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California Regronal Water Quality CMitrol Board f :�,: <br /> \� Central Valley Region ' M:. <br /> Robert Schneider,Chair Gray Davis <br /> Winston H.Hickox Sacramento Main OGovernor <br /> Secreraryfor Office <br /> Environmental Internet Address: http://www.swrcb.ca.gov/rwgcb5 <br /> Protection 3443 Routier Road,Suite A,Sacramento,California 95827-3003 <br /> Phone(916)255-3000-FAX(916)255-3015 <br /> 15 May 2002 Z G 1 A s a L 1 ` <br /> Tony Arnaiz <br /> Central Valley Construction <br /> PO Box 830 <br /> Lathrop, CA 95330 <br /> RF.VIEW OUARTERLYMONITORING AND ADDITIONAL CHARACTERIZATION REPORT, <br /> CENTRAL VALLEY CONSTRUCTION, 146 ALO ROAD,LATHROP,SANJOAOUIN COUNTY <br /> I reviewed the 20 April 2002 Quarterly Monitoring and Additional Characterization Report(Q1-2002 Report) <br /> submitted by John Cummings&Associates(JCA) on behalf of Central Valley Construction. The Q1-2002 <br /> Report presents monitoring and sampling data for three monitoring wells and one domestic well, a 2,000 foot <br /> well receptor survey, and the results of push probe soil sampling near the former above ground storage tank <br /> (AGT) area to define the extent of soil contamination. <br /> The three on-site monitoring wells and the on-site domestic well were sampled on 11 March 2002. The depth to <br /> water was approximately 12 feet below ground surface, and the groundwater flow direction was to the northwest <br /> at 0.002 feet/foot. The water samples were analyzed for total petroleum hydrocarbons as gasoline(TPHg) and <br /> diesel(TPHd),benzene,toluene, ethyl benzene,total xylenes(BTEX), and fuel oxygenates and fuel additives. In <br /> addition, all four water samples were also analyzed for lead by EPA Method 200.7, and a full suite of volatile <br /> organic compounds by EPA Method 8260B. This was the second sampling event for the on-site monitoring wells <br /> that were installed in November 2001. The on-site domestic well noted as"POT W"in JCA's Q 1-2002 Report <br /> was non-detect for all constituents, and only TPHd was identified in monitoring wells MW-1 and MW-2 at a <br /> maximum of 100 micrograms per liter(µg/l). Based on the results of the Q4-2001 and the Q1-2001 monitoring <br /> events,you may discontinue analyzing water samples for fuel oxygenates,lead, and volatile organic compounds. <br /> The results of the well receptor survey identified 23 water supply wells within 2,000 feet of the site. The wells <br /> are mostly domestic water supply for individual residences along Klo Road. The wells are completed with six to <br /> eight inch diameter PVC or steel casing with a total depth ranging from 80 to 233 feet. The depth of the sanitary <br /> well seals for each well was not available to JCA, and therefore,not reported. Besides the on-site domestic well, <br /> the nearest water supply well is approximately 150 feet north and down gradient of the former underground <br /> storage tank and AGT areas. <br /> On 11 March 2002,JCA completed five push probe soil borings near the former AGT area to define the lateral <br /> and vertical extent of soil contamination. (Previous soil samples collected in the AGT area during excavation <br /> activities identified TPHg at 1.5 milligrams per kilogram(mg/kg), and TPHd ranging from 3.9 to 450 mg/kg.) <br /> Starting at ten feet, soil samples were collected at five-foot intervals to a total depth of 30 feet. All soil samples <br /> were analyzed for TPHg,TPHd, and BTEX constituents, and all soil samples were non-detect for all constituents <br /> California Environmental Protection Agency <br /> �a Recycled Paper <br /> The energy challenge facing California is real. Every Californian needs to take immediate action to reduce energy consumption. <br /> For a list of simple ways you can reduce demand and cut your energy costs,see our Web-site at http://www.swrcb.ca.gov/rwgcb5 <br />