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
Access Nature and 54 other Nature Portfolio journals
Get Nature+, our best-value online-access subscription
$29.99 / 30 days
cancel any time
Subscribe to this journal
Receive 12 digital issues and online access to articles
$119.00 per year
only $9.92 per issue
Buy this article
- Purchase on Springer Link
- Instant access to full article PDF
Prices may be subject to local taxes which are calculated during checkout
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
UN World Population Prospects 2019 Highlights (Department of Economic and Social Affairs Population Division, 2022).
Elser, J. & Bennett, E. Phosphorus cycle: a broken biogeochemical cycle. Nature 478, 29–31 (2011).
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).
Strokal, M. et al. Alarming nutrient pollution of Chinese rivers as a result of agricultural transitions. Environ. Res. Lett. 11, 024014 (2016).
Rockström, J. et al. A safe operating space for humanity. Nature 461, 472–475 (2009).
Steffen, W. et al. Sustainability. Planetary boundaries: guiding human development on a changing planet. Science 347, 1259855 (2015).
Springmann, M. et al. Options for keeping the food system within environmental limits. Nature 562, 519–525 (2018).
Childers, D. L. et al. Sustainability challenges of phosphorus and food: solutions from closing the human phosphorus cycle. BioScience 61, 117–124 (2011).
Powers, S. M. et al. Global opportunities to increase agricultural independence through phosphorus recycling. Earth’s Future 7, 370–383 (2019).
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).
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).
Nesme, T., Metson, G. S. & Bennett, E. M. Global phosphorus flows through agricultural trade. Glob. Environ. Change 50, 133–141 (2018).
Wang, Z. et al. International trade reduces global phosphorus demand but intensifies the imbalance in local consumption. Sci. Total Environ. 830, 154484 (2022).
Lun, F. et al. Influences of international agricultural trade on the global phosphorus cycle and its associated issues. Glob. Environ. Change 69, 102282 (2021).
Yang, H. et al. Improving the imbalanced global supply chain of phosphorus fertilizers. Earth’s Future 7, 638–651 (2019).
D’Odorico, P. et al. Feeding humanity through global food trade. Earth’s Future 2, 458–469 (2014).
Fertilizers by Nutrient (FAO, 2022); http://www.fao.org/faostat/en/#data/RFN
Zou, T., Zhang, X. & Davidson, E. A. Global trends of cropland phosphorus use and sustainability challenges. Nature 611, 81–87 (2022).
Roberts, T. L. & Johnston, A. E. Phosphorus use efficiency and management in agriculture. Resour. Conserv. Recycl. 105, 275–281 (2015).
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).
Barbieri, P. et al. Food system resilience to phosphorus shortages on a telecoupled planet. Nat. Sustain. 5, 114–122 (2022).
Xu, Z. et al. Impacts of international trade on global sustainable development. Nat. Sustain. 3, 964–971 (2020).
Mogollón, J. M. et al. More efficient phosphorus use can avoid cropland expansion. Nat. Food 2, 509–518 (2021).
Sun, J. et al. Importing food damages domestic environment: evidence from global soybean trade. Proc. Natl Acad. Sci. USA 115, 5415–5419 (2018).
Wood, S. A. et al. Trade and the equitability of global food nutrient distribution. Nat. Sustain. 1, 34–37 (2018).
Ockenden, M. C. et al. Major agricultural changes required to mitigate phosphorus losses under climate change. Nat. Commun. 8, 161 (2017).
Lassaletta, L. et al. Food and feed trade as a driver in the global nitrogen cycle: 50-year trends. Biogeochemistry 118, 225–241 (2014).
Bai, Z. et al. China’s livestock transition: driving forces, impacts, and consequences. Sci. Adv. 4, eaar8534 (2018).
European Environment Agency Air Quality Standards (EEA, 2021); https://www.eea.europa.eu/themes/air/air-quality-concentrations/air-quality-standards
Schipanski, M. E. & Bennett, E. M. The influence of agricultural trade and livestock production on the global phosphorus cycle. Ecosystems 15, 256–268 (2012).
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).
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).
Alewell, C. et al. Global phosphorus shortage will be aggravated by soil erosion. Nat. Commun. 11, 4546 (2020).
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).
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).
Roy, E. D. et al. The phosphorus cost of agricultural intensification in the tropics. Nat. Plants 2, 16043 (2016).
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).
Tonini, D., Saveyn, H. G. M. & Huygens, D. Environmental and health co-benefits for advanced phosphorus recovery. Nat. Sustain. 2, 1051–1061 (2019).
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).
Neumann, K. et al. The yield gap of global grain production: a spatial analysis. Agric. Syst. 103, 316–326 (2010).
Haygarth, P. M. & Rufino, M. C. Local solutions to global phosphorus imbalances. Nat. Food 2, 459–460 (2021).
Xiong, W. et al. Increased ranking change in wheat breeding under climate change. Nat. Plants 7, 1207–1212 (2021).
Withers, P. J. A. et al. Transitions to sustainable management of phosphorus in Brazilian agriculture. Sci. Rep. 8, 2537 (2018).
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).
Li, B. et al. Network evolution and risk assessment of the global phosphorus trade. Sci. Total Environ. 860, 160433 (2023).
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).
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).
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).
Yao, G. et al. The increasing global environmental consequences of a weakening US–China crop trade relationship. Nat. Food 2, 578–586 (2021).
Freitas, F. L. et al. Potential increase of legal deforestation in Brazilian Amazon after Forest Act revision. Nat. Sustain. 1, 665–670 (2018).
Estoque, R. C. et al. The future of Southeast Asia’s forests. Nat. Commun. 10, 1829 (2019).
Jakob, M. et al. How trade policy can support the climate agenda. Science 376, 1401–1403 (2022).
Brander, M., Bernauer, T. & Huss, M. Trade policy announcements can increase price volatility in global food commodity markets. Nat. Food 4, 331–340 (2023).
Escobar, N. et al. Spatially-explicit footprints of agricultural commodities: mapping carbon emissions embodied in Brazilas soy exports. Glob. Environ. Change 62, 12067 (2020).
FoodData Central (USDA, 2020); https://fdc.nal.usda.gov/download-datasets.html
Glauber, J. W. China’s Accession to the WTO and its Impact on Global Agricultural Trade Vol. 2085 (International Food Policy Research Institute, 2021).
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
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
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).
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).
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.
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.
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).
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).
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).
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.
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.
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).
Supplementary information
Supplementary Information
Supplementary Methods, Figs. 1–10, Tables 1–4 and References.
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.
About this article
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
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1038/s43016-023-00822-w
This article is cited by
-
Opportunity to improve global phosphorus governance
Nature Food (2023)