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Nitrogen processes

Nitrogen is essential to life on Earth. It is a component of all proteins, and it can be found in all living systems. Nitrogen compounds are present in organic materials, foods, fertilisers, explosives, some wastewaters, and poisons. Nitrogen is crucial to life, but in excess it can also be harmful to the environment.

While the nitrogen information below applies to the whole landscape, these web pages have a focus on the inputs, processes, stocks, outputs and management issues associated with aquatic/wetland systems.

Palustrine wetland Photo by Gary Cranitch © Queensland Museum

Quick facts

Nitrogen gas
constitutes 78.1 percent of Earth's air by volume[4] (oxygen is 21%). In its gaseous form, nitrogen is colourless, odourless and is generally considered as inert.

Nitrogen processes

The conceptual models were compiled by researchers in collaboration with a wide range of stakeholders from Natural Resource Management groups, universities and government agencies and based on available scientific information[1].

Click on elements of the model or select from the tabs below

The nitrogen cycle

The nitrogen cycle, in which atmospheric nitrogen is converted into different nitrogenous compounds, is one the most crucial natural processes to sustain living organisms. During the cycle, certain bacteria ‘fix’ atmospheric nitrogen into ammonia, which plants need in order to grow. Other bacteria convert the ammonia into amino acids and proteins. Animals eat the plants and consume the protein. Nitrogen compounds return to the soil through animal and plant waste. Bacteria convert the waste nitrogen back to nitrogen gas, which returns to the atmosphere.

In an effort to make crops grow faster, people use nitrogen in fertilisers. However, excessive use of those fertilisers, as well as urban stormwater and wastewater discharges, can adversely affect the environment and human health, as it can contribute to the pollution of groundwater and surface waters.

Nitrogen processes in the landscape

Excess nitrogen (N) is one of the most prevalent and serious pollutants affecting waterways. Agricultural, urban and industrial activities have increased the amount of reactive N globally by a factor of nine from pre-industrial times[2][5][1]. The N generated from land use and erosion in catchments may be transported by surface water runoff and groundwater flows to waterways and coastal and marine ecosystems, causing eutrophication and the degradation of these ecosystems[3].

As manufactured nitrogen production exceeds what is cycled naturally, the excess nitrogen in its different forms can harm natural ecosystems[7]. The amount and type of nitrogen and its effects, vary across ecosystems as it travels from its source to the sea[6].

Nitrogen is transported in water and can also be stored in sediments and plants, including algae. Algal blooms (both macroalgae and microalgae) and increased plant growth occur in areas with increased nutrients and high light availability.

Different parts of the landscape process dissolved and particulate nitrogen differently depending on the soils, vegetation, hydrology, and sources of nitrogen and carbon. Some land units and land uses contribute nitrogen to waterways, others, like wetlands, remove it.

  Click on the text highlighed in green to view the nitrogen process conceptual model pages hosted on WetlandInfo
  Text highlighted in grey indicates where nitrogen process conceptual models are not available on WetlandInfo

Additional information

Pages under this section


References

  1. ^ a b Adame, MF (2021), 'A conceptual model of nitrogen dynamics for the Great Barrier Reef catchments', Marine Pollution Bulletin, vol. In press.
  2. ^ Galloway, JN & Cowling, EB (2002), 'Reactive nitrogen and the world: 200 years of change', AMBIO: A Journal of the Human Environment. [online], vol. 31, no. 2, pp. 64-71. Available at: http://www.bioone.org/doi/abs/10.1579/0044-7447-31.2.64.
  3. ^ Galloway, JN, Aber, JD, Erisman, JW, Seitzinger, SP, Howarth, RW, Cowlilng, EB & Cosby, BJ (2003), 'The Nitrogen Cascade', BioScience. [online], vol. 53, no. 4, pp. 341-341. Available at: https://academic.oup.com/bioscience/article/53/4/341-356/250178.
  4. ^ Kotz, JC, Treichel, P, Townsend, JR & Treichel, DA (2019), Chemistry & chemical reactivity, p. 1187, Cengage Learning, Boston, MA.
  5. ^ Kulkarni, MV, Groffman, PM & Yavitt, JB (2008), 'Solving the global nitrogen problem: It's a gas!', Frontiers in Ecology and the Environment, vol. 6, no. 4, pp. 199-206.
  6. ^ Seitzinger, S, Harrison, JA, Bohlke, JK, Bouwman, AF, Lowrance, R, Peterson, B, Tobias, C & Vand, D (2006), 'Denitrification across landscapes and waterscapes: A synthesis', Ecological Applications, vol. 16, no. 6, pp. 2064-2090.
  7. ^ Verhoeven, JTA, Arheimer, B, Yin, C & Hefting, MM (2006), 'Regional and global concerns over wetlands and water quality', Trends in Ecology and Evolution, vol. 21, no. 2, pp. 96-103.

Last updated: 9 August 2021

This page should be cited as:

Department of Environment and Science, Queensland (2021) Nitrogen processes, WetlandInfo website, accessed 30 August 2021. Available at: https://wetlandinfo.des.qld.gov.au/wetlands/ecology/processes-systems/nitrogen-concept-model/

Queensland Government
WetlandInfo   —   Department of Environment and Science