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<br /> 			APEX ENVIROTECN  INC.  		Upon removal from the steel rods,approximately the bottom
<br />       							s   			six inches of each tube Is out off and capped to be potentially
<br /> 			STANDARD OPERATING PROCEDURES 			submitted for analysis. The tubes capped with aluminum
<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 spit-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 sail 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 delonized 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 fogs 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 defonized 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 />     											each sampling event.
<br /> 			SOP-2
<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-contaminatlon 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
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