Waste, viii

Wieczorek, A. and Kosaric, N., Analysis of ethanol production from Jerusalem artichoke in a farm-scale operation, in Energy from Biomass and Wastes VIII, Proceedings of Symposium, Institute of Gas and Technology, Lake Buena Vista, FL, 1984, pp. 1113-1130. 

EPA. 1997a. Identification and listing of hazardous waste. Hazardous constituents. U.S. Environmental Protection Agency. Code of Federal Regulations. 40 CER 261, Appendix VIII. 

EPA OSW Hazardous Waste Constituent (Appendix VIII) Yes EPA 1980b (40 CFR 261)... 

After sealing the head, the exterior of the drum shall be decontaminated and then labeled IAW EPA and DOT regulations. All leaking containers shall be overpacked with vermiculite placed between the interior and exterior containers. Decontaminate and label IAW EPA and DOT regulations. Dispose of the material IAW waste disposal methods provided below. Dispose of material used to decontaminate exterior of drum IAW Federal, state and local regulations. Conduct general area monitoring with an approved monitor (see Section VIII) to confirm that the atmospheric concentrations do not exceed the airborne exposure limit (see Sections II and VIII). 

Kolacinski, Z. Prospective of Thermal Plasma Application to Waste Treatment - Invited lecture for the VIII Int. Symp. SAP ETEP 97, Lodz, September 1997, Post-Conf. Materials, 1998, pp. 117-126. 

Hazardous waste management system carbamate production identification and listing of hazardous waste and CERCLA hazardous substance designation and reportable quantities (proposed rule-40 CFR 261, Appendix VIII) Proposed to include hexane as a hazardous constituent in K156 waste 59 FR 9808 EPA 1994f... 

Identification and Listing of Hazardous Wastes Appendix VIII - Hazardous Constituents Yes 40 CFR 261 EPA 1980a... 

Pospisil PA, Marcus MF, Kobus MA. 1992. The application of supercritical fluid capillary chromatography to the analysis of appendix-VIII and IX compounds. In Waste testing and quality assurance third volume, ASTM STP 1075, D Fiedman, Ed., American Society for Testing and Materials,Philadelphia, PA. ppl54-169. 

First, the incinerator must achieve a destruction and removal efficiency (DRE) of at least 99.99% for each of the designated Appendix VIII chemicals present in the waste feed. In other words, 0.01% of the respective compound in the waste feed can be emitted in the incinerator stack gases. The specific Appendix VIII chemicals evaluated are selected by EPA from those found in the hazardous waste at reasonable concentrations and are termed principal organic hazardous constituents (POHCs). 

One incinerator that has been evaluated rather extensively and for which test results have been reported is the liquid chemical waste incinerator facility owned by the Metropolitan Sewer District (MSD) of Greater Cincinnati, Ohio (1 ). The MSD facility uses a rotary kiln and liquid injection cyclone furnace to incinerate a wide variety of liquid industrial chemical wastes. The total design heat release rate is 120 million kJ/h (114 million Btu/h). Tests conducted over a wide temperature range ( 900°C to 1300°C) for six Appendix VIII chemicals (carbon tetrachloride, chloroform, hexachlorobenzene, hexachlorocyclo-pentadiene, and hexachloroethane) have shown DREs equal to or very near 99.99%. 

Flintoff, J. F. HARKER, A. B. 1985. Detailed processes of surface layer formation in borosilicate waste glass dissolution. In Jantzen, C. M., Stone, J. A. Ewing, R. C. (eds) Scientific Basis for Nuclear Waste Management VIII. Materials Research Society Symposia Proceedings, 44, 147-154. 

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