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I <br /> ' INamond Lumber Manteca Quarierty Groundwater Momtortag Page S <br /> pump and tubing from coming into contact with the pavement between sampling each well The <br /> purged water was pumped into 55-gallon drums located adjacent to the three SRK monitoring wells <br /> The drum lids were securely fastened after each well was sampled <br /> Three casing volumes were purged from each of the BEI monitoring wells using dedicated disposable <br /> bailers equipped with nylon cord The purged casing volumes were measured in a calibrated bucket, <br /> then emptied collectively into a 55-gallon drum located near BEI-MW5 The drum lid was securely <br /> fastened after the three BEI wells were sampled <br /> iAfter more than 5 casing volumes were purged from each of SRK monitoring wells, the analytical <br /> groundwater samples were collected from the end of the PVC tubing After more than 3 casing <br /> volumes were purged from the three BEI wells, the analytical groundwater samples were collected from <br /> the tops of the dedicated teflon bailers Analytical water samples from both the SRK and BEI <br /> monitoring wells were preserved in laboratory grade sampling containers The analytical groundwater <br /> samples were placed in a cooler containing additional frozen blue ice packets and shipped following <br /> strict chain-of-custody procedures to a California certified laboratory (ACZ Laboratories) for analysis <br /> These samples were collected after the Ph, temperature and conductivity had stabilized "Stabilized" <br /> is defined as three consecutive readings within 15% of one another Copies of the Geologic Logs and <br /> Monitoring Well construction Diagrams are provided in Appendix C Copies of the purgingisampling <br /> logs are provided in Appendix D <br /> In review of recent correspondence from San Joaquin County PHS, we concur that samples during <br /> future monitor events will be collected using hand bailing techniques following completion of well <br /> purging activities <br /> The analytical parameters include volatile hydrocarbons (by EPA 8015M, GC/FID Purge & Trap), <br /> benzene, toluene, ethylbenzene, and xylene (BTEX) (Aromatics by EPA 60218020, GC/FID Purge & <br /> 1 Trap), and total lead (EPA Method 239 2 GFAA) <br /> ' Ethylenebromide (EDB) was not included in the suite of analytes, because EDB degrades in soil very <br /> rapidly (EDB is converted almost completely within 2 months to ethylene) and also in water, where <br /> it hydrolyzes to ethyleneglycol and bromoethanol (under neutral conditions and ambient temperature <br /> the half-life of the reaction is 5-10 days) <br /> 5 0 ANALYTICAL DATA <br /> Organic and inorganic analyses were performed by ACZ Laboratories (CA Lab #E608) Copies of <br /> the analytical data and chain-of-custody are provided in Appendix E The chain-of-custody clearly <br /> documents that the samples were shipped from California to Colorado and also indicates Sample <br /> Identification ("SRK-MWl-MAN") The top of the chain-of-custody form clearly states the name and <br /> address of ACZ Laboratories in Steamboat Springs, Colorado <br /> �} Table 2 includes all of the available groundwater data for the monitoring wells installed by BEI in 1989 <br /> and SRK in 1991 <br /> �� 32504 22\4 aur Steffen Robertson and Kirsten <br />