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These laboratories will perform the analytical testing of the primary and QA/QC samples collected for this <br /> Site characterization. The respective Laboratory Project Managers who will report solely to the Partner <br /> Project Manager on any and all aspects of the sample analyses. The laboratories will conform to the QA <br /> and QC procedures outlined in their respective laboratory QA plan/standard operating procedures. <br /> 3.0 DATA QUALITY OBJECTIVES <br /> Data quality objectives (DQOs) have been developed to ensure that the objectives of the project are <br /> achieved. Specific DQOs have been developed for the following project activities, including: <br /> • Sampling of soil, soil vapor and groundwater, including the collection of QA/QC samples, as <br /> appropriate; <br /> Analysis of soil, soil vapor, groundwater, and QA/QC samples; <br /> • Compilation and reduction of data; and <br /> • Analysis of data. <br /> The DQOs are designed to ensure that the chemical concentrations reported in the soil, soil gas and <br /> groundwater samples are representative of concentrations existing in these media at the Site. <br /> Representative Field and laboratory data will be obtained through the use of consistent methods for sample <br /> collection, preservation, transportation and analysis. Quality control samples for both field and laboratory <br /> operations are used as measures to assess the precision, accuracy, representativeness, and comparability of <br /> the collected samples. <br /> 3.1 Precision <br /> Precision is defined as a measure of agreement among individual measurements of the same parameter. <br /> Sampling precision may be defined by collecting and analyzing duplicate field samples. However, this can <br /> be somewhat difficult to accomplish with soil samples because of the inherent heterogeneity of soils. <br /> Laboratory precision may be defined by analyzing duplicate samples (matrix spike/matrix spike duplicate <br /> samples for organic analyses). Comparison of duplicate samples is done by calculating relative percent <br /> differences between the sample results. The RPD will be calculated as follows: <br /> %RPD = 200%x (X2—X1) /(X2 +Xl) <br /> where 'X1'is the smaller of the two observed values and 'X2'is the larger of the two observed values. <br /> 3.2 Accuracy <br /> Accuracy is defined as the degree of agreement of a measurement or average of measurements with an <br /> accepted or true value. Accuracy is a measurement of bias in the determination of values and is best <br /> established by analysis of blanks, spikes and continuing calibrations. Bias may result from sampling <br /> protocols or analytical procedures. While laboratory, field, or equipment blanks may easily reveal a positive <br /> bias, a negative bias due to loss of target analytes may be virtually impossible to measure. <br /> Field accuracy will be assessed through the analysis of field and equipment rinsate blanks (see Table Al). <br /> Analysis of these blanks will monitor errors associated with the sampling process, possible field-related <br /> contamination, and sample handling. The DQO for equipment rinsate blanks is that all values are less than <br /> Quality Assurance/Quality Control Plan <br /> Tracy Corners Shopping Center <br /> 3225 North Tracy Boulevard <br /> Tracy,California 95376 <br /> Partner Project Number SM14-129814 <br /> Docket Number HAS-VCA 14/15-108 <br /> August 15,2016 <br /> Page 4 <br />