Gas flare

A gas flare, alternatively known as a flare stack, is a gas combustion device used in industrial plants such as petroleum refineries, chemical plants and natural gas processing plants as well as at oil or gas production sites having oil wells, gas wells, offshore oil and gas rigs and landfills.

In industrial plants, flare stacks are primarily used for burning off flammable gas released by pressure relief valves during unplanned over-pressuring of plant equipment.[1][2][3][4][5] During plant or partial plant startups and shutdowns, flare stacks are also often used for the planned combustion of gases over relatively short periods.

Gas flaring at many oil and gas production sites protects against the dangers of over-pressuring industrial plant equipment. An example of the consequences of failure to flare escaping gas was evident in the Bhopal disaster when a flare tower was broken and couldn't flare escaping methyl isocyanate gas (The gas had been in an overpressured tank and released by a safety valve), which resulted in its release into the surrounding area[6]. When petroleum crude oil is extracted and produced from oil wells, raw natural gas associated with the oil is brought to the surface as well. Especially in areas of the world lacking pipelines and other gas transportation infrastructure, vast amounts of such associated gas are commonly flared as waste or unusable gas. The flaring of associated gas may occur at the top of a vertical flare stack (as in the adjacent photo) or it may occur in a ground-level flare in an earthen pit. Preferably, associated gas is reinjected into the reservoir, which saves it for future use while maintaining higher well pressure and crude oil producibility.[7]

Overall flare system in industrial plants

When industrial plant equipment items are over-pressured, the pressure relief valve is an essential safety device that automatically release gases and sometimes liquids. Those pressure relief valves are required by industrial design codes and standards as well as by law.

The released gases and liquids are routed through large piping systems called flare headers to a vertical elevated flare. The released gases are burned as they exit the flare stacks. The size and brightness of the resulting flame depends upon the flammable material's flow rate in joules per hour (or btu per hour).[4]

Most industrial plant flares have a vapor-liquid separator (also known as a knockout drum) upstream of the flare to remove any large amounts of liquid that may accompany the relieved gases.

Steam is very often injected into the flame to reduce the formation of black smoke. When too much steam is added, a condition known as "over steaming" can occur resulting in reduced combustion efficiency and higher emissions. To keep the flare system functional, a small amount of gas is continuously burned, like a pilot light, so that the system is always ready for its primary purpose as an over-pressure safety system.

The adjacent flow diagram depicts the typical components of an overall industrial flare stack system:[1][2][3]

  • A knockout drum to remove any oil or water from the relieved gases.
  • A water seal drum to prevent any flashback of the flame from the top of the flare stack.
  • An alternative gas recovery system for use during partial plant startups and shutdowns as well as other times when required. The recovered gas is routed into the fuel gas system of the overall industrial plant.
  • A steam injection system to provide an external momentum force used for efficient mixing of air with the relieved gas, which promotes smokeless burning.
  • A pilot flame (with its ignition system) that burns all the time so that it is available to ignite relieved gases when needed.[8]
  • The flare stack, including a flashback prevention section at the upper part of the stack.

Impacts of waste flaring associated gas from oil drilling sites and other facilities

Improperly operated flares may emit methane and other volatile organic compounds as well as sulfur dioxide and other sulfur compounds, which are known to exacerbate asthma and other respiratory problems. Other emissions from improperly operated flares may include, aromatic hydrocarbons (benzene, toluene, xylenes) and benzo(a)pyrene, which are known to be carcinogenic.

Flaring can affect wildlife by attracting birds and insects to the flame. Approximately 7,500 migrating songbirds were attracted to and killed by the flare at the liquefied natural gas terminal in Saint John, New Brunswick, Canada on September 13, 2013.[9] Similar incidents have occurred at flares on offshore oil and gas installations.[10] Moths are known to be attracted to lights. A brochure published by the Secretariat of the Convention on Biological Diversity describing the Global Taxonomy Initiative describes a situation where "a taxonomist working in a tropical forest noticed that a gas flare at an oil refinery was attracting and killing hundreds of these [hawk or sphinx] moths. Over the course of the months and years that the refinery was running a vast number of moths must have been killed, suggesting that plants could not be pollinated over a large area of forest".[11]

As of the end of 2011, 150 × 109 cubic meters (5.3 × 1012 cubic feet) of associated gas are flared annually. That is equivalent to about 25 percent of the annual natural gas consumption in the United States or about 30 per cent of the annual gas consumption in the European Union.[12] If it were to reach market, this quantity of gas (at a nominal value of $5.62 per 1000 cubic feet) would be worth US$29.8 billion.[13]

Also as of the end of 2011, 10 countries accounted for 72 per cent of the flaring, and twenty for 86 per cent. The top ten leading contributors to world gas flaring at the end of 2011, were (in declining order): Russia (27%), Nigeria (11%), Iran (8%), Iraq (7%), United States (5%), Algeria (4%), Kazakhstan (3%), Angola (3%), Saudi Arabia (3%) and Venezuela (3%).[14]

That amount of flaring and burning of associated gas from oil drilling sites is a significant source of carbon dioxide (CO2) emissions. Coupled with fossil fuel combustion and cement production, flaring's carbon dioxide emissions in 2010 have tripled (1300 ± 110 GtCO2) compared to the last recording (years 1750-1970, 420 ± 35 GtCO had been emitted.)[15] 2400 × 106 tons of carbon dioxide are emitted annually in this way and it amounts to about 1.2 per cent of the worldwide emissions of carbon dioxide. That may seem to be insignificant, but in perspective it is more than half of the Certified Emissions Reductions (a type of carbon credits) that have been issued under the rules and mechanisms of the Kyoto Protocol as of June 2011.[12][16]

Satellite data show that from 2005 to 2010, global gas flaring decreased by about 20%. The most significant reductions in terms of volume were made in Russia (down 40%) and Nigeria (down 29%).[12][17]

The Obama administration implemented rules curbing flaring, and subsequently the Trump administration attempted to delay implementation of the rules. In October 2017 a federal magistrate judge vacated the Department of Interior's move to delay implementation.[18]

Environmental benefit

Methane's estimated global warming potential is 34 times greater than that of CO2.[19] Therefore, to the extent that gas flares convert methane to CO2 before it is released into the atmosphere, they reduce the amount of global warming that would otherwise occur.[20]

An important source of anthropogenic methane comes from the treatment and storage of organic waste material including waste water, animal waste and landfill.[21] Gas flares are used in any process that results in the generation and collection of biogas. As a result, gas flares a standard component of an installation for controlling the production of biogas.[22] They are installed on landfill sites, waste water treatment plant and anaerobic digestion plant that use agriculturally or domestically produced organic waste to produce methane for use as a fuel or for heating.

Gas flares on biogas collection systems are used if the gas production rates are not sufficient to warrant use in any industrial process. However, on a plant where the gas production rate is sufficient for direct use in an industrial process that could be classified as part of the circular economy, and that may include the generation of electricity, the production of natural gas quality biogas for vehicle fuel[23] or for heating in buildings, drying Refuse Derived Fuel or leachate treatment, gas flares are used as a back-up system during down-time for maintenance or breakdown of generation equipment. In this latter case, generation of biogas cannot normally be interrupted and a gas flare is employed to maintain the internal pressure on the biological process.[24]

There are two types of gas flare used for controlling biogas, open or enclosed. Open flares burn at a lower temperature, less than 1000 °C and are generally cheaper than enclosed flares that burn at a higher combustion temperature and are usually supplied to conform to a specific residence time of 0.3s within the chimney to ensure complete destruction of the toxic elements contained within the biogas.[25] Flare specification usually demands that enclosed flares must operate at >1000 °C and <1000 °C; this in order to ensure a 98% destruction efficient and avoid the formation of NOx.[26]

See also


  1. EPA/452/B-02-001, Section 3.0: VOC Controls, Section 3.2: VOC Destruction Controls, Chapter 1: Flares. (A U.S. Environmental Protection Agency report, dated September 2000.)
  2. A. Kayode Coker (2007). Ludwig's Applied Process Design for Chemical And Petrochemical Plants, Volume 1 (4th ed.). Gulf Professional Publishing. pp. 732–737. ISBN 978-0-7506-7766-0.
  3. Sam Mannan (Editor) (2005). Lee's Loss Prevention in the Process Industries: Hazard Identification, Assessment and Control, Volume 1 (3rd ed.). Elsevier Butterworth-Heinemann. pp. 12/67–12/71. ISBN 978-0-7506-7857-5.CS1 maint: extra text: authors list (link)
  4. Milton R. Beychok (2005). Fundamentals of Stack Gas Dispersion (Fourth ed.). self-published. ISBN 978-0-9644588-0-2. (See Chapter 11, Flare Stack Plume Rise).
  5. "A Proposed Comprehensive Model for Elevated Flare Flames and Plumes", David Shore, Flaregas Corporation, AIChE 40th Loss Prevention Symposium, April 2006.
  6. Bhopal disaster
  7. Leffler, William (2008). Petroleum Refining in Nontechnical Language. Tulsa, OK: PennWell. p. 9.
  8. Product Overview Ignition Systems, Smitsvonk, November 2001. Excellent source of information about flare stack pilot flames and their ignition systems.
  9. 7,500 songbirds killed at Canaport gas plant in Saint John (online CBC News, September 17, 2013).
  10. Seabirds at Risk around Offshore Oil Platforms in the North-west Atlantic, Marine Pollution Bulletin, Vol. 42, No. 12, pp. 1,285-1,290, 2001.
  11. The Global Taxonomy Initiative - The Response to a Problem (scroll down to the section entitled "Pollinating moths")
  12. Global Gas Flaring Reduction Partnership (GGFR), World Bank, October 2011 Brochure.
  13. Annual Energy Review, Table 6.7 Natural Gas Wellhead, Citygate, and Imports Prices, 1949-2011 (Dollars per Thousand Cubic Feet), United States Energy Information Administration, September 2012.
  14. Estimated Flared Volumes from Satellite Data, 2007-2011. From the website of the World Bank.
  15. IPCC. "IPCC 2014: Summary for Policy Makers.In: Climate Change 2014, Mitigation of Climate Change" (pdf). Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA. Retrieved December 11, 2014.
  16. Global Gas Flaring Reduction. From the website of the World Bank.
  17. Estimation of Gas Flaring Volumes Using NASA MODIS Fire Detection Products (alternative). Christopher Elvidge et al, NOAA's National Geophysical Data Center (NGDC) annual report, February 8, 2011.
  18. Lipton, Eric (2017-10-06). "Courts Thwart Administration's Effort to Rescind Obama-Era Environmental Regulations". The New York Times. ISSN 0362-4331. Retrieved 2017-10-13.
  19. Jain, Atul K.; et al. (August 27, 2000), "Radiative forcings and global warming potentials of 39 greenhouse gases", Journal of Geophysical Research: Atmospheres, 105 (D16): 20773–20790, Bibcode:2000JGR...10520773J, doi:10.1029/2000JD900241.
  20. "Natural gas - Gas flaring and gas venting - Eniscuola". Eniscuola Energy and Environment. Retrieved 23 June 2018.
  21. "Environmental Impact Of Using Biomass And Biogas Technology". Retrieved 2019-03-29.
  22. US EPA, OAR (2016-04-15). "Basic Information about Landfill Gas". US EPA. Retrieved 2019-03-29.
  23. "Alternative Fuels Data Center: Alternative Fuels and Advanced Vehicles". Retrieved 2019-03-29.
  24. "Management of landfill gas: LFTGN 03". GOV.UK. Retrieved 2019-03-29.
  25. "TA Luft", Wikipedia, 2018-06-21, retrieved 2019-03-29
  26. "(PDF) NOx Emissions from Silicon Production". ResearchGate. Retrieved 2019-03-29.

Further reading

  • Banerjee K.; Cheremisinof N.P.; Cheremisinoff P.N (1985). Flare gas systems pocket handbook. Houston, TX: Gulf Publishing Company. ISBN 978-0-87201-310-0.


External images
World Bank video about reducing flaring
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