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• PM2.5 emissions from MSWI, biofuel plant, and natural gas plant in Hämeenkyrö
  ...ively we can just use predetermined values and calculate one single annual emission figure for each plant. var emission:= plant_activity_gas*emission_factor;
  2 KB (327 words) - 06:42, 22 August 2014
• Dioxin emission in Hämeenkyrö
  [[Category:Emission releases]] ...ach dioxin and dioxin-like compound by its corresponding toxic equivalency factor (TEF) and then summing the results. The number that results from this calcu
  4 KB (597 words) - 11:28, 13 March 2009
• Comparative risk assessment of dioxin and fine particles
  |answer = Fine particle risk clearly outweigh the dioxin risk. By stricter emission standards for heavy-duty vehicles, approximately 30 annual premature deaths ...t emission situation of heavy-duty vehicles (CURRENT PRACTISE) to particle emission standards set by the EU, For dioxins: an EU-directive that regulates for co
  12 KB (1,384 words) - 10:27, 29 March 2011
• Primary PM2.5 emissions from bus traffic in Helsinki Metropolitan Area
  * Bus emission factors ** Emission factor: 0.321 g/km (1999) <ref>YTV, Helsinki Metropolitan Area Council. (1999). Va
  3 KB (407 words) - 14:19, 20 March 2010
• Pyrkilo
  | '''Sources''' and '''Releases''': Emission modelling | Identification of sources, Emission factor approach, description how the stressor is released into the environment (e.
  65 KB (9,370 words) - 11:37, 20 November 2009
• Societal costs of personal trips in the Helsinki metropolitan area
  *Emission unit cost *Emission factor<ref name="comptraf">Tuomisto and Tainio: An economic way of reducing health
  5 KB (785 words) - 20:14, 13 April 2011
• Emission assessment of small-scale energy production in the Helsinki metropolitan area
  | page = Emission assessment of small-scale energy production in the Helsinki metropolitan ar ...in purpose of this assessments is to evaluate greenhouse gas emissions and emission trading cost of small-scale energy production in [[:en:Helsinki Metropolita
  10 KB (1,265 words) - 15:43, 29 January 2011
• Gabi 4.3 - life cycle assessment software
  ...ssion from raw material to end of the product. In this case every flow and emission is impossible to model, because vast amount of flows and emissions in energ ...2004 and Karvosenoja M., 2008 – reports or calculated by using companies emission data. Large scale district heating units are divided to six groups based on
  13 KB (1,967 words) - 16:55, 23 March 2015
• Emission factors for burning processes
  [[Category:Emission factors]] [[Category:Emission]]
  35 KB (4,224 words) - 12:50, 9 November 2015
• Assessments - science-based decision support
  * Decision &rarr; factor &rarr; outcome | Consider the intended use, its needs and the [[Assessment on impacts of emission trading on city-level (ET-CL)#Scope|scope of the assessment]] e.g. in light
  13 KB (1,957 words) - 14:12, 27 March 2009
• Variables - evolving interpretations of reality
  ...tructure of a variable. With the purpose of the [[Assessment on impacts of emission trading on city-level (ET-CL)|case assessment]] in mind, first determine th | [[Emission factors for burning processes]]
  7 KB (1,027 words) - 12:04, 26 March 2009
• CLAIH assessment
  ***(U factor 1 W/m2K, air leak factor reduced by 20% to 0.24/h) ***Wall U factor 0.17 W/m2K
  24 KB (3,290 words) - 11:32, 13 March 2015
• District heating production units in Helsinki metropolitan area
  The main district heating network adjustment factor is consumer’s need of thermal energy. Thermal energy provider has to guar ...AT-levels are not emission caps; they are only for help authorities to set emission caps when the local conditions are taken into account.
  47 KB (6,369 words) - 17:08, 2 July 2015
• Quest II
  ...tution specification. Each producer maximises his profit and generates his factor demands for production, including demands for capital, energy and labour. F * Exogenous technical progress (neutral or factor-augmenting)
  7 KB (995 words) - 11:24, 29 June 2009
• POLES
  ...r-technology and inter-fuel substitution, in particular in the case of GHG emission constraints.<ref name="poles">JRC: IA TOOLS. Supporting inpact assessment i * simulation of CO2 emission constraints (through the analysis of marginal abatement cost curves or thro
  16 KB (2,305 words) - 12:18, 29 June 2009
• GEM-CCGT
  ...e introduced such as imperfect competition on commodity markets (including emission permit markets), scale economies, and risk and transaction costs associated ...icy reforms (such as EU enlargement). Besides the model can analyse how EU emission abatement policies will change under efficiency and equity considerations i
  7 KB (1,025 words) - 10:13, 30 June 2009
• GEM-E3
  ...services, provided by production sectors. The quantity of each production factor is the result of supply and demand. The supply of physical capital is fixed ...of abatement, the share of energy use of the demand of fossil fuel and the emission coefficient of a pollutant.
  13 KB (1,781 words) - 10:56, 16 October 2009
• Worldscan
  Because the emission of CO2, the most important greenhouse gas, is directly related to the use o Consumers maximize their lifetime utility, a factor dependent on their consumption in both current and future periods. A consum
  10 KB (1,530 words) - 11:02, 16 October 2009
• Evaluating impact on option's affect on emmission of gases
  Does the option affect the emission of ozone-depleting substances (CFCs, HCFCs, etc.) and greenhouse gases (e.g ...maging ultraviolet (UV) radiation, which is known to be a significant risk factor for skin cancers, eye cataracts, and immune system suppression. Due to the
  4 KB (605 words) - 10:47, 16 October 2009
• Naphthalene emissions from moth repellents
  EF = emission fator (mg/(g*h)) ER = emission rate (mgh)
  1,020 bytes (131 words) - 10:04, 16 October 2009

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