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Mr. Ray Von Flue i <br /> January 26, 2010 <br /> Page 2 of 4 <br /> The hazardous waste criteria for chromium found in footnote (d) of California Title 22 <br /> CCR66261.24(a)(2) states "If the soluble chromium, as determined by the TCLP set forth in <br /> Appendix I of chapter 18 of this division, is less than 5 mg/l, and the soluble chromium, as <br /> determined by the procedures set forth in Appendix II of chapter 11, equals or exceeds 560 mg/1 <br /> and the waste is not otherwise identified as a RCRA hazardous waste pursuant to section <br /> 66261.100, then the waste is a non-RCRA hazardous waste." <br /> During the 1991 effort to incorporate the federal regulations into California regulations, <br /> some interpreted that the Department of Toxic Substances Control (DTSC) was changing the <br /> STLC threshold for chromium III from 560 mg/l to 5 mg/l. In order to remedy this <br /> misinterpretation, DTSC added this footnote to explain that in most cases it remains 560 mg/l. <br /> The federal hazardous waste level for soluble chromium using the TCLP test is 5 mg/1. <br /> California has a WET test threshold for chromium III of 560 mg/l as long as the TCLP test is less <br /> than 5 mg/1. Using the same reasoning,the WET test threshold for chromium VI is 5 mg/l. <br /> A decision tree showing the logic for determining whether a waste containing chromium <br /> III is presented on Figure 1. A decision tree showing the logic for determining whether a waste <br /> containing chromium VI is presented on Figure 2. <br /> Results of the May 29, 2009 sampling event conducted by the County are inconclusive <br /> since the analyses did not seek to determine whether the total chromium was composed of <br /> chromium III or the more toxic chromium VI, and whether the bead blast is a RCRA waste as <br /> determined by the TCLP test. <br /> Independent sampling of the bead blast material was undertaken by Fremouw <br /> Environmental Services, Inc. ("Fremouw") on November 30, 2009. Three samples were <br /> collected and submitted for laboratory analysis according to protocols established by the U.S. <br /> Environmental Protection Agency and were handled under chain of custody control. <br /> Fremouw Sample CS-003 was collected randomly from 5 drums of hot and cold shot <br /> bead blast into two 4 oz glass jars. Siena Testing Labs used this sample to determine partical <br /> size distribution. Results show that 100 percent of the bead blast passes the #10 sieve, thus there <br /> is no need to remove non-friable solids that do not pass this sieve and are extraneous and <br /> irrelevant as hazardous waste constituents (Title 22 Chapter 11, Appendix II-1). <br /> Sample CS-004 was collected randomly from 5 drums of hot and cold shot bead blast <br /> into one 4 oz glass jar. Block Environmental Services used this sample to determine aquatic <br /> toxicity using the acute 96-hour bioassay using fathead minnows in accordance with California <br /> Title 22, Section 66261.24(a)(6). Results show a 95 percent survival rate at 500 mg/l. The <br /> hazardous waste criterion for this test is less than 50 percent survival. <br />