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W nv <br /> p <br /> 30--December 1999 <br /> AGE-NC Protect Na 95-0121 L N <br /> Page 3 of 5 <br /> calculated to be between 10 26 feet and 10 79 feet below mean sea <br /> elevations at the site were cal e 3 Ground water elevation at the site decreased <br /> water el events , <br /> level, gr en the June 1999 and the October 1999 Wound water monitoring <br /> ground water elevations are depicted m igm' , <br /> an average 1 72 feet between W-2,MW-3, MW-6 and <br /> wells MW-1, Nl <br /> per mile and directed <br /> The general ground water gradient in the area bound by approximately 10 feet p roximately 8 <br /> MW-7 was calculated to be approximately Q . w terft/ or <br /> t (Figure, 3) The ground water surface elevation �hM�e�s�iW`4 and MW- <br /> towards the north ( Sdeeper ground water The <br /> feet to 16 feet above the slotted screen intervals nd eld data representative of -3gr V1-4 and VW-6, <br /> 7 Therefore these wells are-drowned", <br /> screened through wells VW , <br /> ground water elevation at the site appropriatelyound water <br /> therefore these wells yield data re resentative of shallow ground <br /> WATER SAMPLES <br /> 3 2 LABORATORY RESULTS OF GROUND W_2 MW-3,MW-4, MW-7, <br /> collected from wells MW-1, M per liter (���)to <br /> TPI-1-9�' detected in water samplesin from 194 micrograms p Mw-2, MW-3, <br />` VW-4, VW-6 and EW-i at concentration lean ollected from wells MW-1, 1 to 4;200 <br /> VW-3, in from 1301u� <br /> 47,000 1,4g/i TPH-d was detected in water same <br /> W-7, VW-3, VW_4� VW-6 and EW-1 at concentrations rang g <br /> W-4,Nl omatograms for the samples did not have typical diesel <br /> M reported that the chr <br /> g/l, the laboratory <br /> charactenstics W_1 MW-2,MW-3' <br /> Samples collected from M � 1 and , <br /> ounds were detected in water camp between 2 2 �gl <br /> Nanous BTEX camp VW-4, VW-6 and EW-1 at concentrations ranging les collected <br /> MW-4, 1,4W-7, VW-3j 1 respectively <br /> -3 MTBE was detected by EPA Metho�0 Q2Q >n water same <br /> 14,000µg41{benzene,MW } 1 and 1 , <br /> from wells MW-2 and VW-4 at concentrations of 2241�1� collected from wells <br /> EPA Method 8260 Modified in water samples and 270 µgl1 TBA was <br /> ` MTBE was detected utilizing in between 12 A, at m <br /> M <br /> W-1 Mw-2,VW-4 and VW-6 at cont ttatlons ells MWan, MW-4 acid VW-6 at co laboratoiry analysis <br /> detected in water samples collected from ounds were detected during the ory reports <br /> i l No other fuel oxygenated camp 2 The <br /> as 72 1�� ound water samples are summarized iri beblll ,A,nalyt cal Inc t1 D 23911 <br /> Ar'ialytical results of the gr <br /> Castle Analytical Laboratory Reference No 2550 and Mc amendix B <br /> ' ( and chain-of-custody forms are presented in APp ' <br /> through 23919} <br /> ` - from MW-3 and EW-1 were. <br /> e submitted for rnicrob�neral microbial <br /> Ground water samp}e$ collected frwere detected <br /> analysis The results of the ariaiysis indaircida�a CFUs <br /> and physicochemical laboratory forming amts(CFUs) from MW-3 microorganisms were <br /> population of 1,200 microbial colonyed that drocarbon-degrading bionutnents (carbon, <br /> from EW-1 The labor atory inbialtenumerattiion aind that naturally occurring <br /> missing frorri the general micro <br /> s � � Advanced GeoEn�kronmental,inc <br />