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CO0042729
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2200 - Hazardous Waste Program
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CO0042729
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Last modified
2/8/2024 11:19:21 AM
Creation date
2/12/2019 9:13:54 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
RECORD_ID
CO0042729
PE
2200
FACILITY_NAME
ESCALON SPORTSMAN CLUB
STREET_NUMBER
25187
Direction
E
STREET_NAME
RIVER
STREET_TYPE
RD
City
ESCALON
Zip
95320
APN
24710004
ENTERED_DATE
12/29/2016 12:00:00 AM
SITE_LOCATION
25195 E RIVER RD
RECEIVED_DATE
12/29/2016 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
FilePath
\MIGRATIONS\R\RIVER\25187\CO0042729.PDF
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EHD - Public
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PROVEN TECHNOLOGIES AND REMEDIES GUIDANCE-REMEDIATION OF METALS IN SOIL <br /> specified LDR concentrations, the soils do not need to be treated prior to off-site land <br /> disposal and can be disposed of appropriately at a landfill. <br /> The sampling results from the soil stockpiles must be included in the waste profile form <br /> for the landfill to review and determine if the profile meets its acceptance criteria. Upon <br /> acceptance by a landfill, the soil stockpiles are loaded into the transport container (e.g., <br /> truck, rail car, bin) and transported to either a Class I landfill under a hazardous waste <br /> manifest or a Class II landfill under a bill of lading. Soils not contaminated above the <br /> site cleanup goal may be left on site and reused to backfill the excavated areas. <br /> 7.5.2 Loading, Transportation, and Manifesting <br /> Soil transported for offsite management or disposal must be transported in accordance <br /> with applicable state and federal laws. Loading of transport containers should be <br /> adjacent to stockpiles or excavations, just outside designated exclusion zones. Any soil <br /> falling to the ground surface during loading should be placed back into the container. <br /> Loaded containers should be inspected to ensure that they are within acceptable weight <br /> limits and should be covered and inspected prior to departure to minimize the loss of <br /> materials in transit. The waste profile analyses should accompany the shipping <br /> document (i.e., bill of lading or hazardous waste manifest) to the offsite facility. <br /> 7.6 BACKFILL AND RESTORATION <br /> Backfilling typically occurs after the cleanup objectives have been met. Confirmation <br /> samples are collected from the sides and bottom of the excavation to confirm that the <br /> clean up goals have been achieved. An annotated outline for a soil confirmation <br /> sampling plan is included in Appendix D3. <br /> Once the cleanup goals have been achieved, backfill operations can begin. Backfill <br /> soils should have physical properties consistent with engineering requirements for the <br /> planned site use. The Uniform Building Code typically requires a compaction between <br /> 90 and 95 percent. The excavated areas should be restored to be consistent with its <br /> continued use and graded to ensure proper runoff. <br /> 7.6.1 Borrow Source Evaluation <br /> When selecting material for backfilling excavated areas, steps should be taken to <br /> minimize the chance of introducing soil to the site that may pose a risk to human health <br /> and the environment at some future time. As a general rule, fill should not be obtained <br /> from industrial areas, from sites undergoing environmental cleanups, or from <br /> commercial sites with potential impacts (e.g., former service stations, dry cleaners). <br /> The DTSC Information Advisory, Clean Imported Fill (DTSC, 2001) suggests that two <br /> approaches can be used to demonstrate acceptable backfill materials: (1) providing <br /> appropriate documentation and conducting analyses as needed; or (2) collecting <br /> 34 <br />
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