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Dry deposition of reactive nitrogen to European ecosystems: a comparison of inferential models across the NitroEurope network

Flechard, C. R. (author)
Nemitz, E. (author)
UK Centre For Ecology & Hydrology (UKCEH)
Smith, R. I. (author)
UK Centre For Ecology & Hydrology (UKCEH)
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Fowler, D. (author)
UK Centre For Ecology & Hydrology (UKCEH)
Vermeulen, A. T. (author)
Stichting Energieonderzoek Centrum Nederland (ECN),Energy Research Centre of the Netherlands (ECN)
Bleeker, A. (author)
Stichting Energieonderzoek Centrum Nederland (ECN),Energy Research Centre of the Netherlands (ECN)
Erisman, J. W. (author)
Stichting Energieonderzoek Centrum Nederland (ECN),Energy Research Centre of the Netherlands (ECN)
Simpson, David, 1961 (author)
Chalmers tekniska högskola,Chalmers University of Technology
Zhang, L. (author)
Environment Canada
Tang, Y. S. (author)
UK Centre For Ecology & Hydrology (UKCEH)
Sutton, M. A. (author)
UK Centre For Ecology & Hydrology (UKCEH)
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 (creator_code:org_t)
2011-03-23
2011
English.
In: Atmospheric Chemistry and Physics. - : Copernicus GmbH. - 1680-7316 .- 1680-7324. ; 11:6, s. 2703-2728
  • Journal article (peer-reviewed)
Abstract Subject headings
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  • Inferential models have long been used to determine pollutant dry deposition to ecosystems from measurements of air concentrations and as part of national and regional atmospheric chemistry and transport models, and yet models still suffer very large uncertainties. An inferential network of 55 sites throughout Europe for atmospheric reactive nitrogen (N-r) was established in 2007, providing ambient concentrations of gaseous NH3, NO2, HNO3 and HONO and aerosol NH4+ and NO3- as part of the NitroEurope Integrated Project. Network results providing modelled inorganic Nr dry deposition to the 55 monitoring sites are presented, using four existing dry deposition routines, revealing inter-model differences and providing ensemble average deposition estimates. Dry deposition is generally largest over forests in regions with large ambient NH3 concentrations, exceeding 30-40 kg N ha(-1) yr(-1) over parts of the Netherlands and Belgium, while some remote forests in Scandinavia receive less than 2 kg N ha(-1) yr(-1). Turbulent Nr deposition to short vegetation ecosystems is generally smaller than to forests due to reduced turbulent exchange, but also because NH3 inputs to fertilised, agricultural systems are limited by the presence of a substantial NH3 source in the vegetation, leading to periods of emission as well as deposition. Differences between models reach a factor 2-3 and are often greater than differences between monitoring sites. For soluble Nr gases such as NH3 and HNO3, the non-stomatal pathways are responsible for most of the annual uptake over many surfaces, especially the non-agricultural land uses, but parameterisations of the sink strength vary considerably among models. For aerosol NH4+ and NO3-, discrepancies between theoretical models and field flux measurements lead to much uncertainty in dry deposition rates for fine particles (0.1-0.5 mu m). The validation of inferential models at the ecosystem scale is best achieved by comparison with direct long-term micrometeorological Nr flux measurements, but too few such datasets are available, especially for HNO3 and aerosol NH4+ and NO3-.

Subject headings

NATURVETENSKAP  -- Geovetenskap och miljövetenskap -- Meteorologi och atmosfärforskning (hsv//swe)
NATURAL SCIENCES  -- Earth and Related Environmental Sciences -- Meteorology and Atmospheric Sciences (hsv//eng)

Keyword

reduced nitrogen
stomatal
oxidized nitrogen
biosphere-atmosphere exchange
surface exchange
particle deposition
deposition
compensation point
bidirectional ammonia exchange
vegetative canopies
ozone
mixed coniferous forest

Publication and Content Type

art (subject category)
ref (subject category)

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