Emission factors for burning processes: Difference between revisions
No edit summary |
|||
Line 23: | Line 23: | ||
</ref> | </ref> | ||
{| {{prettytable}} | {| {{prettytable}} | ||
| | | Type of plant or kettle | ||
| | | Power of fuel (MW) | ||
| Fuel | | Fuel | ||
| Emission factor (mg/MJ) | | Emission factor (mg/MJ) | ||
| | | Number of plants | ||
|---- | |---- | ||
| Poltinpoltto | | Poltinpoltto | ||
Line 73: | Line 73: | ||
| Kerrosleijukattila | | Kerrosleijukattila | ||
| 5-10 | | 5-10 | ||
| | | Wood | ||
| 10-70 | | 10-70 | ||
| 8 | | 8 | ||
Line 79: | Line 79: | ||
| Kerrosleijukattila | | Kerrosleijukattila | ||
| 10-50 | | 10-50 | ||
| | | Wood | ||
| 5-30 | | 5-30 | ||
| 10 | | 10 | ||
Line 85: | Line 85: | ||
| Kiertoleijukattila | | Kiertoleijukattila | ||
| 20-40 | | 20-40 | ||
| | | Wood | ||
| 5-30 | | 5-30 | ||
| 4 | | 4 | ||
Line 91: | Line 91: | ||
| Puuarinakattila | | Puuarinakattila | ||
| <5 | | <5 | ||
| | | Wood | ||
| 20-150 | | 20-150 | ||
| 120 | | 120 | ||
Line 97: | Line 97: | ||
| Puuarinakattila | | Puuarinakattila | ||
| 5-10 | | 5-10 | ||
| | | Wood | ||
| 20-150 | | 20-150 | ||
| 50 | | 50 | ||
Line 103: | Line 103: | ||
| Puuarinakattila | | Puuarinakattila | ||
| 10-50 | | 10-50 | ||
| | | Wood | ||
| 10-150 | | 10-150 | ||
| 35 | | 35 | ||
Line 109: | Line 109: | ||
| Kaasutuskattila | | Kaasutuskattila | ||
| 2-7 | | 2-7 | ||
| | | Wood | ||
| 50-150 | | 50-150 | ||
| 5 | | 5 | ||
Line 118: | Line 118: | ||
Emission factors for wood burning in small scale heating (e.g. secondary heating at houses) can be found from [http://wanda.uef.fi/pupo/index.html PUPO emission and toxicity database] | Emission factors for wood burning in small scale heating (e.g. secondary heating at houses) can be found from [http://wanda.uef.fi/pupo/index.html PUPO emission and toxicity database] | ||
====Emission factors for greenhousegases==== | ====Emission factors for greenhousegases==== |
Revision as of 11:38, 14 September 2011
Moderator:Pauliina (see all) |
|
Upload data
|
Scope
What are the emission factors for burning processes in Finland? D↷
Definition
Emission factors for burning processes is an impact assessment that take a wide perspective over environmental issues that can dealt with on a city level
See discussions with the statements in the discussion page.D↷
Data
In Finland there are about 700 small heating power plants that has under 5MW fuel power. Same amount is between 5 to 50 MW power plants and over 50 MW power plants there are 200 in Finland.[1]
Emission factors for PM
Next table includes emission factors for small power plants in Finland. [2]
Type of plant or kettle | Power of fuel (MW) | Fuel | Emission factor (mg/MJ) | Number of plants |
Poltinpoltto | <5 | Heavy oil | 20-90 | 300 |
Poltinpoltto | 5-15 | Heavy oil | 10-70 | 200 |
Poltinpoltto | 15-50 | Heavy oil | 5-40 | 100 |
Poltinpoltto | <5 | Light oil | <10 | 20 |
Poltinpoltto | 5-15 | Light oil | <10 | 20 |
Poltinpoltto | 15-50 | Light oil | <10 | 10 |
Diesel/kaasumoottori | 20-40 | Heavy oil | 30-60 | 2 |
Kerrosleijukattila | 5-10 | Wood | 10-70 | 8 |
Kerrosleijukattila | 10-50 | Wood | 5-30 | 10 |
Kiertoleijukattila | 20-40 | Wood | 5-30 | 4 |
Puuarinakattila | <5 | Wood | 20-150 | 120 |
Puuarinakattila | 5-10 | Wood | 20-150 | 50 |
Puuarinakattila | 10-50 | Wood | 10-150 | 35 |
Kaasutuskattila | 2-7 | Wood | 50-150 | 5 |
Emission factors for wood burning in small scale heating (e.g. secondary heating at houses) can be found from PUPO emission and toxicity database
Emission factors for greenhousegases
EFs by fuel based classification
Table 1. Fuel classification and emission factors in Finland 2010. [3] [4]. Definitions for classification of fuels and energy sources can be found here.
Code Heading | Fuel-specific unit | CO2 default emission factor [t/TJ] | Default net calorific value (as fired) [GJ/unit] | NB | |||
1 | Fossil fuels | ||||||
11 | Petroleum products | ||||||
111 | Petroleum gases | ||||||
1111 | Refinery gas | t | 54.2 | * | 49.7 | * | |
1112 | LPG (Liquefied petroleum gas) | t | 65.0 | 46.2 | |||
112 | Light distillates | ||||||
1121 | Naphtha | t | 72.7 | 44.3 | |||
1122 | Motor gasoline | t | 72.9 | 43.0 | |||
1123 | Aviation gasoline | t | 71.3 | 43.7 | |||
113 | Medium distillates | ||||||
1131 | Kerosene (jet fuel) | t | 73.2 | 43.3 | |||
1132 | Other kerosenes | t | 71.5 | * | 43.1 | ||
1133 | Diesel oil | t | 73.6 | 42.8 | |||
1134 | Light fuel oil (heating fuel oil) | t | 74.1 | 42.7 | |||
1135 | Gasoil (for non-road use) | t | 73.6 | * | 42.8 | ||
1139 | Other medium distillates | t | 74.1 | 42.7 | |||
114 | Heavy distillates | ||||||
1141 | Heavy fuel oil, sulphur content < 1% | t | 78.8 | 41.1 | |||
1142 | Heavy fuel oil, sulphur content ≥ 1% | t | 78.8 | 40.5 | |||
1143 | Other heavy distillates | t | 79.2 | * | 40.2 | ||
115 | Petroleum coke | t | 97.0 | 33.5 | |||
116 | Recycled and waste oils | t | 78.8 | 41.0 | |||
119 | Other petroleum products | t | 78.8 | 30.0 | |||
12 | Coal | ||||||
121 | Hard coal | ||||||
1211 | Anthracite | t | 98.3 | * | 33.5 | ||
1212 | Hard coal, bituminous | t | 94.6 | 24.6 | * | ||
122 | Other coal | ||||||
1221 | Semi-bituminous coal, brown coal, lignite | t | 108.0 | 20.0 | |||
1222 | Coal briquettes | t | 94.6 | * | 30.0 | ||
1228 | Coal tar | t | 90.6 | * | 37.0 | ||
1229 | Other non-specified coal | t | 108.0 | 10.0 | |||
123 | Coke | t | 108.0 | 29.3 | |||
124 | Coke oven gas | 1000 m3 | 41.5 | 16.7 | |||
125 | Blast furnace gas | 1000 m3 | 263.7 | 3.8 | |||
13 | Natural gas | ||||||
131 | Natural gas | 1000 m3 | 55.04 | 36.0 | |||
2 | Peat | ||||||
21 | Peat | ||||||
211 | Milled peat | t | 105.9 | 10.1 | |||
212 | Sod peat | t | 102.0 | 12.3 | |||
213 | Peat pellets and briquettes | t | 97.0 | 18.0 | * | ||
3 | Renewable and mixed fuels | ||||||
31 | Biomass | ||||||
311 | Forest fuelwood | ||||||
3111 | Firewood (stems and split firewood) | t | 109,6 | 14.0 | * | BIO | |
3112 | Chips from roundwood | t | 109,6 | 9.5 | * | BIO | |
3113 | Forest residue chips | t | 109,6 | 9.0 | * | BIO | |
312 | Industrial wood residue | BIO | |||||
3121 | Bark | t | 109,6 | 7.5 | * | BIO | |
3122 | Sawdust, cutter shavings etc. | t | 109,6 | 8.0 | * | BIO | |
3123 | Wood residue chips | t | 109,6 | 9.5 | * | BIO | |
3128 | Unspecified industrial wood residue | t | 109,6 | 7.5 | * | BIO | |
3129 | Other industrial wood residue | t | 109,6 | * | 8.8 | * | BIO |
313 | Black liquor and other concentrated liquors | tka | 109,6 | 11.5 | * | BIO | |
314 | Other by-products from wood processing | TJ | 109,6 | BIO | |||
industry | |||||||
315 | Recovered wood | t | 109,6 | 12.0 | * | BIO | |
316 | Wood pellets and briquettes | t | 109,6 | 16.0 | BIO | ||
317 | Vegetable-based fuels | ||||||
3171 | NEW!!Reed canary grass | t | 100.0 | 14.6 | BIO | ||
3172 | NEW!!Cereal crops and straw parts | t | 109,6 | 13.5 | BIO | ||
3179 | NEW!! Other vegetable-based fuels | t | 109,6 | 15.0 | BIO | ||
318 | Animal-based fuels | t | 109.6 | 30.0 | * | BIO | |
32 | Other biofuels and mixed fuels | ||||||
321 | Biogas | ||||||
3211 | Landfill gas | 1000 m3 | 56,1 | 17.0 | * | BIO | |
3212 | Biogas from wastewater treatment | 1000 m3 | 56.1 | 23.0 | * | BIO | |
3213 | Industrial biogas | 1000 m3 | 56.1 | 20.0 | * | BIO | |
3219 | Other biogas | 1000 m3 | 56.1 | 20.0 | * | BIO | |
322 | Liquid biofuels | t | 77.4 | 30..40 | BIO | ||
323 | Mixed fuels (fossil and non-fossil) | ||||||
3231 | Recovered fuels | t | 31.8 | 20.0 | 1) | ||
3232 | Demolition wood | t | 17.0 | 15.0 | 1) | ||
3233 | Impregnated wood (chemically treated) | t | 11.4 | 12.0 | 1) | ||
3234 | NEW!! Deinking sludge | t | 60.0 | 4.0 | 1) | ||
3238 | NEW!!Municipal waste (unsorted) | t | 40.0 | 10.0 | 1) | ||
3239 | Other mixed fuels | t | 110.0 | 10.0 | |||
324 | Gasified waste (Product gas) | 1000 m3 | .. | .. | 2) | ||
325 | NEW!!Biosludge | t | 109.6 | 2.5 | BIO | ||
4 | Other energy sources | ||||||
41 | Nuclear energy | ||||||
411 | Nuclear energy | TJ | – | ||||
49 | Others | ||||||
491 | Other by-products and wastes used as fuels | ||||||
4911 | Plastics waste | t | 74.1 | 33.0 | |||
4912 | Rubber waste | t | 90.0 | 33.0 | |||
4913 | Hazardous waste | t | 117.0 | * | 10.0 | * | |
4919 | Other waste | t | 75.0 | 15.0 | * | ||
492 | Exothermic heat from industry | TJ | – | ||||
493 | Secondary heat from industry | TJ | – | ||||
494 | Electricity | MWh | – | ||||
495 | Steam | MWh | – | ||||
497 | NEW!!Sulphur | t | 0.0 | 10.5 | |||
498 | Hydrogen | 1000 m3 | 0.0 | 10.8 | |||
499 | Other non-specified energy sources | TJ | .. |
NB
BIO = biofuel, whose carbon dioxide emissions are not counted in the total emission amounts of Finland's greenhouse gases, nor are they taken into account in emissions trading.
1) CO2 factor of mixed fuels is an estimate taking into account only the share of fossil carbon.
2) Gasified waste (Product gas) is reported in the fuel categories of the source materials of gasification.
Calorific values and emission coefficients describe the properties of fuel as fired, inclusive of moisture content (except for 313, where the measurement unit is tonnes of dry matter). Calorific value of natural gas has been specified in normal conditions (0 °C and 1.013 bar).
Emission factors are updated when necessary.
(* Revised values.
Emission factors for district heating is calculated in Motiva CO2 emission calculation introductions[5]. For district heating joint production emission factor is 220 kg CO2/MWh. In this view other GHGs (CH4 or N2O) are not taken account as CO2-ekv! Emission factors by fuel based on Motiva knowledge is in table 2.
Table 2. Emission factors of CO2 by fuel[6].
Fuels | kg CO2/MWh |
Heavy oil | 279 |
Light oil | 267 |
Gas | 202 |
Fluid gas | 227 |
Peat | 382 |
Coal | 341 |
Coke | 389 |
Wood | 0 |
CO2 EF for electricity can be classified in two categories: purchase electricity and own production. EF for purchase electricity is the same as own electricity vendor has informed or average Finnish electricity procurement CO2 EF (= 200 kg CO2/MWh). EF for own electricity production can be used EF from table 2 (fuel based EFs). If electricity is produced in combined electricity, heating production EFs are calculated with “benefit division method”. Method is explained in Motiva introduction[7] (attachment 2).
Table 4. Average emission factors measured with differed gas analyzator (kk) and FTIR analyzator [8].
Ordinary combustion | Distribution (%) | Bad combustion | Distribution (%) | Unit | |
Temperature of gas | 253 | 1 | 159 | 17 | Celsius |
CO2 (kk) | 7.3 | 5 | 11 | 8 | %, dry |
O2 (kk) | 13.3 | 3 | 8.7 | 14 | %, dry |
H2O (FTIR) | 6.5 | 4 | 7.7 | - | %, wet |
CO (kk) | 2300 | 10 | 8100 | 29 | mg/MJ |
CO (FTIR) | 2000 | 11 | 5700 | - | mg/MJ |
OGC (kk) | 120 | 17 | 1700 | 46 | mg C/MJ |
OGC (FTIR) | 160 | 24 | 1500 | - | mg C/MJ |
CH4 (FTIR) | 30 | 22 | 350 | - | mg C/MJ |
C6H6 (FTIR) | 20 | 27 | 210 | - | mg C/MJ |
Table 5 and 6 are from Heljo et al 2005[9]. Coefficient of CO2-ekv/CO2 as 1.02 is used in transformation CO2 emission factors to CO2-ekv. factors for electricity and district heating.
Table 5. CO2 emission factors of energy use of buildings (kg CO2/MWh)
Gross of building level | Dispersion | Efficiency | Efficienfy energy level | |
Light oil | 267 | - | 0.85 | 314 |
Heavy oil | 279 | - | 0.85 | 328 |
Wood | - | - | - | - |
District heating | ||||
Separate production | 226 | 20-500 | - | 226 |
Co-production | 220 | dispersion | - | 220 |
Electricity production | ||||
Average | 200 | - | - | 200 |
Marginal | 700 | 700-900 | - | 700 |
or | ||||
Basic capacity | 110 | - | - | 110 |
Interval capacity | 450 | - | - | 450 |
Peak capacity | 850 | - | - | 850 |
Table 6. CO2-ekv emission factors of energy use of buildings (kg CO2-ekv/MWh)
Gross of building level | Dispersion | Efficiency | Efficienfy energy level | |
Light oil | 267 | - | 0.85 | 314 |
Heavy oil | 279 | - | 0.85 | 328 |
Wood | 18 | - | 0.6 | 30 |
District heating | ||||
Separate production | 231 | 20-500 | - | 231 |
Co-production | 224 | dispersion | - | 224 |
Electricity production | ||||
Average | 204 | - | - | 204 |
Marginal | 714 | 700-900 | - | 714 |
or | ||||
Basic capacity | 112 | - | - | 112 |
Interval capacity | 459 | - | - | 459 |
Peak capacity | 867 | - | - | 867 |
Causality
Unit
mg/MJ
Formula
Data that have another unit than mg/MJ should be changed.
e.g. t/TJ -> mg/MJ
Result
See also
- USEPA emission factor information web site [2]
- Tissari et al 2009 [3]
- PUPO loppuraportti [4]
- Heljo et al. 2005 Rakennusten energiankulutus ja CO2-ekv päästöt Suomessa [5]
- Motiva 2004. Yksittäisen kohteen CO2-päästöjen laskentaohjeistus sekä käytettävät CO2-päästökertoimet [6]
- Palosuo T. 09 [7]
References
- ↑ http://www.ymparisto.fi/download.asp?contentid=3706
- ↑ http://www.ymparisto.fi/download.asp?contentid=3706
- ↑ [1]
- ↑ http://tilastokeskus.fi/tup/khkinv/fi_nir_150110.pdf
- ↑ http://motiva.fi/files/209/Laskentaohje_CO2_kohde_040622.pdf
- ↑ http://motiva.fi/files/209/Laskentaohje_CO2_kohde_040622.pdf
- ↑ http://motiva.fi/files/209/Laskentaohje_CO2_kohde_040622.pdf
- ↑ http://www.uku.fi/fine/src/raportit/PUPOloppuraportti2007.pdf
- ↑ http://www.tut.fi/units/rak/rtt/tutkimus/ekorem/EKOREM_Loppuraportti_051214.pdf