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Energy and Environment. E nvironmental consequences of combustion processes – Part I (Smog, Acid Rain, and ozone depletion). Dr. Hassan Arafat Department of Chem. Eng. An-Najah University. (these slides were adopted, with modification, from Ms. Paulina Bohdanowicz , KTH Institute, Sweden).
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Energy and Environment Environmental consequences of combustion processes – Part I(Smog, Acid Rain, and ozone depletion) Dr. Hassan Arafat Department of Chem. Eng. An-Najah University (these slides were adopted, with modification, from Ms. Paulina Bohdanowicz , KTH Institute, Sweden)
Combustion Source: WCI 2005
Combustion In order to meet forecasted global electricity demand it is estimated that 2000 MW of additional capacity will have to be installed every week over the next 20 years Source: WCI 2005
Combustion chamber • The type and quantity of compounds created depend on: • the type and composition of fuel, • combustion conditions (type of furnace, air:fuel ratio, and especially temperature) • CO2, depending on fuel composition and generator efficiency • Sulphur oxides (SOx) from sulphur oxidation - more than 95 % SO2, remaining is SO3 • CO, depending on oxidation efficiency of fuel (up to 30% in incomplete combustion) • 20-90 % of N in fuel is converted into NOx. Additionally depending on the temperature of combustion and residence time, N from air combines with O from air • The extras ? - dioxines and furans (coming from combustion of chlorinated plastics)- highly carcinogenic and very dangerous, mainly in waste incineration plants • Coal: small quantities of uranium, radium and thorium present in the coal result in the radioactivity of the fly ash (of varying level)
Combustion • Emissions of concern: • Particulates/fly and bottom ash • Carbon dioxide • Sulphur oxides • Nitrogen oxides • Carbon monoxide • Waste
Flue gas composition from a typical coal-fired power plant Source: Liss R., Saunders A., Power generation and the Environment, Oxford 1990; Turns S.R., An introduction to combustion, concepts and application, Singapore 2000
Air Pollutants • Carbon monoxide • colorless, odorless, non-irritating poison • attaches to hemoglobin; reduces oxygen carrying capacity • results in headaches, drowsiness and asphyxiation • Hydrocarbons • denotes a large group of volatile organic compounds • some are carcinogens, poison etc.
Air Pollutants • Sulfur Dioxide • colorless corrosive gas • respiratory irritant and poison • can result in H2SO4 • Particulates • small pieces of solid or liquid materials dispersed in the atmosphere • 0.005-100 um • reduction in visibility, respiratory problems
Air Pollutants • Nitrogen Oxides • critical component for smog formation • compounds acid precipitation problems • Photochemical Oxidants • products of secondary atmospheric reactions driven by solar energy • e.g., O3 PAN (peroxyacetyl nitrate), acrolein • strong oxidants, eye irritant etc.
Air Pollutants • Lead • released as metal fumes or suspended particles • 2 million metric tons per year • 5-10 times more in urban than rural areas when leaded gas is used • major source was leaded gasoline • Carbon Dioxide • generally considered non-toxic and innocuous • not listed as air pollutant • increasing concentrations have been related to global warming
Waste generated per year in a 1000 MWe coal power plant Coal characteristics: CV of 20 MJ/kg and a sulphur content of 1%. Plant characteristic: efficiency 34%, electricity production 65% of the total electricity it is capable of producing (650 MW-years in one year)
Comparative emission levels from a 300-MW power plant • Source: Interstate Natural Gas Association of America. Natural Gas and the Environment. www.ingaa.org/environment (accessed March 18, 2002)
Results of emissions • Local pollution with particulates and gases • Smog • Acid rains • Greenhouse effect/ Global warming • Thermal pollution from cooling waters • Waste generation
Atmospheric concentration of selected species Source: Siemiński M., Środowiskowe zagrożenia zdrowia, Warszawa 2001
19.7% of EU inhabitants are exposed to excessive levels of ozone (2000) 9.6% - Denmark 18.3% - Finland 41.2% - Greece 69.9% - Italy 95.4% - Austria 36.2% of EU inhabitants are exposed to excessive levels of particulate matter (PM10) (2000) 36.2% - Denmark 56.0% - Sweden 95.6% - Netherlands 97.6% - Greece 100.0% - Italy 100.0% - Portugal Urban air quality
Form of air pollution in which atmospheric visibility is partially obscured by a haze consisting of solid particulates and/or liquid aerosols Occurs mainly in urban areas but not exclusively Smoke + fog = smog Smog
History dates back to the 14th century the "Killer Smog" reported in 1952, claimed 4000 fatalities in London - by far the most devastating event of this type in recorded history. Mechanism Inefficient combustion of high-sulphur coal => high concentration of unburned carbon soot and other particulates, acidic sulfate aerosols (such as sulfuric acid, H2SO4) as well as elevated levels of sulphur dioxide. SO2 and soot, => sulphuric acid, sulfate aerosols Characteristic brownish haze - formed usually under conditions of high humidity and relatively low temperatures, characterised by reducing and acidic properties. In case of humid atmospheres carbon particulates serve as condensation nuclei for water droplets resulting in formation of fog, highly irritant. Classical smog can persist for days when atmospheric conditions allow. Sulphur smog / London smog
Sulphur smog / London smog Batter Sea power station, London, UK
Impacts Deterioration of human made structures and materials Deterioration of flora Respiratory problems, allergies, asthma, lung damage Mitigation Burning of lower S-content coal Desulphurisation of flue gases Clean Air Acts, Sulphur Protocol Sulphur smog / London smog
process by which ozone is being created at low altitudes – ground level encountered in automobile rich cities – with specific climatic conditions History mid-1940s - repeated occurrence of heavy injury to vegetable crops in the Los Angeles area - traced to high concentrations of ozone that appeared to be created at low altitudes Photochemical smog / LA smog
Photochemical smog / LA smog Los Angeles
Photochemical smog / LA smog LA Santiago Las Vegas
Aerosols, ash, soot 3km thick 80% man-made industry, transportation, local wood /dung /kerosene burning, forest fires – clearing can travel half way round the globe in a week solar radiation reduced by up to 15% Hundreds of thousands of deaths annually (2mln in India alone) Acid rain Warming of the atmosphere Climate changes (floods & draughts) Other Brown Clouds: South America, Mediterranean The regional and global impact of the haze will intensify over the next 30 years Asian Brown Cloud
Impacts Impaired visibility Eye and respiratory system irritants Damage to lung tissue Vegetation damage Contribution to acidic deposition Materials destruction (rubber and some plastics) Photochemical smog / LA smog
Photochemical smog / LA smog • How to reduce smog (main goal is to reduce VOC and NOx): • PCV valves • Leak-proof caps • Tune-up • Emission tests • Catalytic converters • Public transportation
History First studies on rain chemistry were conducted in late 1800s, but modern investigations date back to 1960s. Nowadays the chemistry of atmospheric precipitation is fairly well known. The phenomenon of acid rain has been known and studied from 1950s. 1960 – lowered fish production in Scandinavian lakes In 1972 it became an international public policy issue at the first United Nations Conference on the Environment held in Stockholm. The transboundary effect of atmospheric pollution has been officially accepted, based on the fact that sulphur and nitrogen oxides are commonly emitted in one location while the acid deposition occurs in distant area. In Sweden and Norway around 90% of the acid deposition comes from other countries, primarily UK, Germany, Poland and other Central Europe countries. Canada receives major acid contribution form the US. Acid Rain Source: Van Loon G.W., Duffy S.J., 2000.
Acid Rain • Rain that is more acidic than normal because it contains sulfuric acid or nitric acid • result of SOx, NOx, acidic particulates in air • involves all forms of acid deposition, even if rain is not involved • Utility plants contribute to 70% SO2 production and 30% NOx production in USA • Coal contains as high as 5% sulfur
SOx emissions of energy options Source: Boyle et al. 2003
NOx emissions of energy options Source: Boyle et al. 2003
Acidification of water ecosystems Natural surface waters - pH of 6-8, acidified waters pH 3 (conditions unbearable for many aquatic species, which eventually die, and lakes become lifeless) Today some 14000 lakes in Sweden are affected by acidification. Similar situation is in Canada Nitrogen can induce eutrophication, which results in depletion of oxygen in water, further affecting the aquatic flora and fauna Impacts of acid rain
Acidification of soil ecosystems Areas with highly siliceous bedrock (granite, gneisses, quartzite, and quartzstone - acidic) – most vulnerable (Scandinavia, Canada, United Kingdom and Alps). Acid deposition - enhances leaching of important cations such as calcium, potassium, magnesium and sodium - unavailable to plants as nutrients (soil depletion) Reduced fertility of soil Some metals (i.e. aluminium, and mercury) leach from acidified soils into waters Impacts of acid rain
Damage of flora A 1999 survey of European forests - one out of every four trees suffered the loss of 25% or more leaves or needles Decay of structural materials Marble, sandstone, rubber, metals Herten, Germany, 1908 & 1969 Impacts of acid rain
Human health problems respiratory problems including lung disorders, asthma, and bronchitis due to suspended atmospheric sulphates indirect effect of acidification on humans is related to the presence of toxic metals in the food chain Impacts of acid rain
Conventions/Targets the Convention on Long Range Transboundary Air Pollution (1994 Sulphur Protocol) – with amendments 5th Environmental Action Programme and by the Council of Ministers of the Environment) 1999 Gothenburg Protocol to Abate Acidification, Eutrophication and Ground-Level Ozone Mitigation
The annual cost of the multi-effect protocol is estimated at the level of 2.8 billion euro for the year 2010. The returns, in the form of improved health and reduced corrosion to buildings would by that same year amount to euro 12.8 billion. Plus there are benefits that do not carry a price tag… Mitigation
Ozone Depletion • Stratospheric Ozone absorbs harmful ultraviolet (<340nm) radiation from the Sun • 1% loss of ozone = 2% increase in UV radiation = 106 extra cancers • ozone hole = 7.7 million sq. miles • CFCs & HCFCs are the primary causes
Ozone hole above the the Antarctic on October 3, 1999 (NASA satellites) A record size of ozone hole was 10.5 million square miles on Sept 19, 1998 Red color would denote high ozone levels; blue denotes low Antartic/Arctic ozone hole
Impacts Humans (a 10% drop in stratospheric ozone levels is likely to lead globally to 300000 more skin cancers, 1.6 million more eye damage – cataracts) per year Reptiles (damage to eggs) Plants (reduced photosynthesis, increased sensitivity to stress) Damage to marine ecosystems (direct and indirect) Ozone layer depletion