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I
<br /> analysis VOA vials,with"Teflon"septa,are used as sample
<br /> soil sampling at desired intervals. Soil samples are collected ys
<br /> by either hammering(with a 14C)-pound drop hammer)or
<br /> containers.
<br /> hydraulically pushing a conventional split-barrel sampler.. The groundwater sample is decanted into each VOAviat in.
<br /> containing pre-cleaned 2-inch-diameter brass tubes. A
<br /> geologisJt or engineer from Apex Emirotech,Inc.,continuously such a manner that there is no meniscus at the tap of the vial.
<br /> lags each borehole during drilling and constantly checks dri[1 A cap is quickly secured to the top of the vial. The vial is then
<br /> inverted and gently tapped to see if air bubbles are present. It
<br /> cuttings for indications of both the first recognizable
<br /> none are present,the vial is labeled and refrigerated far
<br /> occurrence of groundwater and volatile hydrocarbons using delivery,under strict chain-of-custody,to the analytical
<br /> either a portable photoionization detector,flame ionization ry
<br /> etween laboratory. label information should include a unique sample
<br /> detector,or an explosimeter. The sampler is rinsed bidentification number,jab identification number,date,time,type
<br /> samples and either steam cleaned or washed with all other �
<br /> drilling equipment between borings to minimize the potential for of analysis requested,and the samplers name.
<br /> cross-contamination. j
<br /> For quality control purposes,a duplicate ureter sample is
<br /> Monitoring wells are cased with threaded,factory-perforated collected from each well. This sample may also be analyzed or
<br /> and blank Schedule 40 PVC. The perforated interval consists put on hold at the laboratory. When required,a trip blank.
<br /> of slotted casing,generaily with 0.020-inch wide by 1.5-inch prepared at the laboratory,is placed in the transport cooler. It
<br /> long slots,with 42 slots per foot. A PVC cap may be secured is labeled similar to the well samples,remains in the cooler
<br /> to the bottom of the casing with stainless steel screws;no during transport,and is analyzed by the laboratory along with
<br /> solvents or cements are used. Centering devices may be the groundwater samples. In addition,a field blank may be
<br /> fastened to the casing to ensure even distribution of filter prepared in the field when sampling equipment is not
<br /> material and grout within the borehole annutus. The well dedicated. The field blank is prepared after a pump or bailer
<br /> casing is thoroughly washed and/or steam cleaned,or may be has been either steam cleaned or properly washed,prior to use
<br /> purchased as pre-cleaned,prior to installation. in the ne)d well,and is analyzed along with the other samples.
<br /> The field blank analysis demonstrates the effectiveness of the
<br /> After setting the casing inside the hollow-stem auger,sand or in-field cleaning procedures to prevent cross-contamination.
<br /> gravel fitter material is poured into the annular space to fill from
<br /> boring bottom to generally 1 foot above the perforated interval: To minimize the potential for cross-contamination between otj
<br /> A 1-to 2-foot thick bentonite plug is set above this filter material welts,
<br /> lt ltold well development
<br /> s either and
<br /> water
<br /> steam sampling
<br /> acleaned for properlyequipment ted i
<br /> to prevent grout from infiltrating the fixer pack Either neat
<br /> cement,containing about 5 percent bentonite,or sand-cement between use. As a secondary precautionary measure,wells
<br /> grout is then tremmied into the annular space from the top of are sampled in order of least to highest concentrations as
<br /> the bentonite plug to near surface. A traffic-rated vault is established by available previous analytical data, f
<br /> installed around each wellhead for wells located In parking lots In the event the water samples canna be submitted to the
<br /> or driveways,while steel"stovepipes"are usually set over
<br /> wellheads In landscaped areas. analytical laboratory on the same day they are collected(e.g.,
<br /> r due to weekends or holidays),the samples are temporarily
<br /> After installation,the wells are thoroughly developed to remove stored until the first opportunity for submittal either on water ice
<br /> residual ddlling materials from the wellbore,and to improve well in a cooler,such as when in the field,or in refrigerator at f.
<br /> performance by removing Cine material from the filter pack that Apes office,
<br /> may pass into the well. Well development techniques used
<br /> may include pumping,surging,bailing,swabbing,jetting, SOP - 12
<br /> (tushing,and air-lifting. All development water is collected MEASURING LIQUID LEVELS USING
<br /> either in drums or tanks for temporary storage,and properly WATER LEVEL'METER OR ]INTERFACE.
<br /> disposed of depending on laboratory analytical results. To PRO13E t
<br /> minimize the potential for cross-contamination between wells,
<br /> all development equipment is either steam cleaned or properly Field equipment used for liquid-level gauging typically includes
<br /> washed prior to use. f=ollowing development,the well is the measuring instrument(water-level meter or Interface probe)
<br /> allowed to stand undisturbed for a minimum of 24 hours before and product bailer(s). The field kit also includes cleaning
<br /> its first sampling. supplies(buckets,solution,spray bottles,and deionized water)
<br /> to be used in cleaning the equipment between wells.
<br /> SOP - 7
<br /> GROUNDWATER PURGING AND Prior to measurement,the Instrument tip is lowered Into the well
<br /> SAMPLING until it touches bottom. Using the previously established top-of-
<br /> casing or top-of-box(i.e.,wellhead vauik)point,the probe cord
<br /> Prior to water sampling,each well is purged by evacuating a (or halyard)is marked and a measuring tape(graduated In
<br /> minimum of three wetted well-casing volumes of groundwater. hundredths of a foot)is used to determine the distance
<br /> When required,purging will continue until either the discharge between the probe end and the marking on the cord. This
<br /> water temperature,conductivity,or pH stabilize,a maximum of measurement is then recorded on the liquid-level data sheet as
<br /> ten wetted-casind volumes of groundwater have been the"Measured Total Depth"of the well.
<br /> recovered,or the well is bailed dry. When practical,the
<br /> groundwater sample should be collected when the water level When necessary in using the Interface probe to measure liquid
<br /> In the well recovers to at least 80 percent of its static level. levels,the pr6be is first electrically grounded to either them"
<br /> stove pipe or another metal object nearby. When no ground Is,.
<br /> The sampling equipment consists of ether a"Teflon"bailer, available,reproducible measurements can be obtained by
<br /> PVC bailer,or stainless steel bladder pump with a'Teflon" clipping the ground lead to the handle of the interface probe
<br /> bladder. If the sampling system is dedicated to the well,then caSa•
<br /> the bailer is usually"Teflon,"but the bladder pump is PVC with
<br /> a polypropylene bladder. In general and depending on the
<br /> intended laboratory analysis,40-milliliter glass,volatile organic
<br /> SOP- Monitoring Wells
<br />
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