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ARCHIVED REPORTS XR0009295
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2900 - Site Mitigation Program
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PR0544690
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ARCHIVED REPORTS XR0009295
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Last modified
7/24/2019 1:21:42 PM
Creation date
7/24/2019 1:00:50 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009295
RECORD_ID
PR0544690
PE
3528
FACILITY_ID
FA0005839
FACILITY_NAME
CASTLE AUTOMOTIVE REPAIR INC.
STREET_NUMBER
2315
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95204
APN
12510017
CURRENT_STATUS
02
SITE_LOCATION
2315 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Geolagccal7ecicxlcslnc Page 10 <br /> Site Conceptual Model Report(2006 Revision) <br /> Valentine(Castle Motors) <br /> Project No 723 2 <br /> .lune 16,2006 <br /> ' 2.5 Contaminant Distribution <br /> ' 25.1 Vadose Zone <br /> Figures 7 & 8 illustrate the soil and April 17, 2006 groundwater contaminant distribution as <br /> ' superimposed on cross sections A - A' and B —B' <br /> In order to define the TPH-G distribution in soil, GTI divided the subsurface into two zones - <br /> ' shallow (0 - 25 feet bgs) and deep (25 - 60 feet bgs) <br /> The rationale for choosing 25 and 60 feet bgs as the zone limits is as follows <br /> ' . The only vadose zone samples to contain detectable TPH-G came from boring SB-B <br /> located adjacent to the former dispenser island The on-site wells contained <br /> contamination in the water table smear zone as groundwater fluctuated between 25 — <br /> ' 43 feet bgs in the 1995 — 2006 period (as depicted in Figure 9) The impacted shallow <br /> zone is that area between the detection points in SB-B and half the distance to wells <br /> MW-2 and MW-3 that are the closest non-detect points- see Figure 10 for the lateral <br /> extent of the shallow soil plume The zone is centered on the dispenser island that is <br /> the presumed source of the release <br /> • The highest concentration of detected TPH-G was in boring SB-B but below the water <br /> Mtable- 13000 mg/kg TPH-G at 31 feet bgs Adjacent wells MW-2 and MW-3 also <br /> contained high levels of contamination to depths of 55 feet bgs The high levels <br /> present in this zone appear to stop at the 44 mg/kg concentration detected in 67 feet <br /> ' bgs in boring MW-101 The TPH-G levels attenuate further in SB-201 and MW-201 <br /> below this depth It appears that as the contamination migrated downward toward the <br /> sandy zone present beneath the site at 60 — 75 feet it was diluted and transported <br /> ' laterally due to higher hydraulic conductivity of the sandy zone- see Figure 11 for the <br /> lateral extent of the deep soil plume <br /> ' a The vadose zone samples from off-site boreholes MW-7 & MW-9 were non-detect <br /> for TPH-G <br /> • The soil plume is not shown extending to the soil contamination in boring MW-8 at <br /> ' 30 feet bgs because the adjacent site has had a documented gasoline release <br /> • The vadose zone samples from down gradient off-site boreholes CPT-1, CPT-2 and <br /> CPT-3 were non-detect for TPH-G <br /> 2.5.2 Groundwater <br /> ' As stated above, the site's monitoring wells have been grouped according to the aquifer <br /> interval that the screened section intercepted (see Figure 5 for well screen intervals) <br /> ' Shallow Wells (screened 35 —55 feet bgs) MW-4, 5, 6, 7, 8 & 9 <br /> Intermediate Wells (screened 43 —70 feet bgs) MW-1, 2, 3, 107, 108 & 109 <br /> Deep Wells (screened 76— 80 feet bgs) MW-207, 208 & 209 <br /> Deepest Wells (screened 94—97 feet bgs) MW-101, 307, 308 & 309 <br />
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