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ACZ <br />Laboratories, <br />Batch A distinct set of samples analyzed at a specific time <br />Found Value of the DC Type of interest <br />Limit Upper limit for RPD, in % . , <br />Lower Lower Recovery Limit, in % (except for LCSS, mg/Kg) , <br />MDL Method Detection Limit. Same as Minimum Reporting Limit. Allows for instrument and annual fluctuations. <br />PCN/SCN A number assigned to reagenlslstandards to trace to Ine manufacturers certificate of analysis <br />PQL Practical Quantization Limit, typically S limes the MDL. <br />QC True Value of the Control Sample or the amount added to the Spike <br />Rec Amount of the true value or spike added recovered, in % (except for LCSS, mg/Kg) <br />RPD Relative Percent Difference, calculation used for Duplicate 9C Types <br />Upper Upper Recovery Limit, in % (except for LCSS, mg/Kg) <br />Sample Value of the Sample of interest <br />AS Analytical Spike (Post Digestion) LFM Laboratory Fortifietl Matrix <br />ASD Analytical SDike (Post Digestion) Duplicate LFMD Laboratory Fortified Matrix Duplicate <br />DUP Sample Duplicate LRB laboratory Reagent Blank <br />LCSS Laborelory Control Sample -Soil MS/MSD Matrix Spike/Matrix Spike Duplicate <br />LCSW Laboratory Control Sample -Water PBS Prep Blank -Soil <br />LFB Laboratory Fonified Blank PBW Prep Blank -Water <br />Blanks Verifies that there is no or minimal contamination in the prep method procedure. <br />Control Samples Verifies the accuracy of the method, including the prep procedure. <br />Duplicates Verifies the precision of the instrument and/or method. <br />Spikes/Fortifietl Matrix Determines sample matrix interterences, if any. <br />B Analyze concentration detected at a value between MDL and PUL. <br />H Analysis exceeded method hold time. pH is a Feld test with an immediate hold time. <br />R Poor spike recovery aceepted because the other spike in the set fell within the given limits. <br />T High Relative Percent Difference (RPD) accepted because sample concentrations are less than tOx the MDL. <br />U Analyze was analyzed for but not detected at the indicated MDL <br />V High blank data accepted because sample concentration is 10 times higher than blank concentration <br />W Poor recovery for Silver quality control is accepted because Silver often precipitates with Chloride. <br />% t]uality control sample is out of control. <br />Z Poor spike recovery is accepted because sample concentration is four times greater than spike concentration. <br />(1) EPA 600/4-63-020. Methods for Chemical Analysis of Water and Wastes, March 1983. <br />(2) EPA 600/R-93-100. Methods for the Determination of Inorganic Substances in Environmental Samples, August 1993. <br />(3) EPA 600/R-94-111. Methods (or the Determination of McWls in Environmental Samples -Supplement I, May 1994. <br />(5) EPA SW-646. Test Methods for Evaluating Solid Waste, Third Edition with Update III, December 1996. <br />(6) Standard Methods for the Examination of Water and Wastewater, 19th edition, 1995. <br />(1) QC results calculated from raw tlala. Results may vary slightly if the rountled values are used in the calculations. <br />(2) Soil. Sludge, and Plant matrices for Inorganic analyses are reported on a dry weight basis. <br />(3) Animal matrices for Inorganic analyses are reported on an "as receive8' basis. <br />REPIN03.11.00.01 <br />L34333: Page 4 of 7 <br /> <br />