Atmospheric mercury speciation and mercury in snow over time at Alert, Canada

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Atmospheric mercury speciation and mercury in snow over time at Alert, Canada. / Steffen, A.; Bottenheim, Jan W.; Cole, Amanda S. et al.
In: Atmospheric Chemistry and Physics, Vol. 14, No. 5, 03.03.2014, p. 2219-2231.

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Steffen A, Bottenheim JW, Cole AS, Ebinghaus R, Lawson GS, Leaitch WR. Atmospheric mercury speciation and mercury in snow over time at Alert, Canada. Atmospheric Chemistry and Physics. 2014 Mar 3;14(5):2219-2231. doi: 10.5194/acp-14-2219-2014

Bibtex

@article{7cba32acc93349ada0f5839ecb30667d,
title = "Atmospheric mercury speciation and mercury in snow over time at Alert, Canada",
abstract = "Ten years of atmospheric mercury speciation data and 14 years of mercury in snow data from Alert, Nunavut, Canada, are examined. The speciation data, collected from 2002 to 2011, includes gaseous elemental mercury (GEM), particulate mercury (PHg) and reactive gaseous mercury (RGM). During the winter-spring period of atmospheric mercury depletion events (AMDEs), when GEM is close to being completely depleted from the air, the concentration of both PHg and RGM rise significantly. During this period, the median concentrations for PHg is 28.2 pgm-3 and RGM is 23.9 pgm-3, from March to June, in comparison to the annual median concentrations of 11.3 and 3.2 pgm-3 for PHg and RGM, respectively. In each of the ten years of sampling, the concentration of PHg increases steadily from January through March and is higher than the concentration of RGM. This pattern begins to change in April when the levels of PHg peak and RGM begin to increase. In May, the high PHg and low RGM concentration regime observed in the early spring undergoes a transition to a regime with higher RGM and much lower PHg concentrations. The higher RGM concentration continues into June. The transition is driven by the atmospheric conditions of air temperature and particle availability. Firstly, a high ratio of the concentrations of PHg to RGM is reported at low temperatures which suggests that oxidized gaseous mercury partitions to available particles to form PHg. Prior to the transition, the median air temperature is -24.8°C and after the transition the median air temperature is -5.8°C. Secondly, the high PHg concentrations occur in the spring when high particle concentrations are present. The high particle concentrations are principally due to Arctic haze and sea salts. In the snow, the concentrations of mercury peak in May for all years. Springtime deposition of total mercury to the snow at Alert peaks in May when atmospheric conditions favour higher levels of RGM. Therefore, the conditions in the atmosphere directly impact when the highest amount of mercury will be deposited to the snow during the Arctic spring.",
keywords = "Chemistry, air temperature, atmospheric chemistry, atmospheric deposition, concentration, mercury, snow, speciation",
author = "A. Steffen and Bottenheim, {Jan W.} and Cole, {Amanda S.} and Ralf Ebinghaus and Lawson, {Greg S.} and Leaitch, {W. Richard}",
year = "2014",
month = mar,
day = "3",
doi = "10.5194/acp-14-2219-2014",
language = "English",
volume = "14",
pages = "2219--2231",
journal = "Atmospheric Chemistry and Physics",
issn = "1680-7316",
publisher = "Copernicus Publications",
number = "5",

}

RIS

TY - JOUR

T1 - Atmospheric mercury speciation and mercury in snow over time at Alert, Canada

AU - Steffen, A.

AU - Bottenheim, Jan W.

AU - Cole, Amanda S.

AU - Ebinghaus, Ralf

AU - Lawson, Greg S.

AU - Leaitch, W. Richard

PY - 2014/3/3

Y1 - 2014/3/3

N2 - Ten years of atmospheric mercury speciation data and 14 years of mercury in snow data from Alert, Nunavut, Canada, are examined. The speciation data, collected from 2002 to 2011, includes gaseous elemental mercury (GEM), particulate mercury (PHg) and reactive gaseous mercury (RGM). During the winter-spring period of atmospheric mercury depletion events (AMDEs), when GEM is close to being completely depleted from the air, the concentration of both PHg and RGM rise significantly. During this period, the median concentrations for PHg is 28.2 pgm-3 and RGM is 23.9 pgm-3, from March to June, in comparison to the annual median concentrations of 11.3 and 3.2 pgm-3 for PHg and RGM, respectively. In each of the ten years of sampling, the concentration of PHg increases steadily from January through March and is higher than the concentration of RGM. This pattern begins to change in April when the levels of PHg peak and RGM begin to increase. In May, the high PHg and low RGM concentration regime observed in the early spring undergoes a transition to a regime with higher RGM and much lower PHg concentrations. The higher RGM concentration continues into June. The transition is driven by the atmospheric conditions of air temperature and particle availability. Firstly, a high ratio of the concentrations of PHg to RGM is reported at low temperatures which suggests that oxidized gaseous mercury partitions to available particles to form PHg. Prior to the transition, the median air temperature is -24.8°C and after the transition the median air temperature is -5.8°C. Secondly, the high PHg concentrations occur in the spring when high particle concentrations are present. The high particle concentrations are principally due to Arctic haze and sea salts. In the snow, the concentrations of mercury peak in May for all years. Springtime deposition of total mercury to the snow at Alert peaks in May when atmospheric conditions favour higher levels of RGM. Therefore, the conditions in the atmosphere directly impact when the highest amount of mercury will be deposited to the snow during the Arctic spring.

AB - Ten years of atmospheric mercury speciation data and 14 years of mercury in snow data from Alert, Nunavut, Canada, are examined. The speciation data, collected from 2002 to 2011, includes gaseous elemental mercury (GEM), particulate mercury (PHg) and reactive gaseous mercury (RGM). During the winter-spring period of atmospheric mercury depletion events (AMDEs), when GEM is close to being completely depleted from the air, the concentration of both PHg and RGM rise significantly. During this period, the median concentrations for PHg is 28.2 pgm-3 and RGM is 23.9 pgm-3, from March to June, in comparison to the annual median concentrations of 11.3 and 3.2 pgm-3 for PHg and RGM, respectively. In each of the ten years of sampling, the concentration of PHg increases steadily from January through March and is higher than the concentration of RGM. This pattern begins to change in April when the levels of PHg peak and RGM begin to increase. In May, the high PHg and low RGM concentration regime observed in the early spring undergoes a transition to a regime with higher RGM and much lower PHg concentrations. The higher RGM concentration continues into June. The transition is driven by the atmospheric conditions of air temperature and particle availability. Firstly, a high ratio of the concentrations of PHg to RGM is reported at low temperatures which suggests that oxidized gaseous mercury partitions to available particles to form PHg. Prior to the transition, the median air temperature is -24.8°C and after the transition the median air temperature is -5.8°C. Secondly, the high PHg concentrations occur in the spring when high particle concentrations are present. The high particle concentrations are principally due to Arctic haze and sea salts. In the snow, the concentrations of mercury peak in May for all years. Springtime deposition of total mercury to the snow at Alert peaks in May when atmospheric conditions favour higher levels of RGM. Therefore, the conditions in the atmosphere directly impact when the highest amount of mercury will be deposited to the snow during the Arctic spring.

KW - Chemistry

KW - air temperature

KW - atmospheric chemistry

KW - atmospheric deposition

KW - concentration

KW - mercury

KW - snow

KW - speciation

UR - http://www.scopus.com/inward/record.url?scp=84895818076&partnerID=8YFLogxK

UR - https://www.mendeley.com/catalogue/dbec5d12-ff42-34b2-87e4-4f2097df1c94/

U2 - 10.5194/acp-14-2219-2014

DO - 10.5194/acp-14-2219-2014

M3 - Journal articles

AN - SCOPUS:84895818076

VL - 14

SP - 2219

EP - 2231

JO - Atmospheric Chemistry and Physics

JF - Atmospheric Chemistry and Physics

SN - 1680-7316

IS - 5

ER -

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