Journals / Atmospheric Pollution Research / 2019 / Cilt: 10 - Sayı: 1

Mass balance and behavior of mercury in oil refinery facilities

Pages
145–151
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

The average mass distribution factors ofmercury by oil refinery processes into petroleum products, by-products, and the air was 61.35%, 29.08%, and9.56%, respectively.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:This study aims to provide the mass balance of mercury and an assessment of anthropogenic mercury release intothe air, water, wastes, and products from two oil refinery plants in Korea.
📊
Key Findings & Data:After normalizing themeasured data at low recovery rates, facility A was found to release the most mercury through products, sludge,and air at 77.9%, 8.3%, and 8% respectively, and facility B released the most mercury through products, sludge,and air at 44.8%, 37.6%, and 11.1% respectively.
💡
Conclusion & Impact:The average mass distribution factors ofmercury by oil refinery processes into petroleum products, by-products, and the air was 61.35%, 29.08%, and9.56%, respectively.
🔬Design:Research Article
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Özet

This study aims to provide the mass balance of mercury and an assessment of anthropogenic mercury release intothe air, water, wastes, and products from two oil refinery plants in Korea. The mercury concentrations in inputstreams (crude oil and condensates) and output streams (petroleum products and by-products, such asfly ash,sludge and waste water, andflue gas) were measured at two representative oil refineries. After normalizing themeasured data at low recovery rates, facility A was found to release the most mercury through products, sludge,and air at 77.9%, 8.3%, and 8% respectively, and facility B released the most mercury through products, sludge,and air at 44.8%, 37.6%, and 11.1% respectively. The average national emission factor of mercury into the airfrom oil refineries was estimated at 0.12 mg-Hg ton−1input product. The average mass distribution factors ofmercury by oil refinery processes into petroleum products, by-products, and the air was 61.35%, 29.08%, and9.56%, respectively.

🔖

Cite This Article

MOJAMMAL, A., BACK, S., SEO, Y., KİM, J. (2019). Mass balance and behavior of mercury in oil refinery facilities. Atmospheric Pollution Research, Cilt: 10 - Sayı: 1, 145–151. https://ajindex.com/articles/351341

References (6)

  1. AMAP/UNEP, 2008. Technical Background Report on the Global Anthropogenic MercuryAssessment. Arctic Monitoring and Assessment Programme/UNEP Chemicals Branch,pp. 159. AMAP/UNEP (Arctic Monitoring and Assessment Programme/United NationsEnvironment Programme), 2013. Technical Background Report for the GlobalMercury Assessment 2013. AMAP/UNEP Chemicals Branch, Geneva, Switzerland vi+ 263 pp. BEIS (Business, Energy and Industrial Strategy), 2017. Digest of United Kingdom EnergyStatistics 2017.
  2. Department for Business, Energy and Industrial Strategy (BEIS), UKGovernment Source:https://www.gov.uk/government/uploads/system/uploads/attachment_data/file/643414/DUKES_2017.pdf, Accessed date: 7 December 2017.
  3. Bingham, M.D., 1990. Field detection and implications of mercury in natural gas. SPEProd. Eng. 5, 120–124.https://doi.org/10.2118/19357-PA.BP (British Petroleum), 2016. BP Statistical Review of World Energy. June 2016. Source:https://www.bp.com/content/dam/bp/pdf/energy-economics/statistical-review-2016/bp-statistical-review-of-world-energy-2016-full-report.pdf, Accessed date: 17January 2018.
  4. Ekino, S., Susa, M., Ninomiya, T., Imamura, K., Kitamura, T., 2007. Minamata diseaserevisited: an update on the acute and chronic manifestations of methyl mercurypoisoning. J. Neurol. Sci. 262 (2007), 131–144.https://doi.org/10.1016/j.jns.2007.06.036. European Parliament, 2017. Briefing for Minamata Convention COP1. Policy DepartmentA: Economy and Scientific and Quality of Life Policies, 24 Economy and Scientific andQuality of Life Policies, European Parliament PE 607.347. Key issues at stake at COP1on the Minamata Convention. Geneva, 24–29 September 2017.http://www.europarl.europa.eu/RegData/etudes/BRIE/2017/607347/IPOL_BRI(2017)607347_EN.pdf, Accessed date: 14 January 2018. KEEI (Korea Energy Economics Institute), 2015. Year Book of Energy Statistics. ISSN1226-606X.http://www.keei.re.kr/keei/download/YES2015.pdf.
  5. Kim, J.H., Park, J.M., Lee, S.B., Pudasainee, D., Seo, Y.C., 2010. Anthropogenic mercuryemission inventory with emission factors and total emission in Korea. Atmos.Environ. 44 (2010), 2714–2721.https://doi.org/10.1016/j.atmosenv.2010.04.037.
  6. Lang, D., Gardener, M., Holmes, J., 2012. Mercury Arising from Oil and Gas Production inthe United Kingdom and UK Continental Shelf. Integrating Knowledge to InformMercury Policy (IKIMP). Dept of Earth Sciences, University of Oxford, UK Source:http://www.mercurynetwork.org.uk/wp-content/uploads/2009/09/IKIMP-Oil-and-Gas-2012-F