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' STANDARD OPERATING PROCEDURE <br /> SOIL BOREHOLE DRILLING,WELL INSTALLATION,AND SOIL SAMPLING <br /> • Drilling and Soil Sampling <br /> Permits, Site Safety Plan Utility,Clearance <br /> ATC Associates Inc (ATC) obtains all the required permits, unless otherwise contractually directed ATC <br /> prepares a site specific Site Safety Plan detailing site hazards, site safety and control, decontammation <br /> procedures, and emergency response procedures to be employed throughout the defined phase of work At <br /> least 48 hours prior to drilling Underground Service Alert (USA) or an equivalent agency is notified of the <br /> planned work ATC attempts to locate ail underground and aboveground utilities by site inspection (in <br /> conjunction with its' subcontractors and knowledgeable site managers, if available), and review of site as- <br /> built drawings ATC may employ a private, professional utility locator to refine the site utility inspection <br />' Drilling Equipment <br /> All soil borings are drilled using a truck-mounted hollow-stem auger drill rig, unless site conditions warrant <br />' a different drilling method Subsurface conditions permitting, the first five feet of each boring is advanced <br /> using a hand-auger or post-hole digger All drilling equipment is inspected daily and maintained in safe <br /> working condition by the operator All down-hole drilling equipment is steam cleaned prior to arriving on <br />' site Working components of the drill rig near the borehole, as well as augers and drill rods are thoroughly <br /> steam cleaned between each boring location All ATC drilling and sampling methods are consistent with <br /> ASTM Method D-1452-80 and local, stale and federal regulations <br />' Soil SqWling and Lidioiu ic,Di,scri tion <br /> Whenever possible and approved by the appropriate regulatory agency, the first ATC boring to be drilled at <br /> a site is continuously cored to obtain a complete lithologic description Otherwise, soil samples are typically <br /> collected every 5 feet to the total depth explored, using brass tubes fitted in a California-modified split- <br /> spoon sampler If copper or zinc contamination is the subject of the investigation, stainless steel liners are <br /> used instead of brass Additional soil samples may be collected based upon significant changes in Ilthology <br />' or in areas of obvious soil contamination During soil sample collection, the split spoon sampler is driven <br /> 18 to 24 inches past the lead auger by a 140-pound hammer falling a minimum of 30 inches The number of <br /> blows necessary to drive the sampler and the amount of soil recovered is recorded on the Field Exploratory <br />' Soil Boring Log The soil sampler and liners are cleaned with an Alconon solution and rinsed with tap <br /> water prior to each sampling event New liners are used whenever a soil sample may be retained for <br /> laboratory analysis <br /> Soil samples selected for laboratory analysis are sealed on both ends with Teflon tape and plastic end caps <br /> The samples are labeled, documented on a chain-of-custody form and placed in a cooler for transport to a <br /> state-certified analytical laboratory Soil contained in remaining liners is removed for lithologic <br /> 1 descriptions (according to the Unified Soil Classification System) Additional soil is screened for organic <br /> vapors by placing approximately 30 grams of soil in a sealed plastic bag or a glass jar sealed with aluminum <br /> foil The bag or jar is left undisturbed for approximately 15 minutes, in the sun if possible The headspace <br />' in the bag is accessed in a manner to minimize entry of outside air, and is tested for total organic vapor <br /> using a calibrated photo ionization detector (PID) The results of the field screening are noted with the <br /> lithologic descriptions on the Field Exploratory Soil Boring Log <br />' On encountering an impermeable (clayey) layer three feet or more in thickness below a saturated permeable <br /> layer, where the impermeable Iayer is considered to be a possible confining layer for an underlying aquifer, <br /> drilling is halted until a decision to proceed is obtained from the project manager This process minimizes <br />' the chance of introducing contamination to an underlying, clean aquifer <br /> Soil Waste Management <br /> Soil cuttings are stockpiled on and covered with plastic sheeting to control runoff, or contained in 55-gallon <br /> D 0 T-approved drums on site Waste soil is sampled to chemically profile it for disposable, and hauled by <br />