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APEX ENVIROTECN; INC. <br /> STANDARD OPERATING PROCEDURES <br /> Soil Borings <br /> SOP-4 <br /> SOP-1 SAMPLE IDENTIFICATION AND CHAIN- <br /> SOIL BORING SAMPLING OF-CUSTODY PROCEDURES <br /> During drilling,soil samples for chemical analysis are collected Sample identification and chain-of-custody procedures ensure <br /> in thin-walled brass tubes,of varying diameters and lengths sample integrity as well as document sample possession from <br /> (e.g.,4 or 6 inches long by 2 inches outside diameter). Three the time of collection to ultimate disposal. Each sample <br /> or four of the selected tubes,plus a spacer tube,are set in an container submitted for analysis is labeled to identify the job <br /> 18-inch long spilt-barrel sampler of the appropriate inside- number,date,time of sample collection,a sample number <br /> diameter. unique to the sample,any in-field measurements made, <br /> sampling methodology,name(s)of on-site personnel,and any <br /> Where possible,the split-barrel sampler is driven its entire other pertinent field observations also recorded on the field <br /> length either hydraulically or using a 140-pound drop hammer. excavation or boring log. <br /> The sampler is extracted from the borehole and the brass <br /> tubes,containing the soil samples,are removed. Upon removal Chain-of-custody forms are used to record possession of the <br /> from the sampler,the selected brass tubes are either sample from time of collection to arrival at the laboratory. <br /> immediately trimmed and capped with aluminum foil or"Teflon" During shipment,the person with custody of the samples will <br /> sheets and plastic caps or the samples are extruded from the relinquish them to the next person by signing the chain-of- <br /> tubes and sealed within other appropriate,cleaned sample custody form(s)and noting the date and time. The sample- <br /> containers. The samples are then hermetically sealed,labeled, control officer at the laboratory will verify sample integrity, <br /> and refrigerated for delivery,under strict chain-of-custody,to correct preservation,confirm collection in the proper <br /> the analytical laboratory. These procedures minimize the container(s),and ensure adequate volume for analysis. <br /> potential for cross-contamination and volatilization of volatile <br /> organic compounds(VOC)prior to chemical analysis. If these conditions are met,the samples will be assigned <br /> unique laboratory log numbers for identification throughout <br /> One soil sample collected at each sampling interval is analyzed analysis and reporting. The log numbers will be recorded on <br /> in the field using either a portable photoionization detector the chain-of-custody forms and in the legally-required log book <br /> (PID),flame ionization detector,organic vapor analyzer, maintained in the laboratory. The sample description,date <br /> catalytic gas detector,or an explosimeter. The purpose of this received,client's name,and any other relevant information will <br /> field analysis is to qualitatively determine the presence or also be recorded. <br /> absence of hydrocarbons,and the samples to be analyzed at <br /> the laboratory. The soil sample is sealed in either a brass tube, SOP-5 <br /> glass jar,or plastic bag to allow for some volatilization of VOC. LABORATORY ANALYTICAL QUALITY <br /> The PID is then used to measure the concentrations of ASSURANCE AND CONTROL <br /> hydrocarbons within the containers's headspace. The data is <br /> recorded on both field notes and the boring logs at the depth In addition to routine instrument calibration,replicates,spikes, <br /> corresponding to the sampling point. blanks,spiked blanks,and certified reference materials are <br /> routinely analyzed at method-specific frequencies to monitor <br /> Other soil samples are collected to document the soil and/or precision and bias. Additional components of the laboratory <br /> stratigraphic profile beneath the project site,and estimate the Quality Assurance/Quality Control program include: <br /> relative permeability of the subsurface materials. All drilling <br /> and sampling equipment are either steam cleaned or washed in 1. Participation in state and federal laboratory <br /> solution and doubly rinsed in deicnized water prior to use at accreditation/certification programs; <br /> each site and between boreholes to minimize the potential for <br /> cross-contamination. 2. Participation in both U.S.EPA Performance <br /> Evaluation studies(WS and WP studies)and inter- <br /> In the event the soil samples cannot be submitted to the laboratory performance evaluation programs; <br /> analytical laboratory on the same day they are collected(e.g., <br /> due to weekends or holidays),the samples are temporarily 3. Standard operating procedures describing routine <br /> stored until the first opportunity for submittal either on ice in a and periodic instrument maintenance; <br /> cooler,such as when in the field,or in a refrigerator at ApeXs <br /> office. 4. "Out-of-Control"/Corrective Action documentation <br /> procedures;and, <br /> SOP-3 <br /> SOIL CLASSIFICATION 5. Multi-level review of raw data and client reports. <br /> Soil samples are classified according to the Unified Soil <br /> Classification System. Representative portions of the samples <br /> may be submitted,under strict chain-of-custody,to an <br /> analytical laboratory for further examination and verification of <br /> the in-field classification and analysis of soil mechanical and/or <br /> petrophysical properties. The soil types are indicated on logs <br /> of either excavations or borings together with depths <br /> corresponding to the sampling points and other pertinent <br /> information. <br />