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COMPLIANCE INFO_2023 CVRWQCB WASTER DISCHARGE REQUIREMENTS
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COMPLIANCE INFO_2023 CVRWQCB WASTER DISCHARGE REQUIREMENTS
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Last modified
5/31/2024 10:30:25 AM
Creation date
11/22/2023 10:15:02 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
2023 CVRWQCB WASTER DISCHARGE REQUIREMENTS
RECORD_ID
PR0440005
PE
4433
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
20106001-3, 5
CURRENT_STATUS
01
SITE_LOCATION
9999 AUSTIN RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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DRAFT [TENTATIVE] WASTE DISCHARGE REQUIREMENTS ORDER R5-2023-00XX 91 <br />FORWARD, INC. <br />FORWARD LANDFILL <br />SAN JOAQUIN COUNTY <br />STANDARD PROVISIONS & REPORTING REQUIREMENTS <br />reliably achieved within limits of precision and accuracy specified in the <br />WDRs or an approved Sample Collection and Analysis Plan for routine <br />laboratory operating conditions that are available to the facility. The <br />Discharger’s technical report (Sample Collection and Analysis Plan and/or <br />Water Quality Protection Standard Report), pursuant to Title 27, section <br />20415(e)(7), shall consider the PQLs listed in Appendix IX to Chapter 14 <br />of Division 4.5 of Title 22, CCR, for guidance when specifying limits of <br />precision and accuracy. For any given constituent monitored at a <br />background or downgradient monitoring point, an indication that falls <br />between the MDL and the PQL for that constituent (hereinafter called a <br />“trace” detection) shall be identified and used in appropriate statistical or <br />non-statistical tests. Nevertheless, for a statistical method that is <br />compatible with the proportion of censored data (trace and ND indications) <br />in the data set, the Discharger can use the laboratory’s concentration <br />estimates in the trace range (if available) for statistical analysis, in order to <br />increase the statistical power by decreasing the number of “ties”. <br />43.The water quality protection standard for organic compounds which are <br />not naturally occurring and not detected in background groundwater <br />samples shall be taken as the detection limit of the analytical method used <br />(e.g., USEPA methods 8260 and 8270). <br />44.Alternate statistical procedures may be used for determining the <br />significance of analytical results for common laboratory contaminants (i.e., <br />methylene chloride, acetone, diethylhexyl phthalate, and di-n-octyl <br />phthalate) if part of an approved water quality protection standard. <br />Nevertheless, analytical results involving detection of these analytes in <br />any background or downgradient sample shall be reported and flagged for <br />easy reference by Central Valley Water Board staff. <br />45.Confirmation of Measurably Significant Evidence of a Release. <br />Whenever a constituent is detected at a detection monitoring point at a <br />concentration that exceeds the concentration limit from the water quality <br />protection standard, the Discharger shall conduct verification sampling to <br />confirm if the exceedance is due to a release or if it is a false-positive <br />(unless previous monitoring has already confirmed a release for that <br />constituent at that monitoring point). An exceedance of the concentration <br />limit from the water quality protection standard is considered measurably <br />significant evidence of a release that must be either confirmed or denied. <br />There are two separate verification testing procedures: <br />a.Standard Monitoring Specification I.46 provides the procedure for <br />analytes that are detected in less than 10% of the background
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