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c <br /> i <br /> v <br /> A S S O C I A T E S I N C <br /> contained calcium chloride and sodium dichromate chill water solution. Vaults 7 and 8 had 3,000 <br /> and 5,000-gallon capacities, respectively, and were located against the north wall of the processing <br /> f building (Figure 2). All of the vaults were taken out of service and cleaned in June 1990 Weiss <br /> Associates, April 1991). <br /> Several phases of subsurface oil and groundwater investigation <br /> ct <br /> property since December 1988. This work was Performed h by Weiss ave been oA Associatnducted at es (WA)he subjeof <br /> Emeryville,_ California. <br /> The threeound <br /> gr water monitoring wells were constructed to monitor the upper-most water-bearing <br /> zone, which was encountered at a depth of approximately 71 feet below <br /> in each boring. <br /> wells were screened at a minimum f 56 feet and at a maximum of 89 feet etbelow ground surface <br /> The <br /> (bgs). On January 31, 1991, after appropriately developing each well, WA personnel collected <br /> groundwater samples from each well. Samples collected from monitoring wells MW-I and MW-2 <br /> (adjacent to Vaults I and 6, respectively) wereanalyzed by GC/FID for ethylene and Propylene <br /> glycol. The water sample collected from MW-3, adjacent to Vault 8, was analyzed for total soluble <br /> chromium, sodium and calcium (EPA method 6010), hexavalent chromium (EPA method 7196) <br /> and chlorides (EPA method 325.2). All constituents detected were below the California maximum <br /> contaminant level (MCL) or below the EPA secondary standard (aesthetic); with the exception of <br /> total (0.10 milligrams per liter(mg/1)) and hexavalent(0.11 mg/1) chrome in well MW-3. <br /> In order to assess the validity of the MW-3 results for chrome species, a verification round of <br /> sampling was performed in August of 1991 by WA. Water samples were collected from monitoring <br /> well MW-3, and City wells WP-I and WP-2. Each sample was analyzed for total and hexavalent <br /> chromium by Clayton Environmental Consultants. The results indicated both City wells were <br /> below method detection limits for total (0.05 mg/1) and hexavalent (0.01 mg/1) chrome. However, <br /> total and hexavalent chrome levels of 0.07 mg/l were recorded for the MW-3 sample. <br /> In an effort to determine the, significance of the recorded concentration, a quarterly <br /> monitoring/sampling program was implemented to include all three shallow on-site monitoring <br /> wells in addition to the four adjacent City wells. <br /> . Historical monitoring data are included in Appendix A. <br /> 2.0 METHODS AND PROCEDURES <br /> Nine soil borings were advanced using truck mounted Geoprobe® narrow diameter, direct push <br /> technology. Drilling was conducted by Fisch Environmental, California License C57 #683865. <br />. A field geologist will be present to log all soil samples. Descriptions of soil types encountered <br /> and sample collection intervals were recorded on boring logs. Soil samples were collected from <br /> each of the borings at depths of 20 feet and 40 feet bgs and were submitted for laboratory <br /> 4 analysis. <br /> w:lwordpro1625831reportslSuhsurf repwtdoc <br /> 2 <br />