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ARCHIVED REPORTS_XR0012640
Environmental Health - Public
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ARCHIVED REPORTS_XR0012640
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Last modified
6/9/2020 10:13:42 AM
Creation date
6/9/2020 9:50:08 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012640
RECORD_ID
PR0545764
PE
3528
FACILITY_ID
FA0005330
FACILITY_NAME
ISC WINES OF CALIFORNIA INC
STREET_NUMBER
1
Direction
W
STREET_NAME
TURNER
STREET_TYPE
RD
City
LODI
Zip
95424
CURRENT_STATUS
02
SITE_LOCATION
1 W TURNER RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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l <br /> t <br /> R IM <br /> These tests are viewed as important t-y the writer owing; to the <br /> fact that radial drainage of water into the pit through <br /> essentially flat- lying beds should give a more re presentative <br /> sample of formation water than samples from relatively isolated <br /> mz)nitoring wells . if an infiltration plume existed, lying; in an <br /> attitude that precluded detection by testing water from the <br /> monitoring wells , it should be detected in the pit seepage. Also <br /> drainage volume of the surrounding reservoir , when compared to <br /> the small amount of water recovered from a monitoring well , is <br /> enormous . The fact that these tests are on "mingled" formation <br /> water is an advantage rather than a disadvantage. <br /> Industrial Wells <br /> On July 26, 1989 water samples were collected from the three in- <br /> dustrial wells under the direct observation of the DHS. IW-1 is <br /> located at the east edge of the excavation and IW-2 and IW-3 are <br /> located southwesterly about 60 ' to 75 ' from the excavation ( Fig. <br /> 6 and Appendix A- 12 map) . EPA current method 602 was used to <br /> test for BTEX and GCFID 5030, as specified by the DHS, to test <br /> for TVPH. No hydrocarbons -r-re found above the testing limits . <br /> These data are surrtmied on Table C. <br /> Soil Smples <br /> On July 31 , 1989, CES and JTO, witnessed by the DHS representa- <br /> tive, collected samples at 13 locations around and in the <br /> deep excvation and 16 samples from the sidewalls, 4 each from the <br /> north, south, east and west . These samples were taken from the <br /> approximate depths of -40 ' , -35 ' , -30 ' and -25 ' , g. l . All samples <br /> were approximately located as approved by Diane Hinson, Appendix <br /> 14. All soil samples were collected by pushing laboratory Supp- <br /> lied 2" X 6" brass sleeves into the soil . Standard <br /> collection procedures as listed above were Used. <br /> The instructions given to the laboratory, as agreed to by the <br /> DHS, ( stated by JTO) , was to analyze samples one through <br /> thirteen for BTEX and TEH, rising current EPA methods S020 and <br /> GCFID 5030, and 5015, GCFID 3550. For the sidewall samples above <br /> pit bottom; that is, N-S-E-W, labeled as follows, A at -401 , B ut <br /> -351 , C at -30 ' and D at -25' ; the upper ones were to be analyzed <br /> only if the lower sample (A) showed contamination. All of the "A" <br /> samples were negative at the limits of detection and B, C, and D <br /> samples were not analyzed. <br /> - - --- _.__ <br /> -DISCUSSION ...- .. <br /> contamination in small amounts ,vas foundinonly three of the ' <br /> samples from the pit botton. Nos . 8, 10 and 11 . The amounts were <br /> small , the highest being No. 11 , from near Pit center. No. ll . had <br /> a TEH of 52 mg/kg and Xylene detectable at . 35 mg/kg (':able B-1 ) . <br /> 9 <br />
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