1600 RESULT None 4 2 75 RR EH-280 CSDO 07/11/05 11:31 Enterococcus EPA 1600 RESULT None 280 20 NoR EH-280 CRW 07/11/05 11:31 Fecal Coliform SM 9222D RESULT None 2 2 75 RR EH-280 CSDO 07/11/05 11:31 Fecal Coliform SM 9221E RESULT None 220 20 NoR EH-280 CRW 07/11/05 11:31 Total Coliform SM 9222B RESULT None 4 2 75 RSD04-05 DataPage 98 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-280 CSDO 07/11/05 11:31 Total Coliform SM 9221B RESULT None 2200 20 NoR EH-290 CRW 07/11/05 11:20 Enterococcus EPA 1600 RESULT None 56 2 0 MR EH-290 CSDO 07/11/05 11:20 Enterococcus EPA 1600 RESULT None 36000 20 YesR EH-290 CRW 07/11/05 11:20 Fecal Coliform SM 9222D RESULT < 20 20 0 MR EH-290 CSDO 07/11/05 11:20 Fecal Coliform SM 9221E RESULT None 8000 20 YesR EH-290 CRW 07/11/05 11:20 Total Coliform SM 9222B RESULT < 2 2 0 MR EH-290 CSDO 07/11/05 11:20 Total Coliform SM 9221B RESULT None 130000 20 YesR EH-300 CRW 07/11/05 11:08 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 07/11/05 11:08 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 07/11/05 11:08 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 07/11/05 11:08 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 07/11/05 11:08 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 07/11/05 11:08 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 07/11/05 10:42 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 07/11/05 10:42 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 07/11/05 10:42 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 07/11/05 10:42 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 07/11/05 10:42 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 07/11/05 10:42 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 07/11/05 10:38 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 07/11/05 10:38 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 07/11/05 10:38 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 07/11/05 10:38 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 07/11/05 10:38 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 07/11/05 10:38 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 07/11/05 10:25 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-340 CSDO 07/11/05 10:25 Enterococcus EPA 1600 RESULT None 32000 20 NoR EH-340 CRW 07/11/05 10:25 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-340 CSDO 07/11/05 10:25 Fecal Coliform SM 9221E RESULT None 11000 20 NoR EH-340 CRW 07/11/05 10:25 Total Coliform SM 9222B RESULT None 6 2 75 RR EH-340 CSDO 07/11/05 10:25 Total Coliform SM 9221B RESULT None 50000 20 NoR FM-030 CRW 07/11/05 12:07 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-030 CSDO 07/11/05 12:07 Enterococcus EPA 1600 RESULT None 3400 20 NoR FM-030 CRW 07/11/05 12:07 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-030 CSDO 07/11/05 12:07 Fecal Coliform SM 9221E RESULT None 1100 20 NoR FM-030 CRW 07/11/05 12:07 Total Coliform SM 9222B RESULT None 10 2 75 RR FM-030 CSDO 07/11/05 12:07 Total Coliform SM 9221B RESULT None 23000 20 NoSD04-05 DataPage 99 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-060 CRW 07/11/05 10:56 Enterococcus EPA 1600 RESULT None 4 2 0 MR FM-060 CSDO 07/11/05 10:56 Enterococcus EPA 1600 RESULT None 1100 20 NoR FM-060 CRW 07/11/05 10:56 Fecal Coliform SM 9222D RESULT None 2 2 0 MR FM-060 CSDO 07/11/05 10:56 Fecal Coliform SM 9221E RESULT None 140 20 NoR FM-060 CRW 07/11/05 10:56 Total Coliform SM 9222B RESULT None 140 2 0 MR FM-060 CSDO 07/11/05 10:56 Total Coliform SM 9221B RESULT None 500000 20 NoR FM-080 CRW 07/11/05 10:45 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 07/11/05 10:45 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 07/11/05 10:45 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 07/11/05 10:45 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 07/11/05 10:45 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 07/11/05 10:45 Total Coliform SM 9221B RESULT NS -99 20R EH-250 CRW 07/25/05 12:20 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-250 CSDO 07/25/05 12:20 Enterococcus EPA 1600 RESULT None 180 20 NoR EH-250 CRW 07/25/05 12:20 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-250 CSDO 07/25/05 12:20 Fecal Coliform SM 9221E RESULT None 70 20 NoR EH-250 CRW 07/25/05 12:20 Total Coliform SM 9222B RESULT None 100 2 75 RR EH-250 CSDO 07/25/05 12:20 Total Coliform SM 9221B RESULT None 3000 20 NoR EH-255 CRW 07/25/05 11:58 Enterococcus EPA 1600 RESULT None 42 2 75 LR EH-255 CSDO 07/25/05 11:58 Enterococcus EPA 1600 RESULT None 10000 20 NoR EH-255 CRW 07/25/05 11:58 Fecal Coliform SM 9222D RESULT None 52 2 75 LR EH-255 CSDO 07/25/05 11:58 Fecal Coliform SM 9221E RESULT None 11000 20 NoR EH-255 CRW 07/25/05 11:58 Total Coliform SM 9222B RESULT NS -99 2 75 LR EH-255 CSDO 07/25/05 11:58 Total Coliform SM 9221B RESULT None 220000 20 NoR EH-280 CRW 07/25/05 11:26 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-280 CSDO 07/25/05 11:26 Enterococcus EPA 1600 RESULT None 260 20 NoR EH-280 CRW 07/25/05 11:26 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-280 CSDO 07/25/05 11:26 Fecal Coliform SM 9221E RESULT None 80 20 NoR EH-280 CRW 07/25/05 11:26 Total Coliform SM 9222B RESULT None 4 2 75 RR EH-280 CSDO 07/25/05 11:26 Total Coliform SM 9221B RESULT None 800 20 NoR EH-290 CRW 07/25/05 11:15 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 07/25/05 11:15 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 07/25/05 11:15 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 07/25/05 11:15 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 07/25/05 11:15 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 07/25/05 11:15 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 07/25/05 11:06 Enterococcus EPA 1600 RESULT NS -99 2SD04-05 DataPage 100 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-300 CSDO 07/25/05 11:06 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 07/25/05 11:06 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 07/25/05 11:06 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 07/25/05 11:06 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 07/25/05 11:06 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 07/25/05 10:34 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 07/25/05 10:34 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 07/25/05 10:34 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 07/25/05 10:34 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 07/25/05 10:34 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 07/25/05 10:34 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 07/25/05 10:30 Enterococcus EPA 1600 RESULT NS -99 2R EH-330 CSDO 07/25/05 10:30 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 07/25/05 10:30 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 07/25/05 10:30 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 07/25/05 10:30 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 07/25/05 10:30 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 07/25/05 10:09 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-340 CSDO 07/25/05 10:09 Enterococcus EPA 1600 RESULT None 5400 20 NoR EH-340 CRW 07/25/05 10:09 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-340 CSDO 07/25/05 10:09 Fecal Coliform SM 9221E RESULT None 8000 20 NoR EH-340 CRW 07/25/05 10:09 Total Coliform SM 9222B RESULT < 20 20 75 LR EH-340 CSDO 07/25/05 10:09 Total Coliform SM 9221B RESULT None 80000 20 NoR FM-030 CRW 07/25/05 11:47 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 07/25/05 11:47 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 07/25/05 11:47 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 07/25/05 11:47 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 07/25/05 11:47 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 07/25/05 11:47 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 07/25/05 11:26 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 07/25/05 11:26 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 07/25/05 11:26 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 07/25/05 11:26 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 07/25/05 11:26 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 07/25/05 11:26 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 07/25/05 11:00 Enterococcus EPA 1600 RESULT None 24 2 75 RR FM-060 CSDO 07/25/05 11:00 Enterococcus EPA 1600 RESULT None 2200 20 NoSD04-05 DataPage 101 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-060 CRW 07/25/05 11:00 Fecal Coliform SM 9222D RESULT None 6 2 75 RR FM-060 CSDO 07/25/05 11:00 Fecal Coliform SM 9221E RESULT None 170 20 NoR FM-060 CRW 07/25/05 11:00 Total Coliform SM 9222B RESULT None 800 2 75 RR FM-060 CSDO 07/25/05 11:00 Total Coliform SM 9221B RESULT None 30000 20 NoR FM-080 CRW 07/25/05 10:35 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 07/25/05 10:35 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 07/25/05 10:35 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 07/25/05 10:35 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 07/25/05 10:35 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 07/25/05 10:35 Total Coliform SM 9221B RESULT NS -99 20R EH-250 CRW 08/09/05 12:33 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-250 CSDO 08/09/05 12:33 Enterococcus EPA 1600 RESULT None 440 20 NoR EH-250 CRW 08/09/05 12:33 Fecal Coliform SM 9222D RESULT < 20 20 75 RR EH-250 CSDO 08/09/05 12:33 Fecal Coliform SM 9221E RESULT None 2300 20 NoR EH-250 CRW 08/09/05 12:33 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-250 CSDO 08/09/05 12:33 Total Coliform SM 9221B RESULT None 17000 20 NoR EH-255 CRW 08/09/05 12:14 Enterococcus EPA 1600 RESULT None 46 2 75 LR EH-255 CSDO 08/09/05 12:14 Enterococcus EPA 1600 RESULT None 2600 20 YesR EH-255 CRW 08/09/05 12:14 Fecal Coliform SM 9222D RESULT None 160 2 75 LR EH-255 CSDO 08/09/05 12:14 Fecal Coliform SM 9221E RESULT None 2300 20 YesR EH-255 CRW 08/09/05 12:14 Total Coliform SM 9222B RESULT < 200 200 75 LR EH-255 CSDO 08/09/05 12:14 Total Coliform SM 9221B RESULT None 30000 20 YesR EH-280 CRW 08/09/05 11:55 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-280 CSDO 08/09/05 11:55 Enterococcus EPA 1600 RESULT None 800 20 NoR EH-280 CRW 08/09/05 11:55 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-280 CSDO 08/09/05 11:55 Fecal Coliform SM 9221E RESULT None 220 20 NoR EH-280 CRW 08/09/05 11:55 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-280 CSDO 08/09/05 11:55 Total Coliform SM 9221B RESULT None 800 20 NoR EH-290 CRW 08/09/05 11:45 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 08/09/05 11:45 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 08/09/05 11:45 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 08/09/05 11:45 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 08/09/05 11:45 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 08/09/05 11:45 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 08/09/05 11:33 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 08/09/05 11:33 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 08/09/05 11:33 Fecal Coliform SM 9222D RESULT NS -99 2SD04-05 DataPage 102 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-300 CSDO 08/09/05 11:33 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 08/09/05 11:33 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 08/09/05 11:33 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 08/09/05 9:48 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 08/09/05 9:48 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 08/09/05 9:48 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 08/09/05 9:48 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 08/09/05 9:48 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 08/09/05 9:48 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 08/09/05 9:56 Enterococcus EPA 1600 RESULT None 4 2 75 RR EH-330 CSDO 08/09/05 9:56 Enterococcus EPA 1600 RESULT None 46000 20 NoR EH-330 CRW 08/09/05 9:56 Fecal Coliform SM 9222D RESULT None 8 2 75 RR EH-330 CSDO 08/09/05 9:56 Fecal Coliform SM 9221E RESULT None 3000 20 NoR EH-330 CRW 08/09/05 9:56 Total Coliform SM 9222B RESULT < 200 200 75 RR EH-330 CSDO 08/09/05 9:56 Total Coliform SM 9221B RESULT None 500000 20 NoR EH-340 CRW 08/09/05 12:33 Enterococcus EPA 1600 RESULT None 6 2 75 RR EH-340 CSDO 08/09/05 12:33 Enterococcus EPA 1600 RESULT None 28000 20 NoR EH-340 CRW 08/09/05 12:33 Fecal Coliform SM 9222D RESULT None 4 2 75 RR EH-340 CSDO 08/09/05 12:33 Fecal Coliform SM 9221E RESULT None 11000 20 NoR EH-340 CRW 08/09/05 12:33 Total Coliform SM 9222B RESULT < 20 20 75 RR EH-340 CSDO 08/09/05 12:33 Total Coliform SM 9221B RESULT None 110000 20 NoR FM-030 CRW 08/09/05 12:10 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 08/09/05 12:10 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 08/09/05 12:10 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 08/09/05 12:10 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 08/09/05 12:10 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 08/09/05 12:10 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 08/09/05 11:50 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 08/09/05 11:50 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 08/09/05 11:50 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 08/09/05 11:50 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 08/09/05 11:50 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 08/09/05 11:50 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 08/09/05 11:25 Enterococcus EPA 1600 RESULT None 10 2 0 MR FM-060 CSDO 08/09/05 11:25 Enterococcus EPA 1600 RESULT None 1200 20 YesR FM-060 CRW 08/09/05 11:25 Fecal Coliform SM 9222D RESULT < 20 20 0 MR FM-060 CSDO 08/09/05 11:25 Fecal Coliform SM 9221E RESULT None 1100 20 YesSD04-05 DataPage 103 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-060 CRW 08/09/05 11:25 Total Coliform SM 9222B RESULT < 200 200 0 MR FM-060 CSDO 08/09/05 11:25 Total Coliform SM 9221B RESULT None 11000 20 YesR FM-080 CRW 08/09/05 9:45 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 08/09/05 9:45 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 08/09/05 9:45 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 08/09/05 9:45 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 08/09/05 9:45 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 08/09/05 9:45 Total Coliform SM 9221B RESULT NS -99 20R EH-250 CRW 08/22/05 12:10 Enterococcus EPA 1600 RESULT None 6 2 75 LR EH-250 CSDO 08/22/05 12:10 Enterococcus EPA 1600 RESULT None 120 20 NoR EH-250 CRW 08/22/05 12:10 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-250 CSDO 08/22/05 12:10 Fecal Coliform SM 9221E RESULT None 20 20 NoR EH-250 CRW 08/22/05 12:10 Total Coliform SM 9222B RESULT None 40 2 75 LR EH-250 CSDO 08/22/05 12:10 Total Coliform SM 9221B RESULT None 2300 20 NoR EH-255 CRW 08/22/05 11:48 Enterococcus EPA 1600 RESULT None 5600 2 0 MR EH-255 CSDO 08/22/05 11:48 Enterococcus EPA 1600 RESULT None 6000 20R EH-255 CRW 08/22/05 11:48 Fecal Coliform SM 9222D RESULT > 12000 2 0 MR EH-255 CSDO 08/22/05 11:48 Fecal Coliform SM 9221E RESULT None 2200 20R EH-255 CRW 08/22/05 11:48 Total Coliform SM 9222B RESULT > 16000 2 0 MR EH-255 CSDO 08/22/05 11:48 Total Coliform SM 9221B RESULT None 110000 20R EH-280 CRW 08/22/05 11:28 Enterococcus EPA 1600 RESULT < 2 2 0 MR EH-280 CSDO 08/22/05 11:28 Enterococcus EPA 1600 RESULT None 960 20 NoR EH-280 CRW 08/22/05 11:28 Fecal Coliform SM 9222D RESULT < 2 2 0 MR EH-280 CSDO 08/22/05 11:28 Fecal Coliform SM 9221E RESULT None 5000 20 NoR EH-280 CRW 08/22/05 11:28 Total Coliform SM 9222B RESULT < 20 20 0 MR EH-280 CSDO 08/22/05 11:28 Total Coliform SM 9221B RESULT None 8000 20 NoR EH-290 CRW 08/22/05 11:21 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 08/22/05 11:21 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 08/22/05 11:21 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 08/22/05 11:21 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 08/22/05 11:21 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 08/22/05 11:21 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 08/22/05 10:57 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 08/22/05 10:57 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 08/22/05 10:57 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 08/22/05 10:57 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 08/22/05 10:57 Total Coliform SM 9222B RESULT NS -99 2SD04-05 DataPage 104 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-300 CSDO 08/22/05 10:57 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 08/22/05 10:20 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 08/22/05 10:20 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 08/22/05 10:20 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 08/22/05 10:20 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 08/22/05 10:20 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 08/22/05 10:20 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 08/22/05 10:10 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-330 CSDO 08/22/05 10:10 Enterococcus EPA 1600 RESULT None 8600 20 YesR EH-330 CRW 08/22/05 10:10 Fecal Coliform SM 9222D RESULT None 4 2 75 RR EH-330 CSDO 08/22/05 10:10 Fecal Coliform SM 9221E RESULT None 300 20 YesR EH-330 CRW 08/22/05 10:10 Total Coliform SM 9222B RESULT < 20 20 75 RR EH-330 CSDO 08/22/05 10:10 Total Coliform SM 9221B RESULT None 14000 20 YesR EH-340 CRW 08/22/05 9:51 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-340 CSDO 08/22/05 9:51 Enterococcus EPA 1600 RESULT None 38000 20 NoR EH-340 CRW 08/22/05 9:51 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-340 CSDO 08/22/05 9:51 Fecal Coliform SM 9221E RESULT None 5000 20 NoR EH-340 CRW 08/22/05 9:51 Total Coliform SM 9222B RESULT < 20 20 75 LR EH-340 CSDO 08/22/05 9:51 Total Coliform SM 9221B RESULT None 170000 20 NoR FM-030 CRW 08/22/05 12:00 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 08/22/05 12:00 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 08/22/05 12:00 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 08/22/05 12:00 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 08/22/05 12:00 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 08/22/05 12:00 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 08/22/05 11:28 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 08/22/05 11:28 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 08/22/05 11:28 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 08/22/05 11:28 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 08/22/05 11:28 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 08/22/05 11:28 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 08/22/05 10:51 Enterococcus EPA 1600 RESULT None 10 2 0 MR FM-060 CSDO 08/22/05 10:51 Enterococcus EPA 1600 RESULT None 7200 20 unknownR FM-060 CRW 08/22/05 10:51 Fecal Coliform SM 9222D RESULT None 12 2 0 MR FM-060 CSDO 08/22/05 10:51 Fecal Coliform SM 9221E RESULT None 11000 20 unknownR FM-060 CRW 08/22/05 10:51 Total Coliform SM 9222B RESULT < 20 20 0 MR FM-060 CSDO 08/22/05 10:51 Total Coliform SM 9221B RESULT None 14000 20 unknownSD04-05 DataPage 105 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-080 CRW 08/22/05 10:28 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 08/22/05 10:28 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 08/22/05 10:28 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 08/22/05 10:28 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 08/22/05 10:28 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 08/22/05 10:28 Total Coliform SM 9221B RESULT NS -99 20R EH-250 CRW 09/06/05 11:40 Enterococcus EPA 1600 RESULT None 24 2 75 RR EH-250 CSDO 09/06/05 11:40 Enterococcus EPA 1600 RESULT None 1600 20 NoR EH-250 CRW 09/06/05 11:40 Fecal Coliform SM 9222D RESULT None 26 2 75 RR EH-250 CSDO 09/06/05 11:40 Fecal Coliform SM 9221E RESULT None 40 20 NoR EH-250 CRW 09/06/05 11:40 Total Coliform SM 9222B RESULT None 46 2 75 RR EH-250 CSDO 09/06/05 11:40 Total Coliform SM 9221B RESULT None 2800 20 NoR EH-255 CRW 09/06/05 11:00 Enterococcus EPA 1600 RESULT None 4 2 75 LR EH-255 CSDO 09/06/05 11:00 Enterococcus EPA 1600 RESULT None 18000 20 YesR EH-255 CRW 09/06/05 11:00 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-255 CSDO 09/06/05 11:00 Fecal Coliform SM 9221E RESULT None 7000 20 YesR EH-255 CRW 09/06/05 11:00 Total Coliform SM 9222B RESULT None 20 2 75 LR EH-255 CSDO 09/06/05 11:00 Total Coliform SM 9221B RESULT None 80000 20 YesR EH-280 CRW 09/06/05 10:40 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-280 CSDO 09/06/05 10:40 Enterococcus EPA 1600 RESULT None 60 20 NoR EH-280 CRW 09/06/05 10:40 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-280 CSDO 09/06/05 10:40 Fecal Coliform SM 9221E RESULT < 20 20 NoR EH-280 CRW 09/06/05 10:40 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-280 CSDO 09/06/05 10:40 Total Coliform SM 9221B RESULT None 20 20 NoR EH-290 CRW 09/06/05 10:30 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 09/06/05 10:30 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 09/06/05 10:30 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 09/06/05 10:30 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 09/06/05 10:30 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 09/06/05 10:30 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 09/06/05 10:15 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 09/06/05 10:15 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 09/06/05 10:15 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 09/06/05 10:15 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 09/06/05 10:15 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 09/06/05 10:15 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 09/06/05 9:48 Enterococcus EPA 1600 RESULT NS -99 2SD04-05 DataPage 106 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-320 CSDO 09/06/05 9:48 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 09/06/05 9:48 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 09/06/05 9:48 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 09/06/05 9:48 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 09/06/05 9:48 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 09/06/05 9:35 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-330 CSDO 09/06/05 9:35 Enterococcus EPA 1600 RESULT None 2800 20 NoR EH-330 CRW 09/06/05 9:35 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-330 CSDO 09/06/05 9:35 Fecal Coliform SM 9221E RESULT None 500 20 NoR EH-330 CRW 09/06/05 9:35 Total Coliform SM 9222B RESULT < 20 20 75 RR EH-330 CSDO 09/06/05 9:35 Total Coliform SM 9221B RESULT None 17000 20 NoR EH-340 CRW 09/06/05 9:20 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-340 CSDO 09/06/05 9:20 Enterococcus EPA 1600 RESULT > 120000 20 NoR EH-340 CRW 09/06/05 9:20 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-340 CSDO 09/06/05 9:20 Fecal Coliform SM 9221E RESULT > 1600000 20 NoR EH-340 CRW 09/06/05 9:20 Total Coliform SM 9222B RESULT < 20 20 75 LR EH-340 CSDO 09/06/05 9:20 Total Coliform SM 9221B RESULT > 1600000 20 NoR FM-030 CRW 09/06/05 10:57 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 09/06/05 10:57 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 09/06/05 10:57 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 09/06/05 10:57 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 09/06/05 10:57 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 09/06/05 10:57 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 09/06/05 10:35 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 09/06/05 10:35 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 09/06/05 10:35 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 09/06/05 10:35 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 09/06/05 10:35 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 09/06/05 10:35 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 09/06/05 10:05 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-060 CSDO 09/06/05 10:05 Enterococcus EPA 1600 RESULT None 2000 20 YesR FM-060 CRW 09/06/05 10:05 Fecal Coliform SM 9222D RESULT None 2 2 75 RR FM-060 CSDO 09/06/05 10:05 Fecal Coliform SM 9221E RESULT None 800 20 YesR FM-060 CRW 09/06/05 10:05 Total Coliform SM 9222B RESULT None 20 2 75 RR FM-060 CSDO 09/06/05 10:05 Total Coliform SM 9221B RESULT None 13000 20 YesR FM-080 CRW 09/06/05 9:50 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 09/06/05 9:50 Enterococcus EPA 1600 RESULT NS -99 20SD04-05 DataPage 107 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-080 CRW 09/06/05 9:50 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 09/06/05 9:50 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 09/06/05 9:50 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 09/06/05 9:50 Total Coliform SM 9221B RESULT NS -99 20R EH-250 CRW 09/19/05 12:19 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-250 CSDO 09/19/05 12:19 Enterococcus EPA 1600 RESULT None 940 20 YesR EH-250 CRW 09/19/05 12:19 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-250 CSDO 09/19/05 12:19 Fecal Coliform SM 9221E RESULT None 300 20 YesR EH-250 CRW 09/19/05 12:19 Total Coliform SM 9222B RESULT < 20 20 75 RR EH-250 CSDO 09/19/05 12:19 Total Coliform SM 9221B RESULT None 7000 20 YesR EH-255 CRW 09/19/05 12:00 Enterococcus EPA 1600 RESULT None 26 2 75 LR EH-255 CSDO 09/19/05 12:00 Enterococcus EPA 1600 RESULT None 4000 20 NoR EH-255 CRW 09/19/05 12:00 Fecal Coliform SM 9222D RESULT None 110 2 75 LR EH-255 CSDO 09/19/05 12:00 Fecal Coliform SM 9221E RESULT None 1300 20 NoR EH-255 CRW 09/19/05 12:00 Total Coliform SM 9222B RESULT None 400 2 75 LR EH-255 CSDO 09/19/05 12:00 Total Coliform SM 9221B RESULT None 30000 20 NoR EH-280 CRW 09/19/05 11:34 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-280 CSDO 09/19/05 11:34 Enterococcus EPA 1600 RESULT None 20 20 NoR EH-280 CRW 09/19/05 11:34 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-280 CSDO 09/19/05 11:34 Fecal Coliform SM 9221E RESULT None 170 20 NoR EH-280 CRW 09/19/05 11:34 Total Coliform SM 9222B RESULT None 2 2 75 RR EH-280 CSDO 09/19/05 11:34 Total Coliform SM 9221B RESULT None 2300 20 NoR EH-290 CRW 09/19/05 11:25 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 09/19/05 11:25 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 09/19/05 11:25 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 09/19/05 11:25 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 09/19/05 11:25 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 09/19/05 11:25 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 09/19/05 11:15 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 09/19/05 11:15 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 09/19/05 11:15 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 09/19/05 11:15 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 09/19/05 11:15 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 09/19/05 11:15 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 09/19/05 10:46 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 09/19/05 10:46 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 09/19/05 10:46 Fecal Coliform SM 9222D RESULT NS -99 2SD04-05 DataPage 108 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-320 CSDO 09/19/05 10:46 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 09/19/05 10:46 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 09/19/05 10:46 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 09/19/05 10:35 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-330 CSDO 09/19/05 10:35 Enterococcus EPA 1600 RESULT None 4600 20 NoR EH-330 CRW 09/19/05 10:35 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-330 CSDO 09/19/05 10:35 Fecal Coliform SM 9221E RESULT None 300 20 NoR EH-330 CRW 09/19/05 10:35 Total Coliform SM 9222B RESULT None 6 2 75 LR EH-330 CSDO 09/19/05 10:35 Total Coliform SM 9221B RESULT None 8000 20 NoR EH-340 CRW 09/19/05 10:20 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-340 CSDO 09/19/05 10:20 Enterococcus EPA 1600 RESULT None 3800 20 NoR EH-340 CRW 09/19/05 10:20 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-340 CSDO 09/19/05 10:20 Fecal Coliform SM 9221E RESULT None 800 20 NoR EH-340 CRW 09/19/05 10:20 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-340 CSDO 09/19/05 10:20 Total Coliform SM 9221B RESULT None 50000 20 NoR FM-030 CRW 09/19/05 11:50 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 09/19/05 11:50 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 09/19/05 11:50 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 09/19/05 11:50 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 09/19/05 11:50 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 09/19/05 11:50 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 09/19/05 11:31 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 09/19/05 11:31 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 09/19/05 11:31 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 09/19/05 11:31 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 09/19/05 11:31 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 09/19/05 11:31 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 09/19/05 11:05 Enterococcus EPA 1600 RESULT None 4 2 75 RR FM-060 CSDO 09/19/05 11:05 Enterococcus EPA 1600 RESULT None 2400 20 YesR FM-060 CRW 09/19/05 11:05 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-060 CSDO 09/19/05 11:05 Fecal Coliform SM 9221E RESULT None 800 20 YesR FM-060 CRW 09/19/05 11:05 Total Coliform SM 9222B RESULT None 2 2 75 RR FM-060 CSDO 09/19/05 11:05 Total Coliform SM 9221B RESULT None 5000 20 YesR FM-080 CRW 09/19/05 10:48 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 09/19/05 10:48 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 09/19/05 10:48 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 09/19/05 10:48 Fecal Coliform SM 9221E RESULT NS -99 20SD04-05 DataPage 109 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR FM-080 CRW 09/19/05 10:48 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 09/19/05 10:48 Total Coliform SM 9221B RESULT NS -99 20R EH-250 CRW 10/03/05 12:47 Enterococcus EPA 1600 RESULT None 8 2 75 LR EH-250 CSDO 10/03/05 12:47 Enterococcus EPA 1600 RESULT None 300 20 NoR EH-250 CRW 10/03/05 12:47 Fecal Coliform SM 9222D RESULT None 2 2 75 LR EH-250 CSDO 10/03/05 12:47 Fecal Coliform SM 9221E RESULT None 110 20 NoR EH-250 CRW 10/03/05 12:47 Total Coliform SM 9222B RESULT < 20 20 75 LR EH-250 CSDO 10/03/05 12:47 Total Coliform SM 9221B RESULT None 3000 20 NoR EH-255 CRW 10/03/05 12:29 Enterococcus EPA 1600 RESULT None 4 2 75 LR EH-255 CSDO 10/03/05 12:29 Enterococcus EPA 1600 RESULT None 6400 20 YesR EH-255 CRW 10/03/05 12:29 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-255 CSDO 10/03/05 12:29 Fecal Coliform SM 9221E RESULT None 8000 20 YesR EH-255 CRW 10/03/05 12:29 Total Coliform SM 9222B RESULT None 20 2 75 LR EH-255 CSDO 10/03/05 12:29 Total Coliform SM 9221B RESULT None 50000 20 YesR EH-280 CRW 10/03/05 12:06 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-280 CSDO 10/03/05 12:06 Enterococcus EPA 1600 RESULT None 50000 20 NoR EH-280 CRW 10/03/05 12:06 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-280 CSDO 10/03/05 12:06 Fecal Coliform SM 9221E RESULT None 8000 20 NoR EH-280 CRW 10/03/05 12:06 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-280 CSDO 10/03/05 12:06 Total Coliform SM 9221B RESULT None 50000 20 NoR EH-290 CRW 10/03/05 11:59 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 10/03/05 11:59 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 10/03/05 11:59 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 10/03/05 11:59 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 10/03/05 11:59 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 10/03/05 11:59 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 10/03/05 11:38 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 10/03/05 11:38 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 10/03/05 11:38 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 10/03/05 11:38 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 10/03/05 11:38 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 10/03/05 11:38 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 10/03/05 11:09 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 10/03/05 11:09 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 10/03/05 11:09 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 10/03/05 11:09 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 10/03/05 11:09 Total Coliform SM 9222B RESULT NS -99 2SD04-05 DataPage 110 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-320 CSDO 10/03/05 11:09 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 10/03/05 10:55 Enterococcus EPA 1600 RESULT None 34 2 75 LR EH-330 CSDO 10/03/05 10:55 Enterococcus EPA 1600 RESULT None 1800 20 NoR EH-330 CRW 10/03/05 10:55 Fecal Coliform SM 9222D RESULT None 28 2 75 LR EH-330 CSDO 10/03/05 10:55 Fecal Coliform SM 9221E RESULT None 500 20 NoR EH-330 CRW 10/03/05 10:55 Total Coliform SM 9222B RESULT None 200 2 75 LR EH-330 CSDO 10/03/05 10:55 Total Coliform SM 9221B RESULT None 11000 20 NoR EH-340 CRW 10/03/05 10:37 Enterococcus EPA 1600 RESULT None 42 2 75 RR EH-340 CSDO 10/03/05 10:37 Enterococcus EPA 1600 RESULT None 4600 20 NoR EH-340 CRW 10/03/05 10:37 Fecal Coliform SM 9222D RESULT None 22 2 75 RR EH-340 CSDO 10/03/05 10:37 Fecal Coliform SM 9221E RESULT None 5000 20 NoR EH-340 CRW 10/03/05 10:37 Total Coliform SM 9222B RESULT None 200 2 75 RR EH-340 CSDO 10/03/05 10:37 Total Coliform SM 9221B RESULT None 50000 20 NoR FM-030 CRW 10/03/05 12:25 Enterococcus EPA 1600 RESULT NS -99 2R FM-030 CSDO 10/03/05 12:25 Enterococcus EPA 1600 RESULT NS -99 20R FM-030 CRW 10/03/05 12:25 Fecal Coliform SM 9222D RESULT NS -99 2R FM-030 CSDO 10/03/05 12:25 Fecal Coliform SM 9221E RESULT NS -99 20R FM-030 CRW 10/03/05 12:25 Total Coliform SM 9222B RESULT NS -99 2R FM-030 CSDO 10/03/05 12:25 Total Coliform SM 9221B RESULT NS -99 20R FM-050 CRW 10/03/05 12:02 Enterococcus EPA 1600 RESULT < 2 2 75 LR FM-050 CSDO 10/03/05 12:02 Enterococcus EPA 1600 RESULT None 740 20 NoR FM-050 CRW 10/03/05 12:02 Fecal Coliform SM 9222D RESULT None 2 2 75 LR FM-050 CSDO 10/03/05 12:02 Fecal Coliform SM 9221E RESULT None 130 20 NoR FM-050 CRW 10/03/05 12:02 Total Coliform SM 9222B RESULT < 2 2 75 LR FM-050 CSDO 10/03/05 12:02 Total Coliform SM 9221B RESULT None 3000 20 NoR FM-060 CRW 10/03/05 11:33 Enterococcus EPA 1600 RESULT < 2 2 75 RR FM-060 CSDO 10/03/05 11:33 Enterococcus EPA 1600 RESULT None 4800 20 YesR FM-060 CRW 10/03/05 11:33 Fecal Coliform SM 9222D RESULT None 6 2 75 RR FM-060 CSDO 10/03/05 11:33 Fecal Coliform SM 9221E RESULT None 80 20 YesR FM-060 CRW 10/03/05 11:33 Total Coliform SM 9222B RESULT < 200 200 75 RR FM-060 CSDO 10/03/05 11:33 Total Coliform SM 9221B RESULT None 22000 20 YesR FM-080 CRW 10/03/05 11:15 Enterococcus EPA 1600 RESULT NS -99 2R FM-080 CSDO 10/03/05 11:15 Enterococcus EPA 1600 RESULT NS -99 20R FM-080 CRW 10/03/05 11:15 Fecal Coliform SM 9222D RESULT NS -99 2R FM-080 CSDO 10/03/05 11:15 Fecal Coliform SM 9221E RESULT NS -99 20R FM-080 CRW 10/03/05 11:15 Total Coliform SM 9222B RESULT NS -99 2R FM-080 CSDO 10/03/05 11:15 Total Coliform SM 9221B RESULT NS -99 20SD04-05 DataPage 111 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-250 CRW 10/17/05 8:45 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-250 CSDO 10/17/05 8:45 Enterococcus EPA 1600 RESULT None 3400 20 YesR EH-250 CRW 10/17/05 8:45 Fecal Coliform SM 9222D RESULT None 4 2 75 LR EH-250 CSDO 10/17/05 8:45 Fecal Coliform SM 9221E RESULT None 700 20 YesR EH-250 CRW 10/17/05 8:45 Total Coliform SM 9222B RESULT < 20 20 75 LR EH-250 CSDO 10/17/05 8:45 Total Coliform SM 9221B RESULT None 5000 20 YesR EH-255 CRW 10/17/05 9:21 Enterococcus EPA 1600 RESULT None 540 2 75 LR EH-255 CSDO 10/17/05 9:21 Enterococcus EPA 1600 RESULT None 12000 20 YesR EH-255 CRW 10/17/05 9:21 Fecal Coliform SM 9222D RESULT None 20 2 75 LR EH-255 CSDO 10/17/05 9:21 Fecal Coliform SM 9221E RESULT None 5000 20 YesR EH-255 CRW 10/17/05 9:21 Total Coliform SM 9222B RESULT ND -99 2 75 LR EH-255 CSDO 10/17/05 9:21 Total Coliform SM 9221B RESULT None 70000 20 YesR EH-280 CRW 10/17/05 9:44 Enterococcus EPA 1600 RESULT None 44 2 75 LR EH-280 CSDO 10/17/05 9:44 Enterococcus EPA 1600 RESULT None 100 20 YesR EH-280 CRW 10/17/05 9:44 Fecal Coliform SM 9222D RESULT None 80 2 75 LR EH-280 CSDO 10/17/05 9:44 Fecal Coliform SM 9221E RESULT None 20 20 YesR EH-280 CRW 10/17/05 9:44 Total Coliform SM 9222B RESULT < 200 200 75 LR EH-280 CSDO 10/17/05 9:44 Total Coliform SM 9221B RESULT None 80 20 YesR EH-290 CRW 10/17/05 9:57 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 10/17/05 9:57 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 10/17/05 9:57 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 10/17/05 9:57 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 10/17/05 9:57 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 10/17/05 9:57 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 10/17/05 10:14 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 10/17/05 10:14 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 10/17/05 10:14 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 10/17/05 10:14 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 10/17/05 10:14 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 10/17/05 10:14 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 10/17/05 10:39 Enterococcus EPA 1600 RESULT NS -99 2R EH-320 CSDO 10/17/05 10:39 Enterococcus EPA 1600 RESULT NS -99 20R EH-320 CRW 10/17/05 10:39 Fecal Coliform SM 9222D RESULT NS -99 2R EH-320 CSDO 10/17/05 10:39 Fecal Coliform SM 9221E RESULT NS -99 20R EH-320 CRW 10/17/05 10:39 Total Coliform SM 9222B RESULT NS -99 2R EH-320 CSDO 10/17/05 10:39 Total Coliform SM 9221B RESULT NS -99 20R EH-330 CRW 10/17/05 10:43 Enterococcus EPA 1600 RESULT NS -99 2SD04-05 DataPage 112 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-330 CSDO 10/17/05 10:43 Enterococcus EPA 1600 RESULT NS -99 20R EH-330 CRW 10/17/05 10:43 Fecal Coliform SM 9222D RESULT NS -99 2R EH-330 CSDO 10/17/05 10:43 Fecal Coliform SM 9221E RESULT NS -99 20R EH-330 CRW 10/17/05 10:43 Total Coliform SM 9222B RESULT NS -99 2R EH-330 CSDO 10/17/05 10:43 Total Coliform SM 9221B RESULT NS -99 20R EH-340 CRW 10/17/05 10:53 Enterococcus EPA 1600 RESULT None 16 2 75 LR EH-340 CSDO 10/17/05 10:53 Enterococcus EPA 1600 RESULT None 4000 20 YesR EH-340 CRW 10/17/05 10:53 Fecal Coliform SM 9222D RESULT None 4 2 75 LR EH-340 CSDO 10/17/05 10:53 Fecal Coliform SM 9221E RESULT None 3600 20 YesR EH-340 CRW 10/17/05 10:53 Total Coliform SM 9222B RESULT None 20 2 75 LR EH-340 CSDO 10/17/05 10:53 Total Coliform SM 9221B RESULT None 170000 20 YesR FM-030 CRW 10/17/05 9:05 Enterococcus EPA 1600 RESULT None 94 2 75 LR FM-030 CSDO 10/17/05 9:05 Enterococcus EPA 1600 RESULT None 9200 20 NoR FM-030 CRW 10/17/05 9:05 Fecal Coliform SM 9222D RESULT < 20 20 75 LR FM-030 CSDO 10/17/05 9:05 Fecal Coliform SM 9221E RESULT None 1300 20 NoR FM-030 CRW 10/17/05 9:05 Total Coliform SM 9222B RESULT None 600 2 75 LR FM-030 CSDO 10/17/05 9:05 Total Coliform SM 9221B RESULT None 240000 20 NoR FM-050 CRW 10/17/05 9:42 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 10/17/05 9:42 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 10/17/05 9:42 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 10/17/05 9:42 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 10/17/05 9:42 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 10/17/05 9:42 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 10/17/05 10:11 Enterococcus EPA 1600 RESULT NS -99 2R FM-060 CSDO 10/17/05 10:11 Enterococcus EPA 1600 RESULT NS -99 20R FM-060 CRW 10/17/05 10:11 Fecal Coliform SM 9222D RESULT NS -99 2R FM-060 CSDO 10/17/05 10:11 Fecal Coliform SM 9221E RESULT NS -99 20R FM-060 CRW 10/17/05 10:11 Total Coliform SM 9222B RESULT NS -99 2R FM-060 CSDO 10/17/05 10:11 Total Coliform SM 9221B RESULT NS -99 20R FM-080 CRW 10/17/05 10:31 Enterococcus EPA 1600 RESULT None 14 2 75 RR FM-080 CSDO 10/17/05 10:31 Enterococcus EPA 1600 RESULT None 1400 20 YesR FM-080 CRW 10/17/05 10:31 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-080 CSDO 10/17/05 10:31 Fecal Coliform SM 9221E RESULT None 50000 20 YesR FM-080 CRW 10/17/05 10:31 Total Coliform SM 9222B RESULT None 28 2 75 RR FM-080 CSDO 10/17/05 10:31 Total Coliform SM 9221B RESULT None 130000 20 YesR EH-250 CRW 10/31/05 12:41 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-250 CSDO 10/31/05 12:41 Enterococcus EPA 1600 RESULT None 44000 20 NoSD04-05 DataPage 113 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-250 CRW 10/31/05 12:41 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-250 CSDO 10/31/05 12:41 Fecal Coliform SM 9221E RESULT None 17000 20 NoR EH-250 CRW 10/31/05 12:41 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-250 CSDO 10/31/05 12:41 Total Coliform SM 9221B RESULT None 17000 20 NoR EH-255 CRW 10/31/05 12:18 Enterococcus EPA 1600 RESULT None 2 2 75 LR EH-255 CSDO 10/31/05 12:18 Enterococcus EPA 1600 RESULT None 1000 20 YesR EH-255 CRW 10/31/05 12:18 Fecal Coliform SM 9222D RESULT None 4 2 75 LR EH-255 CSDO 10/31/05 12:18 Fecal Coliform SM 9221E RESULT None 600 20 YesR EH-255 CRW 10/31/05 12:18 Total Coliform SM 9222B RESULT < 2 2 75 LR EH-255 CSDO 10/31/05 12:18 Total Coliform SM 9221B RESULT None 30000 20 YesR EH-280 CRW 10/31/05 11:46 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-280 CSDO 10/31/05 11:46 Enterococcus EPA 1600 RESULT None 20 20 NoR EH-280 CRW 10/31/05 11:46 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-280 CSDO 10/31/05 11:46 Fecal Coliform SM 9221E RESULT < 20 20 NoR EH-280 CRW 10/31/05 11:46 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-280 CSDO 10/31/05 11:46 Total Coliform SM 9221B RESULT None 220 20 NoR EH-290 CRW 10/31/05 9:57 Enterococcus EPA 1600 RESULT NS -99 2R EH-290 CSDO 10/31/05 9:57 Enterococcus EPA 1600 RESULT NS -99 20R EH-290 CRW 10/31/05 9:57 Fecal Coliform SM 9222D RESULT NS -99 2R EH-290 CSDO 10/31/05 9:57 Fecal Coliform SM 9221E RESULT NS -99 20R EH-290 CRW 10/31/05 9:57 Total Coliform SM 9222B RESULT NS -99 2R EH-290 CSDO 10/31/05 9:57 Total Coliform SM 9221B RESULT NS -99 20R EH-300 CRW 10/31/05 10:14 Enterococcus EPA 1600 RESULT NS -99 2R EH-300 CSDO 10/31/05 10:14 Enterococcus EPA 1600 RESULT NS -99 20R EH-300 CRW 10/31/05 10:14 Fecal Coliform SM 9222D RESULT NS -99 2R EH-300 CSDO 10/31/05 10:14 Fecal Coliform SM 9221E RESULT NS -99 20R EH-300 CRW 10/31/05 10:14 Total Coliform SM 9222B RESULT NS -99 2R EH-300 CSDO 10/31/05 10:14 Total Coliform SM 9221B RESULT NS -99 20R EH-320 CRW 10/31/05 10:32 Enterococcus EPA 1600 RESULT < 2 2 75 RR EH-320 CSDO 10/31/05 10:32 Enterococcus EPA 1600 RESULT None 360 20 YesR EH-320 CRW 10/31/05 10:32 Fecal Coliform SM 9222D RESULT < 2 2 75 RR EH-320 CSDO 10/31/05 10:32 Fecal Coliform SM 9221E RESULT < 20 20 YesR EH-320 CRW 10/31/05 10:32 Total Coliform SM 9222B RESULT None 14 2 75 RR EH-320 CSDO 10/31/05 10:32 Total Coliform SM 9221B RESULT None 1400 20 YesR EH-330 CRW 10/31/05 10:18 Enterococcus EPA 1600 RESULT None 2 2 75 RR EH-330 CSDO 10/31/05 10:18 Enterococcus EPA 1600 RESULT None 600 20 NoR EH-330 CRW 10/31/05 10:18 Fecal Coliform SM 9222D RESULT < 2 2 75 RSD04-05 DataPage 114 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Coastal DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR EH-330 CSDO 10/31/05 10:18 Fecal Coliform SM 9221E RESULT None 170 20 NoR EH-330 CRW 10/31/05 10:18 Total Coliform SM 9222B RESULT < 2 2 75 RR EH-330 CSDO 10/31/05 10:18 Total Coliform SM 9221B RESULT None 110000 20 NoR EH-340 CRW 10/31/05 10:01 Enterococcus EPA 1600 RESULT < 2 2 75 LR EH-340 CSDO 10/31/05 10:01 Enterococcus EPA 1600 RESULT None 2000 20 NoR EH-340 CRW 10/31/05 10:01 Fecal Coliform SM 9222D RESULT < 2 2 75 LR EH-340 CSDO 10/31/05 10:01 Fecal Coliform SM 9221E RESULT None 80000 20 NoR EH-340 CRW 10/31/05 10:01 Total Coliform SM 9222B RESULT None 2 2 75 LR EH-340 CSDO 10/31/05 10:01 Total Coliform SM 9221B RESULT None 170000 20 NoR FM-030 CRW 10/31/05 12:08 Enterococcus EPA 1600 RESULT < 2 2 75 LR FM-030 CSDO 10/31/05 12:08 Enterococcus EPA 1600 RESULT None 2000 20 NoR FM-030 CRW 10/31/05 12:08 Fecal Coliform SM 9222D RESULT < 2 2 75 LR FM-030 CSDO 10/31/05 12:08 Fecal Coliform SM 9221E RESULT None 800 20 NoR FM-030 CRW 10/31/05 12:08 Total Coliform SM 9222B RESULT None 6 2 75 LR FM-030 CSDO 10/31/05 12:08 Total Coliform SM 9221B RESULT None 13000 20 NoR FM-050 CRW 10/31/05 9:42 Enterococcus EPA 1600 RESULT NS -99 2R FM-050 CSDO 10/31/05 9:42 Enterococcus EPA 1600 RESULT NS -99 20R FM-050 CRW 10/31/05 9:42 Fecal Coliform SM 9222D RESULT NS -99 2R FM-050 CSDO 10/31/05 9:42 Fecal Coliform SM 9221E RESULT NS -99 20R FM-050 CRW 10/31/05 9:42 Total Coliform SM 9222B RESULT NS -99 2R FM-050 CSDO 10/31/05 9:42 Total Coliform SM 9221B RESULT NS -99 20R FM-060 CRW 10/31/05 11:46 Enterococcus EPA 1600 RESULT < 2 2 0 MR FM-060 CSDO 10/31/05 11:46 Enterococcus EPA 1600 RESULT None 780 20 YesR FM-060 CRW 10/31/05 11:46 Fecal Coliform SM 9222D RESULT < 2 2 0 MR FM-060 CSDO 10/31/05 11:46 Fecal Coliform SM 9221E RESULT None 1400 20 YesR FM-060 CRW 10/31/05 11:46 Total Coliform SM 9222B RESULT < 20 20 0 MR FM-060 CSDO 10/31/05 11:46 Total Coliform SM 9221B RESULT None 30000 20 YesR FM-080 CRW 10/31/05 10:45 Enterococcus EPA 1600 RESULT None 2 2 75 RR FM-080 CSDO 10/31/05 10:45 Enterococcus EPA 1600 RESULT < 20 20 YesR FM-080 CRW 10/31/05 10:45 Fecal Coliform SM 9222D RESULT < 2 2 75 RR FM-080 CSDO 10/31/05 10:45 Fecal Coliform SM 9221E RESULT < 20 20 YesR FM-080 CRW 10/31/05 10:45 Total Coliform SM 9222B RESULT None 4 2 75 RR FM-080 CSDO 10/31/05 10:45 Total Coliform SM 9221B RESULT < 20 20 YesSD04-05 DataPage 115 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA03 LRW 11/02/04 9:24 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 11/02/04 9:24 Enterococcus EPA 1600 RESULT None 6000 20 NoR PENA03 LRW 11/02/04 9:24 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 11/02/04 9:24 Fecal Coliform SM 9221E RESULT None 500 20 NoR PENA03 LRW 11/02/04 9:24 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 11/02/04 9:24 Total Coliform SM 9221B RESULT None 80000 20 NoR PENA06 LRW 11/02/04 9:20 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 11/02/04 9:20 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 11/02/04 9:20 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 11/02/04 9:20 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 11/02/04 9:20 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 11/02/04 9:20 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 11/02/04 9:28 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 11/02/04 9:28 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 11/02/04 9:28 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 11/02/04 9:28 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 11/02/04 9:28 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 11/02/04 9:28 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 11/02/04 9:32 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 11/02/04 9:32 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 11/02/04 9:32 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 11/02/04 9:32 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 11/02/04 9:32 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 11/02/04 9:32 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 11/02/04 9:22 Enterococcus EPA 1600 RESULT NS -99 2PENA11 LSDO 11/02/04 9:22 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 11/02/04 9:22 Fecal Coliform SM 9222D RESULT NS -99 2PENA11 LSDO 11/02/04 9:22 Fecal Coliform SM 9221E RESULT NS -99 20PENA11 LRW 11/02/04 9:22 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 11/02/04 9:22 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 12/13/04 9:25 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 12/13/04 9:25 Enterococcus EPA 1600 RESULT None 1600 20 NoR PENA03 LRW 12/13/04 9:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 12/13/04 9:25 Fecal Coliform SM 9221E RESULT None 70 20 NoR PENA03 LRW 12/13/04 9:25 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 12/13/04 9:25 Total Coliform SM 9221B RESULT None 500 20 NoR PENA06 LRW 12/13/04 9:35 Enterococcus EPA 1600 RESULT NS -99 2SD04-05 DataPage 116 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA06 LSDO 12/13/04 9:35 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 12/13/04 9:35 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 12/13/04 9:35 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 12/13/04 9:35 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 12/13/04 9:35 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 12/13/04 9:40 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 12/13/04 9:40 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 12/13/04 9:40 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 12/13/04 9:40 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 12/13/04 9:40 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 12/13/04 9:40 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 12/13/04 9:45 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 12/13/04 9:45 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 12/13/04 9:45 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 12/13/04 9:45 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 12/13/04 9:45 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 12/13/04 9:45 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 12/13/04 9:36 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 12/13/04 9:36 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 12/13/04 9:36 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 12/13/04 9:36 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 12/13/04 9:36 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 12/13/04 9:36 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 01/18/05 7:25 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 01/18/05 7:25 Enterococcus EPA 1600 RESULT None 100 20 NoR PENA03 LRW 01/18/05 7:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 01/18/05 7:25 Fecal Coliform SM 9221E RESULT None 20 20 NoR PENA03 LRW 01/18/05 7:25 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 01/18/05 7:25 Total Coliform SM 9221B RESULT None 500 20 NoR PENA06 LRW 01/18/05 7:35 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 01/18/05 7:35 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 01/18/05 7:35 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 01/18/05 7:35 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 01/18/05 7:35 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 01/18/05 7:35 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 01/18/05 7:44 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 01/18/05 7:44 Enterococcus EPA 1600 RESULT NS -99 20SD04-05 DataPage 117 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA08 LRW 01/18/05 7:44 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 01/18/05 7:44 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 01/18/05 7:44 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 01/18/05 7:44 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 01/18/05 7:48 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 01/18/05 7:48 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 01/18/05 7:48 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 01/18/05 7:48 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 01/18/05 7:48 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 01/18/05 7:48 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 01/18/05 7:38 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 01/18/05 7:38 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 01/18/05 7:38 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 01/18/05 7:38 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 01/18/05 7:38 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 01/18/05 7:38 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 02/01/05 8:45 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 02/01/05 8:45 Enterococcus EPA 1600 RESULT None 360 20 NoR PENA03 LRW 02/01/05 8:45 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 02/01/05 8:45 Fecal Coliform SM 9221E RESULT None 40 20 NoR PENA03 LRW 02/01/05 8:45 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 02/01/05 8:45 Total Coliform SM 9221B RESULT None 3000 20 NoR PENA06 LRW 02/01/05 8:47 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 02/01/05 8:47 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 02/01/05 8:47 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 02/01/05 8:47 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 02/01/05 8:47 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 02/01/05 8:47 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 02/01/05 8:55 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 02/01/05 8:55 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 02/01/05 8:55 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 02/01/05 8:55 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 02/01/05 8:55 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 02/01/05 8:55 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 02/01/05 9:00 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 02/01/05 9:00 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 02/01/05 9:00 Fecal Coliform SM 9222D RESULT NS -99 2SD04-05 DataPage 118 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA10 LSDO 02/01/05 9:00 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 02/01/05 9:00 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 02/01/05 9:00 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 02/01/05 9:01 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 02/01/05 9:01 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 02/01/05 9:01 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 02/01/05 9:01 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 02/01/05 9:01 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 02/01/05 9:01 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 03/01/05 11:25 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 03/01/05 11:25 Enterococcus EPA 1600 RESULT None 60 20 NoR PENA03 LRW 03/01/05 11:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 03/01/05 11:25 Fecal Coliform SM 9221E RESULT None 20 20 NoR PENA03 LRW 03/01/05 11:25 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 03/01/05 11:25 Total Coliform SM 9221B RESULT None 800 20 NoR PENA06 LRW 03/01/05 11:30 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 03/01/05 11:30 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 03/01/05 11:30 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 03/01/05 11:30 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 03/01/05 11:30 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 03/01/05 11:30 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 03/01/05 11:38 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 03/01/05 11:38 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 03/01/05 11:38 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 03/01/05 11:38 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 03/01/05 11:38 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 03/01/05 11:38 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 03/01/05 11:40 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 03/01/05 11:40 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 03/01/05 11:40 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 03/01/05 11:40 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 03/01/05 11:40 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 03/01/05 11:40 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 03/01/05 11:35 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 03/01/05 11:35 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 03/01/05 11:35 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 03/01/05 11:35 Fecal Coliform SM 9221E RESULT NS -99 20SD04-05 DataPage 119 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA11 LRW 03/01/05 11:35 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 03/01/05 11:35 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 04/04/05 10:08 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 04/04/05 10:08 Enterococcus EPA 1600 RESULT None 1100 20 NoR PENA03 LRW 04/04/05 10:08 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 04/04/05 10:08 Fecal Coliform SM 9221E RESULT None 20 20 NoR PENA03 LRW 04/04/05 10:08 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 04/04/05 10:08 Total Coliform SM 9221B RESULT None 1300 20 NoR PENA06 LRW 04/04/05 10:19 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 04/04/05 10:19 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 04/04/05 10:19 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 04/04/05 10:19 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 04/04/05 10:19 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 04/04/05 10:19 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 04/04/05 10:24 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 04/04/05 10:24 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 04/04/05 10:24 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 04/04/05 10:24 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 04/04/05 10:24 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 04/04/05 10:24 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 04/04/05 10:31 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 04/04/05 10:31 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 04/04/05 10:31 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 04/04/05 10:31 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 04/04/05 10:31 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 04/04/05 10:31 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 04/04/05 10:22 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 04/04/05 10:22 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 04/04/05 10:22 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 04/04/05 10:22 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 04/04/05 10:22 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 04/04/05 10:22 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 04/18/05 8:05 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 04/18/05 8:05 Enterococcus EPA 1600 RESULT None 320 20 NoR PENA03 LRW 04/18/05 8:05 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 04/18/05 8:05 Fecal Coliform SM 9221E RESULT < 20 20 NoR PENA03 LRW 04/18/05 8:05 Total Coliform SM 9222B RESULT NS -99 2SD04-05 DataPage 120 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA03 LSDO 04/18/05 8:05 Total Coliform SM 9221B RESULT None 700 20 NoR PENA06 LRW 04/18/05 8:16 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 04/18/05 8:16 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 04/18/05 8:16 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 04/18/05 8:16 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 04/18/05 8:16 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 04/18/05 8:16 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 04/18/05 8:33 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 04/18/05 8:33 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 04/18/05 8:33 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 04/18/05 8:33 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 04/18/05 8:33 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 04/18/05 8:33 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 04/18/05 8:30 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 04/18/05 8:30 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 04/18/05 8:30 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 04/18/05 8:30 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 04/18/05 8:30 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 04/18/05 8:30 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 04/18/05 8:20 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 04/18/05 8:20 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 04/18/05 8:20 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 04/18/05 8:20 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 04/18/05 8:20 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 04/18/05 8:20 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 05/02/05 9:25 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 05/02/05 9:25 Enterococcus EPA 1600 RESULT None 280 20 NoR PENA03 LRW 05/02/05 9:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 05/02/05 9:25 Fecal Coliform SM 9221E RESULT None 40 20 NoR PENA03 LRW 05/02/05 9:25 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 05/02/05 9:25 Total Coliform SM 9221B RESULT None 5000 20 NoR PENA06 LRW 05/02/05 9:32 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 05/02/05 9:32 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 05/02/05 9:32 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 05/02/05 9:32 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 05/02/05 9:32 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 05/02/05 9:32 Total Coliform SM 9221B RESULT NS -99 20SD04-05 DataPage 121 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA08 LRW 05/02/05 9:40 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 05/02/05 9:40 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 05/02/05 9:40 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 05/02/05 9:40 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 05/02/05 9:40 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 05/02/05 9:40 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 05/02/05 9:48 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 05/02/05 9:48 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 05/02/05 9:48 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 05/02/05 9:48 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 05/02/05 9:48 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 05/02/05 9:48 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 05/02/05 9:50 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 05/02/05 9:50 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 05/02/05 9:50 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 05/02/05 9:50 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 05/02/05 9:50 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 05/02/05 9:50 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 05/17/05 9:05 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 05/17/05 9:05 Enterococcus EPA 1600 RESULT None 80 20 NoR PENA03 LRW 05/17/05 9:05 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 05/17/05 9:05 Fecal Coliform SM 9221E RESULT None 20 20 NoR PENA03 LRW 05/17/05 9:05 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 05/17/05 9:05 Total Coliform SM 9221B RESULT None 700 20 NoR PENA06 LRW 05/17/05 9:14 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 05/17/05 9:14 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 05/17/05 9:14 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 05/17/05 9:14 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 05/17/05 9:14 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 05/17/05 9:14 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 05/17/05 9:35 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 05/17/05 9:35 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 05/17/05 9:35 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 05/17/05 9:35 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 05/17/05 9:35 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 05/17/05 9:35 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 05/17/05 9:28 Enterococcus EPA 1600 RESULT NS -99 2SD04-05 DataPage 122 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA10 LSDO 05/17/05 9:28 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 05/17/05 9:28 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 05/17/05 9:28 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 05/17/05 9:28 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 05/17/05 9:28 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 05/17/05 9:30 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 05/17/05 9:30 Enterococcus EPA 1600 RESULT None 6400 20 YesR PENA11 LRW 05/17/05 9:30 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 05/17/05 9:30 Fecal Coliform SM 9221E RESULT None 300 20 YesR PENA11 LRW 05/17/05 9:30 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 05/17/05 9:30 Total Coliform SM 9221B RESULT None 80000 20 YesR PENA03 LRW 05/31/05 13:00 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 05/31/05 13:00 Enterococcus EPA 1600 RESULT None 260 20 NoR PENA03 LRW 05/31/05 13:00 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 05/31/05 13:00 Fecal Coliform SM 9221E RESULT None 300 20 NoR PENA03 LRW 05/31/05 13:00 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 05/31/05 13:00 Total Coliform SM 9221B RESULT None 3000 20 NoR PENA06 LRW 05/31/05 13:15 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 05/31/05 13:15 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 05/31/05 13:15 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 05/31/05 13:15 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 05/31/05 13:15 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 05/31/05 13:15 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 05/31/05 14:20 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 05/31/05 14:20 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 05/31/05 14:20 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 05/31/05 14:20 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 05/31/05 14:20 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 05/31/05 14:20 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 05/31/05 14:08 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 05/31/05 14:08 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 05/31/05 14:08 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 05/31/05 14:08 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 05/31/05 14:08 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 05/31/05 14:08 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 05/31/05 14:10 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 05/31/05 14:10 Enterococcus EPA 1600 RESULT None 3400 20 NoSD04-05 DataPage 123 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA11 LRW 05/31/05 14:10 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 05/31/05 14:10 Fecal Coliform SM 9221E RESULT None 110 20 NoR PENA11 LRW 05/31/05 14:10 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 05/31/05 14:10 Total Coliform SM 9221B RESULT None 23000 20 NoR PENA03 LRW 06/13/05 9:35 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 06/13/05 9:35 Enterococcus EPA 1600 RESULT None 1500 20 NoR PENA03 LRW 06/13/05 9:35 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 06/13/05 9:35 Fecal Coliform SM 9221E RESULT None 300 20 NoR PENA03 LRW 06/13/05 9:35 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 06/13/05 9:35 Total Coliform SM 9221B RESULT None 13000 20 NoR PENA06 LRW 06/13/05 9:25 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 06/13/05 9:25 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 06/13/05 9:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 06/13/05 9:25 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 06/13/05 9:25 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 06/13/05 9:25 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 06/13/05 9:10 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 06/13/05 9:10 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 06/13/05 9:10 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 06/13/05 9:10 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 06/13/05 9:10 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 06/13/05 9:10 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 06/13/05 8:50 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 06/13/05 8:50 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 06/13/05 8:50 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 06/13/05 8:50 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 06/13/05 8:50 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 06/13/05 8:50 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 06/13/05 8:55 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 06/13/05 8:55 Enterococcus EPA 1600 RESULT None 1200 20 NoR PENA11 LRW 06/13/05 8:55 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 06/13/05 8:55 Fecal Coliform SM 9221E RESULT None 1300 20 NoR PENA11 LRW 06/13/05 8:55 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 06/13/05 8:55 Total Coliform SM 9221B RESULT None 11000 20 NoR PENA03 LRW 06/27/05 7:30 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 06/27/05 7:30 Enterococcus EPA 1600 RESULT None 120 20 NoR PENA03 LRW 06/27/05 7:30 Fecal Coliform SM 9222D RESULT NS -99 2SD04-05 DataPage 124 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA03 LSDO 06/27/05 7:30 Fecal Coliform SM 9221E RESULT < 20 20 NoR PENA03 LRW 06/27/05 7:30 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 06/27/05 7:30 Total Coliform SM 9221B RESULT None 2300 20 NoR PENA06 LRW 06/27/05 7:40 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 06/27/05 7:40 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 06/27/05 7:40 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 06/27/05 7:40 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 06/27/05 7:40 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 06/27/05 7:40 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 06/27/05 7:45 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 06/27/05 7:45 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 06/27/05 7:45 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 06/27/05 7:45 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 06/27/05 7:45 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 06/27/05 7:45 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 06/27/05 7:50 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 06/27/05 7:50 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 06/27/05 7:50 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 06/27/05 7:50 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 06/27/05 7:50 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 06/27/05 7:50 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 06/27/05 8:00 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 06/27/05 8:00 Enterococcus EPA 1600 RESULT None 600 20 NoR PENA11 LRW 06/27/05 8:00 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 06/27/05 8:00 Fecal Coliform SM 9221E RESULT None 20 20 NoR PENA11 LRW 06/27/05 8:00 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 06/27/05 8:00 Total Coliform SM 9221B RESULT None 3000 20 NoR PENA03 LRW 07/11/05 9:30 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 07/11/05 9:30 Enterococcus EPA 1600 RESULT None 180 20 NoR PENA03 LRW 07/11/05 9:30 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 07/11/05 9:30 Fecal Coliform SM 9221E RESULT None 20 20 NoR PENA03 LRW 07/11/05 9:30 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 07/11/05 9:30 Total Coliform SM 9221B RESULT None 17000 20 NoR PENA06 LRW 07/11/05 9:38 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 07/11/05 9:38 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 07/11/05 9:38 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 07/11/05 9:38 Fecal Coliform SM 9221E RESULT NS -99 20SD04-05 DataPage 125 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA06 LRW 07/11/05 9:38 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 07/11/05 9:38 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LSDO 07/11/05 9:53 Enterococcus EPA 1600 RESULT None 22 2 0 MR PENA08 LRW 07/11/05 9:53 Enterococcus EPA 1600 RESULT None 3800 20 NoR PENA08 LSDO 07/11/05 9:53 Fecal Coliform SM 9222D RESULT None 22 2 0 MR PENA08 LRW 07/11/05 9:53 Fecal Coliform SM 9221E RESULT None 500 20 NoR PENA08 LSDO 07/11/05 9:53 Total Coliform SM 9222B RESULT None 600 2 0 MR PENA08 LRW 07/11/05 9:53 Total Coliform SM 9221B RESULT None 2300 20 NoR PENA10 LRW 07/11/05 9:40 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 07/11/05 9:40 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 07/11/05 9:40 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 07/11/05 9:40 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 07/11/05 9:40 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 07/11/05 9:40 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 07/11/05 9:50 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 07/11/05 9:50 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 07/11/05 9:50 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 07/11/05 9:50 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 07/11/05 9:50 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 07/11/05 9:50 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 07/25/05 9:05 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 07/25/05 9:05 Enterococcus EPA 1600 RESULT None 1200 20 NoR PENA03 LRW 07/25/05 9:05 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 07/25/05 9:05 Fecal Coliform SM 9221E RESULT None 230 20 NoR PENA03 LRW 07/25/05 9:05 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 07/25/05 9:05 Total Coliform SM 9221B RESULT None 5000 20 NoR PENA06 LRW 07/25/05 9:15 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 07/25/05 9:15 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 07/25/05 9:15 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 07/25/05 9:15 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 07/25/05 9:15 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 07/25/05 9:15 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 07/25/05 9:38 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 07/25/05 9:38 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 07/25/05 9:38 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 07/25/05 9:38 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 07/25/05 9:38 Total Coliform SM 9222B RESULT NS -99 2SD04-05 DataPage 126 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA08 LSDO 07/25/05 9:38 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 07/25/05 9:30 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 07/25/05 9:30 Enterococcus EPA 1600 RESULT None 74000 20 YesR PENA10 LRW 07/25/05 9:30 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 07/25/05 9:30 Fecal Coliform SM 9221E RESULT None 130000 20 YesR PENA10 LRW 07/25/05 9:30 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 07/25/05 9:30 Total Coliform SM 9221B RESULT None 500000 20 YesR PENA11 LRW 07/25/05 9:18 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 07/25/05 9:18 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 07/25/05 9:18 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 07/25/05 9:18 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 07/25/05 9:18 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 07/25/05 9:18 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 08/09/05 10:55 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 08/09/05 10:55 Enterococcus EPA 1600 RESULT None 1800 20 NoR PENA03 LRW 08/09/05 10:55 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 08/09/05 10:55 Fecal Coliform SM 9221E RESULT None 20 20 NoR PENA03 LRW 08/09/05 10:55 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 08/09/05 10:55 Total Coliform SM 9221B RESULT None 13000 20 NoR PENA06 LRW 08/09/05 10:51 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 08/09/05 10:51 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 08/09/05 10:51 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 08/09/05 10:51 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 08/09/05 10:51 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 08/09/05 10:51 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 08/09/05 10:40 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 08/09/05 10:40 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 08/09/05 10:40 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 08/09/05 10:40 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 08/09/05 10:40 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 08/09/05 10:40 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 08/09/05 10:35 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 08/09/05 10:35 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 08/09/05 10:35 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 08/09/05 10:35 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 08/09/05 10:35 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 08/09/05 10:35 Total Coliform SM 9221B RESULT NS -99 20SD04-05 DataPage 127 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA11 LRW 08/09/05 10:47 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 08/09/05 10:47 Enterococcus EPA 1600 RESULT None 800 20 YesR PENA11 LRW 08/09/05 10:47 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 08/09/05 10:47 Fecal Coliform SM 9221E RESULT None 500 20 YesR PENA11 LRW 08/09/05 10:47 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 08/09/05 10:47 Total Coliform SM 9221B RESULT None 7000 20 YesR PENA03 LRW 08/22/05 8:55 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 08/22/05 8:55 Enterococcus EPA 1600 RESULT None 140 20 NoR PENA03 LRW 08/22/05 8:55 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 08/22/05 8:55 Fecal Coliform SM 9221E RESULT None 500 20 NoR PENA03 LRW 08/22/05 8:55 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 08/22/05 8:55 Total Coliform SM 9221B RESULT None 5000 20 NoR PENA06 LRW 08/22/05 9:05 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 08/22/05 9:05 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 08/22/05 9:05 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 08/22/05 9:05 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 08/22/05 9:05 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 08/22/05 9:05 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 08/22/05 9:25 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 08/22/05 9:25 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 08/22/05 9:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 08/22/05 9:25 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 08/22/05 9:25 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 08/22/05 9:25 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 08/22/05 9:16 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 08/22/05 9:16 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 08/22/05 9:16 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 08/22/05 9:16 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 08/22/05 9:16 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 08/22/05 9:16 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 08/22/05 9:20 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 08/22/05 9:20 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 08/22/05 9:20 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 08/22/05 9:20 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 08/22/05 9:20 Total Coliform SM 9222B RESULT NS -99 2R LSDO 08/22/05 9:20 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 09/06/05 8:25 Enterococcus EPA 1600 RESULT NS -99 2SD04-05 DataPage 128 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA03 LSDO 09/06/05 8:25 Enterococcus EPA 1600 RESULT None 360 20 NoR PENA03 LRW 09/06/05 8:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 09/06/05 8:25 Fecal Coliform SM 9221E RESULT None 8000 20 NoR PENA03 LRW 09/06/05 8:25 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 09/06/05 8:25 Total Coliform SM 9221B RESULT None 23000 20 NoR PENA06 LRW 09/06/05 8:36 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 09/06/05 8:36 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 09/06/05 8:36 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 09/06/05 8:36 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 09/06/05 8:36 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 09/06/05 8:36 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 09/06/05 8:50 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 09/06/05 8:50 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 09/06/05 8:50 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 09/06/05 8:50 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 09/06/05 8:50 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 09/06/05 8:50 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 09/06/05 8:55 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 09/06/05 8:55 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 09/06/05 8:55 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 09/06/05 8:55 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 09/06/05 8:55 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 09/06/05 8:55 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 09/06/05 8:59 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 09/06/05 8:59 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 09/06/05 8:59 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 09/06/05 8:59 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 09/06/05 8:59 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 09/06/05 8:59 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 09/19/05 9:17 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 09/19/05 9:17 Enterococcus EPA 1600 RESULT NS -99 20R PENA03 LRW 09/19/05 9:17 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 09/19/05 9:17 Fecal Coliform SM 9221E RESULT NS -99 20R PENA03 LRW 09/19/05 9:17 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 09/19/05 9:17 Total Coliform SM 9221B RESULT NS -99 20R PENA06 LRW 09/19/05 9:25 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 09/19/05 9:25 Enterococcus EPA 1600 RESULT NS -99 20SD04-05 DataPage 129 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA06 LRW 09/19/05 9:25 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 09/19/05 9:25 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 09/19/05 9:25 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 09/19/05 9:25 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 09/19/05 9:43 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 09/19/05 9:43 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 09/19/05 9:43 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 09/19/05 9:43 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 09/19/05 9:43 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 09/19/05 9:43 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 09/19/05 9:40 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 09/19/05 9:40 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 09/19/05 9:40 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 09/19/05 9:40 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 09/19/05 9:40 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 09/19/05 9:40 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 09/19/05 9:26 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 09/19/05 9:26 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 09/19/05 9:26 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 09/19/05 9:26 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 09/19/05 9:26 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 09/19/05 9:26 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 10/03/05 9:50 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 10/03/05 9:50 Enterococcus EPA 1600 RESULT None 260 20 NoR PENA03 LRW 10/03/05 9:50 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 10/03/05 9:50 Fecal Coliform SM 9221E RESULT None 300 20 NoR PENA03 LRW 10/03/05 9:50 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 10/03/05 9:50 Total Coliform SM 9221B RESULT None 3000 20 NoR PENA06 LRW 10/03/05 10:00 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 10/03/05 10:00 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 10/03/05 10:00 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 10/03/05 10:00 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 10/03/05 10:00 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 10/03/05 10:00 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 10/03/05 10:05 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 10/03/05 10:05 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 10/03/05 10:05 Fecal Coliform SM 9222D RESULT NS -99 2SD04-05 DataPage 130 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA08 LSDO 10/03/05 10:05 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 10/03/05 10:05 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 10/03/05 10:05 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 10/03/05 10:01 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 10/03/05 10:01 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 10/03/05 10:01 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 10/03/05 10:01 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 10/03/05 10:01 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 10/03/05 10:01 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 10/03/05 10:12 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 10/03/05 10:12 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 10/03/05 10:12 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 10/03/05 10:12 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 10/03/05 10:12 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 10/03/05 10:12 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 10/17/05 11:36 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 10/17/05 11:36 Enterococcus EPA 1600 RESULT None 2200 20 NoR PENA03 LRW 10/17/05 11:36 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 10/17/05 11:36 Fecal Coliform SM 9221E RESULT None 130 20 NoR PENA03 LRW 10/17/05 11:36 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 10/17/05 11:36 Total Coliform SM 9221B RESULT None 17000 20 NoR PENA06 LRW 10/17/05 11:31 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 10/17/05 11:31 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 10/17/05 11:31 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 10/17/05 11:31 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 10/17/05 11:31 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 10/17/05 11:31 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 10/17/05 11:18 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 10/17/05 11:18 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 10/17/05 11:18 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 10/17/05 11:18 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 10/17/05 11:18 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 10/17/05 11:18 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 10/17/05 11:23 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 10/17/05 11:23 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 10/17/05 11:23 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 10/17/05 11:23 Fecal Coliform SM 9221E RESULT NS -99 20SD04-05 DataPage 131 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA10 LRW 10/17/05 11:23 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 10/17/05 11:23 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 10/17/05 11:28 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 10/17/05 11:28 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 10/17/05 11:28 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 10/17/05 11:28 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 10/17/05 11:28 Total Coliform SM 9222B RESULT NS -99 2R PENA11 LSDO 10/17/05 11:28 Total Coliform SM 9221B RESULT NS -99 20R PENA03 LRW 10/31/05 9:20 Enterococcus EPA 1600 RESULT NS -99 2R PENA03 LSDO 10/31/05 9:20 Enterococcus EPA 1600 RESULT None 160 20 NoR PENA03 LRW 10/31/05 9:20 Fecal Coliform SM 9222D RESULT NS -99 2R PENA03 LSDO 10/31/05 9:20 Fecal Coliform SM 9221E RESULT None 80 20 NoR PENA03 LRW 10/31/05 9:20 Total Coliform SM 9222B RESULT NS -99 2R PENA03 LSDO 10/31/05 9:20 Total Coliform SM 9221B RESULT None 220 20 NoR PENA06 LRW 10/31/05 11:31 Enterococcus EPA 1600 RESULT NS -99 2R PENA06 LSDO 10/31/05 11:31 Enterococcus EPA 1600 RESULT NS -99 20R PENA06 LRW 10/31/05 11:31 Fecal Coliform SM 9222D RESULT NS -99 2R PENA06 LSDO 10/31/05 11:31 Fecal Coliform SM 9221E RESULT NS -99 20R PENA06 LRW 10/31/05 11:31 Total Coliform SM 9222B RESULT NS -99 2R PENA06 LSDO 10/31/05 11:31 Total Coliform SM 9221B RESULT NS -99 20R PENA08 LRW 10/31/05 11:18 Enterococcus EPA 1600 RESULT NS -99 2R PENA08 LSDO 10/31/05 11:18 Enterococcus EPA 1600 RESULT NS -99 20R PENA08 LRW 10/31/05 11:18 Fecal Coliform SM 9222D RESULT NS -99 2R PENA08 LSDO 10/31/05 11:18 Fecal Coliform SM 9221E RESULT NS -99 20R PENA08 LRW 10/31/05 11:18 Total Coliform SM 9222B RESULT NS -99 2R PENA08 LSDO 10/31/05 11:18 Total Coliform SM 9221B RESULT NS -99 20R PENA10 LRW 10/31/05 11:23 Enterococcus EPA 1600 RESULT NS -99 2R PENA10 LSDO 10/31/05 11:23 Enterococcus EPA 1600 RESULT NS -99 20R PENA10 LRW 10/31/05 11:23 Fecal Coliform SM 9222D RESULT NS -99 2R PENA10 LSDO 10/31/05 11:23 Fecal Coliform SM 9221E RESULT NS -99 20R PENA10 LRW 10/31/05 11:23 Total Coliform SM 9222B RESULT NS -99 2R PENA10 LSDO 10/31/05 11:23 Total Coliform SM 9221B RESULT NS -99 20R PENA11 LRW 10/31/05 11:28 Enterococcus EPA 1600 RESULT NS -99 2R PENA11 LSDO 10/31/05 11:28 Enterococcus EPA 1600 RESULT NS -99 20R PENA11 LRW 10/31/05 11:28 Fecal Coliform SM 9222D RESULT NS -99 2R PENA11 LSDO 10/31/05 11:28 Fecal Coliform SM 9221E RESULT NS -99 20R PENA11 LRW 10/31/05 11:28 Total Coliform SM 9222B RESULT NS -99 2SD04-05 DataPage 132 of 133 Analytical Laboratory: Marine Metro LabAnalytical Units: CFU/100ml and MPN/100ml CSDM Lagoon DataNov 1, 2004 - Oct 31, 2005City of San DiegoPrefix Station ID Station TypeDate Time Analyte MethodSample TypeQualifier ResultReporting LimitDistance DirectionStormdrain Reaches Rec WaterR PENA11 LSDO 10/31/05 11:28 Total Coliform SM 9221B RESULT NS -99 20SD04-05 DataPage 133 of 133 APPENDIX H Data Screening Protocol CSDM Program 2004-2005 Data Screening Protocol To provide consistency to the statistical analyses, the CSDM Copermittees screened the raw data according to rules agreed to by the entire Workgroup. Once these rules were implemented, the dataset was considered to be ‘screened’. This screened dataset included both true paired and unpaired (single sample) records and was used for the analyses contained in the CSDM Report. A record is defined as a water sample analyzed for a single analyte with defined parameters pertaining to location, date etc, represented as a single row of data on the electronic dataset submission. These rules are identified below so that the statistical analyses can be repeated and/or confirmed. The numbers in parenthesis identify the number of samples affected by that rule. 1. All data were collected and submitted using the Data Transfer Templates. 2. Entries that did not have sample results and/or contained other blank fields, and single receiving water samples were deleted. 3. All records with a qualifier of ‘NA’, ‘AE’, or ‘NS’ and –99 in the ‘Result’ column were deleted. 4. Any records with a qualifier of ‘<’ and results of ‘50’ or higher were deleted. 5. Any records with a qualifier of ‘>’ and a result of ‘160000’ were changed to a qualifier of ‘=’ with the result remaining at ‘160000’. 6. Any receiving water or storm drain results with a qualifier of ‘>’ and a result of ‘1600’ or higher were changed to a qualifier of ‘=’ with the result remaining the same. 7. Any results with a qualifier of ‘<’ and a result of ‘1’ were changed to a qualifier of ‘=’ with the result remaining at ‘1’. 8. Any results with a qualifier of ‘<’ were changed to ½ their original value in the ‘result’ column. 9. The data was reviewed manually to match up paired samples, designated with a ‘P’ in the ‘Paired Sample’ column. 95% Percentile Calculation & Sampling Frequency Reduction Additional steps were included to determine the 95th percentile and sampling frequency reduction criteria for both paired and single samples, and for both storm drain and receiving water samples for each indicator, and are identified below. It should be noted that the analyses for each indicator (Total Coliform, Fecal Coliform, and Enterococcus) was conducted using the same process. 95th Percentile 1. The screened dataset was sorted by analyte, and each analyte’s samples were moved to another worksheet. 2. Follow up samples, designated with an ‘F’ in the Prefix column, were deleted. 3. Receiving water samples were deleted. 4. Using the quantitative data in the ‘Result’ column, the 95% was calculated using the ‘Rank and Percentile’ function in Excel. 5. Data was re-entered and proofed manually to ensure data entry integrity so that results are as accurate as possible. Sampling Frequency Reduction 1. The screened dataset was sorted by analyte, and each analyte’s samples were moved to another worksheet. 2. Follow up samples, designated with an ‘F’ in the Prefix column, were deleted. 3. Only paired samples (sites having both storm drain and receiving water collected during the sampling event) were used. Data was manually verified to ensure that there were equal numbers of stormdrain receiving water samples. 4. Storm drain and receiving water results were transformed into log10 values. These values were used to create a scatter (XY) chart, with the receiving waters plotted on the X axis and the storm drains plotted on the Y axis. 5. A trend line identifying the linear regression was added, and the slope and R value were noted. 6. The log10 slope was back transformed to reveal the actual slope. 7. The slope was then multiplied by the appropriate indicator receiving water exceedance level (TC – 10,000; FC – 400; ENT – 104) to determine the dilution factor. Figure 4-3 2004-2005 Enterococcus Adaptive Monitoring Diagram - Coastal1101001,00010,000100,0001,000,0001 10 100 1,000 10,000 100,000 1,000,000Storm Drain (MPN/ 100 mls)Receiving Water (MPN/ 100 mls)Storm drain concentration below 95th percentile criteria - no action necessaryEntero Standard (Ocean)- 104 MPN/ 100 mlsStorm drain and receiving water levels are below receiving water standards. No action necessary.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.95th percentile criteria18,400 MPN/ 100 mls Ent.Unlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms. Figure 4-2 2004-2005 Fecal Coliform Adaptive Monitoring Diagram - Coastal1101001,00010,000100,0001,000,0001 10 100 1,000 10,000 100,000 1,000,000 10,000,000Storm Drain (MPN/ 100 mls)Receiving Water (MPN/ 100 mls)FC Standard - 400 MPN/ 100 mlsHighly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.Storm drain concentration below 95th percentile criteria - no action necessary95th percentile criteria27,600 MPN/ 100 mls FCStorm drain and receiving water levels are below receiving water standards. No action necessary.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms.Unlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate. Figure 4-1 2004-2005 Total Coliform Adaptive Monitoring Diagram - Coastal 1101001,00010,000100,0001,000,00010,000,0001 10 100 1,000 10,000 100,000 1,000,000 10,000,000Storm Drain (MPN/ 100 mls)Receiving Water (MPN/ 100 mls)TC Standard10,000 MPN/ 100 mlsStorm drain and receiving water levels are below receiving water standards. No action necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP.Investigate, if resample confirms.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.Storm drain concentration below 95th percentile criteria - no action necessaryUnlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.95th percentile criteria160,000 MPN/ 100 mlsStorm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary. Figure 4.6 Adaptive Monitoring Diagram For Enterococcus Lagoon Data 2004-2005 1101001,00010,000100,0001,000,0001 10 100 1,000 10,000 100,000Lagoon Storm Drain Outfall (LSDO) (MPN/ 100 mls)Lagoon Receiving Water (LRW) (MPN/ 100 mls)Agua HediondaBatiquitosSan ElijoBuena VistaStorm drain and receiving water levels are below receiving water standards. No action necessary.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.95th percentile criteria 18,400 MPN/ 100 mls Ent.Storm drain concentration below 95th percentile criteria - no action necessaryUnlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms.Infrequent Use Moderate/Light Use Figure 4.5 Adaptive Monitoring Diagram For Fecal Coliform - Lagoon Data 2004-20051101001,00010,000100,0001,000,0001 10 100 1,000 10,000 100,000 1,000,000Lagoon Storm Drain Outfall (LSDO) (MPN/ 100 mls)Lagoon Receiving Water (LRW) (MPN/ 100 mls)Agua HediondaBatiquitosSan ElijoBuena VistaHighly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.Storm drain concentration below 95th percentile criteria - no action necessary95th percentile criteria27,600 MPN/ 100 mls FCStorm drain and receiving water levels are below receiving water standards. No action necessary.Unlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP.Investigate, if resample confirms. TC TC Q FC FC Q ENT ENT Q ReachStation ID Date LRW LSDO LRW LSDO LRW LSDOAH-00611/03/04 400 27,000 IA 244 10,700 IA 140 9,900 IA yesAH-00612/14/04 676 5,650 I 196 300 I 48 700 IA yesAH-00601/19/05 3,850 47,600 IA 240 18,300 IA 132 3,200 IA yesAH-00602/10/05 320 800 I 100 500 IA 56 900 IA yesAH-00603/17/05 20 1,800 I 4 800 IA 56 600 IA yesAH-0064/14/05 140 4,500 I 44 550 IA 52 600 IA yesAH-0064/20/05 120 3,650 I 72 1,820 IA 32 1,060 IA yesAH-0065/3/05 350 9,900 I 200 5,360 IA 152 2,180 IA yesAH-0066/2/05 250 9,700 I 184 840 IA 192 2,140 IA yesAH-006 6/15/05 5010,900IA 1010,550IA 203,600IA yesAH-006 6/27/05 5,100 10 I 4,55010 II130010 IIyesAH-006 7/13/05 601,000I5250I5200 IyesAH-006 7/27/05 1301,980I20200I201,100IA yesAH-006 8/11/05 205,600I201,250IA 102,200IA yesAH-006 8/22/05 2203,700I803,250IA 802,000IA yesAH-006 9/8/05 705,200I5700IA 202,150IA yesAH-006 9/28/05 52014,500IA 2407,400IA 1605,100IA yesAH-006 10/5/05 1,5206,500I 9605,000 IV4303,100 IVyesAH-006 10/26/05 3206,700I 1802,150IA 1802,100IA yesAH-011 01/20/053303,500 I84500 IA481,250 IA yesAH-011 03/10/053001,300 I801,100 IA40350IyesAH-025 11/03/04186 4,500I114 2,800IA40 950IA yesAH-025 12/14/04186 4,500I114 2,800IA40 950IA yesAH-02501/25/05 166 7,700I82 100I68 1,500IA yesAH-025 03/16/05112 850I52 1,660IA32 60 IyesAH-025 4/14/0580 700I60 30I440 IyesAH-0254/19/05 20 740I28 180I220 IyesAH-025 5/3/0512 20I24 1,250IA8 1,160IA yesAH-025 6/2/05100 2,700I80 280I80 40 IyesAH-025 6/15/05 88200I 100300I4160 IyesAH-025 6/29/052 2,020I441,070IA 72420 IyesAH-025 7/14/05 301,800I5750IA 5610IA yesAH-025 7/27/05 52,450I70200I5300 IyesAH-025 8/8/05 103,350I20900IA 10480 IyesAH-025 8/23/05 301,500I5420IA 51,000IA yes TC TC Q FC FC Q ENT ENT Q ReachStation ID Date LRW LSDO LRW LSDO LRW LSDOAH-025 9/7/05 204,800I302,420IA 10580IA yesAH-025 9/28/05 103,475I404,600IA 10660IA yesAH-025 10/4/05 40200I10550IA 51,340IA yesAH-025 10/26/05 30028,600IA 1008,350IA 52,000IA yesAH-19A12/15/04 24 800I16 250I16 150 IyesAH-19A01/20/05 340 2,300I88 250I48 100 IyesAH-19A02/03/05 292 1,160I80 70I192 50 IyesAH-19A 03/16/0552 400I16 190I16 710IA yesAH-19A 4/14/05308 520I80 120I72 180 IyesAH-19A4/19/05 16 460I40 380I4 360 IyesAH-19A5/2/05 12 280I100 260I490 IyesAH-19A5/16/05 2 10I20 120I20 60 IyesAH-19A5/31/05 204 540I508 260 II 80 30 IyesAH-19A 6/14/05 10 10 I 10 80 I 40 170IyesAH-19A 6/29/05 20 80 I 20 40 I 10 30IyesAH-19A 7/13/05 10 300 I 10 220 I 10 150IyesAH-19A 7/26/05 10 10 I 440 3,480 IV 280 2950 IA yesAH-19A 8/8/05 20 10 I 20 780 IA 10 2940 IA yesAH-19A 8/23/05 200 10 I 1,880 320II380 260IyesAH-19A 9/7/05 10 100 I 10 300 I 5 180IyesAH-19A 10/3/05 20 10 I 20 460 IA 10 140IyesAH-19A 10/26/05 10 100 I 10 460 IA 5 220IyesBA-02112/13/04 248 5,800I140 4,900IA116 5,500IA yesCBS-2 11/3/04 200 5500 I 70 2050 IA 20 300IyesCBS-2 12/16/04 10 100 I 690 440 III 4 400IyesCBS-2 1/19/05 300 3000 I 660 100II520 540 IV yesCBS-2 2/2/05 710 9460 I 20 60 I 80 200IyesCBS-2 2/9/05 130 3720 I 130 1040 IA 60 300IyesCBS-2 3/9/05 660 2620 I 20 480 IA 100 200IyesCBS-2 4/6/05 20 340 I 60 550 IA 10 760 IA yesCBS-2 4/20/05 120 1700 I 490 250II20 1700 IA yesCBS-2 5/3/05 40 10 I 5 100 I 130 880 IA yesCBS-2 5/11/05 10 10 I 170 1280 IA 10 380IyesCBS-2 5/16/05 10 10 I 420 100II60 1600 IA yesCBS-2 6/2/05 10 10 I 10 240 I 60 460Iyes TC TC Q FC FC Q ENT ENT Q ReachStation ID Date LRW LSDO LRW LSDO LRW LSDOCBS-2 6/8/05 10 10 I 660 1980 IV 5 520 IA yesCBS-2 6/16/05 10 10 I 10 20 I 160 2200 IA yesCBS-2 6/30/05 10 10 I 10 200 I 20 40IyesCBS-2 7/14/05 10 10 I 80 540 IA 10 20IyesCBS-2 7/28/05 10 10 I 10 1040 IA 20 80IyesCBS-2 8/11/05 20 10 I 3300 10920 IV 40 440IyesCBS-2 8/29/05 40 840 I 520 2350 IV 420 3100 IA yesCBS-2 9/28/05 120 100 I 60 2550 IA 100 450IyesCBS-2 ########140 1600 IA yesCBS-2 10/24/05 280 1400 I 10 350 I 60 1450 IA yesCBS-5 6/7/05 280 25700 IA 360 6700 IA 240 30450 V yesCOAST 20 11/16/04 8000 30000 IA 500 70II800 1790 IV yesCOAST 20 12/14/04 30000 46000 IV 230 400 IA 640 720 IV yesCOAST 20 1/18/05 50000 17500 III 800 110II170 280IyesCOAST 20 2/8/05 17000 15000 III 500 800 IV 183 200IyesCOAST 20 3/8/05 2300 23000 IA 2300 170II2100 1590 III yesCOAST 20 4/12/05 13000 14000 IV 500 800 IV 170 1000 IA yesCOAST 20 4/26/05 30000 15000 III 1700 650 III 550 680 IV yesCOAST 20 5/10/05 29000 22000 III 300 1700 IA 370 980 IA yesCOAST 20 5/24/05 12000 9000 II 2000 4000 IV 340 640 IA yesCOAST 20 6/7/05 65000 30000 III 6500 5000 III 1000 2620 IV yesCOAST 20 6/21/05 90000 21000 III 4000 700 III 5200 790 III yesCOAST 20 7/5/05 15000 8000 II 1100 1100 IV 1800 1460 III yesCOAST 20 7/19/05 13000 30000 IV 3000 2300 III 860 800 III yesCOAST 20 8/2/05 13000 180000 IV 3000 9500 IV 1270 3270 IV yesCOAST 20 8/16/05 13000 6500 II 1300 2000 IV 500 1520 IV yesCOAST 20 8/30/05 3000 5200 I 300 1500 IA 480 4200 IA yesCOAST 20 9/13/05 1100 180000 V 300 4000 IA 160 1700 IA yesCOAST 20 9/27/05 22000 50000 IV 8000 5000 III 500 2300 IV yesCOAST 20 10/11/05 50000 5000 II 17000 800 III 740 550 III yesCOAST 20 10/25/05 920000 23000 III 23000 5000 III 2700 882 III yesSEL-1 3/9/05 192 40 I yesSEL-1 4/6/05 80 180 I 70 140 I 40 20IyesSEL-1 4/20/05 180 240 I 160 80 I 5 100IyesSEL-1 5/3/05 10 60 I 920 20II140 60Iyes TC TC Q FC FC Q ENT ENT Q ReachStation ID Date LRW LSDO LRW LSDO LRW LSDOSEL-1 5/11/05 10 100 I 100 10 I 10 20IyesSEL-1 5/16/05 10 1140 I 120 10 I 40 20Iyes Lagoon Indicator n I IAVII III IVAgua HediondaTotal Coliform 57 5250000Fecal Coliform 57 21 310302Enterococcus 57 25 300101171 57% 39% 0% 2% 0% 2%BatiquitosTotal Coliform1100000Fecal Coliform1010000Enterococcus10100003 33% 67% 0% 0% 0% 0%San ElijoTotal Coliform 27 2610000Fecal Coliform 28 1190413Enterococcus 28 179100183 65% 23% 1% 5% 1% 5%Buena VistaTotal Coliform 20121475Fecal Coliform 20040376Enterococcus 2025006760 5% 18% 2% 12% 33% 30%Table 4-7 Adaptive Diagram Quadrants (Number of Observations in Quadrant Sets) Figure 4.4 Adaptive Monitoring Diagram for Total Coliform - Lagoon Data 2004-20051101001,00010,000100,0001,000,00010,000,0001 10 100 1,000 10,000 100,000 1,000,000 10,000,000Lagoon Storm Drain Outfall (LSDO) (MPN/ 100 mls)Lagoon Receiving Water (LRW) (MPN/ 100 mls)Aqua HediondaBatiquitosSan ElijoBuena VistaStorm drain and receiving water levels are below receiving water standards. No action necessary.Storm drain contamination may contribute to receiving water exceedance. Other sources likely. Resample ASAP. Investigate, if necessary.Elevated storm drain concentration likely to have caused receiving water exceedance. Resample ASAP. Investigate, if resample confirms.Highly elevated storm drain concentration does not cause receiving water exceedance. Investigate storm drain.Storm drain concentration below 95th percentile criteria - no action necessaryUnlikely that storm drain contamination caused receiving water exceedance. Resample ASAP. Eliminate non-storm drain sources, if appropriate.95th percentile criteria160,000 MPN/ 100 mls TOXIC HOT SPOTS MONITORING IN SAN DIEGO BAY The former California Bay Protection and Toxic Cleanup (Toxic Hot Spot) Program was implemented for 10 years and identified five San Diego Bay locations that had sediment contamination causing toxicity to marine life and benthic community impairments. This program is referenced in Appendix B of the Municipal Storm Water Permit, Order No. 2001-01 and requires the Copermittees to report annually on program activities. The Toxic Hot Spot Program goals and tasks were incorporated into the Regional Board’s Pollutant Load Reduction Program for implementation incorporated into the San Diego Bay Total Maximum Daily Load (TMDL) projects. Copermittees activities that have occurred regarding this issue are organized according the Regional Board’s specific TMDL project. 1 CHOLLAS AND PALETA TMDL PROGRAM ACTIVITY SUMMARY In 1998 the sediments at the mouths of Chollas and Paleta Creeks are listed as impaired for toxicity and benthic community degradation in the Clean Water Act 303(d) list. This action requires the implementation of a Total Maximum Daily Load (TMDL) to return the waterbody segment back to water quality standards. The Regional Board initiated the TMDL in 2000 by coordinating monitoring efforts with stakeholders. A majority of the sampling and analysis work was performed by the Southern California Coastal Waters Research Project (SCCWRP) and the US Navy at the request of the Regional Board. PARTICIPATING JURISDICTIONS • City of San Diego • Port of San Diego • US Navy • Southern California Coastal Waters Research Project • San Diego Water Quality Control Board, Region 9 1.1 WATERSHED PRIORITY POLLUTANTS OR STRESSORS ADDRESSED • Metals • Benthic community impacts • Toxicity 1.2 HOW THIS ACTIVITY RELATES TO THE SAN DIEGO BAY WATERSHED This TMDL activity assessed the spatial and temporal extent of the impairments at the mouths of Chollas and Paleta Creeks. The Temporal Assessment of Chemistry, Toxicity and Benthic Communities in Sediments at the Mouths of Chollas Creek and Paleta Creek, San Diego Bay by Southern California Coastal Waters Research Project (SCCWRP) had two objectives. The first objective was to describe the temporal variability in indictors of sediment quality at the selected reference and potentially impaired sites. The second objective was to confirm the aquatic life assessment results for the July and August 2001 sampling. SCCWRP’s findings indicated contaminants were consistently found in the sediments and there was variability between the stations and five sampling events. Based upon this study, sources of contamination need to be found and eliminated and best management practices identified that will improve the sediment quality in San Diego Bay. In the fall of 2005, the Regional Board modified this TMDL project to be included in the Chollas-Paleta-Switzer Creek Mouths TMDL. This modified TMDL is incorporating the previous work at all three creek mouths because of their similarities. Additional meetings have been conducted and new stakeholders are attending. These activities will be reported in the next annual report due to said activities occurring beyond this reporting period. TASKS IMPLEMENTED DURING FY 2004-2005 The following administrative tasks were conducted as part of this TMDL program during Fiscal Year 2005: • September 17, 2004 Alternative Toxicity Study Meeting to provide comments to the US Navy regarding their draft report. • November 15, 2004 Regional Board notice that the draft The Temporal Assessment of Chemistry, Toxicity and Benthic Communities in Sediments at the Mouths of Chollas Creek and Paleta Creek, San Diego Bay by Southern California Coastal Waters Research Project was available on their website. • January 24, 2005 Regional Board solicitation for comments on the draft The Temporal Assessment of Chemistry, Toxicity and Benthic Communities in Sediments at the Mouths of Chollas Creek and Paleta Creek, San Diego Bay by Southern California Coastal Waters Research Project. • February 24, 2005 submission of comments on draft The Temporal Assessment of Chemistry, Toxicity and Benthic Communities in Sediments at the Mouths of Chollas Creek and Paleta Creek, San Diego Bay by Southern California Coastal Waters Research Project. 2 CHOLLAS CREEK DIAZINON TMDL PROGRAM ACTIVITY SUMMARY This total maximum daily load (TMDL) program is to help assess diazinon impacts on the beneficial uses of Chollas Creek. PARTICIPATING JURISDICTIONS • City of San Diego • City of Lemon Grove • City of La Mesa • County of San Diego • San Diego Unified Port District (Port of San Diego) 2.1 WATERSHED PRIORITY POLLUTANTS ADDRESSED • Pesticides (diazinon) 2.2 HOW THIS ACTIVITY RELATES TO THE SAN DIEGO BAY WATERSHED The Chollas Creek TMDL Program seeks to assess diazinon impacts on the beneficial uses of Chollas Creek through active monitoring and data collection with regards to the amount in and the sources of diazinon along the creek. Such information would directly be employed in selecting the appropriate Best Management Practices that would reduce the amount of diazinon loaded into the creek to acceptable levels. Since Chollas Creek is a natural drainage system that traverses inner-city neighborhoods within the City of San Diego from its headwaters in La Mesa and Lemon Grove to San Diego Bay, improving the water quality of the creek would ultimately positively impact the water quality of San Diego Bay. TASKS IMPLEMENTED DURING FY 2004-2005 The following administrative tasks were conducted as part of this TMDL program during Fiscal Year 2005: • The monitoring plan was prepared and submitted to the Regional Water Quality Control Board (RWQCB) as required in Investigation Order No. R9-2004-0277. • The cities of La Mesa, Lemon Grove, and San Diego, together with the County of San Diego and the San Diego Unified Port District, coordinated to conduct the required activities outlined in the August 13, 2004 Monitoring Investigation Order No. R9-2004-0277. • The first annual report for Investigation Order R9-2004-0277 was prepared and submitted to the RWQCB. • The County of San Diego executed an agreement with the State Water Resources Control Board (SWRCB) to implement the Pesticide Research and Identification of Source and Mitigation (PRISM) Grant Program. • The County of San Diego executed a Memorandum of Understanding with the City of San Diego to provide public education and outreach services and monitoring in the Chollas Creek Watershed. • The City of San Diego provided consultant services to perform the Annual Residential Survey to assess the knowledge base of area residents on pesticides and other storm water issues. • The County of San Diego coordinated activities with the University of California Extension Service (San Diego Office) regarding the preparation of pest cards, fact sheets and other educational materials. • The City of San Diego provided consultant services to update the www.ThinkBluesd.org website to include integrated pest management information. • The County of San Diego provided services to update the Project Clean Water website with integrated pest management information. • The PRISM Grant Quality Assurance Project Plan (QAPP) and the Sampling and Analysis Plan (SAP) were submitted to the Regional Board. • The City of San Diego provided consultant services to perform water quality chemistry monitoring of the first storm event as required by Investigation Order No. R9-2004-0277 of the 2004–2005 wet weather season. • The City of San Diego, as a partner in the IPM PRISM Grant, provided consultant services to perform water quality chemistry monitoring of three additional storm events during the 2004–2005 wet weather season. • The City of San Diego provided consultant services to perform focus group meetings. (Refer to the Education Activities section for a fuller description of this activity.) • The County of San Diego coordinated activities with the University of California Extension Service (San Diego Office) for Master Gardener Program to provide nursery tip cards at City Farmers Nursery and Walter Anderson’s Nursery within the watershed. • The County of San Diego coordinated activities with the University of California Extension Service (San Diego Office) for a Master Gardener Program to provide nursery tip cards at additional retail outlets within the watershed. • The City of San Diego, as a partner in the IPM PRISM Grant, provided consultant services to prepare for the next Annual Residential Survey. • The City of San Diego, as a partner in the IPM PRISM Grant, provided consultant services to prepare the Water Quality Monitoring Report. • The City of San Diego, as a partner in the IPM PRISM Grant, provided consultant services to perform sediment quality chemistry monitoring at four stations in the Chollas Creek Watershed. • The County of San Diego coordinated activities with the University of California Extension Service (San Diego Office) to provide workshops on IPM/Water Quality issues on: o April 30, 2005: San Diego Rose Society, Balboa Park o March 5, 2005: General Public, North Park Library o May 10, 2005: OASIS Adult Learning Center, Mission Valley • The County of San Diego coordinated activities with the University of California Extension Service (San Diego Office) for UCCE staff and Master Gardeners to participate in the following community events and provide information on IPM/Water Quality issues: o June 10, 2005: San Diego County Fair o June 18, 2005: Master Gardener Plant Sale, Balboa Park • The County of San Diego coordinated activities with the University of California Extension Service (San Diego Office) so that 25 Master Gardeners completed a training class that included six workshops focused on IPM and water quality issues. A pool of Advanced Master Gardeners from this class are available to support the goals of pesticide reduction in the San Diego Bay Watershed. • The County of San Diego coordinated activities with the University of California Extension Service (San Diego Office) for the continual availability of pest cards at the Cuyamaca Water Conservation Garden, beginning December 2004. In addition, the following projects helped address diazinon in Chollas Creek during Fiscal Year 2005: • Chollas Creek Water Quality Protection and Habitat Enhancement Project • San Diego Region Integrated Pest Management Education and Outreach Project (i.e., Chollas Creek Watershed Focus Groups) Æ This project stems from the Integrated Pest Management (IPM) Pesticide Research and Identification of Source and Mitigation (PRISM) Program funded through a Proposition 13 Non-Point Source Pollution Control grant agreement. The City and County of San Diego initiated the program in July 2004, which includes integrated pest management alternatives for the region with an emphasis on diazinon in the Chollas Creek Watershed. 3 CHOLLAS CREEK DISSOLVED METALS TMDL PROJECT SUMMARY On August 13, 2004, the Chollas Creek Watershed Municipal Copermittees were notified by the San Diego Regional Water Quality Control Board to incorporate dissolved metals monitoring into the Chollas Creek Diazinon TMDL Monitoring Plan (Monitoring Investigation Order No. R9-2004-0277). This regulatory requirement was implemented during the 2004–2005 wet weather season. Flow weighted composite samples were collected from three storm events as required. The first annual report is attached as an appendix to the Annual Receiving Water Monitoring Report. PARTICIPATING JURISDICTIONS • City of Lemon Grove • City of La Mesa • City of San Diego • County of San Diego • Port of San Diego 3.1 WATERSHED PRIORITY POLLUTANTS ADDRESSED • Dissolved copper, lead and zinc 3.2 HOW THIS ACTIVITY RELATES TO THE SAN DIEGO BAY WATERSHED The implementation of activities to reduce and monitor the amount of dissolved metals that cause toxicity in the creek will help comply with the California Toxics Rule and restore Chollas Creek’s designated beneficial uses of WARM (Warm Freshwater Habitat) and WILD (Wildlife Habitat). ACTIVITIES CONDUCTED DURING 2004-2005 The following activities were conducted as part of the TMDL monitoring during Fiscal Year 2005: • Preparation and submission of Quality Assurance Project Plan and Sampling and Analysis Plan to the Regional Board. • Approval of Quality Assurance Project Plan and Sampling and Analysis Plan by the Regional Board. • Water chemistry and toxicity testing sampling of the first flush storm event at four stations on October 17, 2004. • Water chemistry and toxicity testing sampling of the second flush storm event at four stations on October 27, 2004. • Water chemistry and toxicity testing sampling of the third monitoring event at four stations on February 11, 2005. • One time only creek bed sediment testing at four stations for diazinon, chlorpyrifos, dissolved cadmium, dissolved copper, dissolved lead and dissolved zinc. For more information on specific activities, refer to Appendix the Annual Receiving Water Monitoring Report. 4 CHOLLAS CREEK WATER QUALITY PROTECTION & HABITAT ENHANCEMENT PROJECT ACTIVITY SUMMARY The City of San Diego (City) Metropolitan Wastewater Department Storm Water Pollution Prevention Division is managing the design and construction of a creek restoration project in Chollas Creek funded by a $2.244 million Prop 13 grant from the State Water Resources Control Board. The project, titled “Chollas Creek Water Quality Protection & Habitat Enhancement Project,” will remove approximately 5,000 square feet of concrete and other hardscape in and adjacent to Chollas Creek and restore approximately 1.7 acres of native upland and riparian habitat along a 750 foot-long segment of the Encanto Branch of Chollas Creek. The project includes an approximately $500,000 education and outreach component to eliminate polluting practices of residents and businesses in the community. This project is part of the Chollas Creek Enhancement Program. PARTICIPATING JURISDICTIONS/ORGANIZATIONS • City of San Diego • Port of San Diego • City of La Mesa • City of Lemon Grove • San Diego Coastkeeper • Environmental Health Coalition 4.1 WATERSHED PRIORITY POLLUTANTS ADDRESSED • Pesticides • Metals • Trash 4.2 HOW THIS ACTIVITY RELATES TO THE SAN DIEGO BAY WATERSHED This project would implement one segment of the City of San Diego’s Chollas Creek Enhancement Program, a watershed-based planning effort to restore the natural functions and beneficial uses of Chollas Creek and create a linear park for the community. By removing concretized portions, widening the bed to reduce scour and flow velocities, and revegetating with native plants, the restoration effort will improve the biofiltration processes (i.e., filtering and removing pollutants from flows by plant uptake and natural filtration through soils) in the creek. The project will also create a linear park for the community so that the creek becomes a natural asset for the community to protect and not pollute. TASKS IMPLEMENTED DURING FY 2004-2005 • The City initiated the design process and completed the 90% design plans for the creek restoration project, completed the environmental review process under CEQA (California Environmental Quality Act), and met four times with the community during the design process to seek community input on the project. • The City initiated outreach programs for residents and businesses by conducting focus group surveys and establishing working groups with residents and participating businesses. 5 SAN DIEGO WATERSHEDS COMMON GROUND: SAN DIEGO BAY WATERSHED DEMONSTRATION PROJECT ACTIVITY SUMMARY The City of San Diego (City) was selected to receive Proposition 13 (Costa-Machado Act of 2000) funding for $900,000 to implement the San Diego Bay Watershed Demonstration Project. PARTICIPATING JURISDICTIONS • City of San Diego • San Diego State University • San Diego Coastkeeper 5.1 WATERSHED PRIORITY POLLUTANTS ADDRESSED • Sediment • Pesticides • Benthic community degradation 5.2 HOW THIS ACTIVITY RELATES TO THE SAN DIEGO BAY WATERSHED The San Diego Watershed Demonstration Project aims to enhance the capacity of the San Diego region to track and learn about conditions and trends associated with its water resources. Water quality data should be presented to the public in a manner that can easily be interpreted to facilitate decision-making and create better long-term understanding and stewardship of local water resources. The project intends to accomplish its goals of data acquisition, comprehension, and dissemination through a four-pronged approach: (1) establishment of a Regional Water Monitoring and Resource Center; (2) monitoring activities in support of Total Maximum Daily Load (TMDL) programs addressing benthic community degradation and sediment toxicity; (3) development of a Geographic Information System (GIS) database for water resources; and (4) creation of an interactive web-based outreach, education, and decision-making tool. The City’s primary project partners are the San Diego State University Department of Geography (for GIS and cartographic expertise and server support) and the San Diego Coastkeeper (for the regional training center). The project has broad local support from the San Diego Regional Water Quality Control Board, the San Diego Association of Governments, and the San Diego Regional Municipal Storm Water Copermittees. TASKS IMPLEMENTED DURING FY 2004-2005 The following tasks were implemented as part of the San Diego Watersheds Common Ground: San Diego Bay Watershed Demonstration Project during Fiscal Year 2005: • Memoranda of Understanding (MOUs) with project partners were signed. • Regional Water Monitoring and Resource Center: San Diego Coastkeeper worked on the establishment of the center and gearing up for the preparation of the Quality Assurance Project Plan to be submitted to the San Diego Regional Water Quality Control Board by the end of December 2005. • Monitoring activities: Storm water and sediment sampling and analysis and bioassessment studies in three drainage areas (Switzer Creek, Downtown Anchorage, and B Street/Broadway Pier) were completed. The final report is expected to be completed by January 2005. • GIS database: Compilation of hydrological information (location of streams, lakes, and known constructed channelized streams), roadways, and watershed boundaries was worked on for the database. • Interactive web-based tool: Design of the prototype web-based GIS tool continued. APPENDIX G Long Term Effectiveness Assessment Tables Table G-1. Santa Margarita WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelYsidora HA (902.10) 11% N 0 2 0 0.7 D N 0 0 0.0 D N 0 0 0.0 D N 3 3.0 A N 2 1 0 1.0 C Y 0 0 3.0 A N 0 2 1.0 C N 2 3 2.5 A 1.4 N 2 2 2.0 B N 2 0 1.0 C1.5DeLuz HA (902.20) 29% N 0 2 0 0.7 D N 0 0 0.0 D N 1 0 0.5 D Y 2 3.0 A N 3 1 0 1.3 C Y 1 0 3.0 A N 0 2 1.0 C N 1 2 1.5 C 1.4 N 2 2 2.0 B N 2 0 1.0 C1.5Pechanga HA (902.50) 12% N 2 0 1.0 C N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 1 0 0.5 D Y 0 3.0 A N 2 2.0 B N 2 2.0 B 1.3 N 2 2 2.0 B N 2 0 1.0 C1.4Aguanga HA (902.80) 28% N 2 0 1.0 C N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 1 0 0.5 D N 0 0.0 D N 2 2.0 B N 2 2.0 B 0.9 N 2 2 2.0 B N 2 0 1.0 C1.3Oakgrove HA (902.90) 20% N 2 0 1.0 C N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 1 0 0.5 D N 0 0.0 D N 2 2.0 B N 2 2.0 B 0.9 N 2 2 2.0 B N 2 0 1.0 C1.3MLS Results ABLM Results Rating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.74Percentage of Total Area012Heavy metalSanta Margarita(WMA)23Cumulative ScoreBacteria / Pathogens1.91Cumulative Sub-watershed ScoreConstituents / Stressors of Concern0002DCOil and Grease0.15D200.87 0.00Organics2.40APesticides0.80C03Sediments (SS, Turbidity, etc.)BGross Pollutants1.60B01.56NutrientsBBenthic Alterations2.00B2Toxicity1.00C Table G-2. San Luis Rey River WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelLower San Luis HA (903.10) 33% N 0 0 2 0.7 D N 0 0 0.0 D N 1 0 0.5 D Y 3 3.0 A N 3 0 0 1.0 C Y 1 0 3.0 A N 0 0 0.0 D Y 2 2 3.0 A 1.4 N 3 1 2.0 B N 1 0 0.5 D1.3Monserate HA (903.20) 30% N 0 0 2 0.7 D N 0 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 2 0 0 0.7 D N 0 0 0.0 D N 0 0 0.0 D N 3 2 2.5 A 0.7 N 2 1 1.5 C N 1 0 0.5 D0.9Warner Valley HA (903.30) 37% N 0 2 1.0 C N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 0 0 0.0 D N 0 0.0 D N 0 0.0 D N 2 2.0 B 0.6 N 2 1 1.5 C N 1 0 0.5 D0.9MLS Results ABLM Results Rating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.74120CDASan Luis Rey(WMA)0.5000 300BPesticidesDD AD2.48 1.67NutrientsGross PollutantsPercentage of Total Area0Cumulative Sub-watershed ScoreConstituents / Stressors of Concern0Cumulative Score20CHeavy metalOrganicsOil and GreaseSediments (SS, Turbidity, etc.)Bacteria / PathogensBenthic Alterations301DToxicity0.79 0.00 0.17 2.33 0.53 0.99 0.00 Table G-3. Carlsbad WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelLoma Alta HA (904.10) 5% N 1 1.0 C N D N 0 0.0 D N D N 3 D Y 2 3.0 A N 3 3.0 A Y 2 3.0 A 2.0 N D N D2.0Buena Vista HA (904.20) 11% N 0 2 1.0 C N 0 0.0 D N 0 0.0 D Y 3.0 A N 2 0 1.0 C Y 1 3.0 A N 1 1.0 C Y 2 3.0 A 1.5 N 3 3.0 A N 0 0.0 D1.5Agua Hedionda HA (904.30) 14% N 1 0 2 1.0 C N 0 0 0.0 D N 1 0 0.5 D Y 3 3.0 A N 3 3 0 2.0 B N 0 1 0.5 D N 0 1 0.5 D Y 2 3 3.0 A 1.3 N 3 2 2.5 A N 2 0 1.0 C1.6Encinas HA (904.40) 3% N 1 1.0 C N D N 1 1.0 C N D N 3 D N 1 1.0 C N 2 2.0 B N 2 2.0 B 1.4 N D N D1.4San Marcos HS (904.50) 28% N 1 2 1.5 C N 0 0.0 D N 0 0.0 D N D N 2 0 1.0 C N 1 1.0 C N 0 0.0 D Y 2 3.0 A 0.9 N 1 1.0 C N 2 2.0 B1.3Escondido Creek HA (904.60) 40% N 1 0 0 0.3 D N 0 0 0.0 D N 0 0 0.0 D Y 3 3.0 A N 3 2 0 1.7 B Y 1 0 3.0 A N 1 0 0.5 D Y 2 3 3.0 A 1.4 N 3 3 3.0 A N 1 0 0.5 D1.6MLS Results (AH)MLS Results (EC)ABLM Results (BV)ABLM Results (AH)ABLM Results (Bat) ABLM Results (SE)Rating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.74Carlsbad(WMA)1303313232000000CDD A11Percentage of Total Area00Heavy metalOrganics3Oil and GreaseSediments (SS, Turbidity, etc.)02000Benthic AlterationsToxicity20Cumulative Score03Gross PollutantsBacteria / PathogensD0.50ACumulative Sub-watershed ScoreConstituents / Stressors of Concern002000.87 0.00 0.09 3.00BCPesticidesNutrients1.33 2.04 2.9702CB2332.15 0.90 Table G-4. San Dieguito River WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelSolana Beach HA (905.10)13% N 1 0 2 1.0 C N 0 0 0.0 D N 0 0 0.0 D N 3 3.0 A N 2 0 0 0.7 D N 1 0 0.5 D Y 0 1 3.0 A Y 3 2 3.0 A 1.4 N 3 2 2.5 A N 2 2 2.0 B2.0Hodges HA (905.20) 14% N 0 0 2 0.7 D N 0 0 0.0 D N 0 0 0.0 D Y 2 3.0 A N 3 0 0 1.0 C Y 0 0 3.0 A Y 0 1 3.0 A N 2 2 2.0 B 1.6 N 2 2 2.0 B N 2 2 2.0 B1.9San Pasqual HA (905.30)20% N 0 0 2 0.7 D N 0 0 0.0 D N 0 0 0.0 D Y 2 3.0 A N 3 0 0 1.0 C Y 2 0 3.0 A Y 1 3.0 A N 1 2 1.5 C 1.5 N 2 2 2.0 B N 2 2 2.0 B1.8Santa Maria Valley HA (905.40)17% N 0 0 2 0.7 D N 0 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 0 0 0.0 D N 2 0 1.0 C N 0 1 0.5 D N 3 2 2.5 A 0.8 N 2 2 2.0 B N 2 2 2.0 B1.6Santa Ysabel HA (905.50)37% N 0 2 1.0 C N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 0 0 0.0 D N 0 0.0 D N 1 1.0 C N 2 2.0 B 0.8 N 2 2 2.0 B N 2 2 2.0 B1.6MLS Results ABLM ResultsRating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.740San Dieguito(WMA)DD A0.83PesticidesPercentage of Total AreaOil and GreaseSediments (SS, Turbidity, etc.)2.00B2.11 2.06BToxicity232D000300.00 0.00 2.47Cumulative Sub-watershed ScoreConstituents / Stressors of Concern2Cumulative Score20CHeavy metalOrganicsBenthic AlterationsCBB2NutrientsGross PollutantsBacteria / Pathogens0.42 1.24 1.8501 Table G-5. Los Peñasquitos WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelMiramar Reservoir HA (906.10)55% N 1 0 2 1.0 C N 0 0 0.0 D N 1 0 0.5 D Y 3 3.0 A N 3 1 0 1.3 C N 1 1.0 C N 1 0 0.5 D Y 3 3 3.0 A 1.3 N 3 1 2.0 B N 0 0 0.0 D1.1Poway HA (906.20) 45% N 1 0 2 1.0 C N 0 0 0.0 D N 2 0 1.0 C N 2 2.0 B N 2 1 0 1.0 C N 0 0.0 D N 0 0 0.0 D N 2 2 2.0 B 0.9 N 2 1 1.5 C N 0 0 0.0 D0.8MLS ResultsABLM ResultsRating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.74Los Penasquitos(WMA)030131000020Percentage of Total AreaCumulative ScoreCDD A CDDACumulative Sub-watershed ScoreConstituents / Stressors of Concern003Heavy metalOrganicsOil and GreaseSediments (SS, Turbidity, etc.)PesticidesNutrientsGross PollutantsBacteria / PathogensBenthic AlterationsToxicity1.00 0.00 0.73 2.55 1.18 0.55 0.28 2.55 1.78 0.00BD Table G-6. Mission Bay WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelScripps HA (906.30) 15% N 2 1 2 1.7 B N 0 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 2 2 0 1.3 C N 0 0 0.0 D N 0 2 1.0 C Y 3 2 3.0 A 1.1 N 3 3 3.0 A N 1 0 0.5 D1.5Miramar HA (906.4) 64%Y1 1 2 3.0 AN0 0 0.0 DN0 0 0.0 DN2 2.0 BN2 2 0 1.3 CY1 0 3.0 AN0 2 1.0 CY2 2 3.0 A 1.7 N 2 2 2.0 BN1 0 0.5 D1.4Tecolote HA (906.5) 21%Y1 1 2 3.0 AN0 0 0.0 DN0 0 0.0 DN3 3.0 AN2 3 0 1.7 BN0 0 0.0 DN0 2 1.0 CY2 3 3.0 A 1.5 N 2 2 2.0 BY1 0 3.0 A2.2MLS Results ABLM Results Rating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.74Benthic AlterationsMission Bay(WMA)Cumulative ScorePercentage of Total Area0200DD BC ACumulative Sub-watershed ScoreGross PollutantsBacteria / PathogensToxicity1.00 3.0030NutrientsBC21.92Constituents / Stressors of Concern331Heavy metalOrganicsOil and GreaseSediments (SS, Turbidity, etc.)1PesticidesA0302.80 0.00 0.00 2.21 1.4032.15 1.03BC Table G-7. San Diego River WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelLower San Diego HA (907.10) 40% N 1 0 0.5 D N 0 0.0 D N 0 0 0.0 D Y 3 3.0 A N 2 2 2.0 B Y 0 0 3.0 A Y 1 0 3.0 A Y 3 3 3.0 A 1.8 N 3 3.0 A N 0 0.0 D1.6San Vicente HA (907.20) 17% N 0 0 0.0 D N 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 2 2 2.0 B N 1 0 0.5 D N 0 0 0.0 D N 2 2 2.0 B 0.8 N 2 2.0 B N 0 0.0 D0.9El Capitan HA (907.30) 20% N 0 0 0.0 D N 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 3 2 2.5 A N 0 0 0.0 D N 0 0 0.0 D N 2 2 2.0 B 0.8 N 2 2.0 B N 0 0.0 D0.9Boulder Creek HA (907.40) 23% N 0 0.0 D N 0 0.0 D N 0 0.0 D N 2 2.0 B N 2 2.0 B N 0 0.0 D N 0 0.0 D N 2 2.0 B 0.8 N 2 2.0 B N 0 0.0 D0.9MLS Results ABLM Results Rating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.74Benthic AlterationsSan Diego(WMA)Cumulative ScorePercentage of Total Area030DD ABCCACumulative Sub-watershed ScoreNutrientsGross PollutantsBacteria / PathogensToxicity2.40 0.00Constituents / Stressors of Concern330D020Heavy metalOrganicsOil and GreaseSediments (SS, Turbidity, etc.)Pesticides0.20 0.00 0.00 2.40 2.10 1.29 1.20 2.40AD0 Table G-8. San Diego Bay WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelPoint Loma HA (908.10) 2% Y 1 3.0 A N D N 1 D N D N 2 2.0 B N 0 0.0 D N 0 0.0 D Y 1 3.0 A 1.6 Y 3.0 A Y 3.0 A 2.5San Diego Mesa HA (908.20)9% Y 1 3 3.0 A Y 0 3.0 A N 0 0 0.0 D N 3 3.0 A Y 3 3 3.0 A N 1 0 0.5 D N 2 2 2.0 B Y 3 3 3.0 A 2.2 Y 3 3.0 A Y 2 3.0 A 2.7National City HA (908.30) 2% N 1 1.0 C N D N 1 1.0 C N D N 3 3.0 A N 1 1.0 C N 2 2.0 B N 3 3.0 A 1.8 Y 3.0 A Y 3.0 A 2.6Lower Sweetwater HA (909.10)11% N 1 0 2 1.0 C N 0 0 0.0 D N 1 0 0.5 D N 3 3.0 A N 3 2 0 1.7 B N 1 0 0.5 D N 1 0 0.5 D Y 3 3 3.0 A 1.3 N 3 3 3.0 A N 2 0 1.0 C 1.8Middle Sweetwater HA (909.20)19% N 0 0 2 0.7 D N 0 0 0.0 D N 1 0 0.5 D N 2 2.0 B N 3 2 0 1.7 B N 0 0 0.0 D N 0 0 0.0 D N 2 2 2.0 B 0.9 N 2 2 2.0 B N 2 0 1.0 C 1.3Upper Sweetwater HA (909.30)22% N 0 0 2 0.7 D N 0 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 3 2 0 1.7 B N 2 0 1.0 C N 0 0 0.0 D N 2 2 2.0 B 0.9 N 2 2 2.0 B N 2 0 1.0 C 1.3Coronado HA (910.10) 2% N 1 1.0 C N D N 0 0.0 D N D N 2 2.0 B N 1 1.0 C N 0 0.0 D Y 2 3.0 A 1.2 N D N D 1.2Otay Valley HA (910.20) 10% N 2 2.0 B N D N 1 1.0 C N D N 3 3.0 A N 1 1.0 C N 2 2.0 B N 3 3.0 A 2.0 N D N D 2.0Dulzura HA (910.30) 22% N 0 0.0 D N D N 0 0.0 D N D N 0.0 D N 2 2.0 B N 0 0.0 D N 0 0.0 D 0.3 N D N D 0.3MLS Results (CC)MLS Results (SW)ABLM Results Rating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.74San Diego Bay(WMA)230201.59CDD A0.28 2.33 0.92000.96 0.45Percentage of Total Area3032Constituents / Stressors of Concern3003Cumulative Sub-watershed ScoreBacteria / PathogensBenthic AlterationsToxicityCumulative Score1.92 1.542Heavy metalOrganicsOil and Grease0Sediments (SS, Turbidity, etc.)PesticidesNutrientsGross PollutantsBCC1.300020B0.91BC3333 Table G-8. Tijuana River WMA303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority Level303d*Wet WeatherSedimentScore**Priority Level303d*Dry WeatherWet WeatherSedimentScore**Priority LevelTijuana Valley HA (911.10) 7% Y 1 1 0 3.0 A Y 0 0 3.0 A N 1 0 0.5 D Y 3 3.0 A Y 2 3 0 3.0 A Y 1 3 3.0 A Y 1 3 3.0 A Y 2 3 3.0 A 2.7 N 3 2 2.5 A N 3 0 1.5 C2.2Potrero HA (911.20) 18% N 1 0 0.5 D N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 2 0 1.0 C N 2 2.0 B N 2 2.0 B N 2 2.0 B 1.2 N 2 2 2.0 B N 2 0 1.0 C1.4Barrett Lake HA (911.30) 20% N 1 0 0.5 D N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 2 0 1.0 C N 2 2.0 B N 2 2.0 B N 2 2.0 B 1.2 N 2 2 2.0 B N 2 0 1.0 C1.4Monument HA (911.40) 8% N 0 1 0 0.3 D N 0 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 2 0 1.0 C N 0 2 1.0 C N 0 2 1.0 C Y 1 2 3.0 A 1.0 N 2 2 2.0 B N 2 0 1.0 C1.3Morena HA (911.50) 5% N 1 0 0.5 D N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 2 0 1.0 C N 2 2.0 B N 2 2.0 B N 2 2.0 B 1.2 N 2 2 2.0 B N 2 0 1.0 C1.4Cottonwood HA (911.60) 10% N 0 1 0 0.3 D N 0 0 0.0 D N 0 0 0.0 D N 2 2.0 B N 2 0 1.0 C N 0 2 1.0 C N 0 2 1.0 C N 1 2 1.5 C 0.9 N 2 2 2.0 B N 2 0 1.0 C1.3Cameron HA (911.70) 10% N 1 0 0.5 D N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 2 0 1.0 C N 2 2.0 B N 2 2.0 B N 2 2.0 B 1.2 N 2 2 2.0 B N 2 0 1.0 C1.4Campo HA (911.80) 23% N 1 0 0.5 D N 0 0 0.0 D N 0 0.0 D N 2 2.0 B N 2 0 1.0 C N 2 2.0 B N 2 2.0 B N 2 2.0 B 1.2 N 2 2 2.0 B N 2 0 1.0 C1.4MLS Results ABLM Results Rating***Priority LevelNotes:* = 303d listing is N (no) or Y (yes). Y automatically scores 3 points-regardless of Dry or MLS scores** = Score Calculated Based on Average of Dry Weather, Wet Weather, and Sediment data sets*** = Rating Calculated Based on Area Weighted Averages of Score ValueBlank = No Data AvailableGreen = 303d Listing ConfirmedPriority Level (Highest to Lowest)A = 2.25-3.0B = 1.50 - 2.24C = 0.75-1.49 D = 0.0 - 0.7410B1.891.03BC3CBB330232.031.89 2.103Tijuana(WMA)Oil and GreaseSediments (SS, Turbidity, etc.)DDD BPercentage of Total Area0330.64 0.20 0.03 2.07 1.13Heavy metalOrganicsCumulative Sub-watershed ScoreConstituents / Stressors of Concern000Benthic AlterationsToxicityPesticidesNutrientsGross PollutantsBacteria / PathogensCumulative Score APPENDIX H Third Party Data Table H-1. Data Collected Under SWAMP in 2002 for the Carlsbad Watershed. Shaded values either exceed water quality objectives or are potentially toxic.March April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberPhysical Conductivity uS/cm 3.97 4.35 4.63 4.71 2.18 2.29 2.30 2.35 1.63 1.93 1.96 1.83 2.71 2.83 2.75 3.01 1.91 2.28 1.97 2.72Physical Oxygen Saturation Percent 98.1 168.7 153.2 154.3 98.3 203.2 152.4 84.3 94.6 91.1 92.5 107.7 95.8 113.6 94.9 98.9 98 92.7 96.3 94.6Physical Temperature Degrees C 15.87 19.78 21.79 23.16 16.11 23.05 21.9 22.16 17.46 15.41 19.19 18.78 14.44 20.65 15.48 18.78 18.05 16.5 20.02 18.74Physical Turbidity NTU 20 Basin Plan 0.87 0.8 1 2.1 3.7 2.8 2.0 0.85 NA 1.6 3.5 0.54 0.57 0.95 0.24 1.4 3.7 1.7 4.9 8.72Physical Velocity FPS 0.518 NA NA NA 2.01 NA NA 0 2 0.48 NA NA 0.917 1.66 NA 1.34 1.44 0.495 NA 0.5Physical pH pH units 6.5-8.5 Basin Plan 7.89 8.00 7.519.977.988.588.17 8.71 7.41 8.08 8.15 6.59 7.82 8.15 7.76 7.52 8.2 8.1 8.07 7.43Inorganics Alkalinity as CaCO3 mg/L 310 298 329 298 269 240 238 267 255 288 311 275 234 237 229 229 219 241 282 241Inorganics Ammonia as N mg/L 0.07E 0.38 0.07E 0.11 0.07E 0.41 0.07E 0.098 0.07E 0.38 0.07E 0.069 0.07E 0.13 0.07E 0.071 0.07E 0.27 0.07E 0.081Inorganics Nitrate + Nitrite as N mg/L 10 Basin Plan 0.086 0.176 0.146 0.109 0.775 0.313 0.128 0.27415.2 16.8 19.4 10.11.35 1.36 1.18 0.481 0.176 0.227 0.944 0.658Inorganics Nitrogen, Total Kjeldahl mg/L 0.37E 0.5 0.37E 0.47 0.37E 0.37E 0.37E 0.43 0.37E 1.44 0.37E 0.45 0.37E 0.52 0.37E 0.34 0.37E 0.37E 0.37E 0.6Inorganics OrthoPhosphate as P mg/L 0.032 0.05 0.034 0.019 0.105 0.055 0.045 0.099 0.174 0.127 0.159 0.127 0.047 0.052 0.024 0.026 0.175 0.096 0.0920.194Inorganics Phosphorus, Total as P mg/L 2 USEPA Multi-Sector General Permit 0.04E 0.04E 0.04E <0.03 0.1 0.07 0.06 0.1 0.18 0.12 0.16 0.14 0.05 0.05 0.04E 0.036 0.15 0.12 0.12 0.38Inorganics Sulfate mg/L 250 Basin Plan 191250240 204 191259242256 280 413 394 404 327 432 449 522221293 362 373Metals Aluminum µg/L 1000 Basin Plan 1.4 5.87 1.28 <0.1 1.3 4.4 1.39 <0.1 7.49 0.676 1.86 0.805 1.21 0.998 3.65 <0.1 1.4 2.14 1.34 14.9Metals Arsenic µg/L 340/50 40 CFR 131 (a)/Basin Plan 4.94 5.63 6.33 4.85 7 7.24 2.62 7.4 4.54 4.32 1.63 3.95 4.17 4.61 1.88 3.89 12.4 2.98 13.1 3.48Metals Cadmium µg/L 4.3 40 CFR 131 (a) 0.012 <0.01 0.274 0.018 0.055 0.046 0.011 0.072 0.014 <0.01 0.028 0.021 0.055 0.045 0.031 0.078 0.026 0.059 0.271 0.083Metals Chromium µg/L 16 40 CFR 131 (a) 1.72 0.396 1.19 0.423 1.37 0.354 0.127 0.206 2.15 0.192 0.133 0.211 1.4 0.335 0.145 0.3 1.88 0.437 1.25 0.514Metals Copper µg/L 13 40 CFR 131 (a) 1.68 2.58 3.36 2.27 2.12 2.46 1.71 2.26 3.7 4.51 2.21 6.16 2.48 2.89 2.21 2.44 3.52 3.33 3.41 2.99Metals Lead µg/L 65 40 CFR 131 (a) <0.01 <0.01 2.41 0.007 <0.01 <0.01 0.015 0.036 <0.01 <0.01 <0.002 0.036 <0.01 <0.01 <0.002 0.004 <0.01 0.0204 2.41 0.058Metals Manganese µg/L 50 Basin Plan123 64.1 84.6 208 98.6 64.32.85 23.3 35.2 20.111736.876.838.1126 51 513 79.1 140 82.7Metals Nickel µg/L 470 40 CFR 131 (a) 0.67 1.99 4.43 3.14 0.516 1.45 0.427 1.55 0.724 1.27 0.544 0.916 0.561 1.53 0.664 2.75 1.56 1.33 3.65 2.87Metals Selenium µg/L 50 Basin Plan 10 12 12.7 12.3 5.53 6.08 2.54 5.25 3.59 3.67 2.05 3.22 5.82 6.52 2.14 7.74 39.7 5.56 13.6 8.31Metals Silver µg/L 3.4 40 CFR 131 (a) <0.01 <0.01 <0.008 <0.008 <0.01 <0.01 <0.008 <0.008 <0.01 <0.01 <0.008 0.014 <0.01 <0.01 0.0209 <0.008 0.01 <0.01 0.233 <0.008Metals Zinc µg/L 120 40 CFR 131 (a) 1.86 <0.1 1.32 1.58 3.98 1.34 1.48 6.62 2.15 1.18 1.72 2.22 2.04 0.496 1.73 2.7 6.3 14.7 3.78 6.75OC Pesticide Aldrin µg/L 3 40 CFR 131 (a) <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Chlordane, cis µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Chlordane, trans µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Chlordene, alpha µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Chlordene, gamma µg/L 2.4/0.1 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.007 <0.001 <0.001 <0.001 <0.001OC Pesticide DDD(o,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 0.002 <0.001OC Pesticide DDD(p,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001OC Pesticide DDE(o,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001OC Pesticide DDE(p,p') µg/L <0.001 0.005 <0.001 <0.001 <0.001 0.004 <0.001 <0.001 0.006 0.001E 0.002 0.004 <0.001 0.003 <0.001 <0.001 <0.001 0.006 0.002 0.003OC Pesticide DDMU(p,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide DDT(o,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001OC Pesticide DDT(p,p') µg/L 1.1 40 CFR 131 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.003E <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.003E <0.002 <0.002OC Pesticide Dacthal µg/L <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 0.001E <0.001 0.002 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001OC Pesticide Dieldrin µg/L 0.24 40 CFR 131 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endosulfan I µg/L 0.22 40 CFR 131 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endosulfan II µg/L 0.22 40 CFR 131 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.0028 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endosulfan sulfate µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endrin µg/L 0.086/2 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.002 <0.001<0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001OC Pesticide Endrin Aldehyde µg/L <0.002 0.003E <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002<0.002 0.008 <0.002 <0.002OC Pesticide Endrin Ketone µg/L <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002OC Pesticide HCH, alpha µg/L <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 0.0015E <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 0.0015E <0.001 <0.001 <0.001 <0.001OC Pesticide HCH, beta µg/L <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 0.0015E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide HCH, delta µg/L <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide HCH, gamma µg/L <0.001 0.001E <0.001 <0.001 <0.001 0.002 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001OC Pesticide Heptachlor µg/L 0.52/0.01 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Heptachlor epoxide µg/L 0.52/0.01 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Methoxychlor µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Mirex µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Nonachlor, cis µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Nonachlor, trans µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Oxadiazon µg/L <0.001 0.006 0.01 <0.001 0.001E 0.011 0.008 <0.001 0.001E 0.006 0.007 0.0067 0.001E 0.006 0.005 <0.001 0.112 0.063 0.025<0.001OC Pesticide Oxychlordane µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Tedion µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OP Pesticide Aspon µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Azinphos ethyl µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Azinphos methyl µg/L 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Bolstar µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Carbophenothion µg/L 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03OP Pesticide Chlorfenvinphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Chlorpyrifos µg/L 0.02 CA Dept. of Fish & Game <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Chlorpyrifos methyl µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Ciodrin(Crotoxyphos) µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Coumaphos µg/L <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04OP Pesticide Demeton-s µg/L 0.04E <0.04 <0.04 <0.04 0.04E <0.04 <0.04 <0.04 0.04E <0.04 <0.04 <0.04 0.04E <0.04 <0.04 <0.04 0.04E <0.04 <0.04 <0.04OP Pesticide Diazinon µg/L 0.08 CA Dept. of Fish & Game 0.062 0.045 0.024 <0.005 0.039 0.033 0.0330.162<0.005 0.013E 0.013E 0.017 0.032 0.013E <0.005 <0.005 <0.0050.375 0.250.062OP Pesticide Dichlofenthion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Dichlorvos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03Buena Creek - 904CBBUR1UnitsAnalyteAnalyte GroupLoma Alta Creek - 904CBLAC3SourceWQOBuena Vista Creek - 904CBBVR4San Marcos Creek - 904CBSAM3Agua Hedionda Creek - 904CBAQH6Page 1 of 6 Table H-1. Data Collected Under SWAMP in 2002 for the Carlsbad Watershed. Shaded values either exceed water quality objectives or are potentially toxic.March April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberBuena Creek - 904CBBUR1UnitsAnalyteAnalyte GroupLoma Alta Creek - 904CBLAC3SourceWQOBuena Vista Creek - 904CBBVR4San Marcos Creek - 904CBSAM3Agua Hedionda Creek - 904CBAQH6OP Pesticide Dicrotophos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03OP Pesticide Dimethoate µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Dioxathion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Disulfoton µg/L 0.138 0.125 0.03E <0.01 0.03E 0.03E 0.03E <0.01 0.03E <0.01 <0.01 <0.01 0.03E 0.03E <0.01 <0.01 <0.01 0.125 0.05 <0.01OP Pesticide Ethion µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Ethoprop µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Famphur µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fenchlorphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fenitrothion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fensulfothion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fenthion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fonofos (Dyfonate) µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Leptophos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Malathion µg/L 0.43 CA Dept. of Fish & Game <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Merphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Methidathion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Mevinphos µg/L 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03OP Pesticide Molinate µg/L 20 Basin Plan <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1OP Pesticide Naled(Dibrom) µg/L 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03OP Pesticide Parathion, Ethyl µg/L 0.065 40 CFR 131 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03OP Pesticide Parathion, Methyl µg/L 0.065 40 CFR 131 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.03E <0.01 <0.01OP Pesticide Phorate µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Phosmet µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Phosphamidon µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Sulfotep µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Terbufos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Tetrachlorvinphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Thiobencarb µg/L 70 Basin Plan <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1OP Pesticide Thionazin µg/L <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04OP Pesticide Tokuthion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Trichlorfon µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Trichloronate µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03Trianzine Herbicides Ametryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Atraton µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Atrazine µg/L 3 Basin Plan 0.10 <0.02 <0.02 <0.02 0.035E <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 0.035E <0.02 <0.02 <0.02 0.13 0.035E <0.02 <0.02Trianzine Herbicides Prometon µg/L <0.02 0.035E 0.112 0.045 <0.02 <0.02 <0.02 0.035 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Prometryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Propazine µg/L <0.02 <0.02 0.035E <0.02 <0.02 <0.02 0.035E <0.02 <0.02 0.035E <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 0.035E <0.02Trianzine Herbicides Secbumeton µg/L 0.43 0.035E <0.02 <0.02 0.20 <0.02 <0.02 <0.02 0.035E <0.02 <0.02 <0.02 0.035E <0.02 <0.02 <0.02 0.34 0.262 0.75 <0.02Trianzine Herbicides Simazine µg/L 4 Basin Plan <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Simetryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02<0.02Trianzine Herbicides Terbuthylazine µg/L 0.61 <0.02 <0.02 <0.02 0.25 0.287 <0.02 <0.02 0.035E <0.02 <0.02 <0.02 0.13 0.175 <0.02 <0.02 0.5 2.5 0.422<0.02Trianzine Herbicides Terbutryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02PAHs Acenaphthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Acenaphthylene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Anthracene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 0.035E <0.02 <0.0125 <0.02 0.035E <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Benz(a)anthracene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Benzo(a)pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Benzo(b)fluoranthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Benzo(e)pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Benzo(g,h,i)perylene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Benzo(k)fluoranthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Biphenyl µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Chrysene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Dibenz(a,h)anthracene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02<0.02 <0.0125PAHs Dimethylnaphthalene, 2,6- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Fluoranthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Fluorene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Indeno(1,2,3-c,d)pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Methylnaphthalene, 1- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02<0.02 <0.0125PAHs Methylnaphthalene, 2- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02<0.02 <0.0125PAHs Naphthalene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 0.035E <0.02 <0.0125 <0.02 0.035E <0.02 <0.0125 <0.02 0.035E <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Perylene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Phenanthrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 0.035E <0.02 <0.0125 <0.02 0.035E <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PAHs Trimethylnaphthalene, 2,3,5- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125PCBs PCB 005 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 008 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 015 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 018 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 027 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001Page 2 of 6 Table H-1. Data Collected Under SWAMP in 2002 for the Carlsbad Watershed. Shaded values either exceed water quality objectives or are potentially toxic.March April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberBuena Creek - 904CBBUR1UnitsAnalyteAnalyte GroupLoma Alta Creek - 904CBLAC3SourceWQOBuena Vista Creek - 904CBBVR4San Marcos Creek - 904CBSAM3Agua Hedionda Creek - 904CBAQH6PCBs PCB 028 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 029 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 031 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 033 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 044 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 049 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 052 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 056 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 060 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 066 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 070 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 074 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 087 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 095 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 097 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 099 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 101 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 105 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 110 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 114 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 118 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 128 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 137 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 138 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 141 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 149 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 151 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 153 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 156 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 157 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 158 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 170 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 174 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 177 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 180 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 183 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 187 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 189 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 194 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 195 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 200 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 201 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 203 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 206 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 209 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001Toxicity Ceriodaphnia dubia Survival Percent 80 80 50 (b) 100 100 100 90 100 100 100 90 100 100 100 100 100 100090 100Toxicity Ceriodaphnia dubia Reproduction Num/Female14 8 822 22 24 161124 18 1711 17 16 11 1028 -88 27 19Toxicity Hyalella azteca Survival Percent 90 86 9948 53 1 24 21945691 75 802399 7313 157554Toxicity Hyalella azteca Growth mg/ind 0.263 0.194(c) 0.251 0.229 0.1180.050.114 (b) 0.348 0.185(c)0.150.21(c)0.20.13(c) 0.209 0.2070.220.108 0.367 0.1440.208Toxicity Selenastrum capricornutum Growth cells/ml1128000 1218000 938000 7430003823000(c)3963000 3613000 37680004438000 410600028380007803000(c)2733000 2648000 2113000 2793000 2933000 34380005048000 7458000Notes:Concentrations noted with E are estimated as midway between the MDL and the RL.(a) WQO for metals based on hardness of 100 mg/L CaCO3(b) Below threshold value, but not significantly different from negative control.(c) Above threshold value, but significantly different from negative control.Shaded toxicity results are both significantly different from negative control and below threshold value.Page 3 of 6 Table H-1. Data Collected Under SWAMP in 2002 for the Carlsbad Watershed. Shaded values either exceed water quality objectives or are potentially toxic.Physical Conductivity uS/cmPhysical Oxygen Saturation PercentPhysical Temperature Degrees CPhysical Turbidity NTU 20 Basin PlanPhysical Velocity FPSPhysical pH pH units 6.5-8.5 Basin PlanInorganics Alkalinity as CaCO3 mg/LInorganics Ammonia as N mg/LInorganics Nitrate + Nitrite as N mg/L 10 Basin PlanInorganics Nitrogen, Total Kjeldahl mg/LInorganics OrthoPhosphate as P mg/LInorganics Phosphorus, Total as P mg/L 2 USEPA Multi-Sector General PermitInorganics Sulfate mg/L 250 Basin PlanMetals Aluminum µg/L 1000 Basin PlanMetals Arsenic µg/L 340/50 40 CFR 131 (a)/Basin PlanMetals Cadmium µg/L 4.3 40 CFR 131 (a)Metals Chromium µg/L 16 40 CFR 131 (a)Metals Copper µg/L 13 40 CFR 131 (a)Metals Lead µg/L 65 40 CFR 131 (a)Metals Manganese µg/L 50 Basin PlanMetals Nickel µg/L 470 40 CFR 131 (a)Metals Selenium µg/L 50 Basin PlanMetals Silver µg/L 3.4 40 CFR 131 (a)Metals Zinc µg/L 120 40 CFR 131 (a)OC Pesticide Aldrin µg/L 3 40 CFR 131 (a)OC Pesticide Chlordane, cis µg/LOC Pesticide Chlordane, trans µg/LOC Pesticide Chlordene, alpha µg/LOC Pesticide Chlordene, gamma µg/L 2.4/0.1 40 CFR 131/Basin PlanOC Pesticide DDD(o,p') µg/LOC Pesticide DDD(p,p') µg/LOC Pesticide DDE(o,p') µg/LOC Pesticide DDE(p,p') µg/LOC Pesticide DDMU(p,p') µg/LOC Pesticide DDT(o,p') µg/LOC Pesticide DDT(p,p') µg/L 1.1 40 CFR 131OC Pesticide Dacthal µg/LOC Pesticide Dieldrin µg/L 0.24 40 CFR 131OC Pesticide Endosulfan I µg/L 0.22 40 CFR 131OC Pesticide Endosulfan II µg/L 0.22 40 CFR 131OC Pesticide Endosulfan sulfate µg/LOC Pesticide Endrin µg/L 0.086/2 40 CFR 131/Basin PlanOC Pesticide Endrin Aldehyde µg/LOC Pesticide Endrin Ketone µg/LOC Pesticide HCH, alpha µg/LOC Pesticide HCH, beta µg/LOC Pesticide HCH, delta µg/LOC Pesticide HCH, gamma µg/LOC Pesticide Heptachlor µg/L 0.52/0.01 40 CFR 131/Basin PlanOC Pesticide Heptachlor epoxide µg/L 0.52/0.01 40 CFR 131/Basin PlanOC Pesticide Methoxychlor µg/LOC Pesticide Mirex µg/LOC Pesticide Nonachlor, cis µg/LOC Pesticide Nonachlor, trans µg/LOC Pesticide Oxadiazon µg/LOC Pesticide Oxychlordane µg/LOC Pesticide Tedion µg/LOP Pesticide Aspon µg/LOP Pesticide Azinphos ethyl µg/LOP Pesticide Azinphos methyl µg/LOP Pesticide Bolstar µg/LOP Pesticide Carbophenothion µg/LOP Pesticide Chlorfenvinphos µg/LOP Pesticide Chlorpyrifos µg/L 0.02 CA Dept. of Fish & GameOP Pesticide Chlorpyrifos methyl µg/LOP Pesticide Ciodrin(Crotoxyphos) µg/LOP Pesticide Coumaphos µg/LOP Pesticide Demeton-s µg/LOP Pesticide Diazinon µg/L 0.08 CA Dept. of Fish & GameOP Pesticide Dichlofenthion µg/LOP Pesticide Dichlorvos µg/LUnitsAnalyteAnalyte GroupSourceWQOMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June September6.51 6.05 5.15 28.58 3.45 4.49 4.50 3.84 4.65 4.93 4.63 4.57 1.91 1.96 1.86 1.82 2.16 2.36 2.28 2.0153.9 134.3 56.1 40.8 70.9 89.5 72.4 82.8 98.6 124.1 84.5 95.8 100 101.5 143.3 126.5 80.1 67.8 84.1 102.517.19 25.06 19.08 23.4 13.23 15.83 15.8 18 18.75 20.51 19.54 21.17 12.1 16.31 21.8 19.15 15.38 15.21 18.01 18.885.3 3.5 6.97224.4 7 6.45 4.7 2 1.6 1.2 5.6 0.81 0.4 0.74 2.4 NA 6.6 6.4 9.42NA NA NA NA 0.255 NA NA NA 0.707 1.08 NA 0.456 1.74 0.768 0.562 0.342 0.876 0.788 0.59 1.477.72 7.89 7.65 7.56 7.61 7.49 7.588.927.76 7.6 7.529.06 8.548.188.777.00 NA 7.68 7.9711.62220 234 241 205 262 268 275 259 158 154 155 154 289 295 257 286 276 285 252 2480.13 0.24 0.07E 0.11 0.07E 0.32 0.07E 0.077 0.07E 0.38 0.07E 0.2 0.07E 0.07E 0.07E 0.061 0.07E 0.07E 0.07E 0.0750.274 0.245 0.333 0.239 0.298 0.513 0.442 0.41331.4 38 40.8 40.36.38 6.91 6.16 7.65 2.5 2.85 1.0 1.50.68 0.58 0.79 0.69 0.37E 0.72 0.37E 0.64 0.37E 0.8 0.37E 0.69 0.37E 0.37E 0.57 0.38 0.37E 0.56 0.5 0.380.186 0.19 0.221 0.207 0.116 0.161 0.215 0.32 0.126 0.139 0.136 0.148 0.12 0.074 0.025 0.0864 0.126 0.128 0.096 0.0880.27 0.23 0.28 0.26 0.18 0.23 0.31 0.38 0.16 0.14 0.19 0.18 0.12 0.08 0.04E 0.138 0.15 0.16 0.13 0.12577 654 832 1700 683 926 938 869 418 591 542 516 326 426 390 372 332 507 454 4383.54 3.05 24.3 <0.1 1.1 1.57 6.2 0.427 3.02 2.82 3.62 1.57 1.04 0.852 6.81 <0.1 5.94 3.9 1 32.92.77 5.91 2.29 14 4.33 4.28 6.08 3.84 5.13 5.46 6.92 4.28 2.08 1.64 5.66 1.7 2.19 1.87 1.98 2.020.116 <0.01 0.163 0.057 0.011 <0.01 0.048 0.03 0.093 0.053 0.053 0.083 0.039 0.016 0.059 0.046 0.046 0.048 0.017 0.0651.95 0.443 1.89 1.58 3.99 0.465 0.37 0.503 2.41 0.684 0.334 0.736 4.58 1.38 0.396 0.93 3.8 0.431 0.118 1.194.03 3.14 4.25 8.92 3.3 3.7 4.31 3.6 3.49 4.16 4.76 4.04 3.02 3.33 4.18 2.72 2.94 3.17 2.06 2.450.497 <0.01 0.279 0.011 <0.01 <0.01 0.072 0.054 0.018 0.045 0.044 0.059 0.013 <0.01 0.052 0.036 <0.01 <0.01 <0.002 0.02746.749630.2594 246 278 86.7 205 12521.568.711.4 13 2.659514.9131 153 116 881.37 2.55 2.12 1.97 2.2 3.45 2.17 4.05 2.23 3.02 2.17 2.25 0.698 0.686 2.48 1.84 0.638 1.19 0.594 2.134.89 15.8 3.757.210.5 10.2 8.09 8.89 17.7 19.5 6.62 15.2 5.65 4.36 7.66 5.08 5.46 5.09 1.72 5.55<0.01 <0.01 0.049 0.0218 <0.01 0.0176 <0.008 <0.008 <0.01 <0.01 <0.008 0.016 <0.01 <0.01 <0.008 <0.008 <0.01 <0.01 <0.008 <0.00827.9 3.69 15.9 7.16 12.3 11.6 4.22 16.6 13.5 7.48 3.42 8.83 9.74 4.67 3.75 4.38 3.14 2.29 1.39 2.75<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.006<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 0.002 <0.001 <0.001 <0.001 0.01 <0.001 <0.001 <0.001 0.002 0.001E <0.001 <0.001 0.003 <0.001 <0.001 <0.001 0.002 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.003E <0.002 0.003E <0.002 <0.002 <0.002 0.003E <0.002 <0.002 <0.002 0.003E <0.002<0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 0.001E <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 0.006 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.004 <0.001 <0.001 <0.001 0.004<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.002 0.003E <0.002 <0.002 <0.002 0.007 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002<0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002<0.001 <0.001 <0.001 0.005 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 0.001E <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.016 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 0.002 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.0010.017 0.015 0.007 <0.001 0.142 0.057 0.053 <0.001 1.86 0.077 <0.001 <0.001 0.024 0.013 0.014 <0.001 0.018 0.013 0.011 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02<0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04<0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.040.054 0.037 0.037 0.013E0.40.0632 0.051 0.04 0.053 0.0225 0.03 0.0179 0.0370.3250.037 0.029 0.0650.2250.013E 0.013E<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03Escondido Creek - 904CBESC8Cottonwood Creek - 904CBCWC2San Marcos Creek - 904CBSAM6Escondido Creek - 904CBESC5Encinitas Creek - 904CBENC2Page 4 of 6 Table H-1. Data Collected Under SWAMP in 2002 for the Carlsbad Watershed. Shaded values either exceed water quality objectives or are potentially toxic.UnitsAnalyteAnalyte GroupSourceWQOOP Pesticide Dicrotophos µg/LOP Pesticide Dimethoate µg/LOP Pesticide Dioxathion µg/LOP Pesticide Disulfoton µg/LOP Pesticide Ethion µg/LOP Pesticide Ethoprop µg/LOP Pesticide Famphur µg/LOP Pesticide Fenchlorphos µg/LOP Pesticide Fenitrothion µg/LOP Pesticide Fensulfothion µg/LOP Pesticide Fenthion µg/LOP Pesticide Fonofos (Dyfonate) µg/LOP Pesticide Leptophos µg/LOP Pesticide Malathion µg/L 0.43 CA Dept. of Fish & GameOP Pesticide Merphos µg/LOP Pesticide Methidathion µg/LOP Pesticide Mevinphos µg/LOP Pesticide Molinate µg/L 20 Basin PlanOP Pesticide Naled(Dibrom) µg/LOP Pesticide Parathion, Ethyl µg/L 0.065 40 CFR 131OP Pesticide Parathion, Methyl µg/L 0.065 40 CFR 131OP Pesticide Phorate µg/LOP Pesticide Phosmet µg/LOP Pesticide Phosphamidon µg/LOP Pesticide Sulfotep µg/LOP Pesticide Terbufos µg/LOP Pesticide Tetrachlorvinphos µg/LOP Pesticide Thiobencarb µg/L 70 Basin PlanOP Pesticide Thionazin µg/LOP Pesticide Tokuthion µg/LOP Pesticide Trichlorfon µg/LOP Pesticide Trichloronate µg/LTrianzine Herbicides Ametryn µg/LTrianzine Herbicides Atraton µg/LTrianzine Herbicides Atrazine µg/L 3 Basin PlanTrianzine Herbicides Prometon µg/LTrianzine Herbicides Prometryn µg/LTrianzine Herbicides Propazine µg/LTrianzine Herbicides Secbumeton µg/LTrianzine Herbicides Simazine µg/L 4 Basin PlanTrianzine Herbicides Simetryn µg/LTrianzine Herbicides Terbuthylazine µg/LTrianzine Herbicides Terbutryn µg/LPAHs Acenaphthene µg/LPAHs Acenaphthylene µg/LPAHs Anthracene µg/LPAHs Benz(a)anthracene µg/LPAHs Benzo(a)pyrene µg/LPAHs Benzo(b)fluoranthene µg/LPAHs Benzo(e)pyrene µg/LPAHs Benzo(g,h,i)perylene µg/LPAHs Benzo(k)fluoranthene µg/LPAHs Biphenyl µg/LPAHs Chrysene µg/LPAHs Dibenz(a,h)anthracene µg/LPAHs Dimethylnaphthalene, 2,6- µg/LPAHs Fluoranthene µg/LPAHs Fluorene µg/LPAHs Indeno(1,2,3-c,d)pyrene µg/LPAHs Methylnaphthalene, 1- µg/LPAHs Methylnaphthalene, 2- µg/LPAHs Naphthalene µg/LPAHs Perylene µg/LPAHs Phenanthrene µg/LPAHs Pyrene µg/LPAHs Trimethylnaphthalene, 2,3,5- µg/LPCBs PCB 005 µg/LPCBs PCB 008 µg/LPCBs PCB 015 µg/LPCBs PCB 018 µg/LPCBs PCB 027 µg/LMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberEscondido Creek - 904CBESC8Cottonwood Creek - 904CBCWC2San Marcos Creek - 904CBSAM6Escondido Creek - 904CBESC5Encinitas Creek - 904CBENC2<0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.030.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.030.03E 0.03E 0.073 <0.01 0.113 0.095 0.074 <0.01 0.03E 0.03E 0.03E <0.01 0.03E 0.03E 0.03E <0.01 0.03E 0.03E 0.03E <0.01<0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 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0.035E <0.02 <0.02 <0.02 0.035E <0.02 0.1 <0.02 0.167 <0.02 0.12 <0.02 0.14 <0.02<0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02<0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.020.035E 0.875 0.55 <0.02 0.5 1.65 0.55 0.035E <0.02 <0.02 0.035E <0.02 0.035E <0.02 0.187 <0.02 0.15 0.035E 0.15 <0.02<0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.020.035E <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.01250.08 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 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<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.01250.025 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.01250.035E 0.035E <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.01250.08 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001Page 5 of 6 Table H-1. Data Collected Under SWAMP in 2002 for the Carlsbad Watershed. Shaded values either exceed water quality objectives or are potentially toxic.UnitsAnalyteAnalyte GroupSourceWQOPCBs PCB 028 µg/LPCBs PCB 029 µg/LPCBs PCB 031 µg/LPCBs PCB 033 µg/LPCBs PCB 044 µg/LPCBs PCB 049 µg/LPCBs PCB 052 µg/LPCBs PCB 056 µg/LPCBs PCB 060 µg/LPCBs PCB 066 µg/LPCBs PCB 070 µg/LPCBs PCB 074 µg/LPCBs PCB 087 µg/LPCBs PCB 095 µg/LPCBs PCB 097 µg/LPCBs PCB 099 µg/LPCBs PCB 101 µg/LPCBs PCB 105 µg/LPCBs PCB 110 µg/LPCBs PCB 114 µg/LPCBs PCB 118 µg/LPCBs PCB 128 µg/LPCBs PCB 137 µg/LPCBs PCB 138 µg/LPCBs PCB 141 µg/LPCBs PCB 149 µg/LPCBs PCB 151 µg/LPCBs PCB 153 µg/LPCBs PCB 156 µg/LPCBs PCB 157 µg/LPCBs PCB 158 µg/LPCBs PCB 170 µg/LPCBs PCB 174 µg/LPCBs PCB 177 µg/LPCBs PCB 180 µg/LPCBs PCB 183 µg/LPCBs PCB 187 µg/LPCBs PCB 189 µg/LPCBs PCB 194 µg/LPCBs PCB 195 µg/LPCBs PCB 200 µg/LPCBs PCB 201 µg/LPCBs PCB 203 µg/LPCBs PCB 206 µg/LPCBs PCB 209 µg/LToxicity Ceriodaphnia dubia Survival PercentToxicity Ceriodaphnia dubia Reproduction Num/FemaleToxicity Hyalella azteca Survival PercentToxicity Hyalella azteca Growth mg/indToxicity Selenastrum capricornutum Growth cells/mlNotes:Concentrations noted with E are estimated as midway between the MDL and the RL.(a) WQO for metals based on hardness of 100 mg/L CaCO3(b) Below threshold value, but not significantly different from negative control.(c) Above threshold value, but significantly different from negative control.Shaded toxicity results are both significantly different from negative control and below threshold value.March April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberMarch April June SeptemberEscondido Creek - 904CBESC8Cottonwood Creek - 904CBCWC2San Marcos Creek - 904CBSAM6Escondido Creek - 904CBESC5Encinitas Creek - 904CBENC2<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001NA 100 900090 100 100 100 100 100 100 10030100 90 100 80 100 90NA73NA NA11 1221 17581133 24 22 22 33 30 29 187621 26 29857481(c) 9034 68 25 1071(c) 81(c) 91 84 90 81(c) 78440.287 0.258 0.123 0.27 0.1510.0910.1330.2110.154(c) 0.186 20 0.17500.131(c)0.1480.23 0.22(c) 0.2210.150.252(c) 0.2642468000 1768000 1568000 2148000 46830004813000 4198000(c) 66780001878000 3183000 38630007313000 5098000(c) 5938000 4818000 8593000 5378000(c) 5623000(c) 4148000(c) 7553000(c)Page 6 of 6 Table H-2. Data Collected Under SWAMP in 2002 for the Los Peñasquitos Watershed. Shaded values either exceed water quality objectives or are potentially toxic.March April June September March April June September March April June September March April June September March April June SeptemberPhysical Conductivity uS/cm 3.336 0.585 3.506 3.387 2.977 0.475 3.312 3.254 2.593 2.766 2.948 2.863 2.774 1.456 3.021 3.363 3.077 5.965 4.977Physical Oxygen Saturation Percent 100 110.5 117.9 161.8 100 108.7 115.1 195.6 97.1 64.6 54.8 92 100 101.5 147.6 122.2 100 87 64.1Physical Temperature Degrees C 21.4 18.63 24.4 29.36 18.25 18.34 22.54 22.42 12.82 14.63 19.34 18.82 15.44 15.93 20.17 27.95 15.19 16.23 17.61Physical Turbidity NTU 20 Basin Plan 1.3358.9 2.43 5.9453.16 2.25 0.5 2 5.3 7.2 0.711100.75232.1 5.3 15Physical Velocity FPS 1.22 0.614 0.339 0 1.26 1.66 2.68 <88 0.758 <88 <88 1.89 1.12 <88 2.14 0.47 <88 1.33 <88Physical pH pH units 6.5-8.5 Basin Plan8.678.12 8.06 7.46 8.22 7.69 7.9 7.89 8.04 7.64 7.7 7.58.667.54 8.33 7.5 7.85 7.32 7.26Inorganics Alkalinity as CaCO3 mg/L 143 51.2 293 144 199 48.6 211 206 308 310 314 316 195 125 202 192 244 324 342Inorganics Ammonia as N mg/L 0.07E 0.11 0.07E 0.062 0.07E 0.22 0.07E 0.062 0.11 0.07E 0.07E 0.062 0.07E 0.26 0.07E 0.071 0.07E 0.16 0.07EInorganics Nitrate + Nitrite as N mg/L 10 Basin Plan 0.075 0.994 0.09 0.059 0.145 0.946 0.088 0.056 0.866 1.35 0.84 2.35 0.08 1.99 0.081 0.064 0.0440.11 0.122Inorganics Nitrogen, Total Kjeldahl mg/L 0.37E 0.66 0.37E 0.5 0.37E 1.24 0.37E <0.25 0.5 0.56 0.58 0.57 0.37E 2.72 0.37E 0.42 0.37E 0.37E 0.37EInorganics OrthoPhosphate as P mg/L 0.015 0.04 0.095 0.005 0.024 0.088 0.018 0.009 0.071 0.07 0.049 0.067 0.014 0.148 0.011 0.0381 0.023 0.034 0.014Inorganics Phosphorus, Total as P mg/L 2 USEPA Multi-Sector General Permit 0.04E 0.17 0.12 0.055 0.04E 0.24 0.04E <0.03 0.07 0.07 0.06 0.117 0.04E 0.75 0.04E 0.071 0.04E 0.06 0.05Inorganics Sulfate mg/L 250 Basin Plan746149490 1000 641118950 918210272 260 275 554 377 807 928 798 1500 1390Metals Aluminum µg/L 1000 Basin Plan 1.34 10.7 12.1 1.91 1.28 11.8 12.3 2.81 1.87 4.39 2.69 1.35 1.31 17.7 12.3 28 0.934 1.9 53Metals Arsenic µg/L 340/50 40 CFR 131 (a)/Basin Plan 3.55 2.45 8.29 3.1 3.31 2.58 8.28 2.91 3.02 2.76 5.61 3.37 2.64 3.61 8.28 3.63 3.86 5.46 5.63Metals Cadmium µg/L 4.3 40 CFR 131 (a) <0.01 0.015 0.109 0.015 0.012 0.021 0.041 0.019 0.010 <0.01 0.073 0.031 0.032 0.037 0.041 0.037 0.017 <0.01 0.042Metals Chromium µg/L 16 40 CFR 131 (a) 1.56 0.782 0.748 0.254 1.84 0.822 0.877 0.267 4.25 0.215 0.436 0.347 1.76 0.829 0.877 0.407 1.79 0.393 0.478Metals Copper µg/L 13 40 CFR 131 (a) 4.7 4.57 7.03 4.66 3.69 4.74 3.22 3.94 1.73 1.53 3.62 2.63 5.86 7.69 3.22 4.94 3.95 4.94 4.34Metals Lead µg/L 65 40 CFR 131 (a) <0.01 0.187 0.049 0.024 <0.01 0.151 0.152 0.006 <0.01 <0.01 0.015 0.042 <0.01 0.294 0.152 0.046 <0.01 <0.01 0.059Metals Manganese µg/L 50 Basin Plan 15.4 43.8 37.7 26.9103 71.3 186 94.6 136 120 170 1704.98221 18617.1157 279 74Metals Nickel µg/L 470 40 CFR 131 (a) 0.343 2.59 1.84 3.31 0.154 2.52 2.64 2.65 0.858 1.05 1.73 4.1 2.36 5.45 2.64 5.35 0.953 2.01 2.44Metals Selenium µg/L 50 Basin Plan 7.94 1.3 5.27 8.61 7.71 0.868 7.3 7.61 6.33 6.06 5.12 7.05 6.23 4.92 7.3 7.19 10.4 17.7 6.34Metals Silver µg/L 3.4 40 CFR 131 (a) <0.01 <0.01 0.0109 <0.008 <0.01 <0.01 0.0151 <0.008 <0.01 0.0178 <0.008 <0.008 <0.01 <0.01 0.0151 0.0112 <0.010.0103 <0.008Metals Zinc µg/L 120 40 CFR 131 (a) 4.53 15.7 6.41 4.75 5.67 23 4.97 4.26 4.93 3.58 3.33 8.01 8.62 38 4.97 5.39 6.34 5.86 2.48OC Pesticide Aldrin µg/L 3 40 CFR 131 (a) <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.0010.003 <0.001 <0.001 <0.001OC Pesticide Chlordane, cis µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Chlordane, trans µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Chlordene, alpha µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.012 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001 <0.001OC Pesticide Chlordene, gamma µg/L 2.4/0.1 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 0.005 <0.001 0.001E <0.001 <0.001 <0.001 <0.001OC Pesticide DDD(o,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001OC Pesticide DDD(p,p') µg/L <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001OC Pesticide DDE(o,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001OC Pesticide DDE(p,p') µg/L <0.001 0.038 <0.001 <0.001 <0.001 0.031 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 0.035 <0.001 <0.001 <0.001 0.001E <0.001OC Pesticide DDMU(p,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide DDT(o,p') µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001<0.001 <0.001OC Pesticide DDT(p,p') µg/L 1.1 40 CFR 131 <0.002 <0.002 <0.002 <0.002 0.003E <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.003E <0.002 <0.002 <0.002 <0.002OC Pesticide Dacthal µg/L <0.001 0.001E <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Dieldrin µg/L 0.24 40 CFR 131 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endosulfan I µg/L 0.22 40 CFR 131 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endosulfan II µg/L 0.22 40 CFR 131 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.004 <0.001 <0.001 <0.001 0.006 <0.001 0.001E <0.001OC Pesticide Endosulfan sulfate µg/L <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endrin µg/L 0.086/2 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Endrin Aldehyde µg/L <0.002 0.003E <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002<0.002 <0.002 <0.002OC Pesticide Endrin Ketone µg/L <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002OC Pesticide HCH, alpha µg/L <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.038 <0.001 <0.001<0.001 <0.001OC Pesticide HCH, beta µg/L <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 0.006 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide HCH, delta µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide HCH, gamma µg/L <0.001 <0.001 <0.001 <0.001 <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Heptachlor µg/L 0.52/0.01 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Heptachlor epoxide µg/L 0.52/0.01 40 CFR 131/Basin Plan <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Methoxychlor µg/L <0.001 0.001E <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Mirex µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Nonachlor, cis µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Nonachlor, trans µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Oxadiazon µg/L 0.032 0.072 <0.001 0.0182 0.027 0.053 0.052 0.0209 0.001E 0.009 <0.001 0.01 0.145 0.090 0.138 0.025 0.100 0.045 0.055OC Pesticide Oxychlordane µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OC Pesticide Tedion µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001OP Pesticide Aspon µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Azinphos ethyl µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Azinphos methyl µg/L <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Bolstar µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Carbophenothion µg/L 0.058 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03OP Pesticide Chlorfenvinphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Chlorpyrifos µg/L 0.02 CA Dept. of Fish & Game <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Chlorpyrifos methyl µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Ciodrin(Crotoxyphos) µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Coumaphos µg/L <0.04 <0.04 <0.04 <0.04 <0.04 0.05E <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04OP Pesticide Demeton-s µg/L <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04OP Pesticide Diazinon µg/L 0.08 CA Dept. of Fish & Game 0.0310.0950.02 <0.005 0.0320.1070.013E 0.013E 0.045 0.013E 0.046 0.0550.123 0.2080.02 0.033 0.079 0.02 0.013EOP Pesticide Dichlofenthion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Dichlorvos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Dicrotophos µg/L 0.06 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03OP Pesticide Dimethoate µg/L <0.03 0.075 0.062 <0.03 <0.03 0.1 <0.03 <0.03 <0.03 0.04E 0.09 <0.03 <0.03 0.062 <0.03 <0.03 <0.03 0.04E <0.03OP Pesticide Dioxathion µg/L 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03OP Pesticide Disulfoton µg/L 0.03E 0.215 0.03E <0.01 0.03E 0.22 0.03E <0.01 0.03E 0.03E 0.03E <0.01 0.074 0.106 0.03E <0.01 0.091 0.03E 0.03EOP Pesticide Ethion µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Ethoprop µg/L <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03Rose Canyon Creek - 906LPLRSC4 Tecolote Creek - 906LPLTEC3Dry, no sampleSourceLos Peñasquitos Creek - 906LPLC6 Soledad Canyon Creek - 906LPSOL2 Poway Creek - 906LPLPOW2Analyte Group Analyte Units WQOPage 1 of 3 Table H-2. Data Collected Under SWAMP in 2002 for the Los Peñasquitos Watershed. Shaded values either exceed water quality objectives or are potentially toxic.March April June September March April June September March April June September March April June September March April June SeptemberRose Canyon Creek - 906LPLRSC4 Tecolote Creek - 906LPLTEC3SourceLos Peñasquitos Creek - 906LPLC6 Soledad Canyon Creek - 906LPSOL2 Poway Creek - 906LPLPOW2Analyte Group Analyte Units WQOOP Pesticide Famphur µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fenchlorphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fenitrothion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fensulfothion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fenthion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Fonofos (Dyfonate) µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02OP Pesticide Leptophos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Malathion µg/L 0.43 CA Dept. of Fish & Game <0.03 0.36 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Merphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Methidathion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Mevinphos µg/L <0.03 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.0504 <0.03 <0.03 <0.03 0.04E <0.03OP Pesticide Molinate µg/L 20 Basin Plan <0.1 0.1E <0.1 <0.1 <0.1 0.1E <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 0.1E <0.1 <0.1 <0.1 <0.1 <0.1OP Pesticide Naled(Dibrom) µg/L 0.04E 0.04E <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E 0.04E <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Parathion, Ethyl µg/L 0.065 40 CFR 131 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03<0.03 <0.03 <0.03OP Pesticide Parathion, Methyl µg/L 0.065 40 CFR 131 <0.010.097<0.01 <0.01 <0.01 0.03E <0.01 <0.01 <0.01 0.03E <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01OP Pesticide Phorate µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Phosmet µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Phosphamidon µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Sulfotep µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Terbufos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Tetrachlorvinphos µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Thiobencarb µg/L 70 Basin Plan <0.1 0.925 <0.1 <0.1 <0.1 0.1E <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 0.3 <0.1 <0.1 <0.1 <0.1 <0.1OP Pesticide Thionazin µg/L <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04 <0.04OP Pesticide Tokuthion µg/L <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Trichlorfon µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03OP Pesticide Trichloronate µg/L <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 <0.03 0.04E <0.03 <0.03 <0.03 <0.03 <0.03Trianzine Herbicides Ametryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Atraton µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 0.13 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Atrazine µg/L 3 Basin Plan 0.035E 0.035E <0.02 <0.02 0.035E 0.035E <0.02 <0.02 0.1 0.035E <0.02 <0.02 0.1 0.035E <0.02 <0.02 0.1 0.035E <0.02Trianzine Herbicides Prometon µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Prometryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Propazine µg/L <0.02 <0.02 0.035E <0.02 <0.02 <0.02 0.105 <0.02 <0.02 <0.02 0.115 <0.02 <0.02 <0.02 0.035E <0.02 <0.02 <0.02 0.035ETrianzine Herbicides Secbumeton µg/L 0.035E 0.375 0.275 <0.02 0.16 <0.02 0.2 <0.02 0.15 <0.02 0.26 <0.02 0.5 <0.02 0.152 <0.02 0.21 <0.02 0.175Trianzine Herbicides Simazine µg/L 4 Basin Plan <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Simetryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02Trianzine Herbicides Terbuthylazine µg/L 0.14 0.807 0.225 <0.02 0.25 0.15 0.187 0.214 0.22 <0.02 0.262 <0.02 1.250 0.370 0.667 1.250 0.380 0.575 0.280Trianzine Herbicides Terbutryn µg/L <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02 <0.02PAHs Acenaphthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Acenaphthylene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Anthracene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Benz(a)anthracene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Benzo(a)pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Benzo(b)fluoranthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Benzo(e)pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Benzo(g,h,i)perylene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Benzo(k)fluoranthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Biphenyl µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Chrysene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Dibenz(a,h)anthracene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02<0.02PAHs Dimethylnaphthalene, 2,6- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Fluoranthene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Fluorene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Indeno(1,2,3-c,d)pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Methylnaphthalene, 1- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02<0.02PAHs Methylnaphthalene, 2- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02<0.02PAHs Naphthalene µg/L <0.02 0.035E <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Perylene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Phenanthrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Pyrene µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PAHs Trimethylnaphthalene, 2,3,5- µg/L <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02 <0.0125 <0.02 <0.02 <0.02PCBs PCB 005 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 008 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 015 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 018 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 027 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 028 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 029 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 031 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 033 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 044 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 049 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 052 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 056 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 060 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 066 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 070 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 074 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001Dry, no samplePage 2 of 3 Table H-2. Data Collected Under SWAMP in 2002 for the Los Peñasquitos Watershed. Shaded values either exceed water quality objectives or are potentially toxic.March April June September March April June September March April June September March April June September March April June SeptemberRose Canyon Creek - 906LPLRSC4 Tecolote Creek - 906LPLTEC3SourceLos Peñasquitos Creek - 906LPLC6 Soledad Canyon Creek - 906LPSOL2 Poway Creek - 906LPLPOW2Analyte Group Analyte Units WQOPCBs PCB 087 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 095 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 097 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 099 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 101 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 105 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 110 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 114 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 118 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 128 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 137 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 138 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 141 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 149 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 151 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 153 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 156 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 157 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 158 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 170 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 174 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 177 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 180 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 183 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 187 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 189 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 194 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 195 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 200 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 201 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 203 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 206 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001PCBs PCB 209 µg/L <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001Toxicity Ceriodaphnia dubia Survival Percent 100 80 90 90 100 80 100 90 100 100 100 90 100 0 90 90 7040 40Toxicity Ceriodaphnia dubia Reproduction Num/Female 32 31 201327 35 13 (b)833 26 161634 NA 16172785Toxicity Hyalella azteca Survival Percent 88 90 95 7364 399053 25 6079 (c) 60 (b) NS7490 NS NS 81 (c) 93Toxicity Hyalella azteca Growth mg/ind 0.209 (c) 0.251 0.176 (c) 0.288 0.266 (c)0.1140.208 (c) 0.235 0.293 (c)0.1780.156 0.223 (c) NS0.151 0.176NS NS 0.209 0.139Toxicity Selenastrum capricornutum Growth cells/ml360800061280001150000 5268000 400800058830001587500 4698000 3973000 2888000 780000 4343000 450800066130001837500 5603000 2368000 688000 205000Notes:Concentrations noted with E are estimated as midway between the MDL and the RL.(a) WQO for metals based on hardness of 100 mg/L CaCO3(b) Below threshold value, but not significantly different from negative control.(c) Above threshold value, but significantly different from negative control.Shaded toxicity results are both significantly different from negative control and below threshold value.Dry, no samplePage 3 of 3