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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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Water Quality Site Assessment • -3- '✓ <br /> Determination of Water Quality Limits MAR 1 7 1993 <br /> ENVIRONMENTAL HEALTH <br /> To determine whether past waste management activities have degrade ri�IvW'tl V1rr'S <br /> tential to degrade water quality, applicable water quality limits need to be determined for <br /> the contaminants involved. Water quality limits are numerical contaminant concentra- <br /> tions, 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 /> :3 beneficial uses of the water body being investigated; <br /> 7 applicable water quality objectives to protect those beneficial uses; <br /> :1 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 /> Z) 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 background based on <br /> feasibility must still comply with all applicable statutes and regulations,and must not <br /> cause risk to human health and the environment,including beneficial uses of 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 /> Z. 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 our could become acidic. <br />
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