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;F l <br /> 41,_ �� � 7�..'ir Yp�- �-� , -=t �. r = - '- -is"�-- -•'it`' ' , +Y�'�7�s 4.� ..�_� A _:� .. � �- -4 la 3 atr.. _n._ ..i_}� r�r�!f.- <br /> I <br /> 30 November 2005 <br /> „AGE-NC Project No 96-0235' �r <br />' Pagel 10 of 13 <br /> A <br /> I I <br /> 'r 3 51 ' SOUTHERN UST AREA <br /> • A release of petroleum hydrocarbons(TPH-g, TPH-d)and benzene,toluene,ethyl benzene <br /> and xylene (BT EX)''eompounds'withF low"concentrations of, 1,2'DCAr°occurred from-= - ' <br /> dispenser line releases near the northern excavation(UST No 3 area) The southern UST `f <br /> removal samples were non-detected for chemicals of concern Additionally, shallow soll"­ <br /> ` <br /> samples collected iim well MW-2,MW-,7 were non-detect for chemicals of concern TPH-g � Lc� <br /> was reported at a concentration as great as 2,100 mg/kg iri the soil sample collected from the - <br /> northern UST removal'samples, TPH-g was also reported at 320 mg/kg in a soil sample ,SLr1 A <br /> collected at 20 feet bsg in boring B 10 The highest TPH-g and BTEX impact to soil in the <br /> 1 : , upper'vadose zone was removed through excavation t at the UST No' 3 area, it does not <br /> appear that any residual vadose zone hydrocarbons are present in this area The aerial extent <br /> of the soli contamination in soil appears defined to the near the former UST, No 3 area _ <br /> v r k' <br /> Available data is suggestive of a release was most significant at the northern edge of the <br /> former UST No 3 area Once the petroleum hydrocarbons were released to the'subsurface, <br />' the contaminants migrated north under well MW-7 and vertically to a depth of approximately <br /> ,60 feet bsg near well MW42 The,"deep"migration of hydrocarbons indicates a historically <br /> depressed water table depth of near 35 feet bsg >o Y <br /> Based on ten years of ground water monitoring for TPH-g and,BTEX compounds near the <br /> UST No 3 area,the impacts to ground water appear to be stable in the areas of wells MW-l, <br /> MW-2, MW-3 and MW-' 5 The groundwater plume appears to be somewhat symetrical, <br /> extending approximately 80 feet east to west and 80 feet north to south, surrounding UST <br /> No 3 area "' 4 <br /> • Maximum concentrations detected were in the UST No 3 area are TPH-g at 47,000 µg11, q <br /> ' TPH-d at,30,000 µg/l, and�benzene at 5,1001 pg/1 (MW-2) Significant concentratlonsW , ' <br /> TPH-g,'TPH'd and BTEX have been consistently reported in samples collected`from well' <br /> MWS 1', 'located east of the former UST No 3 area The new wells installed(MW-16 through <br /> s T `MWI 24)to define the vertical extent of dissolved hydrocarbron contamination demonstrated.' <br /> "liiriited impact at the�southern edge of the,UST No 3 area,at'a depth of 75 feet bsg, and not ; <br /> greater than 100 feet across the entire UST No r3 area Off-site grab ground water samples _ <br /> were``non-det ce t or hydrocarbon contamination at all`depths sampled A minor release of,-, <br /> ' _ <br />' r 1', -DC_=_7 o y likely occurred with the'TPH, the 1;2-DCA plume appears to be stable in <br /> samples `collected from the monitoring swell network 'The maximum concentration of - <br /> ° 1,2-DCA at the site is currently 41 µg/l'(MW-1)'; ,' ' <br /> The lateral and vertical ektent of TPH and BTEX has been defined by the,sample set Trends ! <br /> '> of contamination detected lin selected, wells are depicted in Appendix F The lateral <br /> ti distribution of hydrocarbon's is depicted iii Figures 4 and 5 as well as by section view in <br /> Figure 7 <br /> Advanced GeoEnvironmental,Inc <br /> 1 <br /> r i , 1 <br /> I i I 1 e <br />