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f � J <br /> i achieving a total chromium reporting limit of 1 gg/L or better. The advantages of a total <br /> chromium screening approach are that <br /> (1)total chromium determinations are less costly, and <br /> (2)total chromium determinations are not subject to the short holding time constraints of <br /> the Cr(VI) method. <br /> Of the atomic spectrometry techniques generally used for total chromium determinations, <br /> i.e., Flame-AAS, GFAAS, ICP-AES, and ICP-MS, only GFAAS and ICP-MS appear to i <br /> have the potential to achieve the required RL. This is based on the results of the recent <br /> multi-analyte and multi-laboratory study performed by the Reporting Level Work Group N <br /> (RLWG). <br /> Utilities and their laboratories may use ICP-MS or GFAAS for initial screening for total <br /> chroi��ium in lieu'of performing the more time-consuming hexavalent chromium method <br /> (EPA 218.6). Iii order to use these screening tools, laboratories must demonstrate that <br /> they can analyze water samples at the 1 gg/L level with a precision(RSD) of 20% and an <br /> accuracy, as measured by percent recovery, in the range 80-120%. A method detection <br /> limit(MDL) must be established following EPA protocol (40CFR136 Appendix B). The <br /> reporting limit should be no less than three times the MDL. EPA approved methods for + <br /> the analytical technology selected must be followed and all of the QC criteria specified in <br /> those methods must be met. Laboratories should maintain their QC criteria for review <br /> . should any questions arise regarding the results and their adequacy for screening. <br /> When samples yield screening results above 1 µg/L, the respective sources should be re- <br /> sampled as soon as practically possible and analyzed by EPA method 218.6 for Cr(VI). <br /> NOTE: Labs using ICP-MS should digest the samples to avoid any positive interference <br /> by carbon that can occur in the analysis of Total Chromium. <br /> UCMR Guidance,January 30,2001 Page 4 <br />