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CORRESPONDENCE_1959 - 1989
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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CORRAL HOLLOW
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31130
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4400 - Solid Waste Program
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PR0440003
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CORRESPONDENCE_1959 - 1989
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Last modified
4/27/2021 2:22:37 PM
Creation date
1/27/2021 2:47:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
1959 - 1989
RECORD_ID
PR0440003
PE
4434
FACILITY_ID
FA0003698
FACILITY_NAME
CORRAL HOLLOW LANDFILL
STREET_NUMBER
31130
STREET_NAME
CORRAL HOLLOW
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25303010
CURRENT_STATUS
01
SITE_LOCATION
31130 CORRAL HOLLOW RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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Class Ell Landfill Waste Acc .tante 0 -2- 0 3 November 1988 <br /> For wastes classified as non-hazardous under Title 22,you must additionally acquire sufficient <br /> information to establish that the waste is not a 'designated waste' under Section 2522 of <br /> Subchapter 15. Under this section of the regulations, a non-hazardous waste is a 'designated <br /> waste' if it"consists of or contains pollutants which, under ambient environmental conditions at <br /> the waste management unit,could be released at concentrations in excess of applicable water <br /> quality objectives,or which could cause degradation of waters of the state." Determination that a <br /> waste is not a 'designated waste' under this definition involves the following steps: <br /> 1) Determine which bodies of water could be affected should waste or leachate migrate from the <br /> WMU. The Findings of your WDRs should name these water bodies. <br /> 2) Determine the existing and probable future beneficial uses of these waters, as defined by the <br /> Water Quality Control Plan Report(Basin Plan). Usually,it is safe to assume that the most <br /> restrictive uses of ground waters will be for drinking water or agricultural purposes. For <br /> surface waters, freshwater aquatic life protection should also be considered. The Findings of <br /> your WDRs should name these uses. <br /> 3) Determine the constituents of the waste which pose a water quality threat, should migration to <br /> waters of the state occur. Total dissolved solids (TDS) and specific conductivity (EC) should <br /> be included. <br /> 4) Determine the water quality objectives which protect the beneficial uses from these waste <br /> constituents of concern. Water quality objectives are listed in the Basin Plan. For ground <br /> water, these objectives are as fisted on the attachment"Water Quality Objectives for Ground <br /> Waters". In determining compliance with these narrative water quality objectives,it is often <br /> necessary to refer to water quality criteria established by state and federal agencies for the <br /> protection of various beneficial uses. A compilation of such criteria is contained in the <br /> Regional Board document"A Compilation of Water Quality Goals",available from this office <br /> for$5.00. Where several numerical objectives and/or criteria are available for a single waste <br /> constituent, the most restrictive number should be selected which will protect all present and <br /> probable future beneficial uses. <br /> 5) Determine whether the disposal environment or the waste could be acidic.Acidic conditions are <br /> assumed if the waste will be discharged with other putrescible wastes in the Class 1H landfill or <br /> if the waste is itself putrescible or otherwise capable of generating acid(e.g., mining waste <br /> which contains oxidizable sulfide minerals and insufficient neutralizing cap zity). One measure <br /> of putrescibility is the determination of the total organic carbon(TOC)content of the waste. If <br /> the TOC is at a significant level, usually considered to be 5% or more, the waste is considered <br /> putrescible. Acid generation potential is determined by an acid-base account,as specified in the <br /> EPA publication"Field and Laboratory Methods Applicable to Overburdens and Minesoils" <br /> (National Technical Information Service Publication PB 280 495)or equivalent methods. <br /> Discharge to a monofill or in the foundation layer of the final cap of the landfill would not be <br /> considered acid generating conditions if the waste itself is not putrescible nor capable of <br /> generating acid. <br /> 6) Determine the soluble or extractable concentrations of the constituents of representative waste <br /> samples by the Waste Extraction Test(WET) [Title 22 CCR, Section 667001. The extraction <br /> solutions should be as specified in the regulations if the waste will be discharged with other <br /> putrescible wastes in the Class III landfill or if the waste is itself putrescible c r otherwise <br /> capable of generating acid. The extraction solution may be deionized water it the waste will be <br /> discharged to a monofill or placed in the foundation of the final cap of the landfill and the waste <br /> is not putrescible nor capable of acid generation. The resulting extract(s) should be analyzed <br /> for all waste constituents specified in section(3)above. The deionized water extract should <br /> also be analyzed for total dissolved solids (TDS), specific conductivity(EC),and pH. <br />
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