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2900 - Site Mitigation Program
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PR0508450
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/29/2019 11:58:23 AM
Creation date
5/29/2019 11:10:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508450
PE
2960
FACILITY_ID
FA0008087
FACILITY_NAME
DDJC-TRACY
STREET_NUMBER
25700
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
01
SITE_LOCATION
25700 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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REC , <br /> WATER QUALITY SITE ASSESSMENT MAR 1 7 1993 <br /> FOR SOILS AND GROUND WATER 11&L HEALTH <br /> This paper will describe how a site-wide water quality site assessment should be conduct- <br /> ed to evaluate the impact of soil contaminants on ground water quality. <br /> The first step is to establish background conditions for both soils and ground water. The <br /> purpose of establishing background concentrations is to accurately assess whether detec- <br /> tion of a constituent represents man-made contamination or a naturally occurring concen- <br /> tration. Assessment of background may also be necessary in determining cleanup levels <br /> that are protective of the quality of waters of the State. If a constituent is detected at a sta- <br /> tistically significant concentration above background, then it is considered a constituent <br /> of concern for water quality and remediation may be necessary to protect beneficial uses <br /> and to restore and protect native water quality, as feasible. A site-wide assessment of <br /> background levels should be conducted in accordance with the regulations of Article 5 of <br /> Chapter 15, Division 3, Title 23 of the California Code of Regulations (CCR). <br /> The stratigraphy of the unsaturated and saturated zones beneath the facility should be <br /> well defined by discharger. Hydrogeologic zones must been clearly defined. This is im- <br /> portant in order to delineate contaminant transport pathways and water resources that <br /> have or may be affected by site contaminants. <br /> Background levels need to be established for all distinct lithologies above and below the <br /> water table. In urban and industrial areas it is often difficult and sometimes impossible to <br /> establish true background concentrations for shallow soils above the water table, due to <br /> extensive past waste management activities. Off-site, undisturbed areas may need to be <br /> sampled. It will be necessary to establish site-wide background levels for soils based on <br /> extractable(soluble)concentrations,determined by a variation of the Title 22 CCR Waste <br /> Extraction Test(WET). By using extractable concentrations, the assessment determines <br /> what quantities of unsaturated zone contaminants and constituents are mobile and pre- <br /> sent a threat to water quality. <br /> First, the process for establishing background concentrations in ground water and select- <br /> ing appropriate water quality limits will be discussed. Second, the process for establish- <br /> ing extractable background concentrations in soils will be described. Finally, this paper <br /> will describe how to convert soil extract data into a form for comparison with back- <br /> ground ground water concentrations and water quality limits. <br /> Site-wide Background Assessment of Ground Water Zones <br /> 1. Select a minimum of four ground water sampling sites that,based on available infor- <br /> mation,are out of the influence of past waste management activities. These should <br /> be upgradient of existing and potential site contaminants. Off-site sampling may be <br /> necessary if unimpacted areas cannot be found on-site. <br />
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