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Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa

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dc.contributor.author Rogers, D
dc.contributor.author Brent, A
dc.date.accessioned 2008-12-10T12:06:58Z
dc.date.available 2008-12-10T12:06:58Z
dc.date.issued 2006-02
dc.identifier.citation Rogers, D and Brent, A. 2006. Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa. CSIR Research and Innovation Conference: 1st CSIR Biennial Conference, CSIR International Convention Centre Pretoria, 27-28 February 2006, pp1 en
dc.identifier.uri http://hdl.handle.net/10204/2692
dc.description CSIR Research and Innovation Conference: 1st CSIR Biennial Conference, CSIR International Convention Centre Pretoria, 27-28 February 2006 en
dc.description.abstract The most toxic group of substances associated with waste incineration emission controls are the 210 dioxin compounds. Concentrations at which it is required to be measured range are 0.1 ng/m3 in the EU where large 100 000 tonne per annum plants are operated and to 0.2 ng/m3 in SA where the largest plants are less than 5000 tonne per annum. EU target daily intakes are 1 pg/kg/day and this is determined by measurements and fate and transport models of emission. Dioxin compounds are formed as by products of all combustion processes in the gas phase. With the introduction of emission controls in USA, the main source of dioxin has changed from industrial activities (12 kg/annum)1 to forest fires (1.3 kg/annum) and open burning of general waste (0.62 kg/annum)2. In SA, as in most developing countries, less than 1% of the 137 medical waste incinerators registered in SA3 are fitted with gas clean up systems, and the exhaust gases are vented at temperatures above the onset of dioxin formation (450 °C to 150 °C). It is not possible to measure in a plume, and the existing stack dispersion models do not address the conditions occurring at the exit of the stack, so it is also not possible to make estimates of the human health impacts of these emissions using international standard methodologies en
dc.language.iso en en
dc.subject Dioxin formation en
dc.subject Incinerators en
dc.subject Temperature plume model en
dc.title Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa en
dc.type Conference Presentation en
dc.identifier.apacitation Rogers, D., & Brent, A. (2006). Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa. http://hdl.handle.net/10204/2692 en_ZA
dc.identifier.chicagocitation Rogers, D, and A Brent. "Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa." (2006): http://hdl.handle.net/10204/2692 en_ZA
dc.identifier.vancouvercitation Rogers D, Brent A, Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa; 2006. http://hdl.handle.net/10204/2692 . en_ZA
dc.identifier.ris TY - Conference Presentation AU - Rogers, D AU - Brent, A AB - The most toxic group of substances associated with waste incineration emission controls are the 210 dioxin compounds. Concentrations at which it is required to be measured range are 0.1 ng/m3 in the EU where large 100 000 tonne per annum plants are operated and to 0.2 ng/m3 in SA where the largest plants are less than 5000 tonne per annum. EU target daily intakes are 1 pg/kg/day and this is determined by measurements and fate and transport models of emission. Dioxin compounds are formed as by products of all combustion processes in the gas phase. With the introduction of emission controls in USA, the main source of dioxin has changed from industrial activities (12 kg/annum)1 to forest fires (1.3 kg/annum) and open burning of general waste (0.62 kg/annum)2. In SA, as in most developing countries, less than 1% of the 137 medical waste incinerators registered in SA3 are fitted with gas clean up systems, and the exhaust gases are vented at temperatures above the onset of dioxin formation (450 °C to 150 °C). It is not possible to measure in a plume, and the existing stack dispersion models do not address the conditions occurring at the exit of the stack, so it is also not possible to make estimates of the human health impacts of these emissions using international standard methodologies DA - 2006-02 DB - ResearchSpace DP - CSIR KW - Dioxin formation KW - Incinerators KW - Temperature plume model LK - https://researchspace.csir.co.za PY - 2006 T1 - Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa TI - Propensity for the formation of dioxins during the cool-down of plumes from medical waste incinerators in South Africa UR - http://hdl.handle.net/10204/2692 ER - en_ZA


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