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-z+. <br /> @'r��>i R�+S.,:..1 <br /> P'. >..,a— t `_., . ,t„ .1. SE£,...a ;r,:: . :Fa_;•. r._�-. , .. R.f�.:.,. � �.(� ,r i 4- ' r. r, r <br /> -.�^ <br /> i i��Nt f�-r .7•r_,� '� i=1 ,r� �.�r� .� �,�.. � _r t., x_, .� s jx,,r . .,�': .,vf „ ,+z,�i."",�' t .;z h .�. ,r .d d.v �-- e, G.. fa., g,. <br /> y '� r.y',,,�1 e. �:F- s }', 'ik:• 7. h ._ !.)f4, ,r .,,.-- ' rµ .,.jy,; ,5 .Z 'du -L�[ . r r•�it .pry ..Jt,x♦:.,�-.�.,''.` ',?:: <br /> l a�`r'�. �kxyn, �. e3, r' ,,� �' -�l- +'�4i. r...:�-.yE>k- .if:-. 1,4, . P. S� .r! y. - � F `{,. "V.• _.Li. ,-� #.y{�,5.. r-r �.,�. "::� -:�� <br /> La 7,r it - :�r � ,i"." l�',r, 7, f�- o y¢ r,_ „'� a f-.• J. ,,,,��L�,.' 4 �Y";w,�6 ?r _.�ft 7- _. S� I .l i��'. •.a3�:.n.4. _,.a>�,:a. C. :�-, It` <br /> �� <br />"ra <br /> 2. a <br /> 1 j <br /> 1 <br /> z <br /> i <br /> in <br /> t:. <br /> 15. 5 foot sample fSee Drill Log) . Field inspection and PID <br /> ,.j testing did not record the presence of organic vapors or <br /> visual staining of soils typically associated with waste oil <br /> contamination in Boring SB2 to a depth of 17.5 feet. Slight <br /> to strong gasoline hydrocarbon odors were noted in boring <br /> SB3 to a depth of 31.5 feet, the maximum depth explored. <br /> PID readings in the 20.5, 25.5 and 30.5 samples were 4751, <br /> 4122, and 1400 ppm, respectively. The depth to first <br /> t,N groundwater beneath the site was recorded approximately 32 <br /> feet below grade in boring SBI. ----- ' <br /> ti <br /> 4.2 Laboratory Analysis - Soil <br /> The laboratory analysis of samples collected at 20.5, 25.5 <br /> and 30.5 feet in boring SBI did not record the presence of <br /> BTEX above the 0.02 ppm method detection limit_ The TPH-G <br /> concentrations in these samples and the TPH-PT concentration <br /> in the 30.5 foot sample were not detected above the 5.0 ppm <br /> detection limit (Table 1 ) . Elevated concentrations of BTEX <br /> and TPH-G were recorded in the 20.5, 25.5 and 30.5 samples <br /> from boring S� The 30_5 footsa e exhibited the highest <br /> levels with BTEX and TPH-G concentrations of 215, 967, 279, <br /> 1358 and 11089 ppm, respectively. The laboratory test <br /> Y <br /> results for these samples, including BTEX concentrations, <br /> are summarized in Table 2. The 11.5 and 16.5 foot samples <br /> from boring SB2 did not record EPA 8010 constituents, <br /> including Chloroform and Trichloroethane, above method <br /> detection limits (Table 3) . Laboratory data sheets, chain <br /> + of custody forms and laboratory quality control data are- <br /> presented <br /> represented in Appendix IV. <br /> 5.0 CONCLUSIONS <br /> The result of field inspection and laboratory apalysis of <br /> # soils collected during tank removal and subsequent borings <br /> drilled within the former tank pits, indicate hydrocarbon <br /> contamination has occurred as a result of leakage of <br /> s gasoline product to the subsurface from 'Tanks A and C. The <br /> absence of significant contamination in the pit sample from <br /> Tank B and the non-detectable concentrations of EPA 8010 <br /> constituents (including Chloroform and Trichloroethane) in <br /> samples collected from sail boring SB2 indicate no <br /> significant leakage of waste oil. occurred at this location. <br /> ; . Primary source control has been achieved at the site with <br /> the removal of the three u/g tanks and associated product <br /> lines. The only other source for continuing contamination <br /> are the soils contaminated by the leakage of gasoline <br /> product from Tanks A and C. <br /> The elevated concentrations of total petroleum hydrocarbons <br /> recorded in soils to a depth of 30. 5 feet beneath Tank A <br /> indicates a significant volume of gasoline has leaked. The <br /> k highest TPH concentration detected in the 30.5 foot sample, <br /> S Y <br /> 4 <br />