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Food waste used as a resource can reduce climate and resource burdens in agrifood systems

Abstract

Global food loss and waste continues to increase despite efforts to reduce it. Food waste causes a disproportionally large carbon footprint and resource burdens, which require urgent action to transition away from a disposal-dominated linear system to a circular bioeconomy of recovery and reuse of valuable resources. Here, using data from field-based studies conducted under diverse conditions worldwide, we found collective evidence that composting, anaerobic digestion and repurposing food waste to animal feed (re-feed) result in emission reductions of about 1 tCO2e t−1 food waste recycled compared with landfill disposal. Emission mitigation capacity resulting from no landfill disposal in the United States, the European Union and China would average 39, 20 and 115 MtCO2e, which could offset 10%, 5% and 17% of the emissions from these large agricultural systems, respectively. In addition, re-feed could spare enormous amounts of land, water, agricultural fuel and fertilizer use. Our findings provide a benchmark for countries developing food waste management strategies for a circular agrifood system.

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Fig. 1: Global–regional distribution of studies selected through comprehensive literature review.
Fig. 2: Carbon footprint of food waste recycling treatment via AC, AD or re-feed compared with that of landfill disposal.
Fig. 3: Transforming existing food waste management schemes in the United States, the EU and China can substantially offset emissions from their agricultural systems.

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Data availability

The source data for the bootstrapping analyses used to compute the means and 95% CIs of the carbon footprints of the food waste treatments, landfill emissions and product metrics and for the impact analysis of the food waste management schemes of the United States, the EU and China are available on Zenodo at https://doi.org/10.5281/zenodo.14826061 (ref. 81). All other data that support the findings of this study are provided in the article. Source data are provided with this paper.

Code availability

The code used in the Stata statistical analysis is available on Zenodo at https://doi.org/10.5281/zenodo.14826061 (ref. 81).

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Acknowledgements

This work was supported by the National Key Research and Development Program of China (2022YFD1901501, 2021YFD1901001, H.Y.), the Major Science and Technology Project of Yunnan Province (202202AE090034, H.Y.), the Major Science and Technology Project of Shandong Province (2023TZXD088, 2024CXPT075, Z.C.) and Natural Science Foundation of Zhejiang Province, China (number LY22E080009, T.C.). This study also received funding from the following sources: University of Pennsylvania Global Engagement (Z.D.), Pennsylvania Department of Agriculture (Z.D.) and USDA-NIFA IDEAS Program (number 2022-68014-36664, project accession number 1028184; Z.D.).

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Z.D. and Z.C. designed and directed the study. Z.W., Y.Y., H.Z. and T.N. contributed to the literature search and data acquisition. T.C. and J.L. participated in project planning and discussion. D.S. conducted bootstrapping and Monte Carlo statistical simulations and analysis, wrote the description of the statistical methods, and reviewed the results. Z.D., Y.W., H.Y. and Z.C. collaborated on data management and organization and paper development. Z.D. and Y.W. wrote the paper, and G.C.S. contributed to the paper review, editing and revision. All authors contributed to the discussion of the study and development of the paper.

Corresponding authors

Correspondence to Zhenling Cui or Zhengxia Dou.

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Nature Food thanks Prajal Pradhan and the other, anonymous, reviewer(s) for their contribution to the peer review of this work.

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Extended data

Extended Data Fig. 1 Flow chart of literature search and selection processes for studies on food waste treatment via aerobic composting (AC), anaerobic digestion (AD), re-purposing to animal feed (Re-Feed), or landfill disposal, in terms of greenhouse gas (GHG) emissions and product for recycling-reuse.

Of 91 studies selected, 50 included two or more food waste treatment methods.

Extended Data Fig. 2 The system starts with food waste collection and coupled with transport, then followed by processing, and ends with the production of the final product.

Standardized system boundaries to cover food waste collection, transport, and processing through AC, AD, or Re-Feed.

Extended Data Table 1 Model-adjusted means and 95% CIs of carbon footprint for food waste treatment via composting (AC), anaerobic digestion (AD), and re-purposing to animal feed (Re-Feed), as well as food waste landfill
Extended Data Table 2 End-of-life food waste management schemes in the US, EU, China, and total greenhouse gas emissions
Extended Data Table 3 Emission mitigation capacity for US, EU, and China under a zero-landfill scenario (S1) and a zero-disposal scenario (S2)1
Extended Data Table 4 Model-adjusted means and 95% CIs of product metrics for 1 t food waste treated via aerobic composting (AC), anaerobic digestion (AD), or re-purposing to animal feed (Re-Feed)
Extended Data Table 5 Total amounts of compost, biogas (expressed as renewable energy), digestate, upcycled feed, and nitrogen (N) and phosphorus (P) contained in compost and digestate under zero-landfill scenario (S1) and zero-disposal scenario (S2)
Extended Data Table 6 Amounts of maize and soybeans substitution with upcycled feed produced from 1/3 of the food waste amounts allocated to Re-Feed under zero-landfill scenario (S1) and zero-disposal scenario (S2)
Extended Data Table 7 Protocol for systematic literature review of studies on greenhouse gas (GHG) emissions of food waste treatment via aerobic composting (AC), anaerobic digestion (AD), re-purposing to make animal feed (Re-Feed), or landfill disposal

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Wang, Y., Ying, H., Stefanovski, D. et al. Food waste used as a resource can reduce climate and resource burdens in agrifood systems. Nat Food 6, 478–490 (2025). https://doi.org/10.1038/s43016-025-01140-z

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