Journals / Atmospheric Pollution Research / 2017 / Cilt: 8 - Sayı: 4

A pilot study of different materials applied for active sampling of gaseous oxidized mercury in the atmospheric air

Pages
791–799
DOI
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AI Summary & Key Takeaways

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

Along with the above experimental results, some insights into the possible mechanism of interaction of ozone with mercury halides have been provided.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Samplers made with different materials were tested for the quantitative collection and recovery of mercury halides from the atmospheric air.
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Key Findings & Data:The tested adsorbent materials included zirconia (ZrO2), titania (TiO2), melted SiO2 (quartz wool) and potassium chloride (KCl).
💡
Conclusion & Impact:Along with the above experimental results, some insights into the possible mechanism of interaction of ozone with mercury halides have been provided.
🔬Design:Research Article
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Özet

Samplers made with different materials were tested for the quantitative collection and recovery of mercury halides from the atmospheric air. The tested adsorbent materials included zirconia (ZrO2), titania (TiO2), melted SiO2 (quartz wool) and potassium chloride (KCl). Different processes affecting the sampler efficiency were investigated specifically: breakthrough during sampling because of the surface passivation and loss of already collected mercury halides due to spontaneous reduction or due to the reaction with ozone. Reduction of mercury because of reaction with the atmospheric ozone appeared to be the major cause of the sample loss and it was inherent in all tested materials at a comparable extent. We hypothesized the zirconia layer covered on a ceramic substrate (patented) to be less sensitive to the ozone-caused reduction, inert to gaseous elemental mercury and completely insensitive to atmospheric humidity. In addition, zirconia samplers were highly resistant to heating and they could be used for multiple adsorption/desorption cycles avoiding degradation in the atmospheric air. Key results of the zirconia sampler tests with mercury halides were: the collection efficiency of >98%; reduction with 50 ppb ozone in the first 4 min of exposition to the atmospheric air e 6% ±1%; spontaneous reduction at 50 C in the first 4 min after spiking e <0.6%. Along with the above experimental results, some insights into the possible mechanism of interaction of ozone with mercury halides have been provided.

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Cite This Article

URBA, A., Valiulis, D., Sarlauskas, J., Kvietkus, K., Sakalys, J., Selskis, A. (2017). A pilot study of different materials applied for active sampling of gaseous oxidized mercury in the atmospheric air. Atmospheric Pollution Research, Cilt: 8 - Sayı: 4, 791–799. https://ajindex.com/articles/351572

References (11)

  1. Ambrose, J.L., Lyman, S.N., Huang, J., Gustin, M.S., Jaffe, D.A., 2013. Fast time resolution oxidized mercury measurements during the reno atmospheric mercury intercomparison experiment (RAMIX). Environ. Sci. Technol. 47 (13), 7285-7294.
  2. Brennan, J.K., Thomson, K.T., Gubbins, K.E., 2002. Adsorption of water in activated carbons: effects of pore blocking and connectivity. Langmuir 18 (14), 5438-5447.
  3. Carrico, C.M., Petters, M.D., Kreidenweis, S.M., Sullivan, A.P., McMeeking, G.R., Levin, E.J.T., Engling, G., Malm, W.C., Collett Jr., J.L., 2010. Water uptake and chemical composition of fresh aerosols generated in open burning of biomass. Atmos. Chem. Phys. 10, 5165-5178.
  4. Choi, H.D., Holsen, T.M., Hopke, P.K., 2008. Atmospheric mercury (Hg) in the adirondacks: concentrations and sources. Environ. Sci. Technol. 42 (15), 5644-5653.
  5. Engle, M.A.,Gustin, M.S., Lindberg,S.E., Gertler, A.W.,Ariya, P.A., 2005. The influence of ozone on atmospheric emissions of gaseous elemental mercury and reactive gaseous mercury from substrates. Atmos. Environ. 39 (2005), 7506-7517.
  6. Gustin, M.S., Huang, J.Y., Miller, M.B., Peterson,C., Jaffe, D.A., Ambrose,J., Finley, B.D., Lyman, S.N., Call, K., Talbot, R., Feddersen, D., Mao, H., Lindberg, S.E., 2013. Do we understand what the mercury speciation instruments are actually measuring? Results of RAMIX. Environ. Sci. Technol. 2013 (47), 7295-7306.
  7. Gustin, M.S., Amos, H.M., Huang, J., Miller, M.B., Heidecorn, K., 2015. Measuring andmodeling mercury in the atmosphere: a critical review. Atmos. Chem. Phys. 2015 (15), 5697-5713.
  8. Huang, J., Miller, M.B., Weiss-Penzias, P., Gustin, M.S., 2013a. Comparison of gaseous oxidized Hg measured by KCl-coated denuders, and nylon and cation exchange membranes. Environ. Sci. Technol. 47 (13), 7307-7316.
  9. Huang, L., Bui, N.-N., Meyering, M.T., Hamlin, T.J., McCutcheon, J.R., 2013. 2013b. Novel hydrophilic nylon 6,6 microfiltration membrane supported thin film composite membranes for engineered osmosis. J. Membr. Sci. 437, 141-149.
  10. Huang, J., Gustin, M.S., 2015. Uncertainties of gaseous oxidized mercury measurements using KCl-coated denuders. Cation-exchange membranes, and nylon membranes: humidity influences. Environ. Sci. Technol. 49 (10), 6102-6108.
  11. Huang, J., Miller, M.B., Edgerton, E., Gustin, M.S., 2015. Use of criteria pollutants, active and passive mercury sampling, and receptor modeling to understand the chemical forms of gaseous oxidized mercury in Florida. Atmos. Chem. Phys.15 (8), 12069-12105. Jo