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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
1/24/2020 3:08:30 PM
Creation date
1/24/2020 2:34:59 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0505432
PE
2960
FACILITY_ID
FA0006779
FACILITY_NAME
DIVIDEND PROPERTY
STREET_NUMBER
13170
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
13170 W GRANT LINE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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'00 P--e Street, 1 0th Floor <br /> San F-arcisco. CA 94111 <br /> '415; 434-9400 • FAX C4151 434-1365 GEOMATRIX <br /> 7 November 1994 <br /> Project C2677A <br /> Ms. Wendy Cohen <br /> Regional Water Quality Control Board - Central Valley Region <br /> 3443 Routier Road, Suite A <br /> Sacramento, CA 95827-3098 <br /> Subject: Response to RWQCB Letter dated 18 October 1994 <br /> Dividend Property <br /> Tracy, CA <br /> Dear Ms. Cohen: <br /> Geomatrix Consultants, Inc. (Geomatrix) has prepared this letter on behalf of Chevron Pipe <br /> Line Company (CPLC) and Texaco Trading and Transportation, Inc. (TTTI) in response to <br /> the letter of 18 October 1994 from Mr. John Moody of your office that requested additional <br /> soil sampling and raised several other matters relating to further work at the Dividend <br /> Property. Mr. Moody and I discussed his comments in a telephone conversation on 31 <br /> October 1994, the substance of which is incorporated into this response. <br /> STOCKPILED SOIL <br /> Mr. Moody's letter stated that the detection limits for polynuclear aromatics (PNAs) and <br /> semi-volatile organic compounds (SVOCs) from the stockpiled soil analysis appeared high <br /> and additional analyses at lower detection limits were required to confirm that use of the soil <br /> as backfill material would not pose a threat to water quality. As he and I discussed on 31 <br /> October, the state of the practice for analysis of soil samples for PNAs or SVOCs is EPA <br /> Method 8270 (or equivalent), with practical quantitation limits of about 330 µg/kg. The <br /> quantitation limits can be lowered to about 200 µg/kg by quantitating the PNA fraction only <br /> (EPA Method 8270 or 8100). There are a few laboratories in the State of California (two <br /> that I know of) that will analyze soil samples for PNAs using EPA Method 8310, which can <br /> usually achieve detection limits of between 5 and 200 µg/kg depending on the specific PNA. <br /> These analyses are typically performed in support of risk-assessment activities, not for site <br /> characterization. Of course, analysis for PNAs by any of these methods may result in higher <br /> detection limits if there are interferences due to high concentrations of petroleum compounds <br /> present in the sample. The detection limits stated herein are typically for unaffected or <br /> slightly-affected soil samples. <br /> As Mr. Moody and I discussed, Geomatrix generally understands the 330 µg/kg detection <br /> limit for PNAs in soil is adequate for characterization and protective of groundwater, because <br /> PNAs have very low water solubilities and very high partitioning coefficients (Kw or Ka). <br /> As a result, PNAs sorb strongly to soil and do not enter the aqueous (dissolved) phase unless <br /> Geomatrix Consultants, Inc. <br /> Engineers Geologists,and Environmental Scientists <br />
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