impact of thermal power plant fly ash and its its mitigation mesure
TRANSCRIPT
Impact of coal based thermal power plant on environment and its mitigation measure
AbstractIndia is the world’s fourth largest economy and has a fast growing energy market. India’s current
power capacity is 30% short of demand. Coal and petroleum are the primary sources of energy.
High ash content in Indian coal and inefficient combustion technologies contribute to India’s
emission of air particulate matter and other trace gases, including gases that are responsible for
the greenhouse Due to thermal combustion of coal produces radionuclide and a portion of
radionuclide’s produces from the ash this create health hazards. Due to increasing the demand of
energy use of coal is increasing significantly so we can mitigate the pollution by using several
alternatives like for removal of fly ash, using fly ash for making bricks, cement, distemper
rceramics,fetilizerand use in road construction .therefore by utililizing fly ash we can reduces the
health hazards.
Key words-Coal, Fly ash, Radionuclide, Thermal power, Green house gas
1. Introduction
Coal is the only natural resource and fossil fuel available in abundance in India. Consequently, It
is used widely as a thermal energy source and also as fuel for thermal power plants producing
electricity. Power generation in India has increased manifold in the recent decades to meet the
demand of the increasing population. Generating capacity has grown many times from 1362MW
in 1947 to 147,403MW (as on December 2008). India has about 90,000 MWe installed capacity
for electricity generation, of which more than 70% is produced by coal- based thermal power
plants. The only fossil fuel available in abundance is coal, and hence its usage will keep growing
for another 2–3 decades at least till nuclear power makes a significant contribution. The coal
available in India is of poor quality, with very high ash content and low calorific value, and most
of the coal mines are located in the eastern part of the country. Whatever good quality coal
available is used by the metallurgical industry, like steel plants. The coal supplied to power
plants is of the worst quality. Some of the coal mines are owned by private companies, and they
do not wish to invest on quality improvement. Combustion process converts coal into useful heat
energy, but it is also a part of the process that produce greatest environmental and health
concerns. Combustion of coal at thermal power plants emits mainly carbon dioxide (CO2),
sulphur oxides (SOx), nitrogen oxides (NOx), CFCs other trace gases and air borne inorganic
particulates, such as fly ash and suspended particulate matter (SPM). CO2, NOx and CFCs are
green house gases (GHGs) High ash content in Indian coal and inefficient combustion
technologies contribute to India’s emission of air particulate matter and other trace gases,
including gases that are responsible for the greenhouse effect.
2. Problems associated with CO2 increase in atmosphere
CO2 produced in combustion is perhaps not strictly a pollutant (being a natural product of all
combustion), nonetheless it is of great concern in view of its impact on global warming. Carbon
dioxide is a stable molecule with less than 10 years average residence time is 3 years in the
troposphere though its residence time is over 100 years in the atmosphere, and its present
concentration in the atmosphere is increasing at an astonishing rate of 0.4% per year. Electricity
has been a preferred form for energy consumption and has consistently registered a higher
growth rate than other forms of energy. India is a developing country with over a billion
population and immense natural resources with total surface area of 3,287,590 sq. km and a huge
land area of 2,973,190 sq. km. Increased consumption of electric power is more intimately bound
up with economic development on the one hand and increased emission of pollutants on the
other hand. Establishment of new industries, plants, commercial complexes and expansion of the
capacity for consumer goods industries to feed its ever increasing population has led to a
considerable increase in the consumption of electricity in India and, consequently, the emission
levels of CO2. Based on their studies in the northern hemisphere, Dunn and Flavin stated that
carbon dioxide, which is released into the atmosphere from the burning of fossil fuels, is the
single most important greenhouse gas contributing to the ‘‘anthropogenic forcing of climate
change’’. Thus, they conclude the share of CO2 in warming is expected to rise from slightly more
than half today to around 3/4th by 2100 and further stated that the average global surface
temperature would be raised more during the 20th century than during any other century in the
last 1000 years. Carbon dioxide comprises about 0.03% of the earth’s atmospheric volume, but
due to the combustion of fossil fuels and deforestation, this percentage has increased by about
25% since preindustrial times. Each year about 5 Gt of carbon is released into the atmosphere
due to fossil fuel combustion. The average concentration of CO2 in the atmosphere has already
reached 358 ppm by volume (ppmv), compared to the pre-industrial level of 280 ppmv.
Scientists project that excessive CO2 emissions into the atmosphere will increase the earth’s
surface temperature In most developing countries, CO2 emissions are between 0.3 and 0.6 tons of
carbon per capita per year. The relative rate of CO2 emission increase in developing countries has
been much larger during the last few decades (about 5% per year in developing regions in
contrast to 1% per year in industrial regions during the last decades) Fast accumulation of carbon
dioxide in the atmosphere can evidently affect the climate of earth rather quickly by warming the
earth surface. This effect is associated with the absorption of long wavelength radiation much
more by CO2 than other GHGs. In particular, the atmosphere of the northern hemisphere will be
warmer because of anthropogenic carbon dioxide when this contribution will have reached
several billion tons, corresponding to a60 ppm increase in concentration from now, such an
increase could take place by the year 2010. The Intergovernmental Panel on Climate Change
(IPCC) suggests that the global mean surface temperature of the earth has increased by between
0.3° and 0.6° C since the late 19th century. Giorgi and Hewitson concluded that a doubling of
CO2 would increase the temperature by 2–4° C and decrease rainfall by 10–20%. Carbon dioxide
has already risen by 30% since the industrial era began. The global atmosphere traps an
increasing amount of heat due to the increased concentration of CO2, and thus, higher
temperatures result globally. This change in atmospheric temperature is of concern since even an
increase of a few degrees would lead to severe regional effects, such as prolonged droughts, crop
failure, change in cropping pattern, vegetative production with increased desertification, polar ice
might partially melt, resulting in ocean flooding and submergence of major portions of low lying
islands and coastal areas. Problems like global warming, climate change, emergence of natural
hazards like flooding and change in sea levels.
3. Problems associated of increasing fly ash
India has about 211 billion tons of coal reserves, which is known to be the largest resource of
energy and presently 240MT of coal is being used annually to meet the Nation’s electricity
demand. In terms of energy, India stands at world sixth position accounting 3.5% of the world
commercial energy demand in 2001, but the electricity generation yet not completely fulfilled the
present requirement. Though nuclear power programmed envisaged for generation of
20,000MWof nuclear energy by the year 2020, India do not have option in the foreseeable future,
except the fossil fuel mainly based on coal sources. The rate of annual increase in power
generation in India is 5%. And at this rate the annual power generation by the year 2020 is
expected to be 180,000MW, which may release about 190MT of CCRs per annum. However, to
achieve sustainable development the Nation may have to generate at least 260,000MW of power
(i.e. 10% increases in rate of annual electricity generation) by the year 2020 and as consequence
273MT of CCRs is expected to be released. Keeping in view of the formidable future problems
due to these huge quantity of CCRs to achieve Environmental Sound Management, it is very
crucial time for confidence building on CCRs utilization and increase in acceptability of CCRs
based products among the end users Environmental pollution by the coal based thermal power
plants all over the world is cited to be one of the major sources of pollution affecting the general
aesthetics of environment in terms of land use, health hazards and air, soil and water in particular
and thus leads to environmental dangers. Coal combustion residues (CCRs) are a collective term
referring to the residues produced during the combustion of coal regardless of ultimate utilization
or disposal. It includes fly ash, bottom ash, boiler slag, and fluidized bed combustion ash and
other solid fine particles(Asokan,2003;Keefer,1993) As per the ASTM standards, in India
bituminous and sub-bituminous coal results in class ‘F’ash and lignite coal produces class‘C’ ash
having high degree of self-hardening capacity. In India, presently coal based thermal power
plants are releasing 105MT of CCRs which possess major environmental problems (Kumar and
Mathur, 2004; Sharma et al., 2003).Presently from all these thermal power plants, dry fly ash has
been collected through Electrostatic Precipitator (ESP) in dry condition as well as pond ash from
ash ponds in semi-wet condition. In India most of the thermal power plants do not have the
facility for automatic dry ash collection system. Commonly both fly ash and bottom ash together
are discharged as slurry to the ash pond/lagoon these affect on environment, economy, and social
factor.
4. Problems associated with radionuclide increase in atmosphere coal combustion
Coal, like most materials found in nature, contains also natural radionuclides. The levels of
natural radionuclides in a geological formation depend on its composition and geological history.
In the production of electric power, coal is burned in a furnace operating at temperatures of up to
1700°C. In the combustion process, volatile radionuclide’s such as Pb210 and Po210 are partly
released in the flue gases and escape to the atmosphere. A significant fraction of the radioactivity
is also retained in the bottom ash or slag .The greatest part of the radioactivity in coal remains
with the ash but some of the fly ash from coal-fired power plants escapes into the atmosphere.
Air pollution in the vicinity of a coal fired thermal power station affects soil, water, vegetation,
the whole ecosystem and human health. Air pollution in the vicinity of a coal fired thermal
power station affects soil, water, vegetation, the whole ecosystem and human health.
"Environmental impact of coal utilization in thermal power plant" notes that "Radon is a
colorless, odorless but noble gas, which is radioactive and ubiquitously present. It poses grave
health hazards not only to uranium miners but also people living in normal houses and buildings
and at work place like coal mines, cement industry, thermal power plants etc. Coal, a naturally
occurring fossil fuel is burnt in conventional power plants to meet out about 72% of the
electricity needs in our country. It was lesser known hitherto until recently that the fly ash which
is a byproduct of burnt coal is a potential radioactive air pollutant and it modifies radiation
exposure.
6. Fly ash mitigation measure
Fly ash is fine glass powder, the particles of which are generally spherical in shape and range in
size from 0.5 to 100 micron. Fly ash is classified into two types according to the type of coal
used. Anthracite and bituminous coal produces fly ash classified as class F. Class C fly ash is
produced by burning lignite or sub-bituminous coal. Class C fly ash has self-cementing
properties. . Fly ash emissions from a variety of coal combustion units show a wide range of
composition. All elements below atomic number 92 are present in coal ash Particulate matter
(PM) considered as a source of air pollution constitutes fly ash. The fine particles of fly ash reach
the pulmonary region of the lungs and remain there for long periods of time; they behave like
cumulative poisons. The submicron particles enter deeper into the lungs and are deposited on the
alveolar walls where the metals could be transferred to the blood plasma across the cell
membrane Fly ash can be disposed-off in a dry or wet state. Studies show that wet disposal of
this waste does not protect the environment from migration of metal into the soil1. Heavy metals
cannot be degraded biologically into harmless products like other organic waste. Studies also
show that coal ash satisfies the criteria for landfill disposal, according to the Environmental
Agency of Japan 2. According to the hazardous waste management and handling rule of 1989,
fly ash is considered as non-hazardous. With the present practice of fly-ash disposal in ash ponds
(generally in the form of slurry), the total land required for ash disposal would be about 82,200
ha by the year 2020 at an estimated 0.6 ha per MW. Fly ash can be treated as a by-product rather
than waste.
i) Fly ash bricks
The Central Fuel Research Institute, Dhanbad has developed a technology for the utilization of
fly ash for the manufacture of building bricks. Fly ash bricks have a number of advantages over
the conventional burnt clay bricks. Unglazed tiles for use on footpaths can also be made from it.
Awareness among the public is required and the Government has to provide special incentives
for this purpose.
Six mechanized fly ash brick manufacturing units at Korba are producing about 60000 bricks per
day. In addition to this, two mechanized fly ash brick manufacturing units have been set up by
private entrepreneurs also at Korba, the total production being about 30000 bricks/day. Apart
from this about 23 entrepreneurs have registered in DTIC proposals for establishing ash brick
units. To give impetus to ash brick manufacturing, District Mining Officer, who is also the Nodal
Officer for fly ash utilization, is ensuring strict compliance of certain vital instructions issued in
connection with conventional brick making by MoEF i.e. mixing a minimum of 25% fly ash with
clay and fixed chimney in place of moving kilns.
ii) Fly ash in manufacture of cement
Fly ash is suitable for use as pozzolana. In the presence of moisture, it reacts chemically
with calcium hydroxide and CO2 present in the environment attack the free lime causing
deterioration of the concrete. A cement technologist observed that the reactive elements
present in fly ash convert the problematic free lime into durable concrete. The difference
between fly ash and Portland cement becomes apparent under a microscope. Fly ash
particles are almost totally spherical in shape, allowing them to flow and blend freely in
mixtures. This property makes fly ash a desirable admixture for concrete.
Current installed capacity of Indian cement industry is 110 MT per annum. Further, it is an
established fact that the mortar and the concrete with PPC perform better on strength as
well as durability parameters. As per the specifications of Bureau of Indian Standards fly
ash upto 35% can be used in manufacture of PPC, while worldwide there are examples of
countries that permit up to 55% utilization of fly ash in PPC production. Keeping in view
the technical advantages use of PPC be preferred on OPC, except in cases where in early
strength is very essential. Setting aside 25% of cement production for OPC for such
applications, the balance 75% can be PPC with an average fly ash content of 30%. It would
consume around 25 MT fly ash, replacing same amount of cement clinker and resulting in
net saving Rs. 2500 crores.
iii) Fly ash in distemper
Distemper manufactured with fly ash as a replacement for white cement has been used in several
buildings in Neyveli, Tamil Nadu, in the interior surfaces and the performance is satisfactory.
The cost of production will only be 50% that of commercial distemper.
iv) Fly ash-based ceramics
The National Metallurgical Laboratory, Jamshedpur has developed a process to produce
ceramics from fly ash having superior resistance to abrasion.
v) Fly ash as fertilizer
Fly ash provides the uptake of vital nutrients/minerals (Ca, Mg, Fe, Zn, Mo, S and Se) by crops
and vegetation, and can be considered as a potential growth improver. It serves as a good
fertilizer. Because It can be a soil modifier and enhance its moisture retaining capacity and fertility. It
improves the plant's water and nutrient uptake, helps in the development of roots and soil binding Use of
fly ash in agriculture has also proved to be economically rewarding. The improvement in yield
has been recorded with fly ash doses varying from 20 tone / hectare to 100 tone / hectare. On an
average 20-30% yield increase has been observed. Out of 150 million hectare of land under
cultivation, 10 million hectares of land can safely be taken up for application of fly ash per year.
Taking a moderate fly ash dose of 20 mt per hectare it would consume 200 million tone flyash
per year. This is more than the annual availability of fly ash, therefore the shortfalls would be
met from accumulated 1500 million tonne stock of fly ash (available in ash ponds). The fly ash
treated fields would give additional yield of 5 million tone food grains per year valued at about
Rs. 3000 crores.
vi) Fly ash in road construction
The use of fly ash in large quantities making the road base and surfacing can result in low value–
high volume utilization.
3 technology demonstration projects at New Delhi, Dadri (U.P.) and Raichur (Karnataka) have
been successfully completed for use of fly ash in road / flyover embankments. Guidelines have
been prepared and approved by Indian Roads Congress (IRC) as national standard. More than 10
multiplier effects have taken place across the country
Nizammuddin Bridge approach road embankment at New Delhi (in flood zone of river Yamuna
vii) Roads and Embankments
Another area that holds potential for utilization of large volumes of fly ash is road and flyover
embankments. Fly ash embankments at Okhla, Hanuman Setu, Second Nizamuddin bridge in
Delhi and roads at Raichur, Calcutta, Dadri etc. have established that on an average Rs. 50 to 75
per MT of earth work cost can be saved by using flyash (in lieu of soil) in such works, primarily
due to reduction in excavation & transportation costs.
7. Mitigation measure of radionuclide
1-The deposited materials like fly ash, bottom slag and their mixtures with gypsum (product of
desulphurization) show slightly enhanced external radiation on the disposal site, but solely on the
bear surface. A dose rate levels approach to the background level at the distance of some metres.
2-The technological improvement such as the dry disposal site for coal ash (instead of direct
inflow of ash slurry into the lake), introduction of a closed circuit of transport water and
introduction of the desulphurization process for stack releases, significantly reduced discharged
radioactivity into the environment. Positive findings of monitoring are reflected consequently in
decreasing trends of environmental contamination and lower environmental impact.
8. References
• Bui Duy Thanh et al, Assessing health impacts of air pollution from electricity
generation: the case of Thailand., 2000
• Chandra A, Chandra H. Impact of Indian and imported coal on Indian thermal power
plants. J Scient Industr Res 2004;23:156–62.
• Cement Manufacturing Association (1999).
• The Science of Climate Change, Intergovernmental Panel on Climate Change.
Cambridge, UK: Cambridge University Press; 1996.
• Dunn S, Flavin C. Moving the climate change agenda forward: In State of the World
2002. Special World Summit Edition. NY: WW Norton and Company, 2002; p. 25–50.
• Electricity Generating Authority Thailand (EGAT). Environmental Impacts Assessment
of Krabi Thermal Power Plant Project at Tambon Khlong Khanan, King Amphoe Nua
Khlong, Changwat Krabi: Main report. Prepared by Team Consulting Engineers Co. Ltd.,
May 1997.
• Eisenbud, M., Petro, H.G., 1964. Radioactivity in the atmospheric eluents of power
plants that use fossil fuels. Science 144, 288–289
• Frederick MD. Voluntary reporting of GHGs emissions reduction achieved in 2000. Air
Pollut Constants (Aspen Pubs Inc.) 2002;12(5):19–113.
• F˙IL˙IZ G ¨ UR and G ¨ UNSEL˙I YAPRAK Natural radionuclide emission from coal-
fired power plants in the southwestern of Turkey and the population exposure to external
radiation in their vicinity Journal of Environmental Science and Health Part A (2010) 45,
1900–1908
• ‘Fly Ash Mission’, Technology Information, Forecasting and Assessment Council
(TIFAC), Department of Science and Technology, Ministry of Science and Technology,
Government of India, Technology
• Flyash Utilisation – India Scenario & Case Studies’, V Kumar, K Zacharia, P Sharma,
Indo- European Workshop on ‘Handling & Utilisation of Coal Combustion by Products
from Indian Power Station, 1999, Ropar.
• Flyash – A Fortune for the Construction Industry’, V Kumar, C N Jha, P Sharma, Build
India 99, New Delhi.
• Fly Ash Utilization Information Centre, Korba The Regional Officer, Chhattisgarh
Environment Conservation Board.
• Hazardous emissions from Philippine coal-fired power plants, Greenpeace Laboratories,
University of Exeter, Exeter, UK, 2002.
• IPCC, Climate Change, The Science of Climate Change. Contribution of Working Group
I to the Second Assessment Report of the Intergovernmental Panel on Climate
Change [Houghton, J.T., L.G. Meira Filho, B.A. Callander, N. Harris, A. Kattenberg, and
K. Maskell (eds.)]. Cambridge University Press, Cambridge, United Kingdom and New
York, NY, 1995: USA, 572 pp.
• International Energy Agency (IEA), Greenhouse Gas R&D Program. Carbon dioxide
capture from power plant station UK, 1995.
• International Energy Agency (IEA), World Energy Outlook-2000. 2000: 66. IPCC, In:
Houghton JT, Ding Y, Griggs DJ, Noguer M, Van der Linden PJ, Dai X, et al., editors.
Climate Change2001: A Scienti.c Basis: Intergovernmental Panel onClimate Change.
Cambridge, UK: Cambridge University Press; 2001
• Japans Environmental Agency Notification No. 13, 1973; Assay of metals and other
contaminants in industrial wastes.1974
• Kumar S, Sinha S. Non-CO2 emitting renewable energy source in India: Paths, reliable
potential and requirement of industry related forestry pattern. Energy Convers Manage
1995;36(6–9):885–8.
• Manas Ranjan Senapati Fly ash from thermal power plants – waste management and
overview current science, vol. 100 , 2011
• Pvrecek,Lbendik Pb210 and Po210 in fossil fuel at the sostanj thermal power plant
(solvenia),Czechoslovak journal of physics, 2003
• Palit, A., Coal ash utilization in India. Urja J., 1992, 32, 39–44.
• Raghuvanshi SP, et al. Greenhouse gas: carbon dioxide emission inventory from
combustion of fossil fuels in power sector in India. In: Proceedings International
Conference World Climate Change Conference 2003, Moscow, Russia, 2003; p. 557.
• Senapati, M. R. and Banerjee, J., Advances in particulate emissions control. Paper
presented at Institution of Engineers (India), Orissa, November 1999.
• Shiv Pratap Raghuvanshi et al , Carbon dioxide emissions from coal based power
generation in India ,2005
• United Nations Scientific Committee on the Effects of Atomic Radiation (UNSCEAR),
1982 Report, United Nations, New York, 1982.
• U.C. Mishra , Environmental impact of coal industry and thermal power plants in India
2003
• Vimal Kumar et al fly ash billon dollar resources -wasted so far 2005