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INFerNITCUR.C. SACRAMENT <br /> O <br /> 2.0 Collection of Samples <br /> 2.1 Soil Samples <br /> LSoil samples are subjected to field analysis with J y t either a flame ionization detector <br /> (FID) or a photoionization detector (PID) with.-and 10.7 EV lamp immediately-following <br /> sample collection. The field analysis is performed as follows: <br /> '. 1. A representative aliquot.of the sample is.placed in' a glass jar:or resealable <br /> freezer bag and broken up (to the extent possible) to allow the release of <br /> contaminant vapors. <br /> L <br /> 2. The container is exposed to direct sunlight for a period of ten:minutes to <br /> facilitate the volatilization of organic compounds within the sample. <br /> L <br /> 3. The probe of the FID or PID is inserted into the container carefully, and a <br /> sample of the vapor is drawn into the instrument. The maximum numerical <br /> L reading observed is noted on the drilling log. <br /> All soil samples to be submitted for laboratory 'analysis are collected in'brass <br /> tubes or precleaned glass jars. The ends of the brass tubes are coveredwith Teflon tape <br /> P <br /> and fitted with airtight caps. Glass jars are laboratory cleaned and fitted with either <br /> ` teflon caps or foil covers andlastic caps. The.selection of samples to be'submit <br /> P P p ted for <br /> laboratory analysis will be based on the filed observations'and headspace analysis. <br /> L <br /> [ 2.2 Ground Water Sampling <br /> 1� Ground water samples will be collected for laboratory analysis using"the <br /> Lprocedures given below. <br /> 1. Open the temporary well and measure the organic vapor concentration with <br /> a FID or PID. <br /> 2. Measure the water and non-aqueous product levels (if any) in the well using <br /> a decontaminated measuring device. All measurements must be made to <br /> the nearest 0.01 foot, and measured relative to the top of the'casing. <br /> Record the depth of the water .and product in the field notebook. <br /> A-2 <br />