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AFJ3015 <br /> Ek=iC General <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 /> Field tests are outside the scope of laboratory accreditation and there is no certification available for field testing. <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 /> (2)-Formerly known as Bis(2-Chloroisopropyl)ether. <br /> Unless otherwise noted,TOC results by SM 5310C method do not include purgeable organic carbon,which is removed along with the <br /> inorganic carbon interference. The POC contribution to TOC is considered to be negligible. <br /> The results in this report apply to the samples analyzed in AFJ3015 FINAL 11042022 1400 <br /> accordance with the chain of custody document. This <br /> analytical report must be reproduced in its entirety. <br /> www.BSKAssociates.com Page 5 of 9 <br />