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,�i u. �., �' ° � ! y. {:, _ a [, �r �,� ` � �x sy i!, �+; +' ' � a _ C�_l•.gg+ �, K�r,�lyl it <br /> , i�� {� - uF <br /> '•,'` L _..-}+ f t •A y 'yv - r+. ' a. ,�. r 'ry , xe ' 'hi-y_ 'fin Irl [ �� 1.1 + �' i , II.aI_: <br /> i��i fi.4.rr -I�4itr�' '�+S -i3.r -�'I• <br /> ' 16 February 2001' ' { <br /> Irk <br /> + , fi AGE-NCPro�ecfNo 95 0114 } � <br /> Page'2 of 5, <br /> '1 '•�r ,• '' _i f, + a ! 'MI 'tJ + It r. , `,ly .•... <br /> F - •E w } + <br /> EPA-'approved,volatile-.organic'analyslsE vials containing 0.5 ml of hydr6chl66.bi acid (18%),;as a`. <br /> ' °'sample preservative and were labeled The samples were,trapsported'in'a-chi lled container under '..,. <br /> ` ch'airi-of-custod to•IVIcCam bell Analytical Inc. MAI `fa State-of Califoinia.De artmerif of Health <br /> 1 y Servlces'(DHS)-certified laboratory.(#1'644):Samples were analyzed in accordance with <br />,.r. , v_.-,EPArMetliod' 8015 Modified for total'petroleum hydrocarbons ,'guaritlfied-as"stoddard, <br /> solvents (TPH=ss), <br /> i ;EPA Method.8020 for volatile aromatics -benzene,,toluene. ethylbenzene and total xylenes. <br /> (BTEX);.and <br /> t= '.- 1 for volatile halocarboris HUOCs <br /> . EPA Method 80. 0 ,( ). . � <br /> 1-0. - FINDINGS , <br /> Ground water flow direction andgradient were inferred from the field data..The current distribution <br /> of dissolved.petroleum.hydrocarbons and dissolved chlorinated hydrocarbons were assessed from <br /> laboratory analytical'results of the ground water'sampl'es. <br /> -'3.1. , '.GROUND WATER GRADIENT AND DIRECTION <br /> Zhq groundwater elevatlons.were calculated by.subtracting the measured depth to ground water-from <br /> the surveyed casing elevations (Table 1): Ground.water.elevations were plotted'ari:cohloured on- <br /> a scaled site map. . ' <br /> The average ground water elevation at the site=decreasedapproximately 2.4 Meet between the; June <br /> and ' ceniber-'2000 sampling events. During the Deceirrber'2000 g'round'water'monitoring event;' t I <br /> 6.' <br /> well depth to ground water at th_e'site •ranged from 22:25 to 22.90 feet:below,topsof the.well casiii& <br /> l The groundwater gradient:and':flow' direction were.variable'across the site during the-December,.,. - <br /> `: ; 2000 monitoring,event.,Ground'water-flow direction'variedfrorri northeast in..the.,eastern portion.of <br /> ' the site and'under the'building, the'area of highest ground water contamination:Ground.water-flow" <br /> was inferred to.be directed westward away from the former UST on the'west'side of the site. The <br /> highest,gradient was'approximately 0.002,generally'toward the northeast,from well MW 3. <br /> Groundwater elevation data are summarized-in Table_1. The relative-ground water elevation,for the ,. • , ^ <br /> De`cember•2QOO ground water monitoringevent.is depicted in Figure_ 3. . <br /> •'•' , .� t. ,. `• — •. — •' _. . .— '. •� ,y T4s' I['.. <br /> Advanced GeoEnvironinental,Inca <br />