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Ceofo uaf7ec(tnus Inc Page 3 <br /> Work Plan <br /> Valentine(Castle Motors) <br /> Project No 723 2 <br /> April 11,2000 <br /> 2.3 Groundwater Monitoring <br /> Groundwater monitoring is proposed on a quarterly basis for the seven monitoring wells and <br /> 1 one domestic well located at 60 E Castle Street Notification will be given to SJC PHS/EHD <br /> prior to a monitoring event being performed The procedure for performing a groundwater <br /> monitoring event is discussed below. <br /> Before sampling is attempted, the well will be sounded for depth to water and then a clear <br /> disposable bailer will be used to determine if floating product is present The well will be <br /> purged of at least 3 well volumes of stagnant water using either a submersible pump or a <br /> stainless steel bailer Purging will continue until the temperature, EC, and pH of the <br /> groundwater has stabilized (<10% variation between three readings) indicating that formation <br /> water representative of aquifer conditions is entering the well These water quality <br /> parameters are measured at intervals of each well volume purged In addition to the normal <br /> water quality parameters measured during well purging, pH, conductivity (EC) and <br /> temperature, we will measure oxidation-reduction potential (ORP) <br /> tA stainless steel or disposable plastic bailer will be used to collect each sample Care will be <br /> taken to minimize sample agitation from the initial filling of the bailer to the transfer of the <br /> sample to the VOA vials and glass amber liter bottles Once the sample container is filled <br /> and capped, the bottle will be inverted, tapped, and checked for headspace bubbles The <br /> sample container is identified and labeled with a unique designation, inserted into foam <br /> holders and placed in an ice chest cooled to 4°C for transport to the Iaboratory <br /> All non-disposable sampling equipment is decontaminated using a steam cleaner before and <br /> between uses Disposable gloves will be used by the sample technician while collecting the <br />' samples and will be changed with each sampling event A bailer blank for each well will be <br /> collected prior to sampling by filling the decontaminated stainless steel/disposable plastic <br /> bailer with water (provided by the laboratory) and then filling a VOA vial (provided by the <br /> laboratory) using the same procedures for actual sample collection <br />' Bailer blanks for each sample, along with a field blank (prepared from water provided by the <br /> laboratory poured into a VOA vial on site), will accompany the samples to the laboratory and <br />' serve as checks against cross contamination <br /> A chain of custody document, listing all samples collected, accompanies the samples from <br /> field to laboratory, thereby providing a means to track their movement and insure their <br /> integrity <br /> All water purged from each monitoring well will be placed in a 55 gallon DOT approved <br />' container, properly labeled and stored on site <br /> 2.3.1 Groundwater Sample Analysis <br />' The groundwater samples will be submitted to Sherwood Laboratories of Hilmar (State <br /> Certified Laboratory #1400) and analyzed for <br /> • benzene, toluene, ethylbenzene and xylene (BTEX by EPA method 602) <br /> gasoline range petroleum hydrocarbons (TPH-Gas by EPA method 5030/8015m) <br /> r the oxygenated fuel compounds (MTBE, DIPE, ETBE, TAME and TBA by EPA method <br /> 8260) <br /> Continued testing for the oxygenated fuel compounds is warranted at the site as previous <br /> rmonitoring events have shown the presence of MTBE, DIPE and TBA <br /> r <br />