in a thermal processing unit capable of volatilizing mercury and subsequently condensing the volatilized mercury for recovery. All aqueous waste and non-aqueous waste residues derived from this process must then comply with the corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g., High or Low Mercury Subcategories). Deactivation to remove the hazardous characteristics of a waste due to its ignitability, corrosivity, or reactivity. 4. Both Cyanides and Cyanides for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes. 3. Concentration requirements for non-aqueous wastes are based on analysis of grab samples. 2. Concentration requirements for aqueous wastes are expressed in mg/L and are based on analysis of composite samples. 7 Both Cyanides and Cyanides for non-
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