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APEX ENVIROTECH,INC.
<br /> STANDARD OPERATING PROCEDURES
<br /> Quarterly Morutortng Reports
<br /> SOP-4 When practical,the groundwater sample should be collected when
<br /> SAMPLE IDENTIFICTION AND CHAIN-OF the water level in the well recovers to at least 80 percent of its
<br /> CUSTODY PROCUDURES static level
<br /> Sample identification and chain-of-custodyThe sampling equipment consists of either a"Teflon"bailer,PVC
<br /> procedures ensure bailer,or stainless steel bladder pump with a"Teflon'bladder if
<br /> sample integrity as well as document sample possession from the
<br /> time of collection to ultimate disposal Each sample container the sampling system isdedicated
<br /> bladder a bladder er to the well,then the bailer is
<br /> submitted for analysts is labeled to identify thejob number,date, usually"Teflon,"but tpump is PVC with a
<br /> polypropylene bladder In general and depending on the intended
<br /> time of sample collection,a sample number unique to the sample,
<br /> any in-field measurements made,other pertinent field observations laboratory analysis, of on'se t glass,volatile organic analysts
<br /> also recorded on the field excavation or boring logs (VOA)vials,with"Teflon' septa,are used as sample containers
<br /> Chain-of-custody forms are used to record possession of the SOP—12
<br /> sample from time of collection to arrival at the laboratory During MEASURING LIQUID LEVELS USING
<br /> shipment,the person with custody of the samples will relinquish WATER LEVEL METER OR INTERFACE
<br /> them to the next person by signing the chain-of-custody form(s) PROBE
<br /> and noting the date and time The sample control officer at the
<br /> laboratory will verify sample integrity,correct preservation,
<br /> confirm collection in the proper container(s),and ensure adequate Field equipment used far liquid level gauging typically includes
<br /> volume for analysis the measuring instrument(water-lcvel meter or interface probe and
<br /> product bailer(s)) The field kit also includes cleaning supplies
<br /> If[hese conditions are met,the samples will be assigned unique (buckets,solution,spray bottles,and deionized water)to be used in
<br /> laboratory log numbers for identification throughout analysts and cleaning the equipment between wells
<br /> reporting The log numbers will be recorded on the chain-of- Prior to measurements,the instrument tip is lowered into the well
<br /> custody forms and in the legally-required log book maintained in
<br /> until it touches bottom Using the previously established top-of-
<br /> the laboratory The sample description,date received,client's
<br /> name,and any other relevant information will also be recorded casing or to (t a,wellhead vault)point,the probe cord
<br /> halyard)is markerke ox d and a measuring tape(graduated in hundredths
<br /> SOP-5 of a foot)is used to determine the distance between the probe end
<br /> and the marking on the cord This measurement is then recorded
<br /> 4* LABORATORY ANALYTICAL QUALITY on the liquid-level data sheet as the"Measured Total Depth"of the
<br /> ASSURANCE AND CONTROL well
<br /> In addition to routine instrument calibration,replicates,spikes, When necessary in using the interface probe to measure liquid
<br /> blanks,spiked blanks,and certified reference materials are levels,the probe is first electrically grounded to either the metal
<br /> routinely analyzed at method-specific frequencies to monitor stove pipe ar another metal object nearby When no ground is
<br /> precision and bias Additional components of the laboratory available,reproducible measurements can be obtained by clipping
<br /> Quality Assurance/Quality Control program include the ground lead to the handle of the interface probe case
<br /> I Participation in state and federal laboratory The probe tip is then lowered into the well and submerged in the
<br /> accreditation/certification programs, groundwater An oscillating(beeping)tone indicates the probe is in
<br /> 2 Participation in both U S EPA Performance water The probe is slowly raised until either the oscillating tone
<br /> Evaluation studies(WS and WP studies)and ceases or becomes a steady tone In either case,this is the depth-
<br /> inter-laboratory performance evaluation to-water(DTW)indication of the DTW measurement is made
<br /> programs, accordingly The steady tone indicates floating liquid
<br /> 3 Standard operating procedures describing routine hydrocarbons(FLH) In this case,the depth-to-product(DTP)
<br /> and periodic instrument maintenance, indication and the DTP measurement is made accordingly
<br /> 4 `out-of-Control'%Corrective Action
<br /> documentation procedures,and, The process of lowering and raising the probe must be repeated
<br /> 5 Multi-level review of raw data and client reports several times to ensure accurate measurements The DTW and
<br /> DTP measurements are recorded on the liquid-level data sheet
<br /> SOP—7 When FLH are indicated by the probe's response,a product bailer
<br /> is lowered partially through the FLH water interface to confirm the
<br /> GROUNDWATER PURGING AND SAMPLING
<br /> FLH thickness,particularly in cases where the FLH layer is quite
<br /> thin This measurement is recorded on the data sheet as"FLH
<br /> Prior to water sampling,each well is purged by evacuating a thickness"
<br /> minimum of three wetted well-casing volumes of groundwater
<br /> When required,purging will continue until either the discharge In order to avoid cross-contamination of wells during the liquid-
<br /> water temperature,conductivity,or pH stabilize,a maximum of ten level measurement process,wells are measured in the order of
<br /> wetted-casing volumes of groundwater have been recovered,or the "clean'to"dirty'(where such information is available) In
<br /> well is bailed dry addition,all measurement equipment is cleaned with solution and
<br /> thoroughly rinsed with deionized water before use,between
<br /> measurements in respective wells,and at the completion of the
<br /> day's use
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