Oxidation of atomic mercury by hydroxyl radicals and photoinduced decomposition of methylmercury in the aqueous phase

• Published in: Atmospheric environment (1994) 2001-06, Vol.35 (17), p.3039-3047
• Main Authors: Gårdfeldt, Katarina, Sommar, Jonas, Strömberg, Dan, Feng, Xinbin
• Format: Article
• Language: English
• Subjects: Applied sciences; Atmospheric pollution; Biogeochemical cycling; Chemical composition and interactions. Ionic interactions and processes; Earth, ocean, space; Exact sciences and technology; External geophysics; Flux; Meteorology; Photolysis; Pollutants physicochemistry study: properties, effects, reactions, transport and distribution; Pollution; Redox reactions
• ISSN: 1352-2310; 1873-2844
• DOI: 10.1016/S1352-2310(01)00107-8

The rate constant for Hg 0+ . OH, k Hg 0+ . OH =(2.4±0.3)×10 9 M −1 s −1 , in the aqueous phase was determined using a relative rate technique with methyl mercury as reference compound. The .OH initiated mercury reaction proceeds via the molecular Hg(I) radical which is oxidised to Hg(II) by dissolved O 2. The reaction can be of importance under certain atmospheric circumstances, such as when the aqueous phase capacity of forming OH radicals is significant and the gas phase concentration of ozone drops. The same end product, i.e. Hg(II) was observed from the photodegradation of methylmercury hydroxide. In this case, molecular Hg(I) radicals are again likely to be formed after photodegradation of the Hg–C bond with subsequent oxidation. A lifetime of 230 h of methylmercury at outdoor conditions was estimated due to this reaction. The action of .OH on methylmercury species also involves breaking of organometallic bonds and formation of Hg(II). Speciation of these reaction products from methylmercury is important for the estimation of biogeochemical cycling of mercury.