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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0527444
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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL
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Last modified
4/10/2020 4:53:44 PM
Creation date
4/10/2020 4:05:28 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
ROY'S AUTO - HISTORICAL
RECORD_ID
PR0527444
PE
2950
FACILITY_ID
FA0018586
FACILITY_NAME
FORMER ROY KNOLL TOWING
STREET_NUMBER
3570
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
14339014
CURRENT_STATUS
01
SITE_LOCATION
3570 E MINER AVE
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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y"S <br /> • Technical Guidance Document: Construction Quality Management for Remedial Action and <br /> Remedial Design Waste Containment Systems (EPA/540/R-92/073), October 1992. <br /> 4.2.2 Solidification/Stabilization Technologies <br /> Solidification and stabilization(S/S) methods of treating contaminated wastes are applied to change <br /> the physical or leaching characteristics of the waste or to decrease Its toxicity. In the solidification process, <br /> waste constituents are physically locked within a solidified matrix in the form of a granular soil-tike mixture <br /> or a monolithic block. Stabilization converts waste contaminants to a more immobile form, typically by <br /> chemical reaction. S/S refers to treatment processes that mix or inject treatment agents into the <br /> contaminated material to accomplish one or more of the following objectives: <br /> Improve the physical characteristics of the waste, without necessarily reducing aqueous <br /> mobility of the contaminant, by producing a solid from liquid or semiliquid wastes <br /> Reduce the contaminant solubility <br /> Decrease the exposed surface area across which mass transfer loss of contaminants may <br /> occur <br /> Limit the contact of transport fluids and contaminants <br /> S/S treatment improves the waste handling or other physical characteristics of the waste and can <br /> reduce the mobility of contaminants. S/S treatment can be accomplished by treatment with inorganic <br /> binders such as cement, fly ash, and/or blast furnace slag or by organic binders such as bitumen. <br /> S/S technology usually is applied by mixing'contaminated soils or treatment residuals with a <br /> physical binding agent to form a crystalline,glassy, or polymeric framework surrounding the waste particles. <br /> In addition to the microencapsulation, some chemical mechanisms also may improve waste <br /> leach resistance. Other forms of S/S treatment rely on macroencapsulation in which the waste is unaltered <br /> but macroscopic particles are encased in a relatively impermeable coating. <br /> 4.2.2.1 In Situ and Ex Situ S/S <br /> S/S can be either an in situ or ex situ process. The following descriptions of in situ and ex situ S/S <br /> are derived primarily from the Engineering Bulletin: Solidification and Stabilization of Organics and <br /> Inorganics, EPA/540/S-92/015, and the Engineering Forum Issue, Considerations in Deciding to Treat <br /> Contaminated Unsaturated Soils In Situ, EPA/540/S-94/500. <br /> Ex situ processing involves: (1) excavation to remove the contaminated waste from the subsurface; <br /> (2) classification to remove oversize debris; (3) mixing;(4) off-gas treatment(if volatile,or dusts are present); <br /> and (5) a system for delivering the treated wastes to molds, surface trenches, or subsurface injection. <br /> In situ treatment processing has only two steps: (1) mixing, and (2) off-gas treatment. The most <br /> significant challenge in applying S/S in situ for contaminated soils is achieving complete and uniform mixing <br /> of the binder with the contaminated matrix (U.S. EPA, 1990, EPA/540/2-90/002). Three basic approaches <br /> are used for in situ mixing of the binder with the matrix: (1) vertical auger mixing; (2) in-place mixing of <br /> binder reagents with waste by conventional earthmoving equipment, such as draglines, backhoes, or <br /> clamshell buckets; and (3) injection grouting, which involves forcing a binder containing dissolved or <br /> suspended treatment agents into the subsurface, allowing it to permeate the soil. Grout injection can be <br /> applied to contaminated formations lying well below the ground surface. The injected grout cures in place <br /> to produce an in situ treated mass. <br /> 4-6 <br />
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