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ARCHIVED REPORTS_XR0007947
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0542364
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ARCHIVED REPORTS_XR0007947
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Last modified
5/4/2020 3:51:13 PM
Creation date
5/4/2020 3:12:47 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007947
RECORD_ID
PR0542364
PE
2960
FACILITY_ID
FA0024340
FACILITY_NAME
PACIFIC CAR WASH
STREET_NUMBER
4405
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
11024014
CURRENT_STATUS
01
SITE_LOCATION
4405 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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19 January 1998 <br /> AGE-NC Protect No 96-0229 <br /> Page 4of8 <br /> relative ground water elevations were calculated by subtracting the depth to ground water from the <br />' surveyed casing elevations (Table 2) Ground water elevations were plotted and contoured on a <br /> scaled site map (Figure I i - Relative Ground Water Elevation Map) <br /> After water levels were measured, a minimum of three well volumes of ground water was purged <br /> from MW 1 through MW6 utilizing a two-stage submersible pump Temperature, pH and <br /> conductivity were measured at regular intervals utilizing an ICM model 52200 water analyzer to <br />' track stabilization of produced water Dissolved oxygen was measured at each well using a YSI <br /> Model 55 Dissolved Oxygen Meter following stabilization of the produced water Stabilization data <br /> and field logs are contained in Appendix C Dissolved oxygen field measurements are summarized <br />' in Table 3- Summary of Dissolved Oxygen Measurements Purged ground water was stored in 55- <br /> gallon drums on-site in an area lacking public access <br />' Monitoring wells MW I through MW6, VW-I were allowed to recover for a minimum of one hour <br /> prior to sample collection Ground water samples were collected from each well utilizing a new, <br />' dedicated, disposable polyethylene bailer and new nylon rope Sufficient sample was collected from <br /> each well to fill three 40-m1 EPA vials containing 0 5 ml 18%hydrochloric acid as a preservative <br /> Care was taken to ensure that visible air bubbles were not present in the VOAs after filling and <br /> capping Ground water sample containers were labeled with the well designation, date, time, and <br /> samplers initials <br /> Following collection, each sample was logged on a chain-of-custody form. placed in a chilled <br /> container and transported to Castle Analytical Laboratories (CAL), a California state-certified <br /> laboratory for analysis by EPA Method 8015-m for TPH-g, by EPA Method 8020 for BTE&X with <br /> MTBE, and by EPA Method 8260 for TBA, DIPE, ETBE, TAME, and to confirm and quantify <br /> MTBE if detected by EPA Method 8020 The results of the analysis are contained in Table 4 - <br /> Analytical Results Of Ground Water Samples <br /> 1 <br />' 25 COLLECTION OF STOCKPILE SOIL SAMPLES <br /> On 17 December 1997, two soil samples were collected from MW1 through MW6 stockpiled soil <br /> cuttings utilizing a slide-hammer and brass sleeves under the supervision of the PHS-EHD The <br /> stockpile soil samples were submitted to Castie Analytical Laboratories fui oiie coiiipV—s,tc analysis <br /> of TPH-g, BTEX and MTBE in accordance with above mentioned EPA methods Analytical results <br />' of the composite soil sample analysis are summarized in Table 1 The laboratory report (Castle <br /> Analytical Laboratory Reference No 1378) and chain-of-custody are included in Appendix D <br /> Advanced GeoEnvironmenlai,Inc <br />
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