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V <br /> APPENDIX G <br /> STATISTICAL ANALYSIS METHODS FOR THE FORWARD LANDFILL <br /> In order to update concentration limits (CLs) for the Forward Landfill, a statistical analysis of <br /> water quality monitoring data was performed by Geo-Logic Associates (GLA) in accordance <br /> with protocols outlined in Order No. R5-2014-0006 issued by the California Regional Water <br /> Quality Control Board — Central Valley Region and Code of Federal Regulations, Title 40, Part <br /> 258 (40 CFR 258) and California Code of Regulations (CCR) Title 27, Section 20415. The <br /> statistical analyses were performed with historical statistical algorithms that recognize that <br /> groundwater quality data may be correlated through time (in contrast, non-historical statistics <br /> rely on the data not being correlated). Geo-Logic Associates performed the historical statistical <br /> analyses described below with the Sanitas° statistical program. This software performs user- <br /> determined statistical analyses using methods recommended by the California State Water <br /> Resources Control Board (SWRCB) and the United States Environmental Protection Agency <br /> (EPA). <br /> INTRAWELL TOLERANCE LIMITS <br /> In accordance with Waste Discharge Order No. 115-2014-0006, intrawell tolerance limits (TLs) <br /> were calculated to establish updated CLs for the Forward Landfill. A TL is a one-sided tolerance <br /> interval constructed from a background population with a specified confidence level. If a <br /> future observation exceeds the calculated upper limit, this is statistically significant evidence of <br /> contamination. For the Forward Landfill, intrawell TLs were developed based on a Type I error <br /> rate a = 0.01 that future observations will fall below the limit. Statistical calculations are based <br /> on the procedures described in the USEPA's 2009 Unified Guidance Document (USEPA, 2009). <br /> For a parametric tolerance limit analysis, the mean (X) and standard deviation (S) are calculated <br /> for the raw or transformed background data and a one-sided (two-sided for pH) tolerance <br /> factor (K) is specified at the 1-a (or 99 percent) confidence level. The prediction limit (TL) is <br /> defined as: <br /> TL= X+ KS <br /> For non-parametric prediction limit analysis, the highest value from the background data set is <br /> used to set the prediction limit. The false positive rate for non-parametric analyses were <br /> established from California standards and determined based on sample size, with all false <br /> positive rates falling below 3.8 percent. <br /> The calculated intrawell TLs for the routine indicator parameters for each groundwater <br /> monitoring well were calculated using screened background data from the first quarter 2009 <br /> through the fourth quarter 2013 (20 sampling events), TL calculations are included as an <br /> attachment to this appendix. For constituents that have not been detected in background <br /> database, the laboratory's practical quantitation limit (PQL) is used as the CL. <br />