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i <br />procedures given in Section 5.3 for the ground water and surface <br />1 water samples will apply. Quality control procedures for copper, <br />zinc, iron, calcium and sodium are the same as those given in <br />' Section 5.3. <br />6.4.2 Total and WAD Cvanide Analysis Onlv: The quality control protocols <br />for total cyanide analysis will be consistent with those described <br />in Section 5.3, subject to modification for the specific analytical <br />' procedure, as described in USEPA Method 9010, Section $, or USEPA <br />Method 9012, Section 8, given in Appendix G. WAD cyanide analyses <br />in the process samples will follow similar protocols aS the total <br />cyanide analyses. <br />' 6.5 Analytical Accuracy and Verification <br />1 6.5.1 Full Analysis: Analytical accuracy and verificatioq protocols <br />' will be the same as described in Section 5.4 if there is sufficient <br />sample for analysis of all parameters listed in Table 2. <br />Analytical accuracy and verification procedures for copper, zinc, <br />iron, calcium and sodium analyses are the same as those given in <br />Section 5.4. <br />Total and WAD cyanide analyses on the process samples will be <br />' consistent with the protocols and data described in Section 6.5.2. <br />' 6.5.2 Total Cyanide Analysis Onlv: The analytical accuracy and <br />verification requirements will be similar to and consistent with <br />' Section 5.4. Limited data on accuracy and precision for total <br />cyanide analysis are given in USEPA Method 9010, Section 10. <br />The sensitivity of the manual method, USEPA Method 9010, using a <br />colorimetric finish, is given as 0.02 mg/L, suggesting a PQL of <br />about 0.04 mg/L. The PQL for cyanide (all forms) in ground water <br />samples for the applicable, or most sensitive, analytical method is <br />' -39- <br /> <br />