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HORIZON ENVIRONMENTAL, INC. <br /> • GROUNDWATER MONITORING <br /> FIELD METHODS AND PROCEDURES <br /> The following section describes field procedures that will be completed by Horizon Environmental <br /> Inc (Horizon) personnel in performance of the tasks involved with this project <br /> 1.0 HEALTH AND SAFETY PLAN <br /> Field work performed by Horizon and subcontractors at the site will be conducted according to guidelines <br /> established in a Site Health and Safety Plan (SHSP) The SHSP is a document that describes the hazards that <br /> may be encountered in the field and specifies protective equipment, work procedures, and emergency <br /> information A copy of the SHSP will be at the site and available for reference by appropriate parties n <br /> work at the site during <br /> 20 GROUNDWATER DEPTH EVALUATION <br /> Each monitoring well is opened and allowed to equalize to atmospheric pressure prior to sounding Depth-to- <br /> water is measured to the nearest 0 01-foot using an electronic, hand-held water level indicator The measuring <br /> point is the survey mark on the top of the well casing The tip of the probe is examined in order to determine the <br /> presence or absence of product sheen <br /> 30 MONITORING WELL PURGING & SAMPLING <br /> Prior to purging a clean, transparent bailer is lowered into the well, and a sample of groundwater is hosted to <br /> the surface The sample fluid is inspected for the presence of free-floating product on its surface Sampiing <br /> activities conducted subsequent to the initial well development activity will be preceded by purging a minimum of <br /> three weil volumes by hand-bailing or the use of an electrically-operated pump Pirge water will be monitored <br /> for the parameters of temperature, pH, and electrical conductivity until stabilized <br /> If required, field readings for dissolved oxygen (d02) displayed in tenths of par's per million (ppm x 0 1) will be <br /> obtained utilizing Hanna Instruments' hand-held, HI-9142 Portable Dissolved Oxygen Meter Generally higher dO2 <br /> concentrations are expected in samples which are unimpacted or marginally impacted by hydrocarbons than for <br /> samples collected from monitoring wells which yield hydrocarbon-impacted water <br /> A well is allowed to recharge to at least 80% of its prepurge volume pnor to sampling If a well dewaters it will <br /> be allowed to recharge for a minimum of one to two hours prior to sampling Ater the water level within the well <br /> has stabilized a sample is collected within a dedicated, clean disposable, plastic baler lowered into the well <br /> and hosted when filled <br /> 40 SAMPLE PREPARATION 8 TRANSPORT FOR LABORATORY ANALYSIS <br /> Samples will be transferred to airtight vials chilled on ice, and transported to a California DoHS-certified <br /> laboratory for analysis Samples will be analyzed within the EPA-specified holding time for the requested <br /> analysis Each sample container submitted for analysis will have a label affixed to identify the fob number, <br /> sample date time of sample collection, and a sample number unique to that sample <br /> A chain-of-custody form will be used to record possession of the sample from time of collection to its arrival at <br /> the laboratory When the samples are shipped, the responsible technician or geologist relinquishes custody of <br /> the samples by signing the chain-of-custody form, noting the date and bme The sample-control officer at the <br /> laboratory <br /> • venfies sample integrity, <br /> • confirms storage in the proper container, <br /> • recognizes that an adequate volume of fluid has been collected for the required analysis <br /> • identifies the method of preservation, and <br /> • accepts custody for the laboratory when these conditions have been satisfied <br />