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<br />11 <br />interfere with the cyanide determination, and it is possible that the green mat-like material <br />could contain these constituents. The composition of the precipitate should be determined <br />so that potential analytical interferences can be identified, and in the interim both filtered <br />and unfiltered samples should be collected for determination of total and WAD cyanide. <br />Samples that have cyanide concentrations above detection should have nitrate+nitrite and <br />fatty acid determinations. Additionally, quality assurance/quality control (QA/QC) <br />procedures such as a cyanide spike recovery analysis should be performed qn samples from <br />the collection pond to determine if anaiytical-interferenc;es are present <br />3.4 Laboratory Turnaround Time <br />The laboratory turnaround time was excessive for this sampling trip. Core laboratories <br />received the samples on November Z5, 1992, and the third-party sampler did not receive the <br />final analytical report until January 11, 1993, resulting in a laboratory turnaround time of <br />nearly seven weeks. This lengthy turnaround time makes it impossible -to sample on a <br />monthly basis, because the third-party monitor must spend time evaluating the analytical <br />results for preparation of the summary report, and DMG and BMRI must see the report <br />and discuss it before the next round of sampling. Core Laboratories was iQt the process of <br />moving its laboratory during this period, which included the holidays, and they have <br />promised that turnaround time in the future will be a maximum of four weeks. If Core <br />cannot meet this requirement for the next round of samples, either anther laboratory <br />should be retained or the MOU should be changed to reflect the increased laboratory <br />turnaround time. <br />4.0 RECOMMENDATIONS FOR CIiaNGES IN THE SAMIPLING AND <br />ANALYTICAL PROTOCOL <br />1) Place a filter in the barrel filtration device when collecting nhe rinse blank. <br />2) For field parameters, make sure that readings have stabilized before recording <br />measurements. <br />3) All field parameters, including dissolved oxygen and specific conductance <br />should be taken at the process point sampling locations. <br />4) Check calibration of field instruments after 3-5 samples are cpllected and after <br />collection of a sample that differs significantly from the following sample. <br />RCG/ITagler, Bailly, Inc. <br />