9. Mercury LU

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    Energy Technology & Innovation Initiative

    FACULTY OF ENGINEERING

    Mercury oxidation

    Alastair Clements

    13/06/2012

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    Outline

    Introduction to mercury

    Mercury oxidation

    Oxidation modelling

    Summary

    Further work

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    Mercury

    ToxicityMethyl mercury ([HgCH3]

    +) forms in the environment.Potent neurotoxin; RfD = 0.1-0.3g/kg per day.Bioaccumulates through the food web into lethal doses.

    Transport6-18 months atmospheric lifetime. Global distribution fromsource.

    CorrosionMercury forms amalgams with many metals, includingaluminium.

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    Mercury oxidation

    Elemental Hg thermodynamically favoured at hightemperatures.

    Hg is volatile, relatively inert and has low solubility.

    Oxidised at moderate temperatures by halides.

    Oxidised to HgCl2 or HgBr2. Mercuric halides are soluble and so can be captured.

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    Relative abundance of Cl

    0

    500

    1000

    1500

    2000

    2500

    3000

    3500

    4000

    4500

    Bulgaria

    Ukraine

    Australia

    USA

    Canada

    Japan

    China

    SouthAfrica

    UK

    Coalcontent(ppmw

    )

    ChlorineBromine

    [Vassilev et al. 2000][Spears and Zheng 1999]Alastair Clements Mercury oxidation 5/18

    http://www.sciencedirect.com/science/article/pii/S0016236199002367http://www.sciencedirect.com/science/article/pii/S0166516298000123http://www.sciencedirect.com/science/article/pii/S0166516298000123http://www.sciencedirect.com/science/article/pii/S0016236199002367
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    Correlation of Hg2+ and HCl

    0

    20

    40

    60

    80

    100

    120

    140

    160

    180

    0 500 1000 1500 2000 2500 3000 3500 4000

    HgE

    (g/dscm)/H

    gT

    (ppmw

    )

    Chlorine (ppmw)

    [EPA 2011]

    Alastair Clements Mercury oxidation 6/18

    http://www.epa.gov/ttn/atw/utility/utilitypg.htmlhttp://www.epa.gov/ttn/atw/utility/utilitypg.html
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    Oxidation pathways

    Gas-phase

    Focus of early work. Unable to model in all situations.

    Paricle-bound

    Activated carbon and fly ash. Influenced by O/S/halogen species.

    Surface-catalysed

    Uncoated surface effects observed. Speculative mechanisms.

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    Gas phase oxidation

    Widmer et al. mechanism:

    Hg + Cl + M HgCl + M (R1)

    Hg + Cl2 HgCl + Cl (R2)

    Hg + HCl HgCl + H (R3)

    Hg + HOCl

    HgCl + OH (R4)

    HgCl + Cl+ M HgCl2+ M (R5)

    HgCl + Cl2 HgCl2+ Cl (R6)

    HgCl + HCl HgCl2+ H (R7)

    HgCl + HOCl

    HgCl2+ OH (R8)

    ReactionR 1-R 4produce the unstable HgCl intermediate. OnlyR 1can proceed at an appreciable rate.

    ReactionsR 5-R 8complete mercury oxidation and occur muchfaster.

    [Widmer et al. 2000]

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    Oxidation levels

    0

    20

    40

    60

    80

    100

    HCl(1

    00ppm)

    HCl(4

    00ppm)

    HBr(2

    5ppm)

    HBr(2

    5ppm)

    +HCl(100ppm

    )

    HBr(2

    5ppm)

    +HCl(400ppm

    )

    HBr(5

    0ppm)

    HBr(5

    0ppm)

    +HCl(100ppm

    )

    HBr(5

    0ppm)

    +HCl(400ppm

    )

    HCl(1

    00ppm)

    HCl(4

    00ppm)

    HBr(2

    5ppm)

    HBr(5

    0ppm)

    Percentag

    e

    Hg

    oxidation

    Oxy-firingAir firing

    [Buitrago 2011]

    Alastair Clements Mercury oxidation 9/18

    http://content.lib.utah.edu/cgi-bin/showfile.exe?CISOROOT=/us-etd3&CISOPTR=465&CISOMODE=printhttp://content.lib.utah.edu/cgi-bin/showfile.exe?CISOROOT=/us-etd3&CISOPTR=465&CISOMODE=print
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    Chlorine modelling

    Leeds mercury-chlorine model:

    Reaction Ref. MethodHg + Cl + M HgCl + M Donohoue et al. PLP/PLIFHg + Cl2 HgCl + Cl Widmer et al. TST/ab initio

    Hg + HCl

    HgCl + H Wilcox TST/ab initioHg + HOCl HgCl + OH Wilcox TST/ab initioHgCl + Cl + M HgCl2+ M Niksa et al. Collision limitedHgCl + Cl2 HgCl2+ Cl Wilcox TST/ab initioHgCl + HCl HgCl2+ H Wilcox TST/ab initioHgCl + HOCl

    HgCl

    2+ OH Wilcox TST/ab initio

    [Gharabaghi et al. 2011]

    Alastair Clements Mercury oxidation 10/18

    http://www.sciencedirect.com/science/article/pii/S1540748910003408http://www.sciencedirect.com/science/article/pii/S1540748910003408
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    Chlorine modelling results

    0

    2

    4

    6

    8

    10

    0 100 200 300 400 500

    Percentage

    Hgo

    xidation

    HCl concentration (ppmv)

    Experimental 440K/s

    Experimental 220 K/sModel 440 K/sModel 220 K/s

    Experimental data from[Cauch 2008]

    Alastair Clements Mercury oxidation 11/18

    http://content.lib.utah.edu/cgi-bin/showfile.exe?CISOROOT=/us-etd2&CISOPTR=90425&CISOMODE=printhttp://content.lib.utah.edu/cgi-bin/showfile.exe?CISOROOT=/us-etd2&CISOPTR=90425&CISOMODE=print
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    Bromine modelling

    Leeds mercury-bromine model:

    Reaction Ref. MethodHg + Br + M HgBr + M Donohoue et al. PLP/PLIFHg + Br2 HgBr + Br Okano TST/ab initio

    Hg + HBr

    HgBr + H Okano TST/ab initioHg + HOBr HgBr + OH Niksa et al. Collision limitedHgBr + Br + M HgBr2+ M Goodsite et al. TST/ab initioHgBr + Br2 HgBr2+ Br Niksa et al. Collision limitedHgBr + HBr HgBr2+ H Okano TST/ab initioHgBr + HOBr HgBr

    2+ OH Niksa et al. Collision limited

    [Hughes et al. 2011]

    Alastair Clements Mercury oxidation 12/18

    http://www.sciencedirect.com/science/article/pii/B9780444537119500353http://www.sciencedirect.com/science/article/pii/B9780444537119500353
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    Bromine modelling results

    0

    20

    40

    60

    80

    100

    0 10 20 30 40 50

    Percentage

    Hgo

    xidation

    HBr concentration (ppmv)

    Experimental 440K/s

    Experimental 220 K/sModel 440 K/sModel 220 K/s

    Experimental data from[van Otten et al. 2011]

    Alastair Clements Mercury oxidation 13/18

    http://pubs.acs.org/doi/abs/10.1021/ef200840chttp://pubs.acs.org/doi/abs/10.1021/ef200840c
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    Summary

    Mercury oxidation chemistry has proven challenging formodellers.

    Existing gas-phase oxidation models have failed to bevalidated across datasets.

    Experimental data only covers the atomic recombinationreactions.

    Not all potential gas-phase pathways have been fullyinvestigated.

    Work has also started on identifying surface-catalysed andparticle-bound mechanisms.

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    Further work

    Continue to improve and validate current model.

    Measure reaction rates under flue gas temperatures. Using flash photolysis and adsorption spectroscopy.

    Analyse and integrate models for heterogeneous reactions.

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    References

    Buitrago, P. A. Gas-phase mercury oxidation: effects of bromine, chlorine and SO2under air firing and oxy-fuel conditions, experimental and modeling study TheUniversity of Utah, 2011Cauch, B. Experimental Investigation And Kinetic Modeling Of HomogeneousMercury Oxidation By Halogens The University of Utah, 2008Donohoue, D. L.; Bauer, D. & Hynes, A. J. Temperature and Pressure DependentRate Coefficients for the Reaction of Hg with Cl and the Reaction of Cl with Cl: A

    Pulsed Laser Photolysis-Pulsed Laser Induced Fluorescence Study The Journal of Physical Chemistry A, 2005, 109, 7732-7741Donohoue, D. L.; Bauer, D.; Cossairt, B. & Hynes, A. J. Temperature and PressureDependent Rate Coefficients for the Reaction of Hg with Br and the Reaction of Brwith Br: A Pulsed Laser Photolysis-Pulsed Laser Induced Fluorescence StudyTheJournal of Physical Chemistry A, 2006, 110, 6623-6632Donohoue, D. L. Kinetic Studies of the Oxidation Pathways of Gaseous ElementalMercury University of Miami, 2008Environmental Protection Agency,http://www.epa.gov/accessed 11/06/2012

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    http://www.epa.gov/http://www.epa.gov/
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    References

    Gharebaghi, M.; Hughes, K.; Porter, R.; Pourkashanian, M. & Williams, A. Mercuryspeciation in air-coal and oxy-coal combustion: A modelling approach Proceedings of the Combustion Institute, 2011, 33, 1779 - 1786Goodsite, M. E.; Plane, J. M. C. & Skov, H. A Theoretical Study of the Oxidation ofHg0 to HgBr2 in the Troposphere Environmental Science & Technology, 2004, 38,1772-1776Hughes, K. J.; Ma, L.; Porter, R. T. & Pourkashanian, M. E.N. Pistikopoulos, M. G.

    & Kokossis, A. (Eds.) Mercury Transformation Modelling with Bromine Addition inCoal Derived Flue Gases 21st European Symposium on Computer Aided ProcessEngineering, Elsevier, 2011, 29, 171 - 175Niksa, S.; Helble, J. & Fujiwara, N. Kinetic modeling of homogeneousmercury/oxidation: The importance of NO and H2O in predicting oxidation incoal-derived systems Environmental Science and Technology, 2001, 35, 3701-3706Niksa, S.; Padak, B.; Krishnakumar, B. & Naik, C. V. Process Chemistry of BrAddition to Utility Flue Gas for Hg Emissions Control Energy & Fuels, 2010, 24,1020-1029Okano, T. High Temperature Mercury Oxidation Kinetics via Bromine MechanismsWorcester Polytechnic Institute, 2009van Otten, B.; Buitrago, P. A.; Senior, C. L. & Silcox, G. D. Gas-Phase Oxidation ofMercury by Bromine and Chlorine in Flue Gas Energy & Fuels, 2011, 25, 3530-3536

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    References

    Spears, D. & Zheng, Y. Geochemistry and origin of elements in some UK coalsInternational Journal of Coal Geology, 1999, 38, 161 - 179Vassilev, S.; Eskenazy, G. & Vassileva, C. Contents, modes of occurrence and origin ofchlorine and bromine in coal Fuel, 2000, 79, 903 - 921Widmer, N. C.; West, J. & Cole, J. A. Proceedings of the Air & Waste ManagementAssociation Annual Conference, 2000Wilcox, J. A kinetic investigation of high-temperature mercury oxidation by chlorine

    Journal of Physical Chemistry A, 2009, 113, 6633-6639

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