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ARCHIVED REPORTS_SITE CONCEPTUAL MODEL 2009
Environmental Health - Public
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2900 - Site Mitigation Program
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ARCHIVED REPORTS_SITE CONCEPTUAL MODEL 2009
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Last modified
2/5/2020 2:25:32 PM
Creation date
2/5/2020 10:56:03 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
SITE CONCEPTUAL MODEL 2009
RECORD_ID
PR0009051
PE
2960
FACILITY_ID
FA0000649
FACILITY_NAME
FORMER NESTLE USA INC FACILITY
STREET_NUMBER
230
STREET_NAME
INDUSTRIAL
STREET_TYPE
DR
City
RIPON
Zip
95366
APN
25938001
CURRENT_STATUS
01
SITE_LOCATION
230 INDUSTRIAL DR
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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amec- <br /> 3.1.3 <br /> Detections of COCs in Plant Production Wells <br /> Nestle collected groundwater samples from production wells N-1 and N-2 for analysis of VOCs <br /> in January 1986. The sample from well N-1 was reported to contain the following VOCs <br /> (RUST, 1994a): <br /> • TCE at a concentration of 638 micrograms per liter (pg/L) <br /> • Trans-1,2-dichloroethene at a concentration of 2.5 pg/L <br /> • Tetrachloroethene (PCE) at a concentration of 0.1 pg/L <br /> • Chloroform at a concentration of 0.5 pg/L <br /> With the exception of 1,2-dichloroethane (1,2-DCA)which was not detected at the unspecified <br /> detection limit; no other VOCs were analyzed. The sample from N-2 was also reported to <br /> contain VOCs, but these results were not published in RUST (1994a). <br /> After detecting VOCs in the sample from well N-1, the well was not operated until a granular <br /> activated carbon (GAC) treatment system was installed for removing VOCs from groundwater <br /> pumped from N-1 prior to TDS treatment. Well N-1 was restarted in June 1986 and pumped at <br /> a rate of approximately 140 — 150 gpm for plant use until the plant closed in late 1994. <br /> 3.1.4 Remedial Investigations <br /> After VOCs were reported in the groundwater sample from N-1, six phases of remedial <br /> investigations were completed: <br /> • Phase 1 (1986): seven monitoring wells (M-1 A, M-1 B, M-2A, M-213, M-3A, M-313 <br /> and M-4) and three vapor/groundwater extraction wells (VE-1, VE-2, and VE-3) <br /> were installed onsite (Figure 3). The highest COC concentration reported for <br /> samples from these wells in January 1987 was 7,100 pg/L for TCE from well M-1A <br /> (constructed with screen from 101 — 121 feet bgs); TCE concentrations ranged <br /> from non-detect to 52 pg/L in groundwater samples from the other monitoring wells. <br /> • Phase 2 (1987): A soil vapor survey was conducted that included collecting 63 soil <br /> gas samples (presumably at a depth of five feet bgs although the depth was not <br /> reported in RUST, 1994b) at different locations onsite and offsite for analysis of <br /> TCE, trichloroethane (TCA) and PCE with a mobile gas chromatograph. The major <br /> COC detected was TCE with the highest concentration reported at 54 lag/L near a <br /> location "where TCE was handled and used", near the former Decaffeination <br /> Building, and 6 lag/L, west of the Decaffeination Building, near Industrial Avenue. <br /> Four offsite monitoring wells (M-5A, M-513, M-9A and M-913) and two onsite vapor <br /> extraction wells (VE-4 and VE-5) were installed. A groundwater sample was <br /> collected from vapor extraction well VE-4 and reported to contain TCE at a <br /> concentration of 2,100 lag/L; VE-4 is near the north side of the Decaffeination <br /> Building. TCE was not detected in the groundwater sample from VE-5 near the <br /> AMEC Geomatrix, Inc. <br /> hDoc_Safe\9000s\9837.005\4000 REGULATORY\SCM_01.30.09\1_text\SCM Report Final.doc 10 <br />
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