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2900 - Site Mitigation Program
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PR0182171
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/19/2020 1:53:47 PM
Creation date
5/19/2020 1:48:45 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0182171
PE
2954
FACILITY_ID
FA0004080
FACILITY_NAME
NAVCOMSTA
STREET_NUMBER
305
Direction
W
STREET_NAME
FYFFE
STREET_TYPE
ST
City
STOCKTON
Zip
952035000
CURRENT_STATUS
01
SITE_LOCATION
305 W FYFFE ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
TSok
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EHD - Public
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WATER QUALITY SITE ASSESSMENT <br /> FOR SOILS AND G ROUND WATER �RA <br /> po F7 <br /> This paper will describe how a site-wide water quality site assessment should be con- <br /> ducted 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 con- <br /> centration. Assessment of background may also be necessary in determining cleanup <br /> levels that are protective of the quality of waters of the State. If a constituent is detected <br /> at a statistically significant concentration above background, then it is considered a con- <br /> stituent of concern for water quality and remediation may be necessary to protect benefi- <br /> cial uses and to restore and protect native water quality, as feasible. A site-wide assess- <br /> ment of background levels should be conducted in accordance with the regulations of <br /> Article 5 of 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 the discharger. Hydrogeologic zones must be 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 <br /> to establish true background concentrations for shallow soils above the water table, due <br /> to extensive past waste management activities. Off-site, undisturbed areas may need to <br /> be sampled. It will be necessary to establish site-wide background levels for soils based <br /> on extractable (soluble) concentrations, determined by a variation of the Title 22 CCR <br /> Waste Extraction Test (WET). By using extractable concentrations, the assessment deter- <br /> mines what quantities of unsaturated zone contaminants and constituents are mobile and <br /> present 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 in- <br /> formation, are out of the influence of past waste management activities. These <br /> should be upgradient of existing and potential site contaminants. Off-site sampling <br /> may be necessary if unimpacted areas cannot be found on-site. <br />
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