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ARCHIVED REPORTS_2005
Environmental Health - Public
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4400 - Solid Waste Program
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PR0440004
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ARCHIVED REPORTS_2005
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Last modified
7/18/2020 3:43:09 AM
Creation date
7/3/2020 10:42:18 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2005
RECORD_ID
PR0440004
PE
4433
FACILITY_ID
FA0004517
FACILITY_NAME
FOOTHILL LANDFILL
STREET_NUMBER
6484
Direction
N
STREET_NAME
WAVERLY
STREET_TYPE
RD
City
LINDEN
Zip
95236
APN
09344002
CURRENT_STATUS
01
SITE_LOCATION
6484 N WAVERLY RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440004_6484 N WAVERLY_2005.tif
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WASTE DISCHARGE REQUIREMENTSORDER NO. 115-2003-0020 -7- <br />FOR COUNTY OF SAN JOAQUIN <br />FOR CONSTRUCTION, OPERATION, CLOSURE AND EVALUATION MONITORING <br />FOOTHILL SANITARY LANDFILL, MUNICIPAL SANITARY LANDFILL <br />SAN JOAQUIN COUNTY <br />calculations assume that there will be one geomembrane defect of a centimeter diameter hole <br />per acre of liner placed. This geomembrane defect assumption was based on current state -of - <br />practice construction quality assurance for landfill liners. Based on these conditions, a leak <br />rate of 0.0005 gal/acre-day was estimated using the HELP -3 computer model. The calculated <br />leakage rate for the prescriptive liner 60 -mil HDPE/24-inch clay with a hydraulic head of 12 <br />inches (Subtitle D) was 0.81 gal/acre-day. <br />42. The VLEACH model was used to determine the potential for groundwater contamination from <br />a leak in the liner system. VLEACH simulates the movement of potential contaminants <br />among three phases: (1) gas phase; (2) liquid phase; and (3) as an adsorbed compound on the <br />solid phase (soil). The maximum concentration of modeled constituents in groundwater after <br />the modeling period of 100 years was calculated to be below 0.1 ppb, which is below the <br />laboratory detection limits for the modeled constituents. The modeled constituents included, <br />but were not limited to, benzene, 1,2-dichloroethane, chloride, and hexavalent chromium. <br />43. The Construction Quality Assurance (CQA) manual incorporates specific testing protocols, <br />inspection, and documentation requirements in accordance with Section 20324 of Title 27, to <br />provide evidence that the construction proceeds in accordance with the design plans and <br />specifications, and that the system will meet or exceed the design intent and regulatory <br />performance standards. <br />44. The Discharger will perform a state -of -practice geoelectric liner leak detection survey for the <br />GCL. The leak testing enables location of defects, which might impact groundwater and the <br />unsaturated zone, and construction contractor repair of the defects prior to the acceptance of <br />the liner construction project. <br />CONSTRUCTION AND ENGINEERED ALTERNATIVE <br />45. On 17 June 1993, the State Water Resources Control Board adopted Resolution No. 93-62 <br />implementing a State Policy for the construction, monitoring, and operation of municipal solid <br />waste landfills that is consistent with the federal municipal solid waste regulations <br />promulgated under Title 40, Code of Federal Regulations, Part 258 (Subtitle D). <br />46. Resolution No. 93-62 requires the construction of a specified composite liner system at new <br />municipal solid waste landfills, or expansion areas of existing municipal solid waste landfills, <br />that receive wastes after 9 October 1993. <br />47. Resolution No. 93-62 also allows the Board to consider the approval of engineered <br />alternatives to the prescriptive standard. Section 1H.A.b. of Resolution No. 93-62 requires that <br />the engineered alternative liner systems be of a composite design similar to the prescriptive <br />standard. <br />48. Section 20080(b) of Title 27 allows the Board to consider the approval of an engineered <br />alternative to the prescriptive standard. In order to approve an engineered alternative in <br />
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