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SITE INFORMATION AND CORRESPONDENCE_1993-2003
Environmental Health - Public
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PR0506824
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SITE INFORMATION AND CORRESPONDENCE_1993-2003
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Last modified
4/7/2020 3:15:47 PM
Creation date
4/7/2020 2:41:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
1993-2003
RECORD_ID
PR0506824
PE
2960
FACILITY_ID
FA0007648
FACILITY_NAME
DDRW - SHARPES
STREET_NUMBER
850
Direction
E
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19802001
CURRENT_STATUS
01
SITE_LOCATION
850 E ROTH RD BLDG S-108
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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�a�b'Ift,i:�'rt� TAL HEALTH <br /> WATER QUALITY SITE ASSESSiE 'r <br /> FOR SOILS AND GROUND AtUT) PM VULrCT <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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