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Assessing critical load exceedances and ecosystem impacts of anthropogenic nitrogen and sulphur deposition at unmanaged forested catchments in Europe.
Forsius, Martin; Posch, Maximilian; Holmberg, Maria; Vuorenmaa, Jussi; Kleemola, Sirpa; Augustaitis, Algirdas; Beudert, Burkhard; Bochenek, Witold; Clarke, Nicholas; de Wit, Heleen A; Dirnböck, Thomas; Frey, Jane; Grandin, Ulf; Hakola, Hannele; Kobler, Johannes; Krám, Pavel; Lindroos, Antti-Jussi; Löfgren, Stefan; Pecka, Tomasz; Rönnback, Pernilla; Skotak, Krzysztof; Szpikowski, Józef; Ukonmaanaho, Liisa; Valinia, Salar; Vána, Milan.
Afiliación
  • Forsius M; Finnish Environment Institute (SYKE), Latokartanonkaari 11, FI-00790 Helsinki, Finland. Electronic address: martin.forsius@ymparisto.fi.
  • Posch M; International Institute for Applied Systems Analysis (IIASA), A-2361 Laxenburg, Austria.
  • Holmberg M; Finnish Environment Institute (SYKE), Latokartanonkaari 11, FI-00790 Helsinki, Finland.
  • Vuorenmaa J; Finnish Environment Institute (SYKE), Latokartanonkaari 11, FI-00790 Helsinki, Finland.
  • Kleemola S; Finnish Environment Institute (SYKE), Latokartanonkaari 11, FI-00790 Helsinki, Finland.
  • Augustaitis A; Forest Monitoring Laboratory, Vytautas Magnus University, Studentu 13, Kaunas distr. LT-53362, Lithuania.
  • Beudert B; Bavarian Forest National Park, Freyunger Str. 2, D-94481 Grafenau, Germany.
  • Bochenek W; Institute of Geography and Spatial Organization, Polish Academy of Sciences, Szymbark 430, 38-311 Szymbark, Poland.
  • Clarke N; Norwegian Institute of Bioeconomy Research, PO Box 115, NO-1431 Ås, Norway.
  • de Wit HA; Norwegian Institute for Water Research, Gaustadalléen 21, NO-0349 Oslo, Norway.
  • Dirnböck T; Environment Agency Austria, Department for Ecosystem Research and Data Information Management, Spittelauer Lände 5, A-1090 Vienna, Austria.
  • Frey J; Tartu University, Institute of Ecology and Earth Sciences, Vanemuise St. 46, EE-51014 Tartu, Estonia.
  • Grandin U; Swedish University of Agricultural Sciences, PO Box 7050, SE-75007 Uppsala, Sweden.
  • Hakola H; Finnish Meteorological Institute, PO Box 503, FI-00101 Helsinki, Finland.
  • Kobler J; Environment Agency Austria, Department for Ecosystem Research and Data Information Management, Spittelauer Lände 5, A-1090 Vienna, Austria.
  • Krám P; Czech Geological Survey, Department of Geochemistry, Klárov 3, CZ-118 21 Prague 1, Czech Republic.
  • Lindroos AJ; Natural Resources Institute Finland (Luke), Latokartanonkaari 9, FI-00790 Helsinki, Finland.
  • Löfgren S; Swedish University of Agricultural Sciences, PO Box 7050, SE-75007 Uppsala, Sweden.
  • Pecka T; Institute of Environmental Protection - National Research Institute, ul. Kolektorska 4, 01-692 Warsaw, Poland.
  • Rönnback P; Swedish University of Agricultural Sciences, PO Box 7050, SE-75007 Uppsala, Sweden.
  • Skotak K; Institute of Environmental Protection - National Research Institute, ul. Kolektorska 4, 01-692 Warsaw, Poland.
  • Szpikowski J; Adam Mickiewicz University in Poznan, Storkowo 32, 78-450 Grzmiaca, Poland.
  • Ukonmaanaho L; Natural Resources Institute Finland (Luke), Latokartanonkaari 9, FI-00790 Helsinki, Finland.
  • Valinia S; Swedish Environmental Protection Agency, Climate Department- Air Unit, SE-106 48 Stockholm, Sweden.
  • Vána M; Czech Hydrometeorological Institute, Observatory Kosetice, CZ-394 22 Kosetice, Czech Republic.
Sci Total Environ ; 753: 141791, 2021 Jan 20.
Article en En | MEDLINE | ID: mdl-32890870
ABSTRACT
Anthropogenic emissions of nitrogen (N) and sulphur (S) compounds and their long-range transport have caused widespread negative impacts on different ecosystems. Critical loads (CLs) are deposition thresholds used to describe the sensitivity of ecosystems to atmospheric deposition. The CL methodology has been a key science-based tool for assessing the environmental consequences of air pollution. We computed CLs for eutrophication and acidification using a European long-term dataset of intensively studied forested ecosystem sites (n = 17) in northern and central Europe. The sites belong to the ICP IM and eLTER networks. The link between the site-specific calculations and time-series of CL exceedances and measured site data was evaluated using long-term measurements (1990-2017) for bulk deposition, throughfall and runoff water chemistry. Novel techniques for presenting exceedances of CLs and their temporal development were also developed. Concentrations and fluxes of sulphate, total inorganic nitrogen (TIN) and acidity in deposition substantially decreased at the sites. Decreases in S deposition resulted in statistically significant decreased concentrations and fluxes of sulphate in runoff and decreasing trends of TIN in runoff were more common than increasing trends. The temporal developments of the exceedance of the CLs indicated the more effective reductions of S deposition compared to N at the sites. There was a relation between calculated exceedance of the CLs and measured runoff water concentrations and fluxes, and most sites with higher CL exceedances showed larger decreases in both TIN and H+ concentrations and fluxes. Sites with higher cumulative exceedance of eutrophication CLs (averaged over 3 and 30 years) generally showed higher TIN concentrations in runoff. The results provided evidence on the link between CL exceedances and empirical impacts, increasing confidence in the methodology used for the European-scale CL calculations. The results also confirm that emission abatement actions are having their intended effects on CL exceedances and ecosystem impacts.
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Texto completo: 1 Bases de datos: MEDLINE Idioma: En Revista: Sci Total Environ Año: 2021 Tipo del documento: Article

Texto completo: 1 Bases de datos: MEDLINE Idioma: En Revista: Sci Total Environ Año: 2021 Tipo del documento: Article