Laserfiche WebLink
leachate at this site would be equal to(0.05 x n)milli- nated Level for arsenic in the solid waste is(0.05 x n) <br /> grams arsenic per liter of leachate. milligrams of soluble arsenic per kilogram of waste. <br /> The goal in calculating Designated Levels for a solid Soluble concentrations of constituents in solid wastes <br /> waste is to determine concentrations of soluble con- are determined by performing the Waste Extraction <br /> stituents in the waste above which leachate may be Test(WET)from§66700 of Title 22 CCR,or a variation <br /> able to carry them to ground or surface waters in of this test. The test involves a ten-fold dilution of <br /> amounts that could cause water quality goals to be solid waste into an extract solution,agitation for 48 <br /> exceeded. Therefore,the next step in the methodology hours,followed by filtration and analysis of the liquid <br /> is to convert the Designated Level for leachate into one phase. Results are expressed in milligrams of ex- <br /> which may be applied to concentrations of constituents tractable constituent per liter of extract solution. The <br /> in a solid waste prior to disposal. Evidence presented Soluble Designated Level for a constituent of a solid <br /> by DHS in the Statement of Reasons for the Hazardous waste,expressed in the same units,is equal to the <br /> Waste Identification Regulations(Title 22 CCR,Divi- water quality goal times the environmental attenuation <br /> sion 4,Chapter 30)indicates that the concentrations of factor divided by the ten-fold dilution of the WET. For <br /> constituents in leachate could either be numerically the Figure 6 example,the Soluble Designated Level for <br /> higher or lower than the soluble constituent concentra- arsenic is equal to(0.05 x n-m-10)milligrams of arsenic <br /> tions in the solid waste prior to leaching. In the per liter of extract. <br /> calculation of Designated Levels,an assumption is <br /> made that these concentrations are numerically equal. Concentrations of constituents in landfill leachate <br /> Therefore,the Soluble Designated Level for a constitu- should not be confused with concentrations of constitu- <br /> ent in a solid waste is numerically the same as the ents in extract from the Waste Extraction Test. They <br /> Designated Level for the same constituent in leachate are not the same. Concentrations of constituents in <br /> which forms at the base of the landfill—the water leachate are the result of the accumulation of constitu- <br /> quality goal times the environmental attenuation ents from the waste as moisture migrates through a <br /> factor. In the example of Figure 6,the Soluble Desig- landfill or waste pile. Concentrations of constituents <br /> in the extract from the WET are the result of a specific <br /> laboratory procedure where waste constituents are <br /> SOLUBLE DESIGNATED LEVEL FOR A extracted from a solid waste by an extract solution <br /> CONSTITUENT OF CONTAMINATED SOIL under a predetermined set of circumstances. The <br /> extract from the WET is,therefore,not a simulation of <br /> DOMESTIC leachate,but a measure of the amounts of waste <br /> WATER constituents that may be leached from the waste in a <br /> WELL CONTAMINATED SITE landfill. <br /> _ As If k0 006 CONTAMINATED SITE CLE.%NUI <br /> oosxn�- '-Mfront <br /> Ntaofoxww <br /> o w.,., rte w�Ee DHS has prepared a document entitled The California <br /> Site Mitigation Decision Tree Manual which presents <br /> m Arsenic <br /> (OAS:n) ° a detailed procedures for determining cleanup/mitiga- <br /> "` * > ;,,..: .�'`� ;" s<'V'>•`k` tion levels for sites contaminated with toxic subs <br /> ie.cirM . <br /> The object of theseP rocedures i P s to revert toxicologic <br /> impacts on humans and other potential "biological <br /> receptors of concern". While sufficient to cover DHS`s <br /> concerns regarding <br /> site cleanups,Ps <br /> the proceduresin this <br /> s <br /> document are <br /> of designed to protect all <br /> present <br /> an <br /> d <br /> probable future beneficial uses of waters of the State <br /> that may be adversely impacted by the contaminants, <br /> . rye <br /> wee®, as required by the Porter-Colog 1e Water Quality <br /> . . . . . . . . . . . - <br /> . . . . . . . . . . • . . Control Act. Therefore,another methodology must be <br /> . . . . . • • • • • • • • • used by the State and Regional Water Boards to fill this <br /> • • -0.05 mg Arsenic!liter of water• . . . . GROUND need. <br /> . . . .(DrbftV Wow ) . . . . <;3 WATER <br /> F1OW Comparison of Figures 6 and 7 shows that the threat <br /> posed to water quality by contaminated soils is similar <br /> Figure 7 to that posed by wastes in an unlined landfill. There- <br /> Designated Level Methodology Summary Page 6 <br />