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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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be equal to"n". The Designated Level for arsenic in differences in the test methods,a 20-fold dilution factor <br /> leachate at this site would be equal to(0.005 x n) is used in calculations based on TCLP results.] For the <br /> milligrams arsenic per liter of leachate. Figure 7 example,the Soluble Designated Level for <br /> arsenic is equal to(0.005 x n + 10)mg/1 of WET <br /> The goal in calculating Designated Levels for a solid extract. <br /> waste is to determine concentrations of soluble con- <br /> stituents in the waste above which leachate may carry Concentrations of constituents in landfill leachate <br /> them to ground or surface waters in amounts that should not be confused with concentrations of constitu- <br /> could cause water quality goals to be exceeded. There- ents in extract from the Waste Extraction Test or the <br /> fore, the next step in the methodology is to convert the Toxicity Characteristic Leaching Procedure. They are <br /> Designated Level for leachate into one which may be not the same. Concentrations of constituents in <br /> applied to leachable concentrations of constituents in a leachate are the result of the accumulation of constitu- <br /> solid waste prior to disposal. Rationale presented by ents from the waste as moisture migrates through a <br /> DTSC in the 1984 Statement of Reasons for the Hazardous landfill or waste pile. The ratio of liquid-to-solids is <br /> Waste Identification Regulations indicates that the not expected to be large within a landfill. Concentra- <br /> concentrations of constituents in leachate could either tions of constituents in the extract from the WET or the <br /> be numerically higher or lower than the soluble TCLP are the result of specific laboratory procedures <br /> constituent concentrations in the solid waste prior to where waste constituents are extracted from a solid <br /> leaching. In the calculation of Designated Levels, these waste by an extract solution under a large liquid-to- <br /> concentrations are assumed to be numerically equal,as solids ratio necessary to ease sample handling. The <br /> in DTSC's Statement of Reasons. Therefore, the Soluble extract from the WET or the TCLP is, therefore,not a <br /> Designated Level for a constituent in a solid waste is simulation of leachate,but a means to measure the <br /> numerically the same as the Designated Level for the amounts of waste constituents that may be leached from <br /> same constituent in leachate which forms at the base of the waste in a landfill. As stated above,actual landfill <br /> the landfill—the water quality goal times the environ- leachate is expected to have considerably higher <br /> mental attenuation factor. In the example of Figure 7, pollutant concentrations than WET or TCLP extracts <br /> the Soluble Designated Level for arsenic in the solid due mainly to this difference in liquid-to-solids ratio. <br /> waste is(0.005 x n)milligrams of soluble arsenic per <br /> kilogram of waste. <br /> CONTAMINATED SrrE AssEssmurr <br /> Soluble concentrations of constituents in solid wastes <br /> are determined by performing the Waste Extraction DTSC has prepared guidance materials which contain <br /> Test(WET)from Title 22 of CCR,Division 45,Chapter procedures for performing risk assessments and <br /> 11,Appendix II,or a variation of this test. (The Toxic- determining cleanup/mitigation levels for sites con- <br /> itv Characteristic Leaching Procedure(TCLP) from taminated with toxic substances. The object of these <br /> Title 22 of CCR,Division 45,Chapter 18,Appendix 1,is procedures is to prevent toxicologic impacts on hu- <br /> used for volatile waste constituents.] The WET in- trans and other potential'biological receptors of <br /> volves a ten-fold dilution of solid waste into an extract concern". While sufficient to cover DTSC's concerns <br /> solution,agitation for 48 hours,followed by filtration regarding site assessment and cleanup,the procedures <br /> and analysis of the liquid phase. Results are expressed in these documents are not designed to fully protect <br /> in milligrams of extractable constituent per liter of water resources that may be adversely impacted by site <br /> extract solution. Therefore,the WET extract is ex- contaminants,as required by the Porter-Cologne Water <br /> pected to be ten-times more dilute than actual landfill Quality Control Act. Therefore,another methodology <br /> leachate. The Soluble Designated Level for a constitu- must be used by the State and Regional Water Boards <br /> ent of a solid waste,expressed in milligrams per liter to fulfill this need. <br /> (mg/1)of WET extract,is equal to the water quality <br /> goal times the environmental attenuation factor Comparison of Figures 7 and 8 reveals that the threat <br /> divided by the ten-fold dilution of the test. [Due to posed to water quality by contaminated soils is similar <br /> Page 14 California's Water Quality Standards <br />
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