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2900 - Site Mitigation Program
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PR0516935
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Last modified
2/21/2020 4:23:10 PM
Creation date
2/21/2020 1:37:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0516935
PE
2960
FACILITY_ID
FA0012937
FACILITY_NAME
MONIER LIFETILE LLC
STREET_NUMBER
9508
Direction
S
STREET_NAME
HARLAN
STREET_TYPE
RD
City
FRENCH CAMP
Zip
95231
APN
19321003
CURRENT_STATUS
01
SITE_LOCATION
9508 S HARLAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Geomatrix <br /> compounds were below the soil screening level of 10 mg/l for TPHd (e.g. water quality goal of <br /> 0.100 mg/l multiplied by an attenuation factor of 1000) and 0.050 mg/1 for Cr and Cr VI (e.g., <br /> the Maximum Contaminant Level [MCL] for Cr). As noted in the FS/RO report, broken roof <br /> tile material was observed in shallow soil at boring LPW-3. <br /> At French Camp,THPd was detected at concentrations of 39 and 51 mg/kg in two shallow soil <br /> samples collected from a depth of 1 and 2.5 feet bgs, respectively, at boring FCW-1. The <br /> highest concentrations of total Cr(13 mg/kg) and Cr VI (0.010 mg/kg)were detected in soil <br /> samples from a depth of 15 feet bgs from boring FCW-3 and from a depth of 27 feet at boring <br /> FCW-2, respectively. The highest concentration of extractable Cr VI (0.0018 mg/1)was <br /> detected in a soil sample collected from a depth of 5 feet bgs at boring FCW-2. The extractable <br /> soil concentrations of Cr VI were below the soil screening level of 0.050 mg/l. Extractable <br /> concentrations of TPHd and total Cr were not detected in the shallow soil samples collected at <br /> depths of 1 and 5 feet bgs. <br /> In order to further assess the leaching potential of TPHd, Cr, and Cr VI in soil adjacent to the <br /> stockpiles, a vadose zone soil investigation was conducted under an approved Work Plan <br /> entitled Vadose Zone Investigation Work Plan (Brown and Caldwell, February 2002 and <br /> March 2002 Addendum). As part of the vadose zone investigation, three shallow borings were <br /> advanced to a depth of 10 feet bgs around the perimeter of each stockpile at locations between <br /> the groundwater monitoring wells. The boring locations are shown on Figures 2 and 3. Soil <br /> samples were collected at a depth of 1, 2.5, and 5 feet bgs and these samples were analyzed for <br /> extractable concentrations of TPHd, Cr, and Cr VI using the DIWET method. Analysis of the <br /> 10-foot soil samples were based on the findings of the 5-foot samples at four boring locations <br /> (LP-G6, LP-111, FC-G6, and FC-G7). A summary of the reported results and test methods is <br /> provided below: <br /> Concentration of Soil Extracts(mg/1) TPHd Cr Cr VI <br /> DIWET Method (EPA Method (EPA Method 6010) (EPA Method <br /> 8015M) 7199) <br /> Lathrop <0.05—2.7 <0.01—0.03 <0.0005—0.0019 <br /> French Camp <0.05—0.16 <0.01—0.02 <0.0005—0.0071 <br /> At Lathrop, extractable concentrations of TPHd were detected in two soil samples collected <br /> from a depth of 1 and 2.5 feet bgs at boring LP-H1 at concentrations of 0.67 to 2.7 mg/l, <br /> respectively. At French Camp, extractable concentrations of the TPHd were detected in one <br /> PAI 0626.000.O\Docs\MLT Soil Work Plan.doc 3 <br />
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