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• Soil samples were collected from several soil gas borings (A2-SG1, A3-SG1, A3-SG2, <br /> A3-SG3, A3-SG5, B1-SG1, D2-SG1 and E1-SG1) based on the observance of potentially <br /> impacted materials; and <br /> • Groundwater Monitoring Well TW-5 was constructed using 0.010-inch slotted screen and <br /> Lonestar #2/12 sand for the filter pack based on observations made in the field. The <br /> original plan was to construct the well with 0.020-inch slotted screen and Lonestar #3 <br /> sand, but due to geologic conditions, the finer screen and filter pack were necessary. <br /> 3.4 HEALTH AND SAFETY MONITORING <br /> Health and safety monitoring, using a PID, was administered during the drilling and sampling <br /> conducted as part of the implementation of the RI/SSI. Although VOCs were identified in <br /> headspace readings conducted on soil samples, there were no detections above action levels in <br /> the breathing zone of the on-site workers. Concentrations of VOCs in the breathing zone ranged <br /> from 0.0 ppmv to a maximum of 1.8 ppmv. The results of the monitoring were recorded in the <br /> boring logs provided in Appendix E. <br /> 3.5 DISPOSAL OF INVESTIGATION DERIVED WASTE <br /> In the process of collecting environmental samples during the proposed field sampling program, <br /> different types of potentially contaminated investigation-derived wastes (IDW) were generated <br /> and include the following: <br /> • Used personal protective equipment(PPE); <br /> • Disposable sampling equipment; <br /> • Soil cuttings; <br /> • Well development and purging fluids; and <br /> • Decontamination fluids. <br /> The USEPA's National Contingency Plan requires that management of IDW comply with all <br /> applicable or relevant and appropriate requirements to the extent practicable. The sampling plan <br /> will follow the Office of Emergency and Remedial Response Directive 9345.3-02 dated May <br /> 1991, which provides the guidance for the management of IDW. In addition, other legal and <br /> practical considerations that may affect the handling of IDW were considered. <br /> Listed below are the procedures that were followed for handling the IDW: <br /> • Used PPE and disposable equipment was double bagged and placed in a municipal refuse <br /> dumpster. These wastes are not considered hazardous and can be sent to a municipal <br /> landfill. Any PPE and disposable equipment that was disposed and could still be reused <br /> was rendered inoperable before disposal in the refuse dumpster. <br /> • Decontamination/development/purge water was placed in Department of Transportation <br /> approved 55-gallon drums and sealed. The drums were identified with labels stating <br /> "Caution: Potentially Hazardous Substance — Pending Analysis". In addition, the label <br /> identified the address of the Site; the source of its contents (i.e., soil boring numbers, <br /> sample depths, etc.); the contents of the drum(i.e., soil, groundwater, etc.); and a notation <br /> PARSONS 30 FINAL RI REPORT-FORMER TRACY MGP <br /> APRIL 2010 <br />