Substantial nitrogen pollution embedded in international trade

  • An Erratum to this article was published on 01 March 2016

Abstract

Anthropogenic emissions of reactive nitrogen to the atmosphere and water bodies can damage human health and ecosystems1,2. As a measure of a nation’s contribution to this potential damage, a country’s nitrogen footprint has been defined as the quantity of reactive nitrogen emitted during the production, consumption and transportation of commodities consumed within that country, whether those commodities are produced domestically or internationally3. Here we use global emissions databases4,5, a global nitrogen cycle model6, and a global input–output database of domestic and international trade7,8 to calculate the nitrogen footprints for 188 countries as the sum of emissions of ammonia, nitrogen oxides and nitrous oxide to the atmosphere, and of nitrogen potentially exportable to water bodies. Per-capita footprints range from under 7 kg N yr−1 in some developing countries to over 100 kg N yr−1 in some wealthy nations. Consumption in China, India, the United States and Brazil is responsible for 46% of global emissions. Roughly a quarter of the global nitrogen footprint is from commodities that were traded across country borders. The main net exporters have significant agricultural, food and textile exports, and are often developing countries, whereas important net importers are almost exclusively developed economies. We conclude that substantial local nitrogen pollution is driven by demand from consumers in other countries.

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Figure 1: Embodied nitrogen emissions and per-capita nitrogen footprints for the top ten net exporters and importers.
Figure 2: International flows of embodied nitrogen emissions between countries of last sale and countries of consumption (top ten flows labelled).

Change history

  • 28 January 2016

    In the original version of the Letter originally published, the sentence comparing the authors' results to those of previous studies was missing a citation and it should have read: 'Our results of per-capita NFPs are higher than those presented in previous studies3,11,12,13—for example 62 kg cap−1 yr−1 for the USA compared to 41 kg cap−1 yr−1 (ref. 3)...'. This has been corrected in the online versions of the Letter.

References

  1. 1

    Erisman, J. W. et al. Consequences of human modification of the global nitrogen cycle. Phil. Trans. R. Soc. B 368, 20130116 (2013).

  2. 2

    Sutton, M. A. et al. Too much of a good thing. Nature 472, 159–161 (2011).

  3. 3

    Leach, A. M. et al. A nitrogen footprint model to help consumers understand their role in nitrogen losses to the environment. Environ. Dev. 1, 40–66 (2012).

  4. 4

    Database Collection of the Food and Agriculture Organization of the United Nations (FAOSTAT, 2015); http://faostat3.fao.org/home.

  5. 5

    Heffer, P. Assessment of Fertilizer Use by Crop at the Global Level 2010-2010/11 AgCom/13/39 (IFA, 2013).

  6. 6

    IPCC in 2006 IPCC Guidelines for National Greenhouse Gas Inventories Vol. 4 (eds Eggleston, H. S., Buendia, L., Miwa, K., Ngara, T. & Tanabe, K.) Ch. 10–11 (IGES, 2006).

  7. 7

    Lenzen, M., Moran, D., Kanemoto, K. & Geschke, A. Building EORA: a global multi-region input–output database at high country and sector resolution. Econ. Syst. Res. 25, 20–49 (2013).

  8. 8

    Lenzen, M., Kanemoto, K., Moran, D. & Geschke, A. Mapping the structure of the world economy. Environ. Sci. Technol. 46, 8374–8381 (2012).

  9. 9

    Galloway, J. N. et al. Nitrogen footprints: past, present and future. Environ. Res. Lett. 9, 115003 (2014).

  10. 10

    Bodirsky, B. L. et al. Reactive nitrogen requirements to feed the world in 2050 and potential to mitigate nitrogen pollution. Nature Commun. 5, 3858 (2014).

  11. 11

    Stevens, C. J., Leach, A. M., Dale, S. & Galloway, J. N. Personal nitrogen footprint tool for the United Kingdom. Environ. Sci. Process. Impacts 16, 1563–1569 (2014).

  12. 12

    Shibata, H., Cattaneo, L. R., Leach, A. M. & Galloway, J. N. First approach to the Japanese nitrogen footprint model to predict the loss of nitrogen to the environment. Environ. Res. Lett. 9, 115013 (2014).

  13. 13

    Pierer, M., Winiwarter, W., Leach, A. M. & Galloway, J. N. The nitrogen footprint of food products and general consumption patterns in Austria. Food Policy 49, 128–136 (2014).

  14. 14

    Lassaletta, L. et al. Food and feed trade as a driver in the global nitrogen cycle: 50-year trends. Biogeochemistry 118, 225–241 (2014).

  15. 15

    Billen, G., Lassaletta, L. & Garnier, J. A vast range of opportunities for feeding the world in 2050: trade-off between diet, N contamination and international trade. Environ. Res. Lett. 10, 025001 (2015).

  16. 16

    Galloway, J. N. et al. Transformation of the nitrogen cycle: recent trends, questions, and potential solutions. Science 320, 889–892 (2008).

  17. 17

    Burke, M., Oleson, K., McCullough, E. & Gaskell, J. A global model tracking water, nitrogen, and land inputs and virtual transfers from industrialized meat production and trade. Environ. Model. Assess. 14, 179–193 (2009).

  18. 18

    Lenzen, M. et al. International trade drives biodiversity threats in developing nations. Nature 486, 109–112 (2012).

  19. 19

    Peters, G. P., Davis, S. J. & Andrew, R. A synthesis of carbon in international trade. Biogeosciences 9, 3247–3276 (2012).

  20. 20

    Lenzen, M. et al. International trade of scarce water. Ecol. Econ. 94, 78–85 (2013).

  21. 21

    Alsamawi, A., Murray, J. & Lenzen, M. The employment footprints of nations: uncovering master–servant relationships. J. Ind. Ecol. 18, 59–70 (2014).

  22. 22

    Kanemoto, K., Moran, D., Lenzen, M. & Geschke, A. International trade undermines national emission reduction targets: new evidence from air pollution. Glob. Environ. Change 24, 52–59 (2014).

  23. 23

    Balazs, C., Morello-Frosch, R., Hubbard, A. & Ray, I. Social disparities in nitrate-contaminated drinking water in California’s San Joaquin Valley. Environ. Health Perspect. 119, 1272–1278 (2011).

  24. 24

    Sutton, M. A. et al. Global Overview of Nutrient Management (CEH, Edinburgh on behalf of the Global Partnership on Nutrient Management and the International Nitrogen Initiative, 2013).

  25. 25

    Erisman, J. W., Grennfelt, P. & Sutton, M. The European perspective on nitrogen emission and deposition. Environ. Int. 29, 311–325 (2003).

  26. 26

    Mandelker, D. R. Controlling nonpoint source water pollution: can it be done? Chic. Kent Law Rev. 65, 479–502 (1989).

  27. 27

    Galloway, J. N., Leach, A. M., Bleeker, A. & Erisman, J. W. A chronology of human understanding of the nitrogen cycle. Phil. Trans. R. Soc. B 368, 20130120 (2013).

  28. 28

    Hoekstra, A. Y. & Wiedmann, T. O. Humanity’s unsustainable environmental footprint. Science 344, 1114–1117 (2014).

  29. 29

    Kander, A., Jiborn, M., Moran, D. D. & Wiedmann, T. O. National greenhouse-gas accounting for effective climate policy on international trade. Nature Clim. Change 5, 431–435 (2015).

  30. 30

    O’Rourke, D. The science of sustainable supply chains. Science 344, 1124–1127 (2014).

  31. 31

    Leontief, W. Environmental repercussions and the economic structure: an input–output approach. Rev. Econ. Stat. 52, 262–271 (1970).

  32. 32

    Leontief, W. Input–Output Economics (Oxford Univ. Press, 1966).

  33. 33

    Feng, K., Chapagain, A., Suh, S., Pfister, S. & Hubacek, K. Comparison of bottom-up and top-down approaches to calculating the water footprints of nations. Econ. Syst. Res. 23, 371–385 (2011).

  34. 34

    Wiedmann, T. et al. A carbon footprint time series of the UK—results from a multi-region input–output model. Econ. Syst. Res. 22, 19–42 (2010).

  35. 35

    Environment at a Glance 2013: OECD Indicators (OECD, 2013).

  36. 36

    UNEP & WHRC Reactive Nitrogen in the Environment: Too Much or Too Little of a Good Thing (UNEP, 2007).

  37. 37

    Wu, R. S. Eutrophication, water borne pathogens and xenobiotic compounds: environmental risks and challenges. Mar. Pollut. Bull. 39, 11–22 (1999).

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Acknowledgements

We thank D. Moran (NTNU, Norway), A. Alsamawi and S. Juraszek (Univ. of Sydney) for technical assistance, J. Shindo (Yamanashi Univ.) and N. Kaneko (Yokohama National Univ.) for their discussions about nitrogen emissions, and C. Jarabak for help with collecting data. A.O. was supported by the Yokohama National University research grant. S.N. and A.O. were supported by the Environment Research and Technology Development Fund (S9 and S14) of the Ministry of the Environment, Japan. M.L., K.K., A.G. and A.M. were financially supported by the Australian Research Council through its Discovery Projects DP0985522 and DP130101293. K.K. was also financially supported by the Grant-in-Aid for Young Scientists (No. 15H05341).

Author information

A.O. and M.L. designed the study; A.O., S.N. and K.K. prepared the data; A.M., A.O. and A.G. conducted the analysis; A.M. and A.O. prepared the figures; A.O., M.L. and A.M. wrote the paper; A.O., M.L., A.M. and K.K. contributed to data interpretation and manuscript editing.

Correspondence to Manfred Lenzen.

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Oita, A., Malik, A., Kanemoto, K. et al. Substantial nitrogen pollution embedded in international trade. Nature Geosci 9, 111–115 (2016). https://doi.org/10.1038/ngeo2635

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