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SITE INFORMATION AND CORRESPONDENCE FILE 1
Environmental Health - Public
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2900 - Site Mitigation Program
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SITE INFORMATION AND CORRESPONDENCE FILE 1
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Last modified
7/24/2019 4:35:43 PM
Creation date
7/24/2019 4:28:58 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0542208
PE
2960
FACILITY_ID
FA0024243
FACILITY_NAME
CALIFORNIA TANK LINES
STREET_NUMBER
3105
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
17512028
CURRENT_STATUS
01
SITE_LOCATION
3105 S EL DORADO ST
P_LOCATION
01
QC Status
Approved
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Nov - 12 - 96 07 : 21P Sierra - Pacific Grnd water 916 933 - 3197 P . 02 <br /> Sierra-Pacific Groundwater Consultants, Inc. <br /> Geologists, Engineers, and Compliance Specialists <br /> November l2, 1996 <br /> Mr. Steve Sasson <br /> San Joaquin County Public Health Services <br /> Environmental Health Division <br /> P. O. Box 388 <br /> Stockton, California 96201A88 <br /> (Via Facsimile) <br /> Dear Mr. Sasson, <br /> As we discussed on the project site yesterday afternoon, this letter has been prepared to <br /> summarize our agreed-upon additional work at the California Tank. Lines Facility, located at 3105 <br /> South E1 Dorado Street in Stockton. We have completed two of the original three borings <br /> scheduled in our workplan dated August 28 , 1996 and amended by letter dated October 15, 1996, <br /> as approved by you. We deepened the second boring, in the center of the former UST excavation <br /> area, from 20 to 40 feet, as we were encountering continuing evidence of soil contamination <br /> based upon field evidence (odors and photoionization detector readings). On reaching <br /> groundwater at 40 feet below ground surface (bgs), we found evidence of contamination <br /> necessitating construction of a ground-water monitoring well (see attached revised figure3). <br /> The new scope of work will include construction of the monitoring well, and three additional soil <br /> borings at the locations indicated on the attached figure. The monitoring well will be constructed <br /> oft-inch PVC, screened from approximately 30 to 50 feet bgs with 0.010-slot PVC well screen. <br /> A 92112 Lonestar sand filter pack will be placed to a paint 28 feet bgs in the well, or 2 feet above <br /> the top of the well screen. A minimum oft feet of bentonite chips, hydrated in place, will be <br /> placed above the sand as a seal against descending waters in the annulus around the casing pipe, <br /> Blank PVC casing will be placed above the well screen to within 0. 5 feet of the ground surface. <br /> A flush-mounted traffic-rated well box will be set in concrete around the top of the casing. The <br /> well will subsequently be developed by surging and purging, and will be sampled in accordance <br /> with Tri-Regional Guidelines dated 10 August, 1990, published by the California Regional Water <br /> Quality Control Board . <br /> In each of the new soil borings, samples will be collected at five-foot intervals beginning at 15 feet <br /> bgs, continuing to approximately 40 feet bgs. At that paint, hydropunch equipment will be driven <br /> approximately 5 feet into the saturated zone, and a grab sample of groundwater will be retrieved <br /> using a small-diameter PVC well screen and a stainless steel bailer. All such equipment shall be <br /> pre-cleaned or decontaminated at the site in accordance with the procedures in the approved <br /> workplan. The groundwater samples obtained will be analyzed for total petroleum hydrocarbons <br /> (TPH) by EPA method 8015-modified, for benzene, toluene, ethylbenzene, total xylene (BTEX), <br /> and for MTBE by EPA method 8020 . Should the 8020 results indicate the presence of MTBE in <br /> any sample, an analysis of that sample for MTBE by EPA method 8270 will also be run. The <br /> (916) 913-1468 <br /> 4911 Winlpl.r nriv Suite 4 Fa Dnesdn Hills, C.e11M1lnlln 95762 (916) 933-31W FAX <br />
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