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It is estimated that municipal solid waste incineration contributes approximately 5% of the total annual release of chlorobenzenes.
New data (Chandler, 2004) suggests that controlled municipal solid waste incineration is not a large source of chlorobenzenes releases in Canada.
Public Health England: Position Statement on Municipal Solid Waste Incineration.
Environment Canada (1999), Municipal Solid Waste Incineration in Canada:
Any new municipal solid waste incineration facilities must also comply with Guidelines A-7 and A-8 that incorporate the CWS.
Most stakeholders supported the ministry's proposal to require individual environmental assessments for coal/oil-fired generation, municipal solid waste incineration to generate electricity and transmission facilities over a certain size.
This is a consolidated report on the achievement of or compliance with Canada-Wide Standard for mercury emissions from the Municipal Solid Waste Incineration sector in Canada.
Municipal solid waste incineration and manufacture of ferrous and non-ferrous metals were found to be the principal culprits, while only trace amounts of dioxin could be attributed to vinyl production.
In 1984, Environment Canada established the National Incinerator Testing and Evaluation Program (NITEP) to examine the potential impact of municipal solid waste incineration on the environment.
The Effect of Waste Stream Characteristics on Municipal Solid Waste Incineration- The Fate and Behaviour of Trace Metals, Vol.
Municipal Solid Waste Incineration According to the 2001 Inventory and Technical Study (Cleghorn and Davies) waste incineration was identified as a potentially significant source of chlorobenzenes.
Controlled high-temperature incineration, above 850C for two seconds, performed with selective additional heating, breaks down toxic dioxins and furans from burning plastic, and is widely used in municipal solid waste incineration.
M. G. WINTER and C. HENDERSON The reuse of municipal solid waste incineration aggregates in manufacturing usual concrete.
It is likely that most of these units are discarded into municipal waste streams, and would therefore be contained in Canadian landfills, with a very small amount possible disposed in municipal solid waste incineration facilties.
Human exposures to environmental cadmium are primarily the result of fossil fuel combustion, phosphate fertilizers, natural sources, iron and steel production, cement production and related activities, nonferrous metals production, and municipal solid waste incineration.
The energy efficiency formula as the sole criteria for municipal solid waste incineration plants being classified as recovery is not coherent with the multi-criteria approach to the definition of recovery and the primary environmental concern of controlling emissions.
The National Incinerator Testing and Evaluation Program (NITEP): A Summary of the Characterization and Treatment Studies on Residues from Municipal Solid Waste Incineration Issue:
Biomass/wastes electricity comprises electricity generated from burning of wood/wood wastes and other solid wastes of renewable nature (straw, black liquor), municipal solid waste incineration, biogas (incl. landfill, sewage, farm gas) and liquid biofuels.
Environment Canada (2003b), Municipal Solid Waste Incineration in Canada: An Update on Operations 1999–2001, Prepared for Environment Canada by A.J. Chandler & Associations Ltd. in conjunction with Compass Environmental Inc.
Municipal Solid Waste Incineration A combustion chamber of a typical mass-burn MSW incinerator is composed of a grate system on which waste is burned and is either water-walled (if the energy is recovered) or refractory-lined (if it is not).
A3.6.5 N2O Emissions from Waste Incineration A3.6.5.1 Methodology Municipal Solid Waste Incineration Emissions of N2O from MSW incineration are estimated using the assumption that the IPCC five- stoker facility factors are most representative.