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V <br /> foot will be determined in the field. Exploratory boring logs shall be prepared under the <br /> direction of a Registered Geologist or Professional Engineer. <br /> Head-space analysis will be performed in the field to check for the presence of volatile organic <br /> compounds. Head-space analysis will be performed using an organic vapor meter(either flame- <br /> ionization or photo-ionization). The method used will be consistent with the method described <br /> by Fitzgerald (1989). Organic vapor concentrations will be recorded on the HETI Soil Boring <br /> Log (Figure 1). The selection of soil samples for chemical analysis are typically based on the <br /> following criteria: <br /> a. Soil discoloration <br /> b. Soil odors <br /> C. Visual confirmation of chemical in soil <br /> d. Depth with respect to underground tanks <br /> e. Depth with respect to groundwater <br /> f. Organic vapor meter reading <br /> �.. The soil sampler and liners will be cleaned with a trisodium-phosphate or Alconox solution, <br /> rinsed with clean tap water and air dried or wiped dry with a clean towel prior to each <br /> sampling event. Soil samples (full liners) selected for chemical analyses will be covered with <br /> aluminum foil or teflon tape and the ends will be sealed with plastic end caps. The end caps <br /> will then be taped to ensure a more secure seal. The samples will then be labeled and entered <br /> onto a Chain-of-Custody document,and placed in a cooler on blue ice(hard shell)for transport <br /> to a state certified analytical laboratory. <br /> Where copper and zinc contamination are the subject of the investigation, stainless steel liners <br /> will be used in lieu of brass liners. Stainless steel liners will also be used when the client, <br /> additional sampling protocol or regulatory agencies require. <br /> V <br /> Soil borings will be backfilled (sealed) to the ground surface using either a neat cement or <br /> cement-bentonite grout mixture in accordance with appropriate local regulations. <br /> V <br /> Pending the outcome of the results of the laboratory analyses,excess drill cuttings will remain <br /> on-site and, when deemed necessary, covered with a plastic tarp or drummed. Confirmed <br /> `, uncontaminated soils may be appropriately disposed of on-site by the client. Soils found to <br /> contain concentrations of contaminants above applicable local or state limits will be placed in <br /> appropriately labeled 55-gallon D.O.T. drums or in a hazardous materials drop bin and left on- <br /> site for proper disposal by the client. At the clients request,HETI will act as the client's agent <br /> `~ by assisting in the disposal of the contained material. In no case will HETI personel sign a <br /> Hazardous Waste Manifest. <br /> Well Construction <br /> Monitoring wells shall be installed using a truck-mounted hollow-stem auger drilling rig or an <br /> ,r air or mud-rotary drilling rig. Typically, the hollow stem rig will be used for the installation <br /> of wells up to 100 feet deep, if subsurface conditions prove favorable. Wells greater than 100 <br /> feet in depth will typically be drilled using air or mud-rotary equipment. Mud-rotary <br /> equipment will typically be used when alternate methods have failed or proven ineffective. <br /> Monitoring well casing and screen shall be constructed of a minimum of Schedule 40,flush joint, <br /> threaded, polyvinylchloride (PVC) pipe. The well screen will be factory mill-slotted. The <br /> ... screen length shall be determined in the field and shall be placed with the intent of setting the <br /> screened interval adjacent to the aquifer material. The screen length shall also be set with the <br /> intent of placing the top of the screened interval a minimum of 2 feet above the static water <br /> 2 <br />