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2. Rinse the:turbidity Probewith deionized ter then place in the standard solutiorL <br /> 3< Adjust the meter for appropriate turVidity scale dien read the turbidity, <br /> . If t 4ustrawt on the meter to corvext the insWjM04t to rtad <br /> c COMX:t turbidity. <br /> The calibradoitprocess winbe recorded on a turbidity cahlx2don log. A Sample <cn <br /> Log is Iccated ' C Copies of mlibradon lop for are kept <br /> in a bhxfcr at the office. 1he loss am mviewed periodically top assess whed=the imsUment is <br /> becoming more diflicuft to dumeforc n e nt by the , or if <br /> new probes are require& <br /> Equipment Decontunination <br /> To reduce the ktential f or Samples.mrapling <br /> cTupmc= that is used repeatedly at dinevent wells ( _xnet=) will< be ed in a <br /> n and triple -with ,o <br /> monitoring" ls am equippedi dedicated-sampling v which-will4Y not- <br /> require <br /> dtcontunin;ation- Sterile factory scaled disposable bailers are wedto collect the samplM Bager <br /> cord is replan <br /> Maftoring Order <br /> , <br /> m <br /> Groundwater monitoring will be _h that depth to water numsurements end <br /> is petformod in dic least contaminatedresults). Measurcment and <br /> -wellssampling order wM then mow irom les:s=impacted as <br /> done to reduce the potential e s can be am coatatninatiul. <br /> order bc&s at 20 and then MW-12,vvhich the <br /> wt&.'listed in order, to b.-- sampled am MW-15, -10. -1 and -3_ Th * contain <br /> evidenceof chemical impacts. lbo last wells to bee'samplod, . order,< c -l4-13 <br /> and -2- ' Proposed vittl 16 will be samoed in an Vpropriateng on <br /> =Wdtx=U am d (d' ) inthe well upon the first SaUVIm& Initially, -I6 will be <br /> ll sampled.. < <br /> 23-4 I IOR3Z A-. 14,2000 <br /> COWWA 200 Kk , <br />