Laserfiche WebLink
Problem Assessment Work Plan <br /> CSUS—Multi-Campus Regional Center <br /> January 23,2003 <br /> Page-5- <br /> 0.01 foot and horizontal accuracy of 1.0 foot. The measuring point for water-level measurements will be s <br /> marked on each well collar. <br /> At least 48 hours following construction, the monitor wells will be developed by surging and bailing the } <br /> groundwater in each well until the discharge water is relatively free of sediment (clear to the unaided.eye). <br /> The monitor wells will be purged until the temperature, electrical conductivity, and pH of the water has <br />{ stabilized. All well-development equipment will be cleaned prior ,to use in each well by washing`in a E <br /> solution of laboratory-grade, non-phosphate detergent and.de-ionized water, and double rinsing with de- <br /> ionized water. The purge water discharged from the wells during development will be placed in 55-gallon <br /> drums, sealed, labeled, and left an-site pending results of laboratory analyses. <br /> Groundwater samples will be collected at least 48 hours following development of the monitor wells. Prior <br /> to sample collection, the static water level in each well will be measured to the nearest 0.01-foot with a <br /> battery-operated, water level meter. A disposable bailer will be lowered into each well to check for floating <br /> product, petroleum odors, and/or sheen. If floating product is present, the thickness will be measured. <br /> Laboratory samples will not be collected from wells that contain floating product. <br /> The monitor wells will be purged using a clean, disposable bailer or a Teflon® and stainlesssteel <br /> submersible pump until the temperature, electrical conductivity, and pH of the water has stabilized At least <br /> three casing volumes of water will be purged from each monitor well. The purged water from each well will <br /> be placed in 55-gallon.drums, sealed, labeled, and left on-site pending results of laboratory analyses. f <br /> Each well will be allowed to recover to at least 80% of its pre-purge water level before sampling. However, <br /> if any of the monitor wells does not recover to at least 80% of its pre-purge water level by the end of the { <br /> day of the purge (standard workday), the monitor well will be sampled at that time and the percent recovery <br /> i <br /> noted The groundwater samples will be collected with clean, disposable bailers or a Teflon® and stainless <br /> steel submersible pump. Each water sample will be gently drained from the bailer or filled from the pump <br /> discharge line at very low flow into the appropriate laboratory supplied containers. The sample containers <br /> will be sealed, labeled, placed in a cooler chilled with ice, and delivered under chain-of-custody procedures <br /> to a California certified laboratory for analyses. <br /> 5.0 LABORATORY ANALYSES <br /> The groundwater samples collected from the borings and monitor wells will be analyzed for total petroleum <br /> hydrocarbons quantified as gasoline (TPH-G) and for total petroleum hydrocarbons (TPH) quantified as <br /> kerosene, diesel, and motor oil by EPA Method 8015M; for benzene, toluene, ethyl benzene, andtotal <br /> xylenes (BTEX) by EPA Method 8020; and for gasoline oxygenates/additives by EPA Method 8260.'The I <br /> gasoline oxygenates/additives include Methyl tertiary-Butyl Ether (MTBE), ethanol, tertiary-Butanol, Di- <br /> isopropyl ether (DIPS), Ethyl tertiary-Butyl Ether (ETBE), tertiary-amyl Methyl Ether (TAME),'1,2- <br /> Dibromoethane, and 1,2-Dichloroethane (1,2-DCA). The samples will be delivered under chain of-custody <br /> procedures to a California certified laboratory for analysis. The analytical methods and analytical detection <br /> limits are presented in Table 1. <br /> 1 <br /> �s _ -- <br /> L1� CONDOR <br />