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ARCHIVED REPORTS_XR0008225
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ARCHIVED REPORTS_XR0008225
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Last modified
6/18/2020 12:53:33 PM
Creation date
6/18/2020 12:22:33 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008225
RECORD_ID
PR0504943
PE
2951
FACILITY_ID
FA0004032
FACILITY_NAME
AMERICAN MOULDING & MILLWORK (FRMR)
STREET_NUMBER
2801
STREET_NAME
WEST
STREET_TYPE
LN
City
STOCKTON
Zip
95204
APN
11709001
CURRENT_STATUS
02
SITE_LOCATION
2801 WEST LN
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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CLOSURE REQUEST REPORT Section No 3 0 <br /> Former American Forest Products Company 07/31/01 <br /> 2801 West Lane Page 3-6 <br /> Stockton,California <br /> i <br /> TPHd has been reported in groundwater samples at a maximum concentration of 440 micrograms per liter <br /> (ltg/L) (DMW-6, 1115/00) Positive identification of diesel has been Iimited to samples collected at <br /> DMW-6, based on laboratory comparison with diesel standard chromatograms Unknown hydrocarbon <br /> has been reported sporadically at all seven monitoring wells at concentrations up to 780 µg/]L Analytical <br /> laboratories have attributed the unknown hydrocarbon to weathered diesel, primarily for samples from <br /> DMW-7 and DMW-6 At other wells, the detections of unknown hydrocarbon have been attributed to <br /> naturally-occurring organic compounds <br /> In order to investigate the nature of the unknown hydrocarbon, a split sample from DMW-3 was analyzed <br /> in November 1999 using the silica gel cleanup method, which can eliminate non-petroleum hydrocarbons <br /> The original sample from DMW-3 analyzed with EPA Method 8015M without the silica gel cleanup had <br /> a reported concentration of 170 pg/L No hydrocarbons were reported in the same sample analyzed with <br /> the silica gel cleanup method, suggesting that a significant portion of the hydrocarbons reported in <br /> groundwater at the site may be derived from naturally-occurring hydrocarbons, unrelated to the TPHd <br /> impacts <br /> The effects of well screen depths have been assessed using two sets of well clusters DMW4/DMW-7, <br /> and DMW-5/DMW-6 The new wells were installed immediately adjacent to the corresponding wells to <br /> allow for the collection of groundwater samples from the water table interface, and from the depths below <br /> the water table surface The sampling was required due to rising water levels that submerged the well <br /> screens in the original wells Comparison of results for the clustered wells suggests that samples <br /> . collected from below the water-table interface have lower TPH concentrations, indicating that <br /> groundwater impacts are concentrated at the interface, and that dissolved TPH impacts are minimal <br /> Monitoring wells DMW-6 and DMW-7 were installed near the centers of the soil impacts Therefore, <br /> TPHd concentrations would be expected to be highest at these wells Analytical data from these two <br /> wells indicates that diesel (primarily weathered) is present in groundwater collected at the water-table <br /> interface TPH is consistently detected, but concentrations are variable and range from 74 }tg/L to 780 <br /> lam <br /> Groundwater monitoring for TPHd has not indicated the presence of a well-defined plume that can be <br /> consistently mapped between sampling events Time-series graphs presenting concentrations of TPHd <br /> over time for site monitoring wells are included in Appendix B These graphs were prepared to evaluate <br /> temporal trends in the TPHd concentrations Increasing or decreasing TPHd concentrations correlating to <br /> rising groundwater levels are not apparent The single TPH detection prior to 1998 was reported at <br /> DMW4 in 1995 (180 pg/L) The highest TPH concentration reported at DMW-4 after 1998 is 190 Lig/L, <br /> indicating that an increase in groundwater TPH concentrations due to rising groundwater levels is not <br /> apparent <br /> In addition to TPHd, groundwater samples have also been analyzed for TPHg, BTEX, VOCs, SVOCs, <br /> and fuel additives Results indicate that groundwater has not been impacted by TPHg, BTEX, or SVOCs <br /> VOCs detected are limited to 1,2-DCA, carbon tetrachloride, and chloroform Repeated analysis for 1,2- <br /> DCA indicates that it is only present in a localized area centered at DMW-5 and DMW-6, and extending <br /> to DMW-2 <br /> Groundwater samples were collected and analyzed for fuel additives in August and November 2000 Fuel <br /> additives included ethanol, methanol, t-butanol, 1,2-DCA, tert-amyl methyl ether, tert-butyl ethyl ether, <br /> isopropyl ether,and methyl tert-butyl ether The only fuel additive detected was 1,2-DCA <br /> K 18401%fp`afp_closure_rpt doc <br />
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