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ARCHIVED REPORTS_XR0002600
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545263
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ARCHIVED REPORTS_XR0002600
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Last modified
2/3/2020 7:09:54 PM
Creation date
2/3/2020 10:53:59 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002600
RECORD_ID
PR0545263
PE
3528
FACILITY_ID
FA0005108
FACILITY_NAME
EGGIMANS HYDRAULIC GARAGE
STREET_NUMBER
1112
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
15102101
CURRENT_STATUS
02
SITE_LOCATION
1112 E HARDING WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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(:VYATC <br /> r� A S S O C i A T E 5 I M1i C ` <br /> EPA method 8015 modified, BTEX by EPA method 8021B, and MTBE, TAME, TBA, ETBE, <br /> DIPE, 1,2-DCA, and EDB by EPA method 8260B The analytical results for groundwater <br /> samples are summarized in Table 2 Laboratory data sheets and chain-of-custody documentation <br /> are included in Appendix C <br /> On January 8, 2004, groundwater samples were collected from wells MW 1 through MW7 The <br /> samples were collected after purging a minimum of three well volumes and stabilization of electric <br /> conductivity, pH, and temperature Field purge logs are presented in Appendix D Subsequent to <br /> purging, groundwater was sampled and transferred to appropriate sample containers, using clean, <br /> disposable bailers with bottom emptying devices to reduce volatilization <br /> Groundwater samples were placed on ice and delivered under chain-of-custody documentation to <br /> Argon Laboratories for chemical analysis Groundwater samples were analyzed for TPHg by EPA <br /> method 8015 modified, BTEX by EPA method 802113, and MTBE, TAME, TBA, ETBE, DIPE, <br /> 1,2-DCA, and EDB by EPA method 8260B The analytical results for groundwater samples are <br /> summarized in Table 2 Laboratory data sheets and chain-of-custody documentation are included <br /> in Appendix C <br /> 3.0 SUBSURFACE CONDITIONS <br /> 3.1 Geoloev <br /> Soil from the borings generally consisted of silts and clays from the surface to 45 feet bgs Soil <br /> consisted of silty sand and sand from depths between 45 to 55 feet bgs <br /> Soil from the CPT boring was classified as alternating layers of stir fine grained soil, silty clay and <br /> clayey soils from approximately 5 feet to 50 feet bgs From approximately 50 to 55 feet bgs the <br /> soil was classified as cemented sand and sandy silt From approximately 55 to 100 feet the soil <br /> was classified as alternating layers of stiff fine grained soil and clayey soil <br /> Soil boring logs with a detailed description of soil types are contained in Appendix B The CPT <br /> report is contained in Appendix A <br /> 3_2 Hydrogeology <br /> Fluid levels were taken on January 8, 2004, utilizing an electronic water probe capable of <br /> measuring with an accuracy of 11100 of a foot Groundwater elevation data are presented in <br /> Table 2 Water levels ranged from 44 12 to 46 70 feet below the tops of the well casing <br /> elevations The water level data were used to develop the groundwater elevation contour map <br /> (Figure 3) Assuming that horizontal isotropic conditions prevail, groundwater in the uppermost <br /> aquifer beneath the site flowed towards the east-northeast The average hydraulic gradient on <br /> r� January 8, 2004 was calculated to be 0 0007 ft/ft or approximately 3 8 ft/mile A summary of <br /> groundwater monitoring data is presented in Table 1 <br /> SIEnviromental\224931REPORTSLsumni doe 5 <br />
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