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L:_, <br /> 292«0 <br /> APEX ENVIROTECH INC . Upon removal from these„epl �app� lrgafQiy, tFte "ttpnr _ I <br /> six inches of each tube is cut qff and-c Aped -tq -pe , pote�tially <br /> STANDARD OPERATING PROCEDURES submitted for analysis . The t 1: c'ap�6 h`aihLkh <br /> foil or "Teflon" sheets and plastic caps or the samples are <br /> SOP-1 extruded from the tubes and sealed within other appropriate , <br /> HOLLOW STEM AUGER SOIL BORING SAMPLING cleaned sample containers . The samples are then <br /> hermetically sealed , labeled , and refrigerated for delivery, <br /> During drilling , soil samples for chemical analysis are under strict chain-of-custody, to the analytical laboratory, <br /> collected in thin-walled brass tubes , of varying diameters These procedures minimize the potential for cross- <br /> and lengths (e. g . , four or six inches long by two inches contamination and volatilization of volatile organic <br /> outside diameter) . Three or four of the selected tubes , plus compounds (VOC) prior to chemical analysis , <br /> a spacer tube , are set in an 18-inch long split-barrel sampler <br /> of the appropriate inside-diameter. The remaining portion of the plastic tube is cut open and a <br /> portion of the soil sample collected at each sampling interval <br /> Where possible , the split-barrel sampler is driven its entire is analyzed in the field using either a portable PID, FID , <br /> length either hydraulically or using a 140-pound drop organic vapor analyzer, catalytic gas detector, or an <br /> hammer. The sampler is extracted from the borehole and explosimeter. The purpose of this field analysis is to <br /> the brass tubes , containing the soil samples , are removed, qualitatively determine the presence or absence of <br /> Upon removal from the sampler, the selected brass tubes hydrocarbons , and the samples to be analyzed at the <br /> are either immediately trimmed and capped with aluminum laboratory. The soil sample is sealed in either a glass jar or <br /> foil or "Teflon" sheets and plastic caps or the samples are plastic bag to allow for some volatilization of VOC . The PID <br /> extruded from the tubes and sealed within other appropriate, is then used to measure the concentrations of hydrocarbons <br /> cleaned sample containers . The samples are then within the container's headspace. The data is recorded on <br /> hermetically sealed , labeled, and refrigerated for delivery, both field notes and the boring logs at the depth <br /> under strict chain-of-custody, to the analytical laboratory, corresponding to the sampling point. <br /> These procedures minimize the potential for cross- <br /> contamination and volatilization of volatile organic Other soil samples are collected to document the soil and/or <br /> compounds (VOC) prior to chemical analysis , stratigraphic profile beneath the project site, and estimate <br /> the relative permeability of the subsurface materials . All <br /> One soil sample collected at each sampling interval is drilling and sampling equipment are either steam cleaned or <br /> analyzed in the field using either a portable photo ionization washed in solution and doubly rinsed in deionized water <br /> detector (PID) , flame ionization detector (FID) , organic vapor prior to use at each site and between boreholes to minimize <br /> analyzer, catalytic gas detector, or an explosimeter. The the potential for cross-contamination, <br /> purpose of this field analysis is to qualitatively determine the <br /> presence or absence of hydrocarbons , and the samples to in the event the soil samples cannot be submitted to the <br /> be analyzed at the laboratory. The soil sample is sealed in analytical laboratory on the same day they are collected <br /> either a brass tube , glass jar, or plastic bag to allow for some (e .g . , due to weekends or holidays) , the samples are <br /> volatilization of VOC. The PID is then used to measure the temporarily stored until the first opportunity for submittal <br /> concentrations of hydrocarbons within the container's either on ice in a cooler, such as when in the field , or in a <br /> headspace . The data is recorded on both field notes and the refrigerator at Apex's office , <br /> boring logs at the depth corresponding to the sampling point. <br /> SOP-3 <br /> Other soil samples are collected to document the soil and/or SOIL EXCAVATION AND SAMPLING <br /> stratigraphic profile beneath the project site, and estimate <br /> the relative permeability of the subsurface materials . All Excavation and subsequent soil sampling is performed <br /> drilling and sampling equipment are either steam cleaned or under the direction of a registered geologist or civil engineer, <br /> washed in solution and doubly rinsed in deionized water To reduce the potential for cross-contamination , all <br /> prior to use at each site and between boreholes to minimize excavation equipment is either steam cleaned or washed <br /> the potential for cross-contamination, prior to use and between excavations . Soil samples for <br /> chemical analysis are collected in cleaned , thin-walled brass <br /> In the event the soil samples cannot be submitted to the tubes of varying diameters and lengths (e .g . , six inches long <br /> analytical laboratory on the same day they are collected by two inches outside diameter) or other appropriate cleaned <br /> (e . g . , due to weekends or holidays) , the samples are sample container, if used , one tube may be set in a two inch <br /> temporarily stored until the first opportunity for submittal inside diameter, hand-driven sampler. To reduce the <br /> either on ice in a cooler, such as when in the field , or in a potential for cross-contamination between samples , the <br /> refrigerator at Apex's office , sampler is washed in a solution and doubly rinsed between <br /> SOP-2 each sampling event. <br /> DIRECT PUSH SOIL BORING SAMPLING Upon recovery, a portion of the soil sample is sealed for later <br /> screening with either a portable PID , FID , or an <br /> During drilling , soil samples for chemical analysis are explosimeter. Another portion of the sample is used for <br /> collected in thin-walled plastic tubes , of varying diameters description of the excavated materials . A third portion of the <br /> and lengths (e.g . , two inches outer diameter by four feet sample is hermetically sealed , labeled and refrigerated for <br /> long) . The plastic sampling tube is placed inside a steel rod delivery, under strict chain-of-custody, to the analytical <br /> and driven into the subsurface to the desired depth using a laboratory . These procedures minimize the potential for <br /> direct push drill rig . The steel rod is then removed from the cross-contamination and volatilization of volatile organic <br /> subsurface and the plastic tube containing the soil sample compounds prior to chemical analysis , <br /> are removed from the steel rod . The process is repeated <br /> until the desired depth of the boring is reached . In the event the soil samples cannot be submitted to the <br /> analytical laboratory on the same day they are collected <br /> (e .g . , due to weekends or holidays) , the samples are <br />