Agricultural climate finance is expected to lower greenhouse gas (GHG) intensity while sustaining yields and reducing dietary exposure to toxic elements. Many protocols still reward a single metric despite shared soil biogeochemical controls, so gains in one outcome can displace risk to another [[1], [2]].
Alternate wetting and drying (AWD) irrigation in rice illustrates this coupling. AWD can cut methane emissions by introducing oxic periods that suppress methanogenesis [3]. Yet the same shift can raise soil redox potential above 200 mV, promoting cadmium desorption and increasing cadmium availability to plants. Field evidence reports grain cadmium increases of 158% to 322% with stronger drying [4]. If credits reward methane reduction alone, mitigation may increase toxic exposure in the same landscapes.
Similar nonlinearities occur for nitrogen and remediation. When nitrogen surplus exceeds about 120 kg N/ha, nitrous oxide losses rise sharply, eroding GHG reduction benefits from nitrogen-focused strategies [5]. Immobilizing metals through liming and related pH manipulation can suppress micronutrient availability and reduce yields by 8% to 15% [6].
We propose governance built around a locally calibrated soil operating window that sets acceptable ranges for GHG intensity and yield, together with safeguard thresholds for nitrogen balance, pH, redox proxy or water regime, soil organic carbon, and bioavailable contaminants. Three elements can operationalize this framework. First, standards specify multidimensional performance targets and require disclosure of nitrogen balance and contaminant risk alongside GHG claims. Second, payments are conditional on verified cobenefits, with credits discounted when safeguard thresholds are exceeded. Third, monitoring systems track operating window indicators using routine soil tests, nutrient accounts, and water regime sensors to support timely management adjustments. China demonstrates feasibility. In Hunan Province, integrated management across 180,000 ha reduced grain cadmium by 57% to 78% without a yield penalty by combining low cadmium cultivars, silicon-based amendments, and irrigation control within defined safe bounds [7]. Embedding these safeguards into agricultural carbon standards could better align climate finance with biogeochemical reality.
CRediT authorship contribution statement
Guoliang Wang: Writing – original draft, Investigation, Conceptualization. Siwen Cheng: Methodology, Investigation. Tian Li: Investigation, Conceptualization. Qixing Zhou: Writing – review & editing, Conceptualization.
Declaration of competing interest
The authors declare there are no known competing interests regarding the publication of this paper.
Acknowledgements
This work was finically supported by the National Natural Science Foundation of China (NSFC) as a NSFC-BRICS project (32461143206), the Ministry of Science and Technology of People’s Republic of China as a national key research and development program project (2023YFC3709001, 2019YFC1804104), the Ministry of Education of People’s Republic of China as a discipline innovation and intelligence introduction project (B17025).
References
- 1.Lehmann J., Bossio D.A., Kögel-Knabner I., Rillig M.C. The concept and future prospects of soil health. Nat. Rev. Earth Environ. 2020;1(10):544–553. doi: 10.1038/s43017-020-0080-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Zhang X., Xue W., Wang G., Liang J., Wang Q., Li Y., Shu W., Zhou Q. Biogeochemical coupling of C/Fe in oil-polluted wetlands associated with iron reduction. Commun. Earth Environ. 2025;6:77. [Google Scholar]
- 3.Linquist B.A., Anders M.M., Adviento-Borbe M.A., Chaney R.L., Nalley L.L., da Rosa E.F., et al. Reducing greenhouse gas emissions, water use, and grain arsenic levels in rice systems. Glob. Change Biol. 2015;21(1):407–417. doi: 10.1111/gcb.12701. [DOI] [PubMed] [Google Scholar]
- 4.Li C., Carrijo D.R., Nakayama Y., Linquist B.A., Green P.G., Parikh S.J. Impact of alternate wetting and drying irrigation on arsenic uptake and speciation in flooded rice systems. Agric. Ecosyst. Environ. 2019;272:188–198. [Google Scholar]
- 5.Chen X., Cui Z., Fan M., Vitousek P., Zhao M., Ma W., et al. Producing more grain with lower environmental costs. Nature. 2014;514(7523):486–489. doi: 10.1038/nature13609. [DOI] [PubMed] [Google Scholar]
- 6.Smith P., Poch R.M., Lobb D.A., Bhattacharyya R., Alloush G., Eudoxie G.D., et al. Status of the world's soils. Annu. Rev. Environ. Resour. 2024;49:73–104. [Google Scholar]
- 7.Li Y., Tao H., Cao H., Wan X., Liao X. Achieving synergistic benefits through integrated governance of cultivated cadmium contamination via multistakeholder collaboration. Nat. Commun. 2024;15(1):9817. doi: 10.1038/s41467-024-53626-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
