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Mr Harlan Knoll, REHS 3 July 24, 1992 <br />' nondetectable concentrations of total lead. Stockpile concentrations of TPH-G ranged <br /> P 9 <br /> from 600 to 19,000 ppm, benzene from ND to 37 ppm, toluene from 3 to 490 ppm, <br /> ethylbenzene from 1 to 150 ppm, xylenes from 44 to 1400 ppm. <br /> Site Assessmgnt W rk Plan <br /> The Site Assessment field program will be performed in two separate field investiga- <br /> tion phases. The health and safety plan for this field program can be found in <br /> Appendix A The first phase will consist of a soil-vapor survey Soil-vapor survey <br /> sample locations and the rationale for placement locations are discussed further <br /> I herein Upon completion, the results of the soil-vapor survey will be summarized in <br /> a Soil Vapor Survey Report which will also recommend any resultant modifications to <br /> the scope of work for the second phase of the field investigation. The second phase <br /> of field investigation will consist of the drilling program. The drilling program will <br /> Include soil boring and soil sampling and the Installation of ground water monitor- <br /> ing/vapor extraction wells. The results of both field investigations will be summarized <br /> in a Site Assessment Report. <br /> The following sections outline the methods proposed for the soil-vapor survey, drilling <br /> and soil sampling, well installation, and vapor extraction testing or well development <br /> and ground water sampling, as appropriate <br />' Phase I - Soil Vapor Survev <br /> The proposed sample locations for the soil-vapor survey are shown on Figure 2 The <br />' sample locations were selected primarily to monitor the northwest area of the site in <br /> the vicinity of the north pump island where highest concentrations were detected. <br /> Prior to commencing the soil-vapor survey, a utility locator will be subcontracted to <br /> mark all utility locations on site, as necessary. A hydraulic ram will be used to <br /> advance soil-vapor probes at the 8 sampling locations at depths of approximately 9 <br />' and 15 feet A clean probe will be used at each sample location <br /> Once the soil-vapor probe is set at the selected depth, an adaptor will be attached to <br />' the top of the probe to enable hookup of a vacuum pump The soil-vapor will be <br /> purged of three probe volumes using a constant flow sampling pump to control <br /> volume A soil-gas sample will be collected in a molecular sieve polymer and charcoal <br />' tubes, as appropriate The tubes will be labeled with the site name, sample <br /> Identification, depth, time , and any field observations This information will also be <br /> recorded onto a sampling log. The sample tubes will be prepared for analyses using <br /> thermal desorption and methanol extraction. Samples will be analyzed on-site using <br /> a mobile laboratory equipped with a GC/FID (or equivalent). The vapor samples <br /> collected will be analyzed for TPH-G and BTEX by the Environmental Protection <br /> Agency (EPA) Methods 8020 and 8015, respectively. Reporting limits will be 10 ppb <br /> for TPH-G and 0.1 ppb for BTEX <br /> PL191-63*REP0RTSIKN0LL RPT[July 22. 1992! CmmAwEnvironmental <br />