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ARCHIVED REPORTS_XR0005088
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ARCHIVED REPORTS_XR0005088
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Last modified
9/16/2020 1:42:05 AM
Creation date
3/18/2020 4:03:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005088
RECORD_ID
PR0545571
PE
3528
FACILITY_ID
FA0003570
FACILITY_NAME
BOBS MUFFLER & RADIATOR
STREET_NUMBER
466
STREET_NAME
MOFFAT
STREET_TYPE
BLVD
City
MANTECA
Zip
95336
APN
22104019
CURRENT_STATUS
02
SITE_LOCATION
466 MOFFAT BLVD
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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11 February 2003 <br /> AGE-NC Project No. 98-0520 <br /> ' Page 4 of 21 <br /> detected in any of the soil samples analyzed from boring MW-10. The BTEX compounds <br /> toluene, ethylbenzene and xylenes were detected in soil samples MW-6-35., MW-8-30 and <br /> MW-9-20 at maximum concentrations of 0.093 mg/kg, 0.83 mg/kg- and 0.7 mg/kg, • <br /> respectively, in the sample from MW-9-20. In addition, MTBE was detected at a <br /> concentration of 0.0075 mg/kg in soil sample MW-9-25. <br /> On 25 February 2002, one additional ground water monitoring well (MW-7) was installed on-site <br /> to a depth of 35 feet bsg. A total of 3 soil samples were submitted for analysis. <br /> • No analytes were detected at or above Iaboratory reporting limits in the soil samples <br /> analyzed. <br /> Analytical results of soil and grab ground water samples,and monitoring well ground water samples. , <br /> to date, are summarized in Tables 2 and 3. Cross-sections depicting the general lithology and the <br /> approximate distribution of contaminants in the soil beneath the site are illustrated on Figures 3A, <br /> ' 313,4A and 4B.'Maps depicting the approximate distribution ofTPH-g in soil and dissolved TPH-g <br /> are illustrated on Figures 5 and 6. <br /> The vertical extent of impacted soil and ground water has been defined. The lateral extent has been . <br /> mostly defined, except towards the north/northwest; however, based on soil analytical results at <br /> MW-3, MW-8 and MW-9 (e.g., apparent deeper.contamination at MW-8 versus MW-3 and the <br /> ' presence of MTBE in MW-9), AGE believes that there may be adjacent sites providing or <br /> contributing to the contamination detected in northernmost wells MW-8 and MW-9. <br /> 4.0. SITE CONCEPTUAL MODEL <br /> ' Based on the data collected to date from soil borings and monitoring well installations, AGE has <br /> developed a site conceptual model for the release, migration and distribution of the contaminants <br /> ' in the subsurface as described below: <br /> The shallow stratigraphy is composed of an-upper layer (Layer 1) of between 15.and 20 feet of <br /> ' yellowish to brownish green, generally unconsolidated, fine to medium sand, underlain by an <br /> approximately 15-foot thick clayey silt layer (Layer 2); northwards, Layer 2 appears to transition <br /> .into a sandy silt or silty sand with clay,and beneath former USTs No. 1 and 2,a discontinuous tense <br /> of green to olive gray fine sand was identified nearthe top of Layer 2. The third layer(Layer 3),at <br /> below 35 feet bsg,appears to bean olive green,to brown,unconsolidated coarse to pebbly sand;.this <br /> layer was defined on the basis of the two deepest soil borings(MW-6 and B-1)located at the former <br /> USTs''No. l and 2, respectively (Figure 2). Geologic cross sections are provided in Figures 3A <br />' and 4A. <br /> Advanced GeoEnviron mental,Inc. <br />
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