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Diamond Lumber Manteca Quarreriy Groundwater Monitonng -, Page 6 <br /> The analytical groundwater samples were collected from the end of the PVC tubing (SRK monitoring <br /> wells) and from the tops of the teflon bailers (BEI monitoring wells) and poured directly into <br /> laboratory grade sampling containers These samples were collected after the Ph, temperature, and <br /> conductivity had stabilized "Stabilized" is defined as three consecutive readings within 15% of one <br /> another Copies of the Field Groundwater Purging/Sampling Logs are provided in Appendix A. <br /> +� Copies of the Geologic Logs and Monitoring Well Construction Diagrams are provided in <br /> ® Appendix B <br /> The analytical parameters include volatile hydrocarbons (by EPA 8015M, GC/FID Purge & Trap), <br /> benzene, toluene, ethlybenzene, and xylene (BTEX) (Aromatics by EPA 602/8020, GC/PID Purge <br /> & Trap), and total lead (EPA Method 239 2 GFAA) The analytical groundwater samples were <br /> placed in a cooler containing additional frozen blue ice packets and shipped following strict chain-of- <br /> custody procedures to a California certified laboratory (ACZ Laboratories) for analysis <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) SRK requested further guidance and justification from Ms <br /> Margaret Lagorio, Senior RENS, San Joaquin County PHS/EHD, prior to the August 1992 sampling <br /> event, however, no response was received by SRK from the PHS/EHD during or after the sampling <br /> event <br /> 6 0 ANALYTICAL DATA <br /> analyses were performed b ACZ Laboratories CA Lab #E608 Copies of <br /> Organic and inorganic analy p y ( ) p <br /> the analytical data and chain-of-custody are provided in Appendix C The chain-of-custody states that <br /> the groundwater samples were received by the laboratory in good condition at 4 C The chain-of- <br /> custody clearly documents that the samples were shipped from California to Colorado and also <br /> indicates Sample Identification ("SRK-MW1-Man") The top of the chain-of-custody form clearly <br /> states the name and address of ACZ Laboratories in Steamboat Springs, Colorado <br /> The constituents of BTEX or volatile hydrocarbons were not detected in SRK monitoring wells SRK- <br /> MW1 or SRK-MW3 The constituents of BTEX were detected at very low levels in SRK monitoring <br /> well SRK-MW2 (Benzene 2 ppb, Ethylbenzene 0 8 ppb, and Xylene 0 6 ppb), while volatile <br /> hydrocarbons were detected at 0 10 ppm Lead concentrations ranged from 100 ppb in SRK-MW2 <br /> to 14 ppb in SRK-MW3 <br /> Elevated levels of BTEX and volatile hydrocarbons were detected in monitoring Ele Y g wells BEI-MW4 <br /> through BEI-MW6 Volatile hydrocarbon levels ranged from 10,000 ppb in BEI-MW6 to 360 ppb <br /> in BEI-MW4 Benzene concentrations ranged from 6,100 ppb in BEI-MW5 to 68 ppb in BEI-MW4 <br /> Toluene levels ranged from 940 ppb in BEI-MW5 to 62 ppb in BEI-MW4 Ethylbenzene levels <br /> ranged from 7,000 ppb in BEI-MW5 to 640 ppb in BEI-MW4,while xylenes concentrations spanned <br /> Steffen Robertson and Kirsten <br />