Difference between revisions of "Hämeenkyrö MSWI risk assessment: Dioxin"
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− | + | Emission factors for different processes | |
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+ | Municipal solid waste incineration (µg TEQ/t MSW burned) | ||
− | + | Low technology combustion, no APC system: air 3500, fly ash 0, bottom ash 75 | |
− | + | Controlled combustion, minimal APC: air 350, fly ash 500, bottom ash 75 | |
− | + | Controlled combustion, good APC: air 30, fly ash 200, bottom ash 7 | |
− | + | High technology combustion, sophisticated APC system: air 0.5, fly ash 15, bottom ash 1.5 | |
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− | + | Energy production (µg TEQ/TJ) | |
+ | |||
+ | Natural gas fired power boiler: 0.5 | ||
+ | |||
+ | Mixed biomass fired power boiler: air 500, residue 0 | ||
+ | |||
+ | Clean wood fired power boiler: air 50, residue 15 | ||
+ | |||
+ | |||
+ | Household heating and cooking (biomass): | ||
Revision as of 08:17, 22 September 2006
See the main page of this assessment: Hämeenkyrö MSWI risk assessment: General
Contents
Dioxin emissions in Hämeenkyrö
Virpi
Intake fraction for dioxin emissions from Hämeenkyrö
Intake fraction for dioxin emissions from Hämeenkyrö
Baseline dioxin exposure in Hämeenkyrö
Marjo
Baseline dioxin exposure in Hämeenkyrö
Dioxin exposure due to MSWI in Hämeenkyrö
Martin
Health effects caused by dioxin exposure
Sanna
Responses of dioxin exposure on human health at the population level