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A6L1119 <br />E3 -4=-K Genera! <br />ASSOCIATES Certificate of Analysis <br />Notes: <br />The Chain of Custody document and Sample Integrity Sheet are part of the analytical report. <br />Any remaining sample(s) for testing will be disposed of according to BSK's sample retention policy unless other arrangements are made in <br />advance. <br />All positive results for EPA Methods 504.1 and 524.2 require the analysis of a Field Reagent Blank (FRB) to confirm that the results are not <br />a contamination error from field sampling steps. if Field Reagent Blanks were not submitted with the samples, this method requirement has <br />not been performed. <br />Samples collected by BSK Analytical Laboratories were collected in accordance with the BSK Sampling and Collection Standard Operating <br />Procedures. <br />J -value is equivalent to DNQ (Detected, not quantified) which is a trace value. A trace value is an analyte detected between the MDL and the <br />laboratory reporting limit. This result is of an unknown data quality and is only qualitative (estimated). Baseline noise, calibration curve <br />extrapolation below the lowest calibrator, method blank detections, and integration artifacts can all produce apparent DNQ values, which <br />contribute to the un -reliability of these values. <br />(1) - Residual chlorine and pH analysis have a 15 minute holding time for both drinking and waste water samples as defined by the EPA and <br />40 CFR 136. Waste water and ground water (monitoring well) samples must be field filtered to meet the 15 minute holding time for dissolved <br />metals. <br />Summations of analytes (i.e. Total Trihalomethanes) may appear to add individual amounts incorrectly, due to rounding of analyte values <br />occurring before or after the total value is calculated, as well as rounding of the total value. <br />RL Multiplier is the factor used to adjust the reporting limit (RL) due to variations in sample preparation procedures and dilutions required for <br />matrix interferences. <br />Due to the subjective nature of the Threshold Odor Method, all characterizations of the detected odor are the opinion of the panel of <br />analysts. The characterizations can be found in Standard Methods 2170B Figure 2170:1. <br />The MCLS provided in this report (if applicable) represent the primary MCLS for that analyte. <br />Definitions <br />mg/L: <br />Milligrams/Liter (ppm) <br />MDL: <br />Method Detection Limit <br />MDA95: <br />Min. Detected Activity <br />mg/Kg: <br />Milligrams/Kilogram (ppm) <br />RL: <br />Reporting Limit: DL x Dilution <br />MPN: <br />Most Probable Number <br />pg/L: <br />Micrograms/Liter (ppb) <br />ND: <br />None Detected at RL <br />CFU: <br />Colony Forming Unit <br />pg/Kg: <br />Micrograms/Kilogram (ppb) <br />pCl/L: <br />Picocuries per Liter <br />Absent: <br />Less than 1 CFU/100mLs <br />%: <br />Percent Recovered (surrogates) <br />RL Mult: <br />RL Multiplier <br />Present: <br />1 or more CFU/100mLs <br />NR: <br />Non -Reportable <br />MCL: <br />Maximum Contaminant Limit <br />State of Washington <br />C824-16 <br />Please see the individual Subcontract Lab's report for applicable certifications. <br />BSK is not accredited under the NELAP program for the following parameters: <br />Certifications: Please refer to our website for a copy of our Accredited Fields of Testing under each certification <br />Fresno <br />State of California - ELAP <br />1180 <br />State of Hawaii <br />4021 <br />State of Nevada <br />CA000792016-1 <br />State of Oregon - NELAP <br />4021 <br />EPA- UCMR3 <br />CA00079 <br />State of Washington <br />C997-16 <br />Sacramento <br />State of California - ELAP <br />2435 <br />San Bernardino <br />State of California - ELAP <br />2993 <br />State of Oregon - NELAP <br />4119-001 <br />Vancouver <br />State of Oregon - NELAP <br />WA100008-008 <br />State of Washington <br />C824-16 <br />A61_1119 FINAL 12212016 1700 <br />Printed: 12/21/2016 <br />Page 9 <br />QA -RP -0001-10 Final.rpt www.BSKAssociates.com of 15 <br />