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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 Qualitv Site Assessment -3- IDR A FT 5 November 1992 <br /> Determination of Water Quality Limits <br /> To determine whether past waste management activities have degraded or have the po- <br /> tential to degrade water quality, applicable water quality limits need to be determined <br /> for the contaminants involved. Water quality limits are numerical contaminant concen- <br /> trations, above which contaminants are considered to have adversely impacted beneficial <br /> uses (to have limited certain uses) of waters of the state. Water quality limits are used to <br /> implement the numerical and narrative water quality objectives contained in the state <br /> and regional Water Quality Control Plans. <br /> To select water quality limits, determine the following: <br /> ❑ beneficial uses of the water body being investigated; <br /> ❑ applicable water quality objectives to protect those beneficial uses; <br /> ❑ numerical water quality limits that will implement all applicable water quality ob- <br /> jectives (i.e. drinking water standards, water quality criteria for agriculture,health <br /> advisories, Proposition 65 No-Significant-Risk Levels, etc.); and finally, <br /> ❑ choose the most limiting value to be the water quality limit for each particular con- <br /> stituent,because it is protective of all beneficial uses. <br /> During the site assessment phase of a site investigation, detected constituent concentra- <br /> tions are compared to numerical water quality limits to determine if beneficial uses have <br /> been impacted. During the cleanup level determination phase, the background concen- <br /> tration is selected as the initial cleanup level, based on State Board Resolution Nos. 92-49 <br /> (Policies and Procedures for Investigation and Cleanup and Abatement of Discharges under <br /> Water Code Section 13304) and 68-16 (Antidegradation Policy). If the discharger demon- <br /> strates that it is technologically and/or economically infeasible to achieve background <br /> concentrations, then some achievable cleanup level between background and the water <br /> quality limit can be negotiated. However, any cleanup level greater than background <br /> based on feasibility must still comply with all applicable statutes and regulations, and <br /> must not cause risk to human health and the environment, including beneficial uses of <br /> water. <br /> Site-wide Background Assessment of Soils <br /> 1. Select a minimum of four soil sampling sites that,based on available information, <br /> appear to be out of the influence of past waste management activities. Off-site sam- <br /> pling may be necessary if unimpacted areas cannot be found on-site. <br /> 2. Collect a soil sample at each location from each lithology type present above the <br /> water table. Each soil sample must be large enough to perform the Waste Extraction <br /> Test (WET) procedure with deionized water,' and to analyze the extract for all of the <br /> following: <br /> The standard citrate buffer should be used if the soils are significantly acidic or could become acidic. <br />
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