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not converted to monitoring wells will be backfilled by pouring a cement slurry not exceeding 5% <br /> ibentonite through the auger. <br /> 3.3 Soil Sampling <br /> Soil samples will be collected to the first occurrence of groundwater and will be collected at 5-foot <br /> intervals Groundwater has been measured at approximately 21 to 25 feet below grade. <br /> Soil samples will be collected through the auger in three 6-inch long brass sleeves with a 2-inch <br /> diameter an a split-spoon sampler. The sampler is driven ahead of the auger by a 140 pound <br /> hammer with a 30-inch drop. The brass sleeves and sampler will be washed with an Alconox <br /> solution and rinsed with deomzed water prior to each use. <br /> One brass sleeve containing soil from each interval will be capped, sealed, labeled in accordance <br /> with EPA protocol, recorded on a chain of custody form, placed in a cooler at 4 degrees <br /> centigrade and transported to a California certified analytical laboratory for the specified analyses <br /> under proper chain of custody documentation. Another brass sleeve will be used for hthologic <br /> description. All field data regarding lithology, recovery and blow counts will be recorded on <br /> boring logs. <br /> 3.4 Field Screening of Soil Samples <br /> • One brass sleeve will be used for field screening of samples. The material from the top tube will <br /> be placed in a sample Jar filled to approximately 50 percent capacity, shaken and stored for a <br /> period of approximately 5 minutes. A standard headspace reading will be collected at this time <br /> using a Foxboro organic vapor analyzer (OVA) or equivalent field instrument and noted on the <br /> boring log. <br /> 3.5 Soil Analyses <br /> Soil samples will be analyzed by a California certified laboratory in accordance with State <br /> guidelines and EPA protocol The samples will be selectively analyzed for total petroleum <br /> hydrocarbons (TPIT) quantitated against gasoline standards and benzene, toluene, ethylbenzene <br /> and total xylenes (BTEX) and using EPA methods 8015M and 8020, respectively. <br /> I <br /> 3.6 Installation of Monitoring Wells <br /> Two groundwater monitoring wells will be constructed in soil borings as shown on Figure 2. The <br /> wells will consist of 4-inch, flush threaded, schedule 40 PVC slotted and blank casing. A <br /> threaded end cap will be placed at the bottom of the PVC which will then be set through the <br /> auger. The screened PVC casing will consist of 0.02 inch machine cut slots Number 2 sand will <br /> be poured down the auger whale removing approximately 2 feet of auger at a time. The filter pack <br /> will be placed 2 feet above the screened interval. Three feet of bentonite pellets will be poured <br /> 5023J2 4 <br />