HR: 0800h
AN: B51A-0177 [Abstracts]
TI: Nitric Acid Phase Partitioning and Cycling in the New England Coastal Atmosphere
AU: * Fischer, E
EM: efischer@mountwashington.org
AF: Mount Washington Observatory, Research Department, North Conway, NH 03860
United States
AU: Keene, W
EM: wck@virginia.edu
AF: University of Virginia, Department of Environmental Sciences
, Charlottesville, VA 22904
United States
AU: Maben, J
EM: jrm@virginia.edu
AF: University of Virginia, Department of Environmental Sciences
, Charlottesville, VA 22904
United States
AU: Pszenny, A
EM: apszenny@mountwashington.org
AF: Mount Washington Observatory, Research Department, North Conway, NH 03860
United States
AU: Pszenny, A
EM: apszenny@mountwashington.org
AF: University of New Hampshire, Institute for the Study of Earth, Oceans, and Space
, Durham, NH 03824
United States
AU: Smith, A
EM: ams6t@virginia.edu
AF: University of Virginia, Department of Environmental Sciences
, Charlottesville, VA 22904
United States
AU: Talbot, R
EM: robert.talbot@unh.edu
AF: University of New Hampshire, Institute for the Study of Earth, Oceans, and Space
, Durham, NH 03824
United States
AB:
During summer 2004, soluble gases were continuously sampled over 2-hour intervals and size-resolved aerosols were sampled
over discrete daytime (~ 15 hr) or nighttime (~ 9 hr) intervals at Appledore Island, ME as part of the
International Consortium for Atmospheric Research on Transport and Transformations (ICARTT) field program. Particulate
NO3- and gaseous HNO3 concentrations were examined as a function of transport sector and dry deposition fluxes
were estimated. HNO3 concentrations varied widely on the time scale of hours; however, all sampling days were
characterized by a distinct minimum in the early morning. The daily peak normally occurred in the early afternoon, and was
followed by a secondary peak at about 2200. The maximum and median concentrations of HNO3, were 337 and 22.5 nmol
m-3 respectively. Aerosol NO3- exhibited a bimodal size distribution with a primary peak associated with
sea-salt Na+ at ~4 μm and a secondary sub-μm peak. The median NO3- concentrations of sub and
super-μm aerosol fractions were 3.3 and 7.7 nmol m-3 respectively.
HNO3 concentrations (median value = 57 nmol m-3) were measured during westerly flow regimes, while super-μm
aerosol peaked during southwesterly flow regimes. Although median total nitrate (HNO3 +
NO3-)concentrations were higher under westerly flow, higher median dry deposition rates for total nitrate were
calculated for southwesterly flow. Both westerly and southwesterly transport regimes carried polluted continental air to the
site, but sea-salt concentrations were a factor of 3 higher during southwesterly flow which shifted the phase partitioning
toward particulate NO3-. Consequently, under westerly flow, the calculated HNO3 deposition flux was ~3 times
greater than the associated aerosol NO3- flux, while for southwesterly flow, the fluxes from the two phases were
comparable. The median dry deposition fluxes for aerosol NO3- and volatile HNO3 were 5.6 and 8.2 μmol
m-2 d-1. Large particles dominated the aerosol dry deposition, because of both higher concentrations and
deposition velocities. This is consistent with previous work suggesting that the mixing of polluted continental and marine
air may enhance dry deposition of total nitrate to coastal ecosystems. Displacement of HCl from sea-salt aerosol via
incorporation of HNO3 helped to sustain high mixing ratios of HCl (up to 255 nmol m-3) and significant production
of atomic Cl via HCl + OH during the daytime, thereby altering the oxidant regime relative to the upwind continent.
DE: 0305 Aerosols and particles (0345, 4801, 4906)
DE: 0345 Pollution: urban and regional (0305, 0478, 4251)
DE: 0365 Troposphere: composition and chemistry
DE: 0368 Troposphere: constituent transport and chemistry
DE: 0469 Nitrogen cycling
SC: Biogeosciences [B]
MN: Fall Meeting 2005