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3 A6E2186 <br /> Lathrop <br /> A S S O C I A T E S 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: Milligrams/Liter(ppm) MDL: Method Detection Limit MDA95: Min.Detected Activity <br /> mg/Kg: Milligrams/Kilogram(ppm) RL: Reporting Limit:DL x Dilution MPN: Most Probable Number <br /> pg/L: Micrograms/Liter(ppb) ND: None Detected at RL CFU: Colony Forming Unit <br /> pg/Kg: Micrograms/Kilogram(ppb) pCi/L: Picocuries per Liter Absent: Less than 1 CFU/100mLs <br /> %: Percent Recovered(surrogates) RL Mult: RL Multiplier Present: 1 or more CFU/100mLs <br /> NR: Non-Reportable MCL: Maximum Contaminant Limit <br /> Please see the individual Subcontract Lab's report for applicable certifications. <br /> BSK is not accredited under the NELAC program for the following parameters: **NA** <br /> Antimony,WET Arsenic,WET Barium,WET <br /> Beryllium,WET Cadmium,WET Chromium,WET <br /> Cobalt,WET Copper,WET Iron,WET <br /> Lead,WET Mercury,WET Molybdenum,WET <br /> Nickel,WET Selenium,WET Silver,WET <br /> STLC Thallium,WET Vanadium,WET <br /> Zinc,WET <br /> Certifications: Please refer to our website for a copy of our Accredited Fields of Testing under each certification. <br /> San Bernardino-CA ELAP 2993 <br /> Fresno <br /> State of California-ELAP 1180 State of Hawaii 4021 <br /> State of Nevada CA000792016-1 State of Oregon-NELAC 4021 <br /> EPA-UCMR3 CA00079 State of Washington C997-16 <br /> Sacramento <br /> State of California-ELAP 2435 <br /> Vancouver <br /> State of Oregon-NELAC WA100008-008 State of Washington C824-15 <br /> A6E2186 FINAL 06272016 1817 <br /> Printed:6/27/2016 "`Amended Report <br /> QA-RP-0001-10 Final.rpt www.BSKAssociates.com Page 30 of 33 <br />