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Indicator Facts

CBD Strategic Goal: B.Reduce the direct pressures on biodiversity and promote sustainable use

Aichi Biodiversity Target: 8. By 2020, pollution, including from excess nutrients, has been brought to levels that are not detrimental to ecosystem function and biodiversity

Headline Indicator: Trends in pressures from habitat conversion, pollution, invasive species, climate change, overexploitation and underlying drivers

Development Status: Partially developed

Key Indicator Partner:

 

Associate indicator partners: SCOPE and IGBP

Data Available: Global and regional time series, 1860 onwards

Development Status: Ready for global and regional use

 

Reason

Energy and food production have resulted in large increases of ammonia and nitrogen oxide emissions to the atmosphere on a global and regional basis, with subsequent increase in Nitrogen (N) deposition. There are now large regions of the world where average N deposition rates exceed 10 kg N/ha/yr, greater than an order of magnitude increase compared with natural rates. These rates are well in excess of the critical loads that have detrimental impacts on receiving ecosystems. Given the growing importance of the atmosphere in Nr distribution, it is critical to get a better understanding of the link between nitrogen deposition and biodiversity loss, hence the development of the ‘nitrogen deposition’ indicator.

Status
Ideally the Nitrogen Deposition Indicator (NDI) would be based on measured data of both wet and dry deposition of reactive nitrogen across the world. However, lack of available measurement data calls for a different approach. Based on emission information of the major nitrogen species, the nitrogen deposition is calculated using a modelling approach. Such an atmospheric model is able to calculate the physical transport, chemical transformations and the ultimate deposition of nitrogen to the world’s ecosystems. The NDI reflects both natural and anthropogenic nitrogen emissions and changes observed since 1860 are generally the influence of anthropogenic actions. Not only the temporal changes since 1860 can be determined by means of this calculation approach, but also the spatial distribution over the different regions of the world.

Another advantage of a calculation approach is the possibility of looking into the future, which however depends on the availability of adequate emission data. By doing so, possible future threats to the worlds ecosystems can be explored and abatement measures be evaluated.
Scale

The indicator is applicable at local, regional and national scales.

The indicator

The indicator is generally presented as maps of N deposition. Additional presentations integrate N deposition with maps of critical loads for ecosystems.

Estimated N deposition from global total N (NOy and NHx) emissions, totaling 105 Tg N y−1. The unit scale is kg N ha−1 y−1, modified from the original units (mg m–2 y–1)

Source: Galloway et al., 2008

How to interpret the indicator

Interpretation of the indicator is straightforward. The larger the deposition of nitrogen from the atmosphere, the greater the potential for negative impacts, including biodiversity losses on receiving ecosystems.

Future development

Future developments will occur on two fronts—improving our knowledge of nitrogen deposition to regions of the world, and improving our understanding of the links between nitrogen deposition and biodiversity loss.  Both of these topics were addressed at the Workshop on Nitrogen Deposition, Critical Loads and Biodiversity, held at 16-18th November, 2009, in Edinburgh, UK and addressed at the Fifth International Nitrogen Conference, in Delhi, India; December 2010.

National use
The NDI can be used on a global, regional, and national basis for a general understanding of nitrogen deposition patterns. For national use, model outputs more specifically focused on individual countries should be used as a supplementary tool for more definitive information. It is recommended that any modeling approach used should evaluate the separate nitrogen sources (provided the necessary emission data are available) like e.g. agriculture, industry, traffic, etc. In this way, intervention points can be assessed on higher spatial scales than would be possible with the global data, enabling an adequate evaluation of possible abatement measures.

For more information on producing national indicators of nitrogen deposition contact James Galloway, Albert Bleeker or Frank Dentener, associated with the International Nitrogen Initiative (jng@eservices.virginia.edu/a.bleeker@ecn.nl/frank.dentener@jrc.ec.europa.eu).
Indicator Publications
 TitleDescription
What controls Tropospheric Ozone? (2000)Journal Article: Lelieveld and Dentener, Journal of Geophysical Research, 3531-3551
Use of dynamic soil-vegetation models to assess impacts of nitrogen deposition on plant species composition and to estimate critical loadsJournal Article: de Vries et al., Ecological Applications, 20, 60 - 79.
Transformation of the nitrogen cycle: recent trends, questions and potential solutions (2008)Journal Article: Galloway et al.,Science 320, 889-892.
N deposition as a threat to the World’s protected areas under the Convention on Biological Diversity (2011)Journal Article: Bleeker et al., Environmental Pollution 159, 2280-2288
Historical (1850-2000) gridded anthropogenic and biomass burning emissions of reactive gases and aerosols: methodology and application (2010)Journal Article: Lamarque et al., Atmospheric Chemistry and Physics, 10, C922-C926
Global Assessment of Nitrogen Deposition Effects on Terrestrial Plant Diversity: a synthesis (2010)Journal Article: Bobbink et al., Ecological Applications, 20, 30 - 59.
2010 Indicator Factsheet


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