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HomeMy WebLinkAboutCT 93-04; CARRILLO RANCH VILLAGES L, M, N, Q, R, T; PRELIMINARY SITE ASSESSMENT; 1989-08-23I I I I I I I I I I I I I I I I I I I PRELIMINARY SITE ASSESSMENT FOR CARRILLO RANCH CARLSBAD, CALIFORNIA FOR PACIFIC SCENE SAN DIEGO, CALIFORNIA PREPARED BY GEOCON ENVIRONMENTAL CONSULTANTS INCORPORATED SAN DIEGO, CALIFORNIA AUGUST 1989 I I I I I I. I I I I I I I I I. I I I I TABLE OF CONTENTS PRELIMINARY SITE ASSESSMENT SECTION I -PRELIMINARY SITE ASSESSMENT INTRODUCTION Purpose SCOPE OF SERVICES Task I -Preliminary Research EXISTING SITE AND GEOLOGIC CONDITIONS Site Location Existing Conditions and Improvements Proposed Improvements .... Review of Geotechnical Reports Santiago Peak Volcanics Delmar Foundation Torrey Sandstone Groundwater Review of Regional Water Quality Control Basin Plan SITE RECONNAISSANCE Onsite Survey Offsite Survey SITE HISTORY -RECORDS REVIEW Review of Aerial Photographs Review of Topographic Maps . RESULTS OF CONTACTS WITH REGULATORY AND GOVERNMENTAL AGENCIES Hazardous Materials Management Divl'sion HE48 Listing HE17 Listing ..... . HE23 Listing ..... . Unauthorized Release Listing Regional Water Quality Control Board Listings Waste Discharge Facilities Listing .... San Diego Air Pollution Control District (APCD) Violator File Register .................... . City of Carlsbad Fire Department ........... . San Diego Department of Agriculture Weights and Measures - Pesticide Use Enforcement Division .... . US Environmental Protection Agency .. . California Department of Health Services (DRS) Page 1 1 1 2 2 4 4 4 5 6 6 7 7 7 8 8 8 10 11 11 14 15 16 16 17 18 18 18 18 19 19 20 21 22 I I I I I I' I I I I I I I I I I I I I TABLE OF CONTENTS (Continued) PRELIMINARY SITE ASSESSMENT SECTION II -LIMITED SOIL SAMPLING INTRODUCTION AND PURPOSE Scope of Services Field Activities . Sample Location Laboratory Testing Discussion of Test Results SUMMARY OF FINDINGS ..... . CONCLUSIONS AND RECOMMENDATIONS PRELiMINARY SITE ASSESSMENT LIMITATIONS Figure 1, Vicinity Map Figure 2, Site Plan Figure 3, USGS Topographic Map Table I, Summary of Analytical Laboratory Results Appendix A Agency Information Sources Appendix B HE48 Listing Appendix C Laboratory Data Page 23 23 23 24 24 25 26 28 30 31 I I I I I I I ,. I I I I I I I I I I I File No. D-8053-601 August 23, 1989 SECTION I -PRELIMINARY SITE ASSESSMENT INTRODUCTION This section presents the results of Task I, the preliminary site assessment (PSA), for the subject property. The property is located south of Palomar Airport Road and north of Alga Road in Carlsbad, California. The location of the site is depicted on the Vicinity Map, Figure 1. Purpose · The purpose of the preliminary site assessment is to estimate the potential for the site to have been impacted by releases of hazardous materials. The services performed for the preliminary site assessment included a review of available records (as outlined in the following scope of services) for historical and current sources of hazardous materials and numerous site visits to attempt to identify areas or facilities/structures on the site and in the vicinity of the site that possess the potential for the presence of hazardous materials. In addition, limited soil sampling was conducted to assess the potential for the presence of detectable concentrations of organochlorine pesticides, organophosphorus pesticides, .and chlorinated herbicides onsite. The guidelines used for the definition of hazardous materials were obtained from the California Code of Regulations, Title 22, Division 4, Chapter 30, Articles 9 and 11. For the purposes of this report, the -1- I I I I I I I I I 1. I I I I I I I I I File No. D-8053-601 August 23, 1989 vicinity of the site is defined as properties located within a one-quarter mile radius from the borders of the site boundaries. SCOPE OF SERVICES Task I -Preliminary Research Research was performed to estimate the potential for significant impacts to the property from the presence of hazardous materials on or within the vicinity of the property. The scope of services for Task I of the PSA are presented as follows: o Performed an onsite reconnaissance to identify indicators suggestive of the potential for the presence of hazardous materials on the property. Surveyed adjacent properties from public thoroughfares to evaluate if these properties possess facilities or structures that potentially use, store, generate or dispose of hazardous materials. Provisions for a formal asbestos survey onsite were not provided in this scope of services. o Contacted the following regulatory agencies to obtain information regarding the potential presence of hazardous materials on the site or in the vicinity of the site: HAZARDOUS MATERIALS MANAGEMENT DIVISION (HMMD) "HE48 Listings", dated August 1, 1989. "HE17 Listings", dated July 26, 1989. "HE23 Listings", dated August 1, 1989. "Unauthorized Release Listing", dated July 13, 1989. REGIONAL WATER QUALITY CONTROL BOARD (RWQCB) "Underground Storage Tank Facilities Listing", dated August 1, 1989. "Regulated Waste Discharger System Listing", dated August 10, 1988. CITY OF CARLSBAD FIRE DEPARTMENT "Underground Storage Tank Permit Records." The permit record search is conducted by the fire department personnel. The search is performed for the site and adjacent properties. -2- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 0 0 0 DEPARTMENT OF AGRICULTURE Contacted the Department of Agriculture for information concerning pesticides and herbicides on the subject property. US ENVIRONMENTAL PROTECTION AGENCY (EPA) "CERCLIS Listing or CERCIA (Comprehensive Environmental Response, Compensation and Liability Act) Superfund Listing", dated March 7, 1989. "RCRA (Resource Conservation and Recovery Act) Compliance Monitoring and Enforcement Log (CMEL) for California", dated March 15, 1989. "RCRA Hazardous Waste Data Management System (HWDMS) Listing", dated Sepcember 19, 1988. "RCRA WASTE Listing", dated June 20, 1989. "RCRA Notifier Listing" dated September 1, 1988. "RCRA WASPROC Listing", dated September 15, 1988. "Proposed and Final National Priority List (NPL)- California", dated March 7, 1989. CALIFORNIA DEPARTMENT OF HEALTH SERVICES (DHS) "Expenditure Plan for the Hazardous Substance Cleanup Bond Act", dated January 1988. "Hazardous Waste and/or Substance Sites List (Cortese List)", dated July 1989. "Abandoned Sites Information System (ASPIS) Listing", dated June 9, 1989. "AB 1803 Follow-up Program", dated December 1988. Reviewed aerial photographs available from the County of San Diego Mapping Division to obtain information concerning the history of the property. Reviewed United States Geologic Survey (USGS) topographic maps to obtain information relative to site topography and previous development and activities on_ the site and properties in the vicinity of the site. Chain of title information for the site was not available for our review during the preparation of this report. Upon submittal of the chain of title study to our firm, an addendum letter will be prepared under separate cover for your review. The title information is reviewed to estimate the potential for past or present property owners to have generated, stored, or disposed of hazardous materials onsite. -3- I I I I I I I I I I I I I I I I I I I File No. D-8O53-6O1 August 23, 1989 0 Reviewed available geotechnical data and geologic reports for this property and adjacent properties to obtain information regarding the prevailing geologic and groundwater conditions. The reports were surveyed to determine if the boring and/or trench logs contained indicators suggestive of the presence of hazardous materials, such as noted discolored soils or excessive organic odors. EXISTING SITE AND GEOLOGIC CONDITIONS Site Location The irregularly shaped 424 acre site is located approximately one mile east of El Camino Real and immediately south of Palomar Airport Road in the City of Carlsbad, California. The site contains approximately 2,000 feet of frontage along Palomar Airport Road. presented on the Site Plan, Figure 2. Existing Conditions and Improvements The site boundaries are A site visit was performed by a representative of GEC on July 24, 1989. Site observations indicate that the majority of the property is essentially undeveloped and is covered with native vegetation (grasses and coastal chaparral). The visit indicates that the property contains a network of tributary gullies and ravines which converge into a west trending canyon. As depicted on the Site Plan, Figure 2, noted man-made improvements to the site include a San Diego Gas and Electric electrical transmission line -4- I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 system supported by wooden poles located along the extreme northeastern portion of the property. The northeastern portion of the site (approximately 40 acres) was observed to support an active tomato field. Numerous dwellings and equipment commonly associated with agricultural activities were observed along the southeastern perimeter of the tomato field. Two above-ground fuel storage tanks and a structure which is apparently utilized for storage were observed in this area. unpaved roads were observed to traverse the property. Numerous Located within the property boundaries, but not part of the Carrillo Ranch project scope, is the City of Carlsbad proposed Park site and Rancho de los Quiotes restoration project (see Site Plan, Figure 2). Contained within this area, of approximately ten acres, are numerous structures. Proposed Improvements The base map for the site entitled "Studies Composite for Carrillo Ranch", prepared by Rick Engineering and dated November 3, 1988, was reviewed during the preparation of this PSA. The map indicates the proposed site development will consist of the construction of numerous single-family residential structures. It is anticipated that the structures will be supported on shallow foundations with slab-on-grade floors. Grading as tentatively proposed will result in cut and fill slopes of 50 feet in height. -5- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 Review of Geotechnical Reports The following geotechnical reports were reviewed during the preparation of this report: 0 "Soil and Geologic Reconnaissance for Bressi Ranch, San Diego County, California", prepared by Geocon Incorporated, dated March 23, 1982. o "Report of Phase I Geotechnical Study for Bressi Ranch, Carlsbad, California", prepared by Geocon Incorporated, dated June 4, 1982. o . "Preliminary Soil and Geologic Investigation -Landslide Area for Carrillo Ranch", prepared by Geocon Incorporated, dated August 9, 1989. A review of the report dated August 9, 1989 indicates that the evaluation of specific geologic conditions within the entire property limits was beyond the scope of that specific investigation. However, based on above geotechnical exploration activities and geologic mapping conducted by Geocon Incorporated for the site and the Bressi Ranch property (located approximately 2,500 feet west of the site), it appears that the property is generally underlain by Eocene Delmar Formation, Torrey Sandstone and by the Jurassic Sant~~&~. Peak Volcanics. Each of these is described as follows: Santiago Peak Volcanics. The Santiago Peak Volcanics are typically characterized by highly fractured and jointed metavolcanic rock. Weathering and decomposition of near-surface exposure result in highly expansive, clayey topsoil. -6- I I I I I I I I I I I i I I I I I I I File No. D-8053-601 August 23, 1989 Delmar Foundation. Soils of the Delmar Formation are generally characterized by yellowish-green, sandy claystone interbedded with medium- gray, coarse-grained sandstone. This formation is generally characterized by inherently weak claystone beds. Torrey Sandstone. The Torrey Sandstone consists primarily of fine to coarse grained, well sorted, white to tan, weakly cemented sandstone. Shaly siltstone or clayey siltstone interbeds, as well as some reddish- brown concretions are also characteristic of this formation. Groundwater A review of the above-referenced report dated August 9, 1989 indicates that ten exploratory borings were advanced to a maximum depth of 72 feet below the ground surface. Groundwater was encountered at a depth of 23 feet below the existing ground surface in an exploratory boring (B-1) advanced in the west/northwest portion of the site during the onsite geotechnical subsurface activities performed on June 5, 1989. Indicators suggestive of the possible presence of petroleum hydrocarbons were not noted in the boring and/or trench logs and text presented in the above-referenced reports. -7- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 Review of Regional Water Quality Control Basin Plan The report published in July 1975 by the Regional Water Quality Control Board entitled, "Regional Water Quality Control Plan, San Diego Basin, California", was referenced for information concerning possible onsite water uses and groundwater quality. The basin plan report indicates that the site is located within the Vista and Agua Hedionda Hydrographic Subunits (4.20 and 4.30, respectively) of the Carlsbad Hydro graphic Unit ( 4. 00). At the time the report was published groundwater was listed as having potential municipal, agricultural and industrial uses. The report indicated that in excess of 1,000 mg/1 of total dissolved solids (TDS) are generally present in the local groundwater and, therefore, it is not reported to be widely used for domestic supply. SITE RECONNAISSANCE Onsite Survey Numerous site visits were performed by representatives of GEC. The site visits included a review of the existing site conditions to attempt to identify indicators suggestive of the presence of hazardous materials. The Site Plan for the property which depicts the existing conditions and improvements observed during the reconnaissance is presented in Figure 2 (Site Plan). -8- I I I I I 1. I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 The visits indicate that approximately 40 acres located in the northeastern portion of the property supports an active tomato field. Numerous structures constructed of wood and aluminum are present adjacent to the east and south of the existing tomato field. Two above-ground storage tanks were observed in this area. At the time of the visit, the above-ground storage tanks were surmised to contain fuel. A rectangular wooden structure was observed immediately south of the fuel storage tanks. A warning sign attached to the door of the structure indicated that the structure is utilized for storage of poisonous materials. It is anticipated that the poisonous materials may include pesticides and/or herbicides. The structure was observed to be secured by a bolt lock. ~quipment associated with agricultural activities was observed approximately 25 feet east of the above-ground storage tanks and apparent pesticide storage structure. These items included a mobile pesticide/herbicide applicator, hoses, plastic piping, a large John Deere tractor, a wide steel plow and a three bin fertilizer applicator. Numerous sections of lattice were observed in this area. In addition, SDG&E high voltage electrical transmission lines, supported by wooden structures traversed the extreme northeastern corner of the property. -9- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 A small shallow body of ponded water was observed along the westerly drainage, immediately adjacent to and northeast of the proposed City of Carlsbad parkland. Vegetation consisting of native grasses was observed throughout the remaining portions of the site. Brush and chaparral was also observed along the steeper slope sides and ravines. In addition, numerous unpaved roads were observed to traverse the property. Offsite Survey The site reconnaissance also included a perimeter survey of adjacent properties from public thoroughfares to assess if operations or structures located on these properties typically use, store, generate, or dispose of hazardous materials. Located within the central portion of the site is the proposed City of Carlsbad parkland/historical monument site. This property, formerly known as Rancho de los Quiotes, contains approximately twelve structures of various sizes and uses. It is our understanding that the City of Carlsbad has initiated plans to restore these structures as historical monuments. Residential structures occupy the adjacent properties to the southeast and south of the site. Undeveloped properties border the site to the northwest, east and west. Palomar Airport Road fronts the northeastern portion of the property. The former Carlsbad Raceway is located -10- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 approximately 1,500 feet north/northwest of the site. The raceway was observed to be situated within an east-west trending ravine. Numerous structures were visible in this area. Observed between the site and the raceway is an apparent skateboard facility with assorted obstacle structures. Visible, approximately 700 feet northwest of the site, was a large above-ground storage tank. Numerous abandoned steel structures were also observed in proximity to the tank. Other properties in the vicinity. (within one-quarter mile) of the site were observed to be undeveloped or used for agricultural purposes. Other indications of the presence of hazardous materials, including petroleum odors, s~il discoloration, irregular vegetation, chemical containers, or the presence of previous structures or facilities, were not noted during the offsite survey. SITE HISTORY -RECORDS REVIEW Review of Aerial Photographs Aerial photographs available at the County of San Diego, Department of . Public Works for the years 1928, 1967, 1970, 1978, and United States Department of Agriculture (USDA) aerial stereo-photographs for 1953 were reviewed for the preparation of this report. Observations noted during the review are discussed below: -11- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 A review of the 1928 County of San Diego aerial photographs indicate that the property is undeveloped. The central portion of the property appears to consist of sparse vegetation (natural grasses). The northeastern property area is covered with natural grasses and chaparral. A narrow section of the site, extending along Palomar Airport Road, appears to support agricultural activities (i.e., absent of vegetation, symmetrical rows, etc.). A generally east-west trending drainage is visible along the east-central and northern portion of the site. Two structures are visible within the proposed City of Carlsbad parkland (northcentral portion of the site). Palomar Airport Road fronts the northeastern property boundary. Other properties adjacent to and in the vicinity of the site appear to be undeveloped at this time. A review of the 1953 aerial photograph indicates that the property is essentially undeveloped. Two large reservoirs are visible in the central and northwestern portions of the site. An earthen dam is visible on the western perimeter of the northwesterly located reservoir. A small elongated portion of the site, located approximately one-quarter mile east of the northwestern reservoir, appears to support agricultural activities. Two small areas of ponded water are visible immediately adjacent to the west and northeast of the apparent agricultural field. What appears to -12- I I I I I I I I I I ' I I : •• J ....... ,, I I I I I I File No. D-8053-601 August 23, 1989 be a grove of trees is present adjacent to the east of the small northeasterly positioned pond. Numerous structures are visible in the area of the future City of Carlsbad Park site. Properties adjacent to and in the vicinity of the site are either undeveloped or used for agricultural purposes. In addition, Rancho Santa Fe Road, located east of the site, appears to be paved at this time. A review of the 1967 aerial photograph indicates very similar observations to the onsite descriptions given above. Visible adjacent to the southwestern portion of the property is an apparent residential development. The Carlsbad Raceway is observed north of Palomar Airport Road. A review of the 1970 aerial photographs indicate that the northeastern portion of the property is used for agricultural purposes. Otherwise, the site development is similar to that noted in the review of the 1967 aerial photograph~. The area immediately north of Palomar Airport Road and in the vicinity of the site appears to be utilized for agricultural purposes. The properties adjacent to the east and south of the site appear to be undeveloped. Agricultural fields are still present to the north and west of the site (south of Palomar Airport Road). -13- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 A review of the 1978 aerial photographs indicate that the previously referenced small elongated agricultural area in the northwestern portion of the site does not appear to support agricultural activities in the photographs. The large and small westernmost reservoirs are observed to be without water and are covered with vegetation growth consisting of grasses and small shrubs. Review of Topographic Maps A review of the 1968 United States Geologic Survey (USGS) topographic map for the Encinitas, Rancho Santa Fe and San Marcos Quadrangles in California was performed to provide additional information regarding site topography and previous site development. Figure 3 presents a reproduction of portions of the three quadrangle maps including the site and properties in the vicinity of the site. A review of the 1968 USGS maps indicates that the site is undeveloped. The only noted improvement to the site is an SDG&E overhead electrical transmission line system traversing the extreme northeastern corner of the site. The topographic map indicates a generally east-west trending drainage with an additional tributary feeding into the above drainage from the northeast. Elevations within the specific site area range from a high of approximately 540± feet above Mean Sea Level (MSL) on the ridge near -14- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 the southern property line to a low of approximately 200± feet MSL within the bottom of the main drainage which dissects the property. A review of Figure 3 indicates that approximately six structures (noted by small black squares) are located within the central portion of the site and referenced as Rancho de los Quiotos. Other noted adjacent improvements include apparent residential structures along the southeastern corner of the site. Palomar Airport Road is observed to front the northeastern portion of the site. Improvements within the vicinity of the site include assorted structures east of the northeastern portion of the property, and Rancho Santa Fe Road to east of the site. RESULTS OF CONTACTS WITH REGUIATORY AND GOVERNMENTAL AGENCIES Information was obtained from the following governmental agencies to assess the potential for the presence of hazardous materials on the subject property: County of San Diego-Hazardous Materials Management Division (HMMD), the San Diego Regional Water Quality Control Board (SDRWQCB), the City of Carlsbad Fire Department, the California Department of Health Services (CDOHS), the San Diego Air Pollution Control District -15- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 (SDAPCD), the San Diego County Department of Agriculture (SDCDA) and the United States Environmental Protection Agency (EPA). obtained from these agencies is summarized below. Hazardous Materials Management Division The following HMMD information sources were reviewed: o "HE48 Listings", dated August 1, 1989. 0 0 "HE17 Listings11 , dated July 26, 1989. "HE23 listings", dated August 1, 1989. The information 0 11 Unauthorized Release Listing11 , dated July 13, 1989. A description of each of these information sources is presented in Appendix A. HE48 Listing. Establishments presented in the HE48 listings are those reported to store, generate and/or dispose of hazardous materials. Included within the listings are businesses that operation above or underground storage tanks. The listings also disclose establishments which are presently on the HMMD mailing list and monitored by the HMMD regarding the nature of their operations. The HE48 listing indicates that Rueben Lopez maintains storage tanks on the site, which contain hazardous materials. Properties adjacent to the site were not included in the HE48 listing. -16- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 Properties in the vicinity of the site referenced in the HE48 listing include: 0 0 0 0 0 0 Semiconductor Technology at 6510 Camino Capistrano located south of the site. Meadow Ridge Sales at 6542 Corte Montecito located south of the site. Ponderosa Country at 2624 La Golondrina Street located west of the site. Carlsbad Raceway at 6600 Palomar Airport Road located north of the site. National Car Rental at 6600 Palomar Airport Road located north of the site. Hollman Yachts at 6600 Palomar Airport Road located north of the site. The above listed sites were indicated as establishments on the HMMD mailing list and were not determined to dispose, generate or transport hazardous materials at the date of listing. The HE48 listings reviewed are presented in Appendix B. HE17 Listin&. The HE17 listing summarizes disclosure and violation information regarding the handling of hazardous materials. The listing reports that Rueben Lopez maintains storage tanks which contain hazardous materials. Properties adjacent to and in the vicinity of the site were not included in the HE17 listing. -17- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 HE23 Listing. The HE23 listing summarizes hazardous materials storage information. The listing reports that Rueben Lopez maintains one 500 gallon above-ground diesel fuel tank and two above-ground 500 gallon liquid nitrogen fertilizer storage tanks. Properties adjacent to and in the vicinity of the site were not included in the HE23 listing. Unauthorized Release Lis ting. Neither the site nor properties adjacent to or in vicinity of the site were included in the HMMD Unauthorized Release Listing. Regional Water Quality Control Board -Listings The following RWQCB information sources were reviewed: 0 0 "Underground Storage Tank Facilities Listing", dated February 2, 1989. "Regulated Waste Discharger System Listing", dated August 10, 1988. The descriptions of the listings reviewed for these properties are provided in Appendix A. Neither the site nor any properties adjacent to and in vicinity of the site are referenced in the Underground Storage Tank Facilities listing. Waste Discharge Facilities Listing. WDR permits are necessary for evaporation ponds, leach fields and irrigation systems. The subject -18- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 property was not referenced in the Waste Discharge Facilities Listing, however, properties in the vicinity of the site are included in this listing as having obtained WDR permits. These properties and the year that these permits were issued are summarized below: 0 Carlsbad Raceway at 6600 Palomar Airport Road located north of the site: WDR I.D. No. 000000276 1 permit 1 permit (1965) (1986) San Diego Air Pollution Control District (APCD) Violator File Register The San Diego Air Pollution Control District (APCD) Violator File Register references facilities which have violated APCD regulations. Neither the site nor properties in the vicinity of the site were included in the APCD Violator File Register. City of Carlsbad Fire Department A search of available underground storage tank permit records for the site and adjacent properties was requested from the City of Carlsbad Fire Department. This search was performed by City of Carlsbad Fire Department personnel. Permits concerning the installation or removal of underground tanks for the site or other properties in the vicinity of the site were not noted by the Fire Department personnel. -19- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 San Diego Department of Agriculture Weights and Measures - Pesticide Use Enforcement Division Ms. Carolyn Nielsen, Deputy Commissioner of the Department of Agriculture, was contacted concerning historic information concerning agricultural practices in the vicinity of the site. Mrs. Nielson indicated that tomatoes have been grown on a portion of the Carrillo Ranch site since the 1960s. Further information obtained from Ms. Carolyn Nielsen indicates that Mr. Tom Lopez and Mr. Rueben Lopez are leasing the northeastern portion of the site. Ms. Nielsen indicated the above parties also have a permit for the application of restricted pesticides/herbicides (Category I). specific restricted pesticides/herbicides include: 0 Guthion 0 Lamate 0 Paraquat 0 Vydate 0 Pydrin 0 Strictnin 0 Methyl Bromide 0 Dasnit 0 Bayleton The I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 Ms. Nielsen also indicated that the site is inspected regularly by the Department of Agriculture inspectors and that violations pertaining to the storage, handling or application of these pesticides/herbicides have not been issued. US Environmental Protection Agency The following EPA information sources were reviewed: 0 0 0 0 0 0 0 "CERCLIS Listing or CERCIA (Comprehensive Environmental Response, Compensation and Liability Act) Superfund Listing", dated March 7, 1989. "RCRA (Resource Conservation and Recovery Act) Compliance Monitoring and Enforcement Log (CMEL) for California", dated March 15, 1989. "RCRA WASTE Listing", dated June 20, 1989. "RCRA Hazardous Waste Data Management System (HWDMS) Listing", dated September 19, 1988. "RCRA WASPROC Listing", dated September 15, 1988. "RCRA Notifier Listing" dated September 8, 1988. "Proposed and Final National Priority List (NPL)-California", dated March 7, 1989. A description of each of these information sources is provided in · Appendix A. The site and properties adjacent to or in the vicinity of the site were not identified in any of the above-referenced listings. -21- I I I I I I I I I I I I I I I I I I I File No. D-8O53-6O1 August 23, 1989 California Department of Health Services (DHS) The following DHS information sources were reviewed: CALIFORNIA DEPARTMENT OF HEALTH SERVICES (DHS) o "Expenditure Plan for the Hazardous Substance Cleanup Bond Act", dated January 1988. o "Hazardous Waste and/or Substance Sites List (Cortese List)", dated August 1988. o "Abandoned Sites Information System (ASPIS) Listing", dated June 9, 1989. The above-referenced information sources are described in Appendix A. A review of the report entitled "Expenditure Plan for the Hazardous Substance Cleanup Bond Act", dated January 1988 indicates that the nearest targeted hazardous waste site is the Chatham Brothers Barrel Site (Bernardo Avenue) located approximately eight miles east of the subject property. The site, properties adjacent to the site, and properties in the vicinity of the site were not referenced in either the Cortese listing or the ASPIS listing. -22- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 SECTION II -LIMITED SOIL SAMPLING INTRODUCTION AND PURPOSE This section presents the results of limited soil sampling (Task II) on the site. Six surficial (6 inches to 1 foot below the existing ground surface) soil samples were obtained at locations indicated on Figure 2 and s·abmitted for laboratory analysis using EPA Test Method 8080 (organochlorine pesticides), EPA Test Method 8140 (organophosphorus pesticides) and EPA Test Method 8150 (chlorinated herbicides). The purpose of the limited soil sampling services was to obtain data to estimate the potential for the presence of organochlorine pesticides, organophosphorus pesticides and chlorinated herbicides related to present and past agricultural activities on the site. Scope of Services As outlined in our "Acknowledgement" dated August 8, 1989, the following scope of services was performed: 0 0 Collected six samples within the confines of the site utilizing a stainless steel spade and a hand auger. The samples were collected from depths of 6 inches to 1 foot below existing grade. Provided quality control/quality assurance procedures during the field exploration. This included chain of custody documentation, cleansing and rinsing sampling equipment prior to each sampling effort. -23- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 o Submitted soil samples to Analytical Technologies, Incorporated to be analyzed for organochlorine pesticides (EPA Test Method 8080), organophosphorus pesticides (EPA Test method 8140) and chlorinated herbicides (EPA Test Method 8150). Field Activities The field activities were performed by representatives of GEC on July 27 and 28, 1989. A total of six soil samples were obtained at various locations within the confines of the property using a hand auger and a stainless steel spade. The samples were obtained from depths of 6 inches to 1 foot below the existing ground surface. The hand auger was used to obtain the soil samples at the 1 foot depths. Sampling equipment was cleansed before and after each sampling effort. The cleansing activities consisted of washing the hand auger and spade in an Alconox solution with two tap water rinses. The samples were packed on ice and delivered to the laboratory for analysis. Sample Location The approximate locations of the samples are illustrated on the Site Plan, Figure 2. Samples CR-1, CR-2 and CR-6 were collected from the soils which, based on the previously discussed aerial photograph review, are surmised to have had a history of agricultural use. Soil Samples CR-1, CR-2 and CR-6 were collected at depths of 6 inches and 1 foot (CR-2 and -24- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 CR-6) below the existing ground surface. Soil Sample CR-1, a very moist sediment sample, was obtained from within the westerly trending drainage. Samples CR-3, CR-4 and CR-5 were collected at respective depths of 6 inches, 8 inches and 1 foot below the existing ground surface. samples were collected from within the active tomato field. Laboratory Testing These The selected soil samples were submitted to Analytical Technologies, Incorporated, a State of California certified environmental testing laboratory. Copies of the analytical test results and chain of custody forms are presented in Appendix C. Based on their location, soil samples CR-3, CR-4 and CR-5 were subjected to three separate analyses. The samples were analyzed for organochlorine pesticides (EPA Test Method 8080), organophosphorus pesticides (EPA Test Method 8140) and chlorinated herbicides (EPA Test Method 8150). Soil samples CR-1, CR-2 and CR-6 were collected from areas suggestive of past agricultural activities. These three samples were analyzed for organochlorine pesticides utilizing EPA Test Method 8080. -25- I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 Discussion of Test Results The analytical laboratory results indicate that samples CR-3 and CR-4 exhibited concentrations of DDT, DDD and toxaphene above the laboratory detection limits. The laboratory test results for toxaphene, DDT and its derivatives DDD and DDE are also presented in Table I. A review of Table I indicates that the summed concentration of DDT+ DDE in each of the six soil samples is less than the Total Threshold Limit Concentrations (TTLC) of 1.0 mg/kg. Further review of the laboratory test results indicates that the concentration of toxaphene in each of the six soil samples are less than the TTLC of 5.0 mg/kg. As stated previously, three soil samples were subjected to analysis using EPA Test Methods 8140 and 8150. Concentrations above the laboratory detection limits were not exhibited for these samples (CR-3, CR-4 and CR- 5). Table I includes the Total Threshold Limit Concentration (TTLC) and Soluble Threshold Limit Concentration (STLC) for each compound. Materials which contain concentrations of a potentially hazardous substance (as defined in Section 66699, California Code of Regulations, (CCR) Title 22) -26- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 greater than the TTLC value are classified as hazardous wastes for disposal purposes. The TTLC values apply to the data obtained in the laboratory analyses performed for the present study. For purposes of comparison with the TTLC value, the summed concentration of DDT and its natural breakdown products, DDE and DDD, is appropriate (Section 66699, CCR Title 22). Proposition 65, the Safe Drinking Water Act of 1986, requires disclosure to any parties/individuals of potential exposures to the listed "Prop 65" chemicals. DDT, DDE and toxaphene are included on the above list and, therefore, the presence of these chemicals on the property may invoke the "Prop 65" disclosure clause. This issue is discussed in thG "Conclusions and Recommendations" section of this report. -27- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 SUMMARY OF FINDINGS 1. A review of the information obtained indicates that the property is and has supported historic and current agricultural activities. As stated, a tomato field, comprising approximately 40 acres, is situated within the extreme northeastern perimeter of the property. 2. A review of the available documentation from government agencies indicates that Mr. Tom Lopez and Mr. Rueben Lopez maintain three 500 gallon above-ground storage tanks. The information obtained from the HMMD indicates that the one storage tank contains diesel fuel and that two contain liquid nitrogen fertilizers. However, only two above-ground storage tanks were observed during the site reconnaissance. In addition, information obtained by the Department of Agriculture indicates that the above party have permits for the storage, handling and application of restricted pesticides/herbicides. Violations concerning the above uses was not reported by the Department of Agriculture. 3. The site reconnaissance indicates that a portion of the property is currently being used for agricultural activities. These activities consist of the production of tomatoes. Two above-ground fuel tanks were observed along the northeastern portion of the property (see Site Plan, Figure 3). Significant soil discoloration was not observed in the areas -28- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 beneath the fuel storage tanks. A wooden storage shed surmised to contain pesticides and herbicides was observed adjacent and south of the above- ground storage tanks. The storage shed contained a warning placard and was, at the time of the site visit, secured by a pad lock. 4. Laboratory test results indicate that measurable concentrations of the organochlorine pesticides DDT, DDE, and toxaphene are present in the surficial soil samples collected for analysis. The soil samples exhibited concentrations of the above-referenced organochlorine pesticides significantly below the appropriate established toxicity threshold limit concentration (CCR, Title 22) and, therefore, classification of these soils as hazardous waste is not indicated. -29- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 CONCLUSIONS AND RECOMMENDATIONS The laboratory results of the limited soil sampling phase (Task II) of this study indicate that it may be necessary to comply with Proposition 65 legislation which requires that sufficient notice be provided to all persons who may be affected by the presence of chemicals at levels which are known by the State of California to cause cancer or lcproductive toxicity (California Health & Safety Code, Section 25249.6). As noted above, the results of laboratory analyses indicate that the compounds toxaphene, DDT, and DDE are present in the soils on the site. These compounds are listed as chemicals known by the State of California to cause a significant risk of cancer or reproductive toxicity at levels of exposure greater than 2 ug/day for the sum of DDT and DDE and 0.6 ug/day for toxaphene (Title 26, California Administrative Code, Section 12711). It is recommended that a quantitative risk assessment (as defined in Title 26, California Administrative Code, Section 12703) be performed for the purpose of establishing whether the concentrations of toxaphene, DDT, and DDE present in the soil on the property have the potential to produce exposure levels which could potentially lead to a significant risk of cancer and or reproductive toxicity. -30- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 PRELIMINARY SITE ASSESSMENT LIMITATIONS This preliminary site assessment has been prepared exclusively for Pacific Scene, Incorporated, and the information obtained is only relevant to the dates of the records reviewed or as of our last site visit. The client should recognize that the preliminary site assessment is not a comprehensive site characterization and should not be construed as such. The findings and conclusions in this report are predicated on our site reconnaissance, a review of regulatory records, a review of the historical usage of the property and the results of the limited soil sampling. The absence of significant indicators which suggests that hazardous materials have impacted the site does not preclude the presence of hazardous materials on the property. The client should also understand that radon gas, asbestos containing materials, and methane gas were not addressed in the preliminary site -assessment scope of services. Therefore, the report should only be deemed conclusive with respect to the information obtained. No guarantee of the results of the study is implied .within the intent of this report. The professional services performed were conducted in accordance with the local standard of care in the geographic region at the time the services were rendered. -31- I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 TABLE I SUMMARY OF ANALYTICAL LABORATORY RESULTS Soil Sarnnles -Organochlorine Pesticides (EPA Test Method 8080) CHEMICAL COMPOUND CR-1 CR-2 CR-3 CR-4 CR-5 P, P' -DDD <0.010 <0.010 <0.050 <0.030 <0.010 p' p I -DDE <0.010 <0.010 0.30 0.15 <0.010 P, P' -DDT <0.010 <0.010 0.13 0.067 <0.010 O,P' -DDD <0.010 <0.010 <0.050 <0.030 <0.010 O,P'-DDE <0.010 <0.010 <0.050 <0.030 <0.010 O,P' -DDT <0.010 <0.010 <0.050 <0.030 <0.010 TOTAL DDT+DDE <0.010 <0.010 0.48 0.217 <0.010 TOXAPHENE <0.10 <0.10 0.064 0.34 <0.10 CR-6 TTLC <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 1.0 <0.10 5.0 Test results are presented in quantities of mg/kg (parts per million) TTLC = Total Toxicity Limit Concentration I I ._ A·PPENDI:X A· I I I • ,-;_ I I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 APPENDIX A Hazardous Materials Management Division The following HMMD information sources were reviewed: 0 0 0 0 The combined HElO and HESS listings dated August 3, 1988. The combined HElO and HESS listing summarizes properties with reported underground storage tanks and facilities that utilize hazardous materials. HE17 listings dated July 28, 1988. The HE17 listing summarizes disclosure/violation information regarding the storage, handling, generation, and/or disposal of hazardous materials per the California Code of Regulations and California Heath and Safety Code. "HE23 Listings", dated January 4, 1989. The HE23 Listings summarizes underground storage tank size/content information and hazardous material/waste information. "Unauthori.zed Release Listing", dated April 3, 1989. This listing was reviewed to assess if unauthorized releases of hazardous materials had been reported for the site or properties in the vicinity of the site. Regional Water Quality Control Board The following RWQCB information sources were reviewed: 0 0 "Underground Storage Tank Facilities Listing", dated February 2, 1989. This listing was reviewed to assess whether unauthorized releases of hazardous materials from underground storage tanks had been reported for the site or bordering properties. "Regulated Waste Discharger System Listing", dated August 10, 1988. This information source provides a listing of entities regulated by the RWQCB with waste discharge requirements. I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 APPENDIX A (Continued) Environmental Protection Agency The following EPA information on sources were reviewed: 0 0 0 0 "CERCLIS listing or CERCLA (Comprehensive Environmental Response, Compensation and Liability Act) Superfund Listing", dated September 15, 1988. This listing provides an EPA inventory of potential hazardous waste sites. "RCRA (Resource Conservation and Recovery Act) Compliance Monitoring and Enforcement Log (CMEL) for California", dated September 1, 1988. This document lists EPA and State inspections and enforcement actions and is generated from the national Hazardous Waste Data Management System (HWDMS). HWDMS contains information on generators, transporters and treatment, storage and/or disposal facilities identified under the Resource Conservation and Recovery Act. This document is a summary reference for those inspections where violations have been determined. "RCRA Hazardous Waste Data Management System (HWDMS) Listing", dated September 19, 1988, "RCRA Notifier Listing", dated September 9, 1988, "RCRA WASTE Listing", dated September 15, 1988, and "RCRA WASPROC Listing", dated September 16, 1988. These listings contain information regarding reported RCRA generators, transporters, and/or treatment, storage, and/or disposal facilities. "Proposed and Final National Priority List (NPL)-California", dated August 12, 1988. This information source provides a listing of designated hazardous waste sites under CERCLA. I I I I I I I I I I I I I I I I I I I File No. D-8053-601 August 23, 1989 APPENDIX A (Continued) California Department of Health Services (DHS) The following DHS information sources were reviewed: o "Expenditure Plan for the Hazardous Substance Cleanup Bond Act," dated January 1988. The DHS developed the site-specific expenditure plan as a basis for appropriating hazardous substance clean up bond act funds. The expenditure plan was developed to provide a complete and accurate outline of the DHS's plans for clean up of statewide hazardous waste sites. The plan identifies hazardous waste sites targeted for clean up by private responsible parties, the DHS and the EPA for the next 5 fiscal years. o "Hazardous Waste and Substances Sites List (Cortese Listing)" dated August, 1988. The Cortese listing was reviewed to assess if any hazardous waste facilities exist in the vicinity of the site which are subject to corrective action pursuant to Section 25187.5 of the Health and Safety Code. This information source lists property designated as hazardous waste properties pursuant to Article 11 of Chapter 6.5 of Division 20 of the Health and Safety Code. Additionally, the listing identifies underground storage tanks for which an unauthorized release report is filed pursuant to Section 25295 of the Health and Safety Code and all solid waste disposal facilities from which there is a migration of hazardous waste pursuant to Subdivision (e) of Section 13273 of the Water Code. 0 "Abandoned Sites Information System Listing (ASPIS) dated June 9, 1989. The ASPIS listing was reviewed to assess if potential hazardous waste sites exist adjacent to or in the vicinity of the subject property. This listing also indicates if properti~s in proximity to the subject site are scheduled for further investigative activities by the Department of Health Services' Toxic Substances Control Division. I-,.:_-.-I ,, I .. ' -1. . -~ •.' I ~ : '; I •·•·• 1· ' I ~ . : . :._,· -,. I -APPENDIX B I I ,> I. I ,, ,_.·, " 1· ., I I I r ------------------- .H.~.804-01 DE~ARIMENLOLH EALT H __ SERUC.ES_ DAI_E__08!_01l.89__£AG.E 44 HAZARDOUS MATERIALS COMBINED HElO AND HE58 LISTING--STREET NAME ORDER SI NAME SI NO Zie ESI NAME ESJ"_N_Q____B U $ INACI PHON.E.__fXP SICl SIAI CODE DATE CABOT DR 9340 92126 UNITED VINTERS H21305 K03 1130 ..cAB.DL.D8 9345 921.26 NAIIONAI rnK me HQl.544.__KOZ l 56628011_0228 2899 03. CABOT DR 9356 92126 H28895 K04 5662570 0531 CABOT DR 9358 92126 TC AUTO REPAIR Hl9354 K04 6959051 0630 01 CABOT DR 9370 92126 MAYER BLUEPRINT H28475 K02 5861336 0731 J:Afill.LD 9312 92126 BRUC.E.!_s.__AUTJLREeAIR H?.841~0 300603__ll22 CABOT DR 9395 92126 NATIONAL PEN CORP. H00170 K07 5667800 0930 2753 9-6- CABOT DR 9455 92126 ECO AIR PRODUCTS INC Hl5125 KOl 2718111 0430 91 CABOT DR 9352-56 92126 BILL POUND AUTOMOTIVE Hl9215 K04 6931107 0831 03 CABOI DR 1B 9358 92126___REYNOLD5-GRAe.H1.<:_ARI..!LCORe H 1 . .9 3 5 .5___K o 2 l 566513o__n63o______s_o84 02__ CABRILLO MEMORIAL DR 1800 92106 CABRILLO NATIONAL MONUMENT H21399 K07 2935450 0630 CACATUA STREET 2909 92009 ENGEL SUSAN C 51880 L CACTUS & AIRWAY RD 92073 NAKANO FARMS H99071 K02 4216581 0000 .CACIIIS & OIAY MESA R· 92023-__SIEMPRE_J[L\ULEARM H99022__K02 431 l.6~!l.__Jl_O_O CACTUS RD 883 92073 R&R AG CHEM INC Hl0861 K04 6196616 0131 5161 3 CACTUS RD 1060 92073 MARTINEZ FARMS H99064 K02 6900879 0000 CACTUS RD 1180 92073 MARTINEZ FARM H99068 K02 6906571 0000 .cAC.IlJS SI 915] 92DAO__.WALIER-.-..J.AME5-DREXI 505.3 CACTUS VIEW DR 3683 92116 FRONTIER TOURS 07105 2622003 2721 G CADDEN WAY 3850 92117 STANLEY E RUNKE 51315 K CAFFEY LN 7666 92126 JERRYS AUTO BODY 27898 F CtiGI E SI 3.21-20.5.ll.__T.HOMA5-.EUGENLHEI.NRLCHS 0650 I(__ CALAVO DR 4059 92041 ACCURATE PHOTOTYPESETTING 07820 4643081 2791 N CALAVO DR 3810 92077 INTERNATIONAL AIR 27358 E CALAVO DR 1449 92026 R L DEAVER H99359 K02 7455630 0000 .CALA\lO DR 1442 22026-RICHARD__L_DFAVER H20338 KQ3. l 7 455.6..3..Q_Q,6 CALDA DE REYES 15654 92128 SPRAGUE ANN MICHELLE 52148 L CALEBAN DR 1785 92024 HALL JAYNE E 51724 L CALEDONIA DR 4261 92111 B & C CLEANING SERVICE 11177 2797 331 7217 7 J:ALEND.A_ RD 11213 9212&-.-S.I.EWARLA DRI.ENNE_ELI_S 52219 L_ CALEXICO ST 4425 92034 P & I AUTO TOM HILL 30791 H CALIF ST 3630 92101 MUDSHARKS 05059 6 CALIFORNIA AV 628 92083 MULTI PR WATER SYS 24777 C J;AUEQRN I A AY. 512 9 2 0_8.~UNNS_AUI.O _ RECONDI U otU.NG 21856 G CALIFORNIA AV 628 92083 J AND M MUSTANG RESTORATION 24607 C CALIFORNIA AV 202 92083 KL SHIELDS RENTALS 24613 C CALIFORNIA AV 512-109 92083 STEVE RAE SANDBLASTING 24609 C J;ALIEORNIA AY. 512 92.08L_ILLJL~E~DlNG 246Q6 C --CALIFORNIA AV 512205 92083 ART HOBAN BOATBUILDER 24610 C CALIFORNIA AV 512 92083 AEOLUS PUBLISHING 24665 C , CALIFORNIA AV 503 92083 G VAN EIK RENTALS 24612 C ..cAllfORtHA AJ/_ 5i2 92083 ELEVEN WESTERN JUJ)RS 2':+.7?.2 C CALIFORNIA AV 512 92083 CHAMBER KRADLE 24667 C CALIFORNIA AV 512 92083 DESERT BOUND RACING 24611 C CALIFORNIA AV 512 92083 D AND M PLASTICS 24608 C CALIFORNIA AV 30219 92070 NORTH COUNTY HEALTH SERVICES Hl4705 KOl 7651642 0731 8081 01 CALIFORNIA AV w 628 92083 MULTI PRECONDITIONING-WATER 21855 G-- CALIFORNIA AV w 512 92083 METAL DOORS & FRAMES 21858 G - - - - --· - - - - - - - - - - - - - .-- ~H-E~48_-_4,>8~Q~4_-~0_l ________________ ~DEPARTMENt_OF_JlEALIH __ SERVJ.CES ___ Dl1_IE.__0_8.!JlJ/8_9_fl\!3E~------'llZ------ ST NAME ST CORRAL WAY 5801 6575 .CORI.E_CIS~C-0 _____ _ CORTE DEL CORTE DEL ABETO CORTE DEL ABETO 6088 6352 6352 6.354 .CDRIE.__DEL_ABfIO ____ ~ CORTE DEL ABETO CORTE DEL ABETO IF CORTE DEL CEDRO 6212 6352 6070 NO 6074 .CDRIE.JlELCEDRD----~-~----6088 6054 6066 CORT E DEL CEDRO CORTE DEL CEDRO CORTE DEL CEDRO ..CORIE.__DEL...CEDRO CORTE DEL CEDRO---~•~~---074 CORTE DEL CEDRO 6060 CORTE DEL CEDRO ..CORIE.__DELCEDRD----~ 6070 6060 CORTE DEL CEDRO, CORTE DEL CEDRO CORTE DEL CEDRO 6060 6072 6086 ..CORJf_l)_fLCEDRO..._ __ _ 6.058 CORTE DEL CEDRO CORTE DEL CEDRO CORTE DEL CEDRO 6060 6078 6082 6oa2 ..CJJRJE_D_EL.C.EDR-0 ___ ~ CORTE DEL CEDRO 6072 CORTE DEL CEDRO 6068 CORTE DEL NOGAL _C_QRI.E.___D.f.LNOG.ll---~ 2052 Z.0..5..!i CORTE MONTECITO' CORTE TIBURON CORTEZ __c_o_S.f:.'IOS CT COSTA BELLA STREETS COSTA DEL MAR RD 6542 3366 1822 2~71 3615 2100 COST EBEL LE COTTONNOOD~----~ 2766 8_8.~_6 COTTOln-lOOD AV COTTOlll~OOD AV , COTTONHOOD AV 8710 8846 8950 COTTONWOOD AV ____ _ COTTON~IOOD DR 9000 8"i"35 2775 26925 COUGAR PASS RD COUGAR PASS RD RTE 6 COUINTRY CLUB LANE COUNTRY CLUB DR __ _ 531 1400 COUNTRY CLUB DR 2070 HAZARDOUS MATERIALS COMBINED HElO AND HE58 LISTING--STREET NAME ORDER ZIP EST NAME ESJ_N.O _ __JlUS INA.CT PHO.ME._ _EXP __ S_lC_l__STAI_ CODE DATE 92037 VINCENT ALOYSIUS KRUZICK 50487 K 92008.__CARLEION_BARBARA.....WALLACE 518Z L__ 92008-HUNTER CORP 22730 C 92008 LEFFERDINK CO 22711 C 92008 BLUE BIRD SYSTEMS 22710 C 92D_Q8.__TABSCO 22112-c __ 92008 REPUBLIC TOOL & MANUFACTURING Hl9301 K04 4387835 0331 3079 03 92008 ELECTRIC REGULATOR CORP Hl4999 K04 4387873 1031 3 92008 ESTALAR ENTERPRISES 22719 C 92008__HUGHES_ELECIRICA 222 92008 INTERSTATE ELECTRIC 22731 C 92008 INNOVATIVE TIME 22713 C 92008 HARO DESIGNS INC 08033 4384812 3079 7 92006-REEERENCE_ 27.23 c __ 92008 MEDIA WORKS CO 22718 C 92008 SILK SCREEN DESIGN 22715 C 92008 SIMPLICITY CALIFORNIA 22720 C 92ooa___seECIALIZED_SYSIEM 22716 c __ 92008 URETHANE TOOLING 22717 C 92008 WESTERN CNL INC 31077 H 92008 VUBOTICS CORP 22729 C 92008-CRllETSMAN_BOOK_COMeANY 01163 4.3.8.18.28 21..3L__7 __ 92008 DATATEL CORPORATION 22714 C 92008 APPLIED POLYMER TECHNOLOGY 22724 C 92008 CALIFORNIA FARM SERVICE 22727 C 920.08_CHURCHES __ eEST 22728 c __ 92008 COAST TIRE WHOLESALE 22721 C 92008 HESTERN CNC INC H09165 KOl 4387839 0228 3599 01 92008 CAL OMEGA INC 22732 C 920Q8 __ llNEAR_CORPORATlON 22733 c __ 92008 MEADOW RIDGE SALES 22734 C 92008 HARLACHER ROBERTA LYNN 51902 L 92025 REHM KAREN ELAINE 51793 L 92QQ9 __ l:AY!-OR_MADE; __ GOLF _COMPl\N_Y H28692_K_0_4 9 3;1,l 9_91 __ (!_7 3_1 92045 DEERING BANJO COMPANY 10069 4648252 3931 6 92009 LA COSTA HOTEL AND SPA H03816 KOS 4389111 0228 7997 96 92037 STEWART BONNIER 51746 L 920?l __ I_Rl\NS~l\JtC 31043 H __ 92071 L W BILLINGS 27302 7 92071 SANTEE TIRE & WHEEL H28443 KOl 4482873 0630 92071 SANTEE STATION 14 H05554 K03 4483648 0630 9224 30 92071 LA COLINAS DETENSION FACILITY H20813 K03 ~794491 0630 92020 JOBEc··rnc· -----·-------30617 ______ g-- 92026 H/T FARMS H99422 K02 4446222 0000 92026 FLYNN CATHERINE ANNABELLE 51615 L 92118 PARRY CAROLYN P 51954 L 92!i"25-ESC-C1TY-SEHAGEL1-FtStAl12 H28844--i<il~ 741~7 063 92025 ASHLAND GRANITE CORPORATION H06566 K04 7471364 0831 ------------------- JiE'i8-'i8D'i-Dl D.EfARIMENLOLHEALJH __ S.ERVJ_C.E.S HAZARDOUS MATERIALS DAT E__QJV O·l / 8 9 PAGE 106 COMBINED HElO AND HE58 LISTING--STREET NAME ORDER SI NAME SI NO Zie ESI NAME _E.SJ_N_Q__llUS-1.N_ACT PHONE_ _E;X.P SICl STAT CODE DATE EL CAMINO REAL & POL 92008 RUEBEN LOPEZ H99157 K02 7267741 0000 .fLCAMUHLREAL & SUN 9 2.llJ)-8._RANCH.CLCHl.C.O .. 91.5 2-K.O 2 72996..ll__QQOO EL CAMINO REAL IA 320 92024 INTERSTATE LUBEN TUNE 26920 E EL CAMINO REAL IA 480 92054 CALIFORNIA SMOG BUSTER 27197 E EL CAMINO REAL IB203 477 92024 TERRIE TOMOYO YOSHIKANE 50300 K ..EL__CAMifill REAL 1205 2121 92Q5.!t_KEITH H WEH~LEY 5069_ EL CAMINO REAL 1504 317 92024 NEIL M FISHBACK 50267 K-- EL CAMINO REAL B-205 477 92024 DENNIS CRAIG FITCH 50268 K EL CAMINO REAL J-207 1740 92024 BRUCE ROBERT BRUMM 50256 K ..EL__CAMltlO REAL ti 380 9 20.5..L_JLJIA!J_l_CQ ·2.420. EL CAMINO REAL N 238 92054 TRUCK DRIVER TRAINING 24206 B EL CAMHIO REAL N 372 92024 MATTESON PRINTING 07618 4369275 2752 7 EL CAMINO REAL N 220 92054 EL CAMINO 76 MOBILE 24205 B _ELCAMlNO_R.EAL ti SIE 267 9202.L_HERILREMLlLCAR 12060 .-42~.5.56 75lL_4 __ EL CAMINO REAL STE 324 92024 ENCINITAS YELLOW CAB 10474 7 536044 4121 7 EL CAMINO REAL STE A 119 92024 DENNIS RICHARD MARSHALL 50280 K EL CAMI NO REAL STE A 477 92024 MICHAEL LEE MYERS 50284 K _EL..C.l\MltHLR.EAL SIE A 47] 2.02!t__BilGDAILRiCHARD..11AD.\!ROWICZ 5021. EL CAMINO REAL STEC 2249 92054 UNICORN GLASS 08176 4395292 3231 5 EL CAMINO REAL STEC 477 92024 PETER DANIELE CANCELLIER 50260 K EL CAMINO REAL STE D 274 92024 CHARLES M HULSEY III 50273 K ..ELC.Afil.tlO._REAL SIE E 19.9 9 2.0. 2'i____Ml\_RLALl_C .E_l-lA LS 50296 EL CAMI NO REAL STE E 2508 92008 RAY N MC CLAVE 50037 K EL CAMINO REAL STE E 2508 92008 JAMES MANUEL RODRIGUEZ 50052 K EL CAMINO REAL STE F 205 92024 GARY J BRAUNSTEIN 50254 K ~M1 I1iQ_R EAL SIE E 2!H!8 92QQ~ __ QNE.__HQVIL_QUIILeHQIO U931 ~_137 7395 9 EL CAMINO REAL STE H 2588 92008 ROBERT RYAN REIHM 50051 K EL CAMINO REAL STE H 6353 92008 IRI 09038 4387 540 3599 ·EL CAMINO REAL STE K 2235 92054 EYE GLASS CO 09976 4392212 3851 8 __!;_l__C_AMI NO R!:ALJ.JE 1 7690 92008 JEFFREY WILLIAM TORAASON 50060 K EL CAMINO REAL STE 1 7690 92008 JON LINCOLN MONTAGUE 50038 k-- EL CAMINO REAL STE 1 2525 92008 LORIEN GALLERY 07794 4344434 2755 9 EL CAMINO REAL STE 1 285 92024 DANIEL GEORGE OLIVER 50285 K EL CAMINO REAL STE 1 2525 92008 D_AUTO 12031 4345051 7512 6 EL CAMINO REAL STE 1 7682 92008 THE LA COSTAN 07019 7.53°6344 27il EL CAMINO REAL STE 1 2191 92054 WILL:AM CRISMAN STEVENSON 50693 K EL CAMINO REAL STE 2 285 92024 SCOTT M JORDAN 50274 K EL CAMINO REAL STE 3 317 92024 JAMES HOLTER SINKS 50293 K EL CAMINO REL 156 92°024 DAVID M--SHIELD--50291 K -- EL CAMINO RL 2103 92054 EL CAMINO LABORATORY 22600 B EL CAMINO RL 2281 92054 JONES PARNELL! FIRESTONE 23674 B EL CANTO DR 3885 92077 KRENZ MAREN 51718 L EL CAPITAN DRIVE 45 92011-7•fRESEARCHlDEVELOPMNict,m~--09068 2'67586 359i,--~ EL CERRITO DR 4616 92115 LLOYDS PAINTING SERVICE 15279 4 EL CERRITO DR 4677 92ll5 WARE DIAtlE LEE 52182 L EL DORADO P!SWY. 9041 92021 BROCKWAY AUTO TRANSP. 25628 D -ELFO'EGO ST 16936 920-6.,--RANCHO-s1iNrA--i=E-f'lR0IST A05401-Ktl sm2s 073r-lJ2'24 30-EL FUERTE&P'ALOMAR AP 92008 LOMA GRANDE FARMS H99163 K02 4389580 0000 ------------------- ~H-E__,__48~--4,.,,8'--"0~4_-=0l,.___ ________________ ~Dl;PA8Il'1ENJ._OF__l:IEALnt __ SERVJ.~_E;S ____ .DATE 08/0l/89.____,_PA=G~_,E,,___ _ __,l,,__,l,.___,O'------ HAZARDOUS MATERIALS COMBINED HElO AND HE58 LISTING--STREET NAME ORDER ST NAME ST NO ZIP l:ST NA_ME _____ ____.,ES_T_tj_O __ BUS INA=C,._,_T _ ____,_P__,__,HONE EXP SICl STAT CODE -DATE ENCINITAS BL 2390 92024 RE BADGER & SONS INC H03841 K03 1 7561402 0630 ..ENClN.UAS,,__..Bu.L'""-VA<.D ___ __..l .... 5"-'-4.Q._ ___ ~9202L_SAtLD1.EGUII_Q_T.ROP-.l:l_---=-~--,c------Q86H _______ -----"_,_42.J..Q2...,_l ____ __,.3'-'-4.,__79,,____7 EflCINITAS BLVD 1293 92024 FRANKLYN DENNIS GILE III 50271 K ENCINITAS BLVD 2240 92024 TODD DAVIS MORGAN 50282 K ENCINITAS BLVD 473 92024 EDI--IARD BARTON COFFEY 50262 K ..El!CIJH_TA_SJLYD 1293 9.20_2-4-__CRAl.<LDPNAL.D_fEARS_ON 50286 K __ EIICINITAS BLVD 1317 681 92024 BETH SANDRA FORMAN 50270 K ENCINITAS BLVD STE E 2240 92024 ROBERT W LONGTON 50277 K EtlCINITAS BLVD STE 1 710 92024 PHILIP MICHAEL ENGEL 50266 K .EHCJJHTAS BLV__D_STE 1 511 92Q_2.4__J_fANN.E_JUiO.EH!AN 02I K __ EtlCIIHTAS BLVD STE 1 710 92024 UNIVERSITY LEASING 12125 7532604 7512 7 EIJCINITAS BLVD STE 3 681 92024 JOHN FRANCIS COUGHLIN 50263 K ENCIIUTAS RD 1930 92.069 MJBS PRECIOUS WATER 04851 6 ..Etlc.I.N.UA.LBD 1'115 9.206.9 __ S.HEILCO_lNC 05240 Y EtlCIIHTAS RD 1930 92069 ALLBRITAIN DRAIN SVC 10179 7 EtlCINITAS RD 2388 92024 DENK RANCH H20247 K03 END OF KAYWOOD DR. 92026 VC 12 CHLORINATION STA H28525 K02 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TON DIVISION 21735 8 E.ALDMAILAlRP.OR._LRD 6.65 92.00L_I.EXACO __ REEil:HNCLLMARKEllNG Hl2879 __ K07 .3.a.3.6..5_6___1_23L__l_5.38--9-2._ PALOMAR AIRPORT RD 850 92008 ANDERSON PEASOUP H20085 T75 1231 PALOMAR AIRPORT RD 899 92009 PALOMAR SERVICE Hl2547 KOS 4382141 1231 7538 96 PALOMAR AIRPORT RD 901 92009 7-ELEVEN FOOD STORES H20090 K03 0228 E.ALOJ.1AR.....ALRf.O.RL8D 901 9.2D.0._9__ARC0_1\I0.08Z l296l __ H5 0630 ______ _ PALOMAR AIRPORT RD 2006 92008 PALOMAR AIRPORT H09614 K03 1 4383181 11°30 PALOMAR AIRPORT RD 2016 92008 MOLLER AND SONS H20083 K03 4389377 0630 PALOMAR AIRPORT'RD 2016 92008 AIRMOD INC Hl9289 K04 4389590 1231 01 YA!Jlli.A!L.Al.Rl'Jl.RLR!> 2051 92.JJJHl __ l:i.!lOHES_A_IRC8~fT_GO H09467 KOl 9313000 0131 3679 1 PALOMAR AIRPORT RD 2128 92008 CARLSBAD AVIATION Hlb~8,-ko1 9319618 0531--4!i~--Ol-- PALOMAR AIRPORT RD 2016 92008 AEROSPACE SPECIALTIES, INC. H08463 K04 4382262 0731 3444 01 PALOMAR AIRPORT RD 2186 92008 CINEMA AIR H20084 K03 4380877 0630 7394 _fALOMAR AIRPORT RD 21&6 92008 R W MAIHIN_.IN Hl0603 K04 4385152 0731 4582 01 PALOMAR AIRPORT RD 2188 92008 FLIGHT TRAILS H21742-i<04 4384797 0·531 :PALOMAR AIRPORT RD 2188 92008 AVIONICS AT PALOMAR H21741 KOl 4382686 0430 PALOMAR AIRPORT RD 2192 92008 AIR RESORTS AIRLINES Hl3977 K07 4383600 0228 96 PALOMARAIRPORT RD 2192 9_2_QO&_fl,_IGHT_T.8.~ILS_Hl;J.._I_<;_QE_T_!;R H21740 K04 4388424 0531 PALOMAR AIRPORT RD 2198 92008 PALOMAR AIRPORT Hl0424-K03 5655251-0630,-------- PALOMAR AIRPORT RD 2206 92008 RILEY INTERNATIONAL H21731 KOl 4389089 0430 PALOMAR AIRPORT RD 2210 92008 WESTERN FLIGHT INTL INC Hl3987 K03 4386800 0630 4521 PALOMAR AIRPORT RD C 4218 92008 UKEGAWA BROS INC 04957 7292191 PALOMAR AIRP'i:IRT ROAD 2Di6 92008--RHEY-AIRCRAFT-CORPORATitiN 10609 438-0660-----4-532 PALOMAR AIRPORT ROAD 2121 92008 COLGAN INST NUTRITIONAL SCIENC 13994 4386866 6 PALOMAR AIRPORT RP 92008 GOLDEN BEARS FARM H99062 K02 4382191 0000 PALOMAR DR 1681 92069 STUFFED STUFF 10817 -PALOMAR D-.i-R------,1r;1-1 ~----,92-011--cvtU-iSTAPIDAR 10041-- PALOMAR DR 3664 92028 BJORN HAUGEN H20447 K03 1 7 42001~~7----~3~9~1~1--;,;- 3513617 1130 ------------------- R.E.e.O.R.LJ1.Ql1.9 . ..,._-_,,___._ ________________ _,,,AN_DlEGO_COUNJ..Y ____________________ ~PAGJ; __ JiQ_. __ l8_4__ DEPARTMENT OF HEALTH SERVICES DIVISION OF ENVIRONMENTAL HEALTH SELECTED HAZ-MATERIALS RECORDS LIST C DTVH ) DATE 07/26/89 ESTAB CTL EST-NAME ESTABLISHMENT ADDRESS ESTAB-CITY ST EST-ZIP BUS-CD ~ll-D_~ll-D _____ Ql,lN.ER _______ ---1:.LMAillNG......ADilRfiS MAI L=CUY.~---~SL.MAI l=Z.I~P __ -EX=D .. l-E __ _ MGT co NAME BUS-PHONE DTE-,_A_s-=-su=r-=-=1E=D---,-c=EN:-:-s-u-=s---=-c-0R=P=---..,,.T=R-:--L-cc-R-UNITS AMOUNT STATUS SIC CDS H04977870601H002 HASTE1 461 QTY PRES INSP: 15 GALS AVG ANNUAL QTY: 330 GALS ----------~IucR~TMNILD.IS.f..L.UcOQILl...._ __________ .....,s,:oRAG..E .. L .. .MEJALD.RUMS....S..5_GALLO.N.----------------HAULER: 0490 DISCL: COMM: H0497799999.2..Il.Q01 PAINT CPERY..O PAINT C.OM~ltYJ_ALS.O......S.IDRED.....lN......DM .......... ___________________________ _ CARCINOGEN: QTY AT 1 TIME: 2800 GALS STORAGE: METAL DRUMS,55 GALLONS H.0§97799999.9..D.002 TRAFFIC PAINJ......IlilNNER QTY AT 1 TI ME: 26 5 GALS S TO RA-G=E=--=-M=E=T--:--A L:--::D:-::R:-:-u=M=s-, -=-55=---=G:--:A-:--L--:-L,:-Ol:--:--~s=----------=--:--=--::-:: CARCINOGEN: I-I04977999<1.9..9..DQ03 TAR REMOV..ER......D.::.JA .. _______________________ _ QTY AT 1 TIME: 20 GALS STORAGE: METAL DRUMS 6-110 GALLONS CARCINOGEN: 1 H04977999999D..0.04 KERQS..EN QTY AT 1 TIME: 5=-5=---=G:--:A-:--L--=-s---=s=-=T=-=o--=R7A7G=E-: --=M=E:-=T:--:-A--:-L-D=-:R::-:U-:7M::-::S:-,--=5-=-5-G,:--,A::--:L--:-L--=o..,..,N-=-s-------::--:-,::-=:-:-:-= CARCINOGEN: 1 CARCINOGEN: H04977999999D..005 LIQUID GRfA.S.E....REMO.llfR-1lOY.su...cc=-,..,.........,.,...,,,-,-c---,.........,--=-------------QTY AT 1 TIME: 55 GALS STORAGE: METAL DRUMS,55 GALLONS 1 CARCINOGEN: H04977999999D006 PART CLEANER CHEVRON'=--=----~-----=-----------~--QTY AT 1 TIME: 55 GALS STORAGE: METAL DRUMS 6-110 GALLONS 1 CARCINOGEN: fi.1J4977999999D007 D~ER...2Q..L VEX_tAT_H.OM.LP!../HH.c--<--,c-==----=---~----------QTY AT 1 TIME: 20 GALS STORAGE: METAL DRUMS 6-110 GALLONS 1 CARCINOGEN: H04977999999DO_Q8 Dl;GREAS_ER SOLVEX CAT __ LACOSTA __ LIFT STATION),;--,_.--,--.--,;=------;..-,:;=-...c QTY AT 1 TIME: 20 GALS STORAGE: METAL DRUMS 6-110 GALLONS 1 'H04977999999D009 CHLORENE TABLETS DRY CAT LAKE CALAVERAS HILLS l•lASTEWATER TREATMENT FACILITY) QTY AT 1 TIME: 500 (BS STORAGE: METAL DRUMs;55·--·GALLONS _____ -------------CARClNOGEN=--1---------------- H99158 9 RUEBEN LOPEZ *~**** RUEBEN LOPEZ E PALOMARA!RPORTRD 440 COX RD 726-7741 CARLSBAD CA 92008 SAN MARCOS CA 92069 0 o.oo KIi 00-00 I I I I I I I I I I I I I I I A AnalyticalTechnologies,lnc. Corporate Offices. 5550 Morehouse Drive San Diego, CA 92121 (619) 458-9141 August 7, 1989 Geocon Environmental Consultants 6970 Flanders street San Diego, California 92121 Project No.: 8053-601 Project Name: Carrillo Ranch Attention: Michael Nalley ATI I.D. 907347 on July 27, 1989, Analytical Technologies, Inc. received four soil samples for analyses. The samples were analyzed with EPA methodology or equivalent methods as specified in the attached analytical schedule. The symbol for "less than" indicates a value below the reportable detection limit. Please see the attached sheet for the sample cross reference. The results of these analyses and the quality control data are enclosed. ~/4;~4.4 Carolyn A. Sites GC/MS supervisor "')\0-~t)___\Jy~~~ Richard M. Amano 0 -f:7\_· Laboratory Manager I CAS: lap I I I I I I I I I I I I I I I I I I I I I I A AnalyticalTechnologies,lnc. ANALYTICAL SCHEDULE CLIENT: GEOCON ENVIRONMENTAL CONSULTANTS PROJECT NAME: CARRILLO RANCH ANALYSIS ORGANOCHLORINE PESTICIDES AND PCBs ORGANOPHOSPHORUS PESTICIDES CHLORINATED HERBICIDES TECHNIQUE GC/ECD GC/NPD GC/ECD ATI I.D. 907347 PROJECT NO.: 8053-601 REFERENCE/METHOD EPA 8080 EPA 8140 EPA 8150 1 ~ AnofyticolTechnologies,lnc I CLIE : GEOCON ENV. CONSULTANTS DATE RECEIVED 07/27/89 : 08/07/89 PROJECT# : 8053-601 PROJECT NAME: CARRILLO RANCH REPORT DATE I ATI I.D. : 907347 --------------------------------------------------------------------------- I I I I I I I I I I I I I I I I ATI # CLIENT DESCRIPTION MATRIX DATE COLLECTED -----------------------------------------------------------------------------01 02 03 04 CR-1 CR-2 CR-3 CR-4 MATRIX SOIL @ 6" @ l' @ 6" @ 8 II -----TOTALS----- # SAMPLES 4 SOIL SOIL SOIL SOIL ATI STANDARD DISPOSAL PRACTICE 07/27/89 07/27/89 07/27/89 07/27/89 The samples from this project will be disposed of in thirty (30) days from the date of this report. If an extended storage period is required, please contact our sample control department before the scheduled disposal date. I I A Analytica/Technologies,lnc. GAS CHROMATOGRAPHY -RESULTS ATI I. D. I TEST EPA 8080 (ORGANOCHLORINE PESTICIDES AND PCB'S) 90734701 CLIENT GEOCON ENV. CONSULTANTS DATE SAMPLED 07/27/89 I PROJECT# 8053-601 DATE RECEIVED 07/27/89 PROJECT NAME CARRILLO RANCH DATE EXTRACTED : 07/27/89 CLIENT I.D. CR-1 @ 6" DATE ANALYZED 07/30/89 SAMPLE MATRIX : SOIL UNITS : MG/KG I---------------------------------------------------~=~~==~~-:~:=~~-:_: ______ _ COMPOUNDS RESULTS I~~~;~;------------------------------------------~;~;;~----------------------- ALPHA -BHC I BETA -BHC GAMlYIA-BHC (LINDANE) DELTA -BHC CHLORDANE I P,P 1 -DDD P,P'-DDE p Ip 1-DDT I O,P'-DDD O,P 1 -DDE O,P 1 -DDT I DIELDRIN ENDOSULFAN ENDOSULFAN ENDOSULFAN I II SULFATE I ENDRIN ENDRIN KETONE I HEPTACHLOR HEPTACHLOR EPOXIDE METHOXYCHLOR 7:'OXAPHENE A.ROCLOR 1016 I AROCLOR 1221 AROCLOR 1232 AROCLOR 1242 I .'-lROCLOR 12 4 8 AROCLOR 1254 AROCLOR 1260 I I IJBC (%) I I I SURROGATE PERCENT RECOVERIES <0.005 <0.005 <0.005 <0.005 <0.050 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.005 <0.010 <0.010 <0.010 <0.010 <0.005 <0.005 <0.050 <0.10 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 107 I A AnalyticalTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS I ATI I.D. 90734702 I TEST EPA 8080 (ORGANOCHLORINE PESTICIDES AND PCB'S) CLIENT I PROJECT # PROJECT NAME CLIENT I.D. I SAMPLE MATRIX COMPOUNDS ALDRIN ALPHA -BHC GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-2@ 1 1 SOIL I I BETA -BHC GAMMA-BHC (LINDANE) DELTA -BHC I CHLORDANE P,P'-DDD P,P'-DDE P,P'-DDT I O, P' -DDD O,P'-DDE O,P 1 -DDT I DIELDRIN ENDOSULFAN ENDOSULFAN ENDOSULFAN I II SULFATE I ENDRIF ENDRIN KETONE HEP'rACHLOR I HEPTACHLOR EPOXIDE _vIETE:::XY CHLOR TOXA?BENE A.RO;--:L1)R 1016 AROCLOR 1221 AROCLOR 1232 I I I I I I I ,:i.ROCL:JR 1242 .-:;.Rc:.=:LOR 1248 AROCLOR 1254 AROCLOR 1260 DBC (%) SURROGATE PERCENT RECOVERIES DATE SAMPLED DATE RECEIVED DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS <0.005 <0.005 <0.005 <0.005 <0.005 <0.050 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.005 <0.010 <0.010 <0.010 <0.010 <0.005 <0.005 <0.050 <0.10 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 94 07/27/89 07/27/89 : 07/27/89 07/30/89 MG/KG 1 I I d.hAnalyticalTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS ATI I. D. ITEST EPA 8080 (ORGANOCHLORINE PESTICIDES AND PCB'S) 90734703 CLIENT GEOCON ENV. CONSULTANTS DATE SAMPLED 07/27/89 I PROJECT# 8053-601 DATE RECEIVED 07/27/89 PROJECT NAME CARRILLO RANCH DATE EXTRACTED 07/27/89 CLIENT I.D. CR-3@ 6 11 DATE ANALYZED 07/30/89 SAMPLE MATRIX: SOIL UNITS : MG/KG I---------------------------------------------------~~~~=:~~-:~==~~-:_: ______ _ COMPOUNDS RESULTS I;~~;~~------------------------------------------:;~;;;----------------------- ALPHA -BHC <0.025 BETA -BHC <0.025 I GAMMA-BHC (LINDANE) <0. 025 DELTA -BHC <0.025 CHLORDANE <0.25 I P,P 1 -DDD <0.050 P,P'-DDE 0.30 P,P'-DDT 0.13 I O,P 1 -DDD <0.050 O,P'-DDE <0.050 O, P' -DDT 0.050 I DIELDRIN <0.050 ENDOSULFAN I <0.025 ENDOSULFAN II <0.050 ENDOSULFAN SULFATE <0.050 I ENDRIN <0.050 ENDRIN KETONE <0.050 ~EPTACHLOR <0.025 I HEPTACHLOR EPOXIDE <0.025 YIETHOXYCHLOR <0.25 ·I·GXAPHENE 0.064 I AROCLOR 1016 <0.25 A.ROCLOR 1221 <0.25 AROCLOR 1232 <0.25 AROCLOF 1242 <0.25 I nrtvCLOR 1248 <0.25 AROCLOR 1254 <0.25 AROCLOR 1260 <0.25 I SURROGATE PERCENT RECOVERIES I DBC (%) 66 I I I A AnalyticalTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS I I ATI I.D. 90734704 I TEST: EPA 8080 CLIENT I PROJECT # PROJECT NAME CLIENT I.D. SAMPLE MATRIX (ORGANOCHLORINE PESTICIDES AND PCB'S) GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-4@ 8 11 SOIL DATE SAMPLED DATE RECEIVED DATE EXTRACTED DATE ANALYZED UNITS 07/27/89 07/27/89 07/27/89 07/30/89 I----------------------------------------------------------------------------- DILUTION FACTOR : MG/KG 3 COMPOUNDS RESULTS I----------------------------------------------------------------------------- ALDRIN ALPHA -BHC <0.015 <0.015 <0.015 <0.015 <0.015 <0.15 <0.030 1 BETA -BHC GAMMA-BHC (LINDANE) DELTA -BHC CHLORDANE I P,P 1 -DDD P,P'-DDE P,P'-DDT I O,P!-DDD 0, P' -DOE O,P 1 -DDT DIELDRIN I I ENDOSULFAN ENDOSULFAN ENDOSULFAN I ENDRIN II SULFATE ENDRIN KETONE 3EFTACHLOR I HEPTACHLOR EPOXIDE "METHOXYCHLOR TOXAPHENE AROCLOR 1016 I A.ROCLOR 12 21 AROCLOR 1232 I I I I I I I.OR AROC:i.ivR AROCLOR AROCLOR DBC ( % ) 1242 1248 1254 1260 SURROGATE PERCENT RECOVERIES 0.15 0.067 <0.030 <0.030 <0.030 <0.030 <0.015 <0.030 <0.030 <0.030 <0.030 <0.015 <0.015 <0.15 0.34 <0.15 <0.15 <0.15 <0.15 <0.15 <0 .15 <0.15 102 I A AnolyticolTechnologies,'iii!<.S CHROMATOGRAPHY -RESULTS I REAGENT BLANK TEST: EPA 8080 (ORGANOCHLORINE PESTICIDES AND I CLIENT PROJECT# I PROJECT NAME CLIENT I.D. COMPOUNDS I ALDRIN ALPHA -BHC GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT BLANK I 3ETA -BHC GAMMA-BHC (LINDANE) i)ELTA -BHC I CHLORDANE P,P 1 -DDD P,P 1 -DDE P,P 1 -DDT I O,P'-DDD O,P'-DDE O,P 1 -DDT I DIELDRIN ENDOSULFAN ENDOSULFAN ENDOSULFAN I II SULFATE I ENDRIN SNDRIN KETONE HEPTACHLOR I ~EPTACHLOR EPOXIDE METHOXYCHLOR I I'CXAPHENE ARCr::'.LOR 1016 ,;\ROCLOR 1221 AROCLOR 1232 AROCLOR 1242 I _)..ROCLOR 1248 1254 _\~OCLOR 1260 I I DBC (%) I I I I SURROGATE PERCENT RECOVERIES PCB'S) ATI I.D. DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS <0.005 <0.005 <0.005 <0.005 <0.005 <0.050 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.005 <0.010 <0.010 <0.010 <0.010 <0.005 <0.005 <0.050 <0.10 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 90 907347 07/27/89 07/29/89 MG/KG N/A I I A AnalyticalTechnologies,lnc. QUALITY CONTROL DATA I TEST ATI I. D. EPA 8080 (ORGANOCHLORINE PESTICIDES AND PCB'S) 907347 CLIENT DATE EXTRACTED: I PROJECT# PROJECT NAME REF ::::.D. GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH 90734701 DATE ANALYZED SAMPLE MATRIX UNITS 07/27/89 07/30/89 SOIL MG/KG I----------------------------------------------------------------------------- DUP. DUP. SAMPLE CONC. SPIKED % SPIKED % I~~~:~~~~~--------------------------~~~~=-~:~~~~-~~:~=-~:::~~:~=-~::: ___ ~:~ GAMMA BHC <0.005 0.027 0.033 122 0.035 130 6 I HEPTACHLOR <0.005 0.027 0.028 104 0.028 104 0 ALDRIN <0.005 0.027 0.022 81 0.023 85 4 DIELDRIN <0.010 0.067 0.082 122 0.081 121 1 ENDRIN <0.010 0.067 0.062 93 0.062 93 0 I DDT <0.010 0.067 0.063 94 0.062 93 2 I I I I I I %i Recovery = (Spike Sample Result -Sample Result) ------------------------------------X 100 Spike Concentration I RPD (Relative% Difference) = (Spiked Sample -Duplicate Spike) Result Sample Result I I I I Average of Spiked Sample X 100 I A AnalyticalTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS I I TEST: EPA 8140 (ORGANOPHOSPHORUS PESTICIDES) CLIENT I PROJECT # PROJECT NAME CLIENT I.D. I SAMPLE MATRIX I COMPOUNDS O-DEMETON S-DEMETON I DIAZINON DISULFOTON METHYLPARATHION MALATHION I ETHYL PARATHION ETHION GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-3 @ 6 11 SOIL AZINPHOSMETHYL (GUTHION) I I I I I I I I I I I ATI I.D. 90734703 DATE SAMPLED DATE RECEIVED DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS <0.033 <0.033 <0.033 <0.033 <0.033 <0.066 <0.033 <0.033 <0.17 07/27/89 07/27/89 : 07/28/89 08/02/89 MG/KG 1 AAnalyticalTechnologies,lnc. I I GAS CHROMATOGRAPHY -RESULTS I TEST : EPA 8140 (ORGANOPHOSPHORUS PESTICIDES) I CLIENT PROJECT# PROJECT NAME CLIENT I.D. I SAMPLE MATRIX COMPOUNDS GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-4@ 8 11 SOIL ATI I. D. 90734704 DATE SAMPLED DATE RECEIVED DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS 07/27/89 07/27/89 07/28/89 08/03/89 MG/KG 1 I----------------------------------------------------------------------------- O-DEMETON <0.033 <0.033 <0.033 <0.033 1 S-DEMETON DIAZINON DISULFOTON METHYLPARATHION MALATHION I ETHYL PARATHION ETHION I I I I I I I I I I I AZINPHOSMETHYL (GUTHION) <0.033 <0.066 <0.033 <0.033 <0.17 I I AAnalytica/Technologies,~~s CHROMATOGRAPHY -RESULTS REAGENT BLANK TEST: EPA 8140 (ORGANOPHOSPHORUS PESTICIDES) I CLIENT PROJECT# I PROJECT NAME CLIENT I.D. COMPOUNDS GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT BLANK ATI I.D. DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS 907347 07/28/89 08/02/89 MG/KG N/A 0-DEMETON S-DEMETON I----------------------------------------------------------------------------- <0.033 <0.033 <0.033 <0.033 <0.033 <0.066 <0.033 <0.033 <0.17 I DIAZINON DISULFOTON METHYLPARATHION MALATHION I ETHYL PARATHION ETHION I I I I I I I I I I I I AZINPHOSMETHYL (GUTHION) I I AAnalytica!Technologies,lnc. QUALITY CONTROL DATA ITEST: EPA 8140 (ORGANOPHOSPHORUS PESTICIDES) ATI I.D. 907347 CLIENT GEOCON ENV. CONSULTANTS DATE EXTRACTED 07/27/89 I PROJECT# 8053-601 DATE ANALYZED 07/31/89 PROJECT NAME CARRILLO RANCH SAMPLE MATRIX SOIL REF I. D. REAGENT SOIL UNITS MG/KG I----------------------------------------------------------------------------- DUP. DUP. SAMPLE CONC. SPIKED % SPIKED % I=~~:~~~~~--------------------------~~~~~=-~:=~~~-~~:~~-~~=:~~:~~-~~:: ___ ~:~ DIAZINON <0.017 0.400 0.37 93 0.39 98 5 ·1 METHYL PARATHION <0.017 0.333 0.32 96 0.29 87 10 GUTHION <0.017 0.667 0.87 130 0.90 135 3 I I I I I I I I I I I I ETHYL PARATHION <0.017 0.333 0.29 87 0.27 81 7 % Recovery = (Spike Sample Result -Sample Result) Spike Concentration X 100 RPD (Relative% Difference) = (Spiked Sample -Duplicate Spike) Result Sample Result --------------------------------Average of Spiked Sample X 100 I I AAnalyticalTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS I TEST : EPA 8150 (CHLORINATED HERBICIDES) I CLIENT PROJECT# PROJECT NAME CLIENT I.D. SAMPLE MATRIX GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-3@ 6" SOIL ATI I.D. : 90734703 DATE SAMP~ED DATE RECEIVED DATE EXTRACTED DATE ANALYZED UNITS I----------------------------------------------------------------------------- DILUTION FACTOR 07/27/89 07/27/89 07/31/89 08/02/89 MG/KG 1 COMPOUNDS 1 2,4-D 2,4,5-TP (SILVEX) I DICAMBA 2,4,5-T 2,4-DB DINOSEB I DICHLOROPROP I I I I I I I I I I I RESULTS <0.004 <0.002 <0.004 <0.002 <0.004 <0.004 <0.004 I I A AnolyticolTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS ATI I. D. 90734704 ITEST : EPA 8150 (CHLORINATED HERBICIDES) CLIENT GEOCON ENV. CONSULTANTS DATE SAMPLED 07/27/89 I PROJECT# 8053-601 DATE RECEIVED 07/27/89 PROJECT NAME CARRILLO RANCH DATE EXTRACTED 07/31/89 CLIENT I.D. CR-4@ 8 11 DATE ANALYZED 08/02/89 I SAMPLE_::::: ___ :::~-------------------------------~~~~~:~~-:~==~~---~:~:: __ _ COMPOUNDS RESULTS I;~~=;-------------------------------------------:~~~~~----------------------- 2,4,5-TP (SILVEX) <0.002 I DICAMBA <0.004 <0.002 <0.004 2,4,S-T 2,4-DB DINOSEB DICHLOROPROP I I I I I I I I I I I I <0.004 <0.004 I I AAnolyticolTechnologie$;~S CHROMATOGRAPHY -RESULTS REAGENT BLANK WEST: EPA 8150 (CHLORINATED HERBICIDES) llcLIENT GEOCON ENV. CONSULTANTS PROJECT# 8053-601 IPROJECT NAME CARRILLO RANCH CLIENT I.D. REAGENT BLANK ATI I.D. DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR 907347 07 /31/89 08/02/89 : MG/KG N/A ICOMPOUNDS RESULTS -----------------------------------------------------------------------------2,4-D <0.004 12, 4, 5-TP (SILVEX) <0. 002 DICAMBA <0.004 2,4,5-T <0.002 2,4-DB <0.004 I DINOSEB <0. 004 DICHLOROPROP <0.004 I I I I I I I I I I I I I I AAnalyticalTechnologies,lnc. QUALITY CONTROL DATA ATI I.D. 907347 I TEST: EPA 8150 (CHLORINATED HERBICIDES) I CLIENT PROJECT# PROJECT NAME REF I. D. GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT SOIL DATE EXTRACTED DATE ANALYZED SAMPLE MATRIX UNITS 07/27/89 07/31/89 SOIL MG/KG I----------------------------------------------------------------------------- DUP. DUP. 1 I I I I I I I I I I I I I COMPOUNDS 2,4-D 2,4,5-TP 2,4,5-T 3,, Reccvery SAMPLE CONC. SPIKED % SPIKED % RESULT SPIKED SAMPLE REC.SAMPLE REC. <0.004 0.033 <0.002 0.033 <0.002 0.033 0.036 0.032 0.031 109 0.035 97 0.030 94 0.031 = (Spike Sample Result -Sample Result) ------------------------------------X 100 Spike concentration 106 91 94 RPD (Relative% Difference) = (Spiked Sample -Duplicate Spike) Result Sample Result --------------------------------X 100 Average of Spiked Sample RPD 3 6 0 I I I I I I I I I I I I I I I I I I I th Analytica/Technologies,I nc. ANALYTICAL SCHEDULE CLIENT: GEOCON ENVIRONMENTAL CONSULTANTS PROJECT NAME: CARRILLO RANCH ANALYSIS ORGANOCHLORINE PESTICIDES AND PCBs ORGANOPHOSPHORUS PESTICIDES CHLORINATED HERBICIDES TECHNIQUE GC/ECD GC/NPD GC/ECD ATI I.D. 907377 PROJECT NO.: 8053-601 REFERENCE/METHOD EP.~ 8080 EPA 8140 EPA 8150 I I I I I I I I I I I I I I I A AnalyticalTechnologies,lnc. CLIENT : GEOCON ENV. CONSULTANTS PROJECT# 8053-601 PROJECT NAME: CARRILLO RANCH ATI I.D. : 907377 DATE RECEIVED REPORT DATE 07/28/89 08/07/89 --------------------------------------------------------------------------ATI # CLIENT DESCRIPTION MATRIX DATE COLLECTED ----------------------------------------------------------------------------- ·- 01 02 CR-5@ 1 1 CR-6@ 1 1 MATRIX ------ SOIL -----TOTALS----- # SAMPLES 2 SOIL SOIL 07/28/89 07/28/89 ATI STANDARD DISPOSAL PRACTICE .The samples from this p;~j;~~-;iii-~;-;1;~~;;;-:;-1~-thirty (30) days from the date of this report. If an extended storage period is required, please contact lour sample control department before the scheduled disposal date. I I J&AnalyticalTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS I I I I I I I ATI I.D. 90737701 TEST: EPA 8080 (ORGANOCHLORINE PESTICIDES AND PCB'S) CLIENT PROJECT# PROJECT NAME CLIENT I.D. SAMPLE MATRIX COMPOUNDS ALDRIN ALPHA -BHC GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-5@ 1 1 SOIL I BETA -BHC GAMMA-BHC (LINDANE) DELTA -BHC CHLORDANE P,P 1 -DDD P,P 1 -DDE P,P'-DDT I O,P'-DDD O,P'-DDE O,P'-DDT I DIELDRIN ENDOSULFAN I ENDOSULFAN II I ENDOSULFAN SULFATE ENDRI::-T ENDRIN KETONE HEPTACHLOR HEPTACHLOR EPOXIDE I METEC:•~:.:CHLOR TOXAPEENE I AROCLOR 1016 AROCLOR 1221 AROCLOR 1232 AROCLOR 1242 I ARC•..::LOR 1248 AROCLOR 1254 AROCLOR,1260 I MIREX KEPONE I DBC (%) I I I SURROGATE PERCENT RECOVERIES DATE SAMPLED DATE RECEIVED DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS <0.005 <0.005 <0.005 <0.005 <0.005 <0.050 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.005 <0.010 <0.010 <0.010 <0.010 <0.005 <0.005 <0.050 <0.10 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.010 <0.010 99 07/28/89 : 07/28/89 07 /31/89 08/01/89 : MG/KG 1 AAnolyticolTechnologies,lnc. GAS CHROMATOGRAPHY -RESULTS I I I I I ATI I.D. 90737702 TEST: EPA 8080 (ORGANOCHLORINE PESTICIDES AND PCB'S) CLIENT PROJECT# PROJECT NAME CLIENT I.D. SAMPLE MATRIX COMPOUNDS ALDRIN ALPHA -BHC GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-6@ 1 1 SOIL I I I BETA -BHC GAMMA-BHC (LINDANE) DELTA -BHC CHLORDANE P,P 1 -DDD P,P'-DDE P,P'-DDT I O,P'-DDD O,P'-DDE I O,P'-DDT DIELDRIN ENDOSULFAN ENDOSULFAN ENDOSULFAN I II SULFATE I ENDRIN ENDRIN KETONE HEPTACHLOR I HEPTACHLOR EPOXIDE YIETHOXYCHLOR TOXAPHENE I AROCLOR 1016 AROCLOR 1221 AROCLOR 1232 I AROCLOR 1242 At\UCLOR 1248 AROCLOR 1254 AROCLOR 1260 I MIREX KEPONE I DBC I I I (%) SURROGATE PERCENT RECOVERIES DATE SAMPLED DATE RECEIVED DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS <0.005 <0.005 <0.005 <0.005 <0.005 <0.050 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.005 <0.010 <0.010 <0.010 <0.010 <0.005 <0.005 <0.050 <0.10 <0.050 <0.050 <0.050 <0.050 <0,050 <0.050 <0.050 <0.010 <0.010 100 07/28/89 07/28/89 07/31/89 08/01/89 : MG/KG 1 I I I I AAnalyticalTechnologie5,lncGAS CHROMATOGRAPHY -RESULTS REAGENT BLANK TEST; EPA 8080 (ORGANOCHLORINE PESTICIDES AND CLIENT PROJECT rr PROJECT NAME CLIENT I.D. COMPOUNDS ALDRIN ALPHA -BHC GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT BLANK I I BETA -BHC GAl""vIT-'IA-BHC (LINDANE) DELTA -BHC I CHLORDANE P,P'-DDD I P,P'-DDE P,P'-DDT O,P 1 -DDD O,P 1 -DDE O,P 7 -DDT I DIELDRIN ENDOSULFAN I ENDOSULFAN II I ENDOSULFAN SULFATE ENDRIN ENDRIN KETONE I HEPTACHLOR HEPTACHLOR EPOXIDE METHOXYCHLOR I TOXAPHENE AROCLOR 1016 AROCLOR 1221 AROCLOR 1232 I AROCLOR 1242 ;,RoCLOB. 1248 1254 1260 AROCLOR I AROCLOR JYlIREX KEPONE I I I I I DBC ( % ) SURROGATE PERCENT RECOVERIES PCB'S) ATI I. D. DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS <0.005 <0.005 <0.005 <0.005 <0.005 <0.050 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.010 <0.005 <0.010 <0.010 <0.010 <0.010 <0.005 <0.005 <0.050 <0.10 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.010 <0.010 104 907377 07/31/89 08/01/89 MG/KG N/A I I I I I A AnalyticalTechnologies,I nc. QUALITY CONTROL DATA ATI I.D. 907377 T'EST: EPA 8080 (ORGANOCHLORINE PESTICIDES AND PCB 1 S) CLIENT PROJECT# PROJECT NAME REF I. D. GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT SOIL DATE EXTRACTED DATE ANALYZED SAMPLE MATRIX UNITS 07/31/89 08/01/89 SOIL MG/KG DUP. DUP. I COMPOUNDS SAMPLE CONC. SPIKED % SPIKED % RESULT SPIKED SAMPLE REC.SAMPLE REC. RPD GAMMA BHC <0.005 0.027 0.032 119 N/A N/A I HEPTACHLOR ALDRIN DIELDRIN <0.005 0.027 0.024 89 N/A N/A <0.005 0.027 0.020 74 N/A N/A <0.010 0.067 0.077 115 N/A N/A I ENDRIN P,P'-DDT <0.010 0.067 0.069 103 N/A N/A <0.010 0.067 0,053 79 N/A N/A I I I I I % Recovery = I (Spike sample Result -Sample Result) ------------------------------------X 100 Spike concentration I RPD (Relative% Difference) = (Spiked Sample -Duplicate Spike) Result Sample Result I I I I --------------------------------X 100 Average of Spiked sample N/A N/A N/A N/A N/A N/A A AnalyticalTechnologies,lnc. I I GAS CHROMATOGRAPHY -RESULTS I TEST: EPA 8140 (ORGANOPHOSPHORUS PESTICIDES) I GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH CR-5@ 1 1 ATI I.D. 90737701 DATE SAMPLED DATE RECEIVED DATE EXTRACTED DATE ANALYZED I ----------------------------------------------------------------------------- CLIENT PROJECT# PROJECT NAME CLIENT I.D. SAMPLE MATRIX SOIL UNITS DILUTION FACTOR 07/28/89 07/28/89 07/31/89 08/02/89 MG/KG 1 COMP RESULTS 1 -----------------------------------------------------------------------------0-DEMETON <0.033 <0.033 <0.033 <0.033 <0.033 <0.066 <0.033 <0.033 <0.17 S-DEMETON I DIAZINON DISULFOTON METHYLPARATHION MALATHION I ETHYL PARATHION ETHION AZINPHOSMETHYL (GUTHION) I I I I I I I I I I I I I A AnalyticalTechnologies,I nc. QUALITY CONTROL DATA I TEST: EPA 8140 (ORGANOPHOSPHORUS PESTICIDES) I I CLIENT PROJECT# PROJECT NAME REF I. D. GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT SOIL ATI I. D. DATE EXTRACTED DATE ANALYZED SAMPLE MATRIX UNITS 907377 07/27/89 07/31/89 SOIL MG/KG DUP. DUP. I COMPOUNDS I I I I I I I DIAZINON METHYL PARATHION GUTHION ETHYL PARATHION SAMPLE CONC. SPIKED % SPIKED % RESULT SPIKED SAMPLE REC.SAMPLE REC. <0.017 <0.017 <0.017 <0.017 0.400 0.333 0.667 0.333 0.37 0.32 0.87 0.29 93 96 130 87 0.39 0.29 0.90 0.27 98 87 135 81 k lo Recovery= (Spike Sample Result -Sample Result) X 100 Spike Concentration I RPD (Relative% Difference) = (Spiked Sample -Duplicate Spike) Result Sample Result I I I I --------------------------------X 100 Average of Spiked sample RPD 5 10 3 7 I AAnalyticalTe<hnologies,lnGAS CHROMATOGRAPHY -RESULTS I REAGENT BLANK TEST: EPA 8150 (CHLORINATED HERBICIDES) I CLIENT I I PROJECT# PROJECT NAME CLIENT I.D. COMPOUNDS 2,4-D GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT BLANK 2,4,5-TP (SILVEX) I DICAMBA 2,4,5-T 2,4-DB I DINOSEB DICHLOROPROP I I I I I I I I I I I I ATI I. D. DATE EXTRACTED DATE ANALYZED UNITS DILUTION FACTOR RESULTS <0.004 <0.002 <0.004 <0.002 <0.004 <0.004 <0.004 907377 07/31/89 08/02/89 MG/KG N/A I I AAnalyticalTechnologies,lnc. QUALITY CONTROL DATA ATI I.D. I TEST : EPA 8150 (CHLORINATED HERBICIDES) 907377 I CLIENT PROJECT# PROJECT NAME REF I. D. GEOCON ENV. CONSULTANTS 8053-601 CARRILLO RANCH REAGENT SOIL DATE EXTRACTED DATE ANALYZED SAMPLE MATRIX UNITS 07/27/89 07 /31/89 SOIL MG/KG I -----------------------------------------------------------------------------DUP. DUP. I COMPOUNDS 2,4-D I 2,4,5-TP 2,4,5-T I I I I I I ~ Recovery 0 I = SAMPLE CONC. SPIKED % SPIKED % RESULT SPIKED SAMPLE REC.SAMPLE REC. <0.004 0.033 <0.002 0.033 <0.002 0.033 0.036 0.032 0.031 109 0.035 97 0.030 94 0.031 106 91 94 (Spike Sample Result -sample Result) ------------------------------------X 100 Spike Concentration I RPD (Relative% Difference) = (Spiked Sample -Duplicate Spike) Result sample Result I I I I --------------------------------X 100 Average of spiked sample RPD 3 6 0 ..,;_ ..,:_ ... :.. ,::r: .. .:.. ~ £ l ;~: ':)0--!·1HHllrJ 00+ "J: "f. f!j C:::'.~ • Ot{> ij 1 ~ J ~ § CARLSBAD UNIF SCHOOL DIST 801 PINE A VENUE CARLSBAD CA 92008 SAN DIEGO COUNTY PLANNING 5201 RUFFIN RD STE "B" SAN DIEGO CA 92123 CITY OF CARLSBAD CMWD CITY OF OCEANSIDE 300 NO HILL ST OCEANSIDE CA 92054 FACILITIES FOR CITY CLERK SAN MARCOS SCHOOL DIST 1290 SAN MARCOS BLVD SAN MARCOS CA 92069 CITY OF CARLSBAD ENGINEERING DEPT CITY OF ENCINITAS 505 S VULCAN AVE ENCINITAS CA 92024 CITY OF VISTA PO BOX 1988 VISTA CA 92085 VALLECITOS WATER DIST 788 SAN MARCOS BLVD SAN MARCOS CA 92069 CITY OF CARLSBAD COMMUNITY SERVICES CITY OF SAN MARCOS 105 W RICHMAR AVE SAN MARCOS CA 92069 CALIF DEPT OF FISH & GAME 330 GOLDENSHORE #50 LONG BEACH CA 90802