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WASTE DISCHARGE REQUIREMENTS ORDER NO.R5-2002-0219 -19- <br /> FOR COUNTY OF SAN JOAQUIN <br /> FOR CONSTRUCTION AND OPERATION OF NORTH COUNTY RECYCLING <br /> CENTER AND SANITARY LANDFILL FACILITY, <br /> SAN JOAQUIN COUNTY <br /> 11. "Trace"results -results falling between the MDL and the practical quantitation limit <br /> (PQL) - shall be reported as such, and shall be accompanied by both the estimated MDL <br /> and PQL values for that analytical run. <br /> 12. MDLs and PQLs shall be derived by the laboratory for each analytical procedure, <br /> according to State of California laboratory accreditation procedures. These MDLs and <br /> PQLs shall reflect the detection and quantitation capabilities of the specific analytical <br /> procedure and equipment used by the lab, rather than simply being quoted from USEPA <br /> analytical method manuals. In relatively interference-free water, laboratory-derived <br /> MDLs and PQLs are expected to closely agree with published USEPA MDLs and PQLs. <br /> 13. If the laboratory suspects that, due to a change in matrix or other effects,the true <br /> detection limit or quantitation limit for a particular analytical run differs significantly <br /> from the laboratory-derived MDL/PQL values, the results shall be flagged accordingly, <br /> along with estimates of the detection limit and quantitation limit actually achieved. The <br /> MDL shall always be calculated such that it represents the lowest achievable <br /> concentration associated with a 99% reliability of a nonzero result. The PQL shall <br /> always be calculated such that it represents the lowest constituent concentration at <br /> which a numerical value can be assigned with reasonable certainty that it represents the <br /> constituent's actual concentration in the sample. Normally,PQLs should be set equal to <br /> the concentration of the lowest standard used to calibrate the analytical procedure. <br /> 14. Unknown chromatographic peaks shall be reported, along with an estimate of the <br /> concentration of the unknown analyte. When unknown peaks are encountered, second <br /> column or second method confirmation procedures shall be performed to attempt to <br /> identify and more accurately quantify the unknown analyte. <br /> 15. All QA/QC data shall be reported, along with the sample results to which they apply, <br /> including the method, equipment, analytical detection and quantitation limits,the <br /> percent recovery, an explanation for any recovery that falls outside the QC limits,the <br /> results of equipment and method blanks, the results of spiked and surrogate samples, the <br /> frequency of quality control analysis, and the name and qualifications of the person(s) <br /> performing the analyses. Sample results shall be reported unadjusted for blank results <br /> or spike recoveries. In cases where contaminants are detected in QA/QC samples (i.e., <br /> field,trip, or lab blanks), the accompanying sample results shall be appropriately <br /> flagged. <br /> 16. The statistical method shall account for data below the practical quantitation limit <br /> (PQL)with one or more statistical procedures that are protective of human health and <br /> the environment. Any PQL validated pursuant to §20415(e)(7)of Title 27 that is used <br /> in the statistical method shall be the lowest concentration (or value)that can be <br /> reliably achieved within limits of precision and accuracy specified in the WDRs for <br />