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Programmatic Sampling and Analysis Plan Project Number:60657245 <br /> • identifies the areas where PFAS-containing materials are stored, used, and/or disposed <br /> • details the various potential pathways (current and historic) for discharge of PFAS from <br /> your facility and the nature of potential PFAS contamination in the surface and <br /> subsurface soil, groundwater, stormwater, and if the facility operates an onsite <br /> wastewater treatment plant, the plant influent and effluent <br /> Based on historical information reviewed and the results of the interview process, the boundaries <br /> of the study area are defined as the areas of concern described in the Work Plan. <br /> Develop the Analytical Approach: <br /> Eurofins Lancaster has been tasked to perform the analytical work for this project. As required <br /> by Order WQ 2021-0006-DWQ (California Water Boards, 2021), this laboratory is accredited by <br /> the California Laboratory Accreditation Program (ELAP) to perform the method compliant with <br /> DoD QSM 5.3 (or most recent). <br /> The laboratory will analyze for the PFAS list provided in Table 1 and must meet the associated <br /> target reporting limits. <br /> Specify Performance or Acceptance Criteria: <br /> The acceptable quality control criteria compliant with Table B-15 of DoD QSM version 5.3 (or <br /> most recent). The laboratory must use in-house acceptance criteria for criteria not outlined in the <br /> DoD QSM. At a minimum, the PFAS analyte list provided in Table 1 must be reported. <br /> The results of the analytical testing will be subjected to Stage 2B data validation procedures. Data <br /> are determined to be valid if the specific limits on precision, accuracy, representativeness, <br /> completeness, comparability, and sensitivity are achieved. Outlier field or laboratory results may <br /> be evaluated using an appropriate statistical test. The quality of the data will be assessed through <br /> the validation procedures described in Section 2.4. <br /> Develop the Plan for Obtaining Data: <br /> Soil and water samples will be collected as described in Section 3 and analyzed as described in <br /> Section 4. <br /> Measurement Quality Objectives <br /> Identifying data quality indicators (DQIs) and establishing quality control (QC) samples and <br /> performance criteria to assess the DQIs are key components of project planning and <br /> development. These components demonstrate an understanding of the data to support project <br /> decisions and help to establish there is a well-defined system in place to assess the DQOs. Data <br /> collected will be used to make informed decisions regarding the nature and extent of <br /> contamination, remedy selection, and the effectiveness of the selected remedy. These uses <br /> require high quality data that is qualitatively and quantitatively precise, accurate, representative, <br /> comparable, adequately sensitive, and legally defensible. The PARCCs parameters (precision, <br /> accuracy, representativeness, completeness, comparability, and sensitivity) outlined below are <br /> used to interpret and assess specific data quality needs for each sample matrix and analytical <br /> operation. <br /> Precision: Precision is a measure of mutual agreement between duplicate samples, or co- <br /> located sample measurements of the same analyte. The closer the numerical values of the <br /> measurements are to each other, the more precise the measurement. Precision for a single <br /> analyte will be expressed as a relative percentage difference (RPD) between results of field <br /> duplicate samples, laboratory duplicate samples, or matrix spike duplicate (MSD) in cases where <br /> both results are greater than five times the reporting limit (RL). RPD is defined as follows: <br /> AECOM <br /> 4 <br />