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PR0505721
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Last modified
5/18/2020 3:35:05 PM
Creation date
5/18/2020 3:22:23 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0505721
PE
2960
FACILITY_ID
FA0012938
FACILITY_NAME
MONIER LIFETILE LLC
STREET_NUMBER
342
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95213
APN
19603002
CURRENT_STATUS
01
SITE_LOCATION
342 ROTH RD
QC Status
Approved
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EHD - Public
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Limited Groundwater Investigation 9 <br /> 5.0 DISCUSSION OF RESULTS <br /> This section presents a discussion of the results and how they compare to the water quality goals. <br /> 5.1 Lathrop Facility <br /> Groundwater samples collected from two of the five sample locations at the Lathrop facility <br /> contained detectable levels of dissolved Cr VI (above the method detection limit [MDL]) at <br /> concentrations greater than the PHG of 0.2 µg/L. The highest dissolved Cr VI concentration <br /> (10 µg/L) found at LP-G2 is less than the concentrations reported previously for the stockpile <br /> extracts DIWET and storm water samples (Brown and Caldwell,April 2001) with the exception of <br /> one stockpile extract (9.5 µg/L) out of a total of 20 stockpiles samples analyzed at Lathrop. A <br /> summary of these data are provided below: <br /> EPA 6010 <br /> dissolved <br /> Range in /L EPA 7199 dissolved Cr VI EPA 6010 total Cr Cr <br /> Grab Groundwater <0.2—10(') 55—860(6)w/one @ 2100 2.3J—16(b) <br /> Stockpile DIWET Extracts (March 2001)(`) 9.5-39.8 12-49 ---(d) <br /> Storm Water(February&March,2001)() 28-144 44-150 28- 150 <br /> (') Two detections out of five samples.Duplicate sample results are included. <br /> (b) Detected in all five samples. <br /> (`) Brown and Caldwell,April 2001. <br /> (d) Stockpile extracts were not assessed for dissolved Cr. <br /> Dissolved Cr VI was not detected by EPA Test Method 7196 in any of the groundwater samples <br /> collected at Lathrop, due to the higher MDLs (8 µg/L) reported for Test Method 7196. <br /> Total Cr and dissolved Cr were detected in all samples collect at Lathrop at concentrations above <br /> the PHG of 2.5 µg/L, except for dissolved Cr at two sample locations (1'P-G3 and LP-G5). In most <br /> cases, the total Cr concentrations were several orders of magnitude greater than the dissolved Cr <br /> concentrations (except at LP-G5). The highest concentration of total and dissolved Cr was detected <br /> in the duplicate sample of LP-G1, located west of the southern stockpile between the southern <br /> stockpile and the fire retention pond (Figure 3). The total Cr levels reported in groundwater were <br /> several orders of magnitude greater than the previously reported stockpile extracts DIWET and <br /> storm water samples (Brown and Caldwell,April 2001). The dissolved Cr levels found in <br /> groundwater were lower than the previous storm water sample results (Brown and Caldwell,April <br /> 2001). <br /> The high total Cr levels observed in the grab groundwater samples (up to 2,100 µg/L at Lathrop) <br /> may be attributed to the suspended soil observed in the samples at the time of collection (samples <br /> were turbid at the time of collection). In San Joaquin County soil background levels for total Cr <br /> have been reported between 26 and 49 mg/kg (Bradford, et al., March 1996). Typically a 10 times <br /> (10X) and/or 20 times (20X) rule thumb is applied to total metal concentrations to estimate the <br /> expected leachate or extract concentration. To make a comparison between the total Cr <br /> groundwater concentrations observed during this investigation and the reported background values <br /> (mg/kg), the 10X and 20X rule of thumb was applied to the maximum total Cr concentration <br /> detected at the facility. As such, the estimated soil concentrations may be up to 21 mg/kg using the <br /> PAwp\jobs\20587\LP_FCG1X'.doc—DCN 102300 June 2001 <br />
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