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Diamond Lodi,CA-November 1993 Groundwater Monitoring page 4 <br /> noted that the groundwater elevations varied by only a few tenths of feet. Based on calculations using data <br /> during the November 29, 1993, sampling event, the groundwater gradient has a very slight gradient (0.2 <br /> %) in a southerly direction. It should also be noted that the groundwater gradient is extremely flat (the <br /> difference in static groundwater elevations between the highest and lowest point is roughly 0.2%, or <br /> approximately 0.4 feet vertically over 140 feet laterally. Copies of the hand calculations and cross-sections <br /> used in determining the groundwater gradient are provided in Appendix B. <br /> 1 <br /> 4.0 GROUNDWATER SAMPLING <br /> Three casing volumes were purged from each of the SRK monitoring wells using dedicated disposable <br /> bailers equipped with nylon cord. The purged volumes were measured in a calibrated bucket,then emptied <br /> collectively into a 55-gallon drum located in the covered material storage area that extends along the south <br /> wall of the former lumber storage area. The drum lid was securely fastened after the three wells were <br /> rsampled. <br /> The analytical groundwater samples were collected after more than 3 casing volumes were purged from each <br /> well, and the Ph, temperature and conductivity had stabilized. "Stabilized" is defined as three consecutive <br /> reading within 15% on one another. The analytical groundwater samples were collected in laboratory grade <br /> sampling containers and placed in a cooler containing frozen ice and blue ice packets,and shipped following <br /> strict chain-of-custody procedures to a California certified laboratory (ACZ Laboratories) for analysis. <br /> The analytical parameters include volatile hydrocarbons (by EPA 8015 M,GC/FID Purge&Trap), benzene, <br /> toluene, ethylbenzene, and xylene (BTEX)(Aromatics by EPA 60218020, GC/FID Purge &Trap); and total <br /> lead (EPA Method 239.2 GFAA). <br /> Ethylenebromide (EDB) was not included in the suite of analytes, because EDB degrades in soil very <br /> ji rapidly (EDB is converted almost completely within 2 months to ethylene) and also in water, where it <br /> hydrolyzes to ethyleneglycol and bromoethanol (under neutral conditions and ambient temperature the half- <br /> life of the reaction is 5-10 days). <br /> 5.0 ANALYTICAL DATA <br /> ' 5.1 Groundwater Data <br /> Organic and inorganic analyses were performed by ACZ Laboratories (CA Lab #E608). Copies of the <br /> analytical data and chain-of-custody are provided in Appendix C. The chain-of-custody clearly documents <br /> that the samples were shipped from California to Colorado and also indicates Sample Identification ("SRK- <br /> MWI-LODI"). The top of the chain-of-custody form clearly states the name and address of ACZ <br /> Laboratories in Steamboat Springs, Colorado. Copies of the analytical data for the municipal wells are <br /> provided in Appendix D. Copies of the purging logs are provided in Appendix E. <br /> Table 2 includes all of the available groundwater data for the monitoring wells installed by SRK in 1991. <br /> ' 72504,24%-QLdy.Lod Steffen Robertson and Kirsten <br />