Plasma gasification

Plasma gasification
Process type Chemical
Industrial sector(s) Waste management
Energy
Main technologies or sub-processes Plasma arc
Plasma electrolysis
Feedstock Municipal and industrial waste
Biomass
Solid hydrocarbons
Product(s) Syngas
Slag
Separated metal scrap

Plasma gasification is a process which converts organic matter into synthetic gas,[1] electricity,[2] and slag[1] using plasma. A plasma torch powered by an electric arc, is used to ionize gas and catalyze organic matter into synthetic gas and solid waste (slag).[1][3][4] It is used commercially as a form of waste treatment and has been tested for the gasification of biomass and solid hydrocarbons, such as coal, oil sands, and oil shale.[3]

Process

A plasma torch itself typically uses an inert gas such as argon. The electrodes vary from copper or tungsten to hafnium or zirconium, along with various other alloys. A strong electric current under high voltage passes between the two electrodes as an electric arc. Pressurized inert gas is ionized passing through the plasma created by the arc. The torch's temperature ranges from 4,000 to 25,000 °F (2,200 to 13,900 °C).[5] The temperature of the plasma reaction determines the structure of the plasma and forming gas. This can be optimized to minimize ballast contents[6], composed of the byproducts of oxidation: {{CO2}}, N2, H2O, etc..

The waste is heated, melted and finally vaporised. At these conditions molecular dissociation can occur by breaking down molecular bonds. Complex molecules are separated into individual atoms. The resulting elemental components are in a gaseous phase. Molecular dissociation using plasma is referred to as "plasma pyrolysis."[7]

Feedstocks

The feedstock for plasma waste treatment is most often municipal solid waste, organic waste, or both. Feedstocks may also include biomedical waste and hazmat materials. Content and consistency of the waste directly impacts performance of a plasma facility. Pre-sorting and recycling useful material before gasification provides consistency. Too much inorganic material such as metal and construction waste increases slag production, which in turn decreases syngas production. However, a benefit is that the slag itself is chemically inert and safe to handle (certain materials may affect the content of the gas produced, however[2]). Shredding waste before entering the main chamber helps to increase syngas production. This creates an efficient transfer of energy which ensures more materials are broken down.[2]

For better processing, air and/or steam is added into plasma gasificator.

Yields

Pure highly calorific synthetic gas consists predominantly of Carbon monoxide (CO), H2, CH, among other components. The conversion rate of plasma gasification exceeds 99%.[8] Non-flammable inorganic components in the waste stream are not broken down. This includes various metals. A phase change from solid to liquid adds to the volume of slag.

Plasma processing of waste is ecologically clean. The lack of oxygen prevents the formation of many toxic materials. The high temperatures in a reactor also prevent the main components of the gas from forming toxic compounds such as furans, dioxins, nitrogen oxides, or sulfur dioxide. Water filtration removes ash and gaseous pollutants.

The production of ecologically clean synthetic gas is the standard goal. The gas product contains no phenols or complex hydrocarbons however circulating water from filtering systems is toxic. The water removes toxins (poisons) and the hazardous substances which must be cleaned.[9]

Metals resulting from plasma pyrolysis can be recovered from the slag and eventually sold as a commodity. Inert slag is granulated. This slag grain is used in construction. A portion of the syngas produced feeds on-site turbines, which power the plasma torches and thus support the feed system. This is self-sustaining electric power.[8]

Equipment

Gasification reactors operate at negative pressure[1] and recover both[10] gaseous and solid resources.

Advantages

The main advantages of plasma technologies for waste treatment are:

Disadvantages

Main disadvantages of plasma technologies for waste treatment are:

Commercialization

Municipal-scale plasma gasification is used commercially for waste disposal[21][22][23][24][25][26][27][28] in five locations worldwide.

In the Northeast of England in the United Kingdom plasma gasification technology was attempted implemented within the Northeast of England Process Industry Cluster(NEPIC) on Teesside by Air Products. Two large units were erected, designed to gasify societal waste to produce power with the synthesis gas produced.[29] By late 2015, Air Products halted construction on the second phase until it fixed issues encountered during commissioning of the first phase. On April 4, 2016, Air Products announced it was leaving the waste-to-energy business, and was taking a write-down of $0.9-$1.0B.[30] [31]

Military Use

The US Navy is employing Plasma Arc Waste Destruction System (PAWDS) on its latest generation Gerald R. Ford-class aircraft carrier. The compact system being used will treat all combustible solid waste generated on board the ship. After having completed factory acceptance testing in Montreal, the system is scheduled to be shipped to the Huntington Ingalls shipyard for installation on the carrier.[32]

See also

References

  1. 1 2 3 4 5 Moustakasa, K.; Fattab, D.; Malamisa, S.; Haralambousa, K.; et al. (2005-08-31). "Demonstration plasma gasification/vitrification system for effective hazardous waste treatment". Journal of Hazardous Materials 123 (1–3): 120–126. doi:10.1016/j.jhazmat.2005.03.038. Retrieved 2012-03-08. (subscription required (help)).
  2. 1 2 3 "How Stuff Works- Plasma Converter". Retrieved 2012-09-09.
  3. 1 2 Kalinenko, R. A.; Kuznetsov, A. P.; Levitsky, A. A.; Messerle, V. E.; et al. (1993). "Pulverized coal plasma gasification". Plasma Chemistry and Plasma Processing 13 (1): 141–167. doi:10.1007/BF01447176. Retrieved 2012-03-08. (subscription required (help)).
  4. Messerle, V. E.; Ustimenko, A. B. (2007). "Solid Fuel Plasma Gasification". In Syred, Nick; Khalatov, Artem. Advanced Combustion and Aerothermal Technologies. Environmental Protection and Pollution Reductions. Springer Netherlands. pp. 141–156. doi:10.1007/978-1-4020-6515-6. ISBN 978-1-4020-6515-6. Retrieved 2012-03-08. (subscription required (help)).
  5. "The Recovered Energy System: Discussion on Plasma Gasification". Retrieved 2008-10-20.
  6. Bratsev, A. N.; V. E. Popov; A. F. Rutberg; S. V. Shtengel’ (2006). "A Facility for Plasma Gasification of Waste of Various Types" (PDF). High temperature 44 (6): 823–828. Retrieved 2013-03-12.
  7. Huang, H.; Lan Tang; C. Z. Wu (2003). "Characterization of Gaseous and Solid Product from Thermal Plasma Pyrolysis of Waste Rubber". Environmental Science & Technology 37 (19): 4463–4467. doi:10.1021/es034193c. Retrieved 2013-03-12.
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  15. Mountouris, A.; E. Voutsas; D. Tassios (2008). "Plasma Gasification of Sewage Sludge: Process Development and Energy Optimization". Energy Conversion and Management 49 (8): 2264–2271. doi:10.1016/j.enconman.2008.01.025. Retrieved 2013-03-20.
  16. Leal-Quirós, Edbertho (2004). "Plasma Processing of Municipal Solid Waste". Brazilian Journal of Physics 34 (4B): 1587–1593. Bibcode:2004BrJPh..34.1587L. doi:10.1590/S0103-97332004000800015. Retrieved 2013-03-20.
  17. Jimbo, Hajime (1996). "Plasma Melting and Useful Application of Molten Slag". Waste management 16 (5): 417–422. doi:10.1016/S0956-053X(96)00087-6. Retrieved 2013-03-20.
  18. Huang, Haitao; Lan Tang (2007). "Treatment of Organic Waste Using Thermal Plasma Pyrolysis Technology". Energy Conversion and Management 48 (4): 1331–1337. doi:10.1016/j.enconman.2006.08.013. Retrieved 2013-03-12.
  19. Pourali, M. "Application of Plasma Gasification Technology in Waste to Energy #x2014;Challenges and Opportunities". IEEE Transactions on Sustainable Energy 1 (3): 125–130. doi:10.1109/TSTE.2010.2061242. ISSN 1949-3029.
  20. Leal-Quirós, Edbertho (December 2004). "Plasma Processing of Municipal Solid Waste". Brazilian Journal of Physics 34 (4B): 1587–1593. Bibcode:2004BrJPh..34.1587L. doi:10.1590/S0103-97332004000800015. ISSN 0103-9733. Retrieved 2013-03-20.
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External links

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