Loading...
HomeMy WebLinkAboutEIR 80-07; DAON CORPORATION RANCHO CARRILLO; DRAFT ENVIRONMENTAL IMPACT REPORT; 1981-04-030 0 0 :O_.. a 0 0 0 0 0 lsa □ 500 newport center drive, suite 525 newport beach, california 92660 phone (714) 640-6363 □ 2927 newbury street, suite c berkeley, california 94703 phone (415) 841-6840 LARRY SEEMAN ASSOCIATES, INC. DRAFT ENVIRONMENTAL IMPACT REPORT RANCHO CARRILLO PLANNED COMMUNITY PREPARED FOR THE CITY OF CARLSBAD PREPARED BY LARRY SEEMAN ASSOCIATES, INC. 500 NEWPORT CENTER DRIVE, SUITE 525 NEWPORT BEACH, CA 92660 (714) 640-6363 APRIL 3, 1981 7 (· 0 ' :o 0 0 0 O· o· 0 0 0 ii TABLE OF CONTENTS INTRODUCTION PROJECT DESCRIPTION ENVIRONMENTAL SETTING, IMPACTS, AND MITIGATION MEASURES Earth Resources Water Resources Biotic Resources Cultural Resources Paleontological Resources Land Use Visual and Aesthetic Aspects Traffic Air Quality Energy Noise Colllllunity Services and Public Utilities Agricultural Resources ALTERNATIVES TO THE PROPOSED PROJECT SUMMARY OF ANY SIGNIFICANT UNAVOIDABLE ADVERSE IMPACTS WHICH CANNOT BE AVOIDED IF THE PROPOSAL IS IMPLE~ENTED ,,;.7·---.• ·-:-,·-•:. __ ..;_ GROWTH,imbd~ING IMPACTS·· • • -.. SIGNIFICANT IRREVERSIBLE ENVIRONMENTAL CHANGES WHICH WOULD BE INVOLV°E_D IN THE PROPOSED ACTION SHOULD IT BE IMPLEMENTED THE RELATIONSHIP BETWEEN LOCAL SHORT-TERM USES OF MAN·' S ENVIRONMENT lsa 1 2 11 11 23 27 32 34 36 . 40 41 59 67 68 82 89 100 103 104 105 AND THE MAINTENANCE .AND ENHANCEMENT OF LONG-TERM PRODUCTIVITY 106 PREPARERS AND CONTRIBUTORS TO THE REPORT PERSONS AND ORGANIZATIONS CONSULTED REFERENCES REFERENCED MATERIALS ON FILE WITH THE CITY OF CARLSBAD 107 108 112 115 I 0 0 0 0 0 0. O· 0 0 0 APPENDICES Appendix A -Hydrology Study Appendix B -Biological Study i i i Appendix C -Cultural Resources Studies Appendix D -Paleontological Study Appendix E -Traffic Study Appendix F -Traffic Comments Appendix G -Air Quality Analysis Appendix H -Energy Study Appendix I -Noise Study, Bioacoustical Engineering Corp., 1980 Appendix J -Noise Study, Vincent Mestre Associates, 1981 Appendix K -Correspondence lsa 0 I 0 , 0 0 0 0 a 0 0 iv LIST OF FIGURES AND TABLES FIGURES Figure 1 -Regional Location Map Figure 2 -Vicinity Map Figure 3 -Proposed Master Plan Figure 4 -Existing General Plan and General Plan Jlmendment Figure 5 -Phasing Figure 6 -Geology Map Figure 7 -So i1 s. Map Figure 8 -Conceptual Grading Plan Figure 9 -Biotic Resources Figure 10 -Areas of Preserved Natural Vegetation Figure 11 -Proposed Circulation System Figure 12 -Directional Distribution Figure 13 -Existing and Project Daily Traffic Figure 14 -Existing, Project, and Related Project Daily Traffic Figure 15 -Palomar Airport Flight Paths Figure 16 -Roadway Segment Location Figure 17 -Ultimate Noise Exposure TABLES Table A -Master Plan Statistical Surnnary Table B -General Plan Land Use Comparison Table C -Soils Characteristics Tablero,-:-.;.,Estimated. Site.-Seismicity for Major Faults Table E .-Trip Generation Rates Table F -Project Trip Generation Tafrle G" -Daily Volume/Capacity Comparisons Table ·H -ICU Sunmary Table I ---°Carlsbad Area Air Quality Surrmary Table J -Rancho Carrillo Vehicular Emissions Table K -Rancho Carrillo Vehicular Basin Burden Analysis Table L -Rancho Carrillo Stationary Source Emissions Table M -Current Aircraft-Related Weekday and Weekend CNEL Exposures Table N -Future Aircraft Weekday and Weekend CNEL Exposures Table.a -Future Roadway Parameter Values Table P •-Future Roadway Noise Levels 100 Feet from Centerline Table Q -Factors Determining Agricultural Viability Table R -Crop Suitability of Soils Table S -Net Farm Revenue (Northern Parcel) Table T -Annual and Cumulative Net Farm Income (Northern Parcel) lsa 4 5 6 8 10 12 15 19 28 31 42 47 48 49 70 77 81 7 9 14 17 44 45 51 53 61 62 63 66 72 75 76 78 90 94 96 97 ------------------ Q Q 0 0 0 0 0 0 0 GENERAL SUMMARY OF IMPACTS ANO MITIGA1ION MEASURES Potential Adverse Impacts Mitigation Measures .·, EARTH RESOURCES (Pages 11-23) '-~ass -gradin!r will --stgnifit'antly:----S1gnificant cut and fill (30 feet impact -·the onsite topograp~y ~.Y' • ~r-'greater in depth); will be con- permanently altering the existing;• , fined to limited areas. All grad- l and form. • .. • • ing will be in full conformance i wlth City ordinances and will reflect the recommendations of all geotechnical studies. ,·. Landslides onsite • pose signifi, . cant safety hazards to develop..: , • ment. Alluvial deposits require com- paction and soils onsite are con- sidered expansiv'e. These may pose developmental safety haz- ards. Identified slide areas and areas of potential slides will be precisely delineated and analyzed. Appropriate stabilization proce- dures such as burial. excavation. buttressing. or shear key support will be incorporated into project design and grading plans to the satisfaction of the City Engineer. The depths and natures of alluvium and colluvium will be more precise- ly determined. All onsite soils will be further analyzed to deter- mine· the precise level of expan- siveness, erodibility, and other soil characteristics. Based on this, appropriate engineering pro- cedures (i.e .• recornpaction, remov- al, etc.) will be incorporated into the project design to the sat i sf ac- t ion of the City Engineer. Level of Significance After Mitigation PartJ ~J_Jy _ mit i_gated. but none the less a 1 __ s1gnHicant adve~se -foipacL Mitigated to an insignificant level. Mitigated to an insignificant level. < 0. 0 0 0 Potential Adverse Impacts Allu~ial groundwater pose, a potential hazard to slop~,:> and: l>uttress stability. . '··i 0 _o 0 Mitigation Measures EARTH RESOURCES (CONTINUED) ,I The. installation of subdrains in' . fill canyons and in stabilization . structures will be further cons id- .. ered and incorporated into the project design as necessary . . ,. Regional faulting presents a·;. All: structures will conform to the potential hazard of groundshaking Uniform Building Code and all during seismic activity, identi-, . applicable building and safety code cal to that for the surrounding.·· .. requirements. area. Urban poll utan ts in runoff wi 11 incrementally degrade local water qualit'y. This_ will contribute incrementally to the cumulative adverse impact associated with increased urban development in the region. Onsite grading will potential for erosion increase sedimentation stream waters. create a and may in down- Onsite impervious surfaces and divers ion of ephemeral streams will alter the existing drainage. pattern. WATER RESOURCES (PAGES 23-27) Weekly streetsweeping implemented on internal will be roadways. A complete erosion control program will be approved by the City, and implemented during grading and between grading phases. • The developer will provide a drain- age control sys tern designed to ensure that IO-year flow rates after development do not exceed existing IO-year peak flow rates. -----------------0 0 Level of Significance After Mitigation 0 Mitigated to an insignificant level. Mitigated to an insignificant level. Part-iall-y __ 0mifig-afed~ -b·ur-·strll · a curii~Xaf.ively .significant-impact. Mitigated-to an insignificant level. Mitigated to an insignificant level. 0 < -'• o .. 0. 0 0 Potential Adverse Impacts 0 _o 0 Mitigation Measures WATER RESOURCES (CONTINUED) • o'etent ion bas ins will be designed to pass runoff safely from a 100- . year storm. •' l, BIOLOGICAL RESOURCES (PAGES 27-32) I Development of the site as pro-.' 'Natural vegetation w,thin the posed will strip the site of areas designated as "natural ter- nearly all existing vegetation.,,· rain" in the conceptual grading Diversion of ephemeral streams·· • plan will be preserved.· Landscap- will eliminate remaining riparian: ing around the detention basins habitat. Wildlife species will • will be native vegetation. The all but be eliminated onsite. • developer will explore the feasi- Offs ite wildlife will be • indi-bil ity of incorporating natural rectly affected by the intrusion· drainage swales into the drainage of urban uses on adjacent par-control plan, to be preserved as eels. upgraded riparian habitat. The project applicants will incorporate all permit conditions formulated pursuant to the Department of Fish and Game's 1603 permit authority. Development of Rancho Carrillo will destroy all or most of the archaeological sites within the project area. CULTURAL RESOURCES (PAGES 32-34) A qualified archaeologist will investigate significant archaeolog- ical sites to determine appropriate salvage procedures. Shell scatters will be surface-collected and anal- yzed. Carrillo Ranch will be pre- served as part of an 20-acre City park. The historic cross will be moved to within the City park. 0 0 Level of Significance ~fter Mitigation 0 (Par-tfaH:V~_1!11Tfgafed :--but: "itJJLi --s'(g:. :~nj_{iC~_!l_t__jijy~_rs_e impact. -Mitigated to an insignificant level. 0 < _,_ o. 0 0 0 .D .. o _o 0 0 .. Potential Adverse Impacts Mitigation Measures PALEONTOLOGICAL RESOURCES (PAGES 34-35) Level of Significance After Mitigation Underlying formations onsite :~ave · A:;; certified paleontologist will the potential for beari_ng signif-s~rvey the project area and will be icant fossils. Grading anct ,con-•·.: ·present during grading of sensitive structfon "°uld destroy or C,over •'.· ·:a.r:~as. The paleontologist will be over these areas. ' • present at all pregrade meetings, .. . an.~ has the authority to halt or • · . •,direct operations for, expeditious •. ·:.fossil salvage. • • •'1i I • • Residential land uses may con- flict with bordering agricultural activities. I LAND USE (PAGES 36-40) When the two land uses are deter- mined to conflict, a 6-foot block wall will be constructed; if aerial spraying is conducted .offsite, the developer will provide a 150-foot buffer zone separating the· land uses. Mitigated to an insignificant level. Mitigated to an insignificant level. VISUAL AND AESTHETIC ASPECTS (PAGES 40-41) Development would irrevocably change the site's appearance and aesthetic character. Greenbelts, open spaces, and natu- ral terrain areas will be included in the design of the project and will preserve some of the original features of the site. /PartTalli mitigated, but sJ]_lL__a_ sig- !oJf.icant _impact. ----- 0 < -'• -'• -'• 0 0 0 ,.o 0 0 Potential Adverse Impacts Mitigation Measures I j .. 1RAFFIC AND CIRCULATION (PAGES 41-59) At completion, the project .~i.11 . Se~ Mitigation Measures 23-30 on generate an estimated 53;840. • .. Pages 57-59. daily trips. This traffic, <Jlong::. 1)· with existing traffic and traffic;:;• ,J1:,: generated from neighboring and '. _: • ;: (,: regional __ deve.lopments-,---wi-l-1-.' , I"::.'·. result 'in sev_er_e= congesttoti "at •·.: i:t. lthe -Pa fomar _)\i_rpo_r:_f~lload/Me-lrose ·.;' ,... :'..- ·Avenue_ intersect-ion.-· • ',; , .;: ---,• ·'' ·•, I !· • I Proposed intersection spacni 0 ngt-·.·::'j along Melrose Avenue does conform to City standards. At completion, Rancho Carrillo will contribute an estimated 0.54-0.70% of the entire San Diego Air Basin's burden of major vehicular pollutants. Dust emissions during construc- t ion will temporarily and locally degrade air quality. Increased stationary source enlis- s ions will result from the proj- ect's consumption of energy. AIR QUALITY (PAGES 59-66) Alternate transportation modes will be encouraged by inclusion of bus facilities, public bikeways, and walkways in the project design. , Diverse land uses within the commu- nity will promote intra-convnunity travel. The grading contractor will imple- ment dust suppression measures dur- ing grading operations. Design features to reduce energy consumption will be incorporated into community designs. ----------· ------------- 0 0 Level of Significance After Mitigation 0 .--ParfTalT i~m-i t}_g_ati~-,-~ huL _s b 11 ~-;i gn:i f- -~:_!_c_~~t.~ __ .- PartLa_ll_y __ !fli_tj_gated, but: sdTCa,:cumu-- ·Ta-t i_ve l-Y -Si gni.flc-ar,t _.-impact. -'/ Mitigated to an insignificant level. ]ar_Ua LlJ<--mH.i gated_, ___ buLsU.l l a ·~l)rtlu.L --1 at ive l-y-sign if ic an t---impact: 0 -'• >< O· 0 0 0 .o .o 0 0 Level of Significance Potential Adverse Impacts Mitigation Measures After Mitigation --'--......,...--------"-------------------__,._ ______ _ Project development will result in increasing consumption·· of. electricity, natural gas. and· automotive fuels. ., ·, Adj ac en t to ex is Ung homes, there • : wi 11 be an expected increase in road-related noise levels of 8.9 dB CNEL along El Fuerte Street and 7 .9 dB CNEL along Alga Road west of El Fuerte. This is a c umu l ati ve impact of this and other projects. Future noise levels wi 11 al so increase as much as 22 dBA along future roadways which do not yet exist. ENERGY (PAGES 67-68) Energy conservation features will be incorporated into project design, and reviewed at the time of tentative map submittal. NOISE (PAGES-68-82) Pr.ior to submittal of the tentative maps, a detailed acoustical analy- sis and noise control program will be completed and reviewed by the City. See Pages 80 and 82 for additional mitigation. Par_qally m_it_igated, hut still a.-etJ111u..;" !J_~(i_yeJy _slgn.i ficant impact. Mitigated to an insignificant level. COMMUNITY SERVICES AND PUBLIC IJTILITIES (PAGES 82-89) An additional fire station and nine personnel wi 11 be required to serve the new corm1un i ty with fire protection at ultimate huildout. The fire station proposed in the Fire Department I s Master Pl an for the area of Alga Road and El Fuerte Street will be operational to meet the needs of Rancho Carrillo resi- dents no later than at the time of occupancy of at least 1,000 dwell- ing units. Mitigated to an insignificant level. 0 X o .. 0 0 0 Potential Adverse Impacts Mitigation Measures \ . .0 .. 0 .. 0 Level of Significance After Mitigation 0 0 COMMUNJTY SERVICES AND PUBLIC UTILITIES (CONTINUED) The Carlsbad Pol ice Department will require 14 additional offi- cers to serve the project ar~~- Rane ho Carri l lo will consume an estimated 1.5 to 1.8 million gal- lons per day of water at project bui ldout. Rancho Carril lo will generate a total wastewater flow of . 76.. mgd per day at buildout. This is not considered a significant impact. Residential sol id waste products will range from 18,700 to 23,400 pounds per day. This is not believed to he an adverse impact. cd11merc i al and industrial areas of the site will employ internal security systems and guards to d~ter burglary • and vandalism~ Design features will be incorporat- ed that will aid pol icing activi- t i,es . Mitigated to an insignificant level. . The Clty and the Costa Real Water~ Not a significant impact. District will review the Rancho Carrillo Master Plan for Public Water Systems to determine its ade- quacy to the proposed Rancho Car- ri 11 o Master Plan: The planned community's non-potable water needs will be defined. Fire flow demands will be re-evaluated. Landscaping in public and private areas will emphasize plants with low water consumption. Public and private water facilities will use low water consumption features. The City will review the proposed sewer system for its adequacy. No mitigation measures are propos- ed. Not a si gni fie ant impact. Not a significant impact. X ..... ----------- 0 0 0 -0 Potential Adverse Impacts .0 Mitigation Measures .0 .. 0 Level of Significance After Mitigation COMMUNITY SERVICES AND PUBLIC UTILITIES (CONTINUED) At buildout, Rancho Carrillo.will generate approximately 780 to 83 school-aged children. The developer will consult with both the San Marcos and Carlsbad School . Districts to determine the :111ost feasible boundary. With . . : approval of the Master Pl an, the ' . districts will assess the specific impacts and, with the developer, formulate appropriate mitigation measures. The project would result in the loss of approximately 178 acres of agriculturally viable land. This would effectively eliminate the ability to use the land for agricultural purposes. This con- version, in concert with the increased regional loss of agri- cultural lands, represents a regionally significant cumulative impact. AGRICULTURE (PAGES 89-99) The City will consider requiring that the developers offer short- term leases of agriculturally via- ble parcels onsite, to the extent feasible, until such time as they are to be developed in phase. Mitigated to an insignificant level. Si gni fie ant -cumulative _impact: 0 X -'• -'• 0 0 0 0 0 0 ,0, 0, I ' 0· lo· I I I 1 lsa INTRODUCTION In 1972, the City of Carlsbad changed the zoning designation of Carrillo Ranch from single-family residential (R-1) to planned community (PC). Also in 1972, the City adopted a Planned Community Master Plan for Rancho Carrillo. The 100-acre Carrillo Estates, a portion·of Rancho Carrillo, was develop- ed in 1976 under the adopted Master Plan. An environmental impact report was prepared for the 100-acre development in 1975 and is on file with the City of Carlsbad. • Si nee these acti ans, a revised Rancho Carri 11 o Master Pl an has been pre- pared for the project app 1 i cants by The Planning Center of Newport Beach for approval by the City of Carlsbad. The present environmental document analyzes the impacts of discretionary actions to be performed by the City of Carlsbad in association with adoption and implementation of the revised Master Plan. Foremost among these actions are: 1. Amendment to the City of Carlsbad's General Plan in accord- ance with the revised Rancho Carrillo Master Plan. 2. Adoption of the revised Rancho Carrillo Master Plan. This Environmental Impact Report has been prepared in accordance with the California Environmental Quality Act of 1970, as amended (Public Resources Code, Section 21000 et seq.), the State Guidelines for Implementation of the California Environmental--Qua.lity Act of 1970, as amended (California Adminis- trative Code, Sectfori 15000 et seq.), and the Environmental Protection Proce- dures for Implementation of the California Env.ironmental Quality Act adopted by the City of Car-lsbad (Title 19, Carlsbad Municipal Code). 0 0 0 0 0 0 0 iO I I 0 0 0 0 2 lsa .PROJECT DESCRIPTION PROJECT LOCATION AND BOUNDARIES The Rancho Carrillo project area consists of 846 acres located 5.5 miles inland from the Pacific Ocean in the City of Carlsbad in the County of San Diego. Figures 1 and 2 show the vicinity. The site is bounded on the north by the Carlsbad Raceway, on the east by the City of San Marcos, on the south by the planned community of La Costa, and on the west by unincorporated San Diego County. PROJECT CHARACTERISTICS Master Plan. Figure 3 illustrates the proposed Master Plan. The plan- ned community will include primarily residential land use of various densities south of Pa 1 omar Airport Road, and commerci a 1 and i ndustri a 1 1 and uses north of Palomar Airport Road. Table A_ gives a detailed statistical surrimary for the proposed planning areas. The Master Plan would allow 2,998 dwelling units at densities ranging from 2.27 to 9.85 dwelling units per gross acre. It would also allow 124 additional dwelling units if the proposed school •site was not needed by the school district and thereby reverted to residential use. There would be 41.1 acres of industrial dev~lopment and 35.1 acres of retail services. The Master Plan also includes approximately 166 acres in community open space, public parks, .and commerc'ial recreation. The plan proposes an internal circulation system· within· the community, including primary and secondary streets, bike paths, and pedestrian trails. General Plan. Amendment. The project applicants have requested that the City of Carlsbad consider an amendment to the City of Carlsbad's General Plan in support ·of the proposed revised Rancho Carrillo Master Plan. Figure 4 illustrates the existing General Plan and the proposed General Plan amendment for the subject property. Table B provides a statistical comparison of the proposed Genera 1 Pl an amendment ·,o1i th the existing Genera 1 Pl an. The proposed Genera 1 Pl an amendment wou 1 d a 11 ow for 485. 6 acres of res i - dential development, which is 56.3 acres more than designated by the existing General Plan. However, it provides for overall lower densities \'lith a maximum of 3,750 .dwelling units compared to the presently allowed 3,886 dwelling units. The proposed amendment would provide only low/medium and medium-den- sity residential development, deleting the 74.1 acres of medium/high-density residential development currently allowed. 0 0 0 0 0 0 0 I 10 0 , 0 3 lsa The proposed amendment would slightly decreasethe amount of acreage des- ignated as neighborhood and travel services commercial, but would designate an area for community commercial facilities which is not currently provided for in the existing General Plan. The area referred to as a special treatment area would be clarified under the designations of planned industrial and community commercial. The recrea- tion commercial area would be decreased in size by 14.2 acres. The two elementary school sites together, totaling about 18.7 acres in size, would be reduced to one centrally located elementary school site total- ing 14.6 acres. Areas designated as open space would be reduced from 189.3 acres to 159.4 acres. Designated open space areas, as proposed, would cover 21% of the site. The section of Me 1 rose Avenue north of Pa 1 omar Airport Road would be realigned along a slightly more northerly course, as opposed to its presently adopted northwesterly alignment. This may require an amendment to the Circu- lation Element. Also, the existing Parks and _Recreation Element map indicates a 7-acre park site at the southwest corner of Melrose Avenue and Carrillo Way. The proposed amendment would move the site to just east of the Carrillo Ranch His- toric Park site and would increase the acreage to 8.2 acres. Finally, -as illustrated in Figure 4, the amendment would require the minor moc;iification of _land use boundaries throughout. the site. Development 'Phasing.· •• Figure 5 identifies six phases which will be developed individually. Completion of each phase is contingent upon comple- tion of the necessary internal circulation components and placement of sani- tary sewer, water, and storm drain facilities. Placement of these utilities, as well as grading, may or may not be sequential. • ADDITIONAL DISCRETIONARY AND.DEVELOPMENTAL APPROVALS Addi ti anal discretionary approvals associated with the development include City approval of specific site plans and subdivision map(s), and issu- ance of the grading permit. The California Department of Fish and Game also has 1603 permitting authority on actions resulting in the alteration of streambeds. 0 :o I • G 0 q 0 0 0 10 ' 0 1 Regional Location Map ... .. :., .... ... '•:, . . ·•:: .. :·_::.; .. Oceans:iJt ... -.: .. .... . . . ~ . . ·•:·. t ••• Carls6~: .. •• _:_-=~: ..... :,,,, -..::it:;'"-.. ·: : . 4 • . ·.:-; :: e I:,• S12 :i' . ·-. : .. •::-. Encinit~~:·, ... :: .... ... . . . ... ·•·.·.· .... . .·: . _. .=rt -- •. • )\ ::••.\c' ~, ,;{f;_Del· -~!~ 0"' -. .. ~ ._ .. -~ :: • :--.-·_ :-. ·.:._-~"':.-->-• • -~-: ·:·~-. ,:·.-·.:.:.~·-.-_ •• -. • ;. :: ::·~ ··-:-. ---.; ~-=--· •• . -"':·.:: __ ."-:-·· . ·: . --.: . . .. . .. .... . ·.::_ . . . . . . .. ~: ... : :;: ... • ... · . . . . ··.·---=---: .,. • •• La Jo·li~; . ·-·· .. Project Site ... C1I lsa 9 mile ~ -0 N 0 0 0 0 0 0 0 0 0 0 2 Vicinity Map Oceanside •·. . ••.•.•·• ·•·. -. :-.. -· .. .... . .... . · .. • , .. . . ·.-~. --.. londa oon . ~ . -. : .::~~ ·_-:..··.F:_:··-: .-_ .. __ ~-=-. . • ·····:·:··:.;· •. , 5 Vista lsa ., ••• Lake San ' Marcos San Marcos • N no scale 0 0 0 0 0 o, 0. 0 0 0 d 6 3 Proposed Master Plan LEGEND D . . . I • I • I • I •· I • I Residential Recreation1 Commercia Commercial Industrial Public A N.A.P. I • I •· . . '-·-·-·-·-·-·-·-·· Source: The Planning Center NOTE: Refer to table A for Land use statistics. lsa ·1 .. . . . . . . . . . .. : . : . : . : . :· . . . : . : . : . : . : . : ·I . . . . . . . . . . •:•:•:•:•:•:•:•:•• .. s ..... . . . . . . . . ::: .. :::::::•· ffi] 0 200 500 '00J - ----------·- 0 0 TABLE A 7 MASTER PLAN STATISTICAL SUMMARY lsa 0 Total Number of Planning Areas Gross Residential Units Gross (Refer to Figure 3). Acres A 11 owed bl'. Area DU/AC 0 Residential B 50 .8 148 2.91 C 74.5 255 3.42 D 32.0 221 6.90 J 53.8 530 9.85 K 43.5 99 2.27 0 L 70.3 198 2.81 M 99.7 700 7.00 N 15.3 50 3.26 0 87.5 332 3.80 p 30.3 240 7.90 Q 17.0 92 5.40 0 s 52.1 133 2.55 : Recreation Commercial E 6.5 G 4.0 0 Commercial R 5.3 u 8.9 V 20.9 Industrial T .--41.1 0 Public F 14.0 . H 8.2 Not a Part Areas 0 A 100.0 I 10.5 TOTALS 846.3 2,9981 -- 0 lThis figure could increase by as much as 124 units if Planning Area F were to revert to residential use in the event the school site was not used. d D Existing Ge neral .._.......,, Dwallyl<M••I -Oenlity{4•10Gl/acl Median Hll.lh Denolty(10-20dulac) Nei;hbol._ Conwnerclal ,.,_ s.rw: .. Comnwclal llacnatlaft c:on-rc:ial a..-1..., Sdlool Plan & Original G -eneral endment ' LM , , ,, .. ~~· I ' ,,,,/ , \ \ •• \ . I ' . , 0 0 0 10 I ·.o_ 0 0 0 0 o· 0 TABLE B GENERAL PLAN LAND USE COMPARISON Land Use Low/medium-density (0-4 du/ac.) Medium-density (4-10 du/ac.) Medium/high-density (10-20 du/ac.) Neighborhood comercial Community commercial Travel services commercial Recreation commercial Special treatmentl Planned industrial School Open space Total Maximum allowable dwelling units lNo land use desi~nati~n·proposed. 2Totals subject to rounding errors. 9 lsa Existing Proposed General Plan General Plan 191.3 acres 184.2 acres 163.9 acres 301.4 acres 74.1 acres 12.3 acres 5.3 acres 20.9 acres 20.8 acres 8.9 acres 24.7 acres 10.5 acres 51.4 acres 41.4 acres 18.7 acres 14.6 acres 189.3 acres 159.4 acres 746.5 acres 2 746.6 acres2 3,886.2 3,750.8 0 I # I I I !o I . 0 0 0 a 10 ! 0 0 0 • 0 5 Phasing LEGEND D . filillfil E] . . . □ I . • I • I • I • Blue Phase Brown Phase Green Phase Orange Phase Purple Phase Red Phase N.A.P • 10 lsa .... ■.111!1111.l;lll!IIII. ■• ·• 1• ~ ■• ~ ~-~ ~ ••■ I -I -I -I -I -I -I . : . : . : . : . : . : . : ............................. · ... :.:.:.: . : . : . : . : . : . : . : . : . : . : . : . : . : . . . . . .. ·1 • ........ ·.. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..... . 1: . •• ·············: ···········1 . ······••••• ............ . I·. . ........... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ................... . . . .............................. •· ... I . . . . ............................... . • . 263 ·du· ............... · · · · ....... · · · · · · · . . . . . . . ............................... .. . . ............................... · 1 o I I I I I I I I ■ I I I I I I I I I I I I I I I I I I I I I I I I I I•. . . ................................ . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ·-................................... • . ••••••• ! ••••••••••••••••••••••••••• ·• I·. . ...... :'-·':112',::, .,:J,. -....:i· ••••••••••••••••• . ·:. •.•. ·.·.·.·,.·, .vv·.·l.lu :.·.· .• .•.•.•. •. •. •. ·.·: .• .•.•• . . . .................................... ·1 I·. . ..................................... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ............................................ • • I • I EB] • ··-·-·-·-·-·-·-·-0 200' --ooo·· 0 I 0 0 0 o. 0' • 0 EARTH RESOURCES 11 ENVIRONMENTAL SETTING, IMPACTS, AND MITIGATION MEASURES lsa Soils engineering and geologic studies for Rancho Carrillo have been com- pleted for the project applicants by GeoSoil s, Inc. Five reports were prepar- ed in August 1979 and April 1980 for the five separately owned parcels com- prising Rancho Carrillo. A sixth report conducted in September 1980 examined in further detail the seismicity of the central portion of the site. In addi- tion to their own reconnaissance, the GeoSoil s reports incorporate pertinent informftion obtained by other geologic firms which conducted previous explora- tions. Multiple copies of all six reports are on file with the City of Carlsbad Planning Department. The following pages provide a summary. Setting. To~ography. Figure 6 illustrates site topography and geologic features. T e area north of Palomar Airport Road is gently sloping, divided rough 1 y in half by a sma 11 canyon trending east and west. Slopes on either side of the canyon range from 5 to 13%. Steeper topography characterizes the area south of Palomar Airport Road. Slopes range from 9 to 30%. Only about one-quarter of the site has a slope less than 9%, with a very small portion having a slope less than 2%. Maximum relief over the site ranges from approx- imately 550 feet at the southeastern boundary to 150 feet in the southwestern portion (Figure 6)~ Geolo~/Soils.· Most of the site is underlain by claystones and sandstones of te Del Mar Formation. Beneath the Del Mar Formation lies the Lusardi Formation, a thick conglomerate of cobbles and boulders in a clayey sandstone and sandy mudstone matrix. Some granitic rock, representing the Southern California bathol ith, occurs onsite. Limited exposures of Santi ago Peak volcanics occur in the southwestern section of the site. The volcanics are of an andesi te composition and are very hard and highly fractured. The volcanic soils are rocky. Topsoils overlying the bedrock consist primarily of dark brown silty clays. Depth ranges from two to four feet. In the central, eastern, and lPrevious geologic studies are: (a) S.C.T. Laboratory, Inc., 3/74, north- western portion of site; (,b) S.G.T. Consultants, 1/77, north-central section; and (c) Shepardson Engineering Associates, Inc., 1/79, central, eastern, and southern sections . • • • 6 Geology Map Legend Qal Quate Qls Quat mary Alluvium Jap Ju:ary Landslide '-Peak ~ S~iago Kgr olcanlCS KL Cretaceous Grant'·. Tdc ~:~t•ous Lusar~I ~~ Tds Tert·ary Claystone Td ,ary Delmar S c-s Tertiary andston S Delmar andstone & Clay Approx. Linit stone s of Lands Approx , i-· Ide · ...... its of A., __ • l'UIUYaJffl 12 lsa 0 20C1 - 0 0 0 0 0 0, o. 0 0 d --------------------- 13 lsa southern portions of the site, a topsoil mantle exists, comprised mainly of Lusardi Formation conglomerates. Thick accumulations of topsoil occur along the back of landslides in the site's central, eastern, and southern portions. Topsoils in general are dry to moist and vary from sands to clays, with expan- sive characteristics varying from non-expansive to highly expansive. In some cases, materials are considered critically expansive. Alluvial deposits occur within the canyons, gullies·, and on some of the lower side slopes. The soils vary from clays to sands and are poorly consoli- dated. These deposits are expected to range from 5 to 35 feet in depth, with deposits of 20 feet and more occurring in the larger canyons. The a 11 uv tum found in the major canyon located in the central portion of the site is wet and soft, and settlement is anticipated if loaded. Colluvium is expected to occur along the gullies and canyon side slopes beyond the deposits mapped as a-lluvium. The colluvium may vary in thickness from three to ten feet. Artificial fill exists at the former dam site, at an earthen berm, along a trunk sewer line, and along the access roads. The dam site and sewer line are in the central section of the site, and the earthen berm is in the south- west corner. Access roads occur north of Palomar Airport Raad and within the central section leading to the Carrillo Ranch facilities. The fill deposit associated with the trunk .sewer line is roughly ten feet thick and appears moderately compacted. Thickness of the other deposits is not known. Fill materials appear to be locally derived, comprised of a mixture of sands and clays. • Table C lists the characteristic_s of onsite soils pertainfog to erodibil- ity, permeability,· and shrink/swell behavior. Figure 7 illustrates the approximate location of these soils on the subject property. Many of the sails are highly erodible and exhibit high shrink/swell behavior. The agricultural sui.tpj)ility of onsite soils is discussed in detail in the ~Agricultural Resources~ section of this report. Landslides. As Figure 6 illustrates, numerous landslides exist throughout the site. The landslides occur mainly along the north-facing slope·s and side slo'pes of the large central canyon, and along the northern boundary of the site. The cause of lands 1 id i ng is prob ab 1 y a combi natfon of factors including adverse bedding conditions resulting from the regionaJ syn- clinal structure and excessive moisture conditions. Deterioration and soften- ing of clay materials, seepage forces, oversteepening of canyon s~dewalls, and possible seismic events may also combine to undermine slope stability. 0 0 TABLE C 14 SOILS CHARACTERISTICS lsa 0 Shri nk/Swe 11 Soil T:tee Erodi bil i t:t Permeabilit:t Cha racteri st i cs AtC -Altamont clay Slight to Slight High 0 5-9% slopes moderate AtD -Altamont clay Slight Slight High 9-15% slopes AtE -A 1 tamont clay Moderate Slight High 0 15-30% slopes AtE2 -A 1 tamont clay • Moderate Slight High 15-30% slopes, eroded Ga£ -Gaviota fine sandy loam Severe Severe Low 9-30% slopes 0~ GaF -Gaviota fine sandy loam Severe Severe Low 30-50%slopes HrC -Huerhuero loam Severe Moderate High 2-9% slopes 0 HrE2 -Huerhuero loam Severe Moderate High 15-30% slopes, eroded LeC -Las FloreSe--Toamy. fine sand Severe Severe High. 2-9% slopes 0 LeE -Las-FT ores 1 oamy fine sand Severe Severe High 15-30% slopes LeE3 -Las Flores loamy fine sand Severe Severe High 15-30% slopes, eroded ' I ,o LrE -Las Posas stony fine sandy Moderate Slight High ! loam, 9-30% slopes LsE -Li nn e c 1 ay 1 o_am Moderate Slight Moderate 9-30% slopes io I Rm -Riverwash Severe Low ScA -Sa 1 i nas c 1 ay Slight Slight Moderate 0-2% slope 0 o· 0 0 0 I o. 0 0 0 7 Soils Map NOTE: Refer to Table C for description of soi 1 s. • HrE2 AtC 15 lsa AtC HrC *Unclassified soils Source: U.S. Soil Conservation Service. 0 • 0 II 0 0 ' I i o, 0 0 16 lsa The main slide area in the large central canyon does not occur as one single 1 arge mass, but as a complex assemb 1 age of superimposed s 1 i de masses. These probably occurred as regressive landslides, in which continual headward . sliding takes place after an initial failure near the canyon bottom, creating an unstable situation upslope. In many instances, subsequent sliding resulted in overriding of the lower slides. Exploratory borings in the central slide area verified slide planes to range from +20 to +70 feet in depth. The toe of the basal slide extends into the creek area of-the major canyon and is part i a 11 y buried by more recent alluvium. The landsliding has consistently occurred within the clayey portions_ of the Del Mar Formation (Figure 6). Slide planes observed in borings are gener- ally soft clay with well-developed polished and striated surfaces. Typically, the overlying slide mass·is intensely disturbed, while the underlying bedrock is hard. Groundwater. Groundwater· exists in the alluvial areas of the major canyon in the central portion of the site and in alluvium in the so.uthwest quadrant. Artesian conditions bring water to, or near, the surface in many cases. Groundwater 1 evel s have been measured at depths of five to 30 feet below the surface.· However, since these measurements were taken, the dam at the site I s center has been dismantled. Because the former impoundment is believed to have fnfluenced groundwater levels, present levels are expected to be different. Groundwater levels are also expected to fluctuate seasonally. Perched water oc~urs _1_n some areas of the site. Seismicity. ···No known active faults occur on the site. A field reconnaissance suggests that rock formations in the property's northeast quad- rant are offset along a fault (Figure 5). • This feature, however, should not be confused with active faulting or a fault 1t1hich could generate an earth- quake. Rather, it is considered an inactive fault which does not alter devel- opment feasibility. Among the regional faults are the Rose Canyon Fault 12 miles from the site, the Whittier-Elsinore Fault whose closest segment is 23 miles from the site, and the San Jacinto Fault-45 miles from the site. Additional regional faults and their distances from the site are given in Table D. Southern Cali- fornia's major fault system, the San Andreas fault zone, occurs 70 miles from the site. 0. 0 0 0 .o .~ . o 0 0 0 0 0 "' :0 Il l Ill Il l z (/) § il 0 "' "' "' ID :I I ;! :; (4 :, :, :, ( :, .. . " ID 'O (? C .. :: , :i : n 0 c.. " t1 "T l IT 1 -I .. n :, .. . .. . . '1 QI .. . >i OV l ► :i "' a. .Q ID rt 0 ID ;o -I to "' :, '1 C: l3 I .. . '1 N .. . . . . r 0 -< ID ID ID H ::, I 0 :a 0 "' ... . :: , :, " l'l z $~ IT 1 ~ ::, (4 " ,Q 0 ... 1'1 ID ... . . (4 c.. . . -I - 1D ,., CJ ... ( :, OI T I 0 0 ;o o -; 0 '1 ? Cl, ID "T l (/ ) )> .. . . . . ... . . ... . "' "' "' ... ... . C: -I :;; ... . 0 0 0 0 UI .. . D[ S T A N C E FR O M S[ T E (M I L E S ) r IT 1 Oil -I 0 n (/ ) VI "' .. . ~ .. . . -, _ , IT 1 .. . ... . 0 UI 0 Q ES 1 ' UI A T E D FA U L T LE N G " r H (M I L E S ) I .. . . 0 0 0 UI 0 0 0 I+ 1+ I+ I+ I+ I+ I+ (/ ) 3: ,, .. . . . . "' "' '" ' :1 ' "' ?' MA X I M U M II I S T O R ! C A L :1 n .. . "' 0 .. . 0 0 EA R ' l ' H Q U A K E (M A G N I T U D E ) .. . . . . -I ,I -< .. . .. . .. . .. . .. . . UI en N 0 0 1/ 2 FA U L T LE N G T H (M I ~ E S I UI 0 0 0 UI 0 0 1+ 1+ I+ I+ ,1 + I+ :1 ' "' :-" ... . ... . :- " .. . . ES T I M A T E D MA X I M U M MA G N I T U D E .. , UI ... . UI 0 .. . . ... . FO R 1/ 2 LE N G T H RU P T U R E E! ' i ' l " f M A T E D MA X I M U M BE D R O C K .. . ... . . 0 0 0 .. . . N AC C E L E R A T I O t l FO R 1/ 2 LE N G " r l l N 0 a, ' "' UI .. . ... . :I I .. . . . ... . . . . . .. . . "' UI -. , . . .. . ... .. . PR E D O M I N A N T PE R I O D (S E C . ) 0 0 0 0 N "' 00 N .. . "' .. . . "' ... . .. . . DU R A T I O N OF ST R O N G MO T I O N .. . .. . . . .. , 0 A "' N SH A K I N G (S E C . ) .. . N .. . "' .. . ... ... . "' UI 0 UI 0 0 0 l/ 5 FA U L T LE N G T H (M I L E S ) I+ 1+ I+ I+ I+ I+ 1+ "' a, en ... . "' .., .. , ES T I M A T E D MA X I M U M MA G N I T U D E .. . 0 a, 0 UI .. . . w FO R 1/ 5 LE N G T H RU P ' r U R E .. . ;:: , 0 0 0 0 ,. . . ES T I M A T E D MA X I M U M BE D R O C K .. . .. . . .. . .. . .. . ,o ,,. , ,\ C C E L E R A T IO N FO R 1/ 5 LE N G " r t l • .. , VI ... . ... ... . ... ... . . PR E D O I - I I N A N T PE R I O D (S E C . ) "' 00 ... . ... 0 ... . .. . ... w ... . .., ... . N N DU R A T I O N OF ST R O N G MO ' l ' I O N ... . ... "' .. . CD ,1 .. , (S E C . I SI I A K I N G ·r o - 0 0 0 0 ·O • o. o• O' 0 ' 0 18 lsa Impacts. Topography/Grading. Mass grading would cause a significant impact by altering the existing topography for most of the project site. Figure 8 presents the proposed conceptual grading plan. The plan illustrates those areas which will experience cut or fill of 30 feet or greater. It also illus- trates those areas (primarily steep slopes} which will remain totally undis- turbed by grading and groundcover removal. The remaining areas will experi- ence grading on a 1 esser magnitude with cut and fi 11 of 1 ess than 30 feet. Preliminary estimates indicate that grading will require 10 million cubic-...... yards of cut and 10 million cubic yards of fill which will balance onsite. Additional grading will be performed subsequent to mass grading to create building pads and on-parcel subgrades. The grading schedule has not yet been finalized. Grading will probably not occur-entirely at once; neither will it occur entirely in phase due to the topographic requirements for onsite borrowing of fill. No significant impacts are anticipated as a result of the grading schedule. Grading of the Del Mar Formation··may require difficult ripping through cemented layers.. The Lusardi Formation may also require difficult ripping. Oversized rocks from both the Lusardi Formation and the granitic batholith will require special rock disposal methods and probably blasting. Hard vol- canics will also need heavy ripping and blasting. Although these features may pose some design constraints, they are not considered to impose si gni fi cant impacts on local geologic conditions or the proposed developments. Geology/Soils.· . Soils from the Del Mar and Lusardi bedrocks are considered expansive and will require. special treatment. before construction. Topsoils are also expansive, and will require recompaction in fill areas due to their. low density. Alluvial deposits are suitable for fill, but must be recompacted to avoid settlement due to their soft, wet quality. Very 1-1et alluvium may req·uire special drying before compaction. The alluvium is also considered expansive. If not properly mitigated, this could cause a severe constraint to the project and a significant safety hazard where buildings are proposed on these soils. However, with feasible mitigation, the sites can be safely developed as proposed, although at possible considerable expense. Landslides. Without sufficient stabilization measures, the extent of landsliding present onsite would pose significant safety hazards. Further analysis is required at later stages of planning to determine the exact nature of existing landslides, and the specific stabilization methods to be utilized. However, analyses already conducted indicate that stabilization of the landslides may be accomplished by a combination of several methods. • • • ' 8 Conceptual Grading -~ CUT * lllllll!lllllllllllll ~FLL* NATURAL TORAIN 19 Plan ::-------;::.---0 rn ~-OJO' - 0 0 0 0 • 0 • Oa 0 0 ' 0 20 lsa Landslides which are situated within enclosed canyon areas may be ade- quately stabilized by filling the canyon. Landslides can also be rendered stable by removing the entire landslide or by partial removal in conjunction with one of the following methods. A buttress or earthen-fill retaining wa 11 may be used to prevent further earth movement. This method calls for removal of the lower portion of the landslide and construction of a compacted fill slope \'lith a key sl;!ction spe- cifically designed to resist slide movement. A shear key can also be used, which is similar to a buttress, except that removal involves excavating into the landslide mass such that a deep trench is created. The trench or shear key penetrates the slide plane and subsequent filling with compacted fill resists movement. Preliminary analysis by Geosoils, Inc. indicates that most onsite land- slides will require the use of shear keys and buttresses in conjunction with excavation for proper stabilization. Other smaller areas can be stabilized by fill placement or ~otal removal. Slide materials may have high moisture content and require special treat- ment prior to compaction. Because of the site's tendency toward landslides and the generally north- dipping of bed planes,. most cut slopes will require stabilization. Without such stabilization, slope failure could occur, creating hazards to develop- ment. Groundwater< .-Groundwater in the · alluvium poses a threat to structural foundations and to slope stability, and will require consideration of subdrains in fill canyons and in stabilization structures such as buttress- es and fill slopes. Seismicity. Seismicity presents no unusual hazard to the site when compared to the Southern California area as a \-1hole. The fault line in the property I s northeast quadrant shows no evidence of recent activity. Its presence, therefore, has no impact on development and poses no si gni fi cant hazard to future inhabitants. Possible impacts exist from faults on a region- al scale. Impacts of offsite regional faults are limited to groundshaking effects rather than onsite ground rupture. The San Jacinto Fault has been associated with earthquake activity in the Richter magnitude range of 6.2 to 7.1. Estimated parameters of possible impacts from the San Jacinto and other regional faults are given in Table D. The most consistently active zone and the largest active fault in California is the San Andreas fault zone. Esti- 0 0 0 0 0 4 q 0. 0 0 0 d 21 lsa mated seismicity of this fault in relation to the site is also given in Table D. There is no potential for liquefaction due to the cohesive nature of the soils. The.. project will have no adverse impacts on unique or noteworthy geologic features. Mitiaation Measures. The preliminary evaluation of geologic and soils con 1t1ons 1nd1cates that there are several geologic features which pose potential hazards to development on the site. However, utilizing proper geo- technical design considerations, the site may be safely developed as proposed. The following mi'tigation measures are included as part of the project or are otherwise required to offset potential adverse impacts or hazards. L A 11 recommendat i ans and cone 1 us i ans of the soi 1 s and geo- 1 ogi c reports (on file with the City of Carlsbad) will be incorporated into the project design. In addition, based on recommendations from these studies and LSA 's review of the existing analyses, the following studies will be con- ducted by'the project applicant and submitted to the City Engineer for review prior to submittal of the tentative map. Based on these more detailed studies, appropriate measures and procedures will be identified and incorporated into the project design subject to the satisfaction of the City Engineer. This required analysis will include, at a minimum, the following study areas. a. The identified· slide areas and areas of potential slides will be precisely delineated and analyzed throughout the property. Based on this i dent i fi -cation and analysis, appropriate stabilization procedures will be formulated and incorporated into project design and grading plans. b. The depths and natures of the identified alluvium and colluvium deposits will be precisely determin- ed. The deposits' suitabi 1 ity for devel apment wi 11 a 1 so be determined. If found to be unsu it- ab le, appropriate engineering procedures (i.e., recompaction, removal, special foundation design, etc.) will be identified and incorporated into the project design. c. The existing moist soils and groundwater condi- tions in the canyon areas will be more fully :0 l 0 0 • o, o. O• O' lo I I 10 22 explored to determine the need for subdrains and similar design features to ensure fi 11 slope sta- bility and stable ground conditions. d. Areas requiring fill will be more precisely deter- mined in conjunction with. the grading plan and more detailed project des i gn. This study 1'/i 11 include detailed estimates of the amount of fill required and the percentage of settlement subsi- dence expected after recompaction. e. All onsite soils will be further analyzed to determine their potential constraints on develop- ment (i.e., expansiveness, erosiveness, etc.). Based on this analysis, appropriate soils engi- neering procedures (i.e., recompaction, removal, selective grading) will be formulated. f. Other than the lithological offset observed in the north-central portion of the site,. no onsite sur- face faulting has been observed during field reconnaissance or review of aerial photos. How- ever, to assure the complete absence of signifi- cant onsite faulting, further review of those areas outside the area covered by the previous seismic study (Geosoils, 1980c) should be under- taken. In addition, all parcels will be scruti- niz.ed· dur-ing .grading for subsurface faulting by the City1s construction inspector. If such fault- ing is evidenced, immediate analysis will be con- ducted to determine the significance of the fault- ing and any measures necessary to minimize hazards. g. Based on results of the studies relating to land- slide characteristics, moisture conditions, soil cha racteri st i cs, and f i 11 requirements , appropri - ate engineering procedures will be formulated for stabilization of all cut slopes. 2. A 11 grading ope rat i ans wi 11 be in fu 11 conformance with City ordinances pertaining to grading. The grading proce- dures wi 11 be reviewed by the City for conformance with City ordinances and the recommendations and cone 1 us ions of lsa I I I 0 0 I lo f 0 • 0 ' a ' 0 d d 23 all geotechnical studies submitted at the time of subdivi- sion map submittal. 3. All structures will conform to the Uniform Building Code and all applicable building and safety code requirements . 4. Si gni fi cant cut and fi 11 (30 feet or greater in depth) wi 11 be confined to limited areas according to the Rancho Car- rillo Master Plan's landfonn modification concept to mini- mize disturbance of steep natural slopes. lsa These measures, when implemented, wil_l adequately mitigate the adverse impacts associated with potential onsite hazards r~lated to slide areas, soils conditions, cut slope instability, groundwater conditions, local and regional seismic conditions, and fill requirements. However, these measures will not completely mitigate .the adverse impact associated with substantial alteration of existing topography. WATER RESOURCES Setting. Rancho Carrillo is located within two drainage systems. The property north of Palomar Airport Road drains into Agua Hedionda Creek, flow- ing ultimately into Agua Hedionda Lagoon. The majority of the property is drained by San Marcos Creek, which drains into Batiquito~ Lagoon. Surface Water ··gualit~. Agua Hedionda Lagoon is about 230 acres in area. The lagoon was create in its present state by a major dredging pro- gram in the· early 1950s ,· and its channel to the ocean is kept open permanent- ly by periodic maintenance. The lagoon has a number of di verse uses. It serves as a public recreation area (ffshing, swimming, and limited boating), as a limited commercial shell fishery, and as a source of industrial cooling water for the Encino power plant. Batiquitos Lagoon, located between the City of Carlsbad on the north and the community of Leucadia on the south, consists of 600 acres of la goon and salt flats. Eutrophication has been a constant problem in the lagoon, con- tributing to bottom sludge deposits, odor, and insect problems. Efforts to restore tidal action by bulldozing at the lagoon mouth have been thwarted by the height and width of the beach barrier, the cobble bar under the beach, and the small size of the lagoon's tidal prism. Existing background levels of pollutants are not knbwn. It is likely that the existing pool of nutrients is sufficient to sustain eutrophic conditions even if the storm loads were elimi- nated completely (Daniel et al., 1978). 0 0 I' 10 0 0 • , ' • o, 0• o· 24 lsa The Regional Water Quality Control Board (RWQCB) has identified existing and potential beneficial uses for surface water of each hydrographic subunit. There are six existing beneficial uses identified for the inland surface waters of the San Marcos drainage system (Montgomery, 1975). These are: • 1. Agricultural supply, including crop, orchard, and pasture irrigation, stock watering, support of vegetation for range grazing, and all uses in support of farming and ranching operations. 2. Water contact recreation, including all recreational uses involving actual body contact with water, such as swimming, wading, water-skiing, skin-diving, fishing, use in thera- peutic spas, arid other uses where ingestion of water is reasonably possible. 3. Non-contact water recr~ation, including recreational· uses which involve the presence of water but do not require con- tact with water. Examples are picnicking, sunbathing, hik- ing, camping, pleasure boating, hunting, and aesthetic enjoyment ~nd sightseeing •. 4. 5. 6. Warm freshwater habitat, provided for aquatic resources associated with a warm-water environment. Wildlife habitat in the form of water supply and vegetative habitat fQr wildlife. Preservation--of aquatic habitat necessary, at least in part, for the survival of certain species established as being rare and endangered. The Agua-Hedionda drainage system provides all of the above beneficial uses assigned to the San Marcos sub-unit, along with the two additional uses of municipal and domestic supply arid industrial supply. No potenti-al uses have been identified for either the San Marcos or the Agua-Hedionda drainage systems. Groundwater Quality. Existing beneficial uses· identified for groundwater within the San Marcos and Agua Hedionda basins include municipal supply, agricultural, and industrial uses. Groundwater quality in the area is generally poor. High TDS (total dissolved solids) concentrations are due to limited rainfall and importation of Colorado River water for irrigation (Montgomery, 1975). ,0 I 0 0 0 0 0. 0. a 25 lsa Hydrology. At least four ephemeral 'streams transverse the Ran- cho Carri 11 o property. The major stream, running through the center of the site, is impounded at several locations in the property 1 s major valley. The largest of this series of earthen impoundments was believed to pose a hazard due to high saturation of the berm and its instability. 0nsite examinations suggest that the dam 1 s foundation was subject to failure, and the reservoir behind it contributed to higher than natural groundwater levels downstream, possibly contributing to landslides on downstream slopes. At the recommenda- tion of Geosoils, Inc., therefore, this berm was recently breached in a con- trolled effort to remove the hazard (Geosoils, 1979e, 1980a). A drainage study was prepared for the site (Leedshill, 1981) to determine the needs and dimensions of storm drains and detention basins (Appendix A). The study identifies peak flow rates and volumes for both 10 and 25-year torms on the property with existing and proposed uses. The study 1 s recommendations conform to the California Coastal Commission 1 s policy (adopted as the City standards for this project) requiring that the peak rate of runoff from the 10-year storm be no greater after development than before. The drainage study also adopts the criterion that detention basins can safely pass runoff from a 200-year storm. The City Engi_neer reviewed the study and found it adequate in both approach and criteria. According to the County of San Diego, Department of Sanitation and Flood Control, the project is outside of any designated floodplain area (Hill, 1980 in Appendix J). Impacts. Surface ·water •• Qua 1 itY. Project development wi 11 effect an increase in urban pollutants in runoff. Increased impervious surfaces and associated motor oils, fuel, asphalt, detergents, fertili_zers, pesticides, and other domestic chemicals will incrementally degrade local water quality. 0nsite grading will create a short-term. potential for erosion. If not properly controlled, onsite erosion could increase sedimentation in downstream waters, such as Batiquitos and Agua Hedionda Lagoons. Although this effect might be only incremental, the cumulative effect of this project in concert with others in the drainage basin could have a significant adverse impact. Long-term cumulative effects on Batiquitos and Agua Hedionda lagoons will result from increased urbanization in the area and an accompanying decrease in agricultural land use. Projected cumulative effects include a 30-35% reduc- tion in tota 1 suspended so 1 ids and nutrient 1 oads. The decrease in nutrient loads can only be beneficial to the problem of eutrophication in Satiquitos ,0 I I ! 0 0 0 0 I 0, 0 :o I 0 I I I ,0 0 26 lsa Lagoon, but this effect is thought to be unsubstantially small. Heavy metal loads are estimated to increase about 100%, resulting in a long-term cumula- tive adverse impact (Daniel et al., 1978). Development of Rancho, 'Carrillo will contribute incrementally to this ~umulative adverse impact. 1 Groundwater Quality. Since the project will be completely sew- ered and no septic systems or leach • lines are p 1 anned, no change in ground- water quality is anticipated. Hydrology. Development will increase storm runoff from the site as a result of increased impervious surfaces. Development will require con- struction of storm drainage facilities, including at least three detention basins. The drainage study (Leedshill, 1981) presents two alternative drain- age control designs. Both designs are capable of mitigating stormwater runoff so that peak flow levels do not exceed existing peak flows. 0nsite agricultural impoundments will be removed. Since· these impound- ments are not hydrological in function; their -removal is expected to have no significant adverse impacts on onsite or offsite hydrology. 0nsite ephemeral streams may be diverted into the storm drain facilities. Effects of this diversion on the hydrological regime are expected to be minimal. • I M. ) . . M 1t1gat1on easures. 5. The developer will incorporate a drainage. control system which wi 11 ensure that peak runoff rates from the 10-year storm after development will not exceed existing 10-year storm· peak fl ow rates. Detention basins wi 11 be des i gned to pass runoff safely from a 100-year storm. The drainage control system will be maintained by an assessment dis- trict. 6. A complete erosion control program to minimize the poten- tial for erosion during development will be approved by the City of Carlsbad prior_ to issuance of the grading permit. This erosion control program will be enforced continuously • during ·grading operations and between grading phases. This program will. include provisions for construction during non-rainy periods, immediate planting of vegetation on all exposed slopes, temporary sedimentation basins (if neces- sary), and ·a watering and compaction program. • 7. After development, a weekly streetsweeping program will be implemented in the project area for all internal roadways 0 0 0 0 0 ' 0, 0 I 1 0 27 to reduce the urban pollutants which would pollute surface runoff. 8. A detailed hydrological and drainage control analysis will be conducted by the project applicant and submitted to the City for review at the time of submittal of the.subdiv1sion map. The study shall identify necessary onsite flood con- trol measures. The study shall also identify measures for assuring that onsite runoff wi 11 not adversely affect off- site areas. Changes in groundwater levels due to grading and the removal of onsite impoundments must also be analyz- ed. The report will also examine hydrological effects of diverting the streams onsite. Results of this. study will be incorporated into the project design to the satisfaction of the City Engineer. lsa Upon implementation; these measures wi 11 adequ~tely mitigate any poten- tial adverse impacts associated with alterations to onsite hydrological condi- t i ans due to development. They wi 11 a 1 so assure that the development wi 11 be protected from significant flooding hazards. Mitigation Measure #6 will ade- quately mitigate adverse impacts associated with the potential increase in erosion on the project site. It will assure that the project will not con- tribute significantly to increased sediment levels in Batiquitos Lagoon. Mit- igation Measure #7 will partially reduce the amount of urban pollutants expected from development of the site. Although not a significant increase by itself, the project-related increase in urban pollutant levels may still ·con- tribute to a cumulative adverse impact on Batiquitos Lagoon associated with the developing region.-,. ··· BIOLOGICAL RESOURCES A bi al ogical study conducted in April 1980 assessed the project site I s biological resources. The study included a field survey and a survey of rele- vant literature (REC0N, 1976). The complete study, including a list of repre- sentative plant and wildlife species, appears in Appendix B. Setting. As indicated in Figure 9, four major biotic communities occur on the project site: 1) coastal sage scrub, 2) riparian, 3) freshwater marsh, and 4) int.reduced grassland. Si nee the ti me of the April 1980 field survey and the writing of the biological report, the major agricultural 111ater impoundment on the property has been breached, allowing the water to flow downstream to remove 111hat was believed to be a hydrological hazard (see \·Jater Resources section; Geosoils, 1979e, 1980a). As a result, most of the fresh- water marsh plants were removed, and much of the riparian habitat at the • • ' • LEGEND □ d Grassland Introduce ~ Coastal Sage ~ Riparian Etf:d Freshwater Marsh tJ] Rural Ruderal g Urban 28 lsa 0 2<Xf wr---- 0 0 0 0 • Q· 0, I I d l " 0 29 lsa impoundment is expected to suffer; the communities onsite are, therefore, in a state of flux. Coastal Sage Scrub. Characteristic of dry, rocky hillsides in ~.outhern California below 3,000 feet, coastal sage scrub occurs scattered throughout the site on steeper hillsides and in drainages. This community typically consists of half-woody shrubs, two to five feet tall, growing close together. Indicative dominants include California sagebrush (Artemisia cali- fornica), black sage {Salvia mellifera), and California brittlebush (EncelTa californica). Groundcover consists of introduced grasses and forbs. Coastal sage scrub is a productive habitat throughout and supports a sur- prising diversity and abundance of wildlife, including many reptiles, small animals, and birds. Riparian Community. Dominants of riparian communities in South- ern California include coast live oaks (Quercus agrifolia) and willows (Salix spp.). Small shrubs provide a dense and bushy understory. Riparian species occur onsite around the impoundment basins and ~long the stream course. The habitat along the stream course has been degraded by human disturbance (clear- ing and dumping). The impoundment habitat is of limited size and almost entirely caused by the artificial impoundment •. Most of this habitat, except for the more deep-rooted species, will disappear as a result of the impound- ment 1s breaching. Consequently, the riparian communities onsite are believed to be no more valuable than the surrounding habitats. Freshwater· Marsh. This community occurs at the breached dam site. Freshwater marsb-1s compos~d of emersed aquatic plants and plants grow- ing in permanently saturated soils. Dominants include cattail (~ latifo- lia) and Olney bulrush (Scirhus olneyi); willows and mulefat (Baccharis gluti- nosa) are also common. Fres water marsh communities serve as habitat for many wildlife forms, particularly amphibians, which could not survive otherwise. The habitat onsite, however, is in a_state of rapid change and will soon dis- appear due to the removal of the impoundment. Willows and cattails will dry up; bulrushes wi 11 disappear. The marshland and area of former open water will be replaced by a ruderal sere of mulefat, sweet fennel (Foeniculum vul- gare), curly dock (Rumix crispus), and wild radish (Raphanus sativus), with introduced grasses and other weedy species finally reverting to coastal sage scrub. Introduced Grassland. This community is the most common vegeta- tion on the Rancho Carrillo property. Its dominants consist of adventitious species that replace native vegetation following clearing and include ripgut- grass (Bromus diandrus), reo brome (Bromus rubens), and slender wild oats 0 ·" 0 0 0 0 ;O 0 0 I 0 0 0 30 lsa (Avena fatua). These grasses occur onsite over lower h_illsides and slopes. They provide habitat for a small number of wildlife species, which occur in high numbers, and foraging habitat for birds of prey. Species. Appendix B contains a species list of dominant and common plants and representative wildlife expected to occur onsite. In addi- tion, several plant species which are on the California Native Plant Society's (CNPS) 1 i st of rare and endangered species have been noted by CNPS to occur within a few miles of the site. These species include Del Mar manzanita (Arc- tostaphylus glandulosa var. crassifolia), adolphia (Adelphia californicaT, pygmy spikemoss (Selaginella cinerescens), and summer holly (Comarostaphylos diversifolia var. diversifolia), which is of concern to the CNPS, but not yet listed. Adelphia and pygmy spikemoss have reportedly been sighted during an unrelated study on the site (Bramlett, personal communication). Small popula- tions of one or more of the other species could have gone undetected. None of these species is on either the Federal or State list for rare, endangered, or threatened species. The CNPS list is only advisory and, according to the list, the two species sighted are common elsewhere (CNPS, 1980). Impacts. Mass grading will strip the site of most existing vegeta- tion. lliversion of the ephemeral streams underground for drainage control will eliminate remaining riparian habitats .. Wildlife species will drastically diminish onsite. Urbanization of the site will also indirectly impact wild- life offsite as animals and birds will avoid the urbanized site. The intro- duction of domestic predators (cats and dogs) will effect an incremental loss of hunting territory for rapt ors offs i te and in preserved natu ra 1 veg et at ion areas onsite. Open-space stands of preserved vegetation wi 11 be subject to foot traffic. from __ th~. development's residents. Roadside kills of wildlife will increase as a result· of traffic entering and leaving the development. Mitigation Measures. 9. The areas designated as "natural terrain" in the conceptual grading plan will be preserved as areas of natural vegeta- tion. This will partially mitigate the impact of removal of vegetation by mass grading onsite. The areas of coastal sage and riparian vegetation that will be preserved within areas of natural terrain are illustrated in Figure 10. 1 \ These areas will also provide potenti-al habitat for those species, of concern to the California Department of Fish and Game and the California Native Plant Society, which are believed to possibly occur onsite or within a few miles of the site. These natural terrain areas could be used for transplantation areas to serve as habitat for plants threatened by regi anal development. • 31 10 Areas of Preserved Natural Vegetation lsa LEGEND ~ Rlpari~n ~ Coastal Sage ~ Are~s to be Preserved :~ :-:,~~;C/¼~., _·. ~~ \ .,,, .. ,,\, \, ,...,../'· ~ >., .✓.::, ""'· ~~~.....-::;;; --, .. ----5 .. , I I j /4.-~--.,,.,. - -~-, . ·( 0 200 -EB ~ Q)0' 0 0 0 0 0 0. 0 0 i !o 0 0 32 10. The developer will examine the feasibility of incorporating. natural drainage swales into portions of the drainage con- trol system and preserving these swales as areas of natural vegetative habitat, particularly in the area of existing riparian vegetation that p·ara 11 e 1 s the future a 1 i gnment of Carrillo Way, west of the existing Carrillo Ranch. Should implementation of this measure be found feasible without exposing the development to significant flood hazards, the preserved riparian habitat should then be upgraded by removing rubbish and ruderal species and limiting human disturbance. If implemented, this measure would partially mitigate impacts on riparian habitats onsite. -11. The project applicant is required to apply for a 1603 per- mit from the California Department of Fish and Game for all disturbance and destruction of onsite creeks and water impoundments. The project app l i cants wi 11 be requ i red to incorporate all permit conditions formulated by Fish and Game into the project design. 12. Landscaping around the retention basins to be used for flood control purposes will be comprised of 100% native vegetation. lsa These measures will partially mitigate expected adverse impacts on onsite biological resources. However, there will still be unavoidable adverse impact on biological resources associated with the loss of onsite habitat and dis- placement of wildlife. -__ CULTURAL RESOURCES In 1976, RECON conducted an archaeological survey of Rancho Carrillo (RECON, 1976). An additional study for an unrelated project was prepared by Neste, Brudi n and Stone in 1979 (Neste et a 1 • , 1979). Recently, WESTEC Ser- vices reviewed these reports and performed additional field surveys to confirm the adequacy of the previous studies (WESTEC, 1979). The RE CON and WESTEC reports appear in Appendix C; Neste, Brudin and Stone 1s report is on file for public review with the City of Carlsbad. Setting. The combined archaeological studies indicate that 28 arch- aeolog.ical or historical sites exist on the-,Rancho Carrillo property. These sites are listed in Appendii C (WESTEC, 1979). The majority of the site~ are small, light concentrations of artifacts or shell and have limited archaeolog- ical potential. Several are isolated finds of debitage or flakes. There are two archaeological and two historical sites of significance. 0 0 0 0 ' Oi o, o· .. 0 33 lsa Site CA-S0i-4396. This site was or1ginally recorded in 1976 and resurveyed in 1979 by \~ESTEC Services. The site encompasses approximate 1 y 4,000 squar·e meters and an approximate depth of 35 centimeters. Artifacts include highly patinated felsite scrapers and flakes, basalt debitage, and a· broken blade fragment. Carbon-14 studies from shellfish remains indicate a dating of 6880 (±_280) B.P. Site CA-S0i-4687. This site has been ca 11 ed "the most substan- tial preh1stor1c archaeological resource on the subject property" (REC0N, 1976). The site includes 200 square meters of midden, approximately 40 centi- meters in depth. Among the artifacts already noted are a wide variety of lithic artifacts, including scrapers, hammerstones, manes, and both primary and secondary flakes and cores. Site CA-S0i-4690. Resources found on this site include 20 flakes and debitage and a wide variety of shells. The 300-square-meter site may contain culture-bearing overburden. Carrillo Ranch (Rancho de las Quiotes). This historic site, located in the central portion of the property, is the remains of a restored early California rancho and consists of a main house and various outbuildings, including a barn and guest house. Rancho de l os Qui ates (Ranch of the Dag- gers) was part of the Agua Hedionda Land Grant. In the 1860s, Matthew Kelly, Sr. built the ranch house as his private residence. Following his death, Kelly's descendants abandoned the area, and the structures fell into disre- pair. In the 1930s, Lep. Carri.11.o purchased the property. Carri 11 o restored the ranch structures with the intent of rec re at i ng and preserving an "e 1 ement of California history."· The ranch area has been well preserved since Carrillo's death in 1961, and is presently being nominated to the National Register of Historic Places. Site CA-S0i-4683. This site is an historic wooden cross set in a plastered adobe block base atop a hill overlooking Rancho de las Quiotes. Structural features, such as plaster, nuts and bolts, and milled wooden compo- nents, and the lack of historical reference to the cross, indicate that it was constructed during Leo Carrillo's occupation of .the property rather than Kelly's earlier use in the 1860s. Lesser Sites. Some of the remaining sites contain light concen- trations of artifacts or shell fragments which may have archaeological signif- icance. These have been registered with the California Archaeological Survey and include sites CA-SDi-4679, 4684, 4685, 4686, 4688, 4689, and 4691 . 0 0 0 0 o. a 0 0 0 0 0 34 lsa Impacts. Implementation of· the proposed Rancho Carrillo development will destroy all or most of the archaeological sites identified within the project area. Mitigation Measures. 13. A qualified archaeologist will investigate sites CA-SOi- 4306, 4687, and 4600 to determine their significance and research potential. These sites will be preserved if pos- sible; if not, a qualified archaeologist will test and excavate. 14. Carrillo Ranch (Rancho de las Quiotes) will be preserved as part of a 20-acre City park. The developers propose to move the historic cross to within the City park fq,r perma- nent preservation. 15. A qualified archaeologist will conduct the surface collec- tion and analysis of shell scatters on CA-SOi-4679, 4688, and 4689 prior to issuance of a grading permit. 16. Sites CA-SOi-4684, 4685, 4686, and 4691 will be mapped with all shell scatter flakes, cores, tools, scrapers, and debitage collected by a qualified archaelogist prior to issuing a grading permit. Implementation of these measures will adequately mitigate any potential adverse impacts on the archaeo.logical resources of the site. PALEONTOLOGICAL RESOURCES A certified paleontologist has made a preliminary evaluation of the kno\'m and potential paleontological resources of Rancho Carrillo based on a review of published and unpublished literature and data. This preliminary study appears in Appendix O. Setting. The property is underlain by unnamed Eocene sands (38 to 55 million years old) that have been correlated to the Santiago Formation of Orange County. Eocene rocks have produced numerous si gni fi cant fossils from several localities, including several new forms of extinct reptiles, birds, and mammals, uncovered in conjunction with the Laguna Riviera development in the City of Carlsbad. The Laguna Riviera site is the closest recorded fossil occurrence to Rancho Carrillo. Since Rancho Carrillo lies within a district that has a history of producing numerous significant fossils, it is highly I I I • 0 0 • 0 • 0 0 o' 35 lsa probable that somewhere within the 846 acres of the site there are fossil remains and that some of them are significant. Impacts. Mass grading and construction on the site would displace or permanently cover areas that have a potential for bearing significant fossils . Golz and Lillegraven (1977) pointed out that in order to improve correlations of the Eocene sands of the Carlsbad area with other uni ts of similar age, additional fossils are necessary from other localities. Since it is possible that fossils likely to be present at Rancho Carrillo could provide information significant to this issue, loss of resources onsite must be considered poten- tially significant. However, it should be noted that the exposure of fossils may occur during development. This could be considered a positive impact since some fossils which otherwise would remain buried will be exposed and made available for scientific study. Mitigation Measures. The following mitigation measure is proposed to mitigate impacts on paleontological resources onsite. 17. A certified paleontologist will perform a walkover survey of the site in order to locate and define areas of paleon- tological sensitivity. The paleontologist will submit a written report to the City Planning ·Department prior to issuance of the grading pe'rmit. Any fossils located dur- ing the survey will be collected prior to grading. The paleontolo9:is.t. will be present at all pregrade meet- ings to determine the necessity for a paleontological observer during various phases of grading. This determi - nation will be based on the findings of the walkover sur- vey and grading plans. The observer will be allowed to divert, direct, or halt grading in a specific area to allow for the expeditious salvage of expos~d fossil materials. Fossils collected will be donated to a public non-profit institution such as the San Diego Natural History Museum, the Paleobiology Department of San Diego State University, or the Natural History Museum of Los Angeles County. Implementation of this measure will adequately mitigate any potential adverse impacts on paleontological resources. 0 0 0 0 0 ' 0 0 d 36 lsa LAND USE Setting. Existing land uses on the Rancho Carrillo property include open space and some very limited agri cul tu re. Land to the west and east of the project is also undeveloped with limited agriculture. These parcels are in unincorporated San Diego County and are designated in the County's General Pl an as intensive agri cultural to the west and medium residential to the east . Immediately north of the project site is the Carlsbad Raceway. This area is in the City of Carlsbad and is designated as recreation commercial (RC) in the City of Carlsbad's General Pl an. Paree ls south and southwest of the project are also within the Carlsbad limits. These areas are designated as planned community, and their existing land uses include the Rancho La Costa community. Future North La Costa residents will also eventually border the site. There is existing residential devleopment within the City of San Marcos southeast of the project site. Existing land use north of the Carlsbad Raceway is open space. This area is within the limits of the City of Vista and is designated as open space and industrial park. Additional proposed .land use north of the Raceway includes the future alignment of Melrose Avenue. The City of Vista's proposed align- ment of Melrose Avenue transects ·the existing racway, while Carlsbad's align- ment skirts outside the raceway's perimeter. These two alignments therefore present a potential conflict in land use north of the project site. The project site is within 2-1/4 miles of Palomar Airport, located at the northwest corner of the El Camino Real/Palomar Airport Road intersection (Fig- ure 2). The San Diego Airport Land Use Commission prepared a comprehensive land use plan for Palomar Airport in 1974. The report .,.,as prepared to assist in achieving compattble· land use development in and around Palomar Airport. The report defined an "airport influence area" based on a projected 1990 air- port operation level of 435,000. operations. This "airport influence area" was defined on the basis of projected noise levels and crash hazard areas. A very small portion of the Rancho Carrillo properties is located within this influ- ence area. The portion is north of Palomar Airport Road along the '"'estern boundary of the project site. This area is in the 110 l II zone described as "minimal crash hazard, low noise impact, and compatible with all types of development including residential, industrial, office, institutional, recrea- tional, and commercial. The County of San o;.ego is currently seeking Federal funding to conduct an Airport Noise Control and Land Use Campa ti bil ity Study (ANCLUC) in 1981. . This study is expected to be available late 1981 or early 1982. The ANCLUC ' will essentially replace the existing Comprehensive Land Use Plan. The study 0 0 0 0 I 0 o. 0 0 0 has not yet begun. this time. 37 lsa Consequently, preliminary results are not available at Imtacts. Adoption of the Master Pl an and General P 1 an Amendment for Ranchoarrillo represents steps toward implementation of the current Planned Community zoning for the site. The major direct impact of implementation will be the introduction of residential, commercial, and industrial land uses on the site. These new uses will displace the current uses of limited agricul- ture and natural open space. The proposed change in land use has implications for all aspects of the natural and manmade environment. These impacts and necessary mitigation measures are discussed in the appropriate sections throughout this report. Additional impacts associated with the project include possible incompat- ibility with offsite agriculture. Agricultural activities, such as crop spraying and noise and dust-from agricultural machinery, may prove incompati- ble with residential land use. Conversely, residential uses may have adverse impacts on agricultural practices. General Plan. Figure 4, Page 8 under Project Description sec- ·tion, illustrates the existing General Plan and the proposed General Plan Amendment for Rancho Carrillo. Pages 2, 3, and 9 contain a description of the proposed General Pl an Amendment. Briefly, the General Pl an Amendment would allow for fewer dwelling units at a lower density on a larger amount of acre- age. It increases the overall amount of commercial (neighborhood, community, travel services), although there is some adjustment within the specific types of commercial land uses. The special treatment area has been defined as planned industrial and community coinmercial. The existing General Plan shows two elementary school sites t~talling 18.7 acres, while the proposed amendment provides for a single centrally·-located 14.6-acre elementary school site. There would be a reduction in designated open space and recreation commercial under the proposed amendment. Also, the Parks and Recreation Element shows a 7-acre park at the southwest corner of future Melrose Avenue and Carrillo Way. Under the proposed amendment, an 8.2-acre park would be provided irrmediately west of the Carrillo Ranch and south of Carrillo Way. Configuration of 1 and uses are bas i ca 11 y the same under the amendment with some minor modifications as illustrated in Figure 4, Page 8. The proposed General Plan amendment appears to be compatible with land use plans for the surrounding areas under the jurisdiction of the City of Carlsbad, County_ of San Diego, City of Vista, and City of San Marcos. 0 0 0 0 0 • 0 0 0 0 b 0 38 lsa Review of the proposed General Plan Amendment in comparison to the exist- ; ng Genera 1 Pl an shows few significant env i ronmenta 1 differences. The pro- posed nature of the area will remain the same, primarily residential to the south and non-residential to the north. With the proposed lower densities and fewer dwelling units, the small reduction in designated open space is not con- sidered significant. Designated open space will still comprise 21% of the total acreage of the site. Consolidation of the two school sites into one centrally located facil~ty also does not appear to have a potential land use impact. The site is adja- cent to landslide prone areas, but with the adequate stabilization measures required, this will not pose a hazard. For a more detailed discussion of educational facilities and needs, please see the Community Services and Public Utilities section of this report. The relocation of the park to a new location does not pose any 1 and use incompatibilities. It is adjacent to the proposed recreation commercial area and the City-owned Carrillo Ranch Historic Si"te. Some concern has been expressed as to the soils condition of the site. Geotechnical studies indi- cate that .the site can be feasibly developed, although soil treatment and site preparation may be costly in comparison to more stable sites. However, the. presently designated park site is located within an existing landslide area which will also require extensive site preparation. The proposed general plan amendment realigns Melrose Avenue north of Pal- omar Airport Road along a slightly more northerly course. The existing Gener- al Plan shows Melrose Avenue skirting around the western edge of the Carlsbad Raceway. However, this alignment does not appear to be consistent with the city of Vista's alignment of Melrose Avenue. The Carlsbad alignment appears to be +500 feet to the west of the Vista alignment at the City boundary. The proposed alignment (as far as it is indicated) appears to be able to align to Vista's alignment of Melrose Avenue. However, this might adversely impact the operations of the Carlsbad Raceway by crossing over the western portion of the raceway area. Until the City conducts further studies as to the most appro- priate alignment of Melrose Drive in the raceway area and connecting to Vista's alignment, further analysis is not possible. Master Plan. The proposed revised Master Plan is consistent with the proposed General Plan Amendment. As such, the above discussion also pertains directly to the proposed Master Plan. The proposed Master Plan is illustrated in Figure 3 and described on Pages 2 and 7. In comparison to the 1972 adopted Master Plan for the site, the revised Master Plan includes planned industrial uses where the previous plan indicated 0 0 0 q Q 0 0 i lo I I 6 • 0 39 lsa non-residential. It also allows only 2,998 dwelling units (3,122 units including the school site conversion units) as compared to the adopted plans allowance of 3,695 dwelling units. Allowable densities under the adopted plan were slightly higher than now proposed. As discussed above, under the adopted plan, two school sites are shown and a park site is located at Melrose Avenue and Carrillo Way. The revised Master Plan reflects a single, central school and a park west of the Carrillo Ranch. No adverse land use impacts were found in the comparison of the adopted and proposed master plans. Palomar· Airport. The project as proposed is not incompatible with the adopted Comprehensive Land Use Pl an for Pa 1 omar Airport. Based on noise studies conducted for this project, it is also not expected to be incon- sistent with the results of the proposed ANCLUC. Please refer to the Noise section of this report for a more detailed discussion of airport-related noise. Mitigation Measures. The following mitigation measure is proposed to offset any potential adverse impacts. 18. The proposed Master Pl an wi 11 be submitted to the Airport Land Use Cammi ss ion for review prior to approv a 1 of the project. 19. The developer will provide an' adequate buffer to mitigate potential incompatibility between proposed residences onsite and existing agricultural land uses offsite. Appropriate buffers to be considered include construction of a 6-foot block wall dividing the two land uses and, if aerial praying occurs over the adjacent agriculture, an open space. buff er of 150 feet or p 1 a cement of a roadway between the two uses. · The adequacy of the buffer wi 11 be reviewed by the City at the time of subdivision map appli- cation. 20 .. The City will conduct a study to determine the most feasible alignment of Melrose Avenue through the Carlsbad Raceway and connecting to the City of Vista. Currently, the City of Vista is reviewing a Master Plan for the area just north of Carlsbad Raceway which indicates a fairly precise aligm:nent consistent with the Vista General Plan. 0 I 0 0 0 0 i 0 l 0 0 0 0 0 40 Consequently, it behooves the City of Carlsbad to study carefully the compatibility of its alignment. As dis- cussed above, preliminary analysis indicates that the pro- posed Rancho Carrillo alignment can be extended across the raceway so as to align with the Vista alignment. It also appears that a slight modification of the adopted align- ment necessary to a 1 i gn with the Vista route may a 1 so impact the raceway. However, further engineering studies by the City need· to be conducted before a definitive determination can be made. lsa These measures, when implemented, will assure that no significant adverse impacts associated with land use issues will occur as a result of this proj- ect. The one. exception to this may be the possible disruption of recreational operations within Carlsbad Raceway as a result of the realignment of Melrose Avenue. However, it is possible this may occur even without the requested realignment if the City must modify the route of Melrose Avenue to align with Vista's Melrose Avenue. VISUAL AND AESTHETIC ASPECTS Setting. Rancho Carrillo is presently vacant land with the exception of the ranch house and the few dirt roads leading to it. Hillsides are cov- ered with grassland and natural vegetation, and valleys are covered with grassland, riparian plants, and ornamental species. The site sits below the bordering hills and is visible only from the property's perimeter, from adja- cent hillsides, and from a brief stretch of Palomar Airport Road. The proper- ty as a who 1 e serves·· as an. iso 1 ated setting for the ranch house, the Rancho's centerpiece. From • the Rancho, there are views of the bordering hi 11 s and adjacent property to the south. Impacts. Development of Rancho Carrillo would irrevocably change the site's appearance. A suburb~n landscape of roadways and houses would replace the open hi 11 s and va 11 ey.s ~ •• The i so 1 ated character of the Rancho and its ranch house would be lost. The ranch house, in its confined park setting among the suburbs, might well seem anachronistic and unnatural in contrast to the return to the past it was originally intended to elucidate. Because of the site's topographic setting, visual impacts from offsite will be limited to the ·views from Palomar Airport Road and properties inme- diately adjacent to the -site. Onsite topography will be altered by mass grad- ing and grading for building pads and street grades. 0 0 0 0 0 0 0 41 lsa Natural and introduced ornamental vegetation will be stripped from the 1 and scape. Ephemeral watercour~es will be diverted underground; their asso- ciated vegetation and wildlife wi 11 be removed or reduced ans ite. Mitigation Measures. 21. An 8.2-acre park site adjacent to the Leo Carrillo Ranch City Park will partially mitigate the transition in land use between the historic ranch house and surrounding com- mercial and residential areas. 22. Greenbelts and natural open spaces will be included in the development in accordance with the propo.sed Master Pl an. Although open space will obviously be reduced by the proj- ect, this measure will partially mitigate the total visual impact. These measures will partially mitigate impacts on the visual and aesthe- tic resources of the site. However, it is unavoidable that the character of the site will be irreyocabl~ altered. TRAFFIC AND CIRCULATION Technical traffic input for this report has been provided from several sources. Weston Pringle and Associates, representing the project applicants, has prepared both a draft and a final report. The final report, dated March 16, 1981, is included in Appendix E. o The City of Carlsbad Engineering Department, and the City• s traffic con- sultant, Berryman and Stephenson,.· Inc. (BSI), have reviewed the draft and final reports and have prepared written comments. These corrrnents are included in Appendix F. Where the recommendations of the applicants• traffic engineer differ from those of the City, the EIR attempts to explain the differences and 0 includes mitigation measures requiring their resolution. Setting. The site is currently undeveloped and is served only by Palomar Airport Road, which has been improved to two lanes in the vicinity of the project. An unimproved dirt road leads from Palomar Airport Road to the • Rancho Carrilld ranch house in the center of the site. The existing traffic volume along Palomar Airport Road is estimated to be 12,500 average daily O traffic (ADT). • 0 Proposed Circulation System. Figure 11 i 11 ustrates the proposed cir- culation system intended to serve the project site and the vicinity. The City 0 0 0 0 0 0 0 0 42 1 1 Proposed Circulation System LEGEND I \ ' ' ' ... ' ' \ \ \ \ I I I , ....... / I I \. .,,.'!' ,' --i I l I I I I I I I -----➔--... --------: \ \ \ .. . --·--··· •.. • \ ____ :. ~---•·-J· Source: Weston Pringle & Assoc. ~ Existing roadway, or proposed on-site impro- ments ,-Proposed off-site, or ~ necessary-to-complete improvements • • lsa ♦ N No scale -Prime arterial roadway I I 0 0 0 I 1.0 0 0 0 0 0 43 lsa- of Car.lsbad's General Plan classifies Palomar Airport Road and Melrose Avenue as prime arterials, and Alga Road as a major arterial. It also classifies Carrillo Way and El Fuerte Street as secondary arterials. Solid lines in Fi.gure 11 indicate existing or proposed onsite improve- ments. The only existing facilities are Palomar Airport Road,· a portion of El Fuerte leading to Alga Road, and Alga Road westerly of El Fuerte Street. Dot- ted lines illustrate proposed offsite improvements necessary to complete the ultimate roadway system. The traffic study completed by Weston Pringle and Associates was based on this proposed circulation system. Impacts. Trip Generation. The first step in determining the effect of the proposed project on the local circulation system is to estimate the number of trips that will be generated by the project. Numerous studies have. been con- ducted by governm~nta 1 agencies and consultants to determine appropriate trip generation rates for various land uses. Based on. these studies, the rates sunmari zed in Tab 1 e E -wer~ ut i 1 i zed in the traffic study. Since definitive land use data were not available for the commercial rec- reation areas, the following assumptions were made for purposes of the traffic study. Soil conditions in t_he areas designated for conmercial recreation would generally preclude major structures on these sites. It was assumed that racquetball courts would be a typical use of the sites. Potential uses were assumed to serve primarily_ the adjacent areas and would not attract regional usage. Consequently, they are not expected to impact the external roadway system. No estimate was made for the ranch house site as no applicable trip gen- eration rates are available. However, this use is expected to have a negligi- ble impact upon the street system. By applying the trip generation rates to the proposed land use quanti- ties, as described in the proposed Rancho Carrillo Master Plan, estimates of daily and peak-hour trip generation for the· project were obtained. These estimates are .surmnarized in Table F. According to these estimates, the proj- ect would generate 53,840 daily trip ends upon completion. There would be 3,060 trips occurring during the a.m. peak hour and 5,780 trips occurring dur- ing the p.m. peak hour. 0 0 TABLE E 44 TRIP GENERATION RATES lsa 0 Rates1 Land Use Descrietor Daill A.M. In A.M. Out P.M. In P .M. Out Low-density 0 residential Dwelling unit 11.0 0.2 a.a a.a 0.2 Medium-density residential Dwelling unit 7.5 0.2 0.6 0.6 0.2 Commercial Acre 900.0 Negligible 45.0 45.0 0 Industrial Acre 80.0 11.0 3.0 3.5 12.5 Commercial recreation Acre 300.0 Negligible 7.7 28.7 0 Park Acre 6.0 Negligible 0.3 Source: Weston Pringle and Associates, Inc. lTrip ends per descriptor. 0 0 0 0 0 0 I I 0 0 0 0 0 0 0 0 I I 10 I 0 TABLE F 45 PROJECT TRIP ~ENERATION lsa Trip Ends Land Use Quantity Dai 1 y A.M. In A.M. Out P .M. In P.M. Out - Low-density residential 701 7,700 140 560 560 140 Medi um-density residential 2,297 17,200 470 . 1,380 1,380 460 Conmerciall 26.2 23,600 1,180 1,180 Industriall 36.7 2,900 400 110 130 460 Commercial recreationl a.a 2,400 60 230 Park 7.0 40 TOTALS 53,840 1,010 2,050 3,310 2,470 laased on estimated net acreage figures as opposed to the gross acreage figures 1 i sted in the proposed Ranch.a Carrillo Master Plan. 0 0 0 0 0 0 0 0 0 0 0 46 lsa A potential increase in estimated trip generation would result from the . conversion of the school site to low-density residential as provided for in the proposed Rancho Carrillo Master Plan under 11 8. Development Standards, Pub- 1 ic Planning Areas Hand F, Number 2,11 on Page 22. This conversion would add 124 dwelling units with 930 daily trip ends and 100 p.m. peak-hour trip ends. The total daily trip ends with the school site conversion would be 54,770. Trip Distribution and Assignment. The second step in the traf- fic analysis is to determine the geographic distribution pattern for project- generated traffic and to assign the traffic to the proposed roadway system .. The Comprehensive Planning Organization I s ( CPO) Series !Vb population proj ec- tions for 1995 were utilized to develop the trip distribution patterns. The resulting patterns were further modified based upon knowledge of the area and professional judgment. The distribution patterns were developed for two future conditions. The first condition· is based upon completion of the project without ultimate develoi:ment of Carrillo Way, Melrose Avenue, and El .Fuerte Street as illus- trated in Figure 12. The second condition is a distribution pattern based on completion of the project· and ultimate planned buildout of the road system as shown in Figure 12. These patterns illustrate distributions for residential and industrial trips only. They do not illustrate commercial and commercial recreation use trips. Utilizing the distribution patterns illustrated in Figure 12, project traffic was assigned to the road system. Figure 13 illustrates daily volumes -at completion of the project. These volume figures include existing traffic plus project traffic on the. road. system as illustrated. They do not include regional traffic increases or ultimate road improvements. Figure 14 i.llustrates daily volumes at completion of the project on the ultimate road system. These volLDTie figures include existing volumes and expected traffic from developing parcels in the vicinity. Specifically, traf- fic expected to be generated by Carlsbad Oaks and La Costa were included in these figures. An adjustment was made in the external traffic from the project. Since some of the trips attracted to the commercial uses would be generated by the project's residential uses, a reduction was made in external traffic. It was assumed that half of the trips attracted to the commercial area at Carrillo Way and Melrose Avenue were generated in the residential areas of the project and would not be external to the site. This commercial area is described in the City of Carlsbad's General Plan as a Community Commercial area. The Gen- er al Pl an describes these uses as serving an area up to one and one-half mil es 0. 0 0 0 0 0 0 0 lo i I I i I '0 10 i 47 12 Directional Distribution lsa .... o~~ a% ,~,,,..,,_,~2~5~-~---~20~%-' ............ ~~~~~:': ~-=?:a1:om:a~r:,A;lr~:;o;;_;rt1111R•d•. -~---r/ .... • • ... • --•• -••• -.-- 25% 20% I \ \ ' ' ... ' ' LEGEND \ \ 00/ /0 XO/ JO. (0%) ,\IOI l\,o Residential See 1. below \ Industrial i I See 2. I I I I I I I . ·, / I / I I , __ ,,_ 0% 0% f + 15;~ 10% I __ -----➔--------I \ \ -···-···-···-' ··-· •• -···-··J -· ·-···-···-···-···-·· Source: Weston Pringle & Assoc. + N No scale I. lrhis distribution pattern assumes that all onsite improvements are com- pleted and connected to the existing system as illustrated in Figure 10. 2rhis pattern will occur following ~ompletion of major offsite arterial highways including Melrose Avenue north of Palomar Airport Road and Carrillo Way west of El Fuerte. ------------------------------------- 0 0 0 0 0 0 0 0 0 0 48 13 Existing and Project Daily Traffic lsa LEGEND \ \ ' ' ... "' ' \ \ \ \ I I I ; ....... / I I -/ I -,, ..--I ' ,. • I --j / : I . I I I I I I I _ ... -·------'-_______ .- I \ \ . ···-···-···-' ··-···-···· •. J 29,700 (12,50 ···-···-··· &4000 1500 ~ . . .•• -···-···---· -··· -··· -···-···-···-----· --... .J I el 120 I I 00,000 Existing and Project Traffic (00,000) Exist~ng traffic + N No scale NOTE: This figure illustrates existing plus project volumes only. It does not include traffic volumes from other future developments. It assumes the construction of all .onsite improvements. 0 0 0 0 0 10 I 0 0 0 0 14 49 , Existing, Project, and Related Project DaHy Traffic LEGEND 000 See 1. below (000) See 2. below , ... , I \ / \.400 .... r I (400) I I I . I 12,800~ (12,900), ~ 1r,soo I (11,900) I . I • \: 15,300 ! ______ .,. (lS~oo)-1-, ' \ ' ------···-···-~ ·r:4.,.5o_g-r-_J : \. 4,soo, . • I ) -- I -· ·-··--···-···-···-···-·· 2, l 00 ( 2, l 00) , 0 (10,400) l ,500.., ( l , 500) lsa 20, l 00 ) 1,800 (1 aoo)\ ____ _ ' ..... ---10800.J .,,. ,. .,,. .., .,. ( 10900) ,,.. + N No scale l'Includes project-related and existing traffic volumes in addition to esti- mated traffic volumes resulting from the Carlsbad Oaks and La Costa develop- ments. 2These volumes also include trips generated from school site conversion residential units. 0 0 0 0 0 0 0 0 0 0 lo I 50 lsa in radius. On the basis of this definition, the assumption that half of the trips attracted to this commercial area are local is conservative. \ This adjustment results in 6% of daily residential trips being internal. Also, 4% of the p.m. peak inbound trips and 13% of the p.m. outbound trips would be internal. I Circ:ulation System Analysis. · Road and Intersection Capacity Analyses. The ability of the planned circul at1on system to accommodate the proposed project has been eval u- ated on two levels. First, daily volume/capacity comparisons were made to provide a general evaluation. Second, peak-hour intersection analyses have been completed on Melrose Avenue at Palomar Airport Road and Carrillo Way to provide a more refined evaluation. These analyses have been completed for traffic conditions illustrated in Figure 13 onsite (partial road improvements, exi,sting plus project traffic volumes) and Figure 14 {ultimate road improve- ments, existing plus project traffic volumes, other project traffic·volumes). I Table G provides a comparison of maximum projected daily volumes and capacities for the arterials serving the project. Review of Table G indicates that, on a daily volume basis, the planned system will be adequate with the exception of Palomar Airport Road. The 42,400 daily volume on Palomar Airport Road easterly of Mel rose Avenue exceed·s the 40,000 ADT capaci-ty by 6%. This indicates a potential problem and the need to develop parallel routes to relieve Palomar Airport Road. This is not related solely to this project as the figure is based on addition1al projects developing in the area. The Draft Environmental Impact Report prepared by the County of San Diego for'the San Dieguito Circulation Element, GPA 80-CE, contains ye-ar 2000 pro- jected daily volumes for. Palomar Airport Road at Melrose Avenue. These vol- umes vary from 38,000 to 40·,000, with the County-proposed pl an at 38,000. The report does not include projections for Melrose Avenue. Rancho Santa Fe Road north of Olivenhain is projected to have. a demand of 34,000 with the County proposal. Since Melrose Avenue splits from Rancho Santa Fe Road just south of Carrillo Ranch, it could be assumed that the year 2000 volumes on r,,1elrose would be somewhat less than 34,000. These projections indicate that, on a daily volume/capacity comparison basis, the planned road system should be adequate. The comparison of daily volumes to projected daily capacity gives a gen- eral indication of the adequacy of a roadway system. However, the 'operation of intersections is the critical factor in determining the adequacy of a cir- 0 0 TABLE G 51 DAILY VOLUME/CAPACITY COMPARISONS lsa 0 Volume Project Completion Ultimate Street Capacityl (Figure 13) (Figure 14) 0 Palomar Airport Road 40,000 38,500 42,400 Mel rose Avenue 40,000 13,400 24,100 Carrillo Way 20,000 4,000 15,300 0 lcity of Carlsbad Engineering Department 0 0 0 0 0 0 0 0 0 0 0 0 0 52 lsa cul at ion system. For the Rancho Carri 11 o development, the intersecti ans on Melrose Avenue at Palomar Airport Road and Carrillo Way are the critical points in the circulation system. Intersection Capacity Utilization (ICU) analyses have been completed for these intersections for the two traffic con- ditions described in Figures 13 and 14. (The ICU methodology is explained· in Appendix E.) The ICU values for the intersections are summarized in Table H. As indicated in Table H, an operational problem is anticipated at Palomar Airport Road and Melrose Avenue. This further confirms the potential for problems identified in the daily volume/capacity comparison. The major factor contributing to the potential capacity problem is traffic flow on Palomar Air- port Road. This is a result not only of this project, but development occur- ring in the vicinity and existing traffic as well. As was mentioned above, development of additional east-west routes would relieve the congested situa- tion expected along Palomar Airport Road. However, without such a route, this intersection wilJ operate under very congested conditions. It must also be emphasized that this congestion occurs even using only partial "ultimate" traffic volumes. Mr. Pringle has prepared an analysis of the proposed realignment of Los Monos. He has concluded that, while this may provide additional east-we·st street capacity west of Melrose, it will not provide any major relief to the Palomar Airport Road/Melrose Avenue intersection. • Intersection s·pacing. In add it ion to intersection capac- ity, intersection spacing along the arterials affects their operation. The City of Carlsbad Street Design Standards require 2,600 feet between intersec- tions on prime major artel"ials and 600 feet on secondary arterials. These standards are met on Carrillo Way and on Palomar Airport Road. However, on : 1 0 Melrose Avenue there are two intersecti.ons which do not meet these criteria. An intersection is proposed on Mel rose Avenue approximately 1,600 feet south of Palomar Airport Road and 1,600 feet north of Carrillo Way. This intersection is proposed in order to provide access to the planned development on both sides of Melrose Avenue. According to the traffic study, due to ter- O rain and other development-constraints, sufficient access cannot be provided without this intersection. The traffic study further states that, while not meeting the City standard, it does provide a reasonable spacing of greater than a quarter-mile. According to Weston Pringle and Associates, such spacing is not unusual in developed areas and satisfactory traffic movement can be 1 obtained. William Stracker, the City's consulting traffic engineer, disagrees 0 and states in a memo dated December 1, 1980 (Appendix F) that "standard inter- section spacing on Melrose should be maintained." 0 0 0 0 0 0 0 0 0 l,Q I . 0 0 TABLE H ICU SUMMARY Intersection Palomar Airport Road and Melrose Avenue Carril lo Way and Melrose Avenue 53 Project Completion (Figure 13) tcul Level of Service! 0.81 D 0.45 A lsa Project with Adjacent Development (Figure 14) !cul Level of Service! 1.04 F 0.79 C lAn explanation of ICU analysis and Level of Service is located in Appendix E of this report. -------~------'---------------------------- 0 0 0 0 0 0 0 0 0 0 0 54 lsa In addition, a second "right turn in and out onl/1 access is proposed on Melrose south of Carrillo Way. With the provision of deceleration and accel- eration lanes, this access should not impact traffic flow on Melrose Avenue. Again, however, the City's traffi.c consultant disagrees. The area north of Palomar Airport Road along Melrose Avenue conforms to City of Carlsbad standards, with intersections on Melrose Avenue and Palomar Airport Road 2,600 .feet apart . . The City Engineering Department has recommended that Palomar Airport Road and Melrose Avenue be realigned in order to improve the horizontal alignment and intersection spacing on Mel rose. The app 1 icants 1• engineer, Rick Engineer- ing Company, has reviewed this alternative and identified some potential prob- lems. While improved intersection spacing is achieved southerly of Palomar Airport Road, intersection spacing· prob 1 ems develop to the north. In add i- t ion, Rick Engineering believes that the realignment 'I.Ould result in vertical and horizontal alignment problems. Primary access to the industrial area is proposed from the street ( Indus- trial Way) which connects Palomar Airport Road and Mel rose Avenue near the western property 1 ine. A secondary right-turn-only access to the industrial area is provided on Melrose Avenue. Driveways are proposed for right-turn in and out only. The City Engineering Department states that the secondary access point and the driveways will not be permitted (memo from Richard Allen to Pat Tessier, February 23, 1981). Intersection Signalization. The traffic study ·al so examin- ed the need for intersection signalization resulting from development of .the Rancho Carrillo project. Based on a traffic signal warrant analysis• (discuss- ed in Appendix E) conducted by Weston Pringle and Associates, the following intersections will require signalization: Palomar Airport Road and Industrial Way (west collector) Palomar Airport Road and Melrose Avenue Melrose Avenue and collector south of Palomar Airport Road Melrose Avenue and Carrillo Way 0nsite Circulation Analysis. Figure 11 illustrates the basic onsite circulation system. This onsite system was reviewed with respect to traffic operations .and safety. Daily volumes are indicated in Figure 14. All projected volumes are within the 5,000 dai-ly volume for collector street·s indicated in the City's standards with two exceptions. The first is the west connection to Palomar Airport Road. The 8,100 daily trips on the segment indicate tha~ a four-lane facili'ty would be required between Palomar Airport -------------,-------------------------------------------- 0 9 0 0 0 0 0 .o 0 0 0 55 lsa Road and the first intersection within the project. Also, it indicates that a left, through, and right-turn lane would be required at the intersection with Palomar Airport Road. The second is a local street extending south from Car- ri 11 o Way west of Mel rose Avenue which shows an ultimate volume of 5,600 (with the school site being converted to residential uses). The internal street system is designed with no four-leg intersect i ans, which is a desirable feature with respect to safety. In general, there are no cul-de-sacs of excessive length within the project. An exception is the area in the southeast quadrant of Palomar Airport Road and Melrose Avenue. Access restrictions on the adjacent arterials, terrain, and site· boundaries result in a single access to this area. This may restrict necessary emergency access. Consequently, some type of emergency access may be necessary to satisfy fire and police needs. • Project Phasing. The Weston Pringle and Associates traffic report studied the phasing of development and associated phasing of the neces- sary road improvements. The fa 11 owing is the phasing p 1 an proposed by the project applicant in the Weston Pringle traffic study. Please refer to Figure 6 for the location of various phases. Phase Green Red Orange Brown Blue Description 148 dwelling units 99 dwelling units 755 dwelling units 263 dwelling units 1,733 ~welling units Circulation Improvements Full El Fuerte within project boundaries Full Melrose Avenue from Car- rillo Way to southern boundary Improve half of Palomar Airport Road within boundaries of the project and improve Me 1 rose Ave- nue from Palomar Airport Road south to first intersection. Traffic sig.nal at Palomar Air- port Road and Melrose Avenue. None Full improvement of Melrose Ave- nue from first intersection south of Palomar Airport Road to Carrillo Way. Full improvement of Carrillo Way from Melrose 0 0 0 0 0 0 0 0 0 0 10 I I I • 56 Purple Industrial/commercial Avenue to west boundary. Traf- fic signal at Carrillo Way and Melrose. Improve half of Palomar Airport Road and Mel rose Avenue from Palomar Airport Road to north boundary. lsa As described in the Rancho Carrillo Master Plan on Page 47, "each phase is independent with the exception of grading. Residential certificates of occupancy within each phase boundary shall not occur until the backbone water, sanitary sewer, and storm drain facilities shown on the Public Facility Maps, and the major circulation components listed ... are in place within each phase boundary." However, the City's traffic engineer was not sat-isfied with this phasing program, both in timing and the extensiveness of the necessary improvements. The following is the recommended phasing improvement program· suggested by the City's traffic engineer (Appendix F). Phase Green Red Orange Brown Blue Circulation Improvements El Fuerte Street -full improvements and signal at Alga Road Melrose Avenue -full improvements from Carrillo Way to Alga Road Alga Road -half-street improvements from Melrose Avenue to El Fuerte Palomar Airport Road -full improvements from Melrose Avenue to west boundary and half improvements east of Melrose Melrose Avenue -full improvements from Palomar Air- port Road to· Carril lo Way El Fuerte Street -full improvements from Palomar Airport Road to first street from development Melrose Avenue -full improvements from Carril lo Way to Alga Road 0 0 0 0 0 0 0 0 0 0 0 57 lsa Carrillo Way -full improvements within project Traffic signals at Carrillo Way/Melrose and El Fuerte Street Purple Traffic signal at Palomar Airport Road and El Fuerte Street (one-fourth responsibility of Rancho Carrillo) Improve half of Palomar Airport Road and Melrose Ave- nue from Palomar Airport Road to north boundary This list is an attempt by the City's traffic engineer to make each phase truly independent since the project applicant is not proposing any sequence of development. The phasing program suggested by the City would allow any phase to proceed independent of any other phase. Howe,ver, as may be apparent, as one or two phases are constructed, many of the improvements listed for a subsequent phase will have already been constructed. Mitigation Measures. The following mitigation meas-ures are necessary to resolve the remaining differences of opinion between the project applicants and the City Engineering Department, and to otherwise mitigate the potential impacts of the project. 23. The roadway alignments shown on the General Plan Amendment and on the Master Plan should be considered as conceptual alignments only. Prior to final approval of the Rancho Carrillo Master Plan, the applicants and the City shall conduct an engineering study to determine fi na 1 a 1, i gn- ments. This study shall focus specifically on the fol- lowing: a. The alignment of Palomar Airport Road through the project site. b. The a 1 i gnment of Me 1 rose Avenue from the southern boundary of Rancho Carri 11 o to. the City boundary north of the Carlsbad Raceway. c. The location and geometrics of all major intersec- tions on Palomar Airport Road and Melrose Avenue. d. The location and geometrics of all secondary intersec- tions and access points on Palomar Airport Road and Melrose Avenue. 0 0 0 0 58 24. Prior to approval of any tentative tract map, a phasing plan and improvement schedule for the entire Rancho Car-:- ri llo Master Plan shall be finalized and approved by the City. 25. As recommended in the traffic study, the following inter- sections will be signalized by the developer: Palomar Airport Road and Industrial Way (west collector) Palomar Airport Road and Melrose Avenue O Melrose Avenue and collector south of Palomar Airport Road Melrose Avenue and Carril lo Way 0 0 0 0 0 0 These will be installed according to the phasing plan and improvement schedule required by Mitigation Measure #24. 26. The intersect ion of Melrose Avenue and Palomar Airport Road should include provisions for lanes as indicated below:· Movement Northbound through Northbound right Northbound left Southbound through Southbound right Southbound left Eastbound through Eastbound right Eastbound left Westbound through Westbound right Westbound left Lane Requirements Project Completion Ultimate 1 1 1 1 1 1 2 1 1 2 2 2 1 1 2 1 2 3 1 1 3 1 2 27. The west connector to'Palomar Airport Road fr-om the south portion of Rancho Carrillo should have provisions for four lanes south to the first intersection. 28. The intern a 1 street system (including intersect ions and access routes) should be examined when tentative tract maps are available for review. 29. During review of the Master P 1 an and subsequent 1 eve 1 s of design, the police and fire departments should· review the lsa 0 , 0 ' 0 r 0 0 0 0 0 0 59 circulation system to assure proper and safe emergency access to the development. 30. The City should review the feasibility of providing an 1 alternative east-west route to Palomar Airport Road. AIR QUALITY lsa An air quality analysis was conducted for the project location to assess potential air quality impacts from the project. This study appears in its entirety in Appendix G. Setting. • The climate of Rancho Carrillo, as in most of Southern Cal- ifornia, 1s controlled. largely by the strength and position of the subtropical high-pressure center over the Pacific Ocean. The high pressure is associated with warm, dry, sinking air that blocks out most mid-1 at itude storms and drives the prevailing onshore breezes. As a result, local climatic conditions are characterized by warm, dry ·sunmers, mild winters, infrequent rainfall in the winter when. the high is weakest and farthest south, and refreshing ocean breezes. The si-nking -air, unfortunately, creates a massive temperature inver- sion that prevents effective vertical ventilation of the air. When the air po 11 utant emissions are trapped by the temperature inversions, Southern Cali - fornia experiences some of the most unhealthful air quality in the entire nation. Temperatures near Rancho Carrillo average 60 .. F annually, with cool surrmer averages of 68 .. F and winters averaging 54 .. F. Rainfall· is highly variable, falling almost all between late November and early April. Average annual rainfall is ten inches, but precipitation is so variable that monthly totals in a wet year may exceed the annual total average. Wind data from the nearby Palomar Airport show that for most of the year winds from the southwest through northwest dominate, except in winter when nocturnal winds reverse the flow and blow offshore. During surrrner days, emissions generated in Carlsbad are blown far inland by strong sea breezes and are dispersed over the central range. In winter, especially at night, off- shore winds and weaker onshore winds balance such that some ·1ocalized pollu- tion stagnation occurs. With clean ocean air usually blowing across .. North County, and with considerable open space and limited emissions sources, air quality near the project is usually healthful and among the best in the Coun- ty. At times, however, polluted air from the Los Angeles Basin drifts south- eastward offshore at night, and then comes onshore across the North County area the next day. These episodes of unhealthful air are responsible for some of the worst conditions observed in San Di ego County in the last decade. 0 0 0 .0 i I 0 0 0 0 0 0 60 lsa Particulates and ozone often exceed Ambient Air Quality Standards (AAQS). As shown in Table I, the episodes of very poor air quality are evident in measurements at the San Diego Air Pollution Control District station at Ocean- side. The Oceanside and Solano Beach stations recorded the only second-stage photochemical smog episode in the County in almost ten years. These episodes are, fortunately, Jnfrequent. NOx, S02 and CO, the pollutant species usually linked to local pollu- tion sources, are typically below AAQS levels because there are only limited sources of these pollutants in North County. .Ambient air quality problems near the site are, therefore, the result of pollutants carried into the area from other source regions. Impacts·. There are three general sources of air resource impacts associated with the project. These sources are vehicle emissions, impacts related to construction activities, and stationary pollution sources. Vehicle Emissions. The major air quality impact from the devel- opment would result from the dependence on the automobile as the primary means of transportation. At project buildout, Rancho Carrillo will generate 53,840 vehicle trips per day. At an estimated average of eight miles per trip, 430,720 vehicle miles traveled (VMT) will be generated by the site. Rancho Carrillo will, therefore, ultimately be responsible for about 1% of the esti- mated 40 million VMT (CPO, 1980) of all traffic within the San Diego Air Basin. Population projections for the proposed development are consistent with the Series IV and Series V population projections. Consequently, project- related population growth and estimated VMT should be consistent with those used for the RAQS. These figures are based on surrrning residential, commer- cial, industrial, and institutional .. trips separately. Actual trips that are multi-purpose are, therefore, counted twice in the estimation which, as a result, is overly conservative. Estimates also include the more conservative assumption that all residents shop and work outside the project boundaries. Using these figures and assuming a linear phasing of the project with completion by 1995, the calculated emissions total as shown in Table J. At buildout, Rancho Carrillo traffic will contribute six tons of CO, one ton of ( . NOx, 0.7 ton of hydrocarbons, and small amounts of S02 and particulates. The additi.onal increment from a possible school site conversion represents a 10% increase above these figures. Table K illustrates that, at completion, Rancho Carrillo will contribute from 0.54 to 0.70% of the entire basin's burden of the main vehicular pollut- ants indicated at the 1987 target date. The fact that impacts from Rancho• Carrillo's traffic emissions alone represent .5% of all air pollution, from 0 0 TABLE I 61 CARLSBAD AREA AIR QUALITY SUMMARY lsa lo 1976 1977 1978 1979 I 1975 \ Days Days Days Days Days Over Hr.* Over Hr.* Over Hr.* Over Hr.* Over Hr.* Po 11 utant Standards Std. Max. Std. Max. Std. Max. Std. Max. Std. Max. 0 Ozone 1 hr > 0.08 ppm 43 0.19 69 0.29 87 0.25 71 0.35 0.36 1 hr > 0.10 ppm 0.19 0.29 61 0.25 51 0.35 45 0.36 1 hr> 0.12 ppm 0.19 0.29 22 0.25 20 0.35 22 0.36 1 hr 2 0.20 ppm 0 0.19 0.29 2 0.25 5 0.35 7 0.36 0 Nitrogen dioxide 1 hr 2 0.25 ppm 1 0.31 4 0.33 2 0.36 2 0.32 0 0.21 Carbon monoxide 8 hrs > 9 ppm 0 10 0 10 o 8 0 9 o 10 0 Hydrocarbons 3 hrs > 0.24 ppm 179 4.0 222 4.2 243 4.5 211 4.0 Sulfur dioxide 1 hr ~ 0.50 ppm 0 0.03 o 0.06 0 0 0.03 0 0.06 0 Particulates 24 hrs> 100 ug/m3 25% 172 20% 146· 21% 173 40% 219 33% 180 Annual > 60 J.Jg/m3 -83 82 82 88 85 0 *In ppm, except for particulates in .ug/m3 Source: San Diego APCD, 1975-79 0 0 0 0 I 0 TABLE J 62 RANCHO CARRILLO VEHICULAR EMISSIONS iroNS7DAY) lsa 0 1985 1990 1995 BASE PROJECT 0 Hydrocarbons VMT-related 0.09 0.22 0.29 Trip-related 0.13 0.33 0.40 TOTAL 0.22 0.55 0.69 o- Carbon monoxide VMT -re 1 ated 1.18 2.79 3.49 Trip-related 0.77 2.06 2.69 TOTAL 1.95 4.87 6.18 0 Oxides of nitrogen 0.26 0.72 0.96 Oxides of sulfur 0.02 a.as 0.07 0 Part i cu 1 ates 0.03 0.10 0.13 BASE AND ADDITIONAL POSSIBLE 0 Hydrocarbons VMT-re 1 ated 0.09 0.23 0.30 Trip-related 0.14 0.33 0.40 TOTAL 0.23 0.56 0.70 0 Carbon monoxide VMT-re 1 ated 1.20 2.85 3.55 Trip-related 0.78 2.10 2.74 I TOTAL 1.98 4.95 6.29 !o Oxides of nitrogen 0.26 0.74 0.98 Oxides of SU 1 fur 0.02 a.as 0.07 Particulates 0.03 0.10 0.13 0 0 0 TABLE K 63 RANCHO CARRILLO VEHICULAR EMISSIONS BASIN BURDEN ANALYSIS lsa 0 Hydro-Carbon Oxides of carbons Monoxide Nitrogen Particulates Base project emissions (1995) 0.69 6.18 0.96 0.13 0 Base and school site I emissions (1995) 0.70 6.29 0.98 0.13 1974/75 RAQS base year 279 1221 187 361 , 0 1987 target at attainment 127 887 150 291 Base/1987 target(%) 0.54 0.70 0.64 0.04 Base and schoo 1 site/ 1987 target ( %) 0.55 0.71 0.65 0.04 0 0 0 0 0 ---------------------------------------------- 0 p 0 0 0 I 10 0 0 0 0 64 lsa both mobile and stationary sources in the basin, indicates that this project, in conjunction with similar developments in the basin, will have a significant impact on regional air quality. Construction Impacts. In addition to vehicular emissions, dust generated during construction activities and combustion of fossil fuels related to construction will originate from the project. Impacts of such sources tend to be less severe, more localized, and somewhat more easily con- trolled than those of other sources. Of all construction activities, genera- tion of fugitive dust from soil disturbance is by far the greatest concern. Although project phasing is not known, it is possible, based on examples of other projects, to estimate the length of the project's construction phases for the purposes of calculating construction-phase impacts. Based on a total project phasing of ten years and an average individual project-intensive con- struction period of six months, approximately 40 acres wi·ll be undergoing con- struction at any one time. The associated fugitive dust emission factor of 1.2 ton per acre per month can be reduced by about one-half through dust sup- press ion measures to achieve a total daily emission rate of 0.8 ton of dust per day. A portion of this dust will remaln suspended and mix with the several hundred tons of particulates emitted within the air basin each day. Compared to regional emission levels, project-related emissions are nominal, a{ld the regional ambient air quality impact will be small. ·Construction dust is typically chemically inert, of large particle diameter easily filtered in the human respiratory tract, and therefore less unhealthfur than other urban pollutants absorbed into the bloodstream. Most of the dust emitted will settle on surfaces near and downwind of the site. This impact is not considered significantly unhealthful, but a local soiling nuisance. Combustion emissions from heavy-duty equipment during construction will also impact air quality very locally. Such emissions are extremely small com- pared to the emissions resulting from 254 million vehicle miles in the County daily. Localized nuisance may result from diesel exhaust and its odor, but ambient air quality impacts from construction emissions will almost never be observed. Stationary Source Im~acts. The project wi 11 result in increased energy consumption. Using SDG& consumption figures for various land uses and dwelling sizes, Rancho Carrillo's estimated energy needs will be 67.8 million KWH and 396 million cubic feet of natural gas per year. About one-half of I 0 0 0 0 0 0 0 0 0 0 65 lsa SDG&E electricity is generated by burning oil, which will cause additonal air pollution. The project-related stationary source emissions are shown in Table L. The emissions are minimal compared to quantities of vehicular emissions in the air basin. The impact on ambient air quality will be correspondingly sma 11 . Mitigation Measures. Vehicular Impacts. 31. The use of alternate transportation modes wi 11 be encour- aged by the inclusion of bus facilities, public bikeways, and walkways in the site plan. 32. The Master Plan includes provisions for a variety of com- patible land use types such as housing, employment, recre- ation, and commercial opportunities within the Rancho Car- rillo conmunity to promote intra-community travel. Construction Impacts. 33. Dust suppression measures, such as regular watering, grad- ing in the spring when soil moisture is high, and early paving of roads, will be implemented to reduce air pollu- tion during construction and grading. Stationary Source Impacts. 34. The project developer shall include, to the fullest extent possible, design features that reduce energy consumption through conservation or the use of alternative less pol- luting energy sources such as solar-assisted heating_ sys- tems and the inclusion of wiring, plumbing, and roof load- bearing design for future active solar co 11 ector systems. Those features considered wi 11 be presented and revi e.wed at the submittal of the tentative map. These measures should adequately mitigate construction-related impacts. However, they will only slightly mitigate the expected increase. in pollutants ·to be generated by this project. This project will contribute to the cumula- .tive impact on air quality resulting from development of the region. 0 0 TABLE L 66 I RANCHO CARRILLO STATIONARY SOURCE E~I55i0NS {iONS7DAYl lsa 0 Electrical Po 11 utant Generation Natural Gas Use Total Sulfur dioxide 0.17 0 Negligible 0 .17 Hydroc arbori s Negligible Negligible Negligible Oxides of nitrogen 0.11 a.as 0.16 Particulates 0.03 0.01 0.04 0 Carbon monoxide 0.02 0.01 0.03 0 0 0 0 Q 0 ------,------------------------------------------- 0 0 0 0 0 0 0 0 0 0 67 lsa ENERGY Setting. The ·current consumption of non-renewable energy resources on Rancho Carrillo property is negligible. As the property is developed, the onsite electrical and natural gas demand and vehicular fuels will constitute a significant energy demand in an era of rapidly declining resources. The coastal environment of Southern California fortunately offers a con- siderable opportunity to minimize energy demand because of a very mild cli- mate. Cool sunmer breezes reduce air--conditioning demand, mild winters reduce heat loads, and abundant sunshine, especially in inland valleys away from coastal clouds, offer considerable possibilities for solar-assisted energy systems. Compared to other areas of California and the nation, the San Diego area has almost the lowest climatically-induced (hot or cold weather) • energy demand. Impacts. Upon project .completion, sources of fess i 1-fue 1 ed energy consumption. there will be three principal These include: • 1. Electrical energy utilization met by combustion of oil, gas, or coal in fossil-fueled power plants. 2. 0nsite natural gas combustion for heating, cooking, or hot water. 3. Automotive fuels and lubricants to meet project-related transportation needs. Standard energy demand estimates can be made using consumption factors derived from SDG&E experience in ·energy supply and vehicular performance char- acteristics. These consumption factors are based on historical performance and, therefore, do not reflect the marked trend, toward conservation created by limited supply and spiraling costs of energy resources. Using somewhat conservative consumption (over-predictive) estimates yields the following project-related energy demand: Electricity -67,755 MWH/year Natural gas -4,170,000 therms natural gas/year Gasoline -.5,250,000 gallons/year SDG&E has indicated in its future energy supply pl_ans that it can keep pace with area growth and that there will be a significant decline in basin- wide oil and gas use within the next decade for electrical generation. Given, however, the rapidly rising cost of electricity, every effort should be made to reduce energy consumption through ·aggressive conservation measures. 0 0 0 0 ro I ! I 0 0. 0 I 0 0 NOISE 68 Mitigation Measures. 35. The devel aper sha 11 incorporate into project design as much as possible energy conservation features such as solar water heating for swimming pools, weatherization (double glazing, attic ventilation, insulation), orienta- tion of houses to allow. later solarization, increased slopes of south-facing roofs, and plumbing for retrofit of solar facilities. The provision for such features will be reviewed by the City at the time of submittal of the tent- ative map. lsa A noise analysis was completed by Bioacoustical Engineering Corporation (BAEC) on December 18, 1980. The complete report is included in its -entirety in Appendix H. Major findings of the report are summarized below. An addi- tional noise study was conducted by Vince Mestre Associates in 1981 to esti- mate. the expected findings of the ANCLUC noise. study as it wi 11 rel ate to Palomar Airport. This study is included in Appendix J. Setting. Noise Criteria. Several rating scales have been developed for measuring community noise. The predominant rating scale now in use in Cali- fornia for land use compatibility assessment is the Community Noise Equivalent Level (CNEL). The CNEL scale is based on the A-w~ighted decibel. A-weighting is a frequency correction that correlates overall sound pressure levels with the frequency of response of the human ear. CNEL is a 24-hour, time-weighted annual average noise 1 evel. Time- weighted refers to the fact that noise which occurs during certain sensitive time periods is penalized for occurring at those times .. The evening time per- iod (7 p.m. to 10 p.m.) penalizes noises by 5 dB, while nighttime (10 p.m. to 7 a.m.) noises are penalized by 10 dB. These time periods and penalties were selected to reflect people's sensitivity to noise as a function of activity. The criterion used to assess the acceptability of community noise levels can vary with the municipality. Most communities use 65 CNEL as the critical criterion for assessing the compatibility of residential land uses with noise sources. The Noise Element of. the General Plan for the City of Carlsbad requires that noise levels in the exterior living areas (yards and patios) for residential land uses do not exceed 65 CNEL. In addition, for multi-family residential projects, the California Noise Insulation Standard (California Administrative Code, Title 25, Chapter 1, Subchapter 1, Article 4) requires 0 0 0 0 0 0 10 0 I IO I I i 0 I io I ! 69 lsa that the interior noise levels in the residential living spaces not exceed a CNEL of 45. The City of Ca~lsbad also applies this interior noise standard to single-family residential homes. Existing Noise Environment. Virtµally all of the Rancho Car- rillo project site and the immediate vicinity is presently undeveloped and contains no noise-sensitive land uses (i.e., residences, hospitals, schools). The few exceptions to this are the existing homes along El Fuerte Street and Alga Road south of the project. Onsite eval uati ans of the current outside noise environment throughout the Rancho Carrillo development site were made by BAEC from January 18, 1980 through January 20, 1980 (Friday-Sunday). These evaluations indicate that the principal existing sources of noise•include: 1. Aircraft activities associated with Pafomar Airport, 2. Motor vehicle activities along Palomar Airport Road, 3. Dragster races at Carlsbad Raceway, and 4. Motocross races at Carlsbad Raceway. The existing noise exposure from each of these primary noise sources is dis- cussed in the following sections. Current Aircraft-Related Noise Exposure. Analysis of I the existing noise exposure from current aircraft operations associated with Palo- mar Airport was made on the basis of fie 1 d measurements at two points on the project site and from field data collected for similar aircraft approaching John Wayne Airport in Orange County. During the onsite field measurements, three primary aircraft flight paths were observed. Aircraft .were observed an: (1) a straight-in approach path, traveling west parallel to and north of Palomar Airport Road; (2) a loop path, where the aircraft depart the airport to the west and ci rel e to the south, returning back to the approach end of the airport; and ( 3) a fly-by pa.th, traveling at random di recti ans over the property. Figure 15 i 11 ustrates a rough approximation of the three flight paths as they re 1 ate to the Rancho Carrillo properties. According to the Comprehensive Land Use Plan for Palomar Airport (CPO, May 1974), three aircraft types use the airport. Single and twin-engine pro- peller aircraft are two types which comprise the majority of aircraft using the airport. In addition, business jets, ·both private and small commercial, operate at the airport. 0 0 0 0 0 0 0 0 0 0 0 I I 70 .15 Palomar Airport Flight Paths . G)@ Noise Measurement Locati ans Source: 3ioacoustical Enq. Corp. lsa JEC1 ITE , ---____ _; ~--\ I r-···JL.y-.::ay ' ' • N 0 0 0 0 0 0 0 0 10 ! I 0 71 lsa BAEC assumed an annual flight count of 268,418 operations (approximately 1,000 aper at i ans each weekend day and an average of 630 aper at i ans per week- day). The current fleet mix is roughly 85% single-engine propeller aircraft, 12.5% twin-engine propeller aircraft, and 2.5% business jet aircraft. Approximately 94.5% of all operations occur during the daytime hours (7 a .m. to 7 p .m.), 5% occur during evening hours (7 p .m. to 10 p .m.), and . 5% occur during nighttime hours (10 p.m. to 7 a.m.). For the purposes of this study, it was assumed that 25% of all weekend traffic and 40% of all weekday traffic typically fly the straight-in approach. Approximately 65% of all weekend traffic and 50% of all weekday traffic use the loop flight path. In addition, 10% of both weekend and .weekday traffic use the fly-by flight path. It was assumed that a 11 business jets use the straight-in path only. ' Based on these assumptions and the single-event noise levels (SEL) recorded· onsite, the current weekday and weekend aircraft CNEL exposures were calculated for the two measurement locations onsite. Results are shown in Table M. This table indicates that on weekdays the project site is exposed to noise levels ranging from 47.6 CNEL to 51.5 CNEL. It also shows that on the weekend the site is exposed to noise levels ranging from 49.1 CNEL to 52.8 CNEL. Current Motor Vehicle-Related Noise Exposure. Traffic on Palomar Airport Road represents the principal source of current motor vehicle noise exposure. Noise measurements were conducted along Palomar Airport Road on Friday, January 18, -1980. These measurements indicate that the noise level at 50 feet from the roadway centerline is 71. 9 dB CNEL. The noise 1 ev_el at 100 feet from the centerline is 67.4 dB CNEL. Current Carlsbad Raceway Dragster Noise Impact. Carlsbad Raceway is located just north of the proposed development property. Each Sat- urday, weather permitting, drag races occur between the hours of 7 p.rn. and 11 p.rn. Onsite noise measurements were conducted between 8 p.m. and 9:30 p.rn. on Saturday, January 19, 1980. Measurement Site 1 was roughly 2,300 feet from the drag strip. Measurement Site 2 was roughly 4,200 feet from the racetrack. Subjective listening during each 10 to 15-second race indicated that the drag- sters produced a very limited noise impact. Based on the "worst-case 11 single-event level (SEL) value, the CNEL expo- sure from dragster operations is 41.9 dB CNEL south of Palomar Airport Road. 0 0 TABLE M 72 CURRENT AIRCRAFT-RELATED WEEKDAY AND WEEKEND CNEL EXPOSURES lsa 0 Total Single-Engine Twin-Engine Aircraft Measurement Propeller Propeller Business Jet Noise Site Number Noise ·Impact Noise Impact Noise Impact Impact 0 {Figure 15} {dB CNELi {dB CNEL} {dB CNEL} { dB CNEL} CURRENT WEEKDAY EXPOSURE 1 45.3 46.6 47.8 51.5 2 42.9 41.4 43.9 47.6 0 CURRENT WEEKEND EXPOSURE. 1 46.2 47.2 49.8 52.8 2 43.9 42.3 45.9 49.1 0 Source: Bioacoustical Engineering Corp. 0 0 0 0 ----------------------------------------- 1 lo I I io 0 0 0 0 0 0 0 0 73 Current Carlsbad Raceway Motocross ·Noise Impact. racing activity occurs at the Carlsbad Raceway on Sunday from as a.m. to 5 p.m. Motocross involves off-road motorcycles in groups 15 vehicles per race. Noise measurements were conducted in late Sunday, January 20, 1980. lsa Motocross early as 8 of roughly morning on Subjective listening at the two measurement points indicated that the motocross sound levels were barely perceptible at the two measurement points. The ."worst-case" analysis indicates a CNEL exposure from Sunday motocross activity to be 48.7 dB CNEL. Impacts. Construction-Related Noise Impacts. There will be a short-term impact on ambient noise levels as a result of temporary construction-related noise. Noise generated by construction equipment, including jack hamners, trucks, rock drills, concrete mixers, blasting, and portable generators, can reach substantial levels. The only potential for problems exists with the residential development north of the property and with future residential development onsite as the property develops in different phases. Future Noise. Environment. Review of the proposed Rancho Car- rillo Planned Community and land use plans for the surrounding area indicates that the property will continue to be exposed to multiple noise sources in the future. Palomar Airport will continue to operate •with the potential for increased operations. Palomar Airport Road will be widened and will experi- ence a s~bstantial increase in traffic (both project-related and non-project- related). It is expected that operations and resulting noise impacts from Carlsbad Raceway wi 11 remain relatively the same. Overall, the project site· is expected to be subject to a greater noise exposure level than is currently experienced. The noise exposure from each primary noise source is discussed in the following sections. Future Aircraft~Related Noise Exposure. The Palomar Air- port Comprehensive Land Use Pl an i nd1 cat es that the 1990 annual operations count may increase to 435,000. Mr. Lacy Clark (Palomar Airport Assistant Man- ager) indicated that this count may be greater than what will probably be realized. However, 435,000 annual operations will be used as a "worst-case" estimate. It is assumed that· the future percentage of aircraft operating on week- ends and weekdays wi 11 be same as the current percentage. This ass um pt ion indicates an average future weekend aircraft count of 1,631 per day and a_n average weekday count of 1,021 per day. 0 0 0 0 0 0 0 0 0 0 74 lsa The Palomar ·Airport Comprehensive Land Use Plan indicates that the cur- rent fleet mix wi 11 change in future years~ The 1990 fleet mix is projected to ··be 75% single-engine propeller aircraft, 22% twin-engine propeller air- , craft, and 3% business jet aircraft. It is assumed that the day/evening/ nighttime operation split will remain relatively unchanged over the next decade. It is also assum~d that the future flight path usage split will be the same as the split for current usage. Weekday flight path operation split will be 40% straight-in, 50% loop, and 10% fly-by. The future weekend flight path operation split is expected to be 25% straight-in, 65% loop, and 10% fly-by. ' Table N shows the results of the noise analysis for future weekday and weekend aircraft CNEL exposure at Site 1 and Site 2 on the property. Compari- son of Tables M and N indicates a· 3.0 to 3.2 dB CNEL increase from current weekday exposure levels to future weekday exposure levels. Comparison of the tables also indicates a 3.0 to 3.2 dB CNEL increase from current weekend expo- sure levels to future weekend exposure levels. Future Motor Vehicle Noise Exposure. As described in the. Circulation Section of this EIR,. traffic volumes along Palomar Airport Road and through the ·project site will greatly increase over the next ten years. Motgr vehicle-related noise levels will comprise a major portion of the noise exposure levels on the Rancho Carrillo properties as a whole. The traffic volumes depicted in Figure 14 of the Circulation section were used as the basis for projecting future (1990) noise exposure levels. As depicted, the traffic study presents two future daily traffic volumes. The first case includes existing traffic,. project-related traffic, and adjacent development traffic (Carlsbad Oaks and La Costa). The second case is identical to the first except for the addition of traffic related to a density housing bonus and school site conversion plan. For purposes of discussion, the two future traffic volumes are referred to as "Ultimate Traffic Without Density Bonus 11 and "Ultimate Traffic With Density Bonus." Table O delineates the roadway parameter values utilized for the noise analysis derived from the traffic report and discussions with Weston Pringle of Weston Pringle and Associates. Table O makes reference to roadway sections by a letter and number designation which is illustrated in Figure 16. The noise analysis included calculations of the expected future noise impact, with and without a d€nsity bonus, for each roadway segment illustrated in Figure 16. Table P presents the results of these calculations. As indi- cated by Table P, there is no significant difference between the two cases .. 0 0 0 0 0 0 0 0 0 0 0 TABLE N FUTURE AIRCRAFT WEEKDAY ANO WEEKEND CNEL EXPOSUREsl Single-Engine Measurement Propeller Site Number Noise Impact (Fi 9ure 15} {dB CNEL} CURRENT WEEKDAY EXPOSURE 1 46.9 2 44.5 CURRENT WEEKEND EXPOSURE 1 47.8 2 45.5 75 Twin-Engine Propeller Noise Impact (dB CNEL} 51.1 45.8 51.9 46.9 Source: Bioacoustical Engineering Corp. 1sased on estimated 1990 aircraft operation counts. lsa Total Aircraft Business Jet Noise Noise Impact Impact {dB CNEL} {dB CNEL} 50.8 54.7 46.9 50.6 52.8 56.0 48.9 52.1 I I I io I 0 TABLE 0 76 FUTURE ROADWAY PARAMETER VALUES lsa 0 0 0 0 0 I I I ! I 10ad"11ay i ?.cadway I ~:.:::.=ace ~'l' I ?ercent Travel Speed ~wrl:er 0f Sec-::..:n i ?ieavy T::af-:ic I l -, I Wit~0UC I • ~iit~ I :.anes I ( see ;:-:G. ::ensi-:y I :ensi~y -=~c:lcs i -~ I I I :lcnus 3cnt:s I ' I i I I I ";alc='.ar I :ll. I 39200 i 4l:!OO s, 40 :-!PH 6 :.i:':'0r! I n 37200 39100 s, I 40 MPH 6 ?.caci I ?J 32900 33500 s, I 40 :-!PH 5 ?4 42400 44200 s, I 40 ':1pg 5 I I 30 MPH i ?-5 aioo !C::300 I 112, 4 I I I l-!ea.:0se !-!l 2::3300 25100 I 31 40 ~H l 4 ... 20500 2.!.000 I I ~vent:e ... I 31 40 MPH 4 ~!3 24.:.co 26600 I 3\ 40 :1PH 4 I I I !·14 20l00 2l600 I 3\ 40 :1PH I 4 l-!5 I l.2900 .l::3600 3% 40 :-.PH· I 4 I I :-!6 ll200 1.:.soo 3' 40 :-!PH 4 !-!7 .!.0800 :.:..;:::io 31 40 l-!li'H 4 I :1-w 2500 3200 o, 25 :-<.Pl! 2 I !·!-E 2200 2700 I o, 25 :-!PH 2 I I i I I ,:ar:r.:.ll0 i --lSJOO 16.300 112, I JS !-'.PH I 4 way ,.. ll500 l.3300 I l/:Zl JS MPH i 4 --l ,... ll400 12200 l/2'\ ?5 )o!l'H I 4 • .1 ' ,., ! l0200 llJOO 11:, 3S :1PH 4 -· I i ---:.osoo i :.:sec l/2 ... 35 :-!PH 4 i -~ I ·== i l400 :.400 l/2 ... ;s :,U,H .. I ! I i .. I :-~9=: :zioo l 2400 0\ 2S :-!PH I 2 c-s~ i lSOO !900 o, is MPH 2 I C-NW I 3800 5000 o, 25 :-!PH 2 I c-s-.-4700 5400 o, 25 !-!PH 2 I I ' :-; i lOOO 1000 Oli ZS !-!PH 2 ; I 1· I 0 .:l Fuerte E:l . 12700 13600 1/2\ JS MPH ~ Str!!~C ::2 12800 -13700 ... l/2'\ JS MPH ,1 E:.3 4500 4800 l/:?'!1 35 MPH 4 C:4 3600 3600 l/:!., JS :-!PH 4 t-E 400 400 l/2'\ 25 :-!PH 2 .Uqa ,\l 2800 2800 l/2'\ JS MPH 4 ?.oad A2 1800 1800 l/2\ 35 MPH 4 0 c~her 11.ll Under Under o, 25 MPH 2. :n'!'l~ior Sections lS00 1500 ! -=~~t!tS 0 0 0 0 0 0 i I io I 0 0 0 0 0 77 16 Roadway Segment Location lsa I I t I... . ... . I \ ~ - / I' ~~--- / " .,, --/ 'rrr I ,I\) I I I C1 I 9l----------\.--- \t -···-···-···-' ... ···-···-···.J .... I I -···-· ·-···-···-···-·· cs (') I (/) rn + N No scale NOTE: Refer to table P for desription of noise levels at indica~ed roadway segments. Source: Bioacoustical Eng. Corp. 0 0 0 0 I 0 0 lo 0 0 0 0 ---------------------- TABLE P 78 FUTURE ROADWAY NOISE LEVELS 100 FEET FROM CENTERLINE lsa ' I I Roadway Roadway rut-:.:re(Ultimate)Noise Impact .\t 100 :'ee~ f:om [ Section Centerline ' t (see F!G. 15) I I 'ilit."l.out Density Bonus I 'ili t."I. Oer.sity Bonus i I i Palomar Pl 70.2 dB CNEL I 70.4 dB CNEL I I Airi)ort P2 70 dB CNEL 70.2 dB CNEL I Road P3 69.4 dB CNEL I 69.5 dB =~EL 1 P4 70.S dB CNEL 70.7 dB CNEL I P-S 55.8 dB CNEL 56.S dB CNEI. Mel:ose Ml ·66.J dB CNEL 66.6 dB CNEL I t Avenue M2 65.8 dB CNEL 65. 9 dB C:-lEL M3 66.S dB CNEL 66.9 dB CNEL M4 65.7 dB CNEL 66 dB CNEL MS 63. 7 dB CNEL 64 dB CNEL M6 63.l dB CNEL 63.2 dB CNEL M7 63 dB CNEL 63.l dB CNEL M-W 47.3 dB CNEL 48.2 dB CNEL M-E 46.6 dB CNEL 47 .5 dB CNEL Carrillo Cl 60.2 dB C!JEL 60.5 dB CNEL Way Cl 59 dB CNEL 59.6 dB CNEL C:3 58.9 dB c:rar. 59.2 dB CNEL C4 58.4 dB CNEL 58.9 dB CNEL cs 58.S dB CNEL 59 dB C:-lEL C6 49.8 d::3 CNEL 49.8 dB CNEL c-m: 46.4 dB CNEL 47 dB CNEL C-SE 44. 9· dB CNEL 46 dB CNEL C-NW 49 dB CNEL 50.l dB CNEL c-sw so dB CNEL ·Sl.2 dB CNEL c-s 43.l dB CNEL 43.l dB CNEL El Fuerte El S9.4 dB CNEL : S9.7 dB CNEL St::"eet E2 ... 59.4 dB CNEL 59.7 dB C~lEL EJ 54.9 dB-C::iEL 55.2 dB CNE:. E4 S3.9 dB·CNEL 53.9 dB C~lEI. E-E 39 . .2·dB-CNEL I 39.2 dB CNEL -I Alqa Al 52.9 dB era:. I 52.S dB OlEL ?.cad .;2 50.9 dB CNEL I 50.9 :S C~JZ!. ' Ot.'ler ... 1 ' -~--44. 9 dB OIEL 44.9 dB ora:. ::i-c:.erior Sect:.::ms St::"ee,:s . • -::,,e :!:~.U-9 :ce:r-•rehi:le:s :,ci.se !...~ac:s ?resen~sC: !.--: :.~!s :able :spr~sa.-11: -·..o:'s-:•-e3se" proje=i:ns. ~"l ~er~or.:iing 1:-~e !~:~:e :-:oisa ~~pac: cal.::-~lai:ions, :10 assu:::pi:icns ~e:a :n&de ==r :'".:~U:-e :::c-cor-•re!'1ic:.le ;-.:ie~i.~g. Al :.~cuc;h ,,ehi:!es !.:i ~~e :· .. n:-:J:~ • ..,ill l.i.<ely =e s0111e1o1hai: quiaca: -:~an =rrani: :::ociels, ~'le .analysi.s •,1as complei:ed .11s.sumi."lg :-:0 ;.::ar:;e :'..."l ·,enic:la :ioise eci.s:sion .. 0 0 0 0 0 0 0 0 0 0 0 79 lsa As would be expected, traffic along Palomar Airport Road and Melrose Ave- nue generates the highest noise levels. Carrillo Way, El Fuerte Street, Alga Road, and other interior streets generate less noise impact. Future motor vehicle noise impact· is projected to increase as little as 2 dBA along existing roadways and as much as 22 dBA along future roadways that do not currently exist. This increase is due to both project-related traffic and traffic generated from future projects in the vicinity (Carlsbad Oaks and La Costa). Future Carlsbad Raceway Dragster Noise Impact. It is assumed that Carlsbad Raceway intends to operate for the i ndefi ni te future. It is assumed the dragster and motocross operations will remain relatively unchanged. Therefore, the current "worst-case" dragster noise impact of 41.9 dB CNEL and "worst-case" motocross noise impact of 48.7 dB CNEL will remain the same in future years. Summary Comparison of Current and Future Noise Exposure. Tab 1 e VII in Appendix I summarizes current and expected future noise exposure levels on and near the project site. In summary, CNEL exposure from aircraft opera- tions is expected to increase up to 3.2 dBA throughout the property. Future motor veh i c 1 e CNEL noise impact is projected to increase as 1 i tt 1 e as 2 dBA a 1 ong existing roadways and as. much as 22 dBA a 1 ong future roadways that do not currently exist. Projected CNEL noise exposure from Carlsbad Raceway dragster and motocross will remain unchanged. These will be unavoidable increases in ambient noise levels. Impacts·· on-·Existing .. Residential. Review of Table VII in Appen- dix I indicates that adjacent to existing homes there is ari increase in road- related noise levels of 8.9 dB CNEL (at 100 feet from the centerline) along El Fuerte Street and 7.9 dB CNEL (at 100 feet from the centerline) along Alga Road west of El Fuerte. This increase is due to both project and non-project- related traffic. The increase, however, does not account for existing topog- raphy or existing manmade barriers. Consequently, it is expected that noise levels at 100 feet from the centerline will be slightly lower and the future increase smaller in magnitude. It is not known whether these increases adversely impact the existing homes because no analysis has been conducted to determine effects of existing- manmade barriers, location of housing,· and topography on these exposure lev- els. Also, the noise analysis does not indicate the contribution of the proj- ect-related traffic to the total noise exposure level. I :O 0 0 10 I 0 0 0 0 I ' 80 lsa Total Future Noise Exposure. Figure 17 illustrates the results of noise mode 1 i ng which combined the effects from the four noise sources i nt_o a total future noise exposure. The figure illustrates four zones of noise exposures which are as follows: Zone 1: Zone 2: Zone 3: Zone 4: Over 70 dB CNEL From 65 dB CNEL to 70 dB CNEL From 60 dB CNEL to 70 dB CNEL From 55 dB CNEL to 60 dB CNEL These zones were calculated by a model which did not take into account exist- ing or future topography, manmade barriers, or effects of development. Fig- ures 10-35 of Appendix I further illustrate these zones. Figure 17 indicates that the area north of Palomar Airport Road was not studied for its future noise exposure. Specific land uses have not yet been determined specifically for the northern area, but initial planning indicates there will not be any noise-sensitive land uses which would require a detailed noise impact assessment and noise attenuation design. Noise-sensitive uses include. such uses as: motels, hotels, certain retail uses, apartments, condo- miniums, single-family dwellings, schools, and hospitals. However, traffic potentially generated from these areas was included in the. total traffic numbers utilized for road-related noise exposure on sur- rounding areas. Mitigation Measures. The following measures are included as part of the project or are otherwise required to bffset any potential adverse impacts. 35. Prior to submittal of ·the tentative maps, a detailed acoustical analysis and noise control program must be com- pleted and submitted to the City for review. This analy- sis and control program must reflect any potential changes in the estimated future noise exposure levels due to revised or new information (i.e., additional traffic vol- umes, etc.). It must provide a noise control program utilizing such features as setbacks, noise barriers, and/ or housing design in order to reduce the noise exposure levels to State and local standards. Effects of natural and manufactured topography must be considered in the analysis.· For clarity, this study should also clearly state the separate contribution of the four various noise sources as well as the total noise exposure level. I I I iO 0 0 0 0 0 0 0 0 I i-o 0 81 17 Ultimate Noise Exposure-lsa .:::"'-1-• .· . ·. _:·_.: • N I • '/ • ·.• . \ ._ ... :. ' ._, . . . . . ' .. . . .. • \_ .. .-~ • ·_ ..• i ·_, . . .. . . . r .-. ·= .' .·_ : ·_ -/ ., . . . . . . ,·· .. .:i 4 .. .. . ,.-. :\! . . . · ... ;·: -••-.;. ,• --·:~ :.\:.. . ·. ~1 . /•.. •• . . . \ · \ :i:~'=:~::;::\:'.;,::;;:_>': ·~ • \. •. \ 4 • • ... \.. . :_ ·:.\· . ·. . .... . ·:\:· ... • .•• • \·· ·-. ' 4 ·\;-·: N.A.P. .. ~EGEND Zone 1. Over Zone 2. 65 - Zone 3. 60 - . . '• ... . . '·~-' . • .. . • . . .,.,__ . 70 dB CNEL ~ _· dB CNEL \ dB CNEL Zone 4. 55 -60 dB CNEL Source: Bioacoustical Eng. Corp. \. ·\ 0 0 0 0 0 0 0 0 ! 0 0 0 36. 37. 31. 82 The noise study in Appendix I discussed commonly used mit- igation measures and their potential mitigating effects. These measures and others wi 11 be considered at the future level of analysis. Prior to submittal of the tentative maps for any area north of Palomar Airport Road, a noise study shall be pre- pared to the satisfaction of the Planning Director. If any noise-sensitive uses are proposed for this area, such a study with an accompanying noise control program should be conducted and submitted to the City with the site pl an. In conformance with Chapter 21.34 (P-M Planned Industrial Zone), Section 2.1.34.010, only those uses which do not generate a sound lev~l in excess of 45 decibels at the boundaries of the site will be permitted in the industrial area. An FAA-funded Airport Noi SE3 Contra 1 and Land Use Compat i - bility study (ANCLUC) is. to be conducted on Palomar Air- port in 1981. This study should be available in late 1981. The ANCLUC will develop a new set of noise contours for Palomar Airport and will identify possible noise abatement actions. When available, the City of Carlsbad will review the ini- tial and final findings of the ANCLUC in relation to the· Master Plan for Rancho Carrillo. 32. All prospective purchasers of residential properties· with- in the Rancho Carrillo Planned Community must be clearly notified of airport operations (both existing and future) in writing by the seller prior to the close of escrow. To this end, the project applicants are asked to review, as a possible mechanism, the feasibility of requiring avi- gation easements, as suggested by Philip Safford, Palomar Airport Manager, in a letter dated July 22, 1980 (Appendix K). COMMUNITY SERVICES ANO PUBLIC UTILITIES lsa Setting. The following discussion describes services to be provided to the project site. Appendix K of this report includes correspondence received from potential purveyors of these services. 0 0 0 0 0 0 0 0 0 0 83 lsa Fire Protection Service. The City of Carlsbad has a substation with four men at Arenal Road and El Camino Road. Estimated response time to the project is five to six minutes to the southern portion and approximately eight minutes for the entire project at buildout. The City 1·s substation at Chestnut and Catalina would provide a response time of approximately nine min- utes. Police Service. The City of Carlsbad Police Department operates from its station at 1200 Elm Avenue. Patrol cars respond in five to six min- utes to calls within the City limits. Water Service. There are existing water lines along Palomar Airport Road adjacent to the site. In 1974,_the Carlsbad Municipal Water Dis- trict prepared a Master· Plan for a public water system for Rancho Carrillo (Woodside/Kubota, 1974). This plan was prepared based on the original Rancho Carrillo Master Plan adopted by the City in 1972. However, since proposed land uses of the proposed revised Rancho Carrillo Master Plan differ from the original, the water system plan will require review and probably revision by the Carlsbad Municipal Water District. Wastewater Service. There are presently no sewer facilities servicing the proJect area. However, the City of Carlsbad recently voted to approve formation of an assessment district to fund the Palomar Airport Waste- water Treatment Project. This project, when completed, will supply Rancho Carrillo, along with several other major developments, with sewer capacity. The estimated date of operation for the Palomar Airport Wastewater Treatment Project is the spring of 1983. Gas and • Electric • Service. The San Di ego Gas and Electric Com-· pany serves the site. There is presently no underground electrical system in the area, but overhead 12 kV and 69 kV lines transverse the site. A 16-inch gas transmission main exists 13 feet under Palomar Airport Road. A 3-inch local distribution line occurs at Poinsettia Avenue (Linda Vista Drive). Solid Waste. The McDougal Sanitation Corporation is currently under contract with the City of Carlsbad to service solid waste. Solid waste is transported to the Palomar Transfer Station at El Camino Real and Palomar Airport Road. Waste is .then sorted and separated for recycling; uncycled waste is taken to either the Bonsall landfill on Gopher Canyon Road, which has a projected life span of three years, or the San Marcos landfill at Rancho Santa Fe and Questhaven, with an estimated life span of 20 years. Hazardous waste is processed at the 0tay Mesa landfill. 0 0 0 0 0 0 0 0 0 0 0 84 lsa Libraries. The City of Carlsbad presently has one library located in the northwest quadrant of the City. Outlying areas are served by a mini-bookmobile. At present, the library is barely adequate to serve the growing City; a new central library is therefore planned. As recommended in Master Plan. No. II for the Carlsbad City Library, the new central library will probably be located near the City1 s geographical center, in the area of Palo- mar Airport Road. School Services. Rancho Carrillo lies within both the San Mar- cos and the Carlsbad Unified School Districts. There are no existing schools within the project area. The San Marcos School District includes four elemen- tary schools, one junio.r high school, and one high school. All four elemen- tary schools are presently beyond their capacity, according to Mr. David Larson, Di rector of Business and Operati ans for the District. The District offers bus transportation services for its students at an estimated cost to the col11llunity of ?Of per student per day. The Carlsbad Unified School District includes five elementary schools, one junior high school, and one high school. None of the District1 s schools ·is at capacity enrollment at this time. The Carlsbad School District does not provide bus services to the students. Hospital Services. Rancho Carrillo lies within the Tri-City Hospital District. The District, which ser~es Carlsbad, Vista, and Oceanside, includes the Tri-City Hospital in Oceanside and Tri-City West, also in Ocean- side. Both hospitals have an urgent overcrowding problem. 'The Tri-City Hos- pital, which is the larger of the two with 231 beds, has an occupancy rate of 95%. Tri-City West has· only 67 beds and 85% occupancy. The district is the fu 11 est in both San Di ego and Imperi a 1 Counties, and more than 600 elective surgeries were turned away in 1980. Most of the turned away would-be patients go outside their district to the North San Diego Hospital District with hospi- tals.;~ Escondido or Scripps Memorial Hospital in Encinitas. Transit Service. The North County Transit District provides bus service on El Cami no Real from Camp Pendleton to Cardi ff. This bus line, Route 1309, is a corridor route with infrequent service. No local routes ser- vice the project area. Impacts. Fire Protectiori·Service. The project 1 s size and number of dwell- ings will increase the frequency of· fire alarms. Fire-related incidents will require a two-station response, and medical emergencies will require a one- station response plus a paramedic response. The two existing substations 0 0 0 0 0 0 0 0 0 0 0 85 lsa closest to the site exceed the m1n1mum five-minute response time. This devel- opment would, therefore, require construction of a future fire station in the area of Alga Road and El Fuerte Street as proposed in the Fire Department's Master Plan. This impact would also include additional personnel of nine firemen to staff the station. Existing paramedic facilities are adequate to service the development. Fire Chief Thompson indicates that the need for the new station will be reached when at least 1,000 dwelling units in Rancho Car~ rillo have been occupied. Police Services. Captain W. D. Rosell of the Carlsbad Police Department estimates a factor of 1.4 officers per 1,000 population, as a rule of thumb. Given a population estimate of approximately 10,000 for Rancho Car- rillo {based on CPO dwelling-unit factors, CPO, 1980a), the project will require 14 additional police personnel. The severity of this impact is not considered significant, since revenues to the City generated by the develop- ment should cover the cost of the additional police personnel and facilities. The Po lice Department I s concerns include increased traffic congestion on Palomar Airport Road and the potential for burglaries in the project's commer- cial area. • • Water Service. Based on CPO projection factors of 2.6 persons per dwelling unit, a residential consumption factor of 170 gallons per day per person, and a commerci a 1-i ndus·tri a 1 factor of 1,600 ga 11 ans per day per acre, Rancho Carrillo's water consumption at occupancy will .be an estimated 1.50 million gallons per day (mgd). This calculation includes the additional units that would result from the school site redesignation to residential use. Wastewater. The report for the Palomar Airport Wastewater Ree- l amat ion ProJ ect estimated a tota 1 wastewater fl ow of . 76 mgd for Rancho Car- ri 11 oat occupancy. This figure, incorporated into the design parameters for the P.alomar Airport wastewater facilities, is based on a residential genera- tion factor of 200 gallons per day per single-family dwelling unit or its estimated equivalent and. 1,600 gallons per day per commercial-industrial acre. The estimate does not include population counts from the school site redesig- nation. The estimated completion date for the Palomar Airport facility is compatible with this project. Gas and Electric Service. SDG&E does not anticipate any prob- lems serving the project with natural gas or electricity. This project has two possible points of service for natural gas. The first would be to tap the 16-inch gas main at Palomar Airport Road. This would require installation of a gas pressure regulator station, since the existing pressure (800 psi) at the main is not appropriate to ·serve local distribution. The second alternative ------------------------------------- I 'O I I 0 0 0 0 0 0 0 0 0 86 lsa is to extend the local distribution li!Je from Poinsettia Avenue. Required extensions for both gas and electricity to serve the proposed development are the responsibility of the developer. Solid Waste. Using the California Solid Waste Management Board 1 s solid waste generation factor for metropolitan residential areas (Cal- ifornia Solid Waste Management Board, 1974), residential solid waste products will be 19,480 pounds per day, including additional units from the school site redesignation. McDougal Sanitation, Inc. foresees no problem in serving Rancho Carrillo (Sims, personal communication). Libraries. The new central library location proposed in the Library Master Plan will service areas of future development. Rancho Carrillo will, therefore, have no adverse impacts on the library system. School Services. The San Marcos Unified School District esti- mates an enrollment factor of .27 school-aged child per dwelling unit (Larson, telephone communication). The Carlsbad Unified School District uses a factor of .25 student per dwelling unit. Based on these factors, and the number of dwelling units plus the additional units resulting from the possible redesig- nation of the chool site to residential use, the total estimated number of students generated at buildout of Rancho Carrillo would be 843 or 780, depend- -ing on the factor used in calculation. Hospital Services. The California Hospital Association recom- mends a service factor of three to four hospital beds per 1,000 persons. This would demand 30 to 40 more beds to accommodate Rancho Carrillo 1 s ultimate pop- ulation based on CPO population factors. The Tri-City District is in the process of filing a Certificate of Need with the Health Systems Agency for the addition of 100 more beds. This petitioning process is lengthy and the expan- sion will probably not be realized for another three or four years, approxi- mately in phase with Rancho Carrillo's development. Scripps Memorial Hospital is petitioning to change 19 psychiatric beds to medical beds within one year and anticipates 200 more beds by 1990. The North San Diego Hospital District has undetermined pl ans to increase its bed count in the next five to eight years. These increases are proposed to mitigate current overcrowding and to offset the impacts of future development. Transit Service. The North County Transit District expands ser- vice as demand warrants (Lichterman, personal communication). Thus, the development of Rancho Carrillo will encourage the transit district to expand its services into the project area. 0 0 0 0 0 0 0 :0 0 ,0 I I I 0 87 Mitigation Measures.· Fire Protection Service. 40. The future fire station proposed in the Fire Department's Master.Plan in the area of Alga Road and El Fuerte Street. wi 11 be constructed to meet the fire protection needs of the deve 1 opment. The new station sha 11 be ope rat i ona 1 no • 1 ater than the ti me of occupancy of 1,000 dwe 11 i n·g uni ts in Rancho Carrillo. Police Services. 41. The commercial and industrial areas of the project will employ internal security systems including security guards and an alarm system to deter burglary and vandalism. This will reduce the demand on police services required by the project. Defensible space concepts wi 11 be incorporated to deter vandalism. "Defensible space" refers to physical design characteristics that maximize control of behavior, partic- ularly crime. Three major objectives of the defensible space concept are: 1) achieving visibility (from building areas to adjacent parking areas and vice versa), 2) creat- ing zones of territoriality through site plan grouping and designation of areas as either public, semi-public, or private, and 3}_ providing easy access for policing capa- bilities. Water Services. 42. At the time of subdivision submittal, the City of Carlsbad and the Costa Real Municipal Water District will review the Rancho Carri 11 o Master Pl an for Public Water System (Woodside/Kubota, 1974) to determine its applicability to revised consumption and fire flow figures of the new Ran- cho Carrillo Master Plan. At that time, the City will also require that t~e planned community's non-potable water needs be defined and that the water district consid- • er services based on these needs. 43. At the time of site plan review, fire flow demands will be re-evaluated, if necessary, since the distribution of lsa 0 0 0 0 0 0 I I 0 0 0 0 0 88 dwelling units within any one given residential area could drastically change fire flow requirements 'and pipeline sizes. 44. Development landscaping in public and private areas will emphasize low-water-consuming plants, such as native spe- cies, and will utilize mulch to maximize water retention. 45. Public and private toilet facilities will be low-flush toilets and low-flow faucets. Insulation will be required for hot water lines in water recirculating systems. Any public flush valve-operated water closets will have a three-gallon flush, and drinking fountains will have self-closing valves. Wastewater Service. 46. The City of Carlsbad's Engineering Department will review the proposed sewer system at the ti me of subdivision map review and approval to assure its adequacy. lsa Gas and Electric Service. No mitigation measures are proposed. Solid Waste. No mitigation measures are proposed. School Services. 47. The developer will consult with both school districts to determine the most feasible boundary line for the dis- tricts within Rancho Carrillo. This boundary alignment shall be defined before approval of the Master Plan, at which time the districts will specifically assess how they will be impacted by the development, and will consult with the developer to formulate appropriate mitigation meas- ures. Libraries. No mitigation measures are proposed. Hospital Services. Transit Service. No mitigation measures are proposed. 48. The Rancho Carrillo circulation system will include fea- tures to accommodate transit services. Features will 0 0 0 0 0 0 . o 0 0 0 0 89 include streets with weight capacities and turning radii for 40-foot coaches and main through arteries to provide access for easy routing. lsa If these measures are implemented, any potential adverse impacts on com- munity services and public utilities will be adequately mitigated. AGRICULTURAL RESOURCES Copley International Corporation (CIC) conducted a study to assess the agricultural viability of Carrillo Ranch. Two studies, based on existing data supplemented by onsite visits, analyzed north and south parcels of the proper~ ty divided by Palomar Airport Road. A sunmary of the reports, which are on file with the City of Carlsbad, is presented on the following pages. Setting, The agricultural viability of a particular parcel is deter- mined by a wide variety of factors. In combination, these factors encourage or limit agricultural use. The factors can be broken down into two broad cat- egories: physical resources and economic considerations. Table Q 1 ists the . items within these two groups which must be evaluated. Physical Resources . Topography. Topography affects agricultural capabilities of r the land by limiting the size of areas suitable for agricultural fields. Also, soils have a greater tendency to erode when they are on sloping ground. These basic fact.ors tend to limit agricultural activities to ground that is nearly level and fairly l~rge. The northern parcel could acconmodate two fields of roughly 30 to 40 acres each. Ultimate size would depend on which crops are produced and wheth- er they could be grown in the canyon which divides the site. On the southern parcel, topography limits the area suitable· for agriculture to only 107 acres of the total 675-acre site. Climate. Rancho Carrillo lies within the Coastal Climate Zone. Just east of the Maritime Zone, the Coastal Climate Zone is outside the summer fog line, but within the climatic influences of the ocean. The mean annual temperature is 60°F, with a 30-day freeze hazard in January. Mean annual precipitation is 10 to 15 inches. Agricultural products that typically do very well in these climatic conditions include tomatoes, flowers, avocados, truck crops, and citrus fruits. 0 0 TABLE Q 90 FACTORS DETERMINING AGRICULTURAL VIABILITY lsa 0 Suitable for A5riculture Truck Noc Ph?sical Resources T0111atoes ~ Flowers Avocados ill!2 Suitable Geology 0 Landslide Potential Law I I I I I High L L L L L L Groundwater Depth Shallow HI N1 N1 HI N1 Deep HI HI NI HI N1 Economic Considerations 0 Cultural Costs Law I I Medium I High I I Harvest Costs Law Medium I I I 0 High I I Fized Costs Low Medium I I I High -I I Price 0 Variable I I I I Stable I Yield Low Medium I High I I I I Competitiou 10 Little I Several I I I I Ket Income Low I I High I I I Return on Investment i Low I ,0 High I I I I I.eat vs. Own Land Beat I I I -Own I I Cropping Program !location I I I Relation co Physical 0 Resources MI MI MI I MI Legend: I -Important MI -Mcderacely Important HI -Not Important lo L -Limiting I i 1,0 I 0 0 0 0 0 0 0 0 0 I 'O I TABLE Q (CONTINUED) FACTORS DETERMINING AGRICULTURAL VIABILITY ?!!Ysic:al ~esou:':99 ~~c~es ~ooa.z:-2:hv Slope r..vel !« 15: • :a: . .. JC: -so: r. 11&.ld S.1:a Saal.l (<':O ac::u) r.. !'.ariiu= c:o-sa 1c::11s) t. i..&r;e (~O ac::as •) t nood lta::lr:-i!!.;h r. !ros1ca ?ocanc~a.l. t.cv t U;h t. i:l!::aca Tlll!l•rac:::a Cold (i:l.c. =~=sc) t. l!adium I itoc r. lt1r 0n1:age Poor ~ Good ~ ~. Qls&il':'] t.cv t. l!atliim ! ua: !£t A.~ili::7 ?oor t.' ~cd I ~ Su~ac•• Qu,al!=-, ?aor r. G.cod t l>ra.:l.:age ?ocr r. C.Ood !£t C.pac1!!:7 C!.s3 ti!: !'!I !II i :7 I '1 -1tI: r. Stcr!e ::iae.,: 30 -~co !£t ,o -:9 t 40 -S9 i. 3elcv :.o r. to.geed: : -::0c~;mc ~ • ~acierace.!.:, ::::ior-::mc n -!foe ::cor:mc: t. .. :.i:L:!.::; 91 lsa S111:ai:li.e ==-:: .-'i:~:::i.L:-.i~!! T::-.:ck !foe ~ :°!.:WCi!!'S A•10c:1d0s ':!::-w:s Sui:~Ol~ !« MI !'!I ~ r. t. !'!I MI • i. r. r. t. .. t. t. I t. . t. t : .. t !£t !£t !£t t. i. t t r. I t !£t MI r. . t. t. t. t. i. t. r. t. t I I I t. t. lit lit !£t !£t t. t. r. !£t !£t I t ... t. t. . r. .. I !£t I t I !£t l!I !" t. . t. t. t. ... t t I I r. • !£t t. t. .. t .. t !£t .. . t. t. r. r. .. !£t ~ :it l!I l!I l!I !II MI t .. lit t .. r. !. !'I t. t. MI !'!I n MI .,. ! n . .. .. r. t. !£t r. r. r. !£t t. . .. (continued) 0 0 0 0 0 0 92 lsa Water. Water from the Carlsbad Municipal Water District is suitable for irrigation of food crops and is readily available. The Leucadia County Water District has plans for a wastewater reclamation plant which will produce reclaimed effluent water. Landscaping and flower crops can be irri- gated with this water. Gladiolus can tolerate the probable chemical levels in the reel aimed water if frequent subsurface drainage and 1 eachi ng management are provided. Gladiolus are compatible with roughly one-fifth of the agricul- turally suitable soils on the southern parcel. Soils. All soils on the 71-acre northern parcel are rated as agriculturally suitable by both the Soil Capability and Storie Index rating systems. Thirty-nine percent of the soi 1 s on the southern parcel (263 acres) are classified as agricultural soils by the ~oil Capability Rating System. However, only 156 acres are very marginally suitable for agricultural produc- tion because of: 1) steep slopes, 2) soils with a high clay content, and/or 3) shapes of some soil units, limiting possible field size. Of these 156 acres, only 107 acres can be deemed truly appropriate for agriculture. Geoloqy. Geologic formations affect soil characteritics and thereby influence agricultural viability. Geologic studies for the Car- rillo Ranch have been conducted by Geosoils, Inc., and are summarized in detail in the Earth Resources section of the EIR. 0 Geologic features of particular importance to agricultural viability include clay content of sails, landslides, and proximity of groundwater ta the surface. Clay sails are expansive and highly erodible. Groundwater close to the surface increases erosion potential and mandates subsurface drainage man- agement if irrigation is to take place. IO Clay soils within the northern parcel having a moderate to high erosion potential would require irrigation and drainage management. In the locations where landslides have been mapped, care would be required for tilling, wet- ting, and drying. The majority of the soils within the southern parcel are either clays or 0 have clay subsoils. Their expansive qualities make the soil unstable and increase landslide potential. Great care would be needed in the areas of wet- ting, drying, and subsoil irrigation drainage if any of these soils were to be cultivated. Geologic bedding on the south and east sides of the southern par- cel dips to the north and northwest. The bedding serves as support for the dynamic clay soil material, and thereby increases the landslide potential. 0 Most of the landslides noted by Geosoils, Inc., however, are on the steeper, non-agricultural soils. 0 \ 0 0 0 0 0 0 0 0 0 93 J lsa On the southern parcel, groundwater exists at 5 to 30 feet below the sur- face in the major valley's alluvial areas. This increases erosion potential and mandates subsurface drainage if irrigation is to take place. Cultivation of the soils on the southern parcel would require great care in tilling man- agement, wetting and drying, and subsoil irrigation drainage. Such measures would be costly and might make agricultural use of these soils unfeasible. Crop Suitabilit~. Agriculturally suitable soils can be better adapted to some crops t an to others. Table R surnmari zes the areas receiving "good" and "fair" ratings. Avocado and citrus crops are not suited to the soils found on Carrillo Ranch. For avocados, clay soils ·and claypan layers below the surface are the major limiting factors. Clay soils coupled with an unfavorable climate prohibit citrus production. Suitability for truck crops is determined by subsoil permeability. Those areas rated "fai r 11 are partially limited. by slow permeability. However, they could be successfully farmed with truck crops provided proper subsoil drainage and careful irrigation management were incorporated. 11Good" and "fai r 11 areas for tomato production are found within both the . north and south p~rcels. The areas rated as "good 11 present few or no limita- tions to tomato production. The areas with "fair" ratings are limited by slope and thus require erosion control measures. Fl ewer crops can be grown on both the north and south parce 1 s. The 11 good 11 areas have no limitations for flower production. Within the "fair" areas, surface soil texture limits yield and increases erosion hazard. Present·· Land Uses. At present, fie 1 ds on th:e northern par- cel have been plowed. However, nothing is being produced on the southern par- cel, although avocados are being raised to the east. Surrounding land uses include Carlsbad Raceway directly north of Rancho Carrillo-, and residential uses along the southern boundary. Proximity of res- idential uses to agricultural land on the southern parcel poses a potential conflict. Agricultural activities such as aerial application of pesticides and fertilizers, and the noise associated with farm machinery, could prove objectionable to nearby residents. Economic Considerations. Based on the analysis of physical resources, 71 acres on the north parce 1 and 107 acres on the south wi 11 sup- port agriculture. Actual farming· cannot be conducted without regard to econ- omics, however. The decision to farm must be based upon the expected income value resulting from the investment in land, equipment, and operating capital. The following pages address the size of the investment required and the income value which could be expected to result. 0 ! 10 TABLE R 94 CROP SUITABILITY OF SOILS lsa 0 Soil l/t of ~ ~ Avocados Ci:':"t!S Tr-.1c:k Cr~t,s Tomatoes Flowers AcC 31 N/R N/R N/R Good N/R 0 AcD 96 ~1/R N/R N/R ?"a::.= (s) ~T/R AcE 35 N/R N/R. N/R. Fai= (s) N/R AcE:? 22 N/R N/R N/R ]:'air (s) N/R C::E2 4 N/R N/R. N/R N/R N/R 0 GaE 59 N/R N/R -N/R ··~UR N/R. GaF, 32 N/R N/R N/R. N/R. N/R. HrC 97 N/_R N/R. Fair (p) Good Fair (C) HrE2 69 N/R N/1l ~t/R N/R N/R 0 Lee . 37 !1/R N/R Fair (p) N/R Good LaE !l N/R N/R N/R. N/R N/R LeE3 4 N/R N/R N/R N/R. N/R LrE l32 · N/R N/R N/R N/R N/R 10 Lr.S:2 2 N/R N/R N/?.. N/R N/R. LsE 9 N/R N/R N/R. N/R N/R Rm 9 N/R N/'8. N/R N/R N/R ScA. • '29" N/R N/R N/R Good N/R 0 Source: Soil Sur.rev of San Die20 Area, Califor.-:.i.a, USDA, Decemcer 1§13. Key: Good no special managemenc is ~ecessar7 Fair some special :nanagernenc is necessar7 0 N/R. not raced, unsuiced :o ag::icul :-ure (s) slope is :he :iain limiting ::ic:or (p) slow per~eabili:y is ~he oain limi:ing fac:o-r (c) surface layer cexcure is :he main li:ni:ing fact:or 0 0 0 0 0 0 0 :o i •o I I 10 0 ---------------------- 95 lsa On the northern parcel, tomatoes and truck .crops are most likely to be grown. Tomatoes could be grown on the 53 acres where clay soils occur, although they should be rotated with other crops (e.g., celery) to control pests and diseases. The remaining 18 acres could support production of truck crops. For the southern parcel as well, the best yields could be expected for tomatoes and truck crops. - Cash Flow Analysis. Tables S and T present cash flow anal- yses for the northern parcel of Carrillo Ranch. Table S presents farm reve- nues for 1980 and 1981 and Table T forecasts revenues for a six-year period through 1985 for both rent a 1 and ownership of the property. Under either sit- uation, Tables Sand T show that a profit can be made in alternate years, cre- ating a positive cash flow in the long run. (A profit in alternate years stems from the fact that eel ery revenues are received only in the odd-numbered years.) When the land is rented, the farm earns an average of $49,091 annual- ly, or S691/acre. When the land is owned, $7,955, or $112/acre, is the aver- age annual earnings. The southern parcel is evaluated according to three different assumptions of operating ownership for economic viability: a) Landlord/tenant arrangement; 1 and is rented at $150 / acre for the first three years and $175/acre each year there- after. b) Net farmable acreage (100 acres) is purchased and the mort- gage payment is included in the fixed costs of production. c) Entire southern parcel of 675 acres is owned. Under Option A where the land is rented, the farm earns an average of $113,291 annually, or $1,133/acre (adjusted for inflation using an 8% discount rate). Under Option B where 100 acres are owned, $63,202 is the average annu- a 1 earnings, or $632/ acre (8% discount rate). The average annua 1 earnings under Option C where the entire parcel is owned are <$299,286>, or <$2,993>/ acre (8% discount rate). The cash flow analyses for both the north and south parcels indicate a trend that has been operating within the agricultural economy for the last ten years. Costs have been increasing faster than revenues, thus shrinking profit margins. Investment Analysis. Given the projected cash flows, the next step is to determine percentage return on Investment (ROI). If the annual ,0 I i 'O ,0 0 0 0 0 ,0 0 0 TABLES NET FARM REVENUE (NORTHERN PARCEL) REVENUES I Spring tomatoes Celery Fall tomatoes Squash Cauliflower Total annual revenues VARIABLE COSTS Spring tomatoes Celery Fall tomatoes Squash Cauliflower Total annual variable costs FIXED COSTS Management Equipment investment Interest on operating capital Depreciation· • General overhead Total fixed costs Total all costa Net f ann revenue 96 1980 $548,011 51,288 56,100 $655,399 $441,452 93,456 42,420 34,155 $611,483 $ 16,300 54,810 9,554 8,143 1,950 $ 91,757 $703,240 $(47,841) lsa 1981 $245,048 453,552 51,288 56,100 $805,989 $ 93,456 377,872 42,420 34,155 $547,903 $ 16,300 54,810 8,561 8,143 2,950 $ 90,764 $638,667 $167,322 Source: Agricultural Crop Report, Department of Agricultural Weights and ~eas- ures, 1968-79. Copley International Corporation. '1 iO I .o 0 .0 lo 0 0 :o lo 0 I I 0 I TABLET ANNUAL AND CUMULATIVE NET FARM INCOME (NORTHERN PARCEL), 1980 CONSTANT DOLLARS Year 1980 Annual Cumulative 1981 Annual Cumulative 1982 Annual Cumulative 1983 Annual Cumulative 1984 Annual Cumulative 1985 Annual Cumulative 97 Source: Copley International Corporation. lsa Rent Purchase 71 Acres 71 Acres $ (58,491) $ (156,663) (58,491) (156,663) $156,672 $126,944 98,181 (29,719) $ (58,491) $ (88,219) 39,690 (117,938) $156,672 $126,944 196,362 9,006 • $ (58,491) $ (88,219) 137,871 79,213 $156,672 $126,944 294,543 47,731 i I lo 0 0 98 lsa return is lower than could be obtained from an alternative investment program, whether in agriculture or another investment opportunity, then the farmer would most likely invest his capital in another way. o The expected returns for the north parcel are 9.89% if the land is rented 0 0 0 0 0 0 0 and 3.16% if owned. (A typical agricultural return for a farm of this size is about 9. 5%.) These rates of return are not expected to be consistent from year to year, however. Revenues for the crops could be expected to vary from 14 to 40%, depending on the crop. In a bad year, revenues might not cover all costs. Rates of return expected for the south parce 1 for the three operating options are 1.36% (rental), 0.5% (100-acre ownership), and 12.5% (675-acre ownership). Again, rates of return are expected to vary from year to year. Under high-risk conditions, an investor will invest capital only when an equally high rate of return is expected. In general, ROis such as those for the northern parcel of 3.16% and 9.89% are considered only moderate rates of return. Because agricultural land values have been appreciating in recent years, however, farmers have been wi 11 i ng to accept 1 ower rates of return on their operations in order to realize large capital gains when their land is sold. ROis for the southern parcel are quite low, however. When risk is incor- porated, neither of the ownership situations could be considered attractive investment options, even when an allowance is made for long-term capital gains based on 1 and appreciation. On 1 y the rent a 1 of 100 acres \'IOU 1 d be economi ca 1- 1 y justified. It should be noted that the land value of $4,820 per acre used by Copley International Corporation (CIC) in these calculations is low. A more real- istic value would be closer to $7,000 per acre. In actuality, then, R0is would be slightly lower than reflected here. Impacts. The project would result in the loss of approximately 178 acres of agriculturally viable land. This loss represents an irreversible commitment to abandon the agricultural resources onsite. These resources include agriculturally suitable soils and the climatic advantages of the coastal climate zone. The impact would not be a direct displacement of exist- ing land use since there is presently no agricultural activity onsite; rather, the impact effectively eliminates the alternative of future agricultural use. / 0 0 0 0 0 0 0 I ,0 0 0 0 99 lsa The conversion of agriculturally viable lands to urban land use is a quickening trend in northern San Diego County. The loss of potential agricul- tural lands onsite would probably result in an incremental decrease in region- al truck crop and tomato production. This conversion, in concert with the loss of an untold amount of additional· acreage in the North County, represents a regionally significant cumulative impact. Mitigation Measures. 4·9. The City will consider requiring that the developers offer short-term leases of agriculturally viable parcels onsite, to the extent feasible, until such time as they are to be developed in phase. 0 0 0 0 0 0 0 'O 0 0 0 ------------" 100 lsa ALTERNATIVES TO THE PROPOSED PROJECT ALTERNATIVE 1 -NO PROJECT This alternative is required by the State EIR Guidelines. Its intent is· to provide insights into the types of effects which could be expected should the project not be implemented. If this alternative were to be selected, it would avoid most, if not all, of the impacts identified in the text of this EIR. The property would remain vacant, undeveloped land with human activity limited to ranch house operations and maintenance of onsite easements (i.e., excess effluent pipeline). • Biological resources onsite would stabilize from their present st.ate of flux and continue in a relatively natural state. Natural topography would remain unchanged, and onsite runoff and groundwater would continue their pres- ent direct i ans of fl ow. Traffic generated by deve 1 opment of the property and its associated incremental degradation of air quality and the noise environ- ment would not impact the site of the local area. Impacts on the site from regional sources would continue to occur without this development, such as increasing traffic volumes on Palomar Airport Road and Melrose Avenue, and increasing the levels of noise and air pollution. This alternative, although environmentally superior to the proposed proj- ect, would not be consistent with the interests of the current property owners and would not necessarily fulfill the intent of the City's General Plan. Additionally, due to the increased rate of development expected in the vicini- ty of the study area, open-space uses would not represent a long-term, econom- ically viable land use. As property values continue to rise, the property wi 11 eventually become an unproductive economic burden to the property owners. In addition, beneficial socio-economic effects (increased jobs, tax revenues, recreational opportunities) would also be avoided. ALTERNATIVE 2 -AGRICULTURAL OPERATIONS The project site is not currently under cultivation. However, the agri- cultural report does indicate that there are soils onsite suitable for agri- cultural operations. Under this alternative, the site would (where feasible) be under active cultivation. Given terrain, soil conditions, and soil loca- tion, the northern parcel is more suitable for extended agricultural opera- tions than the southern. This alternative would avoid most of the impacts associated with urban development and the proposed project. It would avoid impacts on the circulation system, ambient air quality, ambient noise levels, most of the impacts on significant biological resources, some of the impacts on cultural resources, and impacts on existing service systems. 0 0 0 I ' I I I 10 0 0 0 0 0 101 lsa This alternative would also provide an increased supply of actively farm- ed agricultural lands in an area rapidly losing much of its prime farmlands to increased urbanization. However, as indicated in the agriculttiral section of this report, given the expected increase in development in the near vicinity, the types and amounts of crops feasible for the site, and the fractured owner- ship of the properties, agricultural operations would not represent a long- term, economically viable land use. With the expected increase in property values, the property would eventually become an economic burden to the proper- ty owners. ALTERNATIVE 3 -DEVELOPMENT UNDER PREVIOUS MASTER PLAN FOR RANCHO CARRILLO As described in the Land Use section of this report, the previous Master Plan covered the same property as under the currently proposed Master Plan. The mix of uses is basically similar. However, the previous Master Plan allows for a maximum of 3,695 dwelling units as opposed to the currently pro- posed 2,998 (3,122 with the schoo 1 site conversion). It al so included a non- resi denti a 1 reserve area as opposed to the industrial area designated under the currently proposed plan. Other land uses were substantially the same. Development under this alternative would not have any environmental bene- fits over the proposed project. It would have virtually' identical physical environmental impacts on earth, water, cultural, and biological resources. Because of the greater number of residential units allowed under the previous plan, the plan would have marginally greater impacts on circulation, air qual- ity, energy consumption, and service systems. ALTERNAfIVE 4 -REDUCED SCOPE OF DEVELOPMENT The project site could also be developed at a reduced scope. Residential development could be limited to low/medium-density {0-4 du/ac) within areas designated for residential development in the proposed Master Pl an. This \'IOuld allow a maximum of only 1,717 dwelling units, which would be a reduction of 43% from the proposed Master Plan. Such a proposal within the existing design of the project would serve to reduce project-related traffic by about 6,000 trips daily, with subsequent marginal reductions in traffic-related air quality impacts and noise impacts. It would also require less energy consumption than the proposed project. In addition, it could {but not necessarily would) provide a less dense visual appearance and could allow for increased open space areas. 0 0 0 0 0 0 0 :o 0 0 102 lsa However, the reduced scope alternative would have almost identical impacts on landform alteration, given the variable topography and geologic constraints requiring extensive site preparation for any substantial urban development. It would most likely hav·e similar impacts on biological, archae- ological, and paleontological resources. It would require a drainage control program similar to that required for the proposed project. ALTERNATIVE 5 -PROJECT REDESIGN The project could be redesigned so as to totally restrict development from the central canyon bottom in order to avoid impacting the riparian habi- tat along the creekside. However, it is not felt that the existing riparian habitat is so superior that, given implementation of the proposed mitigation. measures, restriction of development in this area should be seriously consid- ered. Such a restriction would have substantial repercussions throughout the Master Plan and would probably necessitate redesign of the entire Master Plan and its concept. 0 0 0 0 0 0 0 0 0 0 103 SUMMARY OF ANY SIGNIFICANT UNAVOIDABLE ADVERSE IMPACTS WHICH CANNOT BE AVOIDED IF THE PROPOSAL IS IMPLEMENTED lsa This summary briefly lists those significant environmental effects which cannot be completely mitigated so as to be insignificant. Page numbers refer to the location of further discussion concerning the effect. 1. Significant, irreversible alteration of natural landforms (Page 18). 2. Cumulative impact associated with the incremental increase in urban pollutants (Page 25). 3. Destruction and/or displacement of most existing vegetation and wildlife onsite (Page 30). 4. Permanent change in the visual and physical character of the project site (Page 40). 5. The project, in combination with developing projects in the area, will increase traffic volumes along Palomar Airport Road, thus lowering the service level to an unacceptable level at Palomar Airport Road and Melrose Avenue (Pages 41-59). 6. The cumulative effect of project-related stationary source and mobile source emissions in combination with other regional growth and resulting pollutant emissions (Pages 59-66). 7. The-cumulative effect of project-related energy consumption in combination with the growing energy demands of the region {Page 67). 8. The cumulative effect of the loss of agriculturally viable lands in combination with additional losses of agricultural acreage in the North County area (Pages 89-99). • iO I I I 10 !O 0 0 0 0 0 0 0 104 lsa GROWTH-INDUCING IMPACTS Rancho Carrillo is in an area which has been experiencing a rapid rate of regional and local development. Population growth in the City of Carlsbad is expected to continue \'/e 11 through 1995. The deve 1 opment of Rancho Carri 11 o represents a continuation of growth that is both symptomatic and causa 1 to a population increase on regional and local scales. Implementation of the project would be growth-inducing in the form of a localized population increase. The increase in population will cause an increased demand for utilities and community services. Growth inducement will result in increased fire protection facilities and personnel, and increased police personnel. Development will induce the transit district to expand its services into the project area. The Tri-City Hospital District will be forced to expand again to accommodate increased service demands. Commercial and industrial land uses onsite will increase the local employment base. Depend- ing on the nature of this employment, an additional, though minor, influx of population may result. Increased commerce and industry will also· increase the demand for goods and support services. The development may have indirect growth-inducing effects on unincorpo- rated parcels to the west of the project site within the domain of San Diego County. This area is currently agricultural, consistent with the County of San Diego's and the City of Carlsbad's General Plans, but may experience pres- sure to develop as a result of the encroaching urban land uses of this and surrounding developments. In some cases, growth inducement has already occurred in anticipation of the project. The Palomar Airport Wastewater Reclamation Project is being designed to accommodate planned future developments, including Rancho Car- ri 110. Plans proposed in the Serra Cooperative Library System's Master Plan accommodate service areas of future deve 1 opment, including Rancho Carri 11 o. These actions evidence that Rancho Carrillo is part of planned growth. The proposed community is in response to and in compliance with current zoning (PC). The City of Carlsbad General Plan, Land Use Element designates the areas south and west of the project as planned communities, so these areas are expected to experience p 1 anned growth. The area east of the project is not within the Carlsbad city 1 imits and not subject to acti ans on the part of the City; the area north of the project is a Non-Residential Reserve and is not expected to be developed. 0 0 0 0 0 0 I 0 0 0 0 0 105 SIGNIFICANT IRREVERSIBLE ENVIRONMENTAL CHANGES WHICH WOULD BE INVOLVED IN THE PROPOSED ACTION SHOULD IT BE IMPLEMENTED lsa Construction of the proposed development is effectively an irreversible commitment of the entire Rancho Carrillo site to an urban use. Project imple- mentation would permanently modify existing physical features and displace all existing flora and fauna. The development would require irreversible consump- tion of non-renewable fossil fuels during construction and throughout its life span. The commitment of non-recyclable materials used for construction of the buildings is also irreversible. 0 0 0 0 0 ,0 I 0 0 0 0 0 ----------------- 106 THE RELATIONSHIP BETWEEN LOCAL SHORT-TERM USES OF MAN 1S ENVIRONMENT AND THE MAINTENANCE AND ENHANCEMENT OF LONG-TERM PRODUCTIVITY lsa Implementation of the project would completely eliminate existing .land uses onsite. Development would constitute a long-term commitment of the Rancho Carrillo site to specific land uses, precluding future opportunities for other uses, or a return to existing land uses on the site. Cumulative and long-term effects of the proposed project which adversely affect the state of the environment include a decrease in biotic resources, a decrease in natural topography, a decrease in natural open space, a decrease in local and regional air quality, an incremental increase in urban pollutants in runoff, and an increase in traffic in and around the site. Increased ener- gy consumption and the demand ·for public services and utilities would result in commitments to service the site. Commitments to urbanized land use would permanently preclude use of limited agricultural resources onsite, such as crop-compatible soils and other environmental conditions conducive to agricul- ture. Urban commitments may have long-term effects on surrounding land uses. Offsite agriculture and its associated dust, noise, and pesticide activities may prove incompatible to the project. Existence of the proposed development may have an indirect effect on future operations at Palomar Airport, depending on what those might be. The only immediate short-term benefit of the project would be construc- tion-related employment. Long-term benefits include the addition of dwelling units in the .housing market and possible employment opportunities associated with cormnercial and industrial land uses. Increased revenue to the City of Carlsbad will result from increased property tax and sales tax. 0 ' . 0 0 0 0 ,o 0 0 0 0 0 ------------. 107 lsa PREPARERS AND CONTRIBUTORS TO THE REPORT PREPARERS Larry Seeman Associates, Inc. CONTRIBUTORS Geotechnical studies Biology study Traffic study Noise study Noise study Agricultural studies William Foley Annette Sanchez Edward Almanza Ronald Douglas Dana Privitt Hans Giroux Geosoils, Inc. EDAW, Inc. F Weston Pringle & Associates Bioacoustical Engineering Corporation Vincent Mestre Associates, Inc. Copley International Corporation 0 0 0 0 0 0 I 0 0 0 0 0 108 lsa PERSONS AND ORGANIZATIONS CONSULTED A11en, Richard Traffic Engineer, City of Carlsbad, CA'; various meetings 1980-81. Austin, Stephanie Institutional Management Consultants, La Mesa, CA; telephone communica- tion 2/20/80. Basom, Wi11i:am Warden, Department of Fi sh and Game, San Di ego, CA; te 1 ephone communi ca- ti on 3/24/81. Bradstreet, David Superintendent of Parks and Recreation, City of Carlsbad; telephone com- munication 3/23/81. Bramlett, Dave Biologist, EGOS Management, Inc.; telephone communication 1/16/81. Burmaster, Mark Community Relations Director, North San Diego Hospital District, Escon- dido, CA; telephone communication 12/16/80. Card, Susan Ulibarri P1 anner, The Planning Center, Newport Beach, CA; persona 1 and telephone communication. Crosthwaite, Joyce Assistant Planner, City of Carlsbad; personal and telephone communication, correspondence. Duncanson, Douglas Superintendent, Department of Parks and Recreation, City of Carlsbad; tel- ephone communications 7/14/80, 12/22/80. Evans, Les Engineer, City of Carlsbad, CA; various meetings 1980-81. Fannon, William W. Consulting Engineer, Lowry & Associates, Carlsbad, CA; personal and tele- phone communication. 0 0 0 0 0 0 0 ,0 0 0 0 109 lsa Higgins, Lois Customer Extension Planner, San Diego Gas & Electric, North Coast District Office,.Carlsbad, CA; telephone corrununication 1/10/81. Indvik, Kathy Community Relations Director, Tri-City Hospital District, Oceanside, CA; telephone communication 12/16/80. Ladwig, Robert C. Vice-President, Rick Engineering Company, Carlsbad, CA; personal and tele- phone communication. Larson, David L. • Director of Business· and Operations, San Marcos Unified School District, San Marcos, CA; correspondence 5/10/80. Lichterman, Thomas Planner-Scheduler, Orange County Transit District; telephone communica- tion 12/16/80. Levens, James Project Manager, ECOS Management, Tustin, CA; telephone communication 1/15/80. Martin, Joan K. Director, Areawide Clearinghouse, San Diego Association of Governments (formerly CPO); correspondence 8/1/80. Mestre, Vincent Principal, Vincent Mestre & Associates, Newport Beach, CA; personal com- munication 1/6/81. Michael, Peter San Diego Regional Water Quality Control Board; telephone communication 7/14/80. Nelson, Steven G. Associate, EDAW, Inc., Newport Beach, CA; personal and telephone communi- cation 1/13/81. Quinn, Julia M. Environmental Management Specialist, Air Pollution Control District, County of San Diego, San Diego, CA; correspondence 6/22/80. 0 0 0 0 0 •O 0 0 0 0 110 lsa Ross a 11 , W. D. Captain, Police· Department, City of Carlsbad; telephone communication 7/14/80. Safford, Philip R. General Manager, Palomar Airport; Personal and written communications, 1980. Samodah 1, Rod San Diego County Flood Control District, San Diego, CA; telephone commun- ication 12/22/80. Sayers, John A. Engineering G~ologist, Geosoils, Inc., Santa Ana, CA; telephone communi- cation 1/8/81. Severson, Richard Assistant Airport Manager, Palomar Airport; personal and written communi- cations, 1981. Sims, Moe McDougal Sanitation, Inc., Carl·sbad, CA; telephone communication 12/16/80. Smikhal, William Administrator, Fallbrook Hospital, Fallbrook, CA; telephone communica- tion 12/16/80. Stracher, William City of Carlsbad traffic consultant, Berryman and Stephenson, Inc.; per- sonal and written conmunications 2/81. Templeton, Peter Principal, The Planning Center, Newport Beach, CA; personal and telephone communication. Tessier, Pat Associate Planner, City of Carlsbad; personal and telephone communica- tion·. Thompson , James Fire Chief, City of Carlsbad, CA; telephone communications 12/16/80 and 3/23/81. 0 0 0 0 0 0 0 0 0 0 0 111 lsa Warnberg, Marilyn Carlsbad Unified School District, Carlsbad, CA; telephone communication 3/9/81. Watson, Ron Engineer, Rick Engineering Company, Carlsbad, CA; numerous communica- tions. Zuercher, Don Corrmunity Relations Director, Scripps Memorial Hospital, Encinitas, CA; telephone conmunication 12/16/80. 0 0 0 0 0 0 0 0 0 0 0 112 lsa REFERENCES Bioacoustical Engineering Corporation, 1980. Evaluation of Exterior Noise Exposure and General Development Restrictions for the Rancho Carrillo Pro- tosed Residential Development in Carlsbad, California. Prepared. for Daon ·orporation, Newport Beach, CA. California Native Plant Society. 1980. Inventory of Rare and Endangered Vas- cular Plants of California. Special Publication No. 1 (Second Edition). California Solid Waste Management Board. 1974. Bulletin #2: Solid Waste Gen- eration Factors in California. Technical Information Series. Carlsbad, City of. 1974. City of Carlsbad General Plan, Land Use. Comprehensive Planning Organization of the San Diego Region. 1974. Comprehen- sive Land Use Plan: Palomar Airport. Comprehensive Planning Organization of the San Diego Region. 1980a. Final Series V Regional Development Forecasts. 1978-2000. Comprehensive Planning-Organization of the San Diego Region. 1980b. Water in the San Diego Region. - Daniel, Mann, Johnson & Mendenhall, and Lowry & Associates. 1978. Areawide Water Quality Management Plan. Prepared for Comprehensive Planning Organ- ization of the.San Diego Region, San Diego, CA. Geosoils, Inc. 1980a. Letter to Mike Ryan, Daon Corporation regarding removal of earth embankment and reservoir, Carrillo Ranch, Carlsbad, CA. Geosoils, Inc. 1980b. Reconnaissance Soils Engineering and Geologic Study, Carrillo Ranch, North of Palomar Airport Road, Carlsbad, CA. Prepared for Carrillo Ranch Partnership. Geosoils, Inc. 1980c. Seismicity Evaluation -Carrillo Ranch Area, Study Par- ee 1 s b, e, f, h-3. i-2, and j. City of Carlsbad, CA. Prepared for Daon Corporation, Newport Beach, CA. Geosoils, Inc. 1979a. Reconnaissance Soils Engineering and Geologic Study, Parcel d, Carrillo Ranch, Carlsbad, CA. Prepared for Don Woodward, New- port Beach, CA, and Active Capital Co., Los Angeles, CA. 0 0 0 0 0 0 ----------- 113 lsa Geosoils, Inc. 1979b. Reconnaissance Soils Engineering and Geologic Study, Parcels a and i-1, Carrillo Ranch. Carlsbad, CA. Prepared for the Woodward Companies, Newport Beach, CA, and the Meister Company, Inc., Newport Beach, CA. Geosoils, Inc. 1979c. Reconnaissance Soils Engineering and Geologic Study, Portion of Parcel g, Carrillo Ranch, Carlsbad, CA. Prepared for Sagewood Homes, Inc., .Irvine, CA. Geosoils, Inc. 1979d. Landslide and Development Feasibility Study, Parcels b, c, e, f, h-3, i-2, and j, Carrillo Ranch Area, City of Carlsbad, CA. Prepared for Daon Corporation, Newport Beach, CA. Geosoils, Inc. 1979e. Letter to Mike Ryan, Daon Corporation, regarding existing earth embankment and reservoir. Carrillo Ranch, Carlsbad, CA. Golz and Lillegraven. 1977. Surrmary of Known Occurrences of Terrestrial Vertebrates From Eocene Strata of Southern California. Contrib. to Geology, University of Wyoming, 15:43-65. Holt, Raymond M. 1978. Moving Ahead: Master Plan No. II for the Carlsbad City Library. Kubota, G. H., Morrison, and Pidd. 1980. A Study to Assess the Agricultural Viability of the Northern Section of Carrillo Ranch. Prepared for Daon Southwest, Newport Beach, CA. Kubota, G .. H., Morrison, and Clark. Viability af-.-Carri-llo R.anch. 1980. A Study to Assess the Agricultural Prepared for Carril lo Ranch Partnerships. 0 Leedshill. 1981. Rancho Carrillo Drainage Study. Prepared for Rick Engi- 0 0 0 neering~ Carlsbad, CA. Lowry & Associates. 1980. Report and Report Supplement for the Palomar Air- port Wastewater Reclamation Project, Carlsbad, CA. Prepared for The Koll Company, Newport Beach, CA. Mestre, Vincent Associates, 1981. Assessment of Palomar Airport Noise Con- tours. Prepared for Larry Seeman Associates, Inc., Newport Beach, CA. Montgomery, James M. 1975. Comprehensive Water Quality Control Plan for the San Diego Basin. Abstract prepared for California Water Quality Control Board, San Diego Region, San Diego, CA. 0 0 0 0 0 0 0 ' :o I 0 0 0 114 lsa Neste, Brudin & Stone, Inc. 1979. Draft Environmental· Impact Report for the San Marcos County Water District. RECON. 1976. Preliminary Environmental Information, Rancho Carrillo, Carls- bad, CA. WESTEC Services. 1979. Known Cultural Resources of Rancho· Carrillo, Carls- bad, CA. Weston Pringle and Associates. 1981. Traffic Engineering Report for Rancho Carrillo in the City of Carlsbad .. Prepared for Daon Southwest, Newport Beach, CA. Woodside, Kubota & Associates. 1974. Rancho Carrillo -Master Plan for Public ·Water System. Prepared for Carlsbad Municipal ~~ater District, Carlsbad, CA. 0 0 0 0 0 0 0 I lo I 0 0 0 115 REFERENCED MATERIALS ON FILE WITH THE CITY OF CARLSBAD lsa Bioacoustical Engineering Corporation, 1980. Evaluation of Exterior Noise Exposure and General Development Restrictions for the Rancho Carrillo Proposed Residential Development in Carlsbad, California. Prepared for Daon Corporation, Newport Beach, CA. Carlsbad, City of. 1974. City of Carlsbad General Plan, Land Use. Geosoils, Inc. 1980a. Letter to Mike Ryan, Daon Corporation regarding remov- al of earth embankment and reservoir, Carrillo Ranch, Carlsbad, CA. Geosoils, Inc. 1980b. Reconnaissance Soils Engineering and Geologic Study, Carrillo Ranch, North of Palomar Airport Road, Carlsbad, CA. Prepared for Carrillo Ranch Partnership. Geosoils, Inc. 1980c. Seismicity Evaluation -Carrillo Ranch Area, Study Parcels b, e, f, h-3. i-2, and j. City of Carlsbad, CA. Prepared for Daon Corporation, Newport Beach, CA. Geosoils, Inc. 1979a. Reconnaissance Soils Engineering and Geologic Study, Parcel d, Carrillo Ranch, Carlsbad, CA. Prepared for Don Woodward, New- port Beach, CA, and Active Capital Co., Los Angeles, CA. Geo soils, Inc. 1979b. Reconnaissance Parcels a and. i-1, Carrillo Ranch. ward Companies, Newport Beach, CA, Beach, CA. i Soils Engineering and Geologic Study, Carlsbad, CA. Prepared for the 1..Jood- and the Meister Company, Inc., Newport Geosoils, Inc. 1979c. Reconnaissance Soils Eng_ineering and Geologic Study, Portion of Parcel g, Carrillo Ranch, Carlsbad, CA. Prepared for Sagewood Homes, Inc., Irvine, CA. Geosoils, Inc. 1979d. Landslide and Development Feasibility Study, Parcels b, c, e, f, h-3, i-2, and j, Carrillo Ranch Area, City of Carlsbad, CA. Prepared for Daon Corporation, Newport Beach, CA. Geosoils, Inc. 1979e. Letter to Mike Ryan, Daon Corporation, regarding existing earth embankment and reservoir. Carrillo Ranch, Carlsbad, CA. Kubota, G. H., Morrison, and Pidd. 1980. A Study to Assess the Agricultural Viability of the Northern Section of Carrillo Ranch. Prepared .for Daon Southwest, Newport Beach, CA. 0 0 0 0 Kubota, G. H., MJrrison, and Clark. Viability of Carrillo Ranch. ' 116 lsa 1980. A Study to Assess the Agricultural Prepared for Carrillo Ranch Partnerships. Mestre, Vincent Associates, 1981. Assessment of Palomar Airport Noise Con- tour. Prepared for Larry Seeman Associates, Inc., Newport Beach, CA. RECON. 1976. Preliminary Environmental Information Rancho Carrillo, Carls- bad,CA. WESTEC Services. 1979. Known Cultural Resources of Rancho Carrillo, Carls- 0 bad,CA. 0 0 0 0 0 0 0 0 0 0 0 0 0 :o I 0 0 APPENDIX A HYDROLOGY STUDY lsa 0 0 DEVELOPMENTAL SERVICES :: Assistant City Manai;'!!r (71,, "38-:596 O Building 0ecartment (71,1 4.38-5525 CJ Engineering 0epartment (71,1 ~-5541 C Housing & Redeveiopment 0e;:iartment~ q,titp of Q!:arl.sbab 1200 ELM AVENUE CARLSBAD, CALIFORNIA 920C8 0 (71,1 "38-5611 0 0 0 0 0 0 0 □ Planning 0ei,artment (71,, .4J8.5591 March 1 0, 1981 Mr. Barry Bender Rick Engineering 3088 Pio Pico, Suite 202 Carlsbad, Ca 92008 RE: Rancho Carrillo Drainage Study I -have reviewed the Leeds,·HiJI, and Jewett study for Rancho Carrillo and find it adequate both in approach a·nd criteria. I have not. reviewed the caltulations for accuracy.nor attempted to verify any information presented in the Tabl~s and Fig~r~s. The design criteria are satisfactory, however, and the alternative plans seem reasonable. I have no objection to the report Consultant for use in-that study. drainage study does not represent or development and planning areas ---c· ·~':"::--2.-= -.---:· ;"":,;.,---~ ~---:: ~ Les Evans City Engineer LE/leg cc: Planning Director being forwarded to the Environmental However, my satisfaction with the the City's agreement to street alignments on which the drainage study is based. 1275 MARKET STREET SAN FRANCISCO, CAL.IFOFINIA 94103 TELEPHONE <•t~I 625-2070 Caci•: LEECSHILL March 3, 1981 Mr. Barry ·sender Rick Engineering Company 3088 Pio Pico Drive, Suite 202 Carlsbad, CA 92008 Reference: Job No. 7495 -Rancho Carrillo Dear Barry: Tnomas A Lat'; Ft Hun~ett. C!O Jonn A aiscr,ot• Ric~a•Cl M G,,man Tnomas C. MacOona,: James S. Jenks pr,,11g L.. Wa~n•" CONSULTING ENGINEERS 0 0 0 Responsive to your request of February 25, 1981, enclosed are twelve O ( 12) copies of LEEDSHILL' s report, nRancho Carrillo Drainage Study". As you requested, the reports have been _consecutively numbered (on title page) so that you can easily keep track of their distribution .. In the study it was assumed that runoff from areas· upstream of Rancho Carrillo would be controlled by others when the ._areas are developed. 0 In most drainage plans this would be a critical assumption, especially if there are no guarantees that upstream drainage controls. would be provided. However., at Rancho Carrillo i~. does not appear that up- stream controls are critical because the currently planned ·topo- graphies· at detention basin. sites 1 -and 2 are probably adequate to control unregulated runoff from both the upstream areas· and tributary 0 areas of Rancho Carrillo. The ability. of basin sites land 2 to accommodate unregulated runoff from upstream areas could easily be confirmed by a computer analysis if you desire. LEEDSHILL will maj_q.t-airr~'th--; -hydrologic computer model for the Rancho Carrillo development so ~hat.: it can be used in future studies that. may 0 be desired. The mode1;; .. would ·be useful in final design of a drainage control plan, sizing of·-·storm_ drains, and sizing of temporary facili- ties (risers) for use during the construction period. It has been a pleasure working with you and the Rancho Carrillo developers in preparation of this Drainage Study. LEEDSHILL would, of 0 course, be pleased to provide any additional services that may be needed to complete the development. Should you have any questions or need any additional analyses, repor~s, etc., please call. Very truly yours, T.C. MacDonald Princical Enaineer -.. Enclosur~s 0 C 0 0 0 0 0 0 0 0 0 0 0 RANCHO CARRILLO DRAINAGE STUDY Prepar1:d For Rick Engineering Company ,•. .. March 3, 19 81· LEEDS,· Hill AND JEWETT, INC • 1 2 7 5 M A A K E T ~ T A E E T SAN FRANCISCO, CA 94103 TELEPHONE i415) 626-2070 009 j:i ii I I. INTRODUCTION Background Authority Scope TABLE OF CONTENTS Drainage Control Criteria II. THE STUDY AREA ~xisting Land Use Conditions Future Land Use Conditions !II. METHOD OF APPROACH AND DESIGN CRITERIA Method of Approach Design Criteria IV. DRAINAGE CONTROL PLANS General Detention Basin Design Alternative Drainage Control Plans Performance of Alternative Plans Sediment Control During Construction V. CONCLUSION l l 2 3 4 5 7 9 16 17 19 20 24 25 i ·io ' l • ' ' i ! l I ] l "I I lo I ~ j 1 I l l ~ ~ ii I i 1 I I ii I I I 0 0 0 0 0 0 ·O 1Q l.o 0 I. INTRODUCTION Sackaround Rancho Garrillo is a Planned Community to be located within the City of Carlsbad in northern San Diego County. This development 0 will include single-and multi-family dwelling uni ts, commercial and industrial facilities, public areas, and open space. The ·community will occupy about 850 acres of land, most cif which is currently undeveloped. 0 0 0 0 Carrillo area .and The City of Carlsbad recognizes that development of Rancho may cause increases· in st·ormwater runoff to the downstream has identified a need to control these increases. Accord- ingly, the City has required that the developer prepare drainage plans for the control of stormwater runoff ·from·Rancho Carrillo. Authority On December 12 and 15, 1980, Rick Engin~ering Company, engineers for the Rancho Carrillo developers, autho~ized Leeds, Hill and Jewett, Inc. (LEEDSHiiL) to proce~d with preparation of alterna- tive drainage control plans for the Rancho Carrillo development. LEEDSHILL's.objectives in this work are: : j '' ; ! ; i .1 l • i I • I I II 11 ,! Ii 'I I ! j' .. ; ;!/ 'ii ,;1 'lj 11, ( l) to ~Eave lop criteria for the c1...,n trol of storm-.,, 0 0 ,0 I 0 water runoff _-that .. will be acceptable to the City of Carlsbad: (2) to dev~lop, for illustrative purposes, practicable alternative drainage control plans that can be used at Rancho Carrillo and that the developers can use to assess the impacts of drainage facilities on the proposed development: and 1 Scope ( 3) to prepare a report which describes the al terna- tive drainage plans and can be used to satisfy, requirements for issuance of development permits. in part, . City Although considerable planning for the Rancho Carrillo development has been completed, these plans do not provide for drai~- age control facilities because the need for such controls is a rela- tively recent requirement imposed by the City of Carlsbad. Thus, drainage studies presente_d in this report are of a preliminary nature· direct~d at establi~hing the feasibi~ity of alternative drainage control plans for the development. Approximately 150 acres of the Rancl')o Carrillo develqpment . are not included in these studies. These 15_0 acres are located at the southwest corner of the development and' ~re designated Planning Areas 0 0 0 0 0 A and B in the nRancho Carrillo Master Plan, City of Carlsbad" that · o was prepared by The-Planning Center. Outflows from this 150 acres are , ' separate from outflows from the remaining portion of· the development· and do not effect th-restilts of these studies. Several different methods can be used to ciontr61 increases in runoff that result !ram development of an area. The most effective method of control is .to-=-collect the runoff in 'detention basins and ----=:.:.:-:...:.. then release it ~~the downstre·am channel at a reduced rate that is controlled by the odiiet_;_~-works of the detention basin. These studies are limited to analyses of alternative numbers and s{zes of detention basins that can be placed throughout the study area for control of runoff. 2 0 0 0 0 0 0 --= --= .-~< .-=~ ;-:r. ~ 7 :~ ---\ ',, ... • . ---=----...:..,• __ • --· - U.EDS, HILi. .ANO JEWETT,INC. J~~inaae Control Criteria 1o A drainage control plan for Rancho Carrillo is needed to obtain _permits from the City of Carlsbad. The City currently has no official~ policy for.the ~ontrol·of drainage: however, discussiohs with Mr. Les Evans, Ci_ty Engineer for the City of Carlsbad, indicate 10 that the criteria for the control of runoff.requited by the California ) I Ccastal Commmission ~or development within the coastal zone would be ac=eptable criteria for developments within. the City of Carlsbad~ lo I The California Coastal Commission's policy for the controi of runoff requires that the peak rate of runoff from a storm that has a recurre_nce frequency of 10-years be no greater after development th-'.2n before development. The Commission does not require that runoff f-;:-om all areas that are develope_d be regulated. However, if runoff I I 0 -. =~om some portions _ of the develop~ent are not;. regulated, runoff from t~-= remaining areas m1:1st be over-regulated suc_h that the total o.utflow -· ::;::·.~m the development to the downstream channel m~ets the 10--year storm ~eak discharge criterion. These criteria have been adopted for the Rancho Carrillo studies. In previous studies the Coastal. Commission has required o that the performance of drain_age _ cont~ol plans be analyzed for a 25-year storm event, although no requirements have been imposed on the o- . . . performance. The perf?rmance of t~e alternative drainage control plans developed for ~ancho· Carrillo have been analyzed for a 25-year storm and are prese-nted in this report. -.. ...;. ... ··:-·-~, ... -. -- Detention ba-sins for the control of runoff should be protected against failure during major storm events to avoid damages o to downstream developments. The criterion tha~ de tent ion basins can safely pass runoff from a 100-year storm have been adopted for the Rancho Carrillo studies. 0 3 0 I I I ·i I r II. THE STUDY AREA The study area .of thi·s report is· about 1, 5 5 O acres in size. About 850 acres of the study area are outside ~he boundary of the Rancho Carrillo development but contribute runoff to the develop- 0 0 ment. The remaining 700 acres of the study area are within the Rancho 0 Carrillo development. The boundaries of the study area and that portion of the Rancho Carrillo development· that were ana·lyzed and are discussed in this report are shown on Figure 1. Existing Land Use ·Conditions. Data on existing land u~e conditions at the study area are available ·from u.s.· ·G~ologic~l 'survey_' t~pographic. ~ap.s and from large scale topographic maps prepared by Rick Engineering Company and The Planning • Center. Soil and ground cover data for the area are available from maps prepared ·by the County of San Diego. In addition to these sources of data, a field inspection of the .study area was made on Dec·ember 16, 1980 • and photographs of the existing land use conditions were taken. Most of the l,Sso· acre study area is in a nat~~al condition, undisturbed by man '-s activities. The terrain of the ~tudy ar.ea is rolling hills that h·ave fairly steep slopes. The area i,s ·drained by a brush-filled unnamed. s-~~ .. ~m ~hat flows through the study area from the northeast to the.72~.fOU~hwest. The stream· has a ·steep grad.ient and th.e channel is fairt~~.well incised through the study area. Natural -.~"T~.i!~_:_ vegetation in the area ~onsists of grasses and dense evergreen shrubs. Soils in the area are classified primarily· as • being in. hydrologic soils groups Band D that have respective infiltration rates of 0.15 to 0.30 inches per h6ur and a.a to a.OS.inches per hour. The major roads that traverse the study area are Palomar • I Airport Road, Linda Vista Drive, Encinitas Road and Rancho Santa Fe 4 0 0 0 0 0 0 0 0 0 \0 0 Ll!EDS, HIU. AHO .tl!Wl!!TT, INC. - Road. In addition to these, there are minor and dirt roads within the study area. A minor portion of the study area is currently developed for ' . .. residential use. There is a rnobil hqme park and some housing develop- ments located along the ridge at the northeast extreme of the. st;udy area outside the boundary of the Rancho Carrillo .development. Also, there are. some developments located along Ran~ho Santa Fe Road in the southeast portion of the study area. Approximately 230 acres within the study area are currently devoted to agricultural use. occupy these lands. Future Land Use Conditions Orchards, _vin_eyards and truck crops Data on future land use, grading., and storm drains within .the Rancho Carrillo development are available from the "Rancho 0 Carrillo Master Plan, City of Carls_bad," that was prepared by The Planning Center. In the Master ~lan, the development is divided into 22 planning areas based on type of development and density of resi- dential dwelling units. These planning areas are shown on Figure 2 0 an_d a statistical summary of the proposed developments within each planning area is presented in Table 1. There are no· • available plans for development of the area 0 east of Rancho Carrillo that is within the study area. Develop--~::~-;.: ment in this area is within the jurisdiction· of the County of San Diego. For these studies it was assumed that this area would be developed in accordance with the current County zoning which is 0 medium density residential. 0 5 PLANNING AREAS Residential A* B* C 0 J -K !, M N 0 p Q s Recreational E G Commercial R 0 V Industrial T Public .. H F I TOTAL TABLE RANCHO CARRILLO Gross· Acres' 100.0 so.a 74.S 32.0 53.8 -43' .·s 70.3 99.7 15.3 8,7 .s 30.3 17.0 52 .. l. Commercial 6.5 4.0 5.3 8.9 ·-·-20. 9 41.l 8.2 14.0 10.s 846.3 Not part of study area. 6 l DEVELOPMENT Total No. Residential Onits • Allowed·'bv Area 148 255 221 530 99 198 700 so 332 240 92· .133 ;.. ... Gross DO/AC· ' - 2.91 3.42 '6. 90 9.85 2.27 2.81: 7.00 3.26 3.80 7.90 5.40 2.55 - ·- llo 0 0 b ' 0 'o .0 i'o I ,,o ! 10 iO I I - 0 0 ,0 I I I lo lo I I ;o lo ,0 0 0 0 -=-=~~· C:~0~:!~~ ~ --~,\,,..,tr,,: . -=-=-=:..:..· ~ '-' .. -...;:1..= LEEDS, HILL AND JIIW2TT, INC. IrI. METHOD OF APPROACH AND DESIGN CRITERIA Method of Accroach Preparation of effective drainage control plans for the Rancho Carrillo area requires determination of stormwater runoff characteristics for existing and future land use conditions. Esti- mates of peak runoff under existing conditions are needed to know the ievel of regulation that will be required .. Estimates of runoff under future developed conditions are nee9ed to size detention basin facilities. Stormwater runoff characteristics for drainage areas within the study area were simulated using the Corps of Engineer's computer rrogram HEC-1. This program estimates the amount and rate of runoff- ?.: :?sed on the drainag_e a~~a size, land use, types of soils, and the intensity of precipitation. The characteristics of drainage areas . within the study area were estimated from . soil, ground cover, . and topographic maps, photog~aphs of the area, and information learned during field inspections. Precipitation intensities were obtained from San Diego County. The HEC-l computer program was used to analyze stormwater r-unoff because it is capable of handling very short precipitation intensity durations. Because the drainage areas 5-elected for analysis are small, and therefo·r·e,''-·have short -times of concentration, a method of analysis that use~ even smaller time intervals in the hydrograph -~~--' calculation. is necessary to accurately estimate peak discharges. A time interval of two minutes was used to calculate the hydrographs from all drainage areas in the Rancho Carrillo.studies. The synthetic unit hydrograph type used in the analyses was the SCS triangular unit hydrograph with curvilinea,; transformation. In general, this synthetic unit hydrograph has been found to give the 7 ~ f f l i I I i ' ! :::est estimate of measured unit hydrographs • for small drainage areas s~ch as. those used for the Rancho Carrillo studies. using a Lag times for each of the drainage areas were calculated modified Corps of Engineers equation: • Tp = 24n [LxLca] 0 •38 x (~86) - s0~S D/2 w:".ere, !P is the lag time in hours, y n is the mean roughness coeff i- c~ent in Manning's Equation, Lis the length of stream path in miles !::~tween the outlet and the most remote point of the drainage area, Lea is • the length along the stream path in miles between the outlet a~d the centroid of the drainage area, 5 is the weighted slope in feet pe::-mile, and D is the time interval used in calculating the unit h~drographs. The D/2 and 0.86 factors in the above equation convert the Corps' definition of lag time to that used by the SCS. Topo- g:-aphic maps of the study area and information learned · during the f i•~ld inspection were used to estimate parameters in the equation for lag time.,- SCS curve numbers were used to estimate--precipitatioff losses in the HEC-1 computer program analyses. Estimates of precipi- tation losses· using SCS curve numbers are based on soil type, the type of vegetation on th~ land surface, the portion of the drainage area that is covered by vegetation, and antecedent moisture coridi tions. Estimates of soil type and vegetation type and cover were made using \ . County soil and· ··g:rau_nd cover· maps, photographs, and information learned during field inspection of the studi area. Antecede~t moisture conditions that are recommended by the County of San Diego were used in the Rancho Carrillo studies. Regional precipitation-fr~quency rel~tionships from the County of San Diego publication,. "Hydrology Manual", were used in the 8 0 0 i 6 . I I I i b b () 0 0 0 0 0 I Pl I t pJ i l C ol-1 .r. t of I 6' t. ~ ti Ot an:ilyses. Precipitation for various durations for the 10-, 25-, a~d 100-year return peri6d 6-hour storm~ are presented in the follow- :.-:-.-~ tabulation. Precioitation, inches Duration 10..;Year 25-Year 100-Year Minutes Storm Storm Storm 2 0.09 0.11 0.13 4 0.17 0.21 0.26 6 0.25 0.30 0.37 8 0.32 0.38 0.48 10 0.38 0.45 0.56 20 ·0.59-0.71 0.89 30 0.74 0.89 1.11 60" 0.97 1.17 1.46 120 1.28 1.54 1.92 180 1.51 1.81 2.26 240. 1.69" 2.03 2.54 300 1.85 2.22 2.78 360 2.00 2.40 3.00 ,~ ~ C~;.1n Crite~ia i J> Hydrologic analyses of the study area for existing _and t I Q I f..:-: :..-e land use conditions were maqe to develop design c.riteria for t~~ alternative drainage control plans. Runoff characteristics fer a 10-year storm for existing land use conditions were estimated to ce-:~·::-::iine peak runoff rates that would Qe allowed after development. R•.::-:-:. ffs from a 25-year storm for existing conditions were al so esti- ~a~ed to assess the performance of alternative drainage control plans ur.c::r this less fregue~t·· .storm. · Runoffs from 10-and 25-year storms !or fut~re land use conditions, assuming no detention basins are -~ ' ~.: -.- i ~s: 3 l led, were analised to provide estimates ~f peak rates and Volumes of runoff for sizing of detention basin facilities. To estimate runoff characteristics for ex is ting land use conditions, the study area was divided into the five subareas shown on Figure· 3. Hydrologic characteristics of each subarea were estimated 9 - using the data and methodology previously described. These charac- teristics are summarized in Table 2. For the estimates of runoff under existing land used conditions the small areas with in the study area that are now developed for res id en tial use were assumed to be undeveloped. The hydrologic characteristics presented in Table 2 and precipitation intensities fo1: the 10-and 25-year storms were used 'vith the HEC-1 computer program to calculate outflows from the five subareas under existing land use conditions. Outflows from ~ubareas I and II were routed downstream and combined with the runoff from the intervening Subarea III to calculate outflows from Subarea III. Separate outflows were calculated for Subareas IV and V. Peak rates and volumes of outflows from the five subareas are summarized in Table 3. To estimate runoff characteristics for future land. use conditions, the study are~ was divided into the 21 subareas shown on Figu~e, 4 and 5. These subareas were ·selec~ed to provide flexibility in developing and analyzing alternative drainage.control plans and are based on proposed land use, grad!°ng,· and 's.torm drain pians. The subareas have been numbered to roughly correspond to the subareas that were analyzed for existing land use conditions. Rydrologic. characteristics of each of the 21 subareas were estimated -for the pl~nned or zoned future l~nd use. In estimat- ing these character.istics overland flow, gutter flow, and flow in storm drains were considered. The estimated hydrologic characteris- tics of the 21 subareas are summarized in Table 4. The hydrologic characteristics presented in Table 4 and P.rec-:ipi tat ion intensities for the 10-and 25-year storms were used With the HEC-1 computer program to calculate runoff characteristics 10 i I lo 0 0 i i 'o I I I I I I ,0 ,Q I I i ' ' I: I , I) ' I ,o /-1 ! ; I. ! ' I 1 • '10 tO 0 0 0 0 0 0 0 0 0 0 0 for future land use conditions. These calculations assumed no drain- age controls are provided. Runoff from upstream subareas were routed downstream and combined with runqff from downs~ream subareas to determine total runoff at key locations within the development and at the outlets from the study area. Peak rates and volumes of outflows from each subarea and combinations of subareas are presented in Table 5. . ··-.. --....;.. ·-- · -•·.·-. ll ..... N 0 TABLE 2 HYDROLOGIC CHARACTERISTICS FOR EXI~TING LAND USE CONDITIONS Mean Lag Percent A.rea 1· Slope Time ]/ ,: Rou.9.hness Area Subarea (acres) (ft/mi.) n l/ (hours) Developed l: / I 512 166 .08 .56 12 II 270 393 .06 .30 0 III 571 45 .05 .44 15 IV V 68 98 .12 .43 14 65 478 .12 .28 65 Mean Manning's Roughness Coefficient. Time between the beginning of excess rainfall and t~e centroid of runoff. Developed for agricultural use. Curve number for antecdent moisture condition (AMC)= 2.0 based on estimates of existing soil 'and cover conditions. (') 0 0 0 0 0 scs 11 Curvf No. _I 81 73 82 · 86 86 0 0 0 0 .... w 0 0 0 0 0 0 0 TABLE 3 . . ·, PEAK DISCHARGE RATES AND RUNOFF VOLUMES AT SUBAREA OUTLETS FOR EXIaTING LAND USE CONDITIONS ii'':,! .1 :,}0-Year Storm 25-Year Storm Pea{c1 Ra·~~ Volume Peak Rate Volume Subarea ,,,ifs) ,;· ( acre""'.feet) (cfs) ( acr·e-feet) I I 106 22.3 171 32.9 II 24 6.0 50 9.9 III 262 !/ 56.9 !/ 423 1/ 84.4 IV 30 4.7 44 6.5 V 30 4.0 44 5.5 !/ Includes unregulated outflows from Subar~as I and II rout~d to the outlet of Subarea III. 1/ 0 ...... ,14 0 'l'ABU: 4 HYDROLOGIC Cll~RACTERISTICS FOR FUTURE LAND USE CONDITIONS Lag Percent Subarea Area (acres) Mean S.lope (ft/mi.) Rou9.hness . 2/ n - Time ll (hours) Area Developed!/ I 554 154 339 .58 2?5 0.015 0.015 0.035 0.030 0.020 0.025 0~025 0.030 0.100 0.045 0.035 0.020 0.050 0;040 0.09 0.06 0.21 0.11 0.05 0.05 0.05 0.08 100 100 68' 76 42 !/ 2/ 3/ 4/ ~/ II Illa Illb Ille Illd Ille Illf lllg Illh Illi IIIj Illk 1111 Illm Illn Illo Illp IVa IVb V 281 74.8 87.8 12.2 57.9 40.3 41.9 34.8 10.7 45.9.!/ 27.5 23.5 19.8 16.3 28.5 44.5 14.5 62.9 5.6 56.7 94 339 . 203 125 606 51 442 130 140 152 152 138 296 110 53 181 70 .0.060 0.025 0.025 0.020 0.040 0.Q.70 0. 0·25 ·o .21 0.17 0.04 0.06 0.09 0.09 0.19 0.07 0.10 0.04 0.09 0.09. 0.10 100 100 100 0 59 100 90 0 100 62 100 77 72 95 95 100 Includes 14.9 acres outside Rancho Carrillo that were assumed to drain into the development. 0 Manning's mean roughness coefficient. Time bet~een the beginning of excess rainfall ~nd _the centroid of runoff. . •, . / Areas not developed are open space or landscap~d aieas. Curve number for antecdent moisture condition (AMC)= 2.0 based on estimates of existing soil and cover conditions. 0 0 0 0 0 0 scs Curv§; No. - 82 83 87 85 88 90 91 89 84 86 89 90 78 79 80 89 88 84 92 92 89 0 I I I lo ' TABLE 5 PEAK DISCHARGE RATES AND RUNOFF VOLUMES AT SUBAREA p OUTLETS FOR FUTURE LAND USE CONDITIONS WITHOUT DRAINAGE CONTROLS 10-Year Storm 25-Year Storm Peak Rate Volume· Peak Rate Volume 0 Subarea (cfs) .(acre-feet) ( cf s) • ·.<acre-feet) I 484. 42;.0 692 56.9 II 158 15.2 251 21.7 0 IIIa 49 5.1 72 7.1 I+IIIa 533 47.1 765 64. 0 IIIb 60 • 5 ~4 91 7.5 II+IIIb 217 20.6. 342 29.3 IIIc 12 0.9 .17 1.2 IIId 67 4.9 93 6.6 0 IIIe 51 3.6 69 • 4. 8 IIId+e 111· 8.6 161 ll.4 IIIf ·34 2.7 48 3.8 IIIg 19 2.4 29 3·~ 4 IIIh 7 0.7 . 10 1.0 IIIf-h 55 5.9 81 8.2 0 IIIi .. 49 .3.6 69 4.8 IIIj 31 2.3 43 3.l IIIi+j 80 5.9 lll 7.9 IIIk 6 0.8 ll l.2 IIIi-k 82 6.8 120 9 .. 2 0 IIIl 6 a.a 10 l.l IIIm 15 0.9 19 1.3 I+II+IIIa-m l,000 86.l .1, 461 118.5 IIIn 26 2.2 38 2.9 IIIo 40 ·-.;.---, .. , ·-3.3 58 4.5 IIIn+o 65.. ... , 5.5 92 7 .-4 _ ... •4: 0 IIIp ·~10. 0.9 15 1.2 ---·•· ~.;, ::-...-• -. I+II+III 1,070 92.5 1,561 127.2 IVa 7 0.6 9 0.7 IVb 79 6.1 -105 a.a 0 IVa+b ·86 6.7 114 8.7 V 55 4.7 78 6.4 0 15 0 - I I I I I ! I i' l ! IV. DRAINAGE CONTROL. PLANS General Two alternative plans for the co~trol of. stormwater runoff from the Rancho Carrillo study area are presented in this section. These two plans were developed to illu.strate t~at. stormwa ter . runoff can be coritrolled by use ~f detention basins and t6_provide guidelines to the developers in their future planning for in~orporating drainage facilities in the development. The two alternative plans that were analyzed can effectively control stormwater runoff from Rancho Carrillo with minimum impacts on the current.plans for grading, storm drains, and land use. These two plans are· by no means the only altern~tives for th~ control of r~noff' --several other alternatives that were not analyze~ can also control runoff. Some of these oiher alternatives are des6ribed in Section V of this report. The effectiven~ss of a det~ntion basin in controlling runoff is dependent on the volume of the ba~in, the characteristics of its.· outlet works, and, to a lesser degree, the shape of the basin. In modifying the development· plans to accommodate detention basins, basin Shapes can be different;· within limits, from those assumed in these . . . stud~es without significantly changing the results of these studies. The total storage· volumes of detention basins calculated in th_~_se studies should be the primary criterion used in future planning. The drainage control criteria adopted for these-studies assumed that runoff from areas east of Rancho ·carrillo would be regulated when they are developed .. • It was also assumed that the level of regulation that would be required for these areas would be the same as that . imposed by the City of Carlsbad. To develop alter- native drainage control plans for Rancho Carrillo it was assumed that 16 _..,_ 0 0 0 0 0 0 0 0 0 C I i 0 0 0 0 0 0 0 inflows into the development from Subareas I and II, shown on Figure_ 4, wi:>uld be regulated. by two detention basins, one at each of the outlets from the two subareas. Alternative methods to control runoff from these two areas were not studied. . . • Current grading and' storm drain pla~s provide_ three outlets ' . from the development for stormwater runoff. 0n_e of these outlets drains Subareas I, II, and III whereas the other two outlets drain -J •• Subareas IV and V, respectively. Subareas IV and_ V are both rela- tively small areas of. the' deve-_lopment and, therefore, it is not practical to consider alternative.numbers or sizes of detention basins to cont·rol runoff from these subareas. In these analyses, one deten- tion basin is provided in each of Subareas IV and V and the charac- teristics of these basiris are the •~me in both of the two alternative plans.- In both of the alternative plans, runoff from Subarea IVb was not regulated. The increase in runoff that results from develop- ment of this subarea is compensated_ for by ove_r regulation of runoff from Subarea IVa such that· the combi~ed peak -~utfl~w du_ring a io-year storm from the. subarea 'is no greater after d~velopment than before development. Detention Basin Design There are ~.9me:~areas wi thi~ the Rancho Carrillo development 0 where the_ currently-·-p1~i:ined topograp_hy is· idealy ~uited for use as detention basins. Stage<'-..:.storage relationships· for the -basins proposed A • • • • • 0 0 0 at these sites were estimated from t~e topographic-data presented on the grading plans. Detention basins. are also proposed for location_s within Rancho-~arrillo .wher~ current grading plans must be mod~fied to accommodate the detention_ basins._ Detention basins .at these locations 17 were assumed to have, ·in general, a· rectangular shape· •with. a floor . . ..... . length to width ra·tio of two' and with bank slope_s of two horizontal to -~ ' ' one vertical. Two types of emergency spillways were assumed for detention basins in the Rancho Carrillo development. When~ver possible or needed, a trapezoidal shaped. overflow spillw.ay with three horizontal to two vertical side slopes ·was assumed because thi~ type of _spillway is easy and in~xpensive to con~truci. This type of spillway was assumed for basins that requfre a large spillway capacity and where ' ' '' -' developments ··downstream of the basin allow. outflows to discharge into. a surface channer. Planned • developments ·downstream· from some-of the proposed detention basins r~~ui;e ·th~t spiilway outflows be contained iq storm drains. For these detention basins a riser type of spillway was assumed. Flow~ entering the riser are conv~y~d in a pipeline through the basin embankment and into the downstream storm drains. Two· different-designs of detention basin outlet wo,rks were used 'in .the studies. For those. basins that wer-~ a~sumed to_ have an overflow type emergency spillway, the outlet works • were assumed to consist of a pipeline that c.onnects the basin floor with the down- strea~ toe of the embankment. Stage-discharge rating curve~ were developed for these.·. ·outle_ts assuming the outlet pipe is 120 f~et • 'in length, .has ,a 2.5 percent slope,-and has roughnes·s coefficients of 0.024 when corregated-metal pipe {CMP) is:·used and;0.01'2 when ·rein- forced concrete pipe ( RCPY is ·used.. RC·P was • assumed when the· outlet pipe has a large diameter and/or• large depth·of·cover. For detention basins that were assumed to have a riser type of emergency: spillway, the ·outlet works w•te -~isu~~d to cbnsist of an orifice, at the base of the spillway ·riser that discharges ·into the spillway:outlet pipe. The orifice equ-tion was used.to caltulate stage-discharge relationships for these outlets. 18 0 0 0 0 0 b 0 0 C C C 0 0 0 0 0 0 n re r-= ~ ((P :: r: r: r, :7 ii jlCI ;;:•,l,~'\'"l•j1•! 11 ~:-c~L-LiC:vi Lf~ :J :.lcL.:c LEEDS, HIU. AND .ll!Wl!TT, INC. Alternative Drainage Control Plans The two alternative drainage control plans that were developed for Rancho Carrillo are designated as Plans A and B. Plan A utilizes a m~nimum number of relatively large detention basins to meet the study criteria. In Plan B basins are provided at the same locations as in Plan A but two additional detention basins are added in order to reduce the required size of the main basin at the outlet of the development. · These alternative plans are described in more· detail in the following paragraphs. The l9cations of all detention basins considered in the alternative plans are shown on Figure S. Plan A Alternative Plan A -utilizes three detentio_n basins to control runoff from Rancho Carrillo. The three basins would be located at sites 3, 4, and 5 that are show·n on Figure 5. These three basins are in addi tic;,n to the two basins ·that· were assumed would be provided by others in Subareas I and II to·control· runoff from areas east of Rancho Carrillo. In this plan, runoff from all of Subareas I,. II, and 0 -III would pass through the basin at site 3. Outflows from Subareas I and II would be regulated by the two basins outside the development before being routed through the basin at site 3. The basins at sites 4 and 5 would regulate --~,utf;J.ows · ~rom Subareas IV and V, respectively. 0 0 0 0 ·-::-·::. .. . ....,... Ch_aracteris0£-'i:-cs .. of the three detention basins proposed for Plan A are presented in Table 6. Also presented in Table 6 .are the assumed characteristics of the detention basins used to control runoff from Subareas I and II. 19 0 Plan B Alternative Plan B utilizes five detention basins to control o runoff from the Rancho Carrillo development, one at each of the sites shown on Figure 5. As with Plan A, these five basins are in addition to the two basins that were assumed would be provided by others to control runoff from Subareas I and II. O In this plan, runoffs from Subareas I and II would first be regulated by the two basins outside of Rancho Carrillo. They would then flow into the basins at sites 1 and 2 along with the unregulated O runoff ·from Subareas· IIIa and IIIb. Regulated outflows from the basins at sites 1 and 2 would then combine with unregulated runoff from the remaining portion of Subarea III and flow into the basin at site 3. The b_asins at sites 4 and 5 that regulate outflows from Subareas IV O and v, respectively, are the same as those proposed iri Plan A. Characte-r-istics of the five detention bas ins proposed for Plan Bare presented in Table 7~ O Performance of Alternative Plans The detention basin chara~teristics presented in Tables 6 and 7, the hydrologic characteristics of the subareas presented in , Table 4, and precipitation intensities of the 10-, 25-, and 100-year storms were used ~it~ the HEC-l computer program to calcuiate runoff characteristics that would occur under future land use condi.tions for· the two al terriative drainage control plans. Peak rates of runoff at key locations within the development for the 10-and 25-year storms were • calculated and are presented in Table 8. For comparison pur- poses, peak discharges that would occur at the same locations under existing and fu.ture land use conditions without detention basins are also presented. Maximum water storage characteristics of the basins- during the 100-year flood are also presented in Table 8. 20 C C C C C 0 N I-' 0 0 Basin Detention Basin Site Shape Subarea I (off site) Rectangular Subarea II (off site) Rectangular 3· Rectangular 4 Rect·angular 5 Rectangular 0 0 0 0 TABLE 6 DETENTION BASIN CHARACTERISTICS FOR ALTERNATIVE PLAN A Outlet Characteristics Characteristics ~ I. ! ' ::iPlQor Embankment o'fmeruiions Height Size _._.· <feet> (feet) ~ (Inches) ! ' ~4 ,. ,,. 150x300 20.S CMP 36 100x200 19.0 CMP 18 120x240 21.s RCP 54 6Sxl30 10.5 CMP 24 S0xlO0 9.5 CMP 24 !/ Base width is given for overflow spillways. 0 0 0 0 Emergency Spillway Characteristics Feet Above Outlet ~ Sizel/ Invert -- Overflow 10' 14~5 1~ -·-· ·- Overflow 10' 15.0 Overflow 10' 13.0 . .t :? Overflow 10' o.o Overflow 10' 7.0 tJ tJ 0 ·Basin Detention Basin Site Shape Subarea r (off site) Rectangular Subarea II (off site) Rectangular 1· Existing 2. Existing 3 Existing l/ 4 Rectangular 5 Rectangular TABLE 7 DETENTION BASIN CHARACTERISTICS FOR ALTERNATIVE PLAN B ,, . . , Outlet ·, Ch~racteristics Characteristics " F.look Embankment Dimensions Height Size (feet) (feet) ~ (Inches) 150x300 20.5 : . CMP 36 100x200 19.0 CMP 18 70.0 Orifice 30 35.0 Orifice ·18 21.0 RCP 54 65xl30 10.5 CMP 24 50xl00 9.5 CMP 24 1/ Some regrading required. 1/ Base witdh of overflow spillways and diameter of circular riser spillways. 0 0 0 0 0 0 Emergency Spillway Characteristics Feet Above Outlet ~ Sizel/ Invert Overflow 10' 14.5 Overflow 10' 15.0 Riser 60" 18.0 Riser 54 II 20.0 Overflow 25' 17.0 Overflow 10' 8.0 Overflow 10' 7.0 0 0 0 0 0 tJ w 0 0 0 0 0 TADLF. 8 RUNOFF CIIARACTERISTS FOR FIITIJRR l,AND USE CONDITIONS ALTERNATIVE PLANS A and B 10-Year Storm 25-Year Storm Peak outflow Peak Outflow 0 0 0 100-Year Storm cfs cfs Maximum Water Storage Characteristics -Water Existing Future Future Existing Future Future Water Surface Lancl Without With Land without With Depth Freeboard Storage Area Location Use Basins Basins Use Basins Basins· (feet) (feet) (acre-feet) (acres) Suharea 111 106 484 ;~ I :: . : 93 171 692 165 20.0 0.5 29.9 2.01 I. ,., Subarea u!I 24 158 '·i. .. 19 50 251 45 18.4 0.6 13.9 1.09 I,. , .. • I I·, Plan A: 1.· ·•' Basin Site 3 262 1,010Y t~43!/ 423 l,56ly 4051/ 20.7 0.8 21.9 1. 50 Basin Site 4 30 86 30 '44 114 42 9.8 0.7 2.9 o. 40 Basin Site 5 30 55 26 ~5 78 46 8.8 0.1 1.6 0.26 Plan B: Basin Site l 533 90 765 112 22.4 47.6 24.l 2. 73 Basin Site 2 217 29 342 38 22.9 12.l· 10.3 1. 20 Basin Site 3 262 1,010Y 262:!/ 423 1,561~/ 351!/ 20.4 0.6 10.7 0.98 Basin Site 4 30 86 30 44 114 42 9.8 0.7 2.9 0.40 Basin Site 5 30 55 26 45 78 46 8.8 0.7 1.6 0.26 --------------------------!/ Outside of Rancho Carrillo y Assumes Subareas I and II are developed but outflows are not regulated. 1/ Assumes Inflows into Rancho Carrillo are regulated by basins in Subareas I and II. ·I Sediment Control Durino Construction During construction of Rancho Carrillo, grading operations will remove existing vegetation and disturb land surfaces which could cause temporary increases in sediment runoff to downstream areas. Protection of land surfaces during the construct.ion period could be provided by revegeta tion, berms, and other on-site controls whi~h could substantially reduce sediment runoff during this critical period and is the most desirable method of sediment control. However, it may not be possible to protect all areas or the protection used may not be 100 percent effective at all times. In these cases, it is necessary to provide additional sediment control devices that act as backup protection against sedimentation problems. The detention basins proposed in the alternative drainage control plans could be used during the construction period as backup controls for sediment runoff. The outlets of the basins could be fitted with temporary risers such that the· basins act as desilting and detent~on basins during· the construction period. The City of Carlsbad has developed a standard design for ·desil tation basin 01,1tlets which would be appropriate for the· temporary risers. After construction is complete and new vegetation is well established sediment runoff would be minimal and the tempo~ary risers could be removed. The basin could then be operated for the single purpose of stormwater detention. 24 0 0 b 0 i 0 I I lo 0 0 C C 0 0 0 0 0 0 '0 • 0 0 0 0 0 : '~ ~; -": ~ ~~ ~ ~ ;~ ... c: :..C i..C ~· '-2,· __; _; -_,c L..= U.E0S, HILi. AHO JEWl!TT, INC. V. CONCLUSIONS The two alternative plans that were analyzed meet the drainage control criteria that were adopted fer the studies. The data in Table 8 show that for both plans the 1O-year storm peak discharges to downstream areas after development would be equal to or less than undez:: existing land use conditions and that· the proposed detention basins for both plans can safely pass runoff from a 1OO-year storm. The performance of the two'. plans during a 25-year storm is also g_iven in Table a·. In evaluating the relative merits of the two alternative drainage control plans, one con~ideration should be the total area of land that must be dedicated to drainage facilities. The maximum surface area of water that is ponded in the basins during a 1OO-year storm is a measure of the amount of land that must be dedicated and is· given in Table 8. In comparing Plans A and B, the water surface areas at basin sites 1 and • 2 should not be considered because these areas are not intended to be developed and the only access to these areas would be for maintenance equipment should they be used as detention basins. Thus, Plan B would require dedication of less usuable area and, thereby, have less impacts on the. development .. Impacts on -storm drain plans should be considered in· evaluating the two drain~_g,!a. __ . control plans.· With 'Plan B, peak dis- charges in the storm drains along Melrose Avenue and Carrillo Way would be less because~£l-ows. in these storm drains would be regulated . ' by the basins at sites land 2. Thus, the required discharge capacity and size of these storm drains w·ould be less~ thereby making costs of the development less for Plan B. Detention basins should be installed before construction begins in the tributary areas and, therefore, phasing· of the develop- ment should be c;:onsidered in evaluating the alternative plans. 25 . . Of the two alternative plans, Plan B provides the greatest amount of flexibility because areas east of Melrose Avenue can be developed without having to construct the detention basin at site 3. Likewise, Subareas IV and V can be developed independent of other areas in Rancho Carrillo. Providing independent detention basins for different areas of the project ~ill allow "last minute" changes in developme~t and drainage control plans for each area. From the results of the analyses presented above, it is concluded that several other alternative plans for the control of a 0 0 runoff from Rancho Carrillo by use of detention basins are possible. 0 A few of these other possible alternatives are briefly described in the follow~ng paragraphs. Alternative Plan A controls runoffs from Subareas I, II, 0 and III with ·one fairly large basin at site 3. In Plan _B, runoffs from these Subareas are.only partially regulated by a basin at site 3, the remaining needed regulation being provided by additional basins at . . sites l a_nd 2.. By providing the additional basins at sites l and 2, 0 the size of the basin required at site 3 is substantially_ reduced. Other basins, in lieu of or in addition to those at sites 1 and 2, could be added to the system to reduce the needed size of the basin at site 3. If enough additional basins are provided the basin at site 3 0 could be eliminated. However, this "pocket basin" approach would prob.ably result _in_,_=i-ncrea.sed -maintenance costs. If tffe-=-g.):'.ading and/or_ storm drain routes used in this study are changed, this could provide other possible alternative drainage control plans. For example, in alternative Plan B a detention basin is needed at site 3 to reduce increases in .runoff that result from development of that portion of Subarea III that is west of Melrose 0 -Avenue. In addition, the basin at site 3 must also accommodate flow that is already regulated by basins at sites l and 2.. If, by rerouting storm drains, • the regulat_ed outflows from the basins at 26 0 0 0 0 0 0 0 0 0 0 0 IQ 0 sites 1 and 2 could bypass the basin at site 3 then the needed size of this downstream basin would be reduced. There are alternative designs for the facilities proposed in Plans A and B. As already mentioned, basin shapes can be changed, within limits, without changing the results of these analyses. Even if ba~in sh-pes are _substantially modified, the outlet works can be redesigned to provide equivalent regulation of runoff. Emergency spillways proposed in Plans A and B can be modified as long as they do not effect outflows during a 10-year storm. For example, in Plan B the basin at site 3 has a 21-foot high ·embankment and a 25-foot wide spillway. . If, for some r~ason, a narrower spillway is desired this I can be done.by increasing the embankment height. 27 FIGURE I C _, ----:' --_.,,... ... . _., C C C i2· -~- C C C C 0 N RANCHO CARILLO DRAINAGE STUDY SCALE: 111 = 20001 0 STUDY AREA Leeds, Hill and Jewett, Inc. Jen. 1981 0 C C I C C C 0 0 0 LEGEND CARILLO WAY , ~-----------~- ! . I I I -I I I I I l N NO SCALE I I I I I I I r 0 .-d -~ . . -.·' - k, -·. ·, ~ ~l -_ ~- J FIGURE 2 -------------~---------------~------ RANCHO CARILLO DRAINAGE STUDY RANCHO CARILLO DEVELOPMENT AND PLANNING AREAS .. Leeds, Hill and Jewett, Inc. Jan. 1981 N SCALE: 111 = 20001 FIGURE 3 RANCHO CARILLO DRAINAGE STUDY SUBAREAS-'EX I STING LAND USE Leeds,Hill and Jewett, Inc. Jon. 1981 C C C C C 0 0 0 0 0 0 0 0 0 0 0 0 G I I :o I io 0 I ... \ J \) . I I i/ .• • I ·.l' . '7 ., ' 0 ·- N SCALE: I"= 2000' FIGURE 4 RANCHO CARILLO DRAINAGE STUDY SUBAREAS-FUTURE LANO USE Leeds,Hill and Jewett, Inc. Jon. 1981 -- PALOMAR AIRPORT ROAD • i :N NO SCALE LEGEND £ Detention Basin Site filn Subarea Designation -Subarea Boundary III n FIGURE 5 :::----j I I I I I I I • • I I I I RANCHO CARILLO DRAINAGE STUDY SUBAREAS WITHIN DEVELOPMENT Leeds,.Hill and Jewett, Inc. Jan. 1981 C C ( C C C C .D 0 0 0 J 0 0 APPENDIX B BIOLOGICAL STUDY . lsa Purposely left blank 0 0 lsa 0 • APPENDIX C CULTURAL RESOURCES STUDIES 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10 I April 7, 1980 Larry Seeman Associates, Inc. 500 Newport Center Drive, Suite-525 Newport Beach; California 92660 Attention: Ms. Ann~tte Sanchez ,_ Subject: Rancho Carrillo Biological Assessment Dear Ms. Sanchez: .. The following letter is _a report of -findings from our assess.- ment of biological resources within -the Rancho Carrillo Planned Community .~tudy area. Methods-used to prepare this assessment included a thorough r_eview of relevant literature. and a field survey conducted on April; 2, 1980. -Literature ' sources reviewed included environmental impact reports· prepared for other projects in the area, publications by the California Department of Fish and Game, regional field guides and floras, publications on rare.and endangered species, and natural resource surveys,by-local governmental agencies and private conservation organizations. During the field survey no quantitative measurements were taken; nor -- was an exhau~tive-species list completed .. Rather, representa- tive wildlife.~nd plant species were· inventoried. • The report is divided into two sections "Setting" and- "Sensitiyity.11 _The.discussion of setting· describes the biological resources ori-site-as they exist, according to biotic -communities .---hf,_biotic community is an assemblage of plant and animal species that is found in a specific physical habitat where it exists as an ecological unit in an orderly, predictable manner. The discussion of sensitivity relates these communities. to their significance within locaf and regional.ecosystems. -The discussion of ·sensitivity -also covers rare and:endangered species.: SETTING There are three native biotic communities represented within the study area: l)·coastal sage scrub, 2) riparian, and 3) freshwater marsh. In addition, there are three communities EDAWinc. Environmemal Planning Urban Design Landscace Architecture San Francisco Newport Beach Alexandr,a Fort Cc:lins Honolu!c New Orreans 0 :i,:,a~o 3o,se 220 Newport Center Drive, Suite 20, Newport Beach, California 92660 Telephone (714) 644-9104 Larry Seeman Associates, Inc. Ms. Annette Sanchez Page Two April 7, 1980 Re: Rancho Carrillo Biological Assessment present which are the result of past disturbances by man. These are urban,, rural and introduced grassland communities. A map of biotic communities within·the study area Js enclosed. A list of the common plant and representa.tive ·anima_ls_ obseryed or expected to be normally found within each community is attached. • Coastal sage scrub is the biotic community char act.er is tic of the lower elevation hillsides and ridges in Southern California where it occupies dry, rocky -·soils. It is found scattered throughout the study area, but primarily on steeper hillsides and in drainages. It is an open community dominated by shrubs that grow two to five feet high and do not usually form a closed canopy.· However, bare ground is ·not ·common. Rainfall and·soil moisture are sufficient to support a variety of grasses and £orbs.· Growth of coastal sage-scrub vegetation occurs· in late winter and spring, following the onset.of ·winter rains. Most flowering will.occur in the • spring, after which the vegetation-becomes dormant and more or le·ss deciduous in summer and fall. • Plant species composition in coastal sage scrub varies on- site depending-on slope exposure. On south-facing -slopes dominants include black sage .(Salvia mellifera) ~ California brittlebush (Encelia californica) and California sagebrush· (Artemisia·californica), where these species-grow in low open stands. In.contrast, coastal sage scrub on north- facing slopes include larger, more robust plant species, such as toyon (Heteromeles .arbutife:>lia), lemonadeberry • (Rhus integrifolia·), ·. laurel' sumac (Rhus .. laurina) , and wartysteni ceanothus· (Ceanothus verrucosus). · Here· these species form very dense stands th-at resemble chaparral, a similar· scrub vegetat,ion known -for its nearly impenetrable stands of stout shrubs. It should be pointed out that chamise -(Adenostoma fasciculatum), the "indicator" of true chaparral, is found on-site; but only sparsely and does not represent a true chaparral community development~ Groundcover·throughout is dominated by annual grasses and forbs that have-been introduced by man through grazing and agriculture. These include brome grasses (Bromus spp.), oats (Avena spp.) and filaree ·(Erodium spp.) . C C C C 0 ·O 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 I Larry Seeman Associates, Inc. Ms. Annette Sanchez Page Three April 7, 19·9 0 Re: Rancho Carrillo Biological Assessment Coastal sage scrub is a productive habitat and supports a surprising diversity and abundance of wildlife including many reptiles, small mammals and birds. Riparian, or streambank, communities are found along drainage courses throughout Californ~a where moisture is at or near the ground surface on a year-round basis. These conditions are favorable for the establishment of a dense cover of trees and shrub understory. On-site, examples of this community can be found at the two impoundment basins and along the drainage·course which runs west from the ranch buildings in the center of the property. These communities are dominated by willows (Salix spp.) and coast live oak (Quereus agrifolia). A variety of large tree-sized shrubs, including lernonadeberry, toyon, laurel sumac and Mexican elderberry (Sarnbucus rnexicana), are also common. Many -·smaller shrubs and a thick moist groundcover of leaf litter are also present. Riparian_ veg.etation around the .i,mpoundment reservoirs remains in good condition. Along the stream course, however, ·there have been many disturbances by man (dumping, clearing, etc.) and the invasion of.non-· native plant species. As a result,· the vegetation and community.integrity here is.in fair to poor condition. Riparian communities normally possess a high wildlife v~lue. The added dimension of trees in combination with a dense understory of shrubs creates a high habitat diversity which, in turn, suppo~ts a high abundance and diversity of wildlife. Habitat diversity is usually further enhanced by the interface of riparian vegetation with.adjacent habitat types. This is not belived to be thea..case for riparian habitats on-site. The small size of riparian habitats at both impoundment areas, and the degraded condition of riparian habitat along the drainage course, limit their ability to attract and s~pport wildlife. As a result, they are belived to be no more important than surrounding habitat types. Freshwater marsh is found at the larger of the two impoundments. This community is composed of ernersed aquatic plants growing Larry Seeman Associates, Inc. Ms. Annette Sanchez Page Four April 7, 1980 Re: Rancho Carrillo Biological Assessment in permanently saturated soils. Dominant species, including cattail (Typha latifolia) and olney bulrush (Scirpus olneyi), grow up to six feet tall in dense stands with nearly complete cover. Willows and mulefat (Baccharis glutinosa) are also common. On-site, this habitat· ~ppears to be in good condition. Freshwater marsh communities serv:e as.the entire habitat ·or a critical component of the habitat for many. wildlife forms, particularly amphibians. Most. of these species spend their entire life-cycle in freshwater aquatic and semi-aquatic habitats, and could not otherwise survive. In association with the freshwater marsh on-site is an area of open water. This is important to water fowl and other water birds which use this area as wintering and resting habitat during their migrations. The most common community in the study area is i"ntroduced grassland, also referred to as valley grassland. This is the type of vegetation which ;replaces native vegetation ·following artificial clearing. In .its development, native plant species are _removed and are replaced by introduced adventitious species that can-withstand frequent disturbance. As a result, the flora of this community is dominated by annual grasses and herbs that grow two to three feet tall and reestablish themselves _on a yearly basis. The vegetative -cover typically germinates during the late fall rainfall, and grows ~nd flowers from winter through spring. -Plans then die and persist as seeds through summer and early fall.· This life cycle is i~_contrast to native grasslands which consist of peren~ial bunch grasses. Relatively large area:s of introduced grassland exist over most level and gently. rolling hillsides within the.study area. Here, this community is dominated by ripgutgrass (Bromus diandrus), red brome (Bromus rubens) and slender wild oaks (Avena fatua). Many other species, mostly non- native invasive forms, are also present. Due to their altered condition·, large open expanses of grassland support limited wildlife populations. They are, C C C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Larry Seeman Associates, Inc. Ms. Annette Sanchez Page Five April 7, 1980 Re: Rancho Carrillo Biological Assessment perhaps, most important to birds of prey which use them as for~ging habitat~ In addition, there .are a handfull of other wildlife which are adapted to grassland habitats and are found here in fairly high numbers~ Rural communities are characterized by orchards, pasture, cultivated croplands, abandoned fields and scattered residences. It is found mostly on broad valley floors and gently rolling hillsides where soils are ~uit~ble for agriculture. Within the study area, rural communities are confined to a smali area around the ranch buildings. The orchards, abandoned fields and ornamental vegetation found here are far removed from natural conditions and represent artificial simplications of habitats. Vegetation found outside of cultivated areas predominantly consists of common roadside weeds. These include tree tobacco (Nicotiana glauca), brome ·grasses, telegraph weed (Heterothera ~randiflora) and mustard. . The native flora in rura_l communities has been heavily impacted, if not totally removed. Consequently, natural habitat diversity and productivity has been greatly reduced. As a result, the abundance and diversity of wildlife is considerably limited. In. addition to the lack of native habitats, wildlife receive predator and competitor pressure from non-native animals which have been introduced to these areas (chickens, ducks, peacocks, house mouse, house finch, rock dove, ca ts and dog.s l .. : Urban communities 'are.found within residential subdivisions, commercial areas and.-industry .. Within the study area, urban areas exist.in the southwest corner where they consist of a recently constructed subdivision. All native vegetation has been removed from this area and replaced by non-native _ ornamental plants. Native wildlife diversity is extremely low with only few species, which are highly adaptable to man's presence and severe alterations in habitat, being able to-survive. Larry Seeman Associates, Inc. Ms. Annette Sanchez Page Six April 7, 1980 Re: Rancho Carrillo Biological Assessment C C SENSITIVITY C No rare, endangered, or threatened wildlife or plants have been reported or were observed to occur on-site. Within a few miles of the site, there are several pla·nt species which are on the California Native Plant Society's (C.N.P.S.) list of rare and endangered specie·s. Presumably, remaining areas C of dense coastal sage scrub repr_esents suitable habitat for some of these. These species include Del Mar manzanita (Arctostaphylus glandulosa ver. crassifolia), adolphia (Adelphia californica) and pygmy spikemoss (Selaginella cine- .rescens), and one ·species of concern to the ~.N.P .. S. but not yet listed, summer holly (C·omarostaphylos diversifolia C var. diversifolia). Although not identified on-site, small populations of one or more of these may have gone undetected. It should be noted, however, that none of these species are on either the Federal or State lists of rare, endangered, or threatened species. Their listing by the C.N.P.S. is advisory only to government wildlife agencies and public decision-C makers. Other species of note which were observed or expected on- site include the white-tailed kite, a "fully-protect,ed" specie.s and several others which are on the Audubon Blue List. Under the California Species Preservation Act of 1970 0 and the California Fish and Game Code, it is unlawful to take, possess or sell species which are fully protected. However, there are no provis~ons regarding the required preservation of habi~~1=-,.:·o-~ ·these species. The Audubon Blue • List is a list of bird species which are believed to be experiencing population declines and are of concern to the . 0 National Audubon Society.· This _list is a~visory only and is not to be interpreted as meaning these species are rare and endangered only worthy of monitoring and attention by researchers, conservationists and wildlife agencies. In local context, habitat·s on-site which are of greatest 0 importance to wildl-ife are the coastal sage scrub and freshwater marsh/open water around the larger of the two impoundments. Both areas are believed to support a reasonably full or 0 0 0 0 0 0 0 0 0 0 0 0 0 Larry Seeman Associates, Inc. Ms. Annette Sanchez Page Seven April 7, 1980 Re: Rancho Carrillo Biological Assessment unique complement of wildlife. In regional context, the freshwater marsh and adjacent open water are noteworthy because of the limited distribution of these habitats in Southern California. These habitats are not extensive or particularly well-developed_ and are therefore not-believed to be significant on a regional basis. We hope this account of our assessment and analysis will meet your needs. If you have any questions regarding our work, please feel free to call. Yours truly, Steven G. Nelson Associate SGN/mvp Enclosures _,: .. .,.,:... -.·-,---- RANCHO CARRILLO PLANT AND WILDLIFE SPECIES INVENTORY The ~allowing is a list of the dominant and .common plants and representative wildlife·observed or expected to occur within the biotic communities on-site. The lists are not intended to be exhaustive;. rather they are intended to ch.a!:"acterize the communities vegetative life forms and plant,diversity and their resultant use by wildlife in a compara.tive manner. Legend 1 2 3 4 5 6 coastal. sage scrub riparian freshwater marsh introduced grassland rural urban C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 PLA~TS Yucca whipplei -our lord's candle native -shrub Allium•fimbriatum -wild onion native -perennial bulb Rhus integrifolia -lernonadeberry native -shrub Rhus laurina -laural sumac native -shrub Schinus.rnolle -pepper tree introduced -tree Toxicodendron diversiloburn -poison oak native -shrub Apium graveolens -wild celery· introduced -annual to perennial herb Foeniculum vulgare -sweet fennel introduced -perennial herb -weed Nerium oleander -oleander, introduced shrub Arternisia californica native -shrub California sagebrush Arternisia douglasiana mugwort native -perennia~ herb -weed Baccharis ernoryi -Emory baccharis native -shrub -- Baccharis glutinosa -mule fat native -shrub Conyza canadensis -horseweed native -annual -weed Encelia californica -California encelia native -shrub Haplopa?;'US -..renetus -coca1stal ':iOldenbush native -shrub 1 • 1,2,5 2,5 2 3,4,5 3,4,5 5 1,2,4 2 1,2 2,3 4,5 1 1,2,4 PLA~TTS Helianthus annuus -com.-non sunflower native -perennial Heterotheca grandiflora -telegraph weed native -annual Sonshus oleraceus -com.-non sow thistle introduced -annual -weed Amsininckia intermedia -common fiddle-neck .· native -annual Brassica geniculata -summer m introduced -biennial -weed Brassica nigra -black mustard introduced -annual -weed Raphanus sati~rus -wild radish introduced -biennial -weed Opuntia occidentalis -prickly-pear Sambucus mexicana -Mexican elderberry native -shrub Atriplex semibaccata -Australian saltbush introduced -perennial herb -weed Chenopodium album· -lamb's-quarters introduced -annual -weed Salsola iberica -Russian thistle introduced -annual -weed Calvstegia macrostegia -western bindweed native -peren~~~~ -herb Cuscuta so. -dodder native -parasite Scirpus olneyi -olney busrush native -perennial -herb Euphorbia oolycarpa -golondrina native -perennial herb Lotus scooarius -·aeerweed native -shrub Lupinus sp. -Lupine native -annual 4,5 4,5 4,5 4 2,4,5 2,4,5 . 3. ,·4, 5 l, 4. 2,5 4,5 5 5 1,2 1 3 4,5 1 4 C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 PLANTS Melilotus indicus -yellow sweet-clover introduced -perenni.al -herb -weed Quercus agrifolia -coast live oak native -tree Erodium cicutarium -red-stemmed filaree introdµced -annual -weed Sisyrinchium bellum. -bl·ue-eyed grass native -perennial -herb Marrubium vulgare -horehound introduced -perennial -weed Salvia mellifera -black sage native -shrub -Malva parviflora -cheeseweed introduced -annual -weed Eucalyptus. sp. -eucalyptus non-native -tree Plantanus racemosa -California·sycamore native..;. tree Avena barbata -s.lender wild o~t introduced -~n:nual --.grass --weed Avena fatua -wild oat introduced -annual -grass -weed Bromus 'diandrus -ripgutgrass introduced -annu~·l ----grass -weed Bromus mollis -soft chess introduced annual~ grass -weed Bromus rubens -red brome introduced annual -grass -weed Hordeum vulgare -common barley· introduced -annual -grass Eriogonum fasciculatum -California• buckwheat native -annual Rume:-:: crispus -curly dock introduced -perennial -weed 4., 5 2 4,5 4 2,4,-5 1·,2 4,5 5 2,5 1,4,5· .1, 4, 5 1,4,5 1,4,5 4 1,2 2,3;4 PLANTS Ceanothus verrucosus -warty-stemmed ceanothus native shrub Salix SP. -willow native tree Salix gooddingii -black willow native -tree Salix lasiolepis -arroyo willow native -tree Nicotiana glauca -tree tobacco introduced -shrub or tree -weed Typha latifolia -cat-tail native -perennial -herb M-lPHIBIANS Bufo boreas -western toad Hyla regilla -pacific treefrog Batrachoseps attenuatus sal.amander California slender 1 2,3 2,3 2,3 2,4,5 3 2,3,5 Batrachoseps pacificus -pacific slender slarriander 2,3 Rana catesbiana -bullfrog REPTILES ... ··. ; .. Gerrhonotus mul ticarinatus· -southern all_igator lizard Pituophis melanoleucus -gophe.r·::snci.ke Thamnophis sirtalis -common garter snake Phrynosoma coronatum -coast horned lizard Sceloporus occidentalis -~estern fence lizard Uta stansburiana·-side-blotched lizard Crotalus ruber -red diEmond rattl~snake 3 2,5 1,2,4,5 2,3 1 1,2,5 1,4 C C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Canis latrans -coyote Odocoileus hemionus -mule deer Microtus californicus -California yole Neotorna lepida -desert woodrat Peromyscus californicus -. Cal-ifornia mouse Peromyscus maniculatus -deer mouse Didelph_is virginiana Virginia opossum Lynx rufus -bobcat Thomomys bottae -Botta pocket goph~r Dipodomys agilis -pacific kangaroo_ rat Perogpathus fallax -San Di~go pocket mouse Sylvilagus audubonii -Audubon ~ottontail Mus musculus -house mouse 1,2,:3,4,5 1,2,3 .2,3 1 1,2 1,2,4,5 2,5 1,2 4,5 :1,2 _ 1, 2 ,1,2 5 Mephitis mephitis -striped skunk 1,2,3 Spermophilus beecheyi California ground squirrel ._ l. 2. 4.·. 5 Several species BIRDS Buteo jamaicensis red-tailed hawk Circus cyaneus -marsh hawk Elanus Leucurus -white-tailed kite Eremophila alpestris -horned_ la~k - Megaceryle alcyon -belted kingfisher Anas acuta -pintail Anas clv:9eata -n_orthern shoveler Anas platyrhvnchos -mallard 1,2, 3, 4 2, 4_ 2-, 4 2,4 4 3 .3 3 3 Bucephala albeola -bufflehead Oxyura jarnaicensis -ruddy duck Ardea hetodias -great blue he~on Bubulcus ibis -cattle egret 3_ _ 3 3 3 Nycticorax nycticorax --black-crowned night heron. ·3 -: Bornbycilla cedrorurn -cedar·waxwing 5 Cathartes aura -turkey·vulture Charnaea fasciata -wrentit Charadrius vociferus -_killdeer Columba livia -domestic pigeon: Streptopelia chinensis: -spott:ed dove Zenaida rnacroura -mourning dove Aphelocorna coerulescens -scrub jay Corvus brachyrhynchos -common crow Corvus corax -common raven Geococcyx californianus -roadrunner Falco sparverius -American kestrel Carpodacus rnexicanus, '=·-: house finch Melospiza rnelodia -·song sparrow Pipilo ervthrophthalmus -rufous-sided towhee Pipilo fuscus -brown towhee· Pooecetes grarnineus -vesper sparrow Spinus psaltria -lesser goldfinch zonotrichia atricapilla -golden-crowned sparrow zonotrichia leucophrvs -white-crowned sparrow- 1,2,3,4 l 3 • 5; 6 4,5 4,5 1,2,5 2,5,'6 -:1,2,4,5 1 2,4,5 1,2,5,6 2,4;5 1,.2 l·, 2 / 5 4 l ;-2, 5 1~2,5 _ .1, 2, s. C C C 0 C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Pe~rochelidon pvrrhonota -cliff swallow Agelaius phoeniceus -red-win9ed blackbird Euphagus cyanoceohalus -Brewer~-blackbird Sturnella neglecta -western meadowlark Lanius ludovicianus -loggerhead shrike Larus delawarensis -ring-billed gull Mimus polyglottos -mockingbird Toxostoma redivivum -California thrasher Psaltriparus minimus -bushtit Dendroica cornata -yellow-ru..'llped warbler Dendroica petechia -yellow warbler Vermivora celata -orange-crowned warbler Lophortyx californicus -California quail Colaptes auratus -common flicker Dendrocopos nuttallii -Nuttall's woodpecker Passer domesticus -house sparrow Podilymbus podiceps -pied-billed grebe Fulica americana -American coot Bubo virginianus -great-horned owl Speotyto cunicularia -burrowing owl Sturnus vulgaris -starling Polioptila caerulea -blue-gray gnatcatcher Calypte anna -Anna's hummingbird Thryomanes bewickii -Bewick's wren Troglodytes aedon -house wren Sialia mexicana -western bluebird 1,2,3-,4,5 3,4 4,5,6 4 .4, 5 3 1,2,5,6 1 1,2 1,2,5 1,2,5 1,2,5 1 1,2,5 1;2 5,6 3 3 2,5 4 2,5,6 1 1,2,5,6 ~,2,5 2,5 4 Turdus rnig:i::-atorius -A.'11erican robin Contopus sordidulus -western wood pewee Sayornis nigricans -black phoebe Sayornis-saya-~.sa~•s phoebe Tyrannus verticalis -western kingbird Tyto alba -barn owl 4,5 2,5 3,4 4 4 2,4,5 C C C 0 0 0 0 0 0 \ 0 0 0 0 I 0 I 0 0 r I I 0 0 0 INTRODUCTION A REPORT ON THE KNOWN CULTURAL RESOU:RCES OF RANCHO CARRILLO CITY OF CARLSBAD In August 1979, WESTEC Services was requested by Daon Southwest to review a report previously prepared· by RECO N regarding the results of their cultural resources survey of Carrillo Ranch in -northern San Diego County (An Archaeological Surf ace Reconnai~ance of the Rancho Carrillo Area; Job No~ 5632; RECON, September 1976). The purpose of WESTEC's effort was to provide Daon with an overview of the major cultural resources constraints to development extant on· the property. While the survey methods used by RECON seemed to be generally acceptable and the result of their survey reasonable, WESTEC Services at the time stated that they reserved professional endorsement of their report unless further surveys by WESTEC were conducted which would confirm (or dispute) RECON findings. In November 1979 Daon Southwest requested that WESTEC Services conduct field surveys, map, and evaluate four of the most significant sites (three archaeological and one historical) known to exist on the property. At about the same time, the results of another series of field surveys conducted as part of a separate pipeline project, and included as part of the associated EIR, became known (Neste, Brudin and Stone; San Marcos County Water Dis~ict Land Outfall Environmental Impact Report; June 1979). This survey confirmed much of the information previously included in the RECON report, but also defined a somewhat larger surface indication for one of the previously recorded sites. The results of both the RECON report and the Neste, Brudin and Stone report were •available fo~ use by WESTEC Services' staff personnel in conducting the mapping surveys for four of the more significant sites (W-915, W-1082, W-1086, W-1089). 1 A summary of the two reports prepared ~y WESTEC Services is provided in the following paragraphs. WESTEC SERVICES' REPORT DATED SEPTEMBER 20, 1979 This report was prepared for Daon Southwest based solely on the information contained in the previously pub~hed RECON report, i.e., RECON's information was not confirmed through additional field surveys nor were additional record searches con- ducted. RECON identified 28 recorded sites within RaJ?,cho Carrµlo however, inasmuch as RECON's report had gone into considerable detail regarding each of the sites, their full particulars were not reiterated within WESTEC's summarized report .. These 28 sites, which are shown in Figure 1, are listed and briefly described below, along with suggested mitigation for each: 1. 2. 3. Resource Rancho de los uiotes ( Carrillo Ranch: Remains of a restored early California Rancho; will be preserved as part of a 20-acre park. SDM-W-1082: Historic cross set in a plastered adobe base overlooking Rancho d~ los Quiotes. SDM-W-915: Size= 4oo·m2, with an indicated depth of 35 centimeters (cm).· Recorded as "highly--patinated felsite scrapers@.~ flakes, basalt debitage and one bro~~" blade fragment" (Kaldenberg, 1976), including shellfish remains dated to 6880 (+280) B.P. (Before Present) (UR-434}. Phaser test would require approximately· five test units. Based on the results of Phase I, Phase II, Salvage, would. call for anywhere from 5~20 percent salvage (20-80 units}, depending not only on the results of Phase I, but also on the requirements of the involved governmental agencies. 2 Proposed Mitigation Preserve Preserve Preserve if possible; if not, then testand • excavate C C C C C 0 0 0 0 0 0 ----------- 0 Proposed 0 Resource. Mitigation 4. SDM•W-1086: Size = 2000 m 2 with an Preserve if estimated depth of midden of 40 cm. possible; if RECON report calls it ''The most not, then substantial prehistoric archaeological test and 0 resource on the subject property." • excavate Contains a wide variety of lithic artifacts, including scrapers, hammer- tones, manes, both secondary and primary flakes and cores. Phase I would require 4-5 test units; Phase n, Salvage, would 0 again call for 5-20 percent salvage (or 100-400 test units), depending on the results of Phase I and governmental requirements. • 5. SDM-W-1089: Size= 300 m2, with a Preserve if 0 possibility of "culture-bearing over-possible; if burden" (RECON, 1973). Resources found not, then include 20 flakes and debitage, plus a test and wide variety of shell. Phase I would excavate require 2-3 test units; Phase Il would again probably call for a 5-20 percent 0 salvage (15-60 units). 6. SDM-W-1087: No size given; "Presence Collect and of shell indicates human activity" analyze (RECON, 1973). 7. SDM-W-1088: No size given; shell Collect and 0 scatter including bean clam. analyze 8. SDM-W-1078: Size= 2000 m2; light -collect and shell scatter. analyze 9. SDM-W-1085: Size~ 100 .m2; two flakes Map and 'O and a single scraper. collect 10. SDM-W-1090: Size= 100 m2; twenty Map and flakes/ debi tage. collect. 11. SDM-W-1083: Size= 70 m2; six Map and 0 artifacts plus a scatter of shell. collect 12c SDM-W-1084: Size= 1700 m2; Map and probable quarry area, consisting of collect several flakes, cores and at least one tool. 0 0 3 C Proposed Resource Mitigation C 13. SDM-W-1091: Size= 2500 m2 No further (probably inflated by recent mitigation agricultural activity); thin scatter necessary of artifacts including one chopping tool, one mano, several flakes, and C a shell. 14. SDM-W-1079: Size = 182 m 2; shell-No further fish remains. mitigation necessary 15. SDM-W-1080: Size= 65 m2; light No further C shell sea tter. mitigation necessary 16. • SDM-W-1081: Size= 460 m2; four No further flakes, two pieces of debitage; very mitigation light scatter of she~. necessary C ' . 17. SDM-W-588: Previdusly surface· No .further collected {Kaldenberg, 1975); site no mitigation longer exists~ necessary 18. SDM-W-587: Previously surface No further C collected {Kaldenberg, 1975); site no mitigation longer exists. necessary 19. SDM-W-589: Previously surface No further collected (Kaldenberg, 1975); site no mitigation longer exists. necessary 0 20. Isolate I: Mano fragment No further mitigation --·· .. · _ _._ .· necessary '21. Isolate n:-,:~-Flake No further 0 mitigation necessary 22. Isolate m. Three pieces of debitage No further mitigation nec~ssary 0 23. ~elate IV: Flake No further mitigation necessary 0 4 0 0 0 0 0 0 0 0 0 0 0 0 Resource 24. Isolate V: Flake (felsite) 25. Isolate VI: • Flake (f elsite) 26. • Isolate vn: Flake 27. Isolate VIII: Single mano 28. .Isolate XIV: Chopping tool Proposed Mitigation No further mitigation necessary No further mitigation necessary No further mitigation necessary No further mitigation necessary No further mitigation necessary It should be stated that although the RECON report suggested postholing as a portion of the recorded. mitigation, WESTEC Services has found this techniqlle to be neither universally accepted throughout th~ archaeological community, nor completely effective as a mitigation measure. Therefore, WESTEC Services would recommend a series of one-meter _square test units rather than postholes as part of either the Phase I or the Phasca II test and salvage activity. WESTEC SERVICE'S REPORT DATED DECEMBER 17, 1979 This report was provided as a narrative to accompany 200 scale work maps which were prepared _by WESTEC Services' staff archaeologists and submitted to Daon's ~roject engineer for consideration as cultural resources constrajnt data during the planning phases of development of Rancho Carrillo. Only one set of maps was prepared; they were not reduced to a more convenient size for inclusion in the December '79 report and are thus also not included herein. WESTEC Services' field survey and mapping effort was directed at only four of the 28 sites listed earlier, namely W-915, W-1082, W-1086 and W-1089. The full text of WESTEC's report follows. 5 INTRODUCTION On November 26, 1979 an archaeological evaluation of· three archaeological and one historic site was conducted by WESTEC Services, Inc. The valuation was conducted by Brian Hunter and Peter Ainsworth, Associate Archaeologists, under the direction of. Richard L. Carrico, Manager, Cultural Resources Group. FIELD TECHNIQUES AND RESULTS The sites were relocated using information from a 1977 archaeological survey report prepared by Charles Bull of RECON. Surface artifacts were located on a 200 scale map ·to delineate site boundaries. Visual observations determined site extent and value. W-915 - This site was described by Bull as being "recorded by Kaldenberg during his survey of La Costa" (1976). At that time he noted ''highly patinated felsite scrapers and flakes; basalt debitage and. one broken blade fragment" (K~denberg 1976). He also presents a Carbon' 14 date of ·saso+ 280 B . .P. (Before Present) (UCR-434) • for shellfish remains collected from the site. The site is located in the Northwest Quarter of the Southeast Quarter of Section 19, Township 12 South, Range 3 West, San Bernardino Base Meridian. It is at a minimum elevation of 500 fe~tabove Mean Sea Level and covers an area of approxi- mately 4000 square met~~;~-···-~ profile of the southern extent of the site, revealed by bUITowing activities, ·indicate_s a mimumum depth of 35 centimeters (Bull, 1977). • Present field observation confirmed Bull's estimation of the site, but would confine the midden area to a 30 x 40 meter area of the site. 6 0 0 0 0 0 0 0 0 0 0 0 I I I 0 0 0 0 0 0 0 0 0 0 0 W-1082 Bull described the site as "an historic cross set in a plastered adobe base. The cross sets atop a hill overlooking the Rancho de Las Quistes, a.n'd would apparently date from that period." A quick check· of the historical records· failed to reveal any specific reference to the cross. Structural features, such as. milled wooden components, nuts and bolts, an.d "recent appearing" plaster would tend to indicate association with the Carrillo use of the area (1938ff) rather than the earlier Kelly occupation. in 1870 (Bull, 1977). Field observation of this site ·confirmed Bull's description. W-1086 . . This site is the most substantial prehistoric archaeological resource on the subject property. It is located on a small knoll overlooking Carrillo Ranch, and lies at an elevation of about 245 feet above Mean Sea Level. Its location can be described as being within the Northeast Quarter of ·the Northwest Quarter of Section 19, Town- ship 12 South, Range 3 West, ·san Bernardino Base Meridian. The site covers an area ot·2000 square m~ters· with an estimated depth of midden of 40 centimeters. A wide variety of lithic· artifacts were identified on the site including scrapers~ hammerstones, manos, both secondary and primary flakes and cores. Moderate ·amounts of shell, primarily Aeguipecten and Chione, were also found at this site. Interestingly, the site is limited to the knoll and does not extend up a small ridge to the north (Bull, 1977). Present field work could not confirm Bull's observation. At this time the site's area is covered by a thick growth of annual grasses. Site boundaries are tentative. until they c~ be delineated by further work. 1 W-1089 "This site covers a surface area of about 300 square meters. It_ lies on a steep slope of a large south-facing hill immediately above the central valley. It falls within the Southeast Quarter of the Northeast . Quarter _of -Se~tfo~ 24, Township 12 South, Range 4 West, San Bernardino Base Meridian, _at an elevation of about .190. feet above . . Mean Sea Level ..... There is a _possibility that this site has a culture-bearing overburden, and thus has markedly greater research potential than the neighboring simple surface scat~er" (Bull, 1977). W-1089 is now badly disturbed. Eighty percent has been bladed away by road construction, leaving only a 10 x 10 meter area und~turbed. MITIGATING MEASURES The following mitigating measures are recommended to further test and assess the possibility of adverse.·· impacts upon the ~chaeological resources noted. in . the previous sectio~~ As currently perceiv_ed, the following m_easures may achieve adequate mitigation of potential adverse impacts to archaeological resourcees within this . . project. However, discovery of human burials, sacred objects or other outstanding cultural resources may require these mitigating measures to be re-evaluated. Ap~roval . . and ultimate implementaU.011:: will ensure that ~xecution of the proposed construction will not· directly or sec0ndarily impact any of these known resources. -~·.:.:.:..· __ -. ' • • • The cultural resources located within this project area require further investiga- tion beyond the field survey level. It is suggested that a phased study be conducted .. . which will produce information that allows the researcher and the developer to make rational and feasible decisions regarding the protection of these cultural resources. 8 0 0 0 0 0 0 0 0 0 0 0 0· i !o I 0 0 0 0 0 0 0 Phase I Phase I testing should in~lude accurate instrument location of each reso(U'ce on 1 ":200' maps, and a thorough mapping of the surf~ce deposits at ea~h site. The goal of • ' ' -. -. .' .. this mapping is to ascertain the precise location and areal distribution of each site, to accurately map previous disruptions, and to f~ther evaluate each site's surface de~osit. P_otential feature~ and possible artU'acts that would be affected by construction should ' ' . . ---. • be photographed, mapped and measured. __ Minimal subsurfa_ce ~esting in the form 9f 5 or .. --= . . . . ' ~ . 6 _ one by one_ meter pits will.also be required. At this time, each isolated. artifact or . . . . . . .. - feature• should r~eive the fc,ll~,wing measures: af!curate_ loc~~ion. of each isolated artifact/feature; photographs . and scaled sketch dl'awings of isolated. features; and surface collection and analysis of isolated artifacts. Data and maps from this study should be compiled as a Phase I. report; .. and be provid_~d to the developer and appropriate governmental agency for their consideration. Phase II • If archaeological site avoidance is not possible~ it is recommended that a further phased program be initiated io salvage the'· artifacts from those portions not avoidable. ~ ; . ' • .; . Since location, type and significance of these resources varies, a phased program will ensure expedience and reduce costs by allowing conc~rent constl:'uction and monitoring to take place in. those areas not recognized as archaeological resources. .. ' A Phase II study should include a limited (less than one percent) subsurface test at eac.'1 site. Goals of these tests should include determination and. analysis 'o{ subsurface disruption, recovery of organic· material ·for dating, assessment of the subsurface ar·eal distribution of the. site and reco~ery of "type" artifacts to better determine the cultural . . affinity of each site. A professional report should be prepared which outlfues the tests and provides results and conclusions. 9 At this point, data available from the current report and data retrieved from these phased tests can be used to develop rational and feasible measures to mitigate the remaining impacts expected to adversely affecf the cultural resources located within ' . this project area; Phase III· Any Phase Ill -program f o·r the resources on the subject property will be based upon the .results and conclusions of the earlier phases. • Potential recommendations for Phase Ill and later phases may also· need to include total or partial preservation of some'sites, salvage programs, or some combination of salvage :and preservation. ·Some sites ·may . further require ri~mination for inclusion on the National Register of Hist~ric Places. Site W-915 W-1os2· W-1086 W-1089 RECOMMENDATION FOR MITIGATION Site Size 4000 Sq. Meters (43040 ·Sq. Ft) io Sq. Meters (108 Sq. Ft) , _ 2000 Sq. Meters _ (21520 Sq.· Ft) 100 Sq. Meters-• - <+-~76 Sq. Ft) _ Avoidance Phase I '.!'est Preservation Preservation Phase I Test Preservation ·Phase !"Test Preservation Mitigation Phased Excavation ·Phase I Test Phased Excavation Phase I Test .. As a final q.ote, it.~ report is to be included as an appendix to the Ranch,o • _ Carrillo EIR, it is_ recommended_ ~t the pe_r~ons preparing, the EIR also review the more detailed information con~ed in the earlier reports (RECON, 1976 and Neste, ' • •' ' . _Brudin and Stone, 1979) and incorporate the data _ co~tained therein into the Rancho Carrillo :EIR by reference; in compliance with recent amendments to CEQA. 10 0 0 0 0 0 0 0 0 0 0 0 I ·o r l I iQ l J I cl I q I ~ • ~ • 0 • ' -. APPENDIX F ARCHAEOLOGICAL SURVEY REPORT l l l I I I . f • ~ •• ~ f ' ii AN ARCHAEOLOGICAL SURFACE RECONNAISSANCE OF THE RANCHO CARRILLO AREA Prepared for RANCHO CARRILLO PARTNERSHIP 530 B STREET, SUITE 2330 SAN DIEGO, C~LIFORNIA 92101 Prepared by (Q:-4,,,~ ~\5£! CHARLES S. BULL SUPERVISORY ARCHAEOLOGIST RICK ENVIRONMENTAL CONSULTANTS :5620 FRIARS ACAC • SAN OleGC. CALIFCF'INIA S2110 • TELSPMCNE 71A I :299-5112' • JOB NO. 5632 SEPTEMBER 197 6 0 0 0 0 -0 0 0 0 C 0 ., J 0. I j· 1ci i CJ I Iii • lo II c'1 al I ~ i TABLE OF CONTENTS ABST'RACT •• . . . . . . . . . . . . . • • t • I. SU.Mi."v!ARY • • . . • • • • 0 • • • 0 . . • 0 • • A. FINDINGS • • • • • ~ • • •. • • • • 0 • • • • l. Section l . . . . . • • .. . . . " . . . • 2. Section 2 . • . • . . . • . . • . . • • ~ 3. Section 3 . • • . • . • . . . • .. • • • . B. IMPACTS AND MITIGATION • • • • • • • • $ • • II. ARCHAEOLOGic;u. IMPACT REPORT . . . . . . . . . . A. PROJECT SETTING. • • • • • • • • • • p • • • B. . GEOLOGICAL RESOURCES . . . . . . . . . . . • C. BIOLOGIC]!..L SETTING . . . . . -. . . . . . . . 1. Description .............. . 2. Exploitation of Bi9logical Environment .. D. ARCHAEQLOGICAL SURVEY ........... . 1. Description . . . . . . . . . . . . . . . . 2. Results of Archaeological Investigation. Section l . . . . . . . . . . . . . . . Section 2 .............. . Section 3 . . .. . . . . . . . . . . . . E. CULTURAL SETTING . . . . . . . . . . . . . . l .. Batiquitos Lagoon Region . . . . . . . . 2. Far Southwest Area . . . . .. . . . . a. Early Man Stage . . . . . . . . . . . b. Milling Stone Stage . . . . . . . . . c. Late Prehistoric . . . . . . . . d. Swmnary . . . . . . . . . . • . . . e. Problems . . . . . . . . . . . . . . ii 1 l· l 4 4 5 7 7 8· 10 10 10 J.2 12 13 13 13 20 22 22 23 24 25 32 36 39 0 Page 0 F. IMPACTS RESULTING FROM THE PROPOSED PROJECT . . . . . . . . . . . . . . . . . . . . 43 i. Section l . . . . . . . . . . . . • . • . 43 2. Section 2 . . . . • • . . . •. . . . • • . 43 3. Section 3 . . . •. . . . . . . . . . . . . 44 0 4. Rancho de Los Quiotes (Carrillo Ranch). ... 44 G. MITIGATING MEASURES-. • . . . . . . . . • • . . 45 l. Site SDM-W-1091 . . . . . . . . • . . . . • 45 2. Sites SDM-W-1078, -:-1087, -1068 . . . • . . 45 0 3. Sites SDM=W-1079, -1080, -1081 . . . . . . 45 4. Sites SDM-W-1083, -1084, -1085, -1091 • . . 45 s. Sites SDM-W-587, -588, -589 . . . . • r •• . . 45 6. Site SDM-W-1089 • . . . . . . . . • . . . . 46 7. Site SDM-W-1056 and SDM-W-915 . •· . . . . . 46 a. Rancho de Los Quiotes (Carrillo 0 Ranch) and W-1082 . • .• . . • . . . . . 46 H. PROJECT STAFF . . . • . . . •· . . . . . 47 . . . • • . I. LIST· OF PERSONS AND ORGANIZATIONS CONSULTED . . 48 0 III. REFERENCES CITES· . . . . . . . • . . . .• . . . . . 49 A.TTACHMENT~ 54 0 0 D 0 0 0 0 0 0 0 0 0 I J I J f ------------ I • SUM..1\f.ARY .A. FINDINGS The proposed Rancho Carrillo project involves 853 acres of land in the City of Carlsbad, California (Figure l). The majority of the area is,located south of Palomar Airport Road, and about l.13 miles east of El Camino Real. The en- tire project area encompasses the Southeast Quarter of Sec- tion 24,-Township 12 South, Range 4 West, and Northwest Quar- ter, North Half of the Scuthwest Quarter, West Half of the Northeast Quarter and the Northwest Quarter of the Southwest Quarter of Section 19, and the South Half of Section 18, Town- ship 12 South, Range 3 West, San Bernardin·o Base Meridian. For clarity, the examination of this area will be divided into three segments (Figure 2). The first of these, Section l, is of prime interest at this time as it is sche- duled for alteration. Sections 2 and 3 will be discussed, but are not presently being considered for development. A total of 18 archaeological sites are scattered throu;hout the Rancho Carrillo area (Figure 2).· In associa- tion with these sites are numerous isolated artifacts. Of the archaeol9gical resources present, one is within Section l, three within Section 3 and 14 within Section 2. These sites vary from small, very light concentrations of artifacts and/or shell to a major historic resource, tjle Carrillo Ranch. Similarly, they range in scientific p_otential from those of. great L~portance to sites with little information potential. l. Section l. This portion of the Rancho Carrillo property lies in the northwestern corner and encompasses lll acres. Development of this area consists of construction of 346 dwelling units on approximately lll acres of land. One archaeological site, SDM-W-1091, and two iso- lated finds lie within this section. This site has been greatly disturbed through present land'use as the entire area is under cultivation for tomatoes. The disturbed nature of the site greatly detracts from its potential to provide infor- mation to local prehistoric archaeologists. The site consists of a very light scatter of arti- facts and a thin distribution of shell. The paucity of cul- tural material, then, combines with the disturbed condition of the resource to greatly limit the scientific potential of the resource. f-1 • j • ~ ~. ~ ~· I • J I ABSTRACT ' In accordance with the California Environmental Quality Act and the requirements of the City of Carlsbad, California, an archaeological survey was conducted of 853-acres known as Rancho Carrillo. The survey involved an on-foot reconnais- sance of 732-acres and an examination of the extensive work previously done on .the remaining 121-acres of the project area by a team of archaeologists representing RECON. As a result of this investigation, 18 archaeological sites were either discovered or revisited. This report is a result of that survey. Included herein are assessments of project impacts on the historic and prehistoric resources of the area, and recommendations for mitigation of those adverse impacts. I,' V ii 0 0 0 0 0 .o 0 0 0 0 0 0 0 Figure l ... ~ ........ 0 This figure shows the relative lOcation of the Raricho Carrillo·project within San Diego County, Califo.-:-11ia .. · 0 0 2 -This figure indicates the setting of the Rancho Carrillo project aFea, and the archaeological resources found. The area has been divided into three segments of clarity. C The isolated finds in this section were, -one chopping tool (ISO VIII) an~ -one mane (I.SO XIV). Impacts to these as well as all other isolated objects are mitigated through their documentation. 2. Section 2. This portion of the. ·~ncho C_arrillo area encompasses a,bout 600 acres and is the most signific~t archaeologically. Fourteen sites were identified within this area ranging from as recent as the Carrillo Ranch to as old as 6,000 years B.P. (Before Present) at· SDM-W-915 (Kaldenberg 1976:np ). The majority of the 14 ,sites identified within this area are _small, light concentrations of. artifacts and/pr shell and have limited archaeological potential. Three areas are of great archaeological· and-historic potential, SDM-W-915, SDM-W-1086 and the Carrillo Ranch area; one site of yet les-• ser significant importance, SDM-W-1089 ,· and one site of his- toric/aesthetic interest; SDM-W-1082, an historic cross set in an adobe base. The other sites, although valuable for the understanding of past lifeways, can provide. only _a limited range of information and are. of less value. As with other isolated finds, those found in Sec- tion 2 have had any impacts to them mitigated by their docu- mentation. 3. Section 3. The third section lies at the south- western extent of the Rancho Carrillo property. It consists of approximately 115 acres in Section 24, Township 12 South, Range 4 West, San Bernardino Base Meridian. The area has three archaeological resources, all -of which have been dealt with extensively in the past (Kaldenberg 1975). The three sites on this portion of the subject property, SDM-W-587, SDM-W-588 and SDM-W-589, were all dis- cussed extensively by Mr·~· Russell-.Kaldenberg. • All sites were collected and discussed (Kaldenberg 1975). In cor.clusion of his work, Mr. Kaldenberg felt that .. "Since the sites have been mapped, collected and analyzed, further arc~aeological inves- tigation is not likely to yield additional in~ormation con- cerning the prehistoric inhabitants of Carrillo Estates. Therefore, any potential loss of information from these ar- chaeological sites, due to development, is considered to have been mitigated" (Kaldenberg 1975:104). f-4 0 ,, ,, ii -b 0 l • I ! l 0 0 0 0 0 I 0 I cl I C! I 0 ~ :I B. IMPACTS AL'-iD MITIGATION Present plans at Rancho Carrillo involve direct im- pacts· only to ·section l. • As additional areas are scheduled for development, specific affects will be evaluated .. There- fore, at the present time, only SDM~W-1091 is subject to di- rect impact·s. As ·mentioned ·earlier-~_ this .archaeological re- source is light and has been greatly· disturbed. As such, no furhter mitigating measures can be recommended. The site could provide very littie additional information. The archaeological sites in Section 2 vary greatly as to importance and therefore as to necessary mitigation. Table l provides a synopsis of the mitigation which would be neces- sary for these ·resources. As no specific plans have been adopted for this area, impacts ~annot be concretely evaluated. All sites found in Sec::tion 3 are considered :mitigated by Kaldenberg's activities in 1975. f-5 ! I I 0 0 0 0 0 0 0 0 0 Site Number· 1 •. SDM-W.;_587 2. SDM-W-588 · .. 3. SOM-W-589 4. SDM-.W-915. 5. SDM-W-1078' 6. SDM-W-1079 1. . SDM~w.:..1oao 8. SDM-W-1081 9. SDM-W-1082 10. SDM-W-1083 ll.. SDM-W-1084 12. SDM-W-1085 13. SDM.;.~-1086 14. SDM-W-1087 15. SDM-W-1088 16. SDM-W-1089 17. SDM-W-1090 18. SDM-W-1091 u, ,.;r.;:-·;,-1 '(( TABLE 1· f-6 Mitigation Needed Prior to Disturbance None·-has been mitigated None~ has been mitigated· None -has been mitigated .·Excavation {Preservation pre- ferable) • • Collection and· analysis of-a . sample of shell None -·has been mitigated None ··-· has been mitigated None -has been mitigated Preservation Surface map and collection Surface map and collection ,· .. Surface map and collection ., Excavation (Preservation pre-. ferable) Collection and analysis of shell Collection and analysis of shell Posthole examination, test ex- cavation and mapping Surface map and collection None -has been mitigated ' . I -! i f I t r i I ' f ] ] I II. ARCHAEOLOGICAL IMPACT REPORT · A. PROJECT SETTING The· Rancho--Carriilo project area is located in the City of Carlsbad, California.. It consists of 853 acres· of land north of Rancho La, Costa, approximately 1·. 2 miles east of Palomar Airport and 1.5 mil_es west of Lake San ·Marcos. The entire project area encompasses the.Southeast Quarter-of Section 24, Township 12 Sout.h, Range 4 West, and Northwest Quarter, North Half of the Southwest Quarter, West Half of the Northeast Quarter and the Northwest Quarter of the Southwest Quarter of Section 19, and the south Half of-Section 18, Town- ship 12·sou~, Range 3 West, San Bernardino Base Meridian. The_project_area lies to the northeast of Batiquitos Lagoon, a major re·source area for prehistoric inhabitants, and is bisected· by -a northern tributary of San Marcos Creek. Thip drainage.would have been.the major source of water for aboriginal inhabitants'of the area. Topographically, the area consists of the major cen- tral drainage surrounded by steep to gradual sloping hills. The slope of these hills range from a minimum o~ six percent to a maxLuum of 25 percent with an estimated mean of 13 per- cent. The property ranges in elevation from 120 to 420. feet. above Mean Sea Level. f-7 0 0 0 0 0 0 0 0 0 0 0 l J I I a • I . B. GEOLOGICAL RESOURCES Throughout time, man has had to adapt his culture to the environmental setting in which it was located. This involved the development of culture traits which would allow for exploitation of local resources, be they biological or physical.. Culture, as man's primacy adaptive mechanism, en.- tails the utilization of available resources to provide the means of maintaining subsistence. Lithic materials ('stone) were-used in all aspects of prehistoric environmental adaptation, incl~ding huntinq a.nd vegetable food gathering and processing. An important char- acteristic of any given location, then is the availability of lithic resources. Aboriginal utilization of lithic material can b~ div- ided into two primary categories; butting and piercing imple- ments and grinding and crushing implements. The latter of these are made from a wide variety of materials, ranging from fine-grained metavolcanics to coarser quartzites and granitics. The former are produced by flaking such materials as felsite, basalt, quartz, obsidian and other fine-grained materials. As such, the occurrence of certain lithic materi- als on or near a specific area is important to the occurrence of archaeological sites. Of prime importance to our discussion, then, is the occurrence of g~ological resources on or near the subject property. The presence or absence of these materials can _ help provide an explanation for the occurrence of archaeo- logical sites. • Weber (1958-1959) · -_indicates that the area is an undi- vided sandstone of Eocene origin. Cretaceous age, quartz and grano-diorites occur at the southeastern portion of the property. Although no fine-grained lithic materials occur on the Rancho Carrillo property, Santiago Peak Metavulcanics are availalle less than one mile to the east ane to the south. There are also no outcrops of bedrock evident on the property, an important resource for the production of milling areas. The only lithic resource readily available on the property would be intrusive cobbles carried into the area by both cul- tural and natural forces. f-8 -0 0 0 0 0 0 0 0 0 C C 0 0 0 0 0 0 0 0 0 0 Topographically, the area is conducive to human oc- cupation. The relatively fla_t areas atop the various knolls of the-subject property, as well as the lower elevation (the central drainage), would have supplied several areas which are level enough for occupation._ The topography, and the availability of water then, would make this area conducive to habitation. • The marked lack of lithic resources, on the other hand, would detract from its attractiveness as a camp areaD f-9 i I I '0~ ~ :O_. , •. o■ ia ell C. BIOLOGICAL SETTING 1. Description. Before the establishment of Euro- pean lifeways in California,· local natives secured the essen- tials of life directly from their surroundings. This entailed a broad knowledge of plant and animal resources as well as an understanding of their applicability. The Native-American populations of San Diego County exploited a wide range of plants and animals. From the natural resources present, they were able to maintain a relatively stable lifestyle rarely seen in hunting and gathering cultures today. Although the area has been greatly impacted from past grazing and agricultural use, a wide variety of plants· and a.."limals still occur. The following plant list was com- piled by Riggan (1976·) for the Rancho Carrillo and represents a limited number of plants found on the property. Datura meteloides Quercus agrifolia Rhus laurina Rhus intearifolia Eriogonum fasiculatum Salvia mellifera Artemisa californica Opuntia englemanni Salix sp. Adelphia californica Nicotiana glauca Jimson Weed Coast Live Oak Laurel sum·ac Lemonade Berry Flat Top Buckwheat Black Sage . ·coastal Sage Brush Prickly Pear Willow California Adelphia Native Tobacco 2. Exploitation of Biological Environment. Many of these plants were used by aboriginal populations in Southern Californ~a. The acorn of the Coast Live Oak (Quercus. agrif~lia) was a primary staple for many historically known cultural groups (Hedges 1967). The Scrub Oak was not, however, a pri- mary food source due to the difficulty in processing of the acorn, though it has been recorded historically as a.a emer- gency food resource (Bean and Saubel 1972:130). Lemonade Ber- ry (Rhus integrifolia) was also used by Native-American popu- latioii°sof the San Diego area to produce a flavo~3d beverage (Bean and Saubel 1972:72). Black Sage (Salvia mellifera), Lemonade Berry (~ integrifolia), and Prickly Pear (Opuntia englemanni) all were used by ethnographically recorded peoples as a food resource (Welch 1976). Past inhabitants not only obtained food from the floral environment, but also other elements of existence. Local aborig1nes smoked Native Tobacco (Nicotiana glauca) used the Laurel Sumac (Rhus laurina) for medicinal purposes, and employed the Willow (Salix sp.) as a construction material (Welch 1976). --- f-10 As well as providing necessary food resources to human populations, this plant community also supported a vari- ety of other faunal life. These animals·added to the plant resources to increase and diversify food resources.available to prehistoric populations. Riggan (1976) noted the following fauna during a bio- logical investigation of the Rancho Carrillo area. Western Fence Lizard Bull Frog Raccoon Ground Squirrel· Mule Deer ~otton Tail. ~abbit Deer Mouse Pocket Mouse Wood Rat Kangaroo Rat Sceloporus occidentalis Rana catesbiana Procyon lotor Spirmoplulus beecheyi Odocorlues hemionus Sylviligus audobuni Peromyscus Perognathus Neotoma Dipodomys merriami As wit."1 geologic and floral resources, no single faunal resource.would suffice to be the main motivating fac- tor in the occupation of the Rancho Carrillo area. The wide variety of species would,_ when· taken in their totality, pro- vide another necessary element to prehistoric and protohis- toric subsistence requirements. 0 0 0 0 0 0 0 0 0 0 0 ~ ~ ;W =ii 11 m iiJI ·D. ARCHAEOLOGICAL SURVEY l. Description. On 21 and 22 July, 1976, a crew of archaeologists surveyed the 732-acres of land constituting the major portion of the Rancho Carrillo project area. The remainder of the subject property has been dealt with exten~ sively both.by May (1973) for David D. Smith and Associates, and by Kaldenberg (.1975) for RECON. This additional 121-acres were, at the time of Kaldenberg's work, known as Carrillo Es- ·tates and were dealt with intensively in. Archaeological Inves- tigations at Rancho Carrillo Estates (Kaldenberg 1975). At that tlllle, Kaldenberg, representing RECON, stated that any potential loss of information from these archaeological sites due to development, is considered to have been mitigated (Kal- denberg 1975:104). The area dealt with by Kaldenberg corres- ·ponds to Section 3 of the Rancho Carrillo project as discussed in this report. A total of 104 manhours was spent in the.field by Charles s. Bull, Supervisory Archaeologist: David Hanna, Jr., Assistant Archaeologist/Field Supervisor; Margret Wie-. dauer, Harvey Hatley, and Kree Easland, Archaeological Assist- ants, all representing RECON. All accessible areas were exar.i.ined on foot for the presence of his~oric, protohistoric a.,d prehistoric remains. As a result of -this survey, 18 archaeological sites were located. These sites varied in age from the rela- tively recent Carrillo Ranch to at least as old as 6,880±280 at SDM-W-915 (UCR-434) (Kaldenberg 1976:71), and they vary in extent from small, sparse scatters of shell to concentrated collections of lithic artifacts and rich midden soil. . For. clarity this project area will be arbitrarily divided into three sections (See Figure 2) .. Section 1 is an irregularly shaped, 111-acre parcel in the northeastern corner of the property. It corresponds directly to Units a and i-1 of the Rancho Carrillc Master Development.Plan. Section 2 consists of 621-acres and encompasses Units h-l, h-2, h-3, b, c, d, e, f, i-2, j and k of the Master DPvelopment Plan. Finally, Section 3 corresponds to Unit g of the Plan and en- compasses 121-acres at the southwestern extent of th·e subject property. Both Sections 1 and 2 were subject to an on-foot survey in conjunction with this report. Section 3 had pre- viously been surveyed by May (1973) and dealt with extensively by Kaldenberg (1975). As such, a re-survey of this area wotild have been needlessly repetitious. f-12 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 In lieu of a re-survey of this area, a discussion of the work performed previously will be presented. 2. Results of Archaeological Investigation Section l. A single archaeological site was located on this portion of the Rancho Carrillo property. In addition, two isolated prehistoric artifacts were also dis- covered. SDM-W-1091. This site is located in the Southwest Quarter of the Southwest Quarter of Section 18-and the Northwest Quarter of the Northwest Quarter of Section 19, Township 12 South, Range 3 West, San Bernardino Base Meridian. It lies at an elevation of about 470 feet above Mean Sea Level and presently covers a surface area of 2,500 square meters. This area.figure appears grossly inflated because of artifact scatter caused by recent agricultural activity. It is not possible to establish the original surface size of this re- source because of this disturbance. The entire site area is presently under cul- tivation for tomatoes. At the time of· the initial survey, the area had been plowed, but not yet planted. As such, ground visibility was excellent. The site consists of a thin scatter of ar- tifacts including one chopping tool, one mano, several flakes, and a sparse scatter of Aequipecten sp. and Chione sp. shell. There is no intact midden on the site and present conditions and activities would prevent the obtainment of any conclusive =ultural information. Radiocarbon dates could be obtained from the shell. The lack .of contectual information would make the results highly dubious, while the absence of much cultural debris would prevent any profitable gain for general San Diego County prehistory. Isolated Finds. In addition to the single, disturbed site identizied in this area, two objects were found which were not associated with any specific resolil'ces. A single mane ISO-VIII and a chopping tool, ISO-XIV, were found and plotted (See Figure 2). Section 2. This portion of the project area encompasses 14 archaeological sites. In addition to these sites, eight isolated objects were f.ound and recorded. Site SDM-W-915. This site is situated at the southeast corner of the subject property. It was initially f-13 0 0 1 0 I I 0 I • Q I I 0 I recorded QY Kaldenberg during his survey of La Costa (1976). At that time he noted'"highly patinated felsite scrapers and flakes, basalt debitage and one broken blade fragment" (Kal- denberg 1976). ·ae also presents a Carbon·14 date of 6880:: 280 B.P. (Before Present) cu·cR-434) for shellfish remains collected from the site. . __ The site is located in the Northwest Quarter of the Southeast Quarter of s·ection 19, Township 12 South, • Range 3 West, San Bernardino Base Meridian. It is at a mini- m~~ elevation of 500 feet above Mean Sea Level and covers an area of approximately 4,000 square meters. A profile of the southern extent of the site, revealed by borrowing activities, indicates a minimum depth of 35 -~entimeters. Site: SDM-W-1078. This site is a light shell scatter, located at the southwestern extent of· Section 2. The site is located in the Northwest Quarter of the Southwest Quarter of Section 19, Township 12 South, Range 3·west, San Bernardin.a Base Meridian. It covers about 2,000 square meters and lies· at a minimum elevation of 430 feet above Mean Sea Level. In addition to Chione sp., Ae~pecten sp . and Ostrea, six small flakes were also found. the shell and artifact concentration are light, it is apparent that use cf· this site area wa·s quite temporary. . • Site: SDM-W-1079. Located on the southern extent of. the subject pr_operty, this site consists solely of shellfish remains. We know that it is the result of past human activity because of its minimum elevation of 490 feet, and distance from the nearest shell resource area, 2.5 miles to the southwest. The site is located in the North Half of the Southwest Quarter of Section 19, Town~hip 12 South, Range 3 West, San Bernardino Base Meridian.· It covers an area of about 182 square meters and there is no.indication of depth. Site: SDM-W-1080. This site, as was w-1079· is a very light scatter of shell. No artifacts were found in association. The site'lies at an ·elevation of 425 feet above Mean Sea Level, and covers an area 65 square meters. The wide dispersion ·of the shell fragments makes boundaries difficult to determine, h~wever. • The site falls within the Northeast Quarter of the Southwest Quarter of Section 19, Township 12 South, Range 3 West, San Bernardino Base Meridian. f-14 0 Site: • SDM-W-1081. SDM-W-1081 is located 0 on a finger of land which extends into the subject property from the southeast. It has a minimum elevation of 475 feet and lies within the Northwest Quarter of the Southeast Quarter of Section 19, Township 12 South, Range 3 West, San Bernardino Base Meridian. The site covers an area 460 square meters and consists of four flakes, two pieces of debitage and a very light scatter of shell. There is no soil discoloration and no evidence of a subsurface component. 0 Site: SDM-W-1082. This site is an historia 0 cross set in a plastered adobe base. • The cross sets atop·a hill overlooking the Rancho de Las Quistes, and would appar- ent1y date from that period. A quick check of the historical records failed to reveal any specific reference to the cro,ss. Structural 0 fe·atures, such as milled wooden components, nuts and bo1lts, and "recent appearing" plaster would tend to indicate associa- tion with the Carrillo use of the area (1938ff) rather than • the earlier Kelly occupation in 1870. . Site: SDM-W-1083 .. Located at an. elevation of about 425 feet above Mean Sea Level, this site covers a surface area 700 square meters. Six· artifacts were found along with a .. sca-:t.ter of shell. 0 The site falls within the Southwest Quarter of the Northeast Quarter of Section 19, T9wnship 12 South, 0 Range 3 West~ San Bernardino Base Meridian. Artifacts identified at this site include two flakes, three pieces of debitage and a biface (knife) frag- ment. As with other light shell scatter·s, this site is appar-0 ently a temporary use .-_,;lrea. • The actual place of _the· site within the lifeways of the inhabitants must involve·an analysis o:£ sites throughout·the Batiquitos Lagoon Region, and Southern California area. ·The general area of the site has been subject to a high degree of disturbance. A road ·cut exists along the southern edge of the·site, while brushing and clearing seems to have occurred throughout the area. This, combined with an apparent lack of depth, limits the research pc:,tential of this site. f-15 0 0 0 cl Site: SDM-W-1084. This site is located in the Northwest Quarter of the Northeast Quarter of Section 19, Township 12 South, Range 3 West, San. Bernardino Base Meridian. It lies at an approximate elevation of 325 feet above Mean Sea Level, and covers an area about 1,700 square meters .. The site is apparently a quarry area, con- sisting of several flakes, cores and at least one tool. The materials present here range greatly in fracturing quality, a prime consideration in lithic technology. There is no midden at the site and no indi- cation .of a subsurface component. Site: SDM-W-1085. This site lies at the northern extent of a small side-wash which empties into the main central valley. It is in the South Half of the Southwest Quarter of Section 18, Township 12 South, Range 3 West, San Bernardino Base Meridian. It has a minimum elevation of 330 ,feet and covers a small" area of 100 square meters . . The cultural material identified·at the site includes two flakes and a single scraper. This either repre- sents a very limited use or a secondary deposition. Either is possible as the site is situated between two stream cuts and below an area near a recorded archaeological site. Site: SDM-W-1086. This site is the most sub- stantial prehistoric archaeological resource on the subject property. It is located on a small knoll overlooking Carrillo Ranch, and lies at an elevation of about 245 feet above Mean Sea Level. . Its location can .be . described as _being wi.thin the Northeast Quarter of the Northwest Quarter of Section 19, Township 12 South, Range 3 West, San Bernardino Base Meridian. The site covers an area of 2,000 square meters with an estimated depth of midden of 40 centimeters. A wide variety 0£ lithic artifacts were identified on the site includ- ing scrapers, hammerstones, manes, both secondary and primary flakes and cores. Moderate amounts of shell primarily Aeau5pec- ten and Chione were also found at this site. - The site is interestingly, limited to·the knoll, and does not extend.up a small ridge to the north. In an at- tempt to delineate tile horizontal extent of midden, soil sam- ples were.taken from the site and adjoining are~ and tested for pH and orthophosphate. Table 2 indicates the results of this•test. f-16 TABLE 2 PH and Orthophosphates at SDM-W-1086 0 PH PO43 On W-1086 s.o 106.l Off W-1086 s-~ o ·s.o 0 f-17 'O : J I 0 I J I °d d } ii 0 !I cj Site: SDM-W-1087. This prehistoric site is located on the side of a large s9uth·sloping hill at an elevation of 2as--feet. • No artifacts were discovered,.but the presence of shell ;ndicate~ human activity. As the ground cover was to.heavy to allow for a good evaluation .of the amount. of shell,· present estimates as to the concentration of . the -resource must be;· heid in abeyanc~. • • • • The site is -·located in •• the West Half of the Northwest Quarter of Section. 19, Township 12 South, Rang:e 3 West, San Bernardino Base Meridian. Site: .-SDM-W-l.088 :, .-This is .also a "·shell only"· site located on-.the side -_of the same hill which sup- ports W~l087 .. It falls within the West Half -0f the N9rthwest Quarter of Section 19, ·Township 12 S9uth, Range·3 West, San Bernardino Base Meridian, at an elevation of approximately 300 feet above Mean S_ea Level. Although the shell. s·caiter at this site is light, the resource. takes on adqed ·significance because.of the occurrence of bean clam. • This discovery· -of the· beach shell makes this a_ ~nique _resource. Site: SDM-W-1089. · This site covers a sur- face area of _a.bout 300 -~quare meters. It lies on a steep slope of a large south-facing hill immediately above the central valley. It fa-J.ls within .the Southeast Quarter of the ~ortheast Quarte:. of Section ·24, Township 12 South, .Range .4 West, San Bernardino Base Meridian, at an elevation of about 190 f~et above Mean .Sea Level. This area is markedly more substantial than the majority of the_· Ran_cho Carriilo resources with 20 flakes and debitage_ and a wide v~ri_ety of shell-being identified.a.• __ There is a_possibility that this site has .a culture-bearing overburden, and thus has markedly greater research potential tha~t the neighboring simple surface scatters. Site: SDM-W-1090. This site lies on the -:;outh side of the-central valley, on the eastern slope of a north-trending finger of land. It falls within the Southwest Quarter of ~he _Northwest Quarter of Section 19, Township 12 South, Range 3· West .. The site covers an estimated area 100 square meters, with a mean elevation of 225 feet. location. dent. ·Twenty flakes/debitage were 'found at this No midden or cultural-bearing over~urden i~ evi- f-18 Rancho, de los Quiotes (Carrillo, Ranch). ·.·.In addition to the numerous prehistoric resources scattered thrqU:ghoU:t this portion of· Rancho Carrillo, an extensive his- toric area also exists~ This· h:i.storic·, resource • is the remains of·.~· restored early California rancho;' ·Rancho de ios Quiotes (Ranch of the Daggers)~· The rancho: is located in the· central por.ti~n qf t~e property and consists of a main house and a varie,:ty,6f.-associated out-buildings· including a barn and guest house. • • , •• The area was initially developed by Matthew Kelly, Sr. , · in •• the 18 6 O ' s • and ·was part ·of :the Agua Hedionda Land Grant ... The house was built: as·Mr.· Kelly's, residence. After.Kelly's death,--his descendants abandoned the area"and the structures fell· into disrepair· (Anonymous 1945)_. • , In the 1930' s, Leo Carrillo purchased this and surrounding property and restored t~e old ranch structures. At-the time of purchase,-Carrillo wished to· re~create and presarve an element of Californ·ia history. ··-•• ·- Historic California is rapidly • aisappearing. On my ne~ rancho I wi-ll-try :,to re-create .a ·part of tl:Ia.t romantic period '(Tribune 1976). Leo Carri11·0 occupied the area· until his death ·in 1961. His d·aughter has lived :there since.· • 0 0 0 0 0 0 The ranch area is very well preserved and C as such, represents a fast-disappearing e_lement of our past. Isolated Finds. In addition to the: numerous archaeological sites found in this portion of the subject prop- erty, seven objects were found which could not be directly· re- lated to a specific site. C Findi ISO~ ISO II ISO III ISO' IV ISO V ISO VI ISO VII f-19 Item Mano fragment Flake 3 Pieces debitage Flake , Flake (Felsi te) Flake (Felsitef . Flake C C C I 0 .... l ol I I 0 I IJ I I d I l Section 3. Three archaeological sites have been described .in length by Kaldenberg (1975} for this area of Rancho Carrillo.· The following descriptions were obtained _di- rectly from that report. Site: SDM-W-587. This site was a surface quarry ·which covered an area of about 5, 3.12 square meters . The site was located in the Southwest Quarter of the South- west Quarter of Section 24, Township 12 South, Range 4 West, San Bernardino Base Meridian, and lies at an elevation of 330 to 394 feet above Mean .Sea Level (Kaldenberg 1975:2). A surface collection and mapping was per- formed by Kaldenberg in Jaunary of 1975. As·a result, the site no longer exists. It is preserved only in Kaldenberg's ar- chaeological report SDM-W-587, and had 651 Native-American artifacts all found on the surface. These included grinding impl=uents, flakes, cores, debitage, hammering artifacts, end- scra?ers, pushplanes and a variety of sidescrapers (Kalden- berg 1975: 58-_72) . Basalt and andesite were the lithic materials· best represented but quartzite also occurred. • In summation of this resource, Kaldenberg states: Based upon the archaeological evidence it seems that the major and perhaps only aboriginal activity which occurred at the Carrillo Estates quarry site was quar- rying and stone-tool production. The preponderant num- ber of flakes indicates that primary stone-tool produc- tion (the removal of flakes from cores) and perhaps the production of core tools occurred at the quarry site, rather than secondary retouching or refining of tools. The paucity of debitage indicates that tool re- finement must have occurred at another site within the general vicinity of Carrillo Estates and La Costa prop- erties. Due to morphological similarities with other tools lo- cated within the San Dieguito trad~tion, we infer that it was persons of that archaeological techno-complex who exploited the lithic resources contained within the subject property. Rogers states that persons of the San Dieguito tradition frequently employed andesite for the maunfacture of tools (Rogers 1958: ). The numerous recorded sites with a San Dieguito aspect near to the lithic quarry further verify the conjectur~ that the San Dieguito were the primary users of the extrusive vein of andesite (Kaldenberg 1975:74). f-20 C Site SDM-W-588. Kaldenberg described this site as a La Jolla Complex containing she~l and a few arti-c facts. The site is located in the Southeast Quarter of the Southwest Quarter of Section ·24, Township 12 South, Range 4 West,·San Bernardino Base Meridian. The majority of the site lies on property administered by the La Costa Land Company. Kaldenberg suggests that "The portion of w-c 588 located on the subject property may represent an area where aboriginal peoples (probably members of the La Jolla tech.."lo-complex) processed shellfish" (1975: 75). As with W-587, this site was also surface collected and no longer exists. c Site SDM-W-589. • This archaeological site was also an aboriginal quarry. The occurrence of 18 tools and. 48.i pieces of debitage covering an area of 3,700 square meters and without depth suggests that tool manufacture was· a primary function of this area.· O The site was located in the Northeast Quarter of the Southeast Quarter of Section 24, Township 12·south, Range 4 West, San Bernardino Base Meridian, but as it, too, was collected, it no longer exists independent of Kaldenberg's report. • O 0 0 0 0 f-21 0 cl I 0 i I 0 I I I t I 0 I E. CULTURAL SETTING As well as being set in a physical and biological environ.-rnent, a historic or prehistoric resource also exists within a cultural setting. This involves the rel·ationship between the creators of a given site and other sites, both temporally, geographically and socially. Evaluation of the cultur.al setting of a prehistoric resource is dependent upon previous archaeological research. The Rancho Carrillo sites should be assessed on the Batiquitos Lagoon Regional level as well as the Southern California area level.· Information gained during an initial survey, however, rarely results in sufficient information to allow conclusive evaluation at either level. _l. Batiquitos Lagoon Region. A major.resource area, Batiquitos Lagoon lies to the Southwest of the Rancho Carrillo area. It extends from the Pacific Ocean inland for approxi- mately 2.5 miles and has an average width of about .5 mile (Mudie, Browning and Speth (1976:16). Althoug:t:,. the l_agoon has long served as an important natural resource for man, it is at present sealed_from the sea with tidal exchange occur- ring very rarely. Mudie, Browning and Speth. (1976:18) feel that Batiquitos Lagoon was a large deep water ocean embayment until about 2,000 years ago .. After this date it became filled with river and stream silt and with marine sand. That the area is important to the occupation of past populations is evident by the large number of. prehistoric archaeological sites which occur around the· Lagoon. Warren· True and Eudey note 33 sites on the Lagoon. Recent work by Kaldenberg (1975 and 1976) indicates that at least 44 archaeo- logical sites occur in the immediate vicinity of the Lagoon. The great amount of work which ha_s been invested in examining the archaeological remains_has resulted in the development of a. Batiquitos Lagoon Region for lo.cal prehistory. The area referred to in this paper as the Batiquitos Lagoon Region lies between Latitudes 33°06'30" West and 33°04'00" north, and be- tween Longitudes 117°13'30" West and 117°19'30" West. The entire area if found within the County of San Diego, Califor- nia. Archaeological surveys have been a~complished on approxi- mately 65 percent of this area, and a total of 102 sites have been recorded. f-22 The archaeological sites which were found during the present survey expand our knowledge of this reason. Lack of. diagnostic traits at many. of the sites greatly restricts the potential of the area. With radiocarbon dates and further examination of cultural information, important understanding could be gained. C The relationship of several sites suggest some interesting possibilities. Sites SDM-W-1078, -1079, and -1080 are sir,.ple small shell scatters and may indicate temporary use areas indicative ·of small population movement. • Dates would help establish the temporal relationship of these sites G important to understanding the regularity or irregularity of activity in the area. The occurrence of only· three possible midden- bearing sites, SDM-W-1086, -1089, and -915, stigg.ests that the area was not as extensively exploited as areas closer to 0 the Lagoon .. Large sites,. such as SDM-W-149, ·w-110 and W-147 all lie about one mile closer to the Lagoon. Additional as~ sessment of functional significance of specific Rancho Carrillo resources and their relationship to other lagoon region sites is d.epe.'1dent on additional information available through in- vestigation. 0 • 2. Far Southwest Area. At the broader area level cultural association is even more·difficult. Se:veral reconstructions for this "Far Southwest area" have been proposed ·and a plethora of terms for what.are substantially like elements have been developed. In 1969, Davis et al proposed the Paleo-Indian stage and three archaic stages, while Warren (1968) proposed the Encinitas, Campbell, Chumash, Shoshonean and. Yuman traditions. In 1955,Wallace suggested four stages.of Southern California prehistory: Hori- zon I, Early Man; Horizon II, Milling Stone; Horizon III, intermediate; i.nd Horizon IV, Late Prehistoric. Each of these "horizons" represents a segment.in an historical sequellce.and as such, is a stage. All of these reconstructions permit the examina- tion of Southern California prehistory, but Wallace's repre- sents a relatively unencumbered outline which provides the best possible framework for our discussion. This is necessary, for although little critical evaluation has been accomplished of these segments, they permit the integration of a great variety of data.· f-23 0 0 0 0 0 I 0 • I c,a I .ii a 0 I cJ d • a. Early Man Stage. The earliest of the four stages identified by Wallace, the Early Man Stage, is the least represented in all of southern California. In San Diego County, the Early Man Stage is manifest by what Malcolm Rogers called the San Dieguito pattern (1938). He felt that this pattern extended from the San Pedro Valley in eastern Arizona to the Pacific Ocean and from Baja, California on the south to Orange County on the north . With a tool assemblage characteristic of a subsistence pattern based upon hunting, the material culture of the San Dieguito pattern consists of numerous types of scrapers and scraper planes, choppers, crescentics, large blades, and points. It has been divided into three main phases: San Dieguito I, San Dieguito II, and San Dieguito III with a fourth phase being tentatively identified in Baja, California (Rogers 1966}. San Dieguito I, the earliest phase of the patta:n, encompasses a tool tradition fo.und throughout San Diego and the Far Sout~west:, but has yet to be defined in pub- lication for that portion of San Diego County west of the La- guna Mountain watershed. Artifacts which characterize this phase include relatively crude stone tools consisting primarily of cho9pers and large flakes produced by percussion flaking, sleeping circles, trail shrines and varied rock alignments (Rog~rs 1966). The second phase, San Dieguito II, is the first to be identified west of the Laguna Mountains watershed. Rogers recorded 52 sites in the county containing cultural -material representative_of this phase (Rogers 1966:178-184). Though the dating of this phase is not explicit, its introduc- tion has been estimated at about 12,000 years B.P. (Before Present). The tool assemblage is characterized by improved flaking techniques and better types of tool materials, which result in more standardized and predictable tool types, and the absence of association with sleeping circles (Rogers 1966: 60) • Artifact assemblages reportedly representative of the third phase of the San Dieguito pattern, San Dieguito III, have been identified throughout San Diego County and prob- ably persisted until 8,500 or 7,500 years B.P. (Warren and True 1961:263). • The basic difference between this phase and the previous one is the appearance of pressure flaking and the increase in the use of more fine-grained lithic materials such as chalcedony, chert and jasper. f-24 With a marked lack of absolute dating, it is impossible to determine whether all three of these phases are, in fact, temporally distinct, or simply regional manifestations of similar tool assemblages. The broad geographic distribu- tion of materials assigned to this pattern combines with the lack of absolute dates and stratified, dual component deposits to caution the archaeologist against inferring a genetic rela- tionship between the people who established each of these di- verse archaeological assemblages. One of the few San Diego County archaeological sites with subsurface materials of the San Dieguito phase is the Harris Site (SDM-W-198). This site (Warren 1966) has no stratigraphic evidence delineating the phases of the pattern as discussed above, but does have a Milling Stone Stage com- pone~t overlying-the San Dieguito component. This superposi- tion of a datable milling element allows for the application of a minimum date for the San Dieguito pattern. Dates of be- ~~een 7,000 and 8,000 B.P., which were presented by Warren (196.7) for this milling component, thus provide a minimum date for the underlying San Dieguito III strata. Recently Kaldenberg and Bull have noted the L~clusion of limited amounts of milling activity within the later portions of the San Dieguito III phase (Kaldenberg and Bull 1975:111).· Although this has yet to be demonstrated conclu~ively, it suggests two interesting possibilities. Either there is evidence for a continum from the San Dieguito pattern of the Early Man Stage to the appropriate pa~tern of the Milling Stone Stage, or the temporal placement of the San Dieguito pattern as temporally distinct from Milling Stone Stage patterns is· incorrect. We will examine both of these possibilities later. . . One criteriurn which has emerged for the iden- tificat'ion of San Dieguito pattern sites is the occurrence of highly patinated flaked lithic artifacts. Sidescr.apers, flakes, blades and knives which have a "high" degree of.patination have traditionally been assessed as being of San Dieguito origin._ Because there has be~n no \qork done de.inonstrat~.ng conclusively that patination must be a slow continuous process, this argu- ment does not hold. Future work needs to be done assessing the occurrence of patinated artifacts with demonstra~ility more recent material such as milling, ceramics and cremation. . b. Milling Stone Stage. Following the Early Man s·tage, Wallace identified a period in which subsistence was based primarily upon gathering. Labeled the Milling Stone Stage, this element is represented throughout the coastal re- gion of Southern Californi~ by a variety of cultural patterns. f-25 C C 0 0 0 .o 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 These oatterns stretch from below the Mexican border to north of Santa Barbara, and exhibit numerous similar manifestations. They all possessed crude chopping and scraping tools, practiced inhumation and subsisted primarily on vegetal and sea food re- sources, as evidenced by the profuse number of grinding imple- ments. In San Diego County, archaeologists have iden- tified the La Jolla pattern as-belonging to the Milling Stone Stage. This pattern was first recognized by Malcolm Rogers in 1929, when he identified them as the "shell midden people." He delineated this pattern as being'characterized by numerous shell middens containing metates, manes, hammerstones and tes- hoa flakes, with a noticeable lack of flaked stone implements and ceramics. Further research of this pattern has resulted in an expanded list of criteria for its delineation which in- cludes a material assemblage of Olivella beads, retouched flakes, flexed burials and an economic subsistence based.on the collection of seeds and shellfish. Rogers gave.the-pattern its present name and at the same time divided it into two phases, La··Jolla ·I and La Jolla II (Rogers 1945:171). Moriarty described the La Jolla I phase-as having ... "crude flat surfaced milling slabs and shallow basined metates accompanied by both unifacial and bi- facial rnanos-. The artifact. assemblage is· based on a rather crude cobblestone, chopper-scraper typology, all of which are percussive" (Moriarty 1966:21) .. La Jolla II is distinguished by the appear- ance of drilled and polished stone implements. .There is a marked increase in the variety of bifaced artifacts and a development of more refined tools (Moriarty 1966:19). Moriarty also proposed another phase of the La. Jolla pattern, La Jolla III. This phase is distinguished from the previous·two phases solely by a change in the geo- graphical location of. the sites. As the peoples represented by thee La Jolla pattern developed, environmental stress made it necessary for them to move inland away from the coastal la- goons which-were constantly decreasing in their productivity (Moriarty 1966:19). • The La Jolla pattern has been delineated for an area extending from south of San Diego to the.San Diego - Riverside County linecin the north, and from the Pacific Ocean to approximately four miles inland. It.has been dated by radiocarbon from as early as 7,370=100 to as late as 3,700: 250 B.P. (Hubbs, Bien and Suess 1960}'. Warren places the span of time encompassed by the La Jolla pattern at from about 7,500 to 1,950 B.P. (Warren 1968:2.). This more recent date f-26 of 2,000 B.P. is further substantiated by dates recovered by P.H. Ezell at the Las Flores site. Here-Ezell· dated-shell remains in conjunction with. inhu."llations at 1,600 B.P. (Ezell 1975:57). This date was later revised to approximately 2,000 B.P. (Bull 1975:70). We can, then, assign a time span of ap- . proximately-6,000 years, from 8,000 to 2,000 B.P. for ·the _es- tablishment and existence of La Jolla .pattern Milling Stone Stage sites. • -It has been noted in several sources that the termination of the La Jolla pattern-corresponded to .a gradual reduction of shellfish resources available from the coastal lagoons of San Diego County. Shumway,· Hubbs and Moriarty (1961) have presented evidence for a markedly different phy- siographic condition for the coastal area of San Diego County during the Milling Stone Stage. By examining the types and amount of shell which occur at La Jolla sites, ·they conclude that" ... during the period from 7,300 years ago or earlier, until at least 3,700 years ago,· the shore north of La Jolla was considerably more rocky than at present'with estuaries sufficiently deep and in sufficient contact with the·· sea to maintain, in bay-like conditions, flourishing populations of pectsn a:id Chione. These conditions would be met by a rapidly risin; sea level during which the accumulation of shore sand would be kept low ... " (Shumway, Hubbs and Moriarty 1961:113). Shtu~way, et· al (1961) feel that San Diego County lagoons sup~ ported sizeable amounts of shell until ~bout 1,000 years ago. Warran, True and Eudey hypothesize that the termination.of the La Jolla pattern corresponded with an en- vironmental shift on the Southern California coast. In research undertaken around Batiquitos Lagoon, archaeologists propose the gradual reduction of accessible shell.• food resources and the subsequent abandonment of the coastal region. _Warren, et al propose that at about 2,050 B.C., the coastal lagoons of San Diego County were silted in sufficiently to reduce the quantities of available shellfish· (Warren, True and Eudey 1961). "Approximately 4,000 years ago, lagoons were silted in enough to reduce the number of shellfish available to prehistoric populations of the area." (warren, ·True and Eudey 1961: 25.) This shift is further documented by dates recently obtained at Green Valley Knolls with the dating of a marked decline in the occurrence of shellfish remains. at 3,300 B.P. (Kaldenberg and Hatl~y 1976) .. Warren and Pavasic propose that silts transported by streams covered any rocky shores that existed in the lagoons. C C C C 0 , . i 'o ,0 It i f ' ( i i 0 I i to r : ------------------~•,,.,,, .. ,·, .. 0 d I 0 I nThe rock dwelling shellfish decreased in number and were repla~ed by those dwelling on the sandy bea- ches and mud flats." (Warren.and Pavesic 1961:424.) 1 Warr~n-, True and Eudey (1961) suggest that this movement of the La Jolla peoples·may have resulted in the establishment of. the nPauma Complex." ':t'he Pauma variant is characterized by flaked stone implements much like those of the San Dieguito pattern, but,unlike the San Dieguito pat- tern, the Pauma variant has a high number of grinding imple- ments. This would indicate an association with a milling tradition (True 1958). The possibility exists that the Pauma variant is related to. _those assembiages which Wallace refers to as Intermediate patterns. If so, it would ·provide evidence for the existence of a hunting-like pattern in San Diego. This.will be examined further in a subsequent discussion of the hunting pa'j:tern. North of San Diego County, ' a number of ·ar- chaeological maµifes-t;ations similar to the .La Jolla have bean. reported. Perhaps the most extensive of these make.up the patter.n known as .11oak. Grove.°'' Initially identified by David Banks. Rogers, the Oak Grove· ·pattern is defined by the occur- rence of metates, manes and large flint flakes that have been roughly retouched (Rogers 1929: 352-353) . .This pattern has been expend·ed to include. crude projectile points, a reliance on gathe.ring of seeds· and a burial of inhumation. • . The pattern has been dated by carbon 14 at several Southern· California sites. ·At the Glen Annie Canyon Site, Owens presents dates which range from 6,380=120 to ·7,270±120 years ago. A date of 3,000 B.P .. was obtained from a site at Zuma Creek {Bright 1965:370), while materials from the World Medical Center were dated at 2;000 B.P. (Kaldenberg and Bull 1975). Archaeologists do not propose an end to the peoples of the Oak Grove, pattern~ rather, they suggest a con- tinual occupation of the coast· by two basic tool traditions. The Oak Grove p~ttern represents the milling tradition, with .the Hunting pattern being iµtroduced into the record around 5,000 B.P. (Harrison and_ Harrison 1966:34), and representing a hunting tradition. The Hunting pattern will be discussed in more--detail at a later time. It is important to note here that some individuals believe that an amalgamation of these groups developed into the more recent Canalino a~i thus the Chumash which were the historically recorded native pop~la- tion of the Santa Barbara area. - f-28 Between San Diego and Santa Barbara Counties, the Milling Stqne Stage is represente_d by a number of sites which share numerous traits, The Little Sycamore Site {Wal- lace 195_4) , Glen ~nie Canyon (Owen, Curtis and Miller 1964) , the Browne Site {Greenwood 1969), Topanga Canyon (Treganza and Bierman 1958), Malaga Cove L~ve1:2 (Walker 1952) and Zuma Creek (Peck 1955) all have characteristics which would allow their placement wi~hirt the Milling Stone Stage. Invariably. the burial pattern is one of inhumation·, subsistence·· is based on the g~thering of foods rather than hunting·, and all have a relatively high quantity of grinding implements. • ~ , ' Warren combines the sites of the Milling Stone Stage within.what he.terms the "Encinitas Tradition" {Warren 1968). Warren defines 'this tradition as a "well de- veloped collection economy" (Warren 1968:6), which.is oriented toward the collection of piny~n, pine cones, and hollyhock, as well.as a wide variety of shellfish. He proposes-an end to the tradition at about l A.D. ---in San 'Diego County and between 3,000 and l, 500 • B.c·. in Santa Barbara County. . . The final determination of the end.of the Mill- ing Stone Stage is dependent· upon the relationship·-of the pat- terns of that ·stage to patterns. which have been found to be more racent. In Wallace's discussion·of Southern-California prehistory, he; ·delinea~ed a· third group of artifact inventor- ies whi:=h ·he referred to as the "Intermediate Cultures" {Wal- lace 1955~221). When he defined this period, he included the nw--iting people of Santa· .Barbara, the San Dune Site of Ventura County, the Big Tujunga Wash site in the San Fernando Valley and the second phase of ·the La Jolla pattern,· La Jolla II,. in San Diego County. The San Diego aspect of this stagewas.not, however, consistent with the other patterns throughout Southern C~lifornia. ·_ Excluding San Diego County, the major cul tura1· :change during this period aside f rem an increased dependence upon hunting,·was the shift in grinding implements from the milling· and hand~stone combination to the mortar-pestle, though the former continued in use on· a red~=ed scale_ (Wallace 1955 :222). Because radiocarbon did not maintain the tem- poral distinctiveness of these patterns--from those of the.Mill- ing Stone Stage, the "Intermediate" is not presented as a sep- arate ·stage. Patterns which:have assemblages similar· to those which Wallace. included within his Intermediate· stage must be dealt with as contemporaneous with Milling Stone patterns. f-29 :J•' ,L ·:p,-,c iL C ~ f"·': ~ ·o fr~ ~ r 0 "I": .o f 0 0 0 0 0 0 0 • I 1 • I l 0 I Ii ) - I if I --------------- Their differences; then, do not reflect change over time, but rather cultural variation within~ given location. Perhaps the most characteristic pattern of this variant .is the Hunting pattern _of ·the Santa Barb_ara area. This pattern was initially described by D. B. Rogers as con- sisting primarily of _.flakecl li thic implements with the intro- duction of· the basket mortar. • Spear and knife blades are des- cribed as being large, usually lea:c-shaped, and· without stem or notches. ~rojectile po•ints are, as a whole, heavy, broad, and -wickedly barbed. • The materials of which they are made vary. greatly _and include quartz, chert, ·chalcedony and obsidian (Rogers 1929). There is a noticeable increase in .the amount of bone at Hunting sites as compared with those of the·oak • Grove patter_n for ·the same area~ • Rc:>gers mentions great quan- tities-of. shell£ ish, .a noticeable lac~ of whale remains, small to medium sandstone bowls, .massive shell and stone beads, red ochre _and asphaltum making up the distinguishing characteris- tics of this pattern. Harrison and·Harrison (1966),· include whale bone-as a Hunting.pattern cultural element. . • ·-' - . Th~ most complete assessment of the Hunting pattern resulted from the investigation of·Aerophysics •site. (SBA-53). Harrison and Harrison propose· the delineation of two phases for the Hunting pattern: the Extranos Phase and the Del Mar Phase· (Harrison and Harr~son 1966). Diagnostic characteristic~ of the earlie.r ·Extranos Phase include: ll Equal pr·oportions cf. milling stones and mullers, _ compared to_'. stone vessels and . pes-:tles. ·.: • • ' ·· • • · • · 2) Large sid.e-notch~d_ ·and stemmed projec- tile points and· bl~des. • 3) The·use 'of asphalt restricted·to mending stone vessels .. 4) Fully" "flexed burials '( f reguent.ly on the ---back. . .-.. 5)_ • Use of scrap,3r. blades. 6), Emphasis on sea and large land mammals, . the larger species of fish, and large var~etie~ of s~ellfish. o·iagnostic trai t_s· which· s_et the more recent Del Mar Phase from. the_ . Extranos ~re: • " _Basket mortars and pestles. 2) -Asphalt_ for ·basket _mortars and for haft~ ing points and blades. 3) Shell .and stone. bea4s. f-30 4) Fully flexed burials (face down). 5) Abalone dishes. 6") Red -.ochre in graves-. 7) Occasionally an exte_nded burial. _ Warren (1968) reassociates the sites and pat-, terns of Wallace's Intermediate stage, and 'by usin_g the Hunt- ing pattern of Santa Barbara to characterize this element, he proposes the establishment of the'"Campbell Tradition." This Tradition is identified for .areas _of Santa Barbara, Ventura--. and Los Angeles Counties with only a brief,: poorly represented • intrusion into San Diego, _County .. The· Campbell Tradition is characterized by a tool assemblage consisting of f-inely worked knives and points,. • the introduction of _t~e µiortar and pestle, and, the movement_away from re~iance. on gathered vegetable· and shellfish resources toward an increased dependence on hunting .. Warren felt that this tradition was not evident in. San Diego County except for one ptjssible exception at.Locus II of the Harris Site (SDM-W-198). He proposed the .continual occupation of the San Diego Coast._ by Milling Stone Stage peoples until the onset of. th.e Late Prehis·toric • Stage with l±ttle or no no- ticeable in:terruption,. • • • Warren· dates the Campbell Tradition at from 4980 years ago (Warren ·1968:3) until the-'onset of the Late Pre- historic and the'emergence of the·Chumash. This• date is fur"'.:" ther substantiated by radiocar~on measurements of 2940 and 2670.B.C. taken.on shell_samples·by Harrison-and Harrison (1966:34). These dates are significant in that they place the Campbell Tradition in the Santa Barbara area at the same time as the Oak Grove-pattern of the Milling Stone Stage. Al- though they admit to the contemporaneity of these two patterns, they feei that the patterns represent two distinct popuiations with two di:stinct cultural heritages. ___ rn summary, then, contemporaneity between these-·two phases is substantiated by radio- carbon dates. Comparison between their re- spective cultural inventories reveal sig- nificant cultural eifferences. Seasonal occupations as a cause of these distinc- tions are ruled.out because both phases share a common ·phy·s'ical· environment, and because they possess completely different and .mutually exclusive.burial patterns. The con6lusion seems inescapable--these phases represent c~lturally variant socie- ties existing side by sid_e • in the same ar- chaeological region (Harrison and Harrison 1966:69). f-31 .. ·,~ 'i i C ![ 1[ [fo [C r :~:r ;•o I 0 I I The mutual· exclusivity of burial patterns mentioned above seems somewhat indefe~sible, both patterns exhibiting flexed inhumations. Also, the sharing of a com- mon environment is questionable as acceptable criteria in that a number of sites have been excavated with limited amounts of material assigned to both patterns, i.e., Zuma Creek (Peck 1955) and Topanga Canyon (Johnson 1966). Without further evidence, it is difficult to state conclusively that the Encinitas Tradition and the Campbel.l Tradition, more specifically the Hunting-pattern and the Oak Grove pattern, are distinct cultural groups. This is complicated by the lack of Campbell Tradi.tion ele:i.nents in San Diego County. Warren. points out certain changes in San Di- ego assemblages at about 3,000 B.C. "Projectile points occur more regularly, but are still rare and mortars and pestles occur for the first time though few in number" (Warren 1968:3). With the discovery of the "Pauma Complex" (True 1958) and the 'increasing inclusion. of milling into typically hunti.ng assem- blages (Kaldenberg and Bull 1975) as well as within Locus II of the Harris Site (Warren 1966), the possibility that a pat- tern quite .similar to the Hunting pattern does exist in San Diego County. If there is an equivalent pattern in San Diego, the possibility that the Campbell:Tradition and the Encinitas Tradition are both manifestations of the same cultural group is increased. c. Late Prehistoric. Three Late Prehistoric Stage patterns have been suggested for the San Diego area: the Cuyamaca pattern, the Yuman pattern and the .San Luis Rey pattern. C. W. Meighan (1954) identified a pattern of the Late Prehistoric Stage for the north portion of San Diego County. The San Luis Rey I and II ·variants of the San Luis Rey pattern are presented by Meighan as representing the re- mains of direct ancestors of the historically recorded occu- pants of the area. San Luis Rey I is characterized by bed- rock and slab metates, small oval manos, either bifacial or unifacial, bedrock mortars with a rare cylindrical pestle, small triangular projectile points, usually with a concave base and straight sides, stone pendants, Olivella disc and spire-lopped beads and quartz crystals. The second phase of this pattern includes all of the above traits with -the.inclu- s_ion of ceramic vessels, tubular pipes, cremation urns, red and black pictographs, historic artifacts, and grooved stea-· tite arrow straighteners. f-32 The extent of this pattern is not yet known. Several sites have been identified as San Luis Rey II with only the type site excavated by Meighan. fitting.the defini- tions for San Luis Rey I. Presently there are no available absolute dates for these San Luis Rey II sites~ The fact that some have historic artifacts indicates that they were occupied into contact times, circa 1770. Dates, however, are available for other Late Prehistoric patterns and-through association we may be able to assess the establishment of this pattern. Another Late Prehistoric.Stage pattern, the Yuman pattern, was defined by M. Rogers (1945) as a Late Pre- historic ceramic culture which expanded from the Colorado River westward approximately 1,000 years ago. The pattern was divided into three phases, Yuman I, Yuman II and Yuman III, only the last of which was thought to have penetrated into ·San Diego County (Figure 3).. Rogers proposes a Southern California origin for his Yuman pattern as evidenced by the similarities between La Jolla II and Yuman III. He admits, however, that there is no absolute connection between the two patterns (Rogers 1945: 171). He maintains an easterly movement of Yuman populations from the Pacific. l:ittoral· to the Colorado River Valley and a r.a--expansion of those people-after they have adopted cer- tain culture traits common to that area. The distinctions drawn by Rogers between the three phases of the Yuman pattern were based primarily on ceramic details, but Yuman II and III are generally richer in deposit than the earlier Yuman·I. All phases of the pattern have metates, manes, beads and pendants, ceramics, cobble chop- pers, flake scrapers, gravel pictographs, trail shrines, and petroglyphs. Rogers also mentions a noticeable lack of lithic projectile points, with. the latter two phases having bedrock mortars, circular clay--walled hearths, and disposal of the dead by cremation. (Rogers 1945). 'l:he final phase of the Yuman pattern, Yuman III, purportedly represents the introduction of ceramic mater- ials into San Diego County. The beginning of the Yuman III period is marked by several population shifts, some of which must have been of considerable magnitude and rather abrupt in nature (Rogers 1945:192). It is this third phase as proposed by Rogers which-would represent the archaeological remnants .of the ancestors of the historical inhabitants of the southern portion of San Diego County. r : t... JC -l ir I ~-·~O Ir! I ~Z [C 0 I □ 0 I fI 0 0 0 0 0 0 0 0 0 0 13· b 0 -"" -C') 0 50 IOOm,: Figure 3 -This. figure indicates tpe boundariE?s of maximum areas of Yuman I (dotted line), Yuman II (dot and dash line), and Yurnan III (dash line) (Rogers 1945). C The final significant Late Prehistoric pat-C tern in the San Diego area is the "Cuyamaca Complex" proposed by D. L. True (1970). Through his work in the Cuyamaca Rancho State Park, he differentiated this pattern from the previously defined San Luis Rey pattern by listing the following criteria evident within the former but not the latter. 1) Defined cemetery areas apart from living areas. 2) Use of grave markers. 3) Cremations placed in urns. 4) Use of specially-made mortuary-offerings such as miniature vessels, miniature shaft straighteners, elaborate projectile points, etc. 5) Cultural preference for side-notched pro- jectile points. 6) Substantial numbers of scrapers, scraper planes, etc., in inventory contrast to _small numbers in San Luis Rey area on this time plane. • . .. 7) Emphasis and stress placed on the use of· ceramics. Wide range of forms.and several specialized ceramic items such as rattles, bow pipes, effigy forms, etc. 8) Steatite industry. 9) Substantially higher frequency of mill- ing-stone elements when compared to San Luis Rey. 10) Clay-lined hearths (Truel970:53-54). The geographical extent of the Cuyamaca pat- tern has not been determined. This is due in part to the .. lack of archaeological investigation subsequent to its identi- fication. Local prehistorians have, generally, tended to approach the Late Prehistoric Stage as though it inherently represents the direct ancestral remains of ethnographically recorded populations~ • In this light, Warren proposes three "tradi- tions" within the Late Pr-ehistoric Stage. These traditions correspond to the three major linguistic groups of the area~ "Chumash, Shoshonean and Yuman" (Warren 1968:1). He presents the Chumash material culture as being highly developed tech- nologically. Among the artifacts characteristic of this pattern, Warren lists: bowls, mortars, pestles, stone balls, grooved stones, doughnut-shaped stones, stone beads, pendants, pipes, tubes, effigies of mammals, stylized objects, chipped stone f-35 C 0 0 [ C I I 0 0 i. 0 I 0 I J I I Q • I !O I I 0 I J I I l I 0 J artifacts including large and small projectile points, drills, scrapers, and a variety of shell and bone artifacts (Warren 1968:3-5). The burials of this group are usually flexed, face down, with· their heads ori~nted either west or north. They are usually located in cemeteries and are frequently marked by whale bone (Warren 1968:5). The Chumash are spread over an area of Santa Barbara, Ventura and portions of .Los Angeles Counties. This "Chu.1nash Tradition" was dealt with by o. B. Rogers as the Canalino culture (1929). It was divided into three develop- me,.,,tal phases and "was the most elaborate of the late coastal manifestations and marks the peak of California Indian cul- ture" (Wallace 1955:224). Areas to the south of the Chumash we.re oc-- cupied by what Warren calls the Shoshonean and Yuman tradi- tions. He relates these traditions with the Cuyamaca and San Luis Rey patterns, respectively. The relation.ship, however, is highly speculative and a.great deal of work is needed to eit.~er substantiate or disprove such claims. The exact relationship between these archaeo- logical patterns and ethnographically recorded populations has not, to date, been determined. Meighan feels that the re- lationship of his San Luis Rey pattern and the historically recorded Luiseno is obvious and will, no doubt, be concretely established. Rogers' entire hypothesi~ is based on the as- sumption that a correlation between archaeological manifesta- tions and ethnographically recorded peoples is justified. McGowan (1955) has made an attempt to associate Temeku with the recorded·Luiseno. That a relationship.between archaeologically obtained evidence and historic, etjlnographically obtained in- formation can lead to valuable understanding of the archaeo- logical record is not in question. The connection of entire archaeological patterns with historically known groups, how- ever, is a risky business and should be approached cautiously. d. Summary. We have been dealing with a myriad of archaeological constructions of a relatively uniform set of data. The work of numerous individuals have resulted in a variety of terms for substantially like elements. Figures 4 and 5 indicate the relationship of several prehistoric constructions proposed for the Pacific littoral of Southern .California. These can be,summarized to allow for a relatively complete picture of archaeologically recorded prehistory. San Diego Los Angeles Ventura Santa Barbara I Diegueno Canalino Canalino Canalino I -Malaga Cove IV II 2,000 La Jolla II Big Tujunga III Sand Dune ./ Hunting - La Jolla I· Malaga Cove II Little Syca-Oak Cove -more -. --Dieguito Malaga Cove I San La Brea 6,00(' -Los Angeles Man· --. 9,000 .. The cultural developmental scheme proposed by Wallace (1955) San Diego Los Angeles Ventura .Santa Barbara Diegueno Shosho-Ch_umash Chumash -nean Early Yuman Malaga Cove III Early Canalino Early Canalinc 2,000 - La Jolla II - La Jolla I - 6,000 - - -· San Dieguito Big· Tujunga Zuma Creek Malaga Cove II Topanga II Topanga I Malaga Cove I? l Little Syca- more Hunting Oa}c Cove 9,0001---------....... -----------------------------1 The cultural developmental scheme proposed by Treganza and Bierman (1955) Figure 4 C C C 0 0 .0 0 0 0 0 0 0 0 0 0 0 0 0 .0 0 0 I 0 2,00( 6,00C 9,000 2,00 6,00 I San Diego Los Angeles Ventui::a Santa Barbara Yuman Shoshonean Chumash Chumash -., ------------. -I C a m. P b e .1 1 T r a d-i t i 0 n ' -' I ---------------------E n C i n i t a s Traditicn --E n C ·i n ; t a s T r a d i t i 0 n --------I . ' San Die-' -guito ' ' The cultural developmental .scheme proposed by. Warren (1968) San Diego Los Angeles San Luis Re Malaga Cove IV ~\ \ Malaga Cove III \,\\~\ \ ~O!.LA 0 Malaga Cove II .\ \ \\ \\',, \ \\' \ \ \ \ \ \ \, Malaga Cove I ------- Transitional San Diegui to Ventura Toi:,anga III 'I'opanga II Topanga I Santa Barbara -Canalino Hunting OAK GROVE 9,00r--------_..;;.._ _______ _;_..;... ______ ....:.... _______ _J The cultural developmental scheme proposed by Kowta (1969) Figure 5 We have proposed a developmental design for local.prehistory which includes three ·basic stages of develop- ment. The first of these, the Early Man Stage, has not been identified north of San Diego County. The actual existence of a distinct Early Mart Stage in San Diego County has been brought into question by the discovery of milling elements ·at Rancho Del Dios (Kaldenberg and Bull 1975) and the noted occurrence of a milling element at the Harris site (Warren 1966), both of which have "typical" San Dieguito III materi- als. This stage has been temporally assessed as having originated sometime prior to 10,000 years ago and per- sisting in the desert areas, and perhaps on the coast of San Diego County until approximately 8,000 years ago. Following the Early Man Stage, archa~ologists have defined the Milling Stone Stage, a period in which there appeared an increased dependence on gathering. . It spans a broad range of time encompassing at least 6,000 years from .about 8,000 to 2,000 B.P. During this same time period,.a pattern emerged in the Santa Barbara-Los Angeles area which is marked by a tool kit indicating extensive hunting activity. This hunting element has yet to be identified for San Diego County, but t.'i-iere is a possibility that the Pauma pattern represents the San Diego expression of this pattern. The Late Prehis~:oric Stage is the f.inal peri- od of prehistory for Southern California. Evidence seems to indi_cate that archaeological remains identified with this stage represent the direct ancestral remains of historically recorded Native Americans. Several patterns have been pro- posed for assemblages of Late Prehistoric· Stage. San Luis Rey I and II, Cuya.maca, and Yuman I, II, and III are all found in San Diego County, with the Canalino (Chumash) representing this stage on the Southern California coast north of Orange County. e. Problems. Several problems are evident with the prehistoric framework developed for Southern California in general, and San Diego County in particular. By adequately delineating these problems, a great deal of the presently su- pervenient r·esults of the public archaeological process can be predicted~ San Diego County archaeology needs revaluation on two levels: the developmental level and the structural level. Although both aspects are coordinated, they are dealt with here as distinct entities to allow simplified evaluation. f-39 C C C C C 0 C ,, '• ' 0 0 0 0 I ~ !I ca The "structural" aspect of the prehistoric framework refers here to the nature and· relative position of prehistoric archaeologically defined components. The nature of the artifact assemblage, absolute temporal assessment and other inferred cultural elements constitute the structural aspect· of the archaeological rec.ord .. The "developmental" aspect, on the other • hand, refers to the activities of the-people involved in the creation and maintenance of the structural elements.· Migra- tions, seasonal _exploitation cycles, and other developmental cultural elements const~tute the developmental aspect . . Structural. The structural problems of San Diego County prehistory deal primarily with the defini- tion of the patterns and stages .. The most pressing of these is the definition of Sa~ Dieguito III assemblages.-To date, little conclusive evidence exists maintaining the cultural continuity of the thre~ phases of the San Dieguito pattern. This also calls ~nto question the relationship of .two as- se~.blages identified as San Diegui~o III and .Milling Stone Stage, La Jolla pattern sites~ Structural probl_ems are also evident in the definition ot the La Jolla pattern. Little in the way of· infer.nation of seasonal variation of the peoples responsible fer this pattern has been presented in the literature. In conj~"'lction, work needs to be done-w:i th the inland mai, ifes- ·tation, whatever it may be, of the Milling Stone Stage . . The greatest amount of infonnation presently available deals.with the Late Prehistoric Stage.· This is not because of more successful investigations of Late Prehistoric patterns, but rather .results from the assumed relationship of· these patterns with ethnographicall.y recorded popul.ations. What is needed,· therefore, -i~ additional substantiation of this assumption of cultural.continuity between Late Prehistoric Stage patterns and historically known populations. Developmental. Structural problems can only see resolution in the clarifica~ion of developmental questions. Only by elucidating· the actiyities which resulted in the ob- served structural elements will we be able to explain prehis- toric framework components. Developmental questions which are of primary concern at this time deal-with the nature of the relationship between the originators of ... the San Diegui to III-and the La Jolla patterns. This involved additional research into the temporal placement.of each pattern. If such·research maintains f-40 C 0 the present assumption of chronotogical distinction, questions about the continuity of occupation between San Dieguito and La Jolla manifestations must be· asked. In conjunction,. re- search should be oriented toward comparing tool.assemblages of the three phases of the San Dieguito pattern in an attempt to determine the nature of its development and subsequent 0 deposition. Kaldenberg (1976) proposes that evidence at the Rancho Park North Site indicates a continuity between the San Dieguito III and La Jolla patterns. Evidence pre.sented by Kaldenberg consists of continuity of several tool types as 0 well as use of shell food throughout the vertical extent of the deposit. Continual occupation of the San Diego Coast from San Dieguito III to La Jolla I is complicated by the lack of an Early Man Stage-pattern in northern· Southe~n .California. With the continual occurrence·of the.Milling Stone Stage through coastal Southern California and an Early Man Pattern limited 0 to the San Diego area, .the only explanation allowing for gene- tic relationship of San Dieguito· and La Jolla would involve the expansion of the Milling Stone Stage from the San Diego area. This brings into quest1on the nature of the 0 relationship between the Early Man Stage pattern and the· M!lling Stone Stage pattern in San Diego County. If research does not maintain the temporal separation of.these stages, a complete revision of the pre- historic framework must be achieved. Investigations would 0 then have to be oriented toward assessing the genetic rela- tionship of both groups, _the San Dieguito III and the La Jolla. Fina.l.ly, research· questions oriented toward an understanding of the relationship between Milling Stone Stage and Late Prehistor.ic Stage patterns are also important 0 in testing the ·applicability of the, present prehistoric frame- work. Are the assump't:ions made by Moriarty (1966) and Roger!3 (1945) which maintain continual occupation of the San Diego Coast by La Jolla populations and .then by a merging of those groups with desert cultures establishing the _Late Prehistoric, Yuman valid., or, as proffered by Bull (1975), was the coast 0 abandoned with the resulting gap being filled by expanding Yuman and :t.uisenic populations? A .complex explanation o·f prehistoric develop- ment for coastal Southern California was presented·by Bull (1975). This proposal correlated linguistic evidence with 0 the archaeological record·to arrive at an explanation of pre- historic ,d1:velopment. At that time, :it· was proposed that the .Q f-41 OJ l o, j I 0 I 0' 0 I I ! 0 d '· i .o 0 onset of the Mi:!.ling Stone :Stage of coastal Southern Cali- fornia, then corresponds to a group of Proto-Chumash, Proto- Seri speakers. Th!i!Y per.sisted on the coast until around 1500 B.P. at which time Late Prehistoric stages appear. ' .,. ' . Placement of the Rancho ·carrillo·prehistorfc archaeological. sites within this framework is dependent upon the presence or absence of certain, critical_elements. The· definition of any given s-t;~-ge, phase or. pattern is accompl_ished by a lis_ting. of nominal cr.i teria·; lack of these diagnostic traits, then, prohibits assessment within the framework. _ All but one of the prehistoric archaeological sites at Rancho_-Carrillo .lack the necessary c;haract~ristics to per.nit.placement within the cultural framework as_ developed to date. This_ is not unusuai: at the survey stage of. archaeo- logical research because of the limited amount of information ga t..i.e.:-ad. SDM-W-9-15,' has been dated by Carbon 14 ~t 6880::280 B.P. (UCR-434) (Kaldenberg 1976:71), a,id as such, can be associated with the Milling Stone Stage· of Southern Cali- fornia prehistory. The occurrence of patinated flaked st·one arti::acts and the predominance of flaked as oppossed to ground li·.thic materials makes-tll,is site of extreme importance for re- fining local cultu~al history. • f-42 J J j I F. IMPACTS RESULTING FROM THE PROPOSED PROJECT Impacts to ·archaeological resources, both historic arid prehistoric, can occur in two primary ways. First, direct impacts can occur to sites from the actual developmental acti- vities.~ Se<:::ondly, indirect impacts can occur to historic and pr.ehistoric resources as a result of the activities· which re-• sult from completion ·of a given project. These include such things as· popu_lation _and/or activity increas·e. Both indirect -and direct impacts must be evaluated when dealing with the fragile record of the past. l. Section l. Plans call'.for the initial develop- ment of this area. Specifically, 346.single-family dwelling. units are proposed on the 111-acre parcel. This construction will. result in an estimated population increase of 1,128-per- sons. As a result of the.development of this section, one archaeologica.t sit_e will be directly impacted. As the design 'presently exists, SDM-W-109·1 will be significantly· im- pacted.. For a discussion of mitigating measuras neecled at this· 1ocation, seE: Section G of this report. In addition to the archa~ological site, develop- men-: of this area will also result· in the removal of:.two iso- lated artifacts. The impacts to these individual specimens as well as to the-site, constitute the direct impacts the development of this area will have on the archaeologi~al rec- ord. Indirect impacts can also be predicted to historic and prehistoric resources as a consequence of the increased population resulting from the proposed development. This is particularly true of the highly identifiable remains of the Rancho de los Quiotes, ·and to a lesser extent to the prehis- toric site SDM-W-1086. Impacts will probably occur by in- creased visitation to-the historic area, and as a result to 1086, which lies directly between the subject property and the Rancho. occur to any the valley. as adequate It is possible that other indirect impacts could one of the several prehistoric sites throughout Their inconspicuousness, however, should serve protection from intentional damage. 2. Section 2. At the present time, there are no specific construction plans for this area. As such, any as- sessment of direct impacts to the resources present are highly tentative·and should be revaluated when a final plan is adopted. f-43 C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 .o 0 0 'o 0 Of the 14 archaeological sites located in this area, all but two lie within areas of proposed residential use. The historic Rancho de las Quiotes and the important prehistoric site SDM-W-1086, both lie in ·special use areas.' The ranch house is within a. 20 acre historical park area, and as such, will be preserved .. SDM-W-1086 lies within an area of scheduled commercial use and as such, may be directly impacted. The sites within the residential areas may be directly· impacted by development and will be dealt with as such. It must be emphasized, however, that all assessment of impacts should be revaluated when specific plans are adopt~d. In addition to the archaeological sites which are threatened by the development of this portion of Rancho Carrillo, seven isolated artifact finds .will also be displaced. Assessment ... of indirect imp~c:ts will involve a knowledge of which sites in the area remain and in what con- dition. Their evaluation must be conditional upon when the area is developed, how much is developed, and what. alteration in neighboring areas has proceeded. There is no doubt that indirect impacts will occur, but to what extent is dependent on the abovementioned criteria. 3. Section 3. ..Three prehistoric archaeological sites have been recorded in this area, SDM-W-587, W-588, and W-589. As these sites were investigated by Kaldenberg {1975) and in that process were collected and possible impacts miti- gated (Kaldenberg 1976:104). Because of previous archaeologi- cal work in the area, development of this portion of the pro~ posed Rancho Carrillo_property will have no adverse direct impacts on the historic and/or prehistoric record. As with Section 2, evaluation of indirect im- pacts necessarily involves too ma~y unknowns to be of any use at this time .. Such an evaluation should be made, however, prior to development of any specific area. 4. Rancho de los Quiotes (Carrillo Ranch}·. Present plans call for the preservation of this important historic· resource as a park area. By providing for the continued exis- tence of this segment of California's past, and making it observ- able to the general public a fast disappearing· component of history is shared. Future development plans should insu·re the preservation of this area. -... ,: J. r J:. I J r J ~ ~ G. MITIGATING MEASURES Archaeology has the somewhat unique capability of being· able to .significantly lessen impacts to specific ar- chaeological resources.. As the value of a particular site lies,to a large extent, in the information stored with it, careful excavation and information recording can preserve a great deal of a site. The archaeological sites found on the Rancho Carrillo property range from small shell scatters to the extensive re- mains of the Rancho de los Quiotes. Measures necessary to lessen the impacts to these resources also vary greatly. • Table 1 provides a summary of the mitigating measures recom- mended to achieve such a lessening. 1 .. Site: SDM-W-1091. As this site has a limited amoun~ of cultural debris·and has been greatly disturbed, very little infoJ:mation could be gained from further exami- nation. -Lack of contectural information and a lack of a major _su~urface component make f~ther work at this site of little value. As such, no further mitigating action·is deemed necassar.1. 2. Sites SDM-W-1078, -1087, -1088. As.these sites are only shell scatters, little cultural information is avail- able. Prior to their disruption, ·.however,· a sample . of. the shells present should ue taken and analyzed~ This should. in- clude radiocarbon dating and/an-in-depth discussion of the relationship between these minor resources and the more sub- stantial contemporaneous sites in the Batiquitos Lagoon Region. 3. SitesvSDM-W-1079, -1080, -1081. These sites are also small scatters of shell, .but due to their extreme sparsity, any work done here would be an exercise in futility. As such, no further mitigating action is necessary at these locations. . 4. Sites SDM-W-1083, ~1084, -1085, -1090. These sites are light deposits of cultural materials consisting of limited numbers of artifacts. When viewed independently, their re- .search potential is 1ow. However, on the locality and regionaJ. level, they can provide valuable insight into settlement pat- terns. As such, prior to destruction, these areas should be mapped and collected and a report should be prepared. 5. Sites SDM-W-587, -588, -589. Impacts to these sites have been mitigated by work done by Kaldenberg (1975)~ No further archaeological work is necessary. f-45 C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 'O 0 0 0 0 0 I lo I I i 6. Site: SDM-W-1089. This site has apparent sub- surface components. It also has numerous shell and artifac- tual materials. It requires then, a degree more work than the previously discussed sites to achieve mitigation. Recom- mended mitigating measures include implementation of a syste- matic rectilinear posthole test, and one hand excavated unit for profiiing purposes. Based on information gained by this examination, a statistical sample should be drawn from the site area. The size of this sample is dependent on the pre- dicted variance present at the site. From infoJ:mation gained through these tests, further mi tiga.ting measures can be recommended if .necessary. As·with any recommendations, these are subject to change upon the obtainment of additional infoJ:mation, and should be con- stantly reassessed during any further investigation. "· 7. SDM-W-10~6 and SDM-W-915. These two sites rep- resent the areas of greatest prehistoric significance within the entire Rancho Carrillo property. Both have a subsurface ele!:lent and numerous artifacts. As such, mitigating-measures. need to be more stringent than with the other prehistoric sites. With both of these sites, preservation of the ac- tual resource is highly preferable to any other mitigating measures. If preservation cannot be achieved ~owever, care- ful five percent test excavation programs should be undertaken. This should be preceded by !imited exploratory work to deter- mine the sampling universe. Systematic postholing is a method which would provide such a measure. Dependent upon the results of these tests, further mitigating action may be necessary. Such an assessment cannot be made until further infoJ:mation is available. As with all archaeological investigations, a re- port of findings should be prepared discussing the research. All work should be done by an archaeologist qualified under the First Addendum to the San Diego County Procedures for En- vironmental Impact Review. 8. Rancho de Los Quiotes (Carrillo Ranch).and W-1082. No amount of archaeological and historical research could miti- gate the destruction of the rancho complex. It has value not only in providing infoJ:mation, but is also of great aesthetic importance~ and as such should be preserved. J ·' ii ; d s d ii • ii H. PROJECT STAFF Charles s. Bull David Hanna, Jr. Kree Easland Henry Hatley . Margret Weidauer Joanne Thompson 0 Supervisory Archaeol_ogist Assistant Archaeologist Archaeological Assistant 0 Archaeological .Assistant \ Archaeological Assistant Production Specialist 0 0 0 0 0 0 f-47 0 01 l 0 • I 0) I oJ ) OJ i I 0 .. a I 0 I J I c1 I :J I i I. LIST OF PERSONS AND ORGANIZATIONS CONSULTED Ken Hedges San Diego Museum of Man David Hanna, Jr. San Diego State University San Diego Historical Society Mr. Richard Carrico Mr. John Larson f-48 Serra Museum Library 1 . l I I m 3 .. I I ;.,. .. I III. REFERENCES CITED Bean, L. J. and K.-saubel 1972 Tamalpakh: Chauilla Indian Knowledge and Usage of Plants. Banning, Maliki Musewn Press. Bright, 1965 Marcia California Radiocarbon Dates in Archaeological Sur- vev Annual Report. ·Department of Anthropology, university of California, Los Angeles. 367-80. Bull, Charles S. 1975 A..i. Archaeological Survey of the Coastal Area of Camp Pendleton Marine Base. Ms prepared for San Diego State University Foundations. Crabtree, Robert H .. , Claude N. Warren, and D.L. True 1963 Archaeological Investigations at Batiquitos Lagoon, San Diego County, California. In University of Cali- fornia at Los Angeles Archaeological Survey Annual Report, 1962-1963., 319-349. Los Angeles: Univer- sity of California Press. Davis, E.L. 1975 Personnal communication. Davis, E.L., D. w. Brott, and D. L. Weide 1969 The Western Lithic·Co-Tradition in San Diego Museum of Man Papers,, No. 6, San Diego, California. Ezell, P.H. 1975 Aboriginal Cemetery at Las Flores Creek, Camp Pendle- ~-Unpublished manuscript. Greenwood, Roberta 1969 The Bro~e Site;_ Early Mil.l.ing Stone Horizon in South- ern California .. society for American Archaeology. American Antiquity 34(4), Part 2. Harrison, W.M., and E. Harrison 1966 An Archaeological Sequence for the Huntin~ People of Santa Barbara. California.Archaeological Survey An- nual Report 1965-66. Department of Anthropology, University of California, Los Angeles. pp 1-90. Hubbs, C., G. Bien, and H. Suess 1960 La Jolla Natural Radio Carbon Measure I. American Journal of Science, Radio Carbon Supplement. 62:204- 238. f-49 --------·-·-··· -- C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Johnson, 1966 Keith -. Site LA 2; A Late Manifestation of the Topanga Complex in Southern California Prehistory. Anthro- pological Records 23. University of Caiifornia, Berkeley. Kaldenberg, R~L. 1975 Archaeological .Investigations at Rancho Carrillo Es- tates. Unpublished manuscript. 1975b An Archaeological Impact Report on the La Costa Far South (Easterly Area) Including Santa Fe Knolls. Unpublished manuscript on file at RECON. 1976 Presentation to the. Society for California Archaeology, dealing with Rancho Park North excavations. April. 1976b An Intensive Archaeological Reconnaissance of the La Costa Land Company Property, Carlsbad, California. Unpublished manuscript. and Charles S •• Bull -....... ----1975 Archaeological Investigations at Rancho Del Dies Units One and Two. Unpublished manuscript prepared for Santa Fe Company by RECON, .San Diego, California. Kowta, Mako'!:a 1969 The Sayle~ Complex, a Late Milling Stone Assemblage from Cajon Pass and the Ecological Implications of its Scraper Planes. 'In University of California Publications in Anthropology, Volume 5:35-69. McGowan, 1955 B.E. Temuka:· Indians. Southern A Page from the History of the Luiseno In Ar~haeological Survey Association of California, Paper No. 3, Los Angeles. Meighan, Clement w. 1954 A -Late Complex in Southern California Prehistory. In Southwestern Journal of Anthropology, 10(2) :255- 264. Moriarty, James R. 1966 -Cultural Phase Divisions Suggested by Typological Change Coordinated with Stratigraphically Controlled Radiocarbon Dating in San Dieg·o. In Anthropological Journal of Canada, 4(4) :20-30. f-50 r: t t r L: t t [ [ [ [ t I Mudie, 1976 Peta J., Bruce M. Browning and John W. Speth The Natural Resources of San Dieguito and Batiauitos •Lagoons. • Department of Fish and Game, Coastal Wet- Lands, Series #12 . . Owen, Roger C., and Freddie Curtis, and Donald S. Miller 1964 The Glen Annie Canyon Site, SBa-142, An Early Hori- zon Site of Santa Barbara County. Archaeological Survey Annual Report, 1963-1964, 431-519. Los An- geles: University of California. Peck, Stuart L. 1955 An Archaeo.logical Report of the Excavation of a Pre- historic Site at Zuma Creek, Los Angeles County, California. Archaeological Survey Association of Southern California No. 2, Los Angeles. Rogers, D.B. 1929 Prehistoric-Man of the Santa Barbara Coast. Santa Barbara Museum of Natural History, Santa Barbara. Roge::::-s, Malcolm 1929 The Stone Art of the San.Dieguito Plateau. In • ,Amer.ican Antllropologist. 31: 454-467. 1938 Archaeological and Geological Invest1gations of the Cultural Levels in an Old Channel of the San Dieguito Valley. In Carnegie Institute of Washins::_ ton Yearbo·ok. 37 :344-345. 1945 An Outline of Yuman Prehistory. Southwestern Journal of Anthropology 1(2) :167-198~ 1966 Ancient Hunters of the Far: West. San Diego: Union Tribune. Publishing Company. Shumway, George, .Carl L. Hubbs, and James R. Moriarty 1961 Scripps Estate Site, San Diego, California, A La Jol- lan Site Dated 5460-7370 Years Before the Present. In Annals of the New York Academy of Science, 93(3): 37-72. . Treganza,·A.E., and A. Bierman 1958 -The Topanga Culture: Final Report on Excavations, 1948. In Anthropological Records, Volume 20, No. 2, University of California Press, Berkeley~ f-51 0 0 0 0 0 0 0 0 0 0 C 0 0 0 0 0 0 0 o· 0 0 0 True, D. L. ·-1958 An Early Complex in Southern California County, California. American Antiquity 23 :25,5-262. 1970 Walker, 1952 Wallace, .1954 1955 Warren, 1966 1967 1968 Warren, 1963 Investigation of a Late Prehistoric Complex in Cuyamaca Rancho State Park, San Diego County, Cali- fornia. Monograph, University of California·Archaeo- logical Survey, Los Angeles. Edwin Francis Five Prehistoric· Sites· in Los Angeles County, Cali- fornia. Publications of the Fredric Weob Hodge Anniversary Publication Fund, Vol. 6., Los Angeles: Southwest Museum. William J. Little Sycamore and the of Southern California~ 123. Early Milling Stone Culture American Antiquity, 20:112- A Suggested Chronology for Southern California, Coasta·l Archaeology. In Southwestern Journal for Anthropologv, 11:214-230. Claude N. The San Dieguito Type Site: M.J. Rogers' 1938 Exca- vation on the San Dieguito River. In San Diego Museum of Man Papers, No. 6, San Diego Museum of Man, San Diego. • ,, The San Oiegui to Complex: A Review and Hypothesis. In American Anthropologist, 32(2):168-185. Cultural Tradition and Ecological Adaptation on the Southern California Coast. In Archaic Prehistory in the Western United States. Eastern New Mexico Contributions in Anthropology, Portales 1(3) :1-14. Claude N. and Max G. Pavesic. Appendix I: Shell, Midden Analysis of Site SDl-603 and Ecological Implications for Cultural Development on Batiquitos Lagoon, San Diego County. In Archaeo- logical Investigations at Batiquitos Lagoon, San Diego County, California, Robert Crabtree, Claude N. Warren, and D. L. True, pps 407-438. f-52 i : I I' 11 1! II IE IE Ir l IE If IL It Ir I· l'- 1 [ I[ Ir ~ . ,. ~ I -~ !; L• I I ~ ~ -i •. -; Warren, Claude N. , and D. L·. True 1961 The San Dieguito· Complex and Its Place in Southern California Prehistory. Archaeological Survey Annual Report 1960-1961, pp.· 1-106 .• Los Angeles: Univer- sity of California Press. Warren, Claude N., D. L. True, and Ardith Eudey 1961 Early Gatherning Complexes of Western San Diego County, California. Results and Interpretation of an Archaeological Survey. Archaeological Survey Annual Reoort 1960-1961, pp. 1-106. Los.Angeles: University of California Press. Weber, F. Harold, Jr. . .. 1957 Mines and Mineral Resources of San Diego County, . California, . Report No. 3.,. California Division of Mines and Geology. f-53 0 0 0 0 0 0 -0 0 0 0 0 i I :. I I I ' I \e I • I • I I :• I • • I l • I J , I ' - I , ATTACHMENT 1 \ J · SAN DIEGO MUSEUM OF MAN 1350 El Prado, Balboa Park, San Diego, Califomia 92101, Tele~hone (714) 239-2001 j REPORT ON ARCHAEOLOGICAL SITE FILES RECORD SEARCH Source of Request: REC ON -Charles S. Bull Paga _t._ of -2_ Date of Request: 2~ Auaust 1976 (X)Letter ( )Telephone () In Person ----------------------- Date _Request Received: 27 August 1976 (X)Map Received (X)Map Returned ~ame of Project: Ca~rillo Ranch -Job #5632 () !he Museum of Man files show no recorded sites for the project area. oc) The Museu~ of Man files show the following sites the project area. (.X)within (I)in ~he vicinity of Site No. W-l!JcA Culture(s): Luiseno or YUiri.a.n III (trace) Description:~}~!i_d_d_e_n_ .• _______________________________ _ Recorded by: _R_o_g...,e_r_s ____ _ Site No. W-18'3 Culture(s): San Dieguito II, I.a Jolla II Descri?tion: ~ighla.--id accretion cam-c -broken metates and manos. Recorded by: .....,.R...,o.,i'e..,.,....,s..,__ __ _ Site Culture(s): S=p p.; er·J1ito TI - Recorded by: __ R_.o...,g,_er __ s ____ _ Site N~. W-le3B Culture(s): San Dieguito II, Yur:-.an III (trace) Description: ~i~hland acc~eticn ca.mn -cobble hearths. Recorded by :_.,.;1...,0...,g~ .... r.,s ___ _ Sict:! No. W-1,% Culture(s): San Dieguito II, YUir.an II Description: :fighland r-ar:r.ar..ent camp -cobble heartns, rr..etates, ml=lnos, fla.idng1 tools. ___________________ Recorded b:y: _Ro_i;;:..,-"'_-r_s ____ _ Site No. :,f-191 Culture(s): San Dies!'i.1ir,o II -----=--------=--------------------------------- Des c rip ti on: ':i;rhJ.and i:-1te:::-mittent ca.Tllo sit.e. Recorded by :__.~ .... oe.srn ... r .... s..__ __ _ ?lease note: The project area may contain archaeological resources in addition to those noted above. This report is made from San Diego Museum of Man files only and may not include data pertaining to localities other than those covered in previous Museum of Man surveys or gathered by other institutio~s or by individuals. Reco:-d check by: Grace Johnson f-55 z ·-Signed: , '-',<,-,df 0 0 0 0 0 0 0 0 0 0 0 ,,o 0 0 0 0 0 0 0 0 APPENDIX D PALEONTOLOGICAL STUDY lsa 0 ROD R . .\SCHKE Pc:!ta"Mf.:J,gic Consulfonf 1762 E.:..ST 1 ST 57REET L~"-G SE:.4-CH. CAL:F. 90802 0 (213).!35-1557 0 10 .January 1981 ~r. ~ori Douolas . Arc~aeolooi~ai Plannino Collaborative 300 ~e·Kpoi'.-t tenter Dri ;e, Suite 525 Xei-.--port Beach, California Paleontological Evaluation of Rancho Carrillo 0 Introduction 0 0. 0 The following evaluation of the·known an9,po~~ntial paleontologic resources of Rancho Carrillo is based on a revi~"N' of published and unpublished paleontologic literature and locality data. The site is located east of central Carlsbad on Palomar Airport Road_ (see Figure 1). Paleontoloav and Stratioraphv The property is underlain by unna.~ed sands of Eocene age (38 to 55 million )tears ago). Golz ( 1976) correlated thC?se sands to the Santiago For~ation of Orange County. Eocene age rocks of San Diego County have·procuced numerous sic~ificant fossils from several localities. Published report of Eoc~ne fo;sils date from the 1930's. • Golz ( 1976),and Golz and Li-llegraven ( 1977) reported on an extensive vertebrate fauna from the Laguna Riviera Development in Carlsbad. Thi~ occurren"C'e •,\·as located in conjunction with the development of the site. This occurrence-produced numerous rer::ains of extinct reptiles, birds. and mammals, many of :Khich .. -ere new forms. At this time the Laguna Riviera locality is the closest recorded_ fossil occurrence to Rancho Carrillo. This•rnay be related to the :act that I was.unable to locate any record of any paleor.tological 0 study in the a.cea of the· property. 0 conclusions 2ancho Carrillo lies within a district tha~ ha~ a rr:.;....:erc~s significant fossil remains. It is highly ,,:-.ere within the 7 50,. acres of the site ':here are a::.d that these rer:1ai:1s are signi:icc:nt. history of produ~ing procable t~at so~e- -I • t :ossl...L• :-e!":".a.1ns Golz and LillGg~a~en (1977) pointed out that in order to irrp~ove correlatior.s of the Eocene sa1:cis of the Car:stad area ~ith 0t~er ~nits of sirni_,~_r ac_e -ddit-io,..;-, -=css1· ,s -re re-0 c:~-..-·-.:·,..om ot::er localities. o -•• a..L .:. .... ,::i_ ., •-~---=--::i-~ --, 0 It. is possible :.~at t1i.e :cssils li}:ely to Ce _;:!-~SE-nt at Ra::c~-"o •~ar!:"'i2.lo 0 will be useful in such an analysis. O Finally, fossil remains are a nor.-renewable resource and the destruction of any fossil is a loss to the science of paleontology. Thus the development of any site with a high potential for the presence of fossils without proper mitigation measures would be an adverse impact on the paleontologic resources of the Carlsbad area. This could be o the case at Rancho Carrillo unless the following recommendations are implemented. • Recommendations These recomrne:ndations are based on CEQA and proven practices used on sites of known paleon~ologic sensitivity. 1. A Kalkover survey of Rancho Carrillo should be performed well in advance of· development. This survey can locate and define ar~as of sensitivity. 2. Any fossils located during the survey should be collected prior to development. This will avoid delays -during con- struct.ion. 0 0 3. A caleontoloaist should be retained to be present on site to.monitor grading ope~atior.s. The paleontoloqist shoulc be C allowed to salva,;e ::ossils exposed by grading. If necessary he should be able to divert or direct grading to allow for salvage .. 4. All fossils collected should be donated to a public, non-profit institution such as the San piego ~~tural History ::fuseurn, the Pal-eobiology-Department of· San Diego State University or the Natural History ~useurn of Los Angeles County. If you have any questions about this evaluation do not hesita~e to C call ■ C F:od ?.ascr...ke Certified ?a:eontologist C C ----------------------,----r----c-;'"--,-, ---... ,, . 0 0 0 'O 0 0 I I I 0 0 0 0 0 I 2e:erences Cited Golz,D.J.,1976 Eocene Artiodactyla of southern Cali:ornia. ~atural Hist. ~us. Los Angeles Co. Sci. 9ull. 26 --------and Lillegraven, J .. ?\., 1977. Su.>r.mary of knm\-n occur .r-ences of terrestrial vertebrates from Eocene strata of southern California. ,.. .... • b .... G 1 ... -• T. • l'"" A~ ,. -,_ on 1..r 1. • 1..0 -eo_. , 1..,nl. v. i\yoming, .:>: '¼--o.:i . ~:CD R~ set -,r~E n, , , . C ,1 t ...-r.,-.c0n,co1r,q1c ans•.:• rJn 1 762 E:..ST 1 S7 S,r=lEE:T ,2 1 3) ~35-1 557 !O C"ar.'.1ary 1981 :-:~. ?on Douglas .=::.rc:ha~ological Plaf1_"1ing Collaborative 500 :r-.:e,,-port. Center Drive, Suite 525 ~~e~,-port Eeach, California ?aleontological Eval~ation of ~anc:10 Carrillo Report Preparation 20 hrs~ ~12.50 ............... $150.00 TOT .. ~ DUE ......................... c-S 130.00 ~od Rasc:1.ke Certi:ied Paleontologist • ••• • • • -- -..... .......... ::.· . .; • . ~ >. ?..):~C:, C::..,,,._.>r.Y cf: CA?..!:eAO. D.:..F:"'=°'-' TH: ·,-,,:-:,:-,,,,...=o cc•.,:.,,..~s. T;.;;; ',l::!STE;:t ~ .... ,. :~. & c~-J"I c c ::.::.::-_-::,:.7,liN VISTA rn SAN M.!.RCCS ;. ,I • ~-•• • ;._:_--~:a ·~·-··-~ .... .:-:-·--~~...:-.<a- 0 0 0 APPENDIX E TRAFFIC STUDY lsa 0 0 0 0 0 0 0 0 0 0 I 10 I March 16, 1981 Mr. Mike Ryan DAON Southwest PO Box 270 Newport Beach, CA 92660 Dear Mr. Ryan: TRAFFIC & TRANSPORTATION ENGINEERING , ' . This letter summarizes our analysis of the·traffic factors related to the Master Plan for the Carrillo.Ranch in the City of Carlsbad and our field reviews of the area. The report·has been revised to reflect comments received from the City relative to our previous reports of June 25, 1980 and November 5, 1980. The City's comments referred to above are dated October· 8, 1980; December 30, }980; February 18, 1981; February 23, 1981; and March 2, i9.in. PROJECT DESCRIPTION The project site is located generally at the future intcr~ection of Palomar Airport Road ~~d Melrose· Avenue with the majority of the ar_ea being southerly of Palomar Airport·Road. Planned land use· is residential except for the area northerly of Palomar· Airport Road, which is commercial and indus.trial, and a commercial area in the northwest quadrant· of Melros~ _Avenue and Carrillo Way. The site is currently undeveloped with Palomar Airport Road being the only existing improved roadway. In addition to Melrose Avenue~ the project would include the. construction o~ Carrillo Way and El .Fuerte St:reet within the site boundaries. Melrose Avenue. is classified-as a Prime Arterial .in the City General Plan and_Carrillo Way and El Fuerte Street are classified as Secondary Arterials. The site-.and proposed road system ·are illustrated in Figure 1. 2651 EAST CHAPMAN AVENUE • SUITE 110 • FULLERTON. CALIFORNIA 92631 • (714) 871-2931 -2- The plan includes the development of 2,998 residential units of various types. There are 36.7 acres of industrial uses and 26.2 acres of commercial µses also indicated on the plan. Park and eight acres of commercial recreation areas are also indicated on the plan. No specific uses for the commercial recreation areas have been determined at this time. TRIP GENERATION In order to analyze the traffic factors related to the project, it is necessary to estimate the number of trips that will be generated. Studies have been conducted by governmen~al agen~ies,and consultants to determine appropriate trip generation rates for various land uses. The i::~tes .u~i:lized in this ·study· are summarized in Table 1. Since definitive land .u~e <;iata ~re not available fo·r the commercial recreation areas, assumptions woul~ generally preclude· major structures on these site_s. It has been .issumcd chat. racqµct ·ball courts· would . . -. ,,. be ·potential use. In .iny case, tht:se. use::; would b~ primarily serving ch~ adjacent area~ and not impact the external road systems. No estimate has been made for the ranch house site as no applicable trip generation rates are available .. This use would also have a negligible impact upon t.hc str~cc system. By applying the trip gcncr.it.ion r:itcs to the 1n·opo:,wd J,mJ use.· qmmtlt I.cs, c.:sLimutc.:s ut daily ai1d -,peak )1our trip generation for the proJ~ct were obtained .. These estimates • + .. • , • ' are summarized.in Table 2. It ,is estimated that the project upon completion would generate 53,840 daily trip e~ds W:ith 3060 occurring.during the AM peak hour and 5, 780 during the PM peak hour. As is discussed below, not all of" these trips are external to the site. The Rancho Catillo Master Plan contains provisions for the conversion of the elementary school. site. to Low De~sity Residenti.il in c·ertain circunstances. This would add,124 dwelling units with 930 daily trip ends ·and 100 PM peak hour trip ends. The ~otal daily.trip_ ends with •the school site conversion would be 54,770 C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 i \ ' , ... ,. ' ~!1-\..0M~R Al ,. ' \ \ \ 1 ... ~-N-L ..... .... ')-.... / ........ I ,..._ I ....,_ . STRIAL NO SCALE / ', I \ _,,,;---I , _ _...., / I I I I I / I f j -_____ L __ C!-~J.'==~--t \ \ \ WESTON PRINGLE AND ASSOCIATES RETAIL RETAIL SITE LOCATION FIGUAE 1 TABLE I TRlP GENERATlON RATES Carrillo Ranch -3- RATES(l) LAND USE DESCRIPTOR DAILY AM IN AM OUT PM IN PM OUT -- Low Density Residential Dwelling Unit 11.0 0.2 a.a 0.8 0.2 Medium Density Residential Dwelling Unit 7.5 0.2 0.6 0.6 0.2 Commercial Acre 900.0 Negligible 45.0 45.0 Industrial Acre 80.0 11.0 3.0 . 3.5 12.5 • Commercial Recreation Acre 300.0 Negligible 7.7 28.7 Park Acre -6.0 Negligible 0.3 (l)Trip ends per descriptor· TABLE 2 TRIP GENERATION Carrillo Ranch TRIP ENDS LAND USE QUANTITY DAILY AM.IN AM OUT PM IN PM OUT ---- Low Density Residential 701 7,700 140 560 560 140 Medium Density 2297 17,200 470 1380 1380 460 Commercial 1 26.2 23,600 1180 1180 Industrial1 36~7 2,900 400 110· 130 460 Commercial Recreation 1 8.0 2,400 60 :!30 Park 7.0 40 TOTALS 53,840 1,010 2,050 3,310 2,470 1 Based on estimated net acreage figures as opposed to the gross acreage figures listed in the proposed Rancho Carrillo Master Plan. C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 -4- TRIP DISTRIBUTION A.'ID ASSIGNMENT The next step in the analysis process is to determine a geographic distribution . ' pattern for the project generated traffic and assign the traffic to be road syste:. San Diego County Planning Organization -1995 proj ecti<:ms were utilized for industrial and commercial trips and Basic Employment·, Retail Trade Employment and Retail Services Employment were utilized for residential trips. :These patterns were further modified based upon knowledge of the area and professional judgement. Distribution patterns were also developed for two future conditions~ First, upon project completion without the ultimate development of Carrillo Way and Melrose as shown in Figure 2. Second a distribution pattern representing ultimate planned buildout of the road system as shown in Figure 3. The distributions indicate.a negligible percentage to Alga Road. Some traffic will utilize Alga Road, as-shown in Figures 4 and 5, which is related to the commercial and commercial recreation uses. Since the illustrated distributions are for residential and industrial.. thl!y are not lncludl.!c.i on Figures 2 and 3. Utilizing the distribution patterns illustrated in Figures_2 and 3, project -tra-ffic was assigned to the road system. Daily volumes at completion of the project are illustrated in Figure 4 and at ultimate development in Figure 5. Th~ volumes in Figure 4 include existing traffic and those in Figure 5 include exist- ing, project and ~djacent development traffic. Other pr.ujccts included wuru Carlsbad Oaks and -La Costa. Figure 6 illustrates daily volumes of the p'roj ect plus school site conversion with ultimate road development. An additional adjustment was made in external traffic from the project. Since some of the trips attracted to the commercial uses would be generated by the pro- ject residential uses, a reduction was made in external traffic. It was assumed that half of the trips attracted to the commercial area at Carrillo Way and Melrose Avenue were generated in the residential areas and would not be external co C~ti! ·---. -60% (60%) ~. NO SCALE I .cARR\l:,;-~--L ------------\ I \ I ---.lo\ ___ l LEGEND 0% -RESIDENTIAL (0%) -INDUSTRIAL WESTON PRINGLE ANO ASSOCIATES DIRECTIONAL DISTRIBUTION AT PROJECT COMPLETION FIGURE 2 C C C C . C 0 0 0 0 0 ----------------------,. •• , ••• 0 0 0 0 0 0 0 0 0 0 0 30% (40%) ~ ~ NO SCALE • 15%(10%) LEGEND 45 % -RESIDENTIAL (50%) -INDU STR!AL WESTON PRl~GLE AND ASSOCIATES 5% (10%) DIRECTIONAL DISTRIBUTION AT ULTIMATE FIGURE 3 ~ NO SCALE I ·CARR\':;-~--L ---• --------·-\ I \ I , ___ l LEGEND 38,500 -EXISTING+ PROJECT TRAFFIC (12,500) -EXISTING TRAFFIC WESTON PRINGLE ANO ASSOCIATES DAILY TRAFF'IC AT PROJECT COMPLETION FIGUJ:IE 4 C C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 39.z.cc ... ~-N--· NO SCALE I I _( ------· WESTON PRINGLE AND ASSOCIATES UL Tl MATE DAILY TRAFFIC 1 / INCLUDES EXISTING, PROJECT, AND .,f! ! t OTHER PARCELS TRAFFIC FIGURE 5 site. This-commercial area is described in the Carlsbad General Plan as a Community Commercial area. The General Plan further describes these uses as serving an area up to one and one-half mile radius. On the basis of this de- finition, the assumption that half of· the trips attracted to this commercial area are local would be conservative. This results in six percent of daily r_esidential trips being internal; four percent of the PM peak inbound trips and 13 percent of the PM peak outbound trips. CIRCULATION SYSTEM ANALYSIS . The ability of the planned circulation system to accommodate the project has been.evaluated on two levels. First, daily volume/capacity comparisons have been made to provide a general evaluation. Second, peak hour intersection analyses have been.completed on Melrose.Avenue at Palomar Airport Road and Carrillo Way to provide a mo·re refined evaluation. These analyses have been completed for conditions upon completion of the project and at.the ultimate development of the circulation system. Table 3 provides a comparison of maximum projected daily volumes and capacities for the ar~erials serving the project. Review of Table, 3 indicates that, on a daily basis, the planned system will be adequate. It does indicate a potential problem and the need to develop parallel routes to relieve Palomar Airport Road. This conclusion has been found in other project analyses and is not related solely to this project. For the ultimate condition, other projects being planned in the· area have been considered; however, this does not represent ultimate build out of the City General Plan. The reference to ultimate is only related to the road system. The Draft Environmental Impact Report prepared by the County of San Diego for the San Dieg1,1ito Circulation Element, GPA 80-CE, contains year 2000 projected daily volumes for Palomar Airport Road at Melrose Avenue. These volumes vary from 38,000 to 40,000 with the County proposed plan at 38,000. The report does -5- ( C C C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3isoo .-..~-N-- NO SCALE WESTON PRINGLE AND ASSOCIATES '.::., ------------------- ULTMATE DAILY TRAFFIC WITH SCHOOL SITE CONVERSION FIGURE S -6- not include projections for Melrose Avenue. Rancho Santa Fe Road north of Olivenhain is projected to have a demand of 34,000 with the County proposal. Since Melrose Avenue splits from Rancho Santa Fe Road just southerly of Carrillo Ranch, it could be assumed that the year 2000 volumes on Melrose would be somewhat less than 34,000. These projections also indicate t~at on a daily volume/capacity comparison basis, the planned road system would be ad~qunte. STREET Palomar Airport Road Melrose Avenue Carrillo Way TABLE 3 DAll.Y VOLUME/CAPACITY COMPARISONS Carrillo Ranch CAPACITY(!) 45,000(2) 45,000<2> 20,000 (!)City of Carlsbad Engineering Department (2)The City's value for Prime Arterials is 40,000 + vpd. VOLUME PROJECT COMPLETION ULTIMATE 38,500 • 42,400 13,400 24,1:00 . 4,000 lS,300 The operation of intersections 1s the critical factor in determining the adequacy of a circulation system. For the Carrillo Ranch development, the intersections on Melrose ~venue at Palomar Airport Road and Carrillo Way are the critical points in the circulation system. Intersection Capacity Utilization (ICU)' analyses have been completed for these intersections at the levels of project ·completion and ul- timate road system. (The ICU methodology is explained in Appendix A and the ICt:/ Level of Service relationship in Appendix B). Analyse_s sheets for these inter- sections contained in Appendi.~ C and the ICU values are summarized in Table 4. C C C C C C C C 0 0 0 I 0 0 0 0 0 0 0 0 0 0 I Jo I -7- As indicated in Table 4, an o_pera_t"ional problem is_ anticipated, at Pal9ma.r Airport Road and Melrose Avenue. This further confirms the p.otent;:ial problem identified :1n the daily_ volume/c~1>acity comparison. Tl)_~ ~ajor _factor-.con~ributing .to the·' potential capacity. problem is._ traffic flows on Palom_a:i;--• Airport Road. These are· a result 9f area-wide dev:elopment. and the prpblem is not relat.ed,_to a single pro-. . ~ ·. . . . . . . -. . . ' . . .. . ' ject~ As was mentipned previously,· there _is a ,ne~d ~~-r . additional east.~west routes to relieve Palomar.:_Ai:c:t>ort Road. Consideration was given to the impact· of· the ~reposed realignment of Los Monos Drive as it would affect Rancho Carrillo traffic. The results did not indicate a major improvement -of ·the Palomar. Airport· Road/~elrose intersection since Los _Mo~s _doe~ not extend easterly of.Melrose.- Table 4 ICU SUMMARY CARRILLO RANCH P~lomar. Airport Road and M~l:rose -Avenue. Carrillo Way and Melrose.Avenue Icu· PROJECT -~(_!tl_l_•_~:f~ . .!:!.!.:!.!!:!,ATli 0.81 .. 0.45 • -1.04 o. 79· The ICU analyses s~eets in Append~ C aiso in~icat.e the required·geomet.rics for . the intersections. ~o . special_. requirements , are indicated; at . the· Carrillo Way/ '· Melrose,Avenue inters~ction~ _The Palomar Airport Road/Melrose Avenue intersec- tion does require specific. geomett:ics at both levels of development.·. • Table 5 lists. t!ie re<1uire4 ge9met-rics fo_r th_e intersection .. The ·required lanes a:t ul- timate can be provided. within the standard. 106 foot curb-to-curb width with no ·: : -• . ,. • -· • . median, 10 foot le_ft t~n lanes, ~nd: ._l,l foot through·.' lanes. If 1'2 foot··through lanes are desired, a 108 foot section would be requi_red. These additional lanes • at ultima_te condltion .:ire required as a res.ult of growth in other traffic as can be seen_ by comparing_ the. l~U · analysis s_heiats. Changes in the ·amount :0£ ·other· developm~n~ and/or planned road systems could result indiffering requirements at this intersection. -8- The Palomar Airport Road/Melrose intersection should be monitored as growth occurs to insure that adequate capacity provisions are maintained. _Improved operations could also·be obtained by 'providing three through'lanes on Melrose at this inter- section. This would.reduce the ICU value to 0.97. Some traffic reauction may also occur since no reduction was made for work trips generated externally that would have destination within Rancho Carrillo, i.e. Carlsbad Oaks to Ra~cho Carrillo. As traffic-volumes,increase; some trip diversion may occur such as·westbound left·. turn· traffic may-divert to Rancho Santa Fe Road. This· study has identified the potential problem as Palomar Airport Road and Melros·e and it is recommended that it be monitored so that these potential problems can be mitigated. In addition to capacity consideratiotls, intersection spacing along •the arterials effects their operation. The City of Carlsbad Street Design Standards require 2600 feet between intersections on Prime Major Arterials and 600 feet on Secondary Arterials. These standards are satisfied on Carrillo Way and on Palomar Airport Road. On Melrose Avenue ther are two intersections which do not meet these criteria. An intersection is proposed on Melrose Avenue approximately 1600 feet southerly of Palomar Airport Road and 1600 feet no.rtherly of Carrillo Way. This intersection is required· to provide access to the planned development on both sides of Melrose Avenue. Due to t"er·rain and other development constraint•s, sufficient access cannot be provided without this .access. While the proposed intersection spacing doeg not meet the Standard, it does provide an reasonable spacing of gr_e_ater than ·a quarter mile.· This spacing is not unusual in developed areas and sa~isfactory traffic.movement.can be obtained. A second right turn in and out only access is proposed on Melrose Avenue. southerly of Carri,llo Way. With-the provision of deceleration and acceleration lanes, ·this access would not impact traffic flow:on Melrose Avenue. The relatively steep (8 percent) grade of Melrose Avenue at this. location would indicate tliat the len'gth of the acceleration lane should be increased to allow entering vehicles to reach the required speed .. A realignment from.the existing City General Plan of Paiomar Airport 'Road through the project was_,propo~ed by City Staff in order to improve·horizontal alignment and intersection spacing on Melrose. This realignment does appear to have advantages from an initial review; however, detailed analysis indicated additional problems. C C C C C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 The real~gnment was examined by Rick Engineering Company and potential problems were identified. While improved intersect.ion spacing is achii!ved southerly of falomar Airprot.·Road, intersection spac.ing rroblems dl!velop to the north. The realignment also results in vertical and horizontal alignment problems, excessive fills and interference with the Carlsbad Raceway to the north. An additional consideration for the current alignment of Palomar Airport Roa4 is that it provides a.division between residential and commercial/industrial land uses. Table 5 PALOMAR AIRPORT ROAD/MELROSE AVENUE GEOMETRICS CARRILLO RANCH MOVEMENT LANE REgUIREMENTS PROJECT COMPLETION ULTIMATE Northbound Through 1 2 Northbound Right 1 l Northbound Left 1 1 Southbound Through 1 2 Southbound Right l l Southbound Left 1 2 Eastbound Through 2 3 Eastbound Right 1 l Eastbound Left 1 l Westbound Through 2 3 Westbound Right 0 1 Westbound Left 2 •) \ -9- -10- The area north of Palomar Airport Road conforms to City of Carlsbad Standards with intersections on Melrose Avenue and Palomar Airport Road 2,600 feet apart. Driveways are proposed for right turn in and out operation only. Primary access to the industrial area is from the street (Industrial Way) which connect·s Palomar Airport Road and Melrose Avenue near the west property line. A secondary right turn only access to the industrial area is provided on Melrose Avenue. All right turn only access points should be carefully designed to minimize operational and safety impacts upon Palomar Airport Road and Melrose Avenue. Final access pro- visions for this area should be analyzed at the development stage when detailed site plans are available. The need for intersection signalization was reviewed to determine needs result- ing from the development of Carrillo Ranch. Traffic signal warrants have been adopted by the Federal Highway Administration and CalTrans. These warrants are based upon the eighth highest hourly volumes in a day. It is generally assumed that the eighth highest hour is 6~ percent of the peak hour and the peak hour is 10 percent of the daily traffic. Thus, the signal warrants can be expressed in terms of peak hour and daily traffic as shown in Table 6. • Comparison of daily volumes indicated on Figure 5 and the warrants in Table 6 indicates that signal- ization will be required at the following intersections: Palomar Airport Road and Industrial Way (West Collector) Ralom~r Airport _Road and Melrose Avenue Melrose Avenue and Collector South of Palomar Airport Road. Melrose Avenue and Carrillo Way ON-SITE CIRCULATION ANALYSIS The on-site circulation system was reviewed with respect to traffic operations and safety. Figure 5 illustrates the basic on-site circulation system. Not all local streets are included on the illustration. Daily volumes arc indicated on Figure 5 ·for the collector system at their connections to the arterial· system. All projected volumes are within the 5,000 daily vehicle volume for Collector Streets of the City Standard except the westerly connection to Palomar Airport C C C C C 0 0 0 0 0 l 0 0 0 0 0 0 0 0 Table 6 SIGNAL WARRANTS -.. -... Warrant Minimum Urban Traffic Volumes Entering Intersection * · Major Street (Both Approaches) Minor Street (Highest Approach) 1 lane 2+ Lanes 1 Lane Daily Eighth Peak Daily Eighth I Peak Daily Eighth Peak Daily Highest Hour Highest . Hour Highest Hour. Hour Hour Hour .. Minimum a.ooo soo,•, 830 9,600 600•: I 1,000 2,400 150* 250 Vehicular Volume ' ! Interruption 12,000 750* 1,250 14,400 900i: , 1,500 1,200 15* 130 of Continuous I Traffic ! ~ * Source: ·calTrans and Federal Highway Administration adopted signal warrants. *'I: Right turns are. not included when calculating approach volume. 3,200 1,600 2+ Lanes Eighth Highest Hour I I l 200* l i I 100-1, I 0 Peak Hour 330 170 I ~ I-' I 0 -----. -- '" -"--~ ........ • ---- ...-----------· • I ■ ~~'--••~••-••-■-••--■---■-■■-■ t -----·-. _-::;;;;;,~-;.: -{ . -~~ PURPLE~. -~--! \ ~ _)_ \._ .. ~ ! ' -~~~~, ! . • ~ \ i ~--. \ ---ORANGE \\ i ..__._ 755du \\ \l BROWN . \ \ 263 du '/ I 1733 du / BLU~_j I. -~ \ I· -~--( •• ( • . ~--. L--·· --~ I L. 'l p----'--~~__:.:) · RED I I . 99du • ~-r-··-·---··-··---•·-·· "\. \ GREEN 148du .. i \J \ ---------· [p)~~~~~~ RANCHO EARRlhLD FIGUAE 7 A PLANNED COMMUNITY BY CARLSBAD, CALIFORNIA O ;on ,..,_, :,,a) THE WOODWARO COMPANIES. THE MEISTER COMPANY. !NC.. & DAON CORPORATION __ , __ ~ .. ·.: • ... 0 0 0 0 0 0 0 0 C 0 0 0 0 0 0 0 0 0 0 I -12- Road. The 8100 daily trips on the ·segment would indicate that a four lane fac- ility would be required between Palomar Airport Road and the first intersection within the project. At Palomar Airport Road, a left, through and right turn lane would be required. A future connection to the west to the extension of El Fuerte Street is indicated on the plan. This connection would be constructed with the development of the property to the west of Carrillo Ranch. This future connection will reduce the number of trips at the westerly connection to Palomar Airport Road. The internal street system is designed with no four-leg intersections which is a desirable feature with respect to traffic safety. In general, there are no cul- de-sacs of excessive length within the project. An exception is the area in the southeast quadrant of Palomar Airport Road and Melrose Avenue. Access restrict- ions on the adjacent arterials, terrain and site boundaries result in a single access to this area. It may be necessary to provide some type of emergency access to this area to satisfy fire and police needs. Additional review of internal . circulation, including intersection design should be made during tract map review. CIRCULATION IMPROVEMENT PHASING Full development of the Carrillo Ranch will occur over a period of time and cir- culation facilities can be progrruwned to cuinclde with the phasing of d~velopment. A phasing plan-has been proposed by the site planners and has been examined with respect to circulation needs. These phases are illustrated in Figure 7 and their attendant circulation requirements are summa~ized in Table 7. The extension of Melrose Avenue from the southerly boundary to Alga Road and the extension of Alga Road from El Fuerte Street to Melrose Avenue would be required at project completion as indicated by the projected volumes in Figure 4. Con- struction of these links would be related to the location of developments within the project and adjacent development. It is recommended that the need for these extensions be reviewed as tract maps arc submitted. Although a part of the overall project, full improvement of Carrillo Way and Melrose Avenue southerly of Carrillo Way are not required to serve traffic until adjacent land is developed. It has been assumed that connections to existing arterials would be provided if isolated areas are developed. PHASE Green Red Orange Brown Blue Purple -13- Table 7 CIRCULATION IMPROVEMENT PHASING Carrillo Ranch . DESCRIPTION 148 Dwelling Units 99 Dwelling Units 755 Dwelling Units • 263 Dwelling Units 1733 Dwelling Units Industrial/Commercial CIRCULATION IMPROVEMENTS Full El Fuerte Street within project Full Melrose Avenue from Carrillo Way to southern boundary~ Improve half of Palomar Airport Road and Melrose Avenue from Palomar Air- port Road southerly to first inter- section. Traffic signal at Palomar Air- port Road and Melrose Avenue. None Full Melrose Avenue .from first in- tersection south of Palomar Airport to Carrillo ~ay and Carrillo Way from Melrose Avenue to western bound- ary. Traffic signal at Carrillo Way and Melrose. Improve half of Palomar Airport Road and Melrose Avenue from Palomar Air- port Road to north boundary. 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ,0 10 0 The City Staff has recommended changes to the Circulation Improvement Phasing summarized in Table 7 and these recommendations are discussed below . . Green Phase. The Staff recommended the signalization of El Fuerte and Alga. As indicated in Figure 4, project traffic would not warrant signal- ization of this intersection. Ultimate development of adjacent ar.eas may result in the need for signalization. A s~aring of the cost of the installation could be a requirement for Rancho Carrillo. -14- Red Phase. The development of Melrose between the project boundary and Alga is a requirement of the adjacent project. If it is not built when the Red Phase is developed, it could be a requirement of the project. The construction of half of Alga from Melrose to El Fuerte is not required to provide access to Rancho Carrillo and is also a requirement of adjacent development. Orange Phase. The traffic signal at Palomar Airport Road and Melrose recommended by the Staff has been.added to Table 7. Full improvement of Palomar Airport Road from the Western Boundary to Melrose is not required-to provide access to ~he Orange Phase. A half section would provide for four lanes with left turn channelization at the interse·ctions with a capacity of 20,000 to 40,000 vehicles per day. There is no need for the cons~ruction of Melrose southerly of the first intersection with respect to access to the Orange Phase. Brown Phase. The construction of roads (El Fuerte) outside the project boundary is not a realistic method of providing access. If the Brown Phase is developed prior to the Orange Phase. the planned.on-site access road should. be constructed from Palomar Airport Road southerly. Access to ~he Brown Phase can only be precisely determined at the time that development is proposed. Blue Phase. The traffic signal on Melrose at Carrillo Way recommended by Staff has.been added to Table 7. As a minimum. the improvements listed in Table 7 would be required. Additional improvements of Melrose may be required if adjacent phases .. (Orange and/or Red) •have not been developed at the time the Blue Phase is constructed. Purpfo Ph:isa.. The Staff did not recommend any changes to th~ phasing indicated in TJbl..: 7. In the case of all areas of the plan, circulation and access provisions will need to be reviewed as tract maps are submitted. Due to the various property owners involved in Ranch Carrillo, the order of development cannot be determined at this time. The phasing proposed in Table 7 is intended to provide a general guide to assist.in determining precise circulation improvement requirements for each individual project. SUMMARY -15- The study has examined the traffic factors related to the proposed Carrillo Ranch development. Recommendations have been developed for the circulation system and are sunmarized in the followirig,section of this report. Principal findings of. the study are the following: l. The project at full development will generate 53,840 daily trip ends with 3,060 occurring during the AM peak hour and 5,780 during the PM peak hour. 2. Based upon··carlsbad General Plan definitions, it was assumed that approximately half of the commercial trips will originate within the project and not impact the external street system. 3. The planned street system with the exception of Palomar Airport Road is adequate to accommodate the project traffic as well as ' . • other projects in the area. 4. The two principle.intersections on Melrose Avenue will.operate at an acceptable Level of Service upon completion of the pro- ject. s~· At ·ultimate development potential capacity problems were ident- • • ified at Palomar Airport Road and Melrose Avenue due to overall area development. 6. While intersection spacing alo~g Melrose Avenue does not conform to City Standards, it ·is necessary to serve the project and does not significantly impact traffic operations. 7. On-site circulation was found to be adequate with respect to traffic operations and safety with the receommended improvements. 8. The circulation and development pqasing plan summarized in Table 7 will be adequate to serve the project. 0 0 0 0 0 0 0 0 0 0 0 0 0 0 'O 0 0 0 0 0 0 0 RECOMMENDATIONS The following improvements and modifications are recommended to provide the re- quired circulation system to serve the development. -16- l. The intersection of Melrose Avenue and Palomar Airport Road should include provisions for the lanes as indicated in Table 5. 2. The need for increased east-west roadway capacity should be further evaluated on an area-wide basis. 3. Access to the parcels north of Palomar Airport Road from Melrose Avenue and Palomar Airport Road shoul~ be limited to right turns in and out only located as far as possible from the intersection with ad~itional analyses conduc~ed when detailed site plans are available. 4. Traffic signals will be warranted on Palomar Airport Road and the West Connector; on Palomar Airport Road at Melrose Avenue on Melrose Avenue and the first intersection south of Palo11UJ.r Airport Road; and on Melrose Avenue at Carrillo Way. 5. The west connector to Palomar Airport Road should have provisions fo~ four lanes southerly to the first int~rsect!un . . 6. The internal street system including intersections and access routes should be examined when tentative tract maps are available. * * . * * * * We trust that this analysis will be of assistance to you in the planning and development of Carrillo Ranch. If you have any questions or require additional information, please contact us .. Respectfully.submitted, WESTON PRINGLE AND ASSOCIATES Weston S. Pringle, P.E. Registered Professional Engineer State of California Numbers Cl6828 and TR565 cc: Mr. Peter Templeton WSP/lu 119530 -17- 0 0 C C C C 0 0 0 0 0 0 0 0 0 0 0 Al'l'lrnll IX A EXPL\NATlON 01: 1.NTER!iEC'l'lllN CAPACITY U'rll.IZATHJN ----------------·--------- The capacity of a street is nearly always greater between intersections and less at intersections. ·The reason for chis is that ~he traffic flows continuously between intersections and only part of the time at intersections. To study intersection capacity, a ·technique known as Intersection Capacity Utilization ({C.U) ha8 been dcvc:Joped. ICU anulysi:; cunsist8 of (..i) dL't~rmining the prb- pul"t.iun uf 1:Jignul. t.lmc: n~edcd tu H(.•rve 1.wch con_fl lctln~ movc~1it, (b) summing the times for the movements, and (c) cumpul"ing the total time required to the time available .. For example, if for north-south _trnff.ic the northbound traffic is 1,000 vehicles per hour, the southbound traffic.is 800 vehicles per hour, and the capacity of either approach is 2,000 vehicles per hour of green, then the northbound traffic is critical and requires l,000/2,000 or 50 percent of the signal time. If for the east-wes·t traffic, 40 percent of· the signal time is required, then it can be se~n ·that the _ICU is 50 plus 40, or 90 percent. When left-tum phases exist, they are incorporated into the analysis. As ICU's approach 100 percent, the quality of traffic-service approaches Level of Service E, as defined in the Highway Capacity Manual, Special Report 87, Highway Research Berard, 1965. Level of Service is used co·describe quality of traffic. flow. Levels of Service A to C ope?'atc quite wcl l~ f.(.•vcf of ScrvJcc O LH Lyplc:11 ly the T.cvul uf Sc:rvlcL• for which an urb.in ::slrl.!cl ls U(.•sl~nc.:u. Lc.tVl!.l uf S'-·L;v fc~• I~ Ls the m.ax.imum volume a facility can aci:uuunudalc ancJ wifl result ln possible stoppages of . momentary duration. Level of Service F occurs when a facility is overloaded and is characterized by stop-and-go traffic ~ith stoppages of long duration. A description of _ the various levels of .se.rvice appcars on the following page. The ICU calculati~ns assume that an intersection is signalized ·and that the signal 1.s !dually timed. Although calculating ICU (or an un:-..ignalizcd intcrsL~ctluns 1:; nut valid, the prc.::,;umptlun 1.:-; that a lili~n.il cun bl:! installc<l and the cnlcul.~atJ.on shuwH whctlu:r Lhe g(.•otnutr1cs aria! cupablc ul accummuuatlug·thc cxpcct&.!u volunu.:. lt b posH.ible to huvt: an_ LCU W4.:ll below .L.O, yet-havu severe tr.iffic cung&.!stiun. This would occur because one or ~re movements is not getting enough time to satisfy its demand with excess time existing on ·other moves·. Capacity is often defined in terns of roadway width.· However, standard lanes have approximately the same capacity whether they are 11 foot or 14 foot lanes. Our data indicates a typical lane, whether a through lane or 'left-iturn lane has a capacity of approximately 1600 vehicles per lane per hour or green time. The Highway Capacity Manwil found capacity to .b~ about 1500 vehicles ·per lane per hour of green for through lanes and 1200 vehicles pcr lane per hour of green for luft-turn lanes. llow1.!vcr, Lh4.: capacity numu.11 i.s bm,cd ori pre-1965 data, anu r~cunt studi~s and ob::mrv:atlons shnw h.ii;hcr c:ap .. Lc:i tics· in the southern C.illfornfo area.· fur thi.:; sLu<ly a capacity of 1600 vuhidu!:> per lane has been assumed for through traffic, an<l 1600 v~hic·lcs per lanl! (or turning lanes. Level of Service B C I) APPENDLX ll TRAr'FIC QUALITY l.1Jw· volumt.•::i; h.i.gh-spu.::us; sp1.·cd 11uL rc~;Lrlt:L1.·<l by othc:r vuhlr:luH; .:11 I sl~n.tl eye I.us dear with no vc:hlcJ~s wai.tlng through murc th.:in . one signal cycle. • ' Operating· speeds beginning to be affected by other traffic; betwe·en one and ten· p(!rcent_. •· of the signal cycles have one or more vehicles which wait·· through more than one si'gnai cycle during peak traffic periods. Operating speeds and maneuverability closely controlled by other traffic; between 11 and }O percent of the signal cycles have one or .. more vehicles which wait through more than one signal cycle during peak truffle p~riods; . rucommundcd • idu,1 l design s·t.:iridard ._ 'l\1 I 1.• r.1b IC • opt.• r.at f Ilg sp1..•1.•us; ·• J 1 l.11. 70 pc-n:1.in_t ul: Lhc-~ig11.:1l ,.:yell.!:,; hav1.•·unc.! ur 111ur1.• vl.'!1ic.lus which wait through muri:: thun ont: s.lb•nal cycle during_ peak .traffic periods; often used as design standard in urban areas. Ca_p:u:ity; the nwxi.mum tr:1rr le· vulluai~• ;m inL1.~r- i:;ccLlu11 «:an aq:ummudaLu; ·rusLrh:L1.·d H('c1.·1.h;; it.to 100 p«.!rc~nt.of the signal cycles havt:! one or more vehicles which wait through more than one signal cycle during peak traffic periods. " Nominal Range of ICU (a) o.uu -0.60 0.6J), -0.70 .. 0.70 -0.80 -- .. .. 0.80 -CJ. 90 ' ., ' 0. 9() -1.00 •' .- Long queues ot tr.af·fic; unstable flow;~ stoppages of· long duration; traffic volume and traffic:.· spce4. can drop to zero; ·traffic vcilum~ will be· lt!ss than the volume whlch occurs .it l.cvuJ of Sc_L"Vicc I::. Not Meaningful_ (a) ICU (Intcr:icction C.:ap.u: ity Utilfa:1tion) at various h•vul 1JI° ,-.l.'l"Vil·1• v1•r:-;11:; l,•v .. l iii ~a•rvi1·1· E l11r 11rl1;111 n1l1"1i:il ,;tl"l.'l•I:;. Suuri;c: lli.li!_1w,!J' C.::IJ•aciLy Manu~il, lligltw:1y Rc:;1.•:1n;h l.loard Special Rcp.,t·t H7, N.:1tio11,il. i\c;Ldl.~IIIY nr Sci1 .. H1CCH, W.1:;hingLlHl n.c.:., 1965, ragl.! J~O. I I i J 0 I I : I ! ! 0 i I I 0 0 0 0 0 C 0 I I@ I I @ ' I I APPENDIX C INTERSECTION ANALYSES TNTERSl•:C:TTClN VOLIIMES AND t:APACTTlES In c~rscc t iun ...l.P_.A;;;i,.(i.-;.r.,..z ..:i~A~A=l<-::...18;....i.JI C,,1:a:a.JPi;;..i..O:.t.!?,-1~C.:::..i-D:::.. • ..,./~M;i..:F.;_.(...::,,C,...,Q5...-....,._r=_.;;A;..,\J.;,i..:,,E ....... - PALruAe A-rePGR--t g.o. LEGEND ... Vo lumt! (V) Lan1:S /0'5 I lbOO o.o, NL ';(- Z/~ 2. 32.CC o.c7 NT D t 34-0 I lbOO 0.2 NR WR /bDO o.z 1.rl t 1"11· 11 l",•.-lu'I Lt>n~t•1s Move-Vohlme Length menc (feet) NL SL EL WL 111111( Int:~rsect:ion Capacity Utilization (ICU) Movement V/C (._ t'l.30 r.apac: i ty (C:) V/C .._..:.1 ~n;...r __ ....... :....' ._o__., _ ___, ~-= :;.::-i::-::.o·md; S = Souc:hbound; E = 1-:ast:b1Jund; W = W,-,..cb,•un.i T = !hrnuih; R = aight; L = Left: * C:-i :ica ~ ~n·1e::::e:nt: inc ludcd in rr.u :;umrnar:i(1n WESTON PRINGLE ANO ASSOCIATES E) 0 0 0 0 0 0 0 0 0 0 0. 0 0 0 0 0 0 0 0 A, P'2.oJECT COM PLE.TIDt.J INTl~l<Sl·:C'l'LON VOI.IIMl•:S ANIJ CAl'AC:1TH:S Intct"St!C:t ion PAL OM A&, Ar g_poeT 2.0, / MEL &+?$E AVE· I PAL-OMA2 Af J2Po2-T qp. □----- I z ... LE(:F:ND EL 3SS' I DD 0.22. ~ V,-i lunlC' (V) Lan1:s Capac i tv (C:) V/C SR IZ.'5' I 120 I Ii 0 0,08 NL t D D ST t ZS' I //-1"10 a.oz + SL 60 I /foDO o.a4- I I oo 0./S NR. 5 NT • (1 ir il'stl m .. •,,·1111·111 inc l11d1•d in lt:IJ ·.1111111.11 i1111 WR ft:; --- ~70 2. Left Turn l'ockL't Lt!ngths Move-Volume Length ment (feet) NL SL EL WL .. WT '93'5" z. -32-aO 0,30· zao o.zr -... Inte~section Capacity Utilization (ICU) Movement V/C /JL Q,08 ~, a. oz. Ei o.4-,;- 'NL O.z.l Ye lll'l,u CJ. ()'5" !Cll D.81 WESTON PRINGLE AND ASSOCIATES ULTIMATE INTERSECTION VOLUMl~S AND CAPACITIES Incerseccion ___ r_._A----~ ... e.=-1L-.:.L ... r ... i__,_\A~(,_A ... 'x .... ··-1-/.~ .... ~.1;;E .... <-C' .. ;...;~..;~ .. E-.... A ..... ~ ... 'f ... • ______ _ I CA" Q.Jt '=:P 'MAY Volume (V) Lanes Capacicy (C) V/C 70 /- b :1-r O.CJ4.. ~ NI. 3b z. 0./2. NT D t -Jc SL ~~ I • 0 NI~ WR zo I 1.rt t "1"111 n 1\,du•l Ll•ngths Move-Volume Length ment (feec) NL SL EL WL .. • !boo wr O.o/ l11t,·1 sc•,·1 f,,n (';1p;1,· f IV LIi f 1 l.::IC t,,n t I C\I) Muveml•nt V/C 0. )4. '· ~ -\, /4.. C:. -'") /' .,.., lCtr c.-1~ ~ = Northbound; S = Southbound; E = Eastbound; W = WL•Stb,,uni T = Through; R = Kighc; L = L~fc 1 " C::-ir::ic.:11 :nnvernent included in ICU summatfon WESTON PRINGLE AND ASSOCIATES 0 0 0 0 0 0 0 0 0 0 0 I 'O 0 0 0 0 0 0 0 0 0 0 AT f'\2.ojE'Cr CoMPLETioA./ INTERSf~CTION VOLUMES ANO CAPAC [TIES In cersec t iun ~c...::A:i..12..~2.=-1...I .:::,L:.l;l-::.;(~)...._.i\A.:.,./.1:.A:l.Y..L.-~/~M~F;.._( ..1.i?i;.....i..O.:.a·S...:Ei-....A;..V:....,E; ____ _ c.eg21 q..,r, 'llA":f.. , ... LEGEND. EL <;;" I F.T z. ) I I f.('lO 0. ~ /ID I .... /boo 0.0 Volume (V) Lanes Capncit v (c.) l.•/C: \ SR /boo (I.C)5' NL }i·r 0.31 2-30 z 3200 O.DP. NT ~ D t SL 7~ I , ·, 10 0 NR WR z.o I /600 ("'l_('f 0 -Le• ft '1'11 rn 111 ,c kl• t J.un~chs Move-Volume Lengch menc (feet) NL SL EL WL t,71' /t;i I /l:-CD 0.()/ Intu rsec t i,,n Capacity Utilization (ICU) Moveml!nt V/C fJC o.oS ST a.31 ~-, o.o/ WL o.c-=. ----<" II 01,, o.c,..;- !CIT '("', _.a..c; N = Nurthb,,und; S = Southbound; E = Eastb11und; W = WL•stbounl ! = Thr:iugh; R = Righc; L = Left * C.:-~:ica: '.lltwr:ment incluJi:d in ICU summation WESTOl"-I PRINGLE ANO ASSOCIATES ----~-------··-... ··•· -----·-------() ·--------------------... ---------~ \ ULTIN\~TE \N'1-nl SC.i.lCl(•L SITE. co,-.Jy1:.,£.s1oi...l lNTt-:l,Sl•:t:TIPN Vlll.llMI·:~; Mil> c:Al',\<:ITlt··. Int:~rscc t ion __ c._t:.._R_~_I L_L_o_..:w..;_~_'(.;..._.;./_.;.M .... ..:i:::-::L::..:.;;;~;.;;o;....;;;;S;...E..=-_A.:. ... v ___ E.._,;..._ ___ _ i GA. 2..~ IL'-0 'VI r:,,,., '( 4s .... 1-:1. I ts,oo o,os ER - .__ . SR /ft:,CO 0,4--Z ) 70 ST e,e,o I /<t,00 0,SS' /~O 0,04-1" NL D t SL 0 NR Wl{ 2,0 • /(p00 0,01 l•.f'ft T,::-n Poc~ec L,•n..;tiu; NL SL EL 71111( t.i'J'· /0 I /ft:,00 0,01 i( Inc~rsection C~pacity Utilizaci~n (ICU) 1bO "2. ,--------,.----............ :-,i,,vement \' Ir: V11l111111• !Vl [ ... nws Capacity (l:) V/C )ZOO 0,11 if!' I --..... .__ :\ --N,,.·tldi,,,111d; S ·• S011thh,11md; I~ -l•:,1!-ill11,und; W ·· l,1,,,.c·h,1111\I ! Tl:1,•11•.•.li; !~ •• l,i,:h1; I. -l.,·t'l l .. n.:;. -l.l'Vl'f ,,1 s .. rvicl' , 1it1,·111 """_.,.,11,·11t i111 1,111,.,1 i11 11:u ,:11111111;11 i .. 11 NL ST O,SS EL 0, I 4- w-r 0,01 YELLOW o.os lCI' 0.79 1.-0.S. ~:.s .... :--: .. t ~d>•.11;1li,:1·d -,,.,._,. 1·iv.1i1 111.-11 -In'< :-tin Lmum V /C "-(). I) I WESTON PRINGLE AND ASSOCIATES 0 0 0 0 0 0 0 0 0 0 0 0 0 0 " 0 I I I 'O I lo 0 0 ULTIMb..TE. vJ ,~ .SC..I.IOOL S 1,E. C-o i.J VS. RS I o..J IN11::RSl-:CTWN VOLUMl-:S AND CAl'i\CIT1ES In Ct! t"Sec t fon PA..LOMe...'R.. b.1E.POR.T R.t). l ME..L Ro.s E A,-./E.. ; -D uJ ~ --l.r• f t Turn 1',>t:kl·L ST t G,e,0 Lcngtl1s ,, uJ '2 M1,ve-Volume Length "' ~ 'JZ.00 nll'nt (feet) NT. o.~, ~ -SL ut SR SL EL ~ ,-z.o 4/S Wt. PAl.ot•U.I •• A.lt.ro~.-r l<l). I ,z. I (,:;00 '$ZOO o,oe, 0,13 1-:1. ) l WR □~ /,$() 4;s I I • I I ET /'400 /~00 t,'T l'170 0,09 0,2. 7 /Zfe5 ; '3 4t;oo 4800 0,4/ Jr '2.iS 9~ 0,2.G, I "2 I I ... /~00 :,zoo ... D 0,/j 1 ( 0,30 ~ ER WL . , .. /OS 34S I I /'400 /fo()O ·0,0i k o.zz NL NR Inte~section Capacity "2.IS l!t:iliz:ation (ICV) -2' •.•,,v•::-r..en t ·: Ir:. •• ! ,,2/X) j NL c.07 I LF.l :;.::.;;, o.o-, ST O,ZI MT ET 0,41 § D , .. --Vn 1 umt• (V) vJL 0,30 !..am·~ '(£LLOW o.os Capncity (C) IC!l I /,04 VIC -L-0. S- .• .. = t'iorthho11nd; s -= So11t:hh,,11nd; .. E = l-:;111 th, ,11nd; \.1 =-\.!,·,,tho, 1111 T Tl,r,,,"'l,; .. I'. i;·,I, I ; I. I.,' I I , .. ,,.::. l.,·v, · I :;,.,·vi ,·1• , .. "I (: i r I, 11 I 111, 1•:1 ·1111·11 I i111 l"d,·d I II I 1 :11 ·a1111111.1I i,,u :--..:;. -~'t,, l ,; i )',II.I I· i .... ,,I I 11·1· I I ,•.hi I 111 11 ,..,~ Minimum V/C:. = O.U/ WESTON PRINGLE ANO ASSOCIATES ·- 0 0 0 0 0 0 0 0 .o 0 I - 0 APPENDIX F CITY OF CARLSBAD COMMENTS ON TRAFFIC STUDY lsa 0 0 DEVELOPMENTAL SERVICES □ Assistant City Manager 17,.-1 '38-5598 □ Building Department l71•1"38-S525 ~ Engineering Department Citp of Carlibab 1200 ELM AVENUE CARLSBAD, CALIFORNIA 92008 0 171.-1 Gl-55it1 0 0 0 0 .0 :0 :o ! □ Housing & Red-iopmant Department 171.-1 "'3N811 □ Planning Department 171.-, <438-591 Annette Sanchez Larry Seeman Associates 500 Newport Center Drive, Suite 525 Newport Beach, California 92660 March 31 , 1981 SUBJECT: RANCHO CARRILLO DRAFT ENVIRONMENTAL IMPACT REPORT The Engineering Department has reviewed the subject report for adequacy of the Traffic and Circulation section and proposed mitigation measures. The data pre- sented and analysis made are generally reasonable and adequate. The report identifies a serious operational problem at the intersection of Palomar Airport Road and Melrose Avenue. The mitigation measures -except numbers 23 and 30 discussed below -are reason- able and adequate. Number 23 recommends a study of the realignment of Palomar Airport Road and Melrose Avenue and number 30 recommends a study of the feasi- bility of an additional east-west route. There are two possibilities as a result of these studies: 1) a realignment or additional route will mitigate the problem or 2) they will not mitigate the problem or an additional route is not feasible. In other words, the studies almost certainly will result in a major redesign of the project or will leave a significant problem unmitigated and the project facing possible denial. Summary: The report and mitigation measures adequately present the problems and possible solutions for the general plan amendment level. Prior to approval of the Master Plan, however, the above studies must be completed to determine their validity as mitigation measures. -~. ~!-/-~)-. Richard H. Allen, Jr. Principal Civil Engineer RHA:ms c: Joyce Crosthwaite, Planning Dept. I i lo 0 lsa 0 APPENDIX G AIR QUALITY ANALYSIS 0 0 ,0 0 0 0 0 0 0 0 ·o 0 0 0 0 0 0 0 0 lsa □ 500 new port center drive, suite 525 newport beach, california 92660 phone (7~ 4) 640-6363 □ 2927 newbury street, suite c berkeley, california 94703 phone (415) 841-6840 LARRY SEEMAN ASSOCIATES, INC. AIR QUALITY ANALYSIS FOR RANCHO CARRILLO ·PREPARED BY HANS GIROUX CONSULTING ASSOCIATE. LARRY SEEMAN ASSOCIATES, .INC. 500 NEWPORT CENTER DRIVE, SUITE 525 NEWPORT BEACH, CA 92660 (714) 640-6363 MARCH 23, 1981 1 lsa AIR QUALITY.ANALYSIS FOR RANCHO CARRILLO METEOROLOGY/CLIMATOLOGY The Mediterranean climate of North San Di ego County I s coast a 1 areas, as with all of Southern California, is controlled by the moderating effects of the vast nearby oceanic heat reservoir, and the air circulation within the semi-permanent high-pressure center, usually located between California and Hawa.ii. The climate is characterized by cool summers, mild winters, fresh daily onshore breezes, comfortable humidities, and low rainfall confined to the wfnter months. Moist maritime air passing over cool coastal waters pro- duces considerable low coastal stratus clouds that change to hazy daytime con- ditions during the heat of the day. A second manifestation of the shallow layer of cool marine air is that when it is capped by a large dome of warm, sinking air in the Pacific high-pressure cell, the boundary between the cool marine and warm subsiding air forms an impenetrable temperature inversion that traps air pollution within the marine air layer. While Southern California has a unique climate that attracts and maintains a gr·eat population density, the inability of the atmosphere to disperse the air pollution generated by the large population creates one of the worst air quality climates in the United States. Temperatures average 60°F annually with cool summers (68°F) and mild win- ters (54°F). Extremes of temperature are rare, with few days in excess of 90°F or temperatures below freezing. • Rainfall, in contrast to the small diurnal and seasonal variations of temperature, is highly variable. Almost all of the annual precipitation of 10 inches falls from late November to early April. Monthly and annual totals vary greatly, such that monthly precipitation in a 11wet 11 year may exceed the entire annual total during drought conditions. Winds are an impo.rtant parameter in determing the air quality impact of additional project-related air pollution sources because the wind speed gov- erns the local (micro-scale) dispersion near a source and the direction gov- erns the regional (mesa-seal e) trajectory of those emissions. The closest wind records to the Rancho Carri 11 o site are from ·pa 1 omar Airport from data taken for the once-proposed Macario Canyon oil refinery. These data show that onshore winds from the southwest through northwest dominate for much of the year except in winter when nocturnal winds reverse and blow offshore. In sum- • mer, especially during the day, emissions generated in Carlsbad are blown far inland by strong sea breezes and are dispersed over the coastal ranges. In winter, especially at night, the offshore winds and subsequent weaker onshore C C 0 0 0 0 0 0 0 0 0 • • 2 lsa winds balance such that some localized pollution stagnation may result. The directional frequency distribution of the Palomar wind data (wind rose) is shown in Figure 1. Because of the difference in the land/sea breeze distribution, there is a corresponding seasonal difference in air pollution dispersion patterns. In summary, the air pollution sources impacting the Carlsbad area are far upwind and the impact of any locally generated emissions is far downwind. In winter, the source and impact of air pollutants occur in a much smaller area. With clean ocean air usually blowing across North County, and with considerable open space and limited emissions sources, the air quality near the project site is usually healthful and among the best in the County. There are times, however, when the polluted air from the Los Angeles Basin drifts southeastward offshore at night and then comes onshore across the North County area the next day. When this polluted air mass passes near the project site, it creates very unhealthful air quality conditions and is responsible for several epi- sodes of the worst air pollution observed in San Diego County in the last decade. Each of the onshore/offshore wind patterns is accompanied by a character- istic vertical temperature structure (usually an inversion) that affects the air quality impact the proposed project will have. During the warm months, the warm, sinking air of the Pacific high-pressure center forms a lid over the area that inhibits vertical mixing. As the clean ocean air moves inland, each source adds more pollutants from below while no dilution takes place from above. As these trapped pollutants react under abundant sunshine, they form the notorious eye-burning photochemi ca 1 smog often found at in 1 and receptors. In winter under calm conditions, cold air pools in low-lying elevations while the air aloft remains warm. These light winds and shallow inversions trap po 11 utants near a source such as a freeway and form 1 oca 1 i zed po 11 ut ion "hot spots," especially from vehicular carbon monoxide and oxides of nitrogen. Few locations in North County have sufficient traffic to generate enough emissions to cause any hot spots, but the growth of the area raises some concerns about possible local air quality degradation. AIR QUALITY In order to determine the significance of the air qua l i ty imp act of a project, that impact, together with baseline air quality levels, must be com- pared to the applicable Ambient Air Quality Standards (AAQS). These standards are the levels of air quality considered safe, with an adequate margin of safety, to protect the public health and welfare. Standards are designed to protect those people most sensitive to further respiratory distress such as asthmatics, the elderly, young children, people already weak from illness, people in heavy exercise requiring deep breathing, etc. Most healthy adults 3 1 Wind Rose w lsa N E s Location: Palomar Airport , Carlsbad, CA. 1972-1973 Frequency of Calms: 7 .96% • • • • 0 0 0 0 0 0 0 I 0 0 0 0 4 lsa can tolerate somewhat higher exposures before adverse effects are noted. Mea~ sures to reduce the margin of safety to trade off the cost of air po 11 ut ion abatement against an ''acceptable level of risk" are now under consideration by the new Federal administration. The current AAQS are an outgrowth of the Clean Air Act Amendments of 1970. National standards for six (now seven) pollution species were developed by the Env i ronmenta 1 Protection Agency (EPA) • States retained the right to estab 1 i sh more stringent standards or to adopt • standards for di ff eri ng expo- sure periods or different pollutants. Since California already had State standards in existence before the . Federal action and has unique air quality problems, there is considerable diversity between State·and Federal AAQS. The standards currently applicable in California are shown in Table A. In the case of conflicting State and Federa 1 AAQS, the most stringent standard is to be enforced. Because of Carlsbad's geographic position relative to the occasional recycling of Los Angeles Basin pollutants through North County, the project area has some of the worst air quality in San Diego County. Ambient air qual- ity measurements at the closest San Diego Air Pollution Control District (APCO) station at Oceanside suggest that on most days the incoming ocean air is except i ona 11 y po 11 ut ion-free. During the intrus i ans of po 11 uted air from populated and industrialized areas to the north, however, the ozone levels in the project area are sometimes the worst in the County. For whatever meteoro- 1 ogi ca 1 reason, the stat i ans at Oceanside and So 1 ano Beach recorded the on 1 y second stage photochemi ca 1 smog epi sades in ·the County in a 1 most ten years, and these were observed in the late 1970s when pollution clean-up had suppos- edly significantly reduced emissions of hydrocarbons and NOx, the raw mate- rials that create the smog. Fortunately, the number of days when the high oxidant levels are observed is much less than in other inland County receptors exposed to coastal area precursor emissions, but when the smog episodes occur, they are very unhealthy for all individuals breathing the polluted air. Table B summarizes the last five years of air quality data at the Ocean- side monitoring station (1980 data have not yet been published). Particulates and ozone, the two species generally related to regional airflow and photo- chemical processes, often exceed their respective standards. Of all the basin monitoring stations, Oceanside often has the highest dust and smog 1 eve 1 s. NOx, S02, and CO,· the species usually linked to local pollution sources, are typically below AAQS levels because there are only limited sources of these pollutants in the North County area. Any ambient air quality problems near the project site are, therefore, the result of pollutants carried into the area from other source regi ans rather than any 1 oca 11 y generated emi s- s ions. C TABLE A 5 C AMBIENT AIR QUALITY STANDARDS lsa C -,..,_ A...-....T-• CMifGfflieSI-Naciall• S.._,., c:-••11111io11 M•tllOd l'rim•tY s .......... .., Met-· Qaiclan1 1,-. 0.10 DOffl Ullra,,10191 ---f200u,v...., 1'1101-11, 0-I"---2COu91m• S-n Primar, i:.,_...,,,,,., .. c■nt 10.1% Ollffll SUftd1td Meutca 0 C:.,.,.MOMaidtl 12:i-IODOIII - 111 ""''"'" SMlleH '"-N_0,1oltliwe NcNt00is;■rsn,• -1n1,., ... 10 m91m• Pnm.,., lldntld Specrroscagy ISDllffll sa-..u S-.;opy I !lour ,&Q-"01119.tm• (Clm;lm'! 135 :::ml NilrogM0io:lide. AllnullAve,1911 -100 u91m• G .. ,i,, .. 10.05 ooml I lleur 5411Zffl■n Melllocl s ..... aal'rim.,., 0i.m,1-•scenc1 ~ 0.251111m -~ ... 0 (470uq.lm'I S..U...Oiaude ~"-·•· -80u9tm• -(0.0lPOml 241iow 0.05 DDIII lHu9/,... - 1131 •"'" Coftdua1fflfllic C0.14 DD~I ,._,,,.n11e .Metllod Meulod :in----llCOuq/,... 10.5 Pllffll 111aw· 0.5gpm --n:uouvm'I 0 s....-. .. All11111IGeometric eo.,..,,,.. 7Su91111• '° 1191'm• PlftlCUIII■ M■an KlqltVolu--Hi911 Vilha-Mallff 2•-100i19.lm' , Samot,119 21101191 .... 150uq.lm• 5-ldl9 S.,lflln 24llaul 25uql .... AINL M9Clllld ---. NA. 51 Laad lOay 1.Su9',... AIHL MatllOcl -I ..,. -... _..,_ NCL 5.& 0 CMet1du --l.5uq.tml 1..Suvm• Ala<IIIC Q11a,1e, Allaatllll<OII ~--1"-0.03-~llffllUffl ---Sullid■ (4ZuG.f...., '4¥druc■ s1,ae1:u MetlU>d ~--311---150 u9/m' Sam••• Flame loN11110" (CGrrectdfor (S-9un.J 10.24ppml Prim■,., ' D••-U11n9 Mes11■ne1 s•-••"• Gas01...,.a1c,q,a,.,,., V"lft'/!01/a,ida 24 llour 0.0tOPOIII Gu Cllrom1109, 0 (Qllaraeclletl■I 1211ua1m•1 rao,,., r,,..18 srall ''"'"" 78•8·.31 Elflyl-· S llout -0.1 l)pffl ----111.w 0.5 001ft Vlsillilir, 1-llion In suflicillll amevnt 10 R-cin9 reduee ,,,. o,..,.,.,~ ..,.,11~•1\' Pamcln to lfla 111a11 10 mllos wne11111• relaliv■ 1111midi1Y ,s Ins 11'1n 701---- APPUCABLS ONLY IN THE LAKE TAHOE AIR BASIN: 0 C.,oonM1111n1de Sllout s ppffl I NOIR .. ---C7_m9/m'I VilillililY I 011SetYa1,on tn suHietcnt amoun1 to R-c,119 reduce lh• fll'fflflJlhfltJ 'VISIO"•lY ---P'sn1d■s to l11a Ill~ .30 mite■ when 1no ,.,_ llufflldlty ,s less lh4n 70" 0 0 0 0 TABLE B 6 CARLSBAD AREA AIR QUALITY SUMMARY lsa 0 1975 1976 1977 1978 1979 Days Days Days Days Days Over Hr.* Over Hr.* O_ver Hr.* Over Hr.* Over Hr.* Pollutant Standards Std. Max. Std. Max. Std .• Max. Std. Max. Std. Max. 0 Ozone 1 hr > 0.08 ppm 43 Q.19 69 0.29 87 0 .. 25 71 0.35 0.36 l hr> 0.10 ppm 0.19 0.29 61 0.25 51 0.35 45 0.36 l hr> 0.12 ppm 0.19 0.29 22 0.25 20 0.35 22 0.36 l hr> 0.20 ppm 0 0.19 0.29 2 0.25 5 0.35 7 0.36 0 Nitrogen dioxide l hr> 0.25 ppm 1 0.31 4 0.33 2 0.36 2 0.32 a 0.21 Carbon monoxide 8 hrs > 9 ppm 0 10 0 10 a 8 0 9 0 10 0 Hydrocarbons I 3 hrs> 0.24 ppm 179 4.0 222 4.2. 243 4.5 211 4.0 I i Sulfur dioxide 1 hr 1. a.so ppm· 0 0.03 0 ,0.06 0 0 0.03 0 0.06 0 ... Particulates 24 hrs> 100 µg/m3 251 172 20% 146 21% 173 40% 219 ·33% 180 Annual > 60 µg/~ -83 82 82 88 85 *In ppm, except for particulates in µg/m3 0 Source: San Di eg_o APCD, 1975-79 0 0 0 7 lsa The fact that much of the North County source of episode-causing air pol- lution is from outside the air basin presents a serious problem in terms of air pollution control. Over the last few years, the Comprehensive Planning Organization (CPO), the APCD, and other agencies developed an Air Quality Man- agement Plan (AQMP) under the acronym RAQS (Regional Air Quality Strategies). The basic premise of RAQS is as fo 11 ows: • The San Diego Air Basin is as·sured of meeting all AAQS as required by the Clean Air Act ,Amendments of 1977 if the following assumptions ·are correct: --The air quality model used to correlate the source/receptor relationship is accurate. --The required legislation is established at the State and local levels. --The future growth patterns are consistent with the 1 oca- ti ons, growth rates, and land uses used in the CPO's Series V projections. • --The future population behavior as to driving patterns, ener- gy consumption, transit utilization, and lifestyle are rea- sonably well predicted. --The air coming from the South Coast Air Basin is pollution- free. If al 1 these assumpti ans are correct, then Rancho Carri 11 o and any other planned growth will not have an adverse effect on regional air quality. Unfortunately, the critical cornerstone of the' RAQS program, a mandatory. vehicle inspection program, has not been passed by the State legislature. The air coming into the project area is not getting any cleaner, and unless there are drastic changes in the next few years, it is highly doubtful that the air quality attainment deadline can be met. AIR QUALITY IMPACT Several general conclusions about the air quality impact from multiple land use growth can be inferred from the impact observed from hundreds of sim- ilar developments. The major air quality impact from any such development results from the dependence on the automobile as the primary means of trans- portation. Because vehicular emi ssi ans, by their very mobile nature, are widely dispersed in space and time, any single development usually does not of C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 :o 0 0 0 8 lsa i tse 1 f contribute enough po 11 utants to cause, AAQS to be exceeded. Rather, each vehicle adds a very sma 11 additi ona 1 amount of unreacted pol 1 utants that directly impact the local environs and then move downwind and· react to cause regional air quality degradation. It is almost impossible to detect the air pollution 11 signature11 of only a few vehicles, but when the air pollutants from over one million·vehicles in San Diego County are combined,. the characteristic air quality problems observed over much of the basin result. In addition to vehicular emissions, the dust generated during construc- tion activities and the consumption of energy requiring the combustion of fos- sil fuels are also significant project air quality impacts. The impacts of such sources tend to be less severe, more localjzed, and somewhat more easily controlled than those of .the ubiquitous automobile. : For all of the growth- related air pollution emissions, the e!!lissi on rates and future transportation and energy use patterns -are not well known •. Although these emis•sions and their impacts have been quantified as well as possible in the following sec- tions, these imp~cts must be reg~rded as. best estimates rather than as highly precise· impact predictions. Construction Impacts. During ·construction activities, clearing, grading, travel on unpaved surfaces, material hauling, and employee commuting to the.construction site will cause various .air pollutants to be added to the regional burden during the construction period.-By far, the generation of fugitive dust from soil disturbance,-. while temporary, is the greatest air quality concern of intensive construction activities. Based on a total proj- ect phasing of ten years and an average individual project-intensive construe-\ ti on period of six months , about 40 acres wi 11 be undergo, ng canst ruction activities at.any one time. The EPA suggests a construction/demolition fugi- tive dust emission factor of 1.2 ton/acre disturbed/month of activity. The emission rate can be_· reduced by about one-half through regular watering for dust suppression as required by APCD. Rule SO. At the controlled fugitive dust emission rate, about 0.8 ton of dust will be r.eleased each day during con- struction. Much of this dust will settle-out on nearby hori zonta 1 surfaces such as vehicles, buildings, foliage, etc. and may cause a soiling nuisance to downwind receptors. A portion of the 0.8 ton/day will remain suspended and mix with the several hundred tons of particulates emitted within the air basin each day. Compared to regional emission levels~ the project-related emissions are nominal and any corresponding regional ambient air quality impact will be similarly small. It should be further noted that the construction dust is typically chemically inert and of a Jarge particle. diameter. readily filtered in the human upper respiratory tract. Such dust emi ss i ans are, therefore, typically _much less unhealthful than the finely •divided organic mists of polluted urban atmospheres that are easily inhaled far into the lungs and absorbed by the bloodstream. 9 lsa Combustion emissions from heavy-duty equipment, trucks, and portable equipment will also be released during construction. s.uch emissions are extremely small when compared to the air pollution resulting from +25 million vehicle miles driven in the County each day. As w.it_h dust emissions, there may be a localized· nuisance from diesel exhaust odor, but any ambient air quality impacts from construction activities will almost never be observed. Vehicular Emissions Impact. Vehicular emissions impact air quality on two primary sea 1 es of motion. The pri nci pal concern is that unburned , hydrocarbons and ·oxides of nitrogen wi 11 combine under abundant Southern Cali- fornia sunshine to·form photochemical oxidants. Since oxidants already exceed AAQS by a wide margin; the additional growth.;.rel ated emissi ans. represent a further burden that must be overcome by concurrent emissi ans rectuct_i ans else- wher~ in the air basin. ·Ona local scale, concentrations of ttaffic, espe- cially during peak-hour congested flow, may create isolated areas of high pri- mary (unreacted) vehicular pollutants generally called "hot spots." Based on the results of the project traffic study, the ambient air quality impact for these two scales of motion is outlined below. Regionally, the indicator of vehicular pollutant generation is the -number of vehicle miles traveled (VMT) by residential, commercial, and industrial. deve 1 opment occupants·. At project buil dout, Rancho Carri 11.o wil 1 generate 53,840 vehi c 1 e trips. At eight mi 1 es per trip, 430, 720 VMT wi 11 be generated • by the project. Compared to the 30-40. milliori VMT dri'ven daily in the basin, Rancho Carrillo will ultimately represent about 1% of all basin traffic. The VMT estimate is based on summing all residential, commercial, industrial, and institutional trips separately. Actua·lly, some of the home-shop, home-work, and home-school trips are. internal within Rancho Cal'."rillo and, thus,. are counted as two project trips when in reality only one trip will be _generated. The more conservative assumption that all residents shop and work outside the project boundaries and that all shoppers and workers come from outside Rancho Carrillo was used because there are no reliable estimates of the internal vs. external trip distribut·ion, but this overestimate should be understood in the following analysis. • • Assumi.ng a linear phasing of Rancho Carrillo with 25% completion by 1985, 75% by 1990, and 100% by 1995, and applying the vehicular emission factors for San Diego Air Basin traffic mixes and driving patterns,· yields an emissions total as shown in Table C. Table C contains project-related emissions data for the basic project plus the ·small additional emissions from a possible school site conversion-to other uses if the school sites are surplus. At. bui l dout, Rancho Carri 11 o traffic wi 11 contribute six· tons of CO, one ton of NOx, 0.7 ton of hydrocarbons, and small amounts of S02 and particulates. The potential additional development adds a little more than 10% above these project-related emissions totals. C C C C 0 0 0 0 0 0 0 0 0 TABLE C 10 RANCHO CARRILLO VEHICULAR EMISSIONS {TONS/DAY l lsa 0 ,, 1985 1990 1995 BASE PROJECT 0 Hydrocarbons VMT-related _ 0.09 0.22 0.29 Trip-related .. • 0.13 0.33 · 0.40 ·- TOTAL 0.22 • ..-0.55 0.69 -·----,. . 0 Carbon monoxide VMT ..;re 1 ated Ll8 2.79 3.49 Tri p;;.fl!l ated _0.77 -2 .. 06. 2.69 - TOTAL 1.95 · .. ,_ 4.87 6.18 0 Oxides of nttrogen o .. 26 0.72 .0.96 Oxides of sulfur 0.02 0.05 0.07 Particulates 0.03 ': 0.10 ... 0.13 0 BASE AND ADOITIONAL POSSIBLE Hydrocarbon's. VMT-related 0.09 • 0.23. 0;30 0 Trip-related ·:'; . 0.14 0.33 0.40 TOTAL 0.23 0.56 0.70 Carbon mo.noxide 0 ·VMT-related 1.20· 2.85 3.55 Trtp.-re 1 ated • 0.7B 2.10 2.74 . ~ .. -- TOTAL • 1.98 4.95 6.29. 0 Oxi~e~ of nitrcigen 0.26· o. 74 0.98 Oxides of ~uifu~ .. I 0.02 0.05 0.07 . 0.03 0.10 0·.13 Particulates I 10 11 .lsa An interesting aspect of the data in Table C, 'especially for. hydrocarbons as precursors to smog, is that as many of the. emissions result from starting, stopping, idling,, evaporative losses after stopping, and inefficien~ combus- tion during start-up as from driving the entire rest of the trip at a steady speed with a pollution-efficient combustion process. It is, therefore, as pollution-effective to eliminate a short trip entirely as to reduce the_ aver- age length of a trip by a few miles. This ·suggests that the polluti.on penalty of extensive North County development away from many major County centers of commerce and employment resulting in longer driving distances can be somewhat offset by integrated project land uses that promote pedestrian,' bicycle, elec- tric cart, or other reduced-pollution means of local travel. Given an emission rate of so many tons/day widely distributed . on the County roadway network, what does t.hat mean in terms of further· i ncrementa 1 degradation of regional air quality? Without complex photochemical air quali- ty models, that is a difficult question to answer. A simplistic answer is to assume that the downwind air qua 1 i ty impact is direct 1 y pro port i ona l • to the upwind source strength. If twice as much air pollution is emitted upwind, downwind ambient air pollution levels might logically be assu!J1ed to be twice as high. Tab 1 e D demonstrates that, at project completion, ' Rancho Carri 11 o will contribute from 0.54 to 0.70% of the entire basin's burden (shown in. line labeled "Base/1987 Target") of the main vehicular pollutants; i.e., hydrocar.: bans, CO, and NOx. To say.. that Rancho Carri 11 o traffic represents. 1/200th of all air pollution, both from all mobile sources and all stationary sources in the basin, attests to the magnitude of this development and the importance in mitigating as much as possible its air pollution impact. The. predicted incremental regional air quality degradation of less· than 1% .of the clean air .standard will obviously not, of itself, prevent the attainment of basinwide clean air; but if the effects of several such projects are combined, there will simply not be enough sources of other pollution reduction to offset the project contribution, and MQS attain·ment, primarily for ozone, will be extremely difficult. Even if regional impacts do not threaten clean air standards, the local accumulation of traffic on Palomar Airport Road could raise local CO concen- trations to unhealthful levels. To test for this possibili.ty, traffic projec- tions from the traffic study for rush-hour conditions were used to·initialize the ·CalTrans roadway dispersion model CALINE3. Vehicular emissibn ·factors were derived from EMFACS, the California-specific version of the national emissions estimation computer model MOBILE!. Hourly maximum CO concentrations were calculated for light winds and stable co·nditions (Pasquill 11F11 Stability and 2 mph winds) with winds parallel to Palomar Airport Road and for _quarter- ing winds across a large intersection such as the future Palomar Airport Road/ Melrose Avenue intersection. The results from the computer dispersion model 0 0 0 0 0 0 0 0 0 0 0 0 0 TABLED 12 RANCHO CARRILLO VEHICULAR EMISSIONS BASIN BURDEN ANALYSIS lsa 0 Hydro-Carbon Oxides of carbons Monoxide Nitrogen Particulates 0 Base project emissions (1995) 0.69 6.18 0.96 0.13 Base and school site emissions (1995) • 0.70 6.29 0.98 0.13 1974/75 RAQS base year 279 1221 187 361 0 1987 target at attainment 127 887 150. 291 Base/1987 target (%) 0.54 · 0.70 0.64 0.04 B.ase ·and school site/ 1987 target· (%) 0.55 0.71 0.65 0.04 0 ,o 0 0 0 0 13 lsa are shown in Figures 2 and 3. In both cases, the maximum one-hour CO concen- tration is six ppm near the roadway edge. This concentration diminishes rapidly away from the roadway and slowly away from the intersection, but is certainly well below the hourly standard of 35 ppm. S"ince neither the· rush- hour traffic nor the . restrictive meteorology remains unchanged over eight hours, the eight-hour CO standard of nine ppm wil 1 al so not be threatened by Rancho Carrillo traffic. Unless regional background ,CO levels· become very high, the localized Rancho Carrillo plus other nearby project traffic will not cause the formation of any CO "hot spots" near the roadway, much less within any populated sensitive receptor sites away from the road. Stationary Source • Impacts. A final source of project impact wi 11 result from the consumption of energy to supply electricity, heat, hot water, etc. Using SOG&E consumption figures for various land uses and dwelling siz- es, 67.8 million KWH and 396 million cubic feet of natural gas will be requir- ed to meet Rancho Carrillo energy needs. Since about one-half of all SDG&E electricity is generated by burning oil at basin power stations, the electric- al demand will cause considerable additional air pollution emissions. By applying APCO-derived emission factors to the oil-fired portion of the elec- trical demand and to the much cleaner-burning onsite natural gas use, the project-related stationary source emissions can be calculated as seen in Table E. Since the stationary source emissions, especially the hydrocarbons that "fuel" the smog-formation reaction, are minimal compared to the vehicular source emissions, the ambient air quality impact from stationary source emis- sions is correspondingly minimal. MITIGATION Si nee much of the proJect impact results from vehicular sources whose emission characteristics are beyond th·e control of local regulatory agencies or developers, there is little potential for significant mitigation of air pollution impacts. Some measures can be implemented to slightly reduce the impacts resulting from ,suburban growth, but these measures represent only a small reduction of the total project-related air pollutant burden. The mea- sures that should be considered during project planning include: Construction Impacts --Use extra dust stabilization measures during clearing and grading. Perform major grading in the spring when soil moisture is h_i ghest. C C C C C 0 0 0 0 0 0 ( 10 ,0 0 0 0 0 0 0 0 0 2 14 Hourly Concentrations (ppm) Adjacent to Palomar Airport Rd. Palomar Airport. Road ~ Wind DirectieA ------------- ~ Travel Lane ~ Travel Lane Bike Lane 5.69 • 5.65 •5_4a 80' • 4.61 • 0.97 Note: quartering winds--hotlf'ly standard• 35-t)pm lsa 3 15 Hourly Concentrations (ppm) Adjacent to Palomar Airport Rd. & Melrose Ave. W~1nd ----------- ~ Travel L~ne Direction ------------- ~ Travel Lane ---- Bike Lane 4.6.9 5.20 5.15 5.04 .1 I 5.58 • 6.09 • 6.04 • 5.93 I 5.50 • 6.01 • 5.96· •s.as I Melrose Ave. I s.30 • s.a1 •s.1e Note: Quartering winds -hourly standard -35ppm 0 lsa Palomar Airport Road 4.99 0 s.as' • s.ao• 0 s.ao• 0 0 0 TABLE E 16 RANCHO CARRILLO STATIONARY SOURCE EMISSIONS ~TONS/DAYl lsa 0 El ect.ri ca 1 Pollutant Generation Natura 1 Gas Use Total Sulfur dioxide 0.,17 Negligible 0.17 0 Hydrocarbons Negligible Negligible Negligible Oxidesof nitrogen 0.11 a.as 0.16 Particulates 0.03 0.01 0.04 0 Carbon monoxide 0.02 0.01 0.03 0 0 0 0 0 0 17 --Pave roads and prevent soil erosion back onto roadways to reduce vehicular dust entrainment. Vehicular.Impacts --Encourage alternate transportation system utilization through subsidized paratransit systems, efficient public transit, carpool incentives, bikeways, cartways and walk- ways, and vehicle-free areas. Maintain adequate roadway capacity to prevent traffic stag- nation. Provide multiple housing, employment, recreational, and com- mercial opportunities within the Rancho Carrillo community to intra-community travel. Stationary Impacts Encourage fossil-fuel energy consumption reduction through conservation and replacement with less polluting energy resources. Develop maximum solar energy utilization through tract lay- out and orientation, passive solar energy capture construc- tion, mandatory solar-assisted heating systems for recrea- tional uses (pools, spas, and community facilities), and include wiring, plumbing, and load-bearing areas in roof designs for future active solar collector systems. lsa 0 0 0 0 0 0 0 0 0 0 0 (} 0 0 0 0 0 ,· • ' vr,' APPENDIX H ENERGY ANALYSIS ' lsa 0 0 0 0 0 0 0 0 0 0 lsa C 500 newport center drive. suite 525 newport beach, california 92660 phone (714) 640-6363 □ 2927 newbury street, suite c berkeley, california 94703 phone (415) 841-6840 LARRY SEEMAN ASSOCIATES, INC. ENERGY ANALYSIS FOR RANCHO.CARRILLO PREPARED BY HANS GIROUX CONSULTING ASSOCIATE LARRY SEEMAN ASSOCIATES, INC. 500 NEWPORT CENTER DRIVE, SUITE 525 NEWPORT BEACH, CA 92660 (714) 640-6363 .. MARCH 23, 1981 1 ENERGY ANALYSIS RANCHO cARRILLd .lsa The current consumption of non-renewable energy resources on Rancho Carrillo property is negligible. As the property is developed, the onsite electrical and natural gas demand and vehh:ular fuels will constitute a sig- nificant energy demand in an era of rapidly declining resources. The coastal environment of Southern California offers a considerable opportunity to minimize energy demand because of a very mild climate. Cool summer breezes reduce air-conditioning demand, mild winters reduce heat loads, and abundant sunshine, especially in inland valleys away from coastal clouds, offers considerable possibilities for solar-assisted energy systems. Compared to other areas of California and the nation, the San Diego area has almost.the lowest climatically-induced (hot or cold weather) energy demand. Upon project completion, there will be three principal sources of fossil- fueled energy consumption .. These include: 1. Electrical energy utilization met by combustion of oil, gas, or coal in fossil-fueled power plants. 2. 0nsite natural gas combustion for heating, cooking, or hot water. 3. Automotive fuels and lubricants to meet project-related transportation needs. Standard energy demand estimates can be made using consumption factors derived from SDG&E experience in energy supply and vehicular performance char- acteristics. These consumption factors are based on hi stori ca 1 performance and, therefore, do not reflect the marked trend toward conservation created by lin:iited supply and-spiraling costs of energy resources. Using the somewhat conservative consumption (over-predict-ive) estimates yields the following project-related energy demand. • Electricity-·· 67,755 MWH/year Natural gas -4,170,000 therms··natural gas/year Gasoline -5,250,000 gallons/year SDG&E has indicated in its future energy supply plans that it can keep pace with area growth and that there will be a significant decline in basin- wide oil and gas use within the next decade for electrical generation. Given, E) 0 0 C C C C 0 0 0 0 0 0 0 0 0 0 0 ' ., 2 lsa however, the rapidly r1s1ng cost of electricity and the weak financial posi- tion of SDG&E, every effort should be made to reduce energy consumption through aggressive conservation measures for economic reasons, if for no other reason. 0 0 ,0 0 0 0 0 0 0 0 0 APPENDIX I NOISE STUDY BIOACOUSTICAL ENGINEERING CORP., 1980 lsa IQ 0 0 0 I lo 0 0 0 0 0 0 80/234 EVALUATION OF EXTERIOR NOISE EXPOSURE AND GENERAL DEVELOPMENT RESTRICTIONS FOR THE RANCHO CARRILLO PROPOSED RESIDENTIAL DEVELOPMENT IN CARLSBAD, CALIFORNIA Prepared for: D~on Corporation P.O. Box 2770 Newport Beach, CA 92660 i Prepared by: _______ .......,.._ Johns. Leyerle Senior Engineer 18 December 1980 1833 East lith Street. Suite 103 • Santa Ana. California }!:271l l • 71.; .-:,.:. 7-51:Jti 0 80/234 0 REPORT SYNOPSIS An acoustical analysis of the proposed Rancho Carrillo develop- ment has been made, Included in this analysis is a determination o of the current and expected future project noise exposures for all property south of Palomar Airport Road. A visual and aural inspection of the development area indicates that there are four principle sources of project noise exposure. Current exposure levels are primarily influenced by motor-vehicle noise along Palomar Airport Road and by aircraft operations associated with 0 Palomar Airport. .Current noise exposure across the development site has a limited impact from dragster and motocross noise sources associated with Carlsbad Raceway. Future noise impact from all community sound sources will be heavily dominated by motor-vehicle traffic on Palomar Air,port Road and on the project interior roadways. (Two analyses of future roadway noise emissions 0 were made. Impact evaluations were completed assuming ultimate traffic flow and assuming ultimate traffic flow with the additional traffic from a housing density bonus and school conversion plan.) Future noise exposures from aircraft operations associated with Palomar Airport, dragster activity at Carlsbad Raceway and moto- cross activity at Carlsbad Raceway are expected to produce a limited impact. Mea,surements and analysis of each principle 0 noise source were performed to determine the range of current and future noise impact across the development property south of Palomar Airport Road. With knowledge·of the exposure levels from each principle sound source, the overall noise impact from all sources was determined for current and future times. The analyses indicate that expected future noise exposure levels o within the ,development site will exceed the current noise impact. Tl+e "worst-case" noise exposure levels expected across the develop- ment site ~outh of Pal.omar Airport Road were divided into four ·noise exposure categories. For each noise exposure category, certain noise ·control measures must be used to insure compliance with o state and local limits for sound levels in all outdoor and indoor _ residential living areas. The report presents three examples of practical noise control barrier des.igns which will reduce the outdoo~ noise exposure to well within the 65 dB CNEL permitted limit. Also discussed are the general requirements for building shell construction to insure compliance with the 45 dB CNEL 0 interior standard. Necessary mitigation measures range from no required controls to stringent sound control steps which represent 0 iii 0 0 0 0 0 0 0 0 0 0 0 80/234 TABLE OF CONTENTS REPORT SYNOPSIS . iii INTRODUCTION . . . . . . . . . CU~T EXTERIOR NOISE ENVIRONMENT Current Aircraft Noise Impact . . . . . . . . . . . e • • • • • • • • o • Current Motor-Vehicle Noise Impact. . . . . . . Current Carlsbad Raceway Dragster Noise Impact. Current Carlsbad Raceway Motocross Noise Impact • Cl ■ ■ FUTURE EXTERIOR NOISE ENVIRONMENT Future Aircraft Noise Impact. Future Motor-Vehicle Noise 1Impact . . . . . . . . . Future Carlsbad Raceway Dragster Noise Impact Future Carlsbad Raceway Motorcross Noise Impact COMPARISON OF CURRENT AND FUTURE NOISE IMPACTS FUTURE OVERALL DEVELOPMENT NOISE EXPOSURE GENERAL NOISE IMPACT MITIGATION MEASURES CONCLUSION-G • REFERENCE LIST ii . . . 1 3 3 14 18 21 22 23 24 26 32 32 32 36 69 7J. BICACDUST1CAL EN~INE:R!NGCO~F. 80/234 INTRODUCTION EVALUATION OF EXTERIOR NOISE EXPOSURE AND GENERAL DEVELOPMENT RESTRICTIONS FOR THE RANCHO CARRILLO PROPOSED RESIDENTIAL DEVELOPMENT IN CARLSBAD, CALIFORNIA BioAcoustical Engineering Corporation (J3AEC) has been retained to determine the expected noise environments and general sound control measures for the proposed Rancho Carrillo residential development. Of particular interest are the acoustical impacts and· mitigation measures needed for each planned residence and all out- door living space. Using the current and projected future exterior noise environments, a total of four noise impact categories are outlined. The general acoustical mitigation measures associated with each impact category are presented. Identification of the sound exposure groups and associated noise control measures was performed to assist in orderly site development planning and help insure compliance with state and local acoustical criteria. • The planned Rancho Carrillo project consists of roughly 300 acres located in the City of Carlsbad. The development is located east of Palomar Airport and South of Palomar Airport Road, due south of the Carlsbad Raceway. (See Figure l on the next page). Principle construction within the development will consist of single and multiple family residential. housing. An approximate total of 2,998 living units ~ill be built within the project. The development will also contain open space, park areas, neighborhood commercial centers and a business/light industrial area north of Palomar Airport Road. Sound control requirements which apply to the Rancho Carrillo aevelopment are listed in both state and local criteria. These standard-s specify the required sound control performance between individual (attached) dwelling units and the maximum exterior noise impact inside and outside all residential construction. Control of noise impact between units is best analyzed much later in the development stage when proposed building plans have been developed. At that time each party wall and common floor-ceiling may be individ- ually analyzed for compliance with the performance criteria. Unit- to-unit noise control will not be addressed in this study. Permitted maximum noise exposuresfrom outdoor sound levels are specified in state and local standards for both indoor and outdoor living areas. Exterior-to-interior noise intrusion is restricted to 45 dB CNEL for multi-family dwelling units by state standard·s and to 45 dB CNEL for single family dwelling units by local criteria. In addition, noise exposure in all principal outdoor living space is limited to 65 dB CNEL by local standards. S!CACD1JST1CAL ENl:iiNE:RirJtitDRF. 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 80/234 REPORT SYNOPSIS(Continued) borderline feasibility for residential construction. However,. despite this impact range, most areas within the development will need little or no noise control measures to satisfy applicable sound control criteria. The general mitigation measures for each exposure category will assist in determining development feasibility and general construction requirements. Of course the specific noise control designs and approvals should.not be considered in the general planning stage of development. The detailed elements of the noise control design are bes1; formul·ated prior to issuance of building permits for review and approval by the Building Depart- ment. Once the specific building plans are completed, analyses should be performed, as needed, to determine the particular noise control measures required. It is expected that State and Local noise exposure criteria will be easily satisfied throughout the development with little or no change in the standard building construction. The noise exposure assessment addressed in this report applies only to that portion of the development south of Palomar Airport Road. Field measurements and projections of current and future noise levels have not been determined for the property north of Palomar Airport Road. If noise-sensitive development is later planned for this area, additional field measurements and noise control design reconunendations are required. Noise sensitive land uses which would require noise· impact assessment and noise control design include: motels, hotels, private and general office spaces, certa~n retail uses, apartments, condo- miniums, and single family dwellings. • iv E!CACDLJSiiCAL ENGiNEiRINEiCC~R 0 0 ,. / - CHIA / ·1 I ' -:P • / 1111 U _ ~j_r p I-# ~:=-=-=--·------c-~ ~. '...-----1, , __ IID. u cos,a ••LOMA• -------_ ...__.......,. __ .. l . ____ Carld1dCllr_L1,.11 Site Location Map ' I l . \ .-• I I I The cross-hatched area shown above indicates the approximate.location of the Rancho Carrillo proposed development. 0 0 0 0 0 0 0 0 00 0 '-. N w ..,. N 0 0 0 0 0 ,0 I I :o 0 0 0 0 80/234 3 In the following discussion, noise exposure conditions expected throughout the development are presented. The anticipated range of sound levels is divided into four impact ca~egories. A com- parison of each category with state and local criteria for exterior noise control indicates the general mitigation measures which will be needed for each exposure group. CURRENT EXTERIOR NOISE ENVIRONMENT .. Evaluations of the current outside noise environment throughout the Rancho Carrillo development site were made by BAEC from Friday, 18 January 1980, through .Sunday, 20 · January 190·0. Subjective observations during the data collection days indicate that there are four primary sources of project noise impact. Visual arid aural inspection of the development environs indicated that the principle sources of noise impact include: aircraft noise exposure from activities associated with Palomar Airport; motor-vehicle sound levels from Palomar Airport Road; dragster noise impact from Carlsbad Raceway1 and sound levels from motocross activity at Carlsbad Raceway. • The project noise-exposure from ea.ch primary noise source is discussed in the following sections. Current Aircraft Noise Impact Analysis of the development noise ~xposure from aircraft operations associated with Palomar Airport was made from field measurements at two points on the development site and from field data collected for similar aircraft approaching John Wayne Airport in Orange , County. Figure 2 on the following page indicates the approximate location. of the aircraft measurement points on the Rancho Carrillo property. Site photographSshown in Figure 3. Aircraft fly-over noise levels were recorded using a calibrated sound level meter at each location, a graphic level recorder at one position, and a magnetic tape recorder at the other data collection point. The measurement equipment at one_ measurement point was comprised of a Bruel and Kjaer model 220·4 S precision Sound Level Meter and a Bruel and Kjaer Model 2305 Level Recorder. Data was· collected at the other measurement point using a GenRad Model 1565-B type 2 Sound Level Meter and a Sony Model TC-772 professional Tape· Recorder. The sound measurement equipment at each point was calibrated before data collection using a Bruel and Kjaer Type 4230 Sound Level Calibrator or a GenRad Type 1562-A Sound Level Calibrator. The sound level meters at all data collection points were adjusted for A-weighted slow respo~se sound level measurement. The measurement microphones were positioned five feet above existing grade and oriented for sound field incidence o0 to 90° from the plane of the- microphone diaphram. 80/234 4 / ~ Coll c-! r,'" I .,... !,; .,. .,. ' ,:11» , .,. ~-~ .. I , ... ------, 1 ,,,_ I I 1 , ·--at ., I . .. 1SIT \ . I • StTE 2 • ---- , __ .... COSTA 'T---r---· I ' d ~ ,. ,--:-, I 1 ____ _ I , • k-!or.:~=-:.::..... • ' .....---11 .....__//), ------1--..,..,.-.... '· # o/ . . . ) FIGURE 2: Aircra~t Noise Measurement Locations The points circled above, indicate _the approxim'ate. locations on the Rancho· Carrillo property where Site 1 and Site 2 aircraft .noise measurements were recorded. C 0 0 0 0 0 0 0 0 0 0 80/234 SI'l'E l r .! U,4 .. i • • • SI'l'E 2 FIGURE 3: Site Photographs Shown above are photographs of the Site 1 • and Site 2 noise measurement stations indicated in Figure 2 . • • 5 80/234 The data collected at each point was ultimately reduced to a time/level strip chart of each aircraft fly-over. Figure 4 on the next page shows a typical time/level recording. During the on-site field measurements, three pr.imary aircraft flight paths were observed. Aircraft were observed on (1) a straight-in approach path traveling west parallel to and north 6 of Palomar Airport Road: (2) a loop path where the aircraft depart the airport and circle to the south returning back to the approach end of the airport (this path carries aircraft over the north-west portion of the site): and (3) a fly-by path traveling at random directionsover the property. Figure 5 on the following page roughly indicates. the three flight paths on which aircraft travel near or over the proposed development. It is understood from the Comprehensive Land Use Plan for Palomar Airport2 that three aircraft types use the airport. Single and Twin engine propeller aircraft are two types which represent the majority of aircraft that use the airport. In addition business jets, both private and small commercial, operate in and out of Palomar Airport. During the on-site field measurement days, data was collected for single and twin engine aircraft flying in each of the three flight paths. Jet engine aircraft did not operate during the measurement days. A "worst-case" determination of expected jet noise impact was made from field measurements of 737 commercial jet aircraft approaching John Wayne Airport. It was assumed that most jet aircraft which fly near Rancho Carrillo use the straight-in flight path. Field measurements of commercial jets approaching John Wayne Airport, at the same slant-range distance between measurement Site 1 and the straight-in flight path, were used to estimate the ex- pected "worst-case" jet noise impact on the development site. Measurements of the commercial jet fly-by sound levels were made using the same instrumentation and procedures used for the on-site measurements. Following completion of the field data collection, the time/ level noise record.for each aircraft fly-over was analyzed to determine a Single Event Level (SEL) value for the event. The SEL value represents a time integrated A-weighted noise level which is expressed by the level of an equivalent one second duration reference signal3 • That is, the SEL value represents a single noise level, one second in duration, which contains the same amount of acoustic energy as aircraft noise emission that is • • • • • • • • • • • • 7 80/234 :::W I I I I I I I I I I I I I I I I I I C-=a I I I I I I I I I I I &a, t4"! /(Llf!;Zk& ( S 001/61-W-l M Fu Gen: f Wctt FIGURE 4: Typicaf Aircraft Fly-by Noise Level Recording Shown above is a typical time/level strip chart of a single engine propeller aircraft in the "straight-in" flight path tsee Figure 5) as measured at Site 1. (See Figure 2). The ordinate represents sound level in increments of one decibel per line. The absicissa represents time in divisions of one second for each three millimeters. An SEL value of 69.6 dB was canputed for this noise event . 1) clCACOLJST~CAL •\'!\ ,~,.~ •~~~ !U ,-~ ~~ '1 1 ti {1 / --- r,UOMAII "/ r ,I I ·: .. . I a • u UUA u,-.· / i FIGURE 5: Aircraft Flight Paths over the Rancho Carrillo Property •• .. I The straight-in, loop and fly-over flight paths shown above indicate the approximate flight paths observed during on-site aircraft noise measurements. • • 00 0 '--N w ~ 00 ! lo 0 0 0 0 0 0 0 0 0 0 80/233 9 many seconds in duration. The SEL value for each time/level noise record was calculated using the following equation.3 SEL = l 0 log [ ~ i=l antilog ~ I 10) At] Where: AL. l. At n = the instaneous A-weighted sound level for the ith sample = the time interval, in seconds, between s~les = the number of samples for which the sound level is at least 10 dB (A) below the maximum All,i Using the above equation, an SEL value was calculated for each aircraft type (single engine propeller, twin engine propeller, and business jet) measured in each typical flight path (straight- in for all aircraft types; loop for propeller aircraft; and fly- by for propeller aircraft). A range of SEL values was determined for each aircraft type in each flight path. An energy average of these multiple SEL findings was made to determine a single, average, SEL for each aircraft type operating in each typical flight path. Table I on the next page summarizes the average SEL results. The current 24-hour aircraft fly-over CNEL exposure level at each measurement point was calculated using the SEL values for each aircraft type in each flight path and the typical operation scenario. Necessary daily operation scenario information includes: Total number of aircraft; typical single engine propeller/twin engine propeller/business jet fleet mix; the day/evening/nighttime operation split; and the typical straight-in/loop/fly-by usage split for each flight path. • A current typical count of 268,418 operations per year was deter- mined in a conversation with Mr. Lacy Clark, Palomar Airport Assistant Manager.~ This current annual estimate was based upon the 12-month count ending in December 1979. Mr. Clark indicated there are typically 1000 operations each weekend day with the bal- ance of operations distributed on weekdays (average of 630 operations per week day). Mr. Philip Safford, Assistant Director of Palomar Airport, indic~ted that the current fleet mix is roughly: 85% single engine propeller aircraft, 12.5% twin engine propeller aircraft, and 2.5% business jet aircraft. 5 e:cACCUSTlCAL ENGiNEER!NtitO~R 80/233 Site Number (See Figure 2) ; 1 2 ... ,,_.1111 I.U TABLE I SUMMARY OF AVERAGE SEL VALUES BY AIRCRAFT TYPE AND FLIGHT PATH Single Engine Propeller Twin Engine Propeller SEL Values SEL Values Straight-In Loop Fly-By Straight-In Loop Fly.:.ey Flight Path Flight Flight Flight Path Flight Flight Path Path Path Path 69.6 dB 62.2 dB 65.7 dB 79 dB 68.2 dB 79.l dB 66.6 dB 58.9 dB 67.4 dB 73.l dB 64.2 dB 75.5 dB 0 C) Business· Jet SEL Values Straight-In Flight Path 84.7 dB 80.8 dB 0 0 .... 0 -j . I 0 0 0 0 0 0 0 0 0 0 0 80/234 11 The day/evening/nighttime operation split was determined from a conversation with Mr. K. Dean, Controller with the Palomar Airport FAA tower.6 Mr. Dean indicated that during daytime hours (7 am to 7 pm) roughly 94.5% of all operations·occur. During evening hours (7 pm to 10 pm) roughly 5% of all operations occur. During nighttime hours (10 pm to 7 am) there are generally only 3 to 4 operations. This count indicates a nighttime operation of roughly 0.5% of all daily operations. The approximate flight path usage split was determined from a conversation with Mr. Philip Safford.5 Mr. Safford indicated that roughly Oto 250 aircraft per day use the instrument pattern (i.e., straight-in flight path)~ This indicates that 0% to 25% of all weekend traffic and 0% to 40% of all weekday traffic use the straight-in flight path. For the purposes of this study it is assumed that 25% of all weekend traffic and 40% of all weekday traffic will typically fly the straight-in approach. Further, since most business jets fly the straight-in path near the development site, for the purposes of this study it is assumed that all business jets use the straight-in path only. Based upon limiteo:-field observations, it is assumed that roughly 10% of all propeller aircraft operations, weekday and weekend, use the fly-by flight path. It is assumed that the balance of all operations, 50% weekday and 65% weekend, use the loop flight path. Calculation of the current aircraft CNEL impact level at each data collection point was perf.ormed us-ing the SEL values and operational scenario information presented above and the following equation from reference 7: CNE1ite i = 10 log [ (Antilog CNEI.single engine) prop. site i + (Antilog CNELtwm engine ) prop. site i + (Antilog ~ines~ jet) ] site i To determine the CNEL 'te . (the CNEL for the i.th site) the above • SJ. l. equation indicates that values for CNELsingle engine' CNELtwin engine prop. site i prop. site i and CNELbus'iness Jet must be known. These values refer to the site i CNEL impact from each aircraft type at the ith site. The CNEL value for each aircraft type,at a given site, is determined from the SIOACOUSilCAL eru~iNE:RINCCC~R 80/234 equation: CNELa.ircraft = SELairc:raft type n + 10 log(~(SI) + 3.16 ~(SI) type n straight-in path + SELaircraft type n + 10 log(~(L)+ 3.16 ~(L) .loop path + 10 ~(L)) -49.4 + SELaircraft type n :f-10 log(~(FB,'+ 3.16 ~(FB) fly-by path + 10 ~(FB)) -49.4 12 The above equation indicates that CNELa.ircraft (the CNEL for type n type n aircraft -single engine propeller, twin engine propeller or ·business jet aircraft) may be determined from a knowledge of several SEL, ND, NE, and NN values. The SELaircraft type n , ~aircraft type n and SEL aircraft type n Fly-by -path straight-in path loop path values refer to SEL values for a given aircraft type measured in the straight-in, loop and fly-by flight paths respectively. The ND(SI), N0 (L), and ND(FB) values refer to the number of.aircraft type n (weekday~ weekend) which fly during the daytime hours (7 am tD 7 pm) on the straight-in, loop and fly-by paths respectively. The NE(SI), ~(L), ~(FB) values refer to the number of aircraft type n (weekday~ weekend) which_ fl.y during the evening hours (7 pm to 10 pm) on the straight-in, loop and fly-by paths respectively. Similarly, the NN(SI) , NN(L) and NN(FB) values refer to the number of aircraft type n (weekday or weekend) which fly during the nighttime hours (10 pm to 7 am) on the straight-in, loop and fly-by paths respectively. Following detailed calculations using the above referenced equations, a determination has been.made of the current weekday and current weekend aircraft CNEL exposure at each on-site measurement point. The results are shown in Table II. This table indicates that on weekdays the proposed development •is exposed to a current approximate 0 0 0 0 0 0 0 0 0 aircraft impact range of 47.6 dB CNEL to 51.5 dB CNEL. Table II C shows that on weekends the current aircraft noise exposure range increases less than 2.dB to between 49.1 dB CNEL and 52.8 dB CNEL. C 0 0 0 0 0 0 0 0 0 0 0 0/234 TABLE II CURRENT AIRCRAFT WEEKDAY AND WEEKEND CNEL EXPOSURES AT EACH ·MEASUREMENT SITE. CURRENT AIRCRAFT WEEKDAY EXPOSURE 13 Site Number Single Engine Twin Engine Business Jet Total (See Figure 2) Propeller ·propeller Noise Impact· Aircraft Noise Impact ·Noise Impact Noise Impact 1 45.3 dB CNEL 46.6 dB CNEL 47.8 dB CNEL 51.5 dB CNEI 2 42.9 dB CNEL 41. 4 dB CNEL 43.9 dB CNEL 47.6 dB CNEI CURRENT AIRCRAFT WEEKEND EXPOSURE ' Site Number Single Engine_ (See Figure 2) Propeller No~se Impact l 46.2 dB CNEL 2 43.9 dB CNEL Twin Engine-Business Jet Total Propeller Noise Impact Aircraft Noise Impact Noise Impact 47.2 dB CNEL 49.8 dB CNEL 52.8 42.3 dB CNEL 45.9 dB CNEL 49.l SICACCUST1CAL ENCaiNEi!i!NCitOFiR dB dB CNEL CNEL - 80/234 14 Current Motor-Vehicle Noise Im~act Field observations during on-site measurements indicated that traffic on Palomar Airport Road represents the principle source of current motor-vehicle noise exposure. Measurements of the motor-vehicle noise level along Palomar Airport Road were made on Friday, 18 January 1980. Sound level measurements were collected using a Metrosonics Type db-602 digital Sound Level Analyzer· with A-weighted slow response. The digii:al noise measure- ment instrumentation was adjusted for a s·ample rate of one measure- ment per second. The road noise measurement position was SO feet south of the Palomar Airport Road centerline, near the east-west center of the property (see Figures 6 and 7}. This measurement location was approximately 49 feet from the roadway "single lane equivalent". This "single lane equivalent" distance represents microphone separation· from·an imaginary lane on which the total traffic flow can be assumed to travel. Determination of the "single lane equivalent" acoustical. cen·ter of the roadway was made in accordance with reference 8. During the site noise level measure- ments, the microphone was positioned five feet above existing grade and oriented for grazing sound field incidence. The noise levels measured were recorded at the point during a representative after- noon period. An Equivalent Level, Leq, value was determined directly from-the measurement equipment for the sample period at the data collection point (Leq corresponds to the measured noise level averaged on an energy basis 9 } ~ .Using the recorded Leq, and typical hourly percent traffic distribution information for roadways with over 10,000 average daily traffic (ADT)10 approximate Leq values were calculated for each hour in the day. The hourly Leq values for the measurement point are listed in Tab~e IIIon the next page. Also shown in this table are the O dBA, 5 dBA, and 10 dBA weighting increases required for the day, evening, and nighttime hours when determining a CNEL value. The adjusted Leq values for each hour ·are tabulated in the last column of the table. Following the method of CNEL determination outlined in reference 7, the adjusted hourly Leq values have been summed on an energy basis and averaged! The results of these cal- culations indicate a current outside sound environment of 71.9 dB CNEL at the measurement point SO feet from the Palomar Airport Road centerline. This method of motor-vehicle CNEL determination using a short-term sample technique represents a state-of-the-art approach. The approach is discussed in detail in the referencell publication. This publication was authored by Johns. Leyerle and Otto c. Bixler, Jr. of Bio-Acoustical Engineering Corporation and presented at the 1978 International Conference on Noise Control Engineering. The current Palomar Airport Road noise impact expected at 100 feet from the roadway centerline was calculated using the field measure- C C C C C 0 0 0 0 0 0 • • • • • • 80/234 ! ... ,.,., .. FIGURE 6: Palomar AirportRoad Noise Measurement Location The point circled above indicates the approximate location on the Rancho Carrillo property where measurements of current Palomar Airport Road motor- vehicle noise levels were recorded at SO feet from the roadway centerline . SICACOUSTlCAL .. "''1-■8', ..... 15 80/234 ,.... FIGURE 7: Site Photograph Shown above is a photograph of the digital noise measurement instrumentation along Palomar Airport Road. 16 • • • • • • l j' !O 0 0 0 0 0 0 0 0 0 0 17 80/234 TABLE III SITE NOISE LEVEL MEASUREMENT.RESULTS A-weighted Leq I,lOise level data collected during a represt:!nta'!:,ive sample period on 18 January-1980, together with calculated hourly Leq values and the resulting CNEL value. • MEASUREMENT LOCATION: SO feet from the Palomar Airport Road centerline as shown in Figure 6. . . One Hour Period • ·' Hourly Leq Data • Houz:ly Leq Weighting Adjusted Beginning at: -(dBA,re.0.0002 dyn~/cm2 } . for _ Hourly CNEL Evalua:tion (dB) . Leq (dBA) -- 0700 71.2 0 71.2 0800 69.3 0 69.3 0900 68.3 o· --68.3 .1000 68.2 0 68.2 1100 .. . 68 .4 -0 ·. 68.4 1200 ' 68.S 0 68.5 .. - 1300 68.6 0 68.6 1400 68.8 0 68.8 1500 . 7 0 (Measured) o· 70 1600 -71.,5 0 71.5 1700 71.2 0 71.2 1800 69.5 -69". 5 0 1900 68.1 5 73.l 2000 67 ,s -· : 72 2100 66.3 5 --71. 3 65.3 -. -75.3 2200 10 2300 64.7 10 74.7 -0000 .. -63.l • 10 .. 73.l 0100 .. 60.7 10 70. 7 59.5 .. 69.5 0200 10 .. 0300 57.7 10 67.7 0400 58. 7 . lb 68.7 0500 62.5. 10 72.5 0600 68.9 .. • 78. 9 -10 .- [ (E Antilog of A~juste4. Hourly Leq>J· ., 10 log1 o -= :Zl.-5! dB CNEL· 24 , · 80/234 18 ment findings and the reference 12 equation which specifies a 4.5 dB reduction in noise level for-each doubling of distance from the no1.se source. Calculations -indicate that at 10 0 f e.et from the Palomar Airport Road centerline, a current noise e~posure-level of 67.4 dB CNEL is expected. Current Carlsbad Raceway Dragster Noise Imoact Carlsbad Raceway is located just north of the proposed development property near the east-west· project center~ It is understood from discussions with Mr. Larry Grismer, the r.aceway operator, that two activities associated with the raceway ~ay influence the Rancho -Carrillo noise environment1 :. ~-Grismer indicated that each Saturday evening, weather permitting, drag races occur. He also indicated that during ~he daylight hours on Sunday, motocross ·races afe held. -- It is understood that the Saturday evening drag races generally· occur between the hours of 7 pm and 11 pm. During this time street-legal and specially designed cars race in pairs. Mr. Grisner indicated there may be up to 20 races per hour. Accordingly, during the four hours of Saturday night operation, there may be up to 80 races. Instrumentation was set up· at sites·l and 2, previously shown in Figure 2, to measure the curr_ent drag race noise levels. Drag •• • noise level measurements were made between 8 pm and 9:30 pm on- Saturday, 19 January 1980. The Site 1 measura~ent point was roughly 2300 feet from the drag strip. • T.he Site 2 measurement point_ was approximately 4200 feet from the race track. Subjective listening during each 10 to 15 second race indicated, that the dragsters produced a very limited noise impact. Field measurements indicated maximum noise levels of 40 dBA to 50 dBA during each typical.race. Dragster noise at Site 1 was very quiet but. perceptable. Dragster noise at Site 2 was very difficult to perceive. It is expected that the difficulty in perceiving the dragster noise at -Site 2 is the result of its long separation from the race track·and because of the high ambient noise levels at Site 2. Measurements of the Site 2 ambient noise levels between races were 45 dBA·to 57 dBA. This ambient level was heavily-influenced by the nighttime sounds· from small insects and frogs. During the same·time period the Site 1 ambient noise level was 1.0 dBA to 20 dBA quieter at 34 dBA to 38 dBA. Due tq the high ambient noise levei at Site 2, the drag race noise level measurements-are greatly contaminated. The drag-race noise level measurements at Site l have very little contamination and are exoected to resoresent a much more accurate ·determination of dragstet noise impact. Since site 2 is farther BJCACOU5TUCAL ENCiiNE:RIN~CDt(R 0 0 0 0 0 0 C C C C C 0 0 0 0 0 I i ' 0 0 0 0 0 0 80/234 19 away than Site l, it is expected that if the ambient level at Site 2 had been sufficiently low to permit accurate drag race noise level measurements, the results would have shown an impact quieter than at Site l. Accordingly, for the ·purposes of this study, only the Site l drag race noise level measurements will be analyzed. As a "worst case11 analysis, the Site 1 impact findings will be assumed to represent the current exposure level at Site 2 and at all other locations across the property. The Site l drag race noise level measurements were made using a Bruel and Kjaer Model 2204S precision Sound Level Meter and a Bruel and Kjaer Model 2305 graphic Level Recorder. Figure 8 on the next page shows a typical t:ime/leve_l strip chart recording of a drag race measurement_.- Following completion~of the field data colleG:tion, the time/level noise record for .each value· for the event. record was calculated Aircraft Noise Impact indicate an SEL range measured· at Site 1. drag race was analyzed to determine an SEL The SEL value for each time/level noise using the equation presented in the Current section. The results of the SEL analysis of 47.8 dB to 58.7 dB for the drag races The "worst-case"_energy average hourly noise level during the hours of Saturday night dragster operation may be computed using the 11worst-case" SEL value and the following equation from reference li: BL= Energy average hourly noise level = 10 log [ ~ antilog .(S~L/10) l i=l • • 36 Where: SEL = the "worst-case" SEL (58.7 dB) n = the number of drag races per hour (20) Using the above equation the "worst-case" energy average noise leyel from drag race operation was found to equal 36 dBA. That is, a .steady noise level of 36 dBA during each hour of dragster operations would yield the same average noise level that is produced by the intermittent 10 to 15 second dragster noise levels produced 20 times per hour. S!CACCUSilCAL ENCiNE:RIN~CO~~ 80/234 __ .;._-_-_--_-_....,... __ --,,-_..,,..._ ....... : _--_--=--::::-:.:.-:.-:.--:..-:.-:..-:..-:..-:.-:.:.-:.:.-:.-:.-:.-:..-=-_·--~_-'""·-=,-,! --= FIGURE 8: Typical Dragster Noise Level Recording Shown above is a typical time/level strip chart of a dragster .race at Carlsbad Raceway as measured at Site l (See Figure 2). 20 The ordinate represents sound level in increments of one decibel per line. The absicissa represents time in divisions of one second for each three millimeters An SEL value of 58.4 dB was computed for this noise event. 0 0 0 0 0 0 0 0 0 C C 0 0 0 0 0 0 0- 0 0 0 0 80/234 21 The "worst-case" hourly average noise level from dragster operations is 36 dBA during the hours from 7 pm to 11 pm. During this same time the ambient noise level range, as previ- ously mentioned, is 34 dBA to 3_8 dBA (36 dBA average). To compute the Rancho Carrillo CNEL. exposure from dragster. operations, we must know the average noise level for each hour on Saturday. The above calculations indicate that the drag noise level average is 36 dBA for the hours 7 pm to 11 pm. The ambient noise level during these hours is also 36 dBA. As a first-cut assumption, it is assumed that the ambient noise level for all other Saturday hours (excluding aircraft and motor-vehicle noise sources) remains at 36 dBA. Accordingly, the average noise level for each of the 24 Saturday hours is 36 dBA. Using this 36 dBA hourly noise level value and the following reference 7 equation, the CNEL exposure from Saturday dragster operations can be· calculated: CNEL= 10 log[(12 antilog(HL/10)+(3) (J°.16)Antilog(HL/10) + (-9) (10) Anti log (BL/10) ] ¼ .24 ] Where: BL= the energy average hourly noise level (36 dBA) Using the above equation the current "worst-case" Rancho Carrillo CNEL exposure from Saturday.dragster operations at Carlsbad Race- way is 41.9 dB CNEL. Current Carlsbad Raceway Motocross Noise Impact Mr. Larry Grismer, operator of Carlsbad Raceway, indicated that motocross activity at the raceway represents the second source of potential noise impact onto the Rancho Carrillo property. It is understood that motocross activities involve off-road motor- cy1es in groups of roughly 15 vehicles per race. Motocross racing activity occurs on Sunday and may begin as early as 8 am and continue uninterrupted until 5 pm. Field measurements of motocross noise·impact were performed during a late-morning period on Sunday, 20 January 1980. Data was collected at both Site 1 and Site 2 shown in Figure 2. Motocross activity was measured at one site using a metrosonics Model db-602 digital Sound Level Analyzer. Data was collected at the other site using a GenRad Model 1565-B type 2 Sound Level Meter and a Sony model TC-772 professional Tape Recorder. The tape recorded data was later play_ed back through the Sound Level Analyzer for data reduction. SiCACOIJSTlCAL Et-iCiNE::;!NCCO!R~ 80/234 22 An energy average noise level for the motocross measurements at each data collection point was read directly from the Sound Level Analyzer instrumentation. The results indicate-an energy average noise level of approximately 42 dBA for both measurement points. It is noted that based upon sound level meter observation and upon subjective listening, the 42 dBA average noise level is largely due to the ambient noise sources. The motocross sound levels were barely perceptable at the two measurement points. It appears that the motocross noise made very little, if any, contribution to the 42 dBA average noise level. Accordingly, it is expected that if the ambient noise level had been much quieter to permit an uncontaminated measurement·of motocross sound levels, the motocross average sound level findings would have been substantially below 42 dBA. As a "worst-case" analysis, it is assumed that the motocross activity creates an average noise level of 42 dBA across the development during the 8 am to 5 pm Sunday operating hours. It is recognized however that this average sound level primarily represents the daytime ambient noise level. ··Accordingly, as a further "worst-case" assumption, it is assumed that the 42 dBA average noise level is sustained, throughout each Sunday before and after the motocross activity. These assumptions indicate that the "worst-case" energy average noise level for each of the 24 Sunday hours is 42 dBA. Using this 42 dBA hourly noise level value and L the reference 7 equation presented in ·the dragster analysis section, the CNEL exposure from Sunday motocross activity has been calculated. The results indicate that a current "worst-case" Rancho Carrillo _ CNEL exposure from Sunday motocross activity at Carlsbad Raceway is 48.7 dB CNEL. FUTURE EXTERIOR NOISE ENVIRONMENT •A review of the Rancho Carrillo proposed development plan and the surrol;lnding area indicates that in future years the property will continue to be exposed to multiple noise sources. It is understood that Palomar Airport.will continue to operate with potentially increased numbers·of operations. This operation increase is expected to increase the aircraft noise exposure on the property. It is understood that the width of Palomar Airport Road, and the number of motor-vehicles which use this roadway, will increase in future years. In addition, in future years a substantial number of motor- vehicles will travel on the Rancho Carrillo interior road system that presently does not exist. This change in the number of motor- vehicles which travel near and through the development will also increase the project nois·e exposure. It is expected that in future years the Rancho Carr~J:lo development will have a_Carlsbad Raceway C C C C C C C 0 C 0 0 I ( ·O I ,0 I -0 0 0 0 0 0 0 ----------------- 80/234 23 noise exposure comparable to the current noise-impacto ' The overall project noise impact is expected to be greater in future years than the current noise impact. The development future noise exposure expected from each primary noise source is discussed in the following sections. Future Aircraft Noise Im~act Analysis of the future noise environment expected on the development property from nearby aircraf.t operations was performed using the same general analytical methods presented in the current aircraft noise impact section. The future aircraft CNEL impact is calculated from a knowledge of the SEL values for each aircraft and the aircraft operational scenario. For the purposes of this study it was assumed that the current SEL values measured and presented in Table I for each aircraft type are representative of the expected "worst-case" future SEL values. Inherent in this assumption is the expectation that future single engine propeller, twin engine propeller and business jet aircraft will be as loud as, or quieter than, their current counterparts. Accordingly, the SEL values presented in Table I were used to compute expected future aircraft CNEL impact. It is understood that some of the future aircraft operational scenario will be different from the current scenario. -The Palomar Airport Comprehensive Land Use Plan indicates that the 1990 annual o-peration count may increase to 435,000.2 However, Mr. Lacy Clark indicates that this count is much greater than will probably be realized. However, 435,000 annual operations will be used as a . "worst-case" estimate. It is assumed that the percentage of aircraft which now operate on weekends and weekdays will remain unchanged in future years. This assumption indicates an average future weekend aircraft count o_~ 1631 and an average weekday count of 1021 per day. The Palomar Airport Comprehensive Land Use Plan indicates that the current f_leet mix will change in future years. The 1990 fleet mix is projected to be 75% single engine propeller aircraft, 22% twin engine propeller aircraft, and 3% business jet aircraft. It is assumed i:hat the day/evening/nighttime operation split will remain roughly unchanged between current and future years. Accord- ingly the future day/evening/ nighttime operation ~plit is expected to be 94.5% (7am to 7 pm), 5% (7 pm to 10 pm) and 0.5% (10 pm to 7 am). It is also assumed that the future flight path usage split will be the same as the split for current times. In future years the weekday BiOACOUSiiCAL ENGiNEi:~INCiCD~P. 80/234 24 flight path operation split is expected to be: 40% S~raight-in, 50% Loop and 10% Fly-by. The future weekend flight path operation sp.lit is.expec.ted to be: 25% Staight-in, 65% Loop and 10% Fly-by. Following detailed calculations using the SEL values from Table I, the operational scenario just mentioned, and the equations pre- viously presented, a determination has been made of the expected future weekday and future weekend aircraft CNEL exposure at Site land Site 2 on the property. The results of projected future noise impact are shown in Table DI. This table indicates that on future weekdays the planned development will be exposed to an approximate impact range of 48.7 dB CNEL to 52.8.dB CNEL. Table III shows that on weekends the future aircraft noise exposure range will increase an expected 5 dB to between 54.l dB-CNEL and 58 dB CNEL. Future Motor-Vehicle Noise Impact Future motor-vehicle noise impact on the Rancho Carrillo property is expected to change from current exposure levels more than for any other noise source category. Future daily traffic counts on Palomar Airport Road along the project are expected to be two to three times the current number. Future numbers of motor- vehicles on project interior roadways are expected to be as high as 26,000 where-roads and daily car travel currently do not exist. A determination of the future motor-vehicle noise impact. on the Rancho Carrillo development is presented below. The traffic engineering studylindicates that one of two ultimate daily traffic volumes are possible for roadways within and adjacent to Rancho Carrillo. The traffic study presents one group of roadway volumes which reflect the .ultimate usage from the project as-planned1 other planned and existing projects and regiona1 growth .. The traffic study a1so indicates the ult~mate roadway volumes for the project with a density housing bonus and school conversion plan, other planned and existing projects and regional growth. For purposes of discussion in this report, the two ultimate traffic volumes are referred to as "Ultimate Traffic Without Density Bonus" and "Ultimate Traffic With Density Bonus". The expected future ultimate roadway noise impact was projected for the "no density bonus" and the "density bonus" conditions using the :Federal Highway Administration (FHWA) noise prediction model 16 and0 several key roadway parameters. The key roadway· parameters which determine the impact of.vehicular traffic noise include: The total vehicle count per day; the percent heavy truck volume; the percent of. total average daily traffic (ADT) which flows each hour throughout a 24-hour period; vehicle travel speed; and the number o.f travel lanes. ) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 80/234 TABLE IV FUTURE AIRCRAFT WEEKDAY AND WEEKEND CNEL EXPOSURES AT EACH MEASUREMENT SITE FUTURE AIRCRAFT WEEKDAY EXPOSURE Site Number Single Engine Twin E-ngine Business Jet (See Figure 2) Propeller Propeller Noise Impact Noise Impact Noise Impact . 1 46.9 dB CNEL 51 . .1 dB CNEL so.a dB CNEL . 2 .. 44.5 dB CNEL 45.8 dB CNEL 46. 9 dB CNEL FUTURE AIRCRAFT WEEKEND EXPOSURE Site Number Single Engine Twin Engine Business Jet (See Figure 2 Propeller Propeller Noise Impact Noise Impact Noise Impact l 47.8 dB CNEL 51 .. 9 d~ CNEL 52.8 dB CNEL - ' 2 -45: S dB CNEL 46.9 dB CNEL 48.9 dB CNEL 25 . Total Aircraft Noise Impact 54.7 dB CNE_ - 50.6 dB CNE: Total Aircraft Noise Impact 56 dB CNEL - 52.1 dB CNE: 80/234 26 The expected future roadway parameter information, for all but the 24-hour hourly percent traffic flow breakdown, was determined from the traffic engineering report15 and from discussions with the project traffic engineer, Mr. Weston Pringle.17 The roadway parameter values specified by Mr. Pringle and used to project future roadway noise impact are presented in Table Von the next page. Table V makes reference to roadway sections by a letter and number designation. (e.g., The 1 first section along Palomar Airport Road is labled Pl.) Figure 9 on the page following Table Vindicates each roadway segment and its label-• The 24-hour hourly percent traffic flow breakdown was taken from a recent Orange County s'tudy of 31 major inter- sections .18 Using the FHWA traffic noise prediction model and the roadway parameters outlined above, calculations of the expected future noise impact,with and without a density bonus, were made for each roadway. The results of these calculations are presented in Table VI on the next page. Table VI indicates the future, ultimate, traffic noise-impact (with and without a density bonus) at 100 feet from each roadway centerline. A review of Table VI indicates that there is very little difference between the road noise impacts with and without the increased traffic from a housing density bonus and school conversion. The noise impact differences rapge from 0 dBA for the interior streets to 0.4 dBA for road segment M3 along Melrose Avenue. This minimal 0.4 dBA increase in noise impact from the density bonus traffic moves the noise contour lines roughly 10 percent farther from • each roadway centerline. (e.g., Along the Melrose roadway segment M3 the noise impact·at 100 feet from the centerline, with no density bonus, is 66.5 dB CNEL. With the -addition of density bonus traffic, the 66.5 dB CNEL contour will move roughly 10 feet farther away to ll0 feet from the roadway centerline). Table VI also shows that the greatest future road noise impact will occur along Palomar Airport Road east of Melrose Avenue .(road segment P4). The minimum future road noise impact is' expected along the side streets. (road segments C-S and E-E) and along the project interior streets. Future Carlsbad ·Raceway Dragster Noise Impact It is understood that the Carlsbad Raceway intends to operate for the indefinite future. Accordingly, it is expected that Saturday night dragster noise levels will continue to influence the Rancho Carrillo noise environment. However, there is no information to indicate the expected future level of dragster operations. It is assumed for the purposes of this study that the current dragster operation and noise emission from Carlsbad Raceway will have essentially no changes in future years. There- fore, the current "worst-case" dragster noise impact of 41.9 dB CNEL is expected to remain the same in future years throughout the Rancho Carrillo developmen~ICACDlJSi]DL -E?,J~iNE::ii?&GtORR 0 0 0 0 0 0 0 0 0 0 0 0 rr 11,W, t: I~ t 1111 ~ ; I ~ I m z r., ;a;. .... 11:... 2 m Ht =ti -2 -Cl n t1 :n :n • ~-11111 ~ 0 0 80/234 Roadway Roadway Section (See Fig. 9} Palomar Pl Airport P2 Road Pl P4 P-S Melrose Ml Avenue M2 M3 M4 MS M6 M7 M-W M-E Carrillo Cl Way C2 Cl C4 cs C6 C-NE C-SE C-NW c-sw c-s 0 0 0 0 TABLE V FUTURE ROADWAY PARAMETER VALUES USED FOR ANALYTICAL PROJECTION OF FUTURE ROADWAY NOISE IMPACT. Ultimate ADT Percent Travel Speed Without With Heavy Density Density Trucks Bonus Bonus .. 39200 41300 51 40 MPH 37200 39100 51 40 MPH· I 32900 33500 51 40 MPH 42400 44200 51 40 MPH 8100 10300 1/21 30 MPH 23300 25100 3% '-40 MPH 20500 21000 3\ 40 MPH 24100 26600 31 40 MPH. 20100 21600 31 40 MPH 12900 13600 31 40 MPH 11200 11500 31 40 MPH 10800 11200. 31 40 MPH 2600 3200 01 25· MPH 2200 2700 o, 25 MPH 15300 16300 1/21 35 MPH 11600 13300 1/2\ 35 MPH 11400 12200 1/21 35 MPH 10200 11300 1/21 35 MPH 10500 11600 1/21 35 MPH 1400 1400 1/2\ 35 MPH 2100 2400 o, 25 MPH 1500 1900 o, 25 MPH 3800 5000 o, 25 MPH 4700 6400 o, 25 MPH 1000 1000 o, 25 MPH 0 0 Number of Traffic Lanes 6 6 6 6 4 4 4 4 4 4 4 .. 4 . 2 2 4 4 4 4 4 4 2 2 2 2 2 0 N -..J 0 0 80/234 • Roadway OJ N El Fuerte Street Alga Road Other Interior Streets Roadway Section (See Fig. El E2 E3 E4 E-E Al A2 All Sections 9) 0 0 Q TI\BLE V FUTURE ROADWAY PARAMETER VALUES USED FOR ANALYTICAL PROJECTION OF FUTURE ROADWAY ~OISE IMPACT Ultimate ADT Percent Travel Speed Without • With Heavy Den~ity Density Trucks Bonus Bonus . 12700 13600 1/2% 35 MPH 12800 • 13700 1/2% 35 MPH 4500 4800 -1/2% 35 MPH 3600 3600 1/2% 35 MPH 400 400 1/2% 25 -MPH 2800 2800 1/2% 35 MPH 1800 1800 1/2% 35 MPH Under Under 0% 25 MPH • 1500 1500 0 0 0 Number of Traffic Lanes 4 4 4 4 2 4 4 ·- 2 ? I ' I ) ; 0 6 0 0 0 0 0 0 0 10 I ' . 80/234 . 29 l. , I I • I ------· -• FIGURE 9: • Roadw~y Segments Lab.els EUOACOUS7JCAL ;~l~r:r;~ ~ :bel letter and number lab~~i~§i5RINGCDJ:i!=; e V. roadway se gment 80/234 Roadway Palomar Airport Road Melrose Avenue ·-' . . Carrillo. Way El Fuerte Street 30 TABLE VI* FUTURE. (ULTIMATE) ROADWAY NOI~E. IMPACT Roadway Section (See Fig. 9) Pl P2 P3 P4 P-S Ml M2 M3 M4 MS M6 M7 ' M-W M-E Cl C2 C3 C4 cs CG C-NE C-SE C-NW ·c-sw c-s El -- E2 -:e:3 E4 E-E ·Future(Ultimate)Noise Impact At 100 Feet From Centerline Without Density Bonus.= With Dens i_ty Bonus 70.2 dB CNEL 70.4" dB CNEL 70 dB CNEL 70.i dB CNEL : 69. 4 dB CNEL 69.5 dB CNEL 70.5 dB CNEL 70.7 dB CNEL 55.8 dB CNEL 56.8 dB CNEL -. 66.3 dB CNEL 66.6 dB CNEL 65.8 dB CNEL 65.9 dB CNEL 66.5 dB CNEL 66 .9 dB CNEL 65.7 dB CNEL 66 dB CNEL 63.7 dB CNEL 64 dB CNEL 63.l dB CNEL 63.2 dB·CNEL 63 dB CNEL • 63.1 dB CNEL 47.3 dB CNEL 48.2 dB CNEL 46. 6 dB CNEL 47.5 dB CNEL ... 60.2 dB CNEL 60.5 dB CNEL 59 dB CNEL 59.6 dB CNEL 58.9 dB CNEL 59.2 dB CNEL 58.4 dB CNEL ·sa. 9 dB CNEL 58.5 dB CNEL 59 dB CNEL 49 ., 8 dB CNEL 49. 8 dB CNEL _46. 4 dB CNEL 47 dB CNEL 44.9 dB CNEL . 46 dB CNEL 49 dB CNEL 50.l dB CNEL 50 dB. CNEL 51.2 dB CNEL 43.1 dB CNEL 43.1 dB CNEL 59.4 dB CNEL· 59.7 dB CNEL 59. 4 dB CNEL 59.7 dB CNEL 54.9 dB CNEL 55.2 dB CNEL 53.9 dB CNEL 53.9 dB CNEL 39 0 2 dB CNEL 39.2 dB CNEL * The future ·motor-vehicle noise impacts presented· in _ this table represent ,;worst-case" projections. In perfo:rming the future noise impact calculations, no assumptions were made for future motor~vehicle quieting.· Although vehicles in the future will likely be somewhat quieter than current models, the analysis was completed assuming no change in vehicle noise emission. • 0 0 0 0 0 0 0 0 0 :O I )0 I lo I I I 0 I 0 10 I 0 0 0 0 31 80/234 TABLE VI* ·FUTURE (ULTIMATE) ROADWAY NOISE IMPACT Roadway Roadway •. Future(Ultimate)Noise Impact· At 100 Feet From Section Centerline (See Fig.9) Without Density Bonus With Density Bonus ·, Alga Al 52.8 dB CNEL 52.8 dB CNEL Road A2 50.9 dB CNEL 50.9 dB CNEL Other All 44.9 dB CNEL 44.9 dB CNEL Interior Sections Streets * The future motor-vehicles noise impacts presented in this table represent "worst-case" projections. In performing the future noise impact calculations, no assumptions were made for future motor-vehicle quieting.· Although vehicles in the future will likely be somewhat ·quieter than current models, the analysis was completed assuming no change in vehicle noise emission. BIOACCUSTlCAL . ENtiiNEi:~!NGCO~R 32 80/234 Future Carlsbad Racewav Motocross Noise Imoact As with the dragster operations, it is expected that the Carlsbad Raceway Sunday Motocross activity will rern·ain unchanged in future 0 years. It is assumed that the current "worst-case" 48. 7 dB CNEL 0 motocross noise impact will remain the same in future years throughout the Rancho Carrillo development. COMPARISON OF CURRENT AND FUTURE NOISE IMPACTS The preceeding analyses indicate that the proposed Rancho Carrillo development has a current and future noise exposure from four dif_ferent sound sources. The noise environment on the develop- ment property is influenced by: Aircraft operations, motor-vehicle travel; dragster operations; and motocross activity. In future years the development CNEL exposure from aircraft sound sources is expected to increase up to3.2dBA throughout the property. Future motor-vehicle CNEL noise impact is projected to increase as little as 2 dBA along existing roadways and as much as 22 dBA along future roadways that do not currently exist. Project CNEL noise exposure from Carlsbad Raceway dragster and motocross activities is expected to remain unchanged in future years. Table VII on the next page shows a comparison of the current and expected future Rancho Carrillo noise exposures. FUTURE UNMITIGATED OVERALL DEVELOPMENT NOISE EXPOSURE The unmitigated overall future Rancho Carrillo noise exposure is expected to be somewhat greater than the current noise impact. As previously mentioned, the future noise impact will be the result of four different sound sources: Aircraft operation, motor-vehicle traffic, dragster races, and motocross activity. Among these four noise source categories, motor-vehicle traffic is expected to be the greatest contributor to the overall noise impact. Noise impact from the future aircraft operations is ex- pected to be very moderate. The future worst-case aircraf~ weekend noise impact of 58 dB CNEL will add less than-2 dBA to road· noise impacts of 60 dB CNEL and above. The expected future noise impact from dragster and motocross activities is projected to be quite minimal. It is expected that the overall development noise exposure will be increased by less than 0.5 dBA from Carlsbad Raceway activities. The future unmitigated overall noise impact expected within the development -has been divided into four impact ~ategories. These categories include: Zone 4: Future unmitigated overall exposures from 55 dB CNEL to 60 dB CNEL. elCACCU5i1CAL ENCU\IE:ttlNCCC~R 0 0 0 0 0 0 0 0 0 0 NOISE SOURCE Palomar·Airport Aircraft Operations Palomar Airport Road Segment: Pl I (See Figure 9) P2 ' ; P3 • P4 .. I PS t-1elrose Avenue Road Segment: Ml (See Figure 9) 1' M2 -M3 M4 M5 M6 0 0 0 0 0 0 0 TABLE VII COMPARISON OF CURRENT AND EXPECTED FUTURE (ULTIMATE) Rl\NCIIO CARRILLO DEVELOPMENT NOISE EXPOSURE CURRENT "1-JORST-CASE" '• EXPECTED FUTURE (ULTIMATE) NOISE IMPACT "WORST-CASE" NOISE IMPACT 51.5 dB CNEL (weekdays) 54.7 dB CNEL (we~kdays) • 52.8 dB CNEL ·cweekend) 56 dB CNEL (weekend) 67.4 dB CNEL (100' from Centerline) 70.4 dB CNEL (1001 from Centerline) 67.4 dB CNEL (1001 from Centerline) 70.2 dB CNEL (100 1 from Centerline) 67.4 dB.CNEL (1001 from Centerline) 69.5 dB CNEL (100 1 from Centerline) 67.4 dB CNEL (100' from Centerline) 70.7 dB CNEL (100' from Centerline) Ambient level (-45dB CNEL) 56,8 dB CNEL (100 1 from Centerline) Ambient level (~ 45 dB CNEL) 66.6 dB CNEL (100' from Centerline) Ambient level (~ 45 dB CNEL) 65 •. 9 dB CNEL (100' from Centerline) Ambient level (~ 45 dB CNEL) 66.9 dB CNEL (100' from Centerline) Ambient level ,,., 45 dB CNEL) 66 dB CNEL (1001 from centerline) Ambient level ( ,v 45 dB CNEL) 64 dB CNEL (1001 from Centerline) • Ambient level (~ 45 dB CNEL) 63.2 dB CNEL (loo·• from Centerline) w l.J 80/'>34 NOISE SOURCE Melrose Avenue (Continued·) Road Segment: (See Figure 9) t, D::arrillo Way ''~oad Segment: f,,(See Figure 9) . m 2 Cl 0 --z m Lil.Ill 2 Cl M l~ A'1 :u I ~ j .:A ; ~ ~ M7 M-W M-E - Cl C2 CJ C4 cs C6 C-NE C-SE C-NW c-sw 0 TABLE VII(Continued) COMPARISON OF CURRENT AND EXPECTED FUTURE (ULTIMATE) RANCHO CARRILLO DEVELOPMENT NOISE EXPOSURE CURRENT "WORST-CASE" EXPECTED FUTURE (ULTIMATE) NOISE IMPACT "WORST-CASE" NOISE IMPACT Ambient level (~ 45 dB CNEL) 63 •. l dB CNEL (190' from Centerline) Ambient level ( ~ 45 dB CNEL) .48.2 dB CNEL (100 1 from Centerline) All!bient level (,., 45 dB CNEL). 47.5 dB CNEL (100' from Centerline) Ambient level (~ 45 dB CNEL) 60.5 dB CNEL (100' .from Centerline) Ambient level (~ 45 dB CNEL) 59.6 dB CNEL (100' from Centerline) Ambient level (~45 dB CNEL) 59.2 dB CNEL (100 1 from Centerline) Ambient level ,,.,45 dB CNEL) 58.9 dB CNEL (100' from Centerline) Ambient level (~45 dB CNEL) 59 dB CNEL (100 1 from Centerline) Ambient level (-45 dB CNEL) 49.8 dB CNEL (100'· from Centerline) Ambient level (-45 dB CNEL) 47 dB CNEL (100' from Centerline) Ambient level (,., 45 dB CNEL) 46,dB CNEL uoo• from Centerline) Ambient level (~45 dB CNEL) 50.1. dB CNEL (100' from Centerline) Ambient level , ....... 45 dB C_NEL) 51.2 dB CNEL (100 1 from Centerline) 0 0 0 0 0 0 0 I,. .t, _() 0 0 NOISE SOURCE Carrillo Way (Continued) Road Segment c-s (See Figure 9) El Fuerte Street Road Segment: El (See Figure 9) E2 I ii E3 8 ,..,. rl t» E4 ·m ti ... 2 m ... ~ E-E f~ 11 la !Alga Road II~ I Road Segment: -Al ~(See Figure 9) -A2 Other Interior Streets Carlsbad Raceway z Cl n t1 Al :0 Dragster Operations Carlsbad Raceway Motocross Activity I , 0 0 0 0 0 0 0 TABLE VII(Continued) COMPARISON OF CURRENT AND EXPECTED FUTURE (ULTIMATE) RANCHO CARRILLO DEVELOPMENT NOISE EXPOSURE CURRENT "WORST-CASE" EXPECTED FUTURE (ULTIMATE) NOISE IMPACT "WORST-CASE" NOISE IMPACT t Ambient level ( ~ 45 dB CNEL) 43.\ dB CNEL (100 1 from Centerline) Ambient level (~ 45 dB CNEL) 59.7 dB CNEL (1001 from Centerline) Ambient level l~ 45 dB CNEL) 59.7 dB CNEL (1001 from Centerline) Ambient level (~ 45 dB CNEL) 55.2 dB CNEL (1001 from Centerline) Ambient level ( ..... 45 dB .CNEL) 53.9 dB CNEL -(1001 from Centerline) . Ambient level (""" 45 dB CNEL) ""45 dB CNEL ' Ambient level (,., 45 dB CNEL) 52.8 dB CNEL (100' from .Centerline) Ambient level (,.. 45 dB CNEL) 50.9 dB CNEL (100' from Centerline) Ambient level (,., 45 dB CNEL) 44.9 dB CNEL (100 1 from Centerline)· 41.9 dB CNEL(Saturday only) 41.9 dB CNEL (Saturday only) 48.7 dB CNEL(Sunday only) 48.7 dB CNEL (Sunday only) 0 w Ul J 36 80/234 Zone 3·: Future unmitigated overall exposures from 60 dB CNEL to 65 dB CNEL. Zone 2: Future unmitigated overall exposures from 65 dB CNEL to 70 dB CNEL. Zone 1: Future unmitigated overall exposures over 70 dB CNEL. The location of each future unmitigated noise exposure zone within the Rancho Carrillo development is shown by shaded noise contours in Figures 10 through 35 on the next pages. Figure 10 shows the entire project site plan divided into 25 sections. Each· section is numbered and enlarged in the subsequent figures to show the unmitigated noise contours in detail. It is understood that in an alternative development plan Palomar Airport Road may be re-aligned to the north. Land use plans for the property north of the current roadway alignment call for industrial usage. The property south of the road is planned for ·residential development. If Palomar Airport Road was re-positioned to the north and the industrial and.residential areas remained • unchanged, several changes in the residential noise exposure would be expected. First, with a substantial (200 to 300 foot) northerly re-alignment of Palomar Airport Road, the residential area road noise impact would be greatly reduced. Second, with the removal of Palomar Airport Road as a buffer between the two land uses, the residential area would be adjacent to the potentially high industrial noise emissions. The net change in residential noise exposure is unknown. If the industrial uses represent heavy industry with facilities that tend to leave manufacturing bay doors open, the residential noise impact may be as high as, or greater than, the projected road noise impact. Alternatively, if the industrial land uses represent medium to light industry with moderate noise emissions, the projected residential noise exposure may decrease 5 dBA to 10 dBA. An accurate determination of the actual residential· noise impact resulting from a northerly re-a1ignment of Palomar Airport Road is dependent upon further information regarding the actual distance of roadway movemen~ and the types of industrial uses. GENERAL NOISE IMPACT MITIGATION MEASURES State and local standards for exterior noise impact limit the,per- mitted outside-to-inside noise intrusion to 45 dB CNEL for all residential construction. In addition, local criteria limit noise impact in all primary outdoor living space to 65 dB CNEL. Based upon the noise impact category for each area of the Rancho Carrillo.development, varying noise control measures will be needed _to comply with state and local standards. A summary of the general mitigation measures required for each noise impact category is shown below. 0 0 0 0 0 0 0 0 0 0 0 • • • ULTIMATE NOISE EXPOSURE UNMITIGATED WORST CASE CONDIT IONS. ULTIMATE PALOMAR AIRPORT, ROADWAY AND CARLSBAD RACEWAY NOISE SOURCES. !WITH TRAFFIC FROM DENSITY HOUSING BONUS AND SCHOOL CONVERSION.) 2 3 4 5 studied. 37 .·:.:~i:. ,._ ~:: • :: :~1';"~ ' .. • ' ~;:.: ~':. ~~-. :,.: ~. r • • -... _• P ·• ·1• I 6 - l:IZ0NE1: OV 70d8 CNS. P+UONE2: 65 70d8 CNEL EDZONE3: 60 o 65dB CNB. OZDNE4: 55 o 60dB CNS. 1 I 16 . 13 14 24 25 GURE 10: Rancho Carrillo Site Plan Secti ons -ach ares own individually in Figures 11 through 35. (On file with· City of Carls- bad B!CACDU5T1CAL ENCiNEEttlNCCO~~ 63 80/234 Zone 4: Noise imoact 55 dB CNELto 60 dB CNEL Zone 3: Zone 2: Zone 1: For compliance with the exterior-to-interior noise exposure limit of 45 dB CNEL, operable windows and doors must be closed and a means of mechanical ventilation must be provided. Such ventilation w-ill provide a habitable interior environment while operable windows and doors are closed for sound control. This ventilation may be supplied by a "summer switch" on the forced air heating/cooling unit or air conditioner to operate the fan for air circulation independent of the heating/cooling function. If a "summer switch" is added to the FAU, the UBC requires a fresh air intake duct to supply 20 percent of the air from outside. In addition, this means of ventilation must provide at least two air changes per hour. Noise impact 60 dB CNEL to 65 dB CNEL To satisfy the state and local exterior-to-interior 45 dB CNEL noise control limit, operable exterior windows and doors must be closed, mechanical ventilation is required, and the dwelling facades must be acoustically engineered. The dwelling shell acoustical engineering involves a room-by-room analysis of each floor plan. This analysis shows the exterior doors and windows needed in each outside wall to provide satisfactory • noise control performance~ Noise impact 65 dB CNEL to 70 dB CNEL Areas within this noise impact category require measures for control of outside-to-inside intrusion to meet the 45 dB CNEL limits, and measures for reduction of outdoor living space sound levels to meet the 65 dB CNEL criteria. Outside-to-inside mitigation requires operable windows and doors closed, mechanical ventilation provided and acoustically engineered dwelling shells. Control of noise impact in primary outdoor living areas requires design of an acoustical barrier for placement between the roadway and outdoor area. The design of necessary acoustical barriers involves specification of the barrier plac·ement and top-of-wall grade. Minimum barrier height will provide a line-of-sight break between a point five feet above the outdoor living space grade and a point zero feet (for cars) or eight feet (for trucks) above the road grade. Common barrier construction materials include, masonry block, masonry block and earth berm combination, and continuous solid wood. Noise imoact 70 dB CNEL and above Development areas subject to this noise impact category require substantial abatement measures to reach the • ) ) 0 0 0 0 \O I I 0 0 80/234 Zone l: (cont'd) 64 required 45 dB CNEL interior noise environment and 65 dB CNEL exterior noise exposure. Control of noise in interior living areas requires operable windows .and doors closed, mechanical ventilation,. and acoustically engineered dwelling shells. In this impact category, dwelling construction requirements will incorporate increased window glazing thickness or double sash construction. Compliance with the outdoor living space sound·exposure limits requires an acoustical barrier design. _ The necessary sound control barrier will be higher than for all other noise impact categories. Areas within this.sound exposure group are on the borderline of feasibility for residential construction. Detailed recommendations for control of sound exposure in indoor and outdoor living areas cannot be accurately made in the general planning stage of a development. Specific mitigation measures are best made in the final stages of development when grading plans, building positions and floor plans are complete. Specific noise control recommendations should be formulated prior to issuance of building permits and reviewed by the Building Department. Although specific noise control measures cannot be outlined at this time, it is useful to show the approximate mitigation that can be achieved by general noise control approaches. Presented below is an indication of the outdoor living space acoustical shielding that can be expected from representative, practical, noise control barriers·. ·- Figure 36 on the next page shows the development unmitigated noise exposure and the general exposure mitigation that can be expected for three representative barrier sections. Figures 37, 38_ and 39 present the barrier sections 1, 2 .and 3 respectively at a larger scale. Noise-control barrier sections 1 and 2 are located along Palomar Airport Road. Section 1 is at a point where the roadway is roughly 40 feet above the project property to the south. Section 2 is at a point where the road grade is roughly the same as the property grade to the south. Noise control barrier section 3 is located along Melrose Avenue. Section 3 i·s located where the roadway is approximately 30 feet·above the property grade to the west. For each of the representative barrier cuts (1,2, and 3) the barrier for control of· outdoor noise impact was located at the approximate near edge of roadway right-of-way. Calculations of the expected acoustical shielding were made using the reference 19 barrier analysis equations and using the typical motor-vehicle spectra in reference 20. The. shielding analyses were performed BHJACOU5i1CAL ENCiNEi~INGt:OFiF. ULTIMATE NOISE EXPOSURE . . UNMITIGATED WORST CASE CONDITIONS.• ULTIMATE PALOMAR AIRPORT, ROADWAY AND CARLSBAD RACEWAY NOISE SOURCES. !W 1TH TRAFFIC FROM ·oENSITf HOUSING BONUS AND SCHOOL CONVERSION.] -... . . --:::----~~ -This area not studied., • ·:-.:•·::•:•.: .. ,., ...... •:::,.::·:·❖·:.:.:•.·-:-•:;::".·'··•-:•.···:.:::··•.•::.:,::.:::'.:·:::'.::::::%'.:.:::,:: ··::; ··-~:, ......... -... C""· ~~ • KE~-\ :~:~:::1~:~~~ ~ ' OZ0NEJ: soto 65dB CNEL •• OZONE4= 55to60dB CNEL M . -~~-===--::::::.:::r::;::. FIGURE 36: Typical Barrier Noise Control Shielding Shown above are three cuts which·indicate the reduction in exterior noise exposure from typical noise control barriers. Each cut is enlarged in Figures 39,38 and 39. 65 BIO ACOUSTICAL ENGINEERING CORP. ( C C C 0 0 0 0 • • 66 ----.. ~ ------··-------- .:•:::.:;:;. __ - • • e e A e • e • • • • •• • • ••.•.:-• • e • e • ., . ·.·.···· ..... ·.·.···· ... ·.·.·. • .... _ .... · .... • : •• .-.·. ·.·.·····~·.··· •.•.•·•••••••• • ·.= ,..~~-····•:•:•.······ . . . " . . . ... ·• . . . ...... ·. --..,/ -. . . ... . . . . .. . . . . . . . . . . . . . . . ---· . . . .. ' • • • • • • ••••• • • • ,. • , •• •••• • • • • • • .•--:;t • • • • • • . . . . . . . . ,. . . . .. '• .... .......... = ;a C I : I . . . . . ,. . . ...................... •- -----------·---------.. ......... • .. -:.,, ..................... It.in' = -~ ::::~:} l:IZONE1: OV 70dB CNB,· :~·\*<::.·:)J(~ • _ ',1 : .. :.; .. :..... ·:.;.·:•; .. :: .. ; .... ;.· .. ~:,·: .... : .. :•: .. :•: ... ~~ = ·::-:./::• f,>+tz0NE2: 65 70dB CNEL :•:.::•:./::•::-:.::•:.;:•:-::-::::~:-~ -= ~::::::::::::. :::::~:::}::~:::;:::::f::~::::;::::::::::::::~ • .._ ........... ~NE3· 60 o 65dB CN8. ............................. : ......... --....._ ____ -:}::::::::: . ::::::::::::::}::::::::::::~}:::::{:::{:: -= .. ..-.. ..-.... OZ[)NE4: 55 O 6DdB CNa .............................. ..-.. ..-............. • - ~ FI.GORE 37: Cut 1, Typical Barrier Noise Control Shielding Shown above is the Cut 1 barrier along Palomar Ai rport Road. Also shown is the change in exterior noise exp osur expected from the 4 foot barrier at edge of right-of- way. s;cACDUST]CAL E?-J~iNEitt!NGCO~~ 80 2 4 67 -. § = = ~ ---------~ -~ § ~ -~ FIGURE 38: Cut 2, Typical Barrier Noise Control Shielding Shown above is the Cut 2 barrier along Palomar Airport Road. Also shown is the change in exterior noise exposure expected from the 8 foot barrier at edge of right-of-way. • • • 68 80 234 FIGURE 39: Cut 3, Typical Barrier Noise Control Shielding Shown above is the Cut 3 barrier along Melrose Avenue. Also shown is the change in exterior noise exposure expected from the 3 foot barrier at edge of right:-of-way . 80/234 69 assuming approximate barrier heights of 4 feet for cut 1 (Figure 37), 8 feet for cut 2 (Figure 38) and 3 feet for cut 3 (Figure 39). A receiver height of 5 feet above pad grade, an automobile noise source height of zero feet above road grade, and a truck noise source height of eight feet above road grade were also used in the calculations. In performing the barrier.analyses, expected noise impact, vehicle-to-barrier distance, and barrier- to-receiver separation were also considered. Expected attenuations for automobile and heavy truck traffic were determined separately. Figures 37, 38, and 39 indicate the general changes in development exterior noise exposure which would be accomplished by the representative barriers. Figure 37 (Cut 1) indicates that a 4 foot barrier positioned at this location would eliminate the Zone 1 (over 70 dB CNEL) and Zore 2 (65 to 70 dB CNEL) exposures. The Cut 1 barrier would change the unmitigated noise exposure to a small Zone 3 exposure (60 to 65 dB CNEL) directly behind the barrier and a Zone 4 exposure (55 to 60 dB CNEL) in all areas beyond Zone 3. Figures 38 (Cut 2) shows that an 8 foot barrier positioned at the indicated location along Palomar Airport Road would also eliminate the Zone 1 (over 70 dB CNEL) and Zone 2 (65 to 70 dB CNEL) exposures. The Cut 2 acoustical shielding would change both the unmitigated Zone land Zone 2 exposures to a Zone 3 exposure (60 to 65 dB CNEL). Figure 39 (Cut 3} indicates a 3 foot barrier along the edge of the • Melrose Avenue right-of-way. Calculations indicate that the Cut 3 barrier would be expected to change the unmitigated Zone 2 (65 to 70 dB CNEL) and Zone 3 (60 to 65 dB CNEL) exposures into a small Zone 3 area and a Zone 4 exposure (55 to 60 dB CNEL) in all areas beyond the mitigated !Zone 3. The representative barrier cuts shown in Figures 37, 38 and 39 indicate the general sound control performance that can be expected from typical, practical, barriers. Each of the typical barrier cuts indicate that the unacceptable exterior exposures above 65 dB CNEL can be reduced to below 65 dB CNEL and well within permitted limits. It is noted that Figures 37, 38, and 39 are not intended to represent specific noise control barrier designs. Rather, these figures show the-general mitigation that is feasible. The specific noise control barrier placements, heights and materials of construction must be determined at a later time when more detailed development information is available. CONCLUSION An acoustical analysis of the proposed Rancho Carrillo residential development has been performed. In performing this analysis, the current noise environment was measured at several locations on the property. The current field measurements indicate that there are four noise source groups which produce measureable sound exposure levels within the projec~. The sources of present noise exposure include: Aircraft fly-over activity, motor-vehicle 210ACDU571CAL E?JC3~E::i!NCCD~~ I ') I '0 I 0 I 0 0 ,0 I 0 0 80/234 70 traffic, Carlsbad Raceway dragster operations, and Carlsbad Raceway motocross activities. The only significant source of current noise exposure is from motor-vehicle traffic along Palomar Airport Road. This exposure is concentrated at the northern portion of the planned development. Aircarft fly-overs currently produce a low CNEL exposure across the entire develop- ment. Carlsbad Raceway noise emission produces an insignificant contribution to the current noise environment. An analysis of the future (ultimate) project noise exposure indicates that the same four noise source categories will influence the Rancho Carrillo noise environment. The future overall·project noise exposure is expected to be greater than the current impact due to a large increase in motor·-vehicle noise impact and a moderate increase in aircraft noise impact. The future Carlsbad Raceway noise impact is expected to remain essentially the same· as the current levels. In future years motor-vehicle noise impact will remain the only significant contributor to the project CNEL exposure. Future aircraft operations are expected to make ·a very small contribution to the Rancho Carrillo CNEL exposure levels. Future Carlsbad Raceway noise levels are projected to produce essentially no change in the project noise environment. Using the future noise impact information, the overall noise exposure from all four principle sound sources has been determined for the development area south of Palomar Airport Road. The noise exposure range expected within the project has been divided into four future noise impact zones. • Compliance with state and local noise limits in all indoor and outdoor residential living areas requires certain mitigation measures. Among the four exposure zones·, the control measures range from nothing to stringent acoustical design requirements. In general, the majority of the planned Rancho Carrillo develop- ment will be exposed to an expected minimal to moderate future noise exposure. Once preliminary site and building plans are deveioped, acoustical engineering design will be required for dwellings exposed to 60 dB CNEL or more and outdoor living areas exposed to 65 dB CNEL or more. It is _expected that compliance with the interior 45 dB CNEL exposure criteria will be easily met using standard construction with only minor material upgrades. Calculations indicate that the attenuation expected from typical, practical, barriers will reduce the exterior noise exposures to within the 65 dB CNEL exposure limits. elCACCUSTlCAL ENCiNEERINCtO~P. 80/234 71 REFERENCE LIST 1. California Administrative Code, Title 25, Chapter 1, Subchapter Article 4; Section l092i "Noise Insulation Standards". 2. Comprehensive Planning Organization of the San Diego Region, Comprehensive Land Use Plan Palomar Airport, May 1974, Page 10, Table 11-1. 3. Pearsons, Karl., et. al., Handbook of Noise Ratings, NTIS U.S. Department of Commerce Document #N74-23275, pr,epared by Bolt, Beranek, and Newman under Contract #NASl-11, 839 Task 2, for National Aeronautics and Space Administration, April 197 4, ·-Pages 104 through 112. 4. Private telephone discussion with Mr. Lacy Clark, Palomar Airport Assistant Manager, 11 January 1980. 5. Private telephone discussion with Mr. Philip Safford, Assistant Director of Palomar Airport, 17 January 1980. • 6. Private telephone.discussion with Mr. K. Dean, Controller for the Palomar Airport FAA tower, 17 January 1980. 7. Pearsons, Karl S., ·op. cit. Pages 198 through 205. 8. Gorden, C.G., et. al., Highway Noise, A Design Guide for Highway Engineers, Nat~onal Cooperative Highway Research Program Report 117, by Bolt, Beranek and Newman·, 1971, Page 11. 9. Pearsons, Karls., op. cit., Pages 100 through 103. 10. Urban Development and Transportation Studies, Los Angeles International Airport Series, Volume 4, prepared by Olson Laboratories, Inc., for the Los Angeles Department of Airports and FAA, July 1975, page 2-51, Figure 2.14. 11. Leyerle, John S. and Bixler, Otto C. Jr. , Short-Term· Sampling Techniques for Determination of Motor-Vehicle Traffic Noise Exposure, published in Proceedings, 1978 International Conference on Noise Control Engineering, May 1978, pages 671 through 674. 12. Fundamentals and Abatement of Highway Traffic Noise, prepared by Bolt, Beranek ana Newman, Inc., 1:or f'ederal Highway Administration, June 1973, _PB-222 7 03, Pages 1-10. 13. Private telephone discussion with Mr. Larry Grismer, Carlsbad Raceway Operator, 10 January 1980. 14. Pearsons, Karl S. I I I j I C' \ \ I CY \ \ \ 1, '· C 1 I ' I I \ ! \ 0 0 0 0 0 0 0 C 0 0 0 0 0 0 0 0 0 0 0 APPENDIX J NOISE STUDY ,,;, VINCENT MESTRE ASSOCIATES, 1981 lsa 0 0 0 0 0 0 0 0 0 0 0 March 25, 1981 Ms. Annette Sanchez LARRY SEEMAN ASSOCIATES 500 Newport Center Drive Suite 525 Newport Beach, CA 92663· SUBJECT: Palomar Airport Noise Contours Dear Annett.e, VINCENT MESTRE ASSOCIATES CONSUL TING ENGINEERS The following report summarizes the noise impacts of Palomar Airport on the Carrillo Ranch project. Assessment of the airport noise was based upon the generation of noise contours for Palomar Airport operations. Contours were developed for· existing conditions (1980} and a future year estimate of operational levels (1990}. OPERATIONS Existing contours were generated based upon 257,762 annual operations while 1990 contours were based upon· an assumed traffic volume of 435,000 annual operations. While the total number of operations were projected to increa~e substantially, the aircraft mix for the future years is anticipated to be composed of quieter aircraft. Helicopter-flights were not included in the .model. Appendix A ,summarizes, in detail, the operational data used to generate the noise contours. Since thfs report is specifically for analyzing the impacts of airport noise on the Carrillo Ranch project, greater detail in flight track and operational modeling was included for that region of the airport I s environs. • Operational assumptions were derived from a month long survey conducted by the airport of aircraft types, runway utilization, and flight tracks. Additional infonnation was gathered from a meeting with Mr. Philip Safford, Palomar Airport Manager, and Mr Richard Severson; Assistant Airport Manager. METHODOLOGY The airport noise contours were generated utilizing the Integrated Noise Model (INM), Version 2.7, developed by the Federal Aviation Administration (FAA). The INM was designed to provide a noise model with standard aircraft noise and performance data that •can also be tailored to the characteristics of the airport being analyzed. ZOO NEWPORT CENTER DRIVE, SU.ITE 213 • NEWPORT BEACH, CALIFORNIA 92660 • (714) 760-0891 The !NM program requires the input of the physical and operational characteristics of the airport. Physical characteristics include runway coordinates, airport altitude and temperature. Operational characteristics include aircraft mix, time distributfon, flight tracks, approach and departure profiles, and optional noise curves. The computer program takes this input data and computes locations of equal noise values, or, noise contours. In addition to generating noise contours, the INM noise model will also determine the noise level at any specific location. In the State of California, airport noise contours are typically depicted in terms of the Community Noise Equivalent Level (CNEL) index. Appendix B gives a detailed discription of the CNEL index and of airport noise assessment criteria. In general, the critera used for assessment of airport noise on· residential land use is 65 CNEL. RESULTS The existing noise contours for Palomar Airport are depicted ·in Figure 1. The dominate aircraft in determining the size of the contours is the turbo-jet business aircraft that operate out of Palomar. This would include aircraft such as the Lear 24's and 25's and the Saberliner 60 1 s. Even though very few of these aircraft are at the airport (5 operations per day), they are by far the loudest aircraft. The results show that the. 65 CNEL contour .does not reach the Carrillo Ranch property. The ·model est·imates that the no.i se 1 evel in the center of the property would be a CNEL of 51. • At the northern boundry of,. the . property, closer to the arri va 1 tracks,· the noise level is estimated to be a. CNEL of-55. The noise environment on the Carrillo Ranch is • affected by noise from business jets on the• ILS approach and from smaller.piston aircraft overflyi_ng the site on approach for landing. The Palomar Airport contours for 1990 are shown in Figure 2. The 65 CNEL contour for 1990 is estimated to also not reach the Carrillo· Ranch .property. These contours are based upon 435,000 annual operations. This is cons.idered an optimistic assumption for airport growth,. 'thus, these contours are an estimate of worst case ·noise, in terms of operational level. The noise level in the c.enter of the . property is projected to be a CNEL of 53. At the northern boundary of the property the.noise level is estimated to be a CNEL of 57. Thus, the noise environment at the site is anticipated to increase by 2 dBA. The small increase in the noise levels even with the large increase in operations is due to the anticipated increase in the proportion of the quieter turbo-fan engined aircraft in the bus-iness jet fleet. This is considered a valid assumption because nearly all new business jet aircraft are using qui et high-bypass· ratio turbo-fan engines. • 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 The noise environment on the project site is well below the 65 CNEL criteria. However, this does not mean that there is not a potential for noise complaints from_ residences once the project is completed._ The greatest potential impact will be from the occasional piston aircraft that overfly the site when on approach .to land at the airport. Peak noise on the site from these operations could be as high as 70 to 80 dBA. While these occasional aircraft are not loud, they may result in sporadic, unpredictable single event annoyance. Yours Truly, VINCENT MESTRE ASSOCIATES R-,QL~- Paul H. Dunholter Engineer FIGURES 1 AND 2 ARE OVERSIZED FIGURES AND ARE INCLUDED IN A COPY OF THE REPORT ON FILE WITH THE CITY OF CARLSBAD. lsa 0 0 0 ! 10 0 0 0 0 0 0 0 0 I ',O ' Pagel APPENDIX A PALOMAR AIRPORT' -OPERATIONAL DATA I. AVERAGE DAILY AIRCRAFT OPERATIONS 1980 ------ Business Jet (turbo.jet) 5 Business Jet ~turbo fan) a light Single Riston) 188 Medium Single (piston) 390 Twin Engine (piston) 88 ------TOTAL 679 II. PERCENT OF OPERATIONS IN EACH TIME PERIOD Day (0700-1900). -94% Evening. (1900-2200) -Si Night (2200-0700) -11 III. RUNWAY UTILIZATION 1990 -----~ 7 28 357 538 262 • ------1190 For all aircraft types, Runway 24 is assumed to be utilized' 99 % of the time. Runway 06 is estimated to carry 1% of the traffic. Page 2 IV. FLIGHT TRACK UTILIZATION Nine flight tracks have been specified for Palomar Airport. The tracks are depicted in Figure A. These flight tracks and their utilization is assumed to be the same for 1980 and 1990. Because this report is analyzing the noise impacts on the Carrillo Ranch project located southeast of the airport, more detail in modeling flight tracks is done in this region. The percentage utilization of each flight track per each aircraft type is depicted in Table A for Runway 24 operations. This Runway is utilized 99 percent of the time. All business jet traffic is assumed to depart on Track 11 and arrive on Track 21 ... The light single engine piston aircraft is modeled primarily for Touch and' Go 1 s and is placed on these tracks. When modeling Touch and Go operations, Tracks 12 and 13 end where Tracks 22 and 26 begin. For the other operations on these tracks, the tracks are infinite in length. When Runway 06 is utilized (1% of the time), all aircraft will arrive on Track 11 and depart on Track 21. AIRCRAFT TYPE TABLE A FLIGHT TRACK ·ULTIZATION FOR RUNWAY 24 ARRIVAL TRACKS DEPARTURE TRACKS 11 12 13 21 22 23 24 25 26 ------------------------------------------------------------------------- Business Jet (TJ) 100 100 Business Jet (TF) 100 100 Light Single (Pist) 33 67 -33 67' Medium Single (Pist) 40 20 40 40 10 5 3 2 40 Twin Engine (Pist) . 40 20 40 40 10 5 3 2 40 ------------------------------------------------------------------------- 6 0 0 0 0 0 0 0 0 0 0 n n 11 0 2000 4000 SCALE (Fl) VINCENT MESTRE ASSOCIATES CONSULTING ENGINEERS n 0 0 0 0 0 0 0 13 26 12 22 23 24--- 25 FIGURE A PALOMAR AIRPORT FLIGHT TRACKS. Page 1 APPENDIX B NOISE CRITERIA Noise has been defined as unwanted sound and it is known to have several effects on people. From these known effects of noise, criteria have been , established to help protect the public health and safety. This criteria is based on the following known effects of noise on people: 1. Hearing 1 oss 2. Speech Interference 3. Sleep Interference 4. Physiological responses 5. Annoyance Each of these potential noise impacts on people are briefly discussed in the following paragraphs. Hearing loss is, in general, not a concern in environmental noise problems. The potential for noise induced hearing loss is more commonly associated with occupational noise exposures in heavy industry or very noisy work environments. Noise 1 eve 1 s in neighborhoods, even in very noisy airport environs, is not sufficiently . loud to cause hearing loss. For example, the Occupational Safety and Health Administration (OSHA) has identified a noise exposure of 90 dBA 8 hours ·per day 5 days per week for 40 years as accept ab 1 e for the prevention of hearing loss. For shorter exposure times, higher noise levels are permissable. Speech interference is one of the pri_mary concerns in environmental noise problems. Normal conversational speech is in the range of 60 to 65 dBA and any noise in this range or louder may interfere with speech. There are specific methods of describing speech interference as a function of distance between speaker and listener and voice level. Sleep interference is a major noise concern in resJdential areas and is most critical during nighttime hours. Interior noise levels above 45 dBA have been identified as having the potential to cause sleep disturbance. Note that sleep disturbance does not necessarily mean causing people to awaken but can refer to altering the pattern and stages of sleep. Physiological responses are those measurable effects of noise on people which are realized as changes in pulse rate, blood pressure, etc. While such effects· can be induced and observed it is not known the extent to which physiological -responses cause harm or are sign of harm. Annoyance is the most difficult of all noise responses to describe. Annoyance is a very individual characteristic and can very widely from person to person. What one person considers unbearable can be quite tolerable to another of equal hearing capability. In selecting noise criteria it is desirable to design towards the middle of the spectrum of peoples annoyance. C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Page 2 Several rating scales have been developed for the measurement of cormiunity noise on people. They are designed to account for the above known effects of noise on people. Based on these effects, the observation has been made that the potential for a noise to impact people is dependent on the total acoustical energy content of the noise. For a time varying noise the energy average noise level represents the energy content of the noise and is called the Equivalent Noise Level or Leq. Leq is the sound level corresponding to a steady-state sound level containing the same total energy as a time-varying signal over a given sample period. Leq is the 11energy 11 average noise level. Community Noise Equivalent Level, CNEL, is similar to Leq but applies a weighting factor which places greater significance on noise events occurring during the evening and night hours (when sleep disturbance is a concern). CNEL is a 24-hour, time-weighted annual average noise level. Time-weighted refers to the fact that noise that occurs during certain sensitive time periods is penalized for occurring at· these times. In the CNEL scale those events that take place during the evening time period (7 pm to 10 pm) are penalized by 5 dB while events that take place during the night time period (10 pm to 7 am) are penalized by 10 dB. These time period and penalty were selected to reflect people's sensitivity to noise as a function of activity. The CNEL scale is specified by the State of California for airport noise assessment. A CNEL level of 6~ is identified as the maximum outdoor noise level fo.r residential land uses with outdoor activities. For high rise residential (apartments or condominiums) with no outdoor use, higher noise levels are possible with special interior noise mitigation. It is worthwhile to note that the 65 CNEL standard is a compromise based on known health effects and tradeoffs with economic costs. Sensitive individuals may find noise levels less than 65 CNEL annoying. Restricting residential areas to noise exposures less than 65 CNEL does not ensure the elimination of all aircraft noise complaints. The problem of noise complaints occurring in areas subject to noise levels less than 65 CNEL is more common at airports with very few but noisy events. CNEL is a noise metric which combines the loudness of the noise event with the number of noise events. When the noise environment is dominated by a few very noisy events then the CNEL can be quite low but certain single events can be quite loud. It is these few but loud events that can cause annoyance and adverse community response. I 0 0 0 0 0 0 0 0 0 APPENDIX K CORRESPONDENCE lsa 0 0 0 0 0 0 0 0 0 San Marcos Unified School District July 18, 1980 Annette M. Sanchez Associate Project Manager Larry Seeman Associates, Inc. 500 Newport Center Drive, Suite 525 Newport Beach, California 92660 Dear Ms. Sanchez: . • -. 270 San Marcos Boulevard San Marcos, California 92069 Phone: (714) 744-4776 Our district has. reviewed the proposed Rancho Carrillo Planned Cormnunity and have evaluated the impact of that development on the facilities of our· district as follows: • 1 ) Location of existing f acil i ti es -Pl e·ase see enc 1 osed map. · 2) School district generation factors -~27 based upon surrounding developments. - 3) ·Capacity and adequacy of existing facilities -Schools are at capacity with the exception of the high, sthoo 1 . -• • • 4) Potential problems in serving the project site -Excess -~osts of transportation to existing facilities and overcrowding at the elementary school. .. 5) Additional facilities required -School site is included in attached map. Sincerely, ;faeit(r/4~ David L. Larson Director of Business and Operations DLL: 1 g ·-/ --· -✓ j / COMPREHENSIVE ... , PLANNING ORGANIZATION ,_ Suite 524, Security Pacific Plaza 1200 Third Avenue San Diego, California 92101 (714) 236-5300 Ms. Annette M. Sanchez Larry Seeman Associates, Inc. 500 Newport Center Drive, Suite 52S Newport Beach, CA 92660 Dear Ms. Sanchez: .August 1, 1980 As the Airport Land.Use Commission (ALUC) for the San Diego Region, CPO is responsible for the development of compatible land uses-witlrin·the· Airport Influence .Area. The Rancho Carrillo development which is pro- posed.for the City of-Carlsbad would be significantly impacted by aircraft· operations of Palomar-Airport. • • The environmental report you are preparing should thoroughly address the issue of aircraft relat~ noise· from. the airport~-The report should· also describe the var:i,ous mitigation measures which will be implemented to mini-mize the adverse • impacts. • ' ' As you know, the.existing Pal~ Comprep.ensiv~ Land Use Plan is scheduled to be updated :in early 1981. The updated report will have more recent noise contours, an enlarged airport influence area, and a list of r_ecommen- ded-actions for the City, County and CPO to implement to ensure compatible land uses near the· airport. CPO staff supports-the concern express~ to you-by·Mr. Phil Safford in his letter dated July 22,1980 regarding this issue. If you have any questions regarding these matters, please feel free to contact Jack Koerper .at 236-5372. Sincerely, )--,_,,__,_ f ) )( a_ <---t:,:: V JOAN K. MARTIN Director, Areawide Clearinghouse J'IM/JK/oc cc: Phil Safford Bill Hoffman SAN DIEGO REGION'S COUNCIL OF GOVERNMENTS 0 0 0 0 .o 0 0 0 0 0 Member Agencies: Cities of Carlsbad. Chula Vista. Coronado. Del Mar. El Ca1on, Imperial Beacn. La Mesa, Lemon Grove. National City. Oceanside. 0 San Diego. San Marcos. Vista, and County of San DiegoiEx-offic10 Member: California Depan:ment of Transpon:at1on/Honorarv Member: Tijuana. S. CF'A 0 0 0 0 0 0 I. iO I 0 'O 10 R J Massman -·-· 0uectar COUNTY OF SAN DIEGO DEPARTMENT OF TRANSPORTATION Bldo 2. 5 S S S Ovar land Ave. San OieQo. California 92123 OfficH of TelaphaH: (714) 565• 5l 77 Caunty Enoinaar & Raad Commisa1onar County Survayar Caun1y Airport■ July.22, 1980 Annette M. Sanchez Associate Project Manager 500 Newport Center Drive Suite 52S Newport Beach, CA. 92660 Dear Ms. Sanchez: This is in reply to your request of July 8, 1980, for comment relative to the proposed Rancho Carrillo development in the vicinity of Palomar Airport. Palomar Airport is a County owned and operated general aviation facility located within the City of Carlsbad. The airport is open 24 ho:urs a day. In 1979 a total of 268,000 take-offs and landings were completed, making Palomar one of the busiest single runway airports in the nation. The adopted Master Plan forecasts an increase to 400,000 movements by 1990. The Master Plan is scheduled for review and update in early 1981. In recent years as a result of residential growth in the vicinity of the airport, the County and City have received an increasing number of complaints over aircraft noise. These complaints generally come from residents·. two to five miles from the airport. The proposed Rancho Carrillo development is in this area. • A number of actions have already been taken to reduce the impact of airport noise in nearby communities. These include in-flight noise abatement procedures, as well as restructures on use of the airport. While noise abatement flight procedures can mitigate the noise problem, it is unrealistic to assume that such acdons can "solve" the problem. Additional study to identify other possible noise abatement actions is to be undertaken in the near future under an FAA funded Airport Noise and tand Use Compatibility study (ANCLUC). A new set of noise contours for Palomar will be prepared during the ANCLUC studh and should be available in early 1981. The existing noise contours cannot be considered as applicable for the Rancho Carrillo development pending the ANCLUC study which is expected to enlarge the airport influence area and significantly modify the concept of impact zones. t Annette M. Sanchez -2-July 22, 1980 Rancho Carrillo lies within the Palomar Airport three-mile Air Traffic Control Zone. The area is now subject to frequent low level overflight by aircraft and helicopters making both visual and instrument approaches to Runway 24. There is no practicable means by which such overflights can be avoided in the future. Based upon recent noise complaint experience at Palomar, the Rancho Carrillo location is clearly a noise sensitive area. There is no doubt that the residents will encounter problems of compatibility with respect to the airport environment. Requirements for residential sound proofing in the project area can reduce interior noise levels and be of some benefit, but not a solution. If this development is undertaken it will be of utmost importance for the impact of aj.rport operations to be clearly identified to and acknowledged, in writing. by each prospective purchaser prior to the close of escrow. To this objective, airport management will recommend to the City of Carlsbad that the developers be required to grant an avigation easement over the property as a condition for approval of the project. -- PRS: lt cc: CPO (J. Kcerper) City of Carlsbad (J. Hagaman) FM (H.C. Bliss) Dept. of Transportation (R.J. Massman) PMC C C C C C 0 0 0 0 0 0 0 0 ,0 0 o· .. 0 0 ,0 I 0 March 20, 1980 City of C2.rlsbad Planning Department 1200 El Avenue C2.rlsbad, CA 92008 Gentlemen: County of San Diego Environmental Analysis Division 9150 Chesapeake Drive, Room 136 San Diego, California 92123 Telephone: (714) 565-5757 Subject: Notice of Preparation, Rancho Carrillo Master Plan EIR, EAD Log H's 80-7-17; 80-NP-3 We have canpleted our review of the subject Notice of Preparation, and our concerns in addition to those included as 'lhe Potential Issues are as follows: 1.. k?-i.culture: We observe tbat"ithe project· area is within the coastal. • ag:-:.~ulture dependent zone, and as such,. would. comprise-a major issue u::.:::r County procedures. If the County is to act as a formal responsible ~-:::cy, we will require that agriculture be discussed as a land ·use isS".;e independent of economic evaluations, i.e., in terms of agricultural pr=duct, coastal dependence, soils, and other technical factors separate from an anticipated rationale that agriculture is not economically v::b1.e. 2. Sc.."-!~ols: Discussion on the basis of permanent design capacity of af'f'ected facilities and the ability of affected school districts to meet new-enrollments. We observe that this may be a sub-heading under ths included issue of Community Services. 3. Sswage and Solid Waste Disposal.: .. As in the above, these issues may ~sady exist as sub-headings under Comm.mity-Services. 4. Gro-,.-th Induction Due to the volume of projects reviewed by this office, please reference the EAD log #'s given above_ in future corr-...spondence relating to this project.· Respect!"'ully yours, . /~ /' ,;r.-@~ BRADFOR Environme BK'w:jr 68/6 STATE OF CALIFORNIA-RESOURCES AGENCY DEPARTMENT OF FISH AND GAME 3 50 Golden Shore LJng Beach, CA 90802 (213) 590-5ll3 July 24, 1980 Annette M. Sanchez Associate Project Manager Larry Seeman Associates, Inc. 500 Newport Center Drive, Suite 525 Newport Beach, CA 92660 Dear Ms. Sanchez: EDMUND G. BROWN JR,. Governor We have reviewed the Notice of Preparation for the proposed Rancho Carrillo Planned Community and we recommend that the following information be included in the Draft EIR: l. A description of the proposed development along with mapping, quanti-. fication and a list of aJJ, plants and animals found· within the project boundaries with emphasis on rare and endangered species. Animals that use the area for foraging, nesting, or refuge should also be included. 2. A discussion of direct and indirect impacts on the biological ·habitat and proposed mitigation measures to offset these impacts should be provided. All open space easements and/or dedicated open space should be fully described and shown on maps. We recommend that mature trees be left intact to provide nesting and roosting for avian species and that major rock outc:rpppmgs be left imdisturbed in order to provide sanctuary for terrestrial species. 3. A hydrology and drainage map of the site and discussion of possible impacts from increased surface runoff, soil erosion, .and sedimentation on nearby streams, watercourses, and. coastal wetl.ands shoul.d be incl.uded. To alleviate erosion we recommend that slopes over 30% be retained as permanent open space. 4. Alternatives to the proposed project, including "no project", operation on a lesser scale, etc., should be discussed along with the impacts of each alternative on the biota. Mitigation measures shoul.d be included in the discussion of alternatives. 5. The lengt:,h of natural watercourses proposed for· channelization into surface and subsurface drains should be addressed in the EIR. Also, the project sponsor should be advised that alteration of any streamb~d within the high water mark wilJ. require notification to the Department of Fish and Game pursuant to Section 1603 of the Fish and Game Code. This notification and the subsequent agreement must be completed prior to coiilmencement of the C 0 0 0 0 0 0 0 0 0 0 0 0 . 0 0 0 0 0 0 0 0 Annette Mo Sanchez 2 July 24, 1980 streambed alteration. It should be noted that this state law may require significant changes in project .features associated with streams or streambeds. For this reason we strongly urge compliance with this code section prior to .finalization of the specific project design. Thank you for the opportunity to review and comment on this projecto I! you have any cpestions, please contact Kris Lal or Jack L. Spruill of our Environ- mental Services staff at (213) 590-5137 o Sincerely, -.d;.,;..,_, ---;},<-6!,;;;t;,_;: a;::; ..btv Fred A. Wort.hley Jr • {" Regional Manager Region 5 1275 ELM AVENUE CARLSBAD, CALIFORNIA 92008 July 18, 1980 Citp of Carlsbab FIRE DEPARTMENT Larry Seeman Associates, Inc. 500 Newport Center Drive, Suite 525 Newport Beach, California 92660 Attention: Annette M. Sanchez Subject: Rancho Carrillo Planned Community TELEPHONE: (7141 ;z;lg 5931 - In response to your letter concerning the proposed Rancho Carrillo Planned Community and its impact on the Carlsbad Fire Department, points will be-expressed regarding the project impact. Specific questions will be answered that you included in your letter. Fire protection for that portion of the City would. be provided by two engine companies from two sub-stations. One station, with four men is located at Arenal Road and El Camino Real. The travel time to this proposed project exceeds the minimum desired response time of five minutes~ it is estimated that the first respondent would be 5/6 minutes to the southern portion and as high as 8 minutes when totally built. The estimated travel time from the Chestnut and Catalina Station is approximately nine minutes to the northern section. Considering the size of this project it is reasonable to project problems·related to fire protection. The amount of dwellings fore- cast for this community will increase the frequency of alarms. Fire related incidents will require a two station response and medical emergencies will ~equire a one station response plus a paramedic unit response. The reduction in manpower on this response leaves. large geographical areas of the City unprotected. If a greater alarm depletes the firefighting force it will require personnel recall and possibly a mutual aid assignment will be required. C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 LSA, Inc. -2-7-18-80 The fire department Master Plan shows a future proposed fire station in the area of Alga Road and, El Fuerte Streets. This development would fall into the minimmn 5 minutes response from this area. __ '!'~e ~~~ct o_f this development would require the construction of . this fire station and necessary equipment and manning to provide fire protection. • I hope that the information provided will assist you in the formu- lation of your report. If you have any further questions regarding this subject, p-lease contact me. i) Serra Cooperative Library System July.21, 1980 Anette M. Sanchez Associate Project Manager Larry Seeman Associates, Inc. 500 Newport Center Dr., Suite 525 Newport Beach, CA 92660 CARLSBAD CITY LIBRARY 1250 Elm Avenue Carlsbad, CA. 92008 • SUBJECT: ENVIRONMENTAL IMPACT REPORT FOR RANCHO CARRILLO PLANNED COMMUNITY, CITY OF CARLSBAD, COUNTY OF SAN DIEGO - REQUEST FOR COMMENT Dear Ms. Sanchez: In response to your letter dated July 8, 1980 we offer the following concerning libraries. At present, the City of Carlsbad has one library which is located in the northwest quadrant of the City. Outlying areas are served through the use of a mini-bookmobile (a Dodge maxi-van). The present library is only adequate at this point and with the current influx of new people to the area the overcrowding is compounded. Concerning the need for additional facilities, the Library Board of Trustees is focusing its efforts on the building of a new Central Library, which would be located somewhere near the geographical center of the City. The existing facility would then become a branch td serve the northern portion of Carlsbad. Attached is information taken directly from "Moving Ahead: Master Plan No. II for the Carlsbad City Library" by Raymond M. Holt, Library Consultant, August 1978. Sincerely yours, . blo~r~\,cu ~-C~ Georgina b. Cole Library Director GDC:ch Enclosure CARLSBAD CITY LIBRARY •CHULA VISTA PUBLIC LIBRARY ■CORONADO PUBLIC LIBRARY •ESCONDIDO PUBLIC LIBRARY NATIONAL CITY PUBLIC LIBRARY •OCEANSIDE PUBLIC LIBRARY ■SAN DIEGO COUNTY LIBRARY •SAN DIEGO PUBLIC LIBRARY 0 0 0 0 0 0 0 0 0 0 0 0 0 0 B. Site criteria and:Selection. Selecting a site on which to relocate the Central Lil:>rary is a matter of major interest and importance. Experience indicates that the loca~ion of a library facility has an eno.rmous impact on its usefulness to the community it serves. Therefore, criteria established by the experience of other libraries should be adopted. Fortunately, recent studies of successful library locations indicate .that certain time- tested factors are not·susceptible to change in the foreseeable future. In spite of the publicity given innovative means of conveying informa- tion such as video tape, computers for home use, etc., there is general agreement that tapping the eno.rmous and varied resources of libraries will remain necessary and desirable for most people and will. continue -38- \ ( to be done most effectively by visits to the library. Therefore, it remains imperative-that the site which will be most convenient for the greatest number of Carlsbad residents be selected. • l. Site Criteria. The assembling of criteria for site selection can be done by analyzing the literature on this subject.3 There is remarkable concurrence as to the most important factors in successful library location, applicable to both the Central Library and to branches. For convenience, these can be divided into three groups: (l) those which are essential, (2) those viewed as important, and (3) the remainder which are desirable. Using these divisions, site criteria should include those listed in Table III-6. Application of these criteria to Carlsbad leads one almost instinctively to consider sites in the vicinity of El Camino Real and Palanar Airport Road because of the nature of these major "highways and the projected distribution of population. Th~s same logic seems to have led to ·the conclusions reached in the 1973 Library Master. Plan and to·the recommendations of this location for a new c±vic .Center by SUA, Inc.: The City of Ca:zalsbad has many avai'Labt.e land pazocet.s ?,Jhich couZd be used for future government facilities and considera- tion should be given to as many of these areas as possibZe. Given the Zayout of the city, e:::i.sting roa~aya, popu.Zation distribution, zoning factors, and open-land avaiZabZe, Zand in the vicinit:y of "the Palomar Airport seems to be ideal, for 1,oca-tion of f'.1.tiaoe governmen-t facilities. 'l!he Pa'l,ornazo Airporz area is nea:za.the geographic center of the city and has direct aecess to the fl'ee?,)ay (via Pa'l,omal' Airport Road) as ?,JeZ,l as thoroughfares to e:r:isting and pZa:nited deve'l,opment. The land is currently zoned for can- mercia'l,, government, a:n.d special, treatment use. It is also in the· vicinity of the Ca:zalsba.d Muni~paZ Water Distric"t property (5 acres of Zand at Et. Camino ReaZ and .PaZanazo Airport; Road), and if the City d.oes acquire jUZoisdiction over this propert:y, it is feasible that ne?,J faciZities couZd be pZanned in conjunction un.th the acquil'ad Zand. 3 •see especially the following: Hoyt R. Galvin, "A Public Library Site Symposium," in Library Space Planning (L.J. SpeciaZ Report #1.) R.R. Bowker. 1976. Joseph L. Wheeler, The Effective Location of "Public Library Buildings. University of Illinois (Occasional Papers No. ,52, J~ly 19Sa.) 1958. Joseph L. Wheeler, A-Reconsidezoation of the Strategic Location for Publ;ic Lwra:ry Buildings. University of Illinois. (Occasional Papers No.-as, July 1967.) 1967. -39- 0 0 0 0 0 0 0 0 0 0 0 0 ! ( IQ 0 0 0 o( 0 0 0 0 II. Although it ma.y not be practical at this time to puzosue construction of aZZ new faci.Zities, serious consideration shou~d be given to acquiring the amount of Zand necesscusy fo~ eventw::ily reZocating the "Civic Center." A phased bui.Zdin,g proogram .can then be deveZoped which assures that Zong-te'I'trl goals cuse met at -the same time as ·short-teI'ffl czrises aroe solved. This kind of planning can minimize the number-of.moves necesscrry and save considerable "ad- minisi:1'ative-" costs. 4 _ • TABLE III-6 SITE CRITERIA ARRANGED BY :REIATIVE IMPORTANCE ESSENTIAL •.. A. Easily accessible to·the.maximum number of residents arriving by motor vehicle, public-_transportation,-etc. ' .. ' -. . . -~ B •. , Sufficient land for building, parking, a highly visible public entrance, and ·side or rear delivery~ - C. Adequate on-site parkin9'..- D. Space for incremental· expansion to me~t foreseeable future space requ~ements. IMPORTANT. A. . Adjacent to· commercial area so that library users may, if they wish; combine trips·to the library with necessary and conven- ience . shopping_. B. Easy and safe access to the.·site -for v~icular tra£fic including cars and.busses to facilitate drop-off and pick-up of library users -espec~ally children and old~ adul~-. c. High vis:i:bility so that the library is easily identifiable. III. DESIRABLE. A •. Reasonable distance from regional shopping-centers or other facilities which draw heavily from areas·beyond the City of carlsbad for their customers.·- B. Neighboring facilities should be ·of a canpatible nature in- cluding .commercial and professional buildings, cultural build- ings, and --perhaps other civic buildings. c~ Proximity to supplementary public·off~street parking which may be shared by the library, 1;hereby reducing the amount of land which the City must pur~hase for the library. -,. Do Access to the s-ite from more than one str~et -as may occur when the library is located at the intersection of .two major streets .. -.- 40sUA, Incorporated·. Op. Cit. p. 2-22-23. ( ( ( c . Sinc.e i.t must be conceded that El Camino Real will undoubtedly remain the most important local arterial for residents throughout carlsbad,· the search· for a library site must of necessity focus along this.highway. ·The lands adjacent to the intersection of Palom,ar Airport Road and El Camino Real are riot, of course, the 9nly canidates. As development·of the land on either side of El Camino Real continues; it will be important to reassess each poten- tial location. Basically, these·will probably occur at or near the intersection of major roads with El Camino Real. The proposed intersections shown .on .. the City's General Plan map are indicated on Figure III-5, beginning with Tamarack on the north and proceed- ing to Alga Road on the south_. The concentric rings at one mile intervals give some indication of the distance from the Palomar Airport Road and El Camin9 Real intersection. Generally speaking, it would seem desirable to locate the new Central Library build- ing somewhere within these parameters~ While.a location at an intersection is not an· imperative, it does provide a potential in most cases for better visibility and access.to the site'from more than one direction. Since these projected roads are not precisely aligned, it is not poss.ible to evaluate the nature of the topography immediately surrounding them where they intersect El.Camino Real. Conceiv- ably, an excellent site on the map may prove impossible in.real-- ity because the two roads, for instance, meet in very hilly terrain. Similarly, on-going commercial.and industrial develop- m~t of this area will alter both the availability and desirability of given parcels in due time. Since the library and its required parking and landscaping may require from three to five acres of land, depending upon whether or not·some parking might be shared with another facility, the amount of usable land at a given spot will certainly be a factor.- I£ a decision had to be made based.on the limited knowledge available today., it would seem that a site on ·the ·east side of El camino Real between Palomar Airport Road. and the proposed exten- ·sion of cannon Road would be the most logical. While keeping the iocation near the· gee-center_ of the ·City,· .such a site would provide the least overlap with the branch service areas proposed in the following chapter. Needless to say, a very thorough study of all factor~ will be necessary whenever the selection processes begin. Steps to be Taken in Implementing the New Central Library . Recommendation. Before a new Central Library building can become a reality, a number of steps must be taken. These are outlined below fer the guidance of those concerned with the orderly conduct cf this process. While circum- stances may affect the actual sequence, a~d mere than one of the steps 0 0 0 0 0 0 0 0 0 may be taken concurrently, each i tern -must be addressed if' a successful product is t9 ensue. 0 -41- 0 0 0 0 0 0 0 0 0( 0 FIGURE I.II-5 PROJECTED GENERAL ACCESS ROADS CROSSING EL CAMINO REAL , . • I . ~. t ~ ~"!J ,.i.l • _-_ . ,• -~ -~t • -• I • • :.:r. .• -:::::: ,,2~-----~---~~,... • "---....-- Q Existing Libr 0 Recommended Site for Branch Libr -42- . -... ·-,\ .... .. ~ -. -·-....... ·:_ '·· :i·, .... ,. ~CI L ITV NO. 01 07 08 09 10 IIA II 12 13 ,,. : •• '· .,,;,.: :i-i -.;~;,i •1:l \ff : .,_;.,;,\i:,i,_:~~rJ:,H i;i,~t;i :~-., ~j~~r~·<\'1·,1g,:tJr~~:1i\~l'11.i;i~t~~j~fi1~n!!1?1i1ii!ij1~){~1:i;:fr(:i1g'.:.,iJiii)ii~~-;;;.i;~i~iai'itfii#.~~Ma1ji1\'~!i~iir:Jiil/l ~,j~lt1ii1i~H ;:;, ;j,-;: e,:;:,I :;~ iii;_,;::,i,',,Jl ; -l~i: 1r:,;::1.w,:,i; \jl 1',, ':,I 'I ,' _ i ;, ; .,f LOCATION At Enclnlta1 Rd. Alga Rd. South of Alga Rd. Deleted luclcrnaga St. Abejorro St. la Costa Headows Al lsma St. La Coua Headows Alyo Rd; Abanto St, Alga Rd. Upstream of Fc1cl II ty 13 DRAINAGE AREA hg.ml.) 0.3 5,2 0.15 0.25 0.25 O.J !,LJtl'1,0•.l1 1 JI lll~lltd, l1.-h(1JJ1,.,t,•, 1-.•,·:r 11·~_ ..... ••f• . .'I.: 1H11•~••••th,0I~ lGlll I LA COSTA NllRTII ·1•111n•; e, 'I,-~!! .... ;:..~~?. LENGTH -1.f!.:l 100 4,800 360 450 740 I ,280 ~75 EXISTING COIID IT IONS Unknown 3 -7211 RCP. Golf Course with Low-Flo Ch. ~2" RCP 51,11 RCP 60" RCP 5'•" RCP i.211 llCP CAPAC ITV (cfs) ~ REQUIRED JOO* 2,560 ,.:.' 120 . 11()* 230 250* 260 260* 320 JW• IV-11!) ASSOCIATED PROBLEMS flooding of Golf Cour=,e Adequate Adequate ·Adequate • Adequate Adequate -------.-•--~---··..,. . . . . . . ~ .. (!) (!) RHOl:\t1ENDEb1 I MPROVE11EIITS :··. ·: N(?n:e_ Need~d . ,: ,,•.' I, '•·, •,,' ! : ;:: : ··: '. ... _ .'. ::, ' / .: tlone N~ed~d ll~nc llccdcll 1 l)lf1L [t, I . CO~T PRIO"ITY (DOLLARS) ll11S Ill ZOti[ 8,00Q A '.~C:'_\\,: ,. • ·NIA , N/A 11/A fP-J FP-3 i,:•· .. : :· .. ,, ..... :· . •~:; 0 0 0 0 0 0 0 0 !Q I 0 COUNTY OF SAN DIEGO Department of Sanitation & Flood Control <oaso> C. J. H0US0N Dlrectar County Operltlllfll Cant•, 5555 Overland Av.nue, San Dle10, C.allfarnl.a 92123 ..... Tele!lllllfl■: 565-5325 JUL 2 2 1980 Larry Seeman Associates, Inc. 500 Newport Center Drive, Suite 525 Newport Beach, CA 92660 Subject: Rancho Carillo EIR REF: We have your request for comment on flood control matters related to the planned community in the City of Carlsbad. 3124 Since the project is still in its initial stages,, we cannot make specific comments on all your questions. The project does lie in the San Marcos Creek drainage basin and is outside of any designated flood plain area. Enclosed are excerpts from our Comprehensive Plan for Flood Control and Drainage Zone I which should provide valuable input to your environmental analysis. If you need more information, you may call Art Scotese on 565-5849. C. J. HOUSON sy· l .. / .. --1. i ... _ ~-.:f 5..'----. l .,i-J·_ I : JOSEPH C. HILL , Principal Civil Engineer AGS:lm Enclosures: @) San Diego Gas & EJec-tric City of Ca:rlsb.::.d 1200 Elm Avenue Carlsbad, CA 92008 March 21, 1980 Attention: Joyce Crosthwarte/ Planning Department Subject: Rancho Carrillo Master Plan E.I.R. Gentlemen: ••lE •.o PLA 10 0 Thank you for providing San Diego Gas & Electric Compan7 with the opportunity to provide input to this drait E.I.R. Gas and el~ctric distribution facilities can be made available to t.~is project according to SDG&E's rules filed with and approveq by the California Public Utilities Commission. The continued availability of both gas and electric energy !or this and future projects is dependent on the supply of fue: and other essential materials, and the obtaining of governmsnt authorization to construct the facilities required. I have enclosed recent copies of releases concerning this subject for your information. Should you need to discuss the above material in more detail, please call me at (714) 232-4252, extension 1887. WMS:cag Enclosure (2) Sincerely, Walt M. Smith Land Planner CiT'( G;: ; ~.:.;;:,,ii}g (~; ·\::.:~~~---' ... , S ~ ;;.:..;-~~1"!-2t, i. C C C C C C C 0 0 0 0 .. I • ' .. -. • I ' ' ... . . I -· j -·-. J 0 --l .. --- en . \ · .. i I 0 I' I • •. U) 0 ... . ··••·• . 0 0 .. 1 ; • · ...... -~ •. r•• .. :· • • ,._., -• .o 0 0 •. 1 I I I I I I I I ' I 0 Larry Seeman Associates, Inc. 500 Newport Center Drive Suite 525 Newport Beach, CA. 92660 Attention: Edward Almanza January 12, 1981 Subject: Rancho Carrillo Planned Community Gentlemen: PLA 520 Thank you for your tentative information regarding the above-mentioned project. In response to your questions on Page Two, the location of electric facilities are as shown on the map sent to you by Judy Isais. These are 12 KV and_ 69 KV lines. We have_a 3" gas line at Palomar Airport Road at Linda Vista and a 3" and 4" gas line in Rancho Santa Fe Road. The required extensions to serve this proposed development is the responsibility of the developer. If you wish to continue with this development, please contact me and I will send you our requirements of plans needed to design a distribution system. An early response will not only be beneficial to us, but to you, as the day that we have sufficient plans to process your project for design will constitute the Applicants Final Submittal date (AFS). This date will determine the E~tension:Rule in which your project is interpreted. Also please be advised that the preliminary design for the gas and electric system takes approximately four to seven weeks to complete. The sooner the above plans and information are submitted to us, the sooner your project can be completed. (If overhead relocation of SDG&E poles is required or conversion from overhead poles to an underground system is required, more time will be needed to complete your electrical design.) A meeting may be beneficial as it could possib_ly avoid any misunderstandings before they develop on the project. If I may be of further assistance to you, or for arranging a meeting time, please feel free to call me at our North Coast office. lcf • S • erelY. , ~ (}d/.-(✓99~1--1tJ_) i A. Higgins Customer Extension Planner Phone: 438-3160 C C C 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Larry Seeman Associates 500 Newport Center Drive Suite 525 Newport Beach, CA 92660 July 23, 1980 RE: RANCHO CARRILLO, PALOMAR AIRPORT ROAD E/0 EL CAMINO REAL Attn:· Ms. Annette M. Sanchez I am responding to your letter dated July 8, 1980, requesting information pertaining to the environmental impact as a result of serving this development with natural gas. Presently San Diego Gas and Electric Company has a 16 inch (800 PSI) Gas Transmission Main located 13 feet north of. the existing center line of Palomar Airport Road. Due to· the operating pressure of. this gas line it is not normally used to serve Local Distribution. This project would have possibly two points of service for natural gas. The first would be to extend a gas line from Linda Vista Drive, (Poinsettia Ave.), the nearest Local Distribution Line. The second option wouid be to tap the 16 inch gas line and install a gas pressure regulator station. The decision would be made by San Diego Gas & Electric Company. It:should be noted that either option would be at the expense of the develop-er. --------- I do not anticipate any problems environmentally or ecologically with the necessary requirements to serve this development with natural gas. Please be aware that due to the importance of this gas line and the poten- tial hazards if this line was punctured San Diego Gas and Electric Company does not allow any work to be.done within 25 feet of this gas line without standby personnel present at time of work. For· standby service please con- tact (714) 235-6323 48 hours in advance of work to be done. I hope this information will be of help to you. If I can be of further assistance ,please do .not hesitate to call.me. RWK:ecs Enclosures Sincerely, Robert W. Keithly . Field Engineering Services (714) 232-4252 Ext. 1653 C .,t-~~\ AIR POLLUTION CONTROL DISTRICT ,:· :. \\; l1 ··. t'-. lt-J;!~~~+-:. =-,".~;; ··•:f:f!iftl COUNTY OF SAN DIEGO c R. J. Sommerville WILLl.0.1\,1 SIMMONS 9150 ChesapeaK!l ::rive Air Pollution Control Officer July 22, 1980 Annette M. Sanchez Larry Seeman Associates, Inc. 500 Newport Center Drive, Suite 525 Newport Beach, CA 92660 San Diego,C.i,,f.92123 17141 565-5901 ':VlS 0176i SUBJECT: REQUEST FOR COMMENT ON THE PREPARATION OF A DRAFT ENVIRONMENTAL , IMPACT REPORT (EIR) FOR RANCHO CARRILLO PLANNED COMMUNITY CITY OF CARLSBAD The Air Pollution Con~rol District (APCD) has reviewed the above referenced subject material and has the following comment: C C C The draft EIR should address project consistency ·with the Comprehensive Planning C Organization's. (CPO) adopted Series IV-B population proj.ections since·the Air • Quality Management Plan.(AQMP) and the State Implementation Plan (SIP) for the region are both based in part.on Series IV-B popultaion forecasts. Additionally, Section 1~142(b) of the adopted amendments to the State EIR guidelines, states: (b) The EIR shall discuss any inconsistencies between the proposed project and applicable general plans and regional plans. Such regional plans include, but are not limited to, the applicable Air Quality Manage-. ment Plan (or. State Implementation Plan once adopted), area-wide waste treatment and water quality plans, regional transportation plans, and regional land use plans for the protection of the coastal zone, ... ; We have evaluated the two 4 square kilometer grids in which this project site is located to determine the Comprehensive Planning Organization's (CPO) Series IV-B population projections for thisarea and have found that the proposed project, which emcompasses 43% of the grid survey area, represents a 150% increase over the 1985 popul~tion projections (assuming a 1985 completion date) anticipated in the Series IVB estimates (for the entire grid areas) which are contained in the locally adopted Air and Water Quality Plans mandated by the Federal Clean Air and Water Quality Acts. The projects unanticipated population increase will add air pollutants to the atmosphere that may interfere with the attainment and main- tenance of the National Ambient Air Quality Standards (NAAQS). The draft EIR should inform the decision-makers and the public that the p.roject is inconsistent with the adopted revised -Regional Air Quality Strategies (R-RAQS) to attain and maintain the National Ambient Air Quality Standards as prescribed in the Clean Air Act. Failure to make reasonable further progress toward attaining the standards may (1) cause sanctions to be imposed, thereby jeopardizing state 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 .0 Annette M. Sanchez Larry Seeman Associates, Inc. July 22, 1980 -2- and federal funding for sewers and highways in the region, and (2) place prohibition on major new source construction. The Air Quality Management Plan (AQMP) and the State Implementation Plan (SIP) for the region are both based on population estimates, the Series IV-8 forecasts. Since the San Diego Air Basin has been designated a non-attainment area for ozone, carbon monoxide, particulates and oxides of nitrogen and the project appears inconsistent with the Revised Regional Air Quality Strategies (R-RAQS), air quality must be considered a significant issue. If this project is approved, then legally enforceable mitigation measures must be provided and implemented to offset any additional pollutants. Additionally, air pollution impacts associated with the commercial and industrial uses.proposed to occur on the project site should be quantified and discussed in the EIR. Enclosed is a copy of our letter which describes the information required in the air quality Section of an EIR. If you have any questions, please call me at 565-3609. • ~b~~ JUL!gM~-;;NN Environmental Management Specialist JMQ:RU~:mk cc: Carolyn Stromberg, ARB Richard Huff, CPO John Wise, EPA Enclosures --------------------------------------------- 0 0 0. 0 County of San Diego Air Pollution Control District 9150 Chesapeake Drive San Diego, CA 92123 SAN biEGO' S AIR POLLUT!ON: 1979 SCORECARD 12/31/79 FOR IMMEDIATE RELE.~SE - Air qua·lity in San Diego County improved during 1979 compared with 1976, according to· County Air Pollution Control Officer R.J. Sommervilie. The San Diego Air•Basin exceeded. the federal standard fer clean air, 12 parts per hundri:d million (pphm) of ozone, on 67 days jn ·1979, compared with 88 days jn 1976. Alpine recorded the biggest improvement? e."<ceeding the standard only 44 days this year,· compared with 65 in 197G. --Readings at most qf the Air P<>l lutic:>l',1 Contro-1 District• s. seven other monitoring 0 stations_ were similar ~o .last· yeaz:'s or slightly iower. Escondido exceeded the standard on 13 days this year, compared with 15 in 1978; downtown San Diego recorded 5 violations, compared with 8 last year. Kearny Mesa had 6 exceed- O ances in·l979 and 9 in 1978, while Solana Beach experience~ 16 days over the standard this year and 17 last year. Chula Vista ,had 6 violati_ons in 19i9. and 7 in 1976. Stations showing a slight i~crease -in number of days over o the standard included El Cajon, with one !ff0re day this year (7 as opposed to 6 i~ 1978) and Oceanside with 2 more (~2 ccmpared ·with 20) .. - 0 0 o· 0 While the overall pi~ture improved significantly, Sonmerville said the number of days .on which smog alerts we?"e issued remaine<l the same (11 in 1979 and 1973). Smog alerts, issued when photochemical smog {ozone) reaches 20 pphm or higher, usually occur when meteorological conditions transpor~ pol.lutants in~o San Diego County from the Los Angeles area. This happens only occasionally during the year but when it does, North County coastal ccr.munities genera11y are affected most severely. • {MORE) Air-· ocl1ution levels in an area of re1ative':y constant-;-aay.:..to-day emissions, • '"• I • ar-: determined primarily by existin~ mateor-_:logical. conditions. Clear skies, ,· . ' ' . above-nonnal daytime temperatures and the ani1abi_ljty of sunshine are condi-.. . • ' tions favorable for the tracoina of emissions near ariJund level.and the. • ' ·., • • -_,. w. \. • formation of ozone through photochemi_cal l""Sactions Jn the atmosphere. Nine- taen-se•ienty nine was an above-a'lerage _ year for both. temperature and sunshine.· . ' The ii.Ost unusual months were June and Septerr:::er. Both months had subst:mtiaily _ . ' .... above-average temperatures, ,..,; th September 1979 being the warmest September si nee i87l (when temperature' reco·rding •11as ·"ini tiatsdj and 'the sunniest since 1960. Correspondingly, ·June· and September were the rr.onths of highest c·zcne levels· in San Diego County and also: accounted for near1y half of all days in 1979 ,,,hen the federal ozone. standard was exceeded. J,n :he Les ;.nl]:1esarea, the uni:que·:r.eteoro1cgy of 1979 ·resulted in the worst Sil:Og siege in 2-5 years. The so·uth Coast Air Basin, which ·;ncll!des Los Ange1es, Orange, Ri versi.de, and San Bernardi no Coun~'f :S, exper, e!?Ced fl Stage II smog a 1 erts ( 35 pphm of ozone O'I'"' great-er) in one :hi rt1:en-day period• in September. -• San Diego County expe_rienced an unpl'"ec~dented 3 Stage II alerts,. one. i.n Ju.ne (only the second in ts!'l years} and t\oJO in Sept,:mber. An i.nitial survey of other pol1utant 1sveis indi<;:ates tf:tat the ~urnt:er. of days over the carbon monoxide 8-hour standard wa,s siightly higher than in 19.78, and. the number'of violations of the ni"troi;an di~xice standard was l_ow~r. Scn,mervi1ie stressed that ail figures are orelim"!n2r"1 and suoject to ·veri_fic.1tion. r.. cafii~ . C C C C C 0 0 0 0 plete report for 1979 wi11 be issued by the !.ir Pollution Control Dist-rict 1",ne:1 -o all data is anaiyzed. 0 p p ·1979 OZONE ALERTS ( ;:· 2□ ;:chm} SAN DIEGO COUNTY 0 o.o..r:: • LOCATION LEVEL (cchm} p May 12 Oc2anside 22 ~-~ay 12 · Solana Beach 22 May 13 Solana Beach 28 0 ~une 9 Oceanside 21 June 10 Oc2ansic:e 26 Solana Beach 21 0 June 11 Oceansida 36 So1ana Beach 22 Escondido 32 Chula Vista 21 June 12 Escondido 22 0 June 13 Escondido 20 . September a Esccndi do 23 !o September 15 Oceanside 35 Soiana Beach 32 September 17 Oceanside 36 Solana Be:c:i 21 0 September 22 Oceanside 21 0 0 -:30- -• . . ' El Cajon Chula Vista Escondido Oowntc·Nn . San Diego Oceanside Kearny Mesa A1pine Solana Beach Basin 1979 PHOTOCHEMICAL SMOG (OZONE) -DAYS OVER CLEAN AIR STANDARD (12 pphm} SAN DIEGO COUNTY AIR POLLUTION CONTROL OISiRICT Maximum 1-Hour in Parts Davs Per Hundr~d ~1i 11 ion i979 / 19i8 1979 1978 7 6 17 18 6 7 . 22 20 13 15 32 i8 5 a 19 21 22 20 36 35 6 9 17 18 44 65 19 24 16 17 32 39 67 88 (MORE) C C Date of Maximum 1979 C June 11, 1979 June 12, 1979 June 11, 1979 C June 11, 1979 June 11, 1979 Sept. 22 '· 1979 C Sept. 9, 197~ Sept. 15, 1979 C 0 0 0 0 p p p 0 0 0 0 lo ,0 [ AIR POLLUTION CONTROL DISTRICT COUNTY OF SAN DIEGO R. •J. Sommerville Air Pollution Control Officer July 21, 1980 Annette M. Sanchez LarT)" Seeman Associates, Inc. 500 Newport Center Drive, Suite 525 Newport Beach, CA 92660 -9150 Chesa;::eake Om,e San Diego, Calif. 92123 .(714) 565-5901 IMS 01761 In response to your request for information required_in __ the air quality section of an Environmental Impact Report, the District is currently preparing a-short document listing.items we would:expect to be· included in the report. However, this document is not available at the present time. In the interim, the comments below will suffice. • The air quality section should include maps, tables and/or discussions of the project in terms of the following topics: 1. Project location 2. Topography of project area 3. Meteorology .4. Present zoning and land use· S. Existing air quality 6. Project impact 7. Mitigating measures 8 .. Revised Regional Air Quality Strategy 9. Regional Growth Management 1. PROJECT LOCATION -The project should be located on a topographical map showing the project's exact boundaries. The. project should also. be located on a regional map to locate the project-in the San Diego Air Basin. 2. TOPOGRAPHY OF PROJECT AREA -In many cases, the transport and diffusion of air pollutants is complicated by terrain features.· Therefore, a narrative description of the specific local topographical features of the project site should be included in _the report (e.g., inland coastal valleys, foothills, mountainous areas, river canyons, etc.).· 3. METEOROLOGY -Meteorological conditions can cause extreme variations in air quality on a daily, seasonal and year-to-year basis. The two main meteorological parameters are winds and mixing heights. -2- m.xing height refers to the mo.ximum height at which pol lutcJ.nts may dilute. The meteorologist estirncJ.tes t::is figure on the basis of expec- ted m:i.xirnum tempercJ.ture and the early :::.orni.ng temperature profile. A low mixing height without strong bree:es suggest elevated pollution levels. 4. PRESE:;T ZO~IXG AND LAND USE -The exis-cing zoning and land use should be discussed in layperson's terms (e.g., the existing zoning allows for ''x" number of dwelling units per acre; the land use is designated on the community plan as agricultural preserve). If the proposed pro- ject requires rezoning or a change in -:he community plan, then this should be so stated. S. EXISTIXG AIR QUALITY -A three to five-year summary of available and current ambient air quali.ty data which encompasses the project impact area is required to demonstrate the present severity of the air pollu- tion problem. A table illustrating the number of days standards were exceeded for each year and the annual high one-hour concentrations at appropriate air monitoring stations in or near the project area should be presented. At a minimum, photochemical oxidants, carbon monoxide, nitrogen dioxide, sulfur dioxide and particulate matter neecj to be included. 6. PROJECT I~IPACT -Air quality impacts should be discus~ed in quantita~ tive terns as much as possible. The a:1alysis should include both mobile and stationary sources. The emissions nssociated with vehicle traffic should be discussed and presented in tabulal" form. The discussion should include an estimate of the nui:lber of vehicle trips and vehicle miles traveled.· The method- ology used to estimate the emissions should be included in the report itself, or as an addendum. Emissions from stationary sources should be addressed as well as an analysis of the pollution associated with the increased generation of electrical po,-.er. If' future residents or existing ho::1es, parks or employ- ees will be ir.ipacted from pollutants up-wind of thi;? project location, then this ::.hould be stated, including· a discussion of the type of pollution impact and possible adverse effects on public heal th and property. 7. ?4ITIGATI:-;G ?-'EASURES -Titis discussion should identify those mitigatin~ measures.which are p'I"oposed by project p-:-oponents to be included in the project and other measures that are no~ included, but could reasonably be expected to reduce adverse impacts. Mitigating r.ieasures should include the relevant Regional Air Quality Strnter,ies (RAQS) tactics which inclute, but are not limited to: . T -1 (:•k•di fied) P\·oposcd process fer .coo·rdinnted land use and trnns- pQrta.t1 on actions to i:'.'.!?rove ah.· .quality. "This proposed pl~cess envisions modifications to hoth general plans and t'he regional comprehensive plan C C C C C 0 0 0 0 ,0 10 -0 0 0 0 0 0 8. 0 0 T -2 T -7 -3- so as to achieve consistency of purpose 3nd achieve air quality benefits. Compatibility among plans and policies would be bro-:.ii:.t about by a cooperative effort between local agencies and the Comprehensive Planning Organization (CPO), \i:lerein incompatibilities ad•1erscly affecting· air qualit:i,· are jointly identified> appropri- ate changes determined, and then these changes proposed to local ageJ1,cies or CPO as appropriate." Maximum carpool and van-pools with incentives. The most essential incentive to carpooling is a computer matching·program to identify potential carpools groupings .and to promote the formation of carpools by assisting with matching, routing and scheduling. Industries and business.can provide another incentive for cnrpooling by designating preferential parking areas for carpool cars. These spaces could be closer to the destination building or in a covered area protected from the. weather, or in another desirable location.. Vanpools -This tactic is initiated by the employer who purchases a van which is driven by an employee.-The employee drives a group of employees to and from work. Operating expenses of the vanpools may be paid by either the employer ·or employee. A subscription transit program entails the charter of buses by employers from public or private transit opera- tors to provide employees -with subscription buspool. service. Subscribers are ensured that they will have a space on the bus. In addition, the employer sometimes guarantees a minimum nu~ber of passengers or subsidizes a portion· of the subs.cri?tion fare. Buspools are com-· parable to ca-rpools in that the same individuals may ride together each day and the same adv.antages accrue to the employer and employee. Maximum bicycle syste:n. 'This tactic envisions a oajor expansion of bicycle facil- ities, including: the adopted regional bicycle route system, community oriented routes> bicycle feeder system to public transit, possible employer incentives and includes facilities. Such facili tics include theft resistant racks, connections with express bus service, showers and locker roo:.1.s. REVISED REGIO~AL AIR QUALITI STRATEGY -A coordination process to include air quality considerations in land use and tr.i.nsportntion planning is included in both the Regional Air Quality Strategies (RAQS) and the Air Management Process (A~IP) . The A!-:? stipulates: ) . -4- "The cities in San Diego County, the County of San Diego, the Comprehensive planning Organization (CPO), the Unified Port District, and other appropriate agencies will include air quality considerations in all land u~e and ,transportation actions subject to the California Environmental Quality Act of 1970 (CEQA) by addressing consistency with the RAQS as part of required Environ- mental Impact Reports." The relevant RAQS tactics are addressed under mitigating measures. The required information need not necessarily be included within the Air Quality Section of an EIR or EIS, but must be appropriately referenced in the Air Quality section if discussed elsewhere in the document. If you have any questions, please contact me at 565-3609. =~!~ Environmental Management Specialist JMQ:RLW:mk C C C C C 0 0 0 0 0 0 o, __ _ .,.-0 ( .,9/C~ /f/~&'": 6: ,,-,:-:: / .:S .s / p /.,/ ;:-,,9c,,,· ~..,<?-rP .,,o _:- /:/ /7'?c:o G,.-= ,,,,u_ ----... - ------------ ,$,9.S.:: /?/'/..0 .,,O~!'Jv cC:r/o,u ✓/c/2'/?.;!;; /1/7>--, ; 96;···· -·-/7&°~·--r ✓-1::::.0 /9.9S /7.7,6 I .. .?. :!..-;[ __ . •··-.. ·•···•· .. 1. ----- ~S-38 •• 1 ~7 . . ·-. . .. ·-... ~ -. -----------j----· ·--····---J---•-·-------·---·--·· ·-· --• O· . c,{,7' .. 9p57 0 I ~ ··-····------ ------·as=-· ;.;;~.rr ----1--·· · -· · · · · · · ·--·----i------.. --• ·----------• ---·-(p~~v:;)----:. -~: ?_?:_ ___ ... !~:.f!_ ____ ---~·<_?______ ..... :-!' /:!~ ... ·--~•-t:'-?_... -:2.· C 0 0 ---· ··•·------... . .. ------· --------- ( ~~ ./..,".:'•-::::;;-.:'✓-' ) . . --·-. • ---·-·-• • • .,.-::-1/ , / _} ._., . . . . . •• . . . . . . . .. . . . .. -.. -. . l __ ::_ . --. . . . . ·-.. .. --. . t-·---. . I i ~--.. !· - . ---. ! ........ -··. ···-. I _______ _ ___ L~ • . .... L __ _ I f •: PROJECT NAME CONSULT Pu 'IT !\'ORK SHEET ~ FOR. ESTIMATING HYDROCARBONS, CAPJ30N MONOXIDE A~D NITROGEN OXIDE E!-!ISSIONS ( . Vehicle Population Mix; Average Speed -35 MPl:l) DATE ---:------------,------- NID-lBER OF VEHICLE TRIPS PER DAY ----------- AVERAGE ~!ILES PER TRIP Day Hydrocarbon Emissions Carbon Monoxide Emissions = --------------- Vehicle Trips x _____ Miles = Trips -----Miles/Day ....... ---'c,.~n-~rr ....... )_x 365 Days x Day Year Gram ·X 1. 1023 x 10-6 Tons Mile Gram + (Trips) x 365 Days x Grams 1.1023 x 10-6 Tons. D Y --T~r~1.~p--x Gr~ ay . ear = Tons + Tons Year (V?-lT related) Year (Trip related) -Tons/Year ----- = (Vl-IT) x 365 Days x Grams x 1.1023 X 10-6 Tons Day Year Mile Gram + (TriEs) ·x 365 Days X Grams 1.1023 X 10-6 Tons· Day Year Trip X Gra.-n. Tons = ...,..._...,.,_,,,_~---:-.-Year (~-rr related) +· Tons Year (Trip related) = Tons/Year -----~----------------------------------------------- Nitrogen Oxide Emissions • (V?-IT) x 365 Days x Gra.::s X 1.1023 X 10-6 Tons = Da)' Year Mile Grar.i + (Trips) X 365 Days Grams 1.1023 X 10-6 Day Year X Trip :;c Gram Tons = ,,.,..----,.,,-::-:=::----=---:-~ Year (V:•IT related) + Tons Year (Trip ~elated) = Tons/Yc~r ----- Tons C C C C I..., 0 0 0 0 0 0 0 0 0 0 0 .o 0 0 0 ' roa ESTil·lATING P~-~ICu1:..~ES {TSP) , SOU"L'3. DIOXIDE: (S02 ), C.~~l H~;QXID:! (CO) AND NIT!CG.Ei.'t OXIDE (NO ) Et·lISSIC~?S X ProJECl' NA!•1E DATE --------------------------- FIRM ---------------------- NtDlBER OF D;·lELI,ING Wl'XS (DU) •• -• Ntr.-1SER OF THER-IS PER DU PER ~-1~l'!'H-. . . ... ·• ..... --------- • • • • • • s • • • • --------- TSP 502 co * . . . . •• . . . . . . . . . . . . . . ---~----- 10 lb~ l ft3 H.G. 12 l•;onths 1 ton 106 ft3 X 1050 BT"'u X 100,000 B'IU THE~l X Year x 2000 lbsx ( ) THER-IS/Mont:h = Tons/year -----· ------ 0.6 lbs* 106 ft3 1 ft3 • 100,000 B'I'J -12 ·Months l ton· x ioso STU x THEEt·l x Year x 2000 'lbsx ( _____ ). THER:-IS/Month = ____ Tons/year 20 lb~ 106 ft3 1 ft3 N.G. x 100,oop BTU x 12 Months 1 ton x l050 ·BTU THER-1 Year Xzooo lbs x ( ) THER-1S/Honth = Tons/year -----· ---- 100 lbs-Ir 1 ft3 100,000 BTU 12 t•tonths 1 ton 106 ft3 x 1050 BT"u x 'l"'rlER>i x Year x 2000 lbsx (. • ) T".dER·?S/t-bnth = Tons/year ·--------- T'nese. anission factors were obtained fran 5:JP?lement 7 of the U.S. Erw·iror .. 'T.enta:.. Protection Agency's Comoilation of Air Polluta.11t Emission Factors, AP-42~ .. .. • ~\OR.CC SHEE:'L' *6 ( ?:-;•~-=?. PLANT) EOR ESTitr!ATI!\G Pil.RrI.:t-:;,TES (TSP} , SULFUR DIOXIDE:· (S02), C.~=2C)l t-10:,0XIDE (CO) A.'ID NITFCGEN OXIDE (::o ) E.MISSICC-S X P~CI' N.,?o.HE DATE --------------------------- FiroI ----------------------- NID1BER OF CWEI,LI~~ UNITS (DO) . . . . . . . . . . . . . •. ----------- KII.a•i'ATT HCORS (~m) PER DO PER :-lONm • . . . . . . 'lOTAL KViS/MO~"I'H • • . . . . . . . . . . . . . . . .. . 'I'Sl? S02 co 10 lbs* 1000 gal. *** 1 gal. 3 BI'O X 1501 000 BT"u X 0.00029 1:·:H 12 rronth 1 ton x Year x 2000 lbs x (. _____ ) l\'WH/Month = ____ lbs/year- 157 lbs* *** ** 3 cal. l BTU 12 month 1000 gal. X (S) .0034 X 150,000 E?J X 0.00029 K~-3 X Year (' ) KWH/Honth X 1 ton 2000 lbs = Tons/year -*** 5 lbs* 1 9al. 3 B'I'"J -12 ronth. 1 ton 1000 gal. X 150 ,·000 BID X 0.00029 K;•;:~ X Yeai::: x 2000 lbs.x (. ______ ) KWH/!ibnth = _____ -Tons/year 35. 7 lb~. 1000 gal. x 1 gal. x 150,000 °BTU *** 3 BT"t..J ..,,_...,,..,,..,,..,....,,_.... __ X 0. 0JQ23 I\1·i!'f (. ______ ) IwiH/Month = _____ Tons/year 12 rr.-onth l ton Year x 2000 lbsx C C C C C X 0 0 0 * T'nese e:nission factors were obtained fran S~??lertent 7 of the U.S. • ~wiron.1.1ental O Protection Agency's Corr.pilation of Air Poll~~ait Emission Factors, AP-42. ** .0034 is the decimal equivalent. of (S) the ~~r~entc:;e, by weight, of sulfur in the oil. *** ·1· ,:-• . • . . This factor is used as an average of bo1 er e~:1c1enc1es at tne various 0 S.D.G.&E. p:,wer station. 0 0 0 \IDRK SHEET ~7 (RESIDE~;•.cr.;u, FIREPL.'Z\.CE:) EOR ESTI!·lATit-:G PA..tn'ICUCATES (TSP)', O\FBON t-tOi.~OXIDE: (CO}, Hrn:D:APBO~S {EC) A.~10 NITFCGEN OXIDE (NO ) EMISSIQ.'lS X PFDJECT NM·lE DATE --------------------------- CONSULT;io~n FIRM ----------------------- :t-."'t.JMBER OP DWELLTh"'G UNITS {DO} WIT"rl A E'IREE>rACE . . . . •. --------- 0 TSP 0 0 0 0 0 0 CD ... - NO X * 20 lbsk 'Ibn X 1.98 Tons** Cord .s Cords 1 ton ( ) DU X: DU, Year x 2000 lbs x ·------· = ______ Tons/year 120 lbs* 'lbn X 1.98 'Ibns**' x .5 Cords l ton ( ) DU Cord DU, Year x 2000 lbs x ·-------· = 'lbns/year ------ 1.98 Tons** ·s lbs* . Ton X Cord .5 Cords l ton ( ) DU x DU, Year x 2000 lbs x ·------· = Tons/year ------ l lbs-': X 'lbn 1.98 Tons** .s Cords 1 ton ( ) DU Cord X DO, Year .x 2000 lbs X ------· = 'Ibns/year ------ 'Ihese enission factors were obtained fran Supplement 7 of the U.S. Erwiron."1\ental Protection Agenc-.f' s Cocrpilation of Air l?olluta"'lt Emission Factors, F-.P-42. ** l'i.sstrnes red oai~ with a 12 percent moisture con::ent, refer to Table 2-