Skip to main content

Thank you for visiting nature.com. You are using a browser version with limited support for CSS. To obtain the best experience, we recommend you use a more up to date browser (or turn off compatibility mode in Internet Explorer). In the meantime, to ensure continued support, we are displaying the site without styles and JavaScript.

  • Article
  • Published:

Agricultural trade impacts global phosphorus use and partial productivity

Abstract

The spatio–temporal distribution, flow and end use of phosphorus (P) embedded in traded agricultural products are poorly understood. Here we use global trade matrices to analyse the partial factor productivity of P (output per unit of P input) for crop and livestock products in 200 countries and their cumulative contributions to the export or import of agricultural products over 1961–2019. In these six decades, the trade of agricultural P products has increased global partial factor productivity for crop and livestock production and has theoretically saved 67 Tg P in fertilizers and 1.6 Tg P in feed. However, trade is now at risk of contributing to wasteful use of P resources globally due to a decline in trade optimality, as agricultural products are increasingly exported from low to high partial factor productivity countries and due to P embedded in imported agricultural products mainly lost to the environment without recycling. Integrated crop–livestock production systems and P-recycling technologies can help.

This is a preview of subscription content, access via your institution

Access options

Buy this article

Prices may be subject to local taxes which are calculated during checkout

Fig. 1: P flow in agricultural product trade and use across regions.
Fig. 2: Annual changes for trade functionality and optimality.
Fig. 3: Changes in fertilizer-P productivity for traded countries.
Fig. 4: Factors of P fertilizer productivity and crop product trade.
Fig. 5: Theoretical savings or wastage of fertilizer- and feed-P.

Similar content being viewed by others

Data availability

All data needed to evaluate the conclusions of this study are available in the paper itself and/or the Supplementary Information file. Source data are provided with this paper.

Code availability

The custom algorithm used for this study is available in the Methods and the Supplementary Information.

References

  1. UN World Population Prospects 2019 Highlights (Department of Economic and Social Affairs Population Division, 2022).

  2. Elser, J. & Bennett, E. Phosphorus cycle: a broken biogeochemical cycle. Nature 478, 29–31 (2011).

    ADS  CAS  PubMed  Google Scholar 

  3. Schindler, D. W. et al. Eutrophication of lakes cannot be controlled by reducing nitrogen input: results of a 37-year whole-ecosystem experiment. Proc. Natl Acad. Sci. USA 105, 11254–11258 (2008).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  4. Strokal, M. et al. Alarming nutrient pollution of Chinese rivers as a result of agricultural transitions. Environ. Res. Lett. 11, 024014 (2016).

    ADS  Google Scholar 

  5. Rockström, J. et al. A safe operating space for humanity. Nature 461, 472–475 (2009).

    ADS  PubMed  Google Scholar 

  6. Steffen, W. et al. Sustainability. Planetary boundaries: guiding human development on a changing planet. Science 347, 1259855 (2015).

    PubMed  Google Scholar 

  7. Springmann, M. et al. Options for keeping the food system within environmental limits. Nature 562, 519–525 (2018).

    ADS  CAS  PubMed  Google Scholar 

  8. Childers, D. L. et al. Sustainability challenges of phosphorus and food: solutions from closing the human phosphorus cycle. BioScience 61, 117–124 (2011).

    Google Scholar 

  9. Powers, S. M. et al. Global opportunities to increase agricultural independence through phosphorus recycling. Earth’s Future 7, 370–383 (2019).

    ADS  Google Scholar 

  10. Schneider, K. D. et al. Options for improved phosphorus cycling and use in agriculture at the field and regional scales. J. Environ. Qual. 48, 1247–1264 (2019).

    CAS  PubMed  Google Scholar 

  11. Liu, L. et al. A higher water-soluble phosphorus supplement in pig diet improves the whole system phosphorus use efficiency. J. Clean. Prod. 272, 122586 (2020).

    CAS  Google Scholar 

  12. Nesme, T., Metson, G. S. & Bennett, E. M. Global phosphorus flows through agricultural trade. Glob. Environ. Change 50, 133–141 (2018).

    Google Scholar 

  13. Wang, Z. et al. International trade reduces global phosphorus demand but intensifies the imbalance in local consumption. Sci. Total Environ. 830, 154484 (2022).

    ADS  CAS  PubMed  Google Scholar 

  14. Lun, F. et al. Influences of international agricultural trade on the global phosphorus cycle and its associated issues. Glob. Environ. Change 69, 102282 (2021).

    Google Scholar 

  15. Yang, H. et al. Improving the imbalanced global supply chain of phosphorus fertilizers. Earth’s Future 7, 638–651 (2019).

    ADS  Google Scholar 

  16. D’Odorico, P. et al. Feeding humanity through global food trade. Earth’s Future 2, 458–469 (2014).

    ADS  Google Scholar 

  17. Fertilizers by Nutrient (FAO, 2022); http://www.fao.org/faostat/en/#data/RFN

  18. Zou, T., Zhang, X. & Davidson, E. A. Global trends of cropland phosphorus use and sustainability challenges. Nature 611, 81–87 (2022).

    ADS  CAS  PubMed  Google Scholar 

  19. Roberts, T. L. & Johnston, A. E. Phosphorus use efficiency and management in agriculture. Resour. Conserv. Recycl. 105, 275–281 (2015).

    Google Scholar 

  20. Fixen, P. et al. in Managing Water and Fertilizer for Sustainable Agricultural Intensification (eds Drechsel, P. et al.) Ch. 2 (IFA, IWMI, IPNI & IPI, 2015).

  21. Barbieri, P. et al. Food system resilience to phosphorus shortages on a telecoupled planet. Nat. Sustain. 5, 114–122 (2022).

    Google Scholar 

  22. Xu, Z. et al. Impacts of international trade on global sustainable development. Nat. Sustain. 3, 964–971 (2020).

    Google Scholar 

  23. Mogollón, J. M. et al. More efficient phosphorus use can avoid cropland expansion. Nat. Food 2, 509–518 (2021).

    PubMed  Google Scholar 

  24. Sun, J. et al. Importing food damages domestic environment: evidence from global soybean trade. Proc. Natl Acad. Sci. USA 115, 5415–5419 (2018).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  25. Wood, S. A. et al. Trade and the equitability of global food nutrient distribution. Nat. Sustain. 1, 34–37 (2018).

    Google Scholar 

  26. Ockenden, M. C. et al. Major agricultural changes required to mitigate phosphorus losses under climate change. Nat. Commun. 8, 161 (2017).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

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

    Google Scholar 

  28. Bai, Z. et al. China’s livestock transition: driving forces, impacts, and consequences. Sci. Adv. 4, eaar8534 (2018).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  29. European Environment Agency Air Quality Standards (EEA, 2021); https://www.eea.europa.eu/themes/air/air-quality-concentrations/air-quality-standards

  30. Schipanski, M. E. & Bennett, E. M. The influence of agricultural trade and livestock production on the global phosphorus cycle. Ecosystems 15, 256–268 (2012).

    CAS  Google Scholar 

  31. Lim, J. Y. et al. Agricultural nitrogen and phosphorus balances of Korea and Japan: highest nutrient surplus among OECD member countries. Environ. Pollut. 286, 117353 (2021).

    CAS  PubMed  Google Scholar 

  32. Bai, Z. et al. Food and feed trade has greatly impacted global land and nitrogen use efficiencies over 1961–2017. Nat. Food. 2, 780–791 (2021).

    PubMed  Google Scholar 

  33. Alewell, C. et al. Global phosphorus shortage will be aggravated by soil erosion. Nat. Commun. 11, 4546 (2020).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  34. Lun, F. et al. Global and regional phosphorus budgets in agricultural systems and their implications for phosphorus-use efficiency. Earth Syst. Sci. Data 10, 1–18 (2018).

    ADS  Google Scholar 

  35. Van der Velde, M. et al. African crop yield reductions due to increasingly unbalanced nitrogen and phosphorus consumption. Glob. Change Biol. 20, 1278–1288 (2014).

    ADS  Google Scholar 

  36. Roy, E. D. et al. The phosphorus cost of agricultural intensification in the tropics. Nat. Plants 2, 16043 (2016).

    CAS  PubMed  Google Scholar 

  37. Sattaria, S. Z. et al. Residual soil phosphorus as the missing piece in the global phosphorus crisis puzzle. Proc. Natl Acad. Sci. USA 109, 6348–6353 (2012).

    ADS  Google Scholar 

  38. Tonini, D., Saveyn, H. G. M. & Huygens, D. Environmental and health co-benefits for advanced phosphorus recovery. Nat. Sustain. 2, 1051–1061 (2019).

    Google Scholar 

  39. Bouwman, A. F. et al. Lessons from temporal and spatial patterns in global use of N and P fertilizer on cropland. Sci. Rep. 7, 40366 (2017).

    ADS  CAS  PubMed  PubMed Central  Google Scholar 

  40. Neumann, K. et al. The yield gap of global grain production: a spatial analysis. Agric. Syst. 103, 316–326 (2010).

    Google Scholar 

  41. Haygarth, P. M. & Rufino, M. C. Local solutions to global phosphorus imbalances. Nat. Food 2, 459–460 (2021).

    CAS  PubMed  Google Scholar 

  42. Xiong, W. et al. Increased ranking change in wheat breeding under climate change. Nat. Plants 7, 1207–1212 (2021).

    PubMed  Google Scholar 

  43. Withers, P. J. A. et al. Transitions to sustainable management of phosphorus in Brazilian agriculture. Sci. Rep. 8, 2537 (2018).

    ADS  PubMed  PubMed Central  Google Scholar 

  44. Wang, J. M. et al. Impacts of international food and feed trade on nitrogen balances and nitrogen use efficiencies of food systems. Sci. Total Environ. 838, 156151 (2022).

    ADS  CAS  PubMed  Google Scholar 

  45. Li, B. et al. Network evolution and risk assessment of the global phosphorus trade. Sci. Total Environ. 860, 160433 (2023).

    ADS  CAS  PubMed  Google Scholar 

  46. Jin, X. et al. Spatial planning needed to drastically reduce nitrogen and phosphorus surpluses in China’s agriculture. Environ. Sci. Technol. 54, 11894–11904 (2020).

    ADS  CAS  PubMed  Google Scholar 

  47. Gulan, A., Haavio, M. & Kilponen, J. Can large trade shocks cause crises? The case of the Finnish–Soviet trade collapse. J. Int. Econ. 131, 103480 (2021).

    Google Scholar 

  48. Alexander, P. et al. High energy and fertilizer prices are more damaging than food export curtailment from Ukraine and Russia for food prices, health and the environment. Nat. Food 4, 84–95 (2023).

    PubMed  Google Scholar 

  49. Yao, G. et al. The increasing global environmental consequences of a weakening US–China crop trade relationship. Nat. Food 2, 578–586 (2021).

    PubMed  Google Scholar 

  50. Freitas, F. L. et al. Potential increase of legal deforestation in Brazilian Amazon after Forest Act revision. Nat. Sustain. 1, 665–670 (2018).

    Google Scholar 

  51. Estoque, R. C. et al. The future of Southeast Asia’s forests. Nat. Commun. 10, 1829 (2019).

    ADS  PubMed  PubMed Central  Google Scholar 

  52. Jakob, M. et al. How trade policy can support the climate agenda. Science 376, 1401–1403 (2022).

    ADS  CAS  Google Scholar 

  53. Brander, M., Bernauer, T. & Huss, M. Trade policy announcements can increase price volatility in global food commodity markets. Nat. Food 4, 331–340 (2023).

    PubMed  PubMed Central  Google Scholar 

  54. Escobar, N. et al. Spatially-explicit footprints of agricultural commodities: mapping carbon emissions embodied in Brazilas soy exports. Glob. Environ. Change 62, 12067 (2020).

    Google Scholar 

  55. FoodData Central (USDA, 2020); https://fdc.nal.usda.gov/download-datasets.html

  56. Glauber, J. W. China’s Accession to the WTO and its Impact on Global Agricultural Trade Vol. 2085 (International Food Policy Research Institute, 2021).

Download references

Acknowledgements

This work was supported by National Natural Science Foundation of China (U20A2047, T2222016, 32102496, 41925004); the Youth Innovation Promotion Association, CAS (2019101); Key R&D Program of Hebei (21327507D); Hebei Dairy Cattle Innovation Team of Modern Agro-industry Technology Research System (HBCT2018120206) and China Postdoctoral Science Foundation (2021M693395).

Author information

Authors and Affiliations

Authors

Contributions

Z.B. and L.M. developed the original research question and designed the paper. L.L. performed the original data collection and data processing and prepared the figures and tables. All the authors wrote and revised the paper.

Corresponding authors

Correspondence to Zhaohai Bai or Lin Ma.

Ethics declarations

Competing interests

The authors declare no competing interests.

Peer review

Peer review information

Nature Food thanks Philip Haygarth, Johan Karlsson and the other, anonymous, reviewer(s) for their contribution to the peer review of this work.

Additional information

Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Extended data

Extended Data Fig. 1 Illustration of trade functionality and optimality.

Sensitivity of trade functionality and optimality (a), Crop productivity of exporting (b) and importing (c) countries in terms of calorie-corrected partial factor productivity of fertilizer-P, Livestock productivity of exporting (d) and importing (e) countries in terms of calorie-corrected partial factor productivity of feed from 1961 to 2019. Note: CPHE is the relative concentration of production in high-productivity countries applied to importing and exporting countries (CPHEim and CPHEex; dimensionless). CWPE is the CPHE weighted production efficacy applied to importing and exporting countries (CWPEim and CWPEex; M kcal kg-1 P). CPHE and CWPE were also defined as trade functionality and optimality in this study. The error bars represent the change of the maximum productivity at 98.5%, 99.0% and 99.5% contributions to the total traded products (n = 3).

Source data

Extended Data Fig. 2 Cumulative calorie-corrected productivity-trade distribution curves.

a-f, Crop productivity of exporting and importing countries in terms of calorie-corrected partial factor productivity of fertilizer-P. g-l, Livestock production in terms of calorie-corrected partial factor productivity. Note: CPHE is the relative concentration of production in high-productivity countries applied to importing and exporting countries (CPHEim and CPHEex, dimensionless). CWPE is the CPHE weighted production efficacy applied to importing and exporting countries (CWPEim and CWPEex, M kcal kg-1 P). The error bars represent the change of the maximum productivity at 98.5%, 99.0% and 99.5% contributions to the total traded products (n = 3).

Source data

Extended Data Fig. 3 Factors of feed-P productivity and livestock product trade.

The correlation between partial factor productivity of feed-P for livestock production (PFPlivestock) and impact factors (a), and the correlation between livestock products trade and impact factors (b) in the different countries for the two recent decades. Note: Exporting and importing countries are determined by the net livestock calorie trade per country during 2017 and 2019; Low and high PFPlivestock was determined by the PFPlivestock value of each country below or above global average PFPlivestock during 2017 and 2019. The left column represents contribution to export or import (in %); The colour and direction of arrows represent the changes of PFPlivestock and trade, determined by the slope of correlations and R2 values. The colour and size of circles represents the correlation of different factors with PFPlivestock and contribution to trade, respectively. The larger the values is, the larger the positive or negative effects are. The middle colour shaded squares represent the level of grazing intensity for different countries.

Source data

Extended Data Fig. 4 Changes in feed-P productivity for traded countries.

a, c, high-productivity exporting (a) and importing (c) countries, b, d, low-productivity exporting (b) and importing (d) countries from 1961 to 2019. Geographical distribution of PFPlivestock for high or low productivity exporting and importing countries in 2019 (e), Top 20 exporting and importing countries in 2019 (f). Note: The dotted line in Extended Data Fig. 4a, b, d represents a shift in trade state. Map layers were obtained from site: https://datacatalog.worldbank.org/search/dataset/0038272/World-Bank-Official-Boundaries.

Source data

Extended Data Fig. 5 Cumulative curves of calorie corrected productivity-trade and its impact.

Cumulative productivity-trade distribution curves of exporting and importing countries for crop calorie corrected partial total P productivity (a), changes of the ratio between CWPEex and CWPEim (b), the summed (c) and average (d) theoretical saving or wastage of total P through trade from 1961 to 2019. Note: CPHE is the relative concentration of production in high-productivity countries applied to importing and exporting countries (CPHEim and CPHEex, dimensionless). CWPE is the weighted production efficacy, applied to importing and exporting countries (CWPEim and CWPEex, M kcal kg-1 P). The error bars represent the change of maximum productivity at 99.0% ± 0.50% contributions to the total traded products (n = 3 for summed theoretical total P saving, n = 10 for average theoretical total P saving).

Source data

Extended Data Fig. 6 Current cumulative productivity-trade distribution curves.

Crop calorie corrected partial fertilizer-P productivity (a), partial total P productivity (b) of exporting and importing countries in 2017/19. Note: CPHE is the relative concentration of production in high-productivity countries applied to importing and exporting countries (CPHEim and CPHEex, dimensionless). CWPE is the weighted production efficacy, applied to importing and exporting countries (CWPEim and CWPEex, M kcal kg-1 P). The error bars represent the change of the maximum productivity at 98.5%, 99.0% and 99.5% contributions to the total traded products (n = 3).

Source data

Extended Data Fig. 7 Changes of cumulative productivity-trade distribution curves after used the advanced technology in 2017/19.

Treated human waste (a-c), poultry manure (d), pig manure (e) and all waste (f).Note: CPHE is the relative concentration of production in high-productivity countries applied to importing and exporting countries (CPHEim and CPHEex, dimensionless). CWPE is the weighted production efficacy, applied to importing and exporting countries (CWPEim and CWPEex, M kcal kg-1 P). The error bars represent the change of the maximum productivity at 98.5%, 99.0% and 99.5% contributions to the total traded products (n = 3).

Source data

Extended Data Fig. 8 Sensitivity of functionality, optimality, P resource saving.

a-c, crop trade functionality (a), optimality (b), and ratio of optimality (c) at 98.0% ± 1.0%, d-f, crop trade functionality (d), optimality (e), and ratio of optimality (f) at 97.0% ± 2.0%. g-i, livestock trade functionality (g), optimality (h), and ratio of optimality (i) at 98.0% ± 1.0%, j-l, livestock trade functionality (j), optimality (k), and ratio of optimality (l) at 97.0% ± 2.0%. m-o, fertilizer-P saving at 99.0 ± 0.5% (m), 98.0% ± 1.0% (n), 97.0% ± 2.0% (o). p-r, fertilizer-P saving at 99.0 ± 0.5% (p), 98.0% ± 1.0% (q), 97.0% ± 2.0% (r). Note: Shading in Extended Data Fig. 8 a-c, g-i, n, q shows 1.0% sensitivity. Shading in Extended Data Fig. 8 d-f, j-l, o, r shows 2.0% sensitivity. Shading in Extended Data Fig. 8m, p shows 0.5% sensitivity.

Source data

Extended Data Fig. 9 Cumulative protein-corrected productivity-trade distribution curves.

a-f, crop productivity of exporting and importing countries in terms of protein-corrected partial factor productivity of fertilizer-P. g-l, livestock production in terms of protein-corrected partial factor productivity.

Source data

Extended Data Fig. 10 Cumulative curves of protein-corrected productivity-trade and its impact.

Cumulative productivity-trade distribution curves of exporting and importing countries for protein-corrected fertilizer-P (a), feed-P (d), and total P productivity (g). The summed theoretical saving of fertilizer-P (b), feed-P (e), and total P (h), average theoretical saving of fertilizer-P (c), feed-P (f), and total P (i) through trade from 1961 to 2019. Note: The error bars represent the change of the maximum productivity at 98.5%, 99.0% and 99.5% contributions to the total traded products (n = 3 for CPHE, CWPE and summed theoretical saving; n = 10 for average theoretical saving).

Source data

Supplementary information

Supplementary Information

Supplementary Methods, Figs. 1–10, Tables 1–4 and References.

Reporting Summary

Source data

Source Data Fig. 1

Statistical source data.

Source Data Fig. 2

Statistical source data.

Source Data Fig. 3

Statistical source data.

Source Data Fig. 4

Statistical source data.

Source Data Fig. 5

Statistical source data.

Source Data Extended Data Fig. 1

Statistical source data.

Source Data Extended Data Fig. 2

Statistical source data.

Source Data Extended Data Fig. 3

Statistical source data.

Source Data Extended Data Fig. 4

Statistical source data.

Source Data Extended Data Fig. 5

Statistical source data.

Source Data Extended Data Fig. 6

Statistical source data.

Source Data Extended Data Fig. 7

Statistical source data.

Source Data Extended Data Fig. 8

Statistical source data.

Source Data Extended Data Fig. 9

Statistical source data.

Source Data Extended Data Fig. 10

Statistical source data.

Rights and permissions

Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Bai, Z., Liu, L., Obersteiner, M. et al. Agricultural trade impacts global phosphorus use and partial productivity. Nat Food 4, 762–773 (2023). https://doi.org/10.1038/s43016-023-00822-w

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1038/s43016-023-00822-w

This article is cited by

Search

Quick links

Nature Briefing Anthropocene

Sign up for the Nature Briefing: Anthropocene newsletter — what matters in anthropocene research, free to your inbox weekly.

Get the most important science stories of the day, free in your inbox. Sign up for Nature Briefing: Anthropocene