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<br />STANDARD PROVISIONS AND REPORTING REQUIREMENTS, JANUARY 2012 - 18 - <br />FOR WASTE DISCHARGE REQUIREMENTS <br />FOR DISCHARGES REGULATED BY SUBTITLE D AND/OR TITLE 27 <br /> <br /> <br />shall be selected from among those methods which would provide valid results <br />in light of any matrix effects or interferences. <br /> <br />11. The laboratory reporting limit (RL) for all reported monitoring data shall be set <br />no greater than the practical quantitation limit (PQL). <br /> <br />12. “Trace” results - results falling between the MDL and the PQL - shall be <br />reported as such, and shall be accompanied both by the estimated MDL and <br />PQL values for that analytical run. <br /> <br />13. Laboratory data shall not be altered or revised by the Discharger. If the <br />Discharger observes potential lab errors, it shall identify the issue in the <br />monitoring report and shall describe steps that will be taken to prevent similar <br />errors in the future. <br /> <br />14. MDLs and PQLs shall be derived by the laboratory for each analytical <br />procedure, according to State of California laboratory accreditation procedures. <br />These MDLs and PQLs shall reflect the detection and quantitation capabilities <br />of the specific analytical procedure and equipment used by the lab, rather than <br />simply being quoted from USEPA analytical method manuals. In relatively <br />interference-free water, laboratory-derived MDLs and PQLs are expected to <br />closely agree with published USEPA MDLs and PQLs. MDLs and PQLs shall <br />be reported. <br /> <br />15. If the laboratory suspects that, due to a change in matrix or other effects, the <br />true detection limit or quantitation limit for a particular analytical run differs <br />significantly from the laboratory-derived MDL/PQL values, the results shall be <br />flagged in the laboratory report accordingly, along with estimates of the <br />detection limit and quantitation limit actually achieved. The MDL shall always <br />be calculated such that it represents the lowest achievable concentration <br />associated with a 99% reliability of a nonzero result. The PQL shall always <br />be calculated such that it represents the lowest constituent concentration at <br />which a numerical value can be assigned with reasonable certainty that it <br />represents the constituent’s actual concentration in the sample. Normally, <br />PQLs should be set equal to the concentration of the lowest standard used to <br />calibrate the analytical procedure. <br /> <br />16. All QA/QC data shall be reported, along with the sample results to which they <br />apply, including the method, equipment, analytical detection and quantitation <br />limits, the percent recovery, an explanation for any recovery that falls outside <br />the QC limits, the results of equipment and method blanks, the results of spiked <br />and surrogate samples, the frequency of quality control analysis, and the name <br />and signature of a responsible person from the laboratory. Sample results <br />shall be reported unadjusted for blank results or spike recoveries. In