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https://doi.org/10.1038/s41467-026-69018-7
Received: 7 October 2025
Accepted: 21 January 2026
Cite this article as: Liao, X., Li, Y.,
Wang, J.
et al. Governing black soils
for food and climate security.
Nat
Commun (2026). https://doi.org/
10.1038/s41467-026-69018-7
Xiaoyong Liao, You Li, Jieyong Wang, Jinwei Dong, Qixing Yao, Jing Li, Ruixing Hou,
Zehong Li, Yitao Zhang, Xiaoxu Jia & Guoyong Leng
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Governing black soils for food and climate security
Xiaoyong Liao
1*
, You Li
1
, Jieyong Wang
1
, Jinwei Dong
1
, Qixing Yao
1
, Jing Li
1
, Ruixing Hou
1
,
Zehong Li
1
, Yitao Zhang
1
, Xiaoxu Jia
1
, Guoyong Leng
1
1
Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences,
Beijing 100101, China.
*e-mail: liaoxy@igsnrr.ac.cn
Black soils feed the world yet remain undervalued in food and climate governance frameworks. A
policy package, including global monitoring as public infrastructure, co-designed and place-based
solutions based on tailored tools, planning that fits land and people, mobilizing alliance with
finance and force, and mainstreaming black soils in global pacts, can contribute to decline land
quality and stabilize yields where it matters most.
The black soils, characterized by a thick, dark-colored soil horizon, and rich organic matter content,
cover just 17 % of global cropland yet yield two-thirds of sunflower seed, half of millet, 42 % of
sugar beet, 30 % of wheat, and a quarter of potatoes while storing roughly 30 % of cropland carbon
1
.
Black soils constitute not only a critical global food production base (Fig. 1a), but also deliver key
ecosystem services, including regulatory functions (e.g., carbon sequestration, nutrient cycling)
and provisioning benefits (e.g., biodiversity maintenance, climate mitigation). As vital regulators
of socio-ecological systems, they sustain agricultural productivity while enhancing rural
livelihoods. However, intensified cultivation, driven by escalating food demand resulting from
population growth and dietary shifts, has triggered widespread degradation
2
.
The black soils are becoming poorer, thinner, harder, and dirtier. Over the past 70 years, intensive
tillage, residue removal, land clearing, and a warming climate have stripped 20–50 % of their
original soil-organic-carbon (SOC) stocks
1
and thinned topsoil from 60–80 cm in the 1950s to 20–
40 cm in China’s Songnen Plain in the 2020s
3
. Comparable losses haunt Iowa’s prairies, where
“conservation” tillage still costs an estimated US $3 billion in annual yield penalties
4
, and
Ukraine’s chernozems, where decades of monoculture have drained up to 22 % of soil organic
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matter while topsoil blows into the Dnipro River basin
1
.
Beyond surface erosion, modern
mechanization has introduced an invisible threat: subsoil compaction. In regions with long-term
monoculture and intensive machinery use, this persistent compaction impairs root elongation and
water infiltration
5
. Degradation is further compounded by climate change and other unsustainable
practices such as excessive agrochemical inputs (Fig. 1b).
Fig. 1 | Agricultural productivity and key parameters of the world's four major black soil regions.
a,
Contribution of each region to global production of key staple and oilseed crops. Values represent the percentage
of global output sourced from black-soil cropland within each region. Region A: Ukraine and European Russia;
B: Northeast China; C: United States and Canada; D: South America. b, Regional comparison of agricultural
inputs (fertilizer, irrigation, and pesticide), subsoil compaction susceptibility index (SCSI), and key soil
properties (bulk density, soil organic carbon, pH). Values are cropland-weighted means derived from publicly
available global datasets. We integrated multiple datasets to characterize cropland conditions across four major
black-soil regions. Cropland extent was derived from Historic Land Dynamics Assessment Plus (HILDA⁺), and
black-soil boundary were compiled from the USDA NRCS Global Soil Type Database (Ukraine/European Russia,
North America and South America) and China’s Second National Soil Survey (Northeast China). All layers were
rasterized, reprojected and resampled to the HILDA⁺ grid, then intersected to delineate cropland within each
black-soil region. Crop harvested area (SPAM v2.0, 2020) was used to compute total harvested area and
dominant crop shares. Agricultural inputs were summarized from global products: fertilizer (Global Crop
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Specific Fertilization dataset for 1961 to 2019), irrigation (GMIE, a global maximum irrigation extent and central
pivot irrigation system dataset), and pesticides (PEST-CHEMGRIDS). SCSI and SoilGrids 2.0 soil properties
were aggregated over cropland for each region. Detailed data sources and processing steps are provided in
Supplementary Note 1.
Soil degradation and climate change jointly threaten food security
6
, with the high stakes in carbon-
rich, highly productive black soil regions
1
. As soils lose organic carbon and experience intensified
erosion, their capacity to retain nutrients and water declines, directly undermining crop
productivity and yield stability
7
. In Northeast China, topsoil thinning due to erosion has been
linked to yield reductions of approximately 27%
8
, with every additional 1,000 t km⁻² yr⁻¹ of soil
loss corresponding to estimated declines of around 170 kg ha⁻¹ for maize and 44.6 kg ha⁻¹ for
soybean
9
. Notably, such degradation is not inevitable, as conservation tillage can improve soil
quality and increase maize yields by more than 15%
10
. Beyond on-farm impacts, the release of
CO₂ from soil carbon loss exacerbates climate warming
6
, while rising temperatures and altered
precipitation patterns further accelerate erosion and organic matter decomposition
11
. This self-
reinforcing feedback is projected to drive ongoing declines in soil organic carbon across global
black soil regions under future climate change
12
. Concurrently, climate extremes including
droughts and floods impose additional shocks on crop production
13
. Combined drought and
extreme heat have been shown to reduce both yields and harvested area, contributing to production
losses across 94% of U.S. counties and an estimated 7.6% decline in total maize production under
the warming scenarios
14
.
Black soils hold crucial significance in safeguarding food security and alleviating climate change.
Nevertheless, it has long been overlooked in mainstream international discourse on food and
climate issues, and this neglected is reflected in the lack of robust regulatory frameworks and
effective enforcement mechanisms. Only five of 166 Nationally Determined Contributions (NDCs)
even mentioned black soils
15
, while multilateral trade and biodiversity continue to treat them as an
afterthought.
The Food and Agriculture Organization of the United Nations (FAO) began addressing this gap
with the establishment of the International Network of Black Soils (INBS) in 2018 and the release
of its
Global Status of Black Soils
report in 2022. However, moving from assessment to action
requires a coherent framework that integrates real-time information with locally adapted
technology and equitable governance. Here we outline such a framework (Fig. 2), spanning global
monitoring, inclusive planning, tailored tools, a dedicated alliance, and mainstreaming in global
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pacts, and show how it can stabilize food security, rural livelihoods, and climate mitigation on the
world’s most productive soils.
Fig.2 | An integrated framework for black soils conservation.
The diagram visualizes a strategic pathway
linking science, policy, and practice. Foundational global monitoring informs the development of tailored Tools
and inclusive planning, which are synergized by a central alliance for action to drive mainstreaming in global
pacts. Global monitoring provides a high-precision knowledge graph of black soils, while inclusive planning and
tailored tools offer regional-scale and localized governance strategies. Alliance for Action synergizes these
efforts to drive the highest goal: Mainstreaming black soil targets into global governance. Conceived as an
overarching strategic guide, its effective implementation at national or regional levels must be tailored to specific
institutional, financial, and environmental settings. Phase 1, integration & demonstration (short-term: 1–3 years)
establishes core global black soil knowledge graph, launches select high-impact black soil demo hubs, and builds
stakeholder consensus to secure initial commitments. Phase 2, scaling & customization (medium-term: 4–6 years)
divides agricultural regions to enable all-for-one customization, develops place-based solutions that meet agro-
ecological demands while upholding the principle of equality, and constitutes the Global black soil protection
alliance (GBSPA) to consolidate commitments and coordinate scaling. Phase 3, mainstreaming & sustained
governance (long-term: 7+ years) mainstreams black soil targets into global carbon markets and trade agreements
and sustains conservation through permanent institutional support and innovative financing mechanisms.
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Abbreviations: UNEP, united nations environment programme; WB, the world bank; IPCC, intergovernmental
panel on climate change.
Global monitoring as public infrastructure
Black-soil stewardship today is a cartographer’s patchwork. Fewer than one-third of black-soil
regions have repeat SOC plots, and national inventories diverge in terms of sampling depths,
laboratory protocols, and reporting formats. The absence of interoperable data leaves agronomists
guessing where erosion bites hardest and policymakers blind to whether subsidies are slowing
carbon loss.
A two-tier architecture is proposed. At the top sits an
open-access Black Soil Knowledge Graph
stewarded by FAO and INBS. Built on FAIR (Findable, Accessible, Interoperable, Re-usable)
principles, the graph would fuse legacy soil surveys, high-frequency sensor feeds, multispectral
imagery, farm-record data, and peer-reviewed studies. A harmonized indicator suite, including
SOC-stock change, topsoil thickness, aggregate stability, erosion risk, and below-ground
biodiversity, would render trends comparable across borders and feed open-source modules for
carbon accounting, drought forecasting, and land-use simulation.
Ground truth comes from a Real-Time Monitoring Network operated by national and sub-national
agencies. China already streams hourly SOC-moisture readings from > 2,000 probes across
Heilongjiang Province; paired with Unmanned Aerial Vehicle imagery and smartphone uploads
from growers, these data feed regional dashboards that pinpoint hotspots for straw-return subsidies.
Europe’s LUCAS programme (Land Use/Cover Area frame statistical Survey), which tags soil
samples to 10-metre Sentinel-2 pixels, demonstrates how continental harmonization can refine
local policy. Scaling such capacity requires funding: a multilateral trust fund, seeded by Article 6
climate finance flows and the Global Environment Facility, should co-finance sensors, lab
upgrades, and technician training in low-income chernozem belts. With alerts from this backbone,
ministries can target payments to the most vulnerable hectares and verify outcomes; without it,
stewardship remains a matter of guesswork.
Co-designed and place-based solutions based on tailored tools
Biophysical fixes founder when they ignore social reality. On China’s Sanjiang Plain, variable-
rate fertilizer spread only after
trusted neighbors
demonstrated its ease-of-use
16
, revealing that
social proof outweighed cost–benefit spreadsheets. Comparable social dynamics appear in
Argentina’s Pampas, where the Argentina no-till farmers association promote conservation
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practices through field demonstrations, workshops, and technical exchanges
17
. Likewise, in
Kazakhstan’s steppe regions, where the shared use of farm machinery and transport vehicles
reduces per-unit costs of inputs and services
18
.
Technologies must also meet agro-ecological constraints. Multi-strain, bio-engineered straw-
decomposition agents reduce residue breakdown time by 75% and boost rice yields in cold
Northeast soils
19
. In drier steppe climates, they risk mineralizing scarce moisture, so a shallow-
incorporation or surface-mulch approach works better. AI-guided planters, trained on centimeter-
scale microtopography, allow Iowa growers to seed corn directly into previous-crop stubble,
preserving soil armor while maintaining high yields. Flexibility, modularity and local calibration
are therefore design imperatives.
Integrating advanced in-season crop yield prediction models is crucial for food security under
climate change. Recent advancements demonstrate the value of assimilating seasonal climate
forecasts and satellite-based observations for timely yield forecasting in Northeast China, enabling
predictions up to one month before harvest with an average bias of ~5%
20
. Such forecasts allow
farmers to proactively mitigate climate risks through adaptive practices like adjusted irrigation or
residue management, while assisting policymakers in setting trade tariffs, adjusting market prices,
and enhancing overall food security.
Equity is non-negotiable. FAO gender guidelines require sex-disaggregated metrics and safeguards
against bias in land or labor access
21
. Mechanization that overlooks women’s shorter credit
horizons or seasonal labor peaks can entrench inequalities. However, well-designed agricultural
technology can also serve as a powerful tool for promoting equity. For instance, smart agriculture
tools can lower entry barriers for women, who often excel in technical training, machinery
operation and data analysis. Participatory co-design, which engages women and marginalized
groups in testing prototypes and negotiate trade-offs, transforms them from passive adopters into
active co-innovators, directly addressing potential biases
22
. To institutionalize these principles,
FAO should issue
Inclusive Innovation Standards
, fund regional “Black-Soil Demo Hubs” with
explicit equity targets, and host an open-license digital toolbox. Governments can bundle these
tools with gender-responsive micro-loans to bridge credit gaps and outcome-based soil-health
payments that reward stewardship rather than acreage alone, thereby building a fairer system for
all land managers.
Planning that fits land and people
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High-resolution soil intelligence must mesh with tenure and power on the ground. SOC maps are
only as good as the planning regimes that use them. High-resolution chernozem layers fused with
cadastral boundaries helped Ukrainian councils adjust crop-rotation rules and re-establish
shelterbelts, cutting wind-erosion losses by 1.8 t ha⁻¹ yr⁻¹
23
. Where Ethiopian highland villages—
half the participants were women—co-drew contour terraces and fallow corridors, SOC loss fell
by a third, and grain yields rose 9 % within three seasons
24
.
China has gone further, enacting the world’s first dedicated Black Soil Conservation Law in 2022
and backing it with large—scale projects and annual white papers. China’s
All-for-One
Customisation
offers a template for multiscale integration
25
. Parcel-level soil surveys (1:5 000)
feed village land-use maps, which in turn inform county master plans aligned with provincial dual
objectives of food security and ecological conservation and provincial targets. The "whole-
territory customization" approach employs stratified interventions: At the county level,
management units are delineated by erosion sensitivity and SOC thresholds; at the village level,
site-specific packages. The system funnels straw-return subsidies, no-till machinery banks, and
erosion-control terraces to the thinnest soils, lifting SOC by 0.3 % yr⁻¹ while maintaining grain-
output goals
26
.
Exporting this model means translating and adapting it for localization, not transplanting it. FAO
can curate open-source workflows (data pipelines, governance protocols, and performance
dashboards) and broker South–South exchanges, allowing, for instance, Mongolian herder
associations or Brazilian Cerrado municipalities to adapt the approach to their tenure mosaics and
climate risks. Host countries should pilot inclusive planning cells anchored in local tenure law,
indigenous knowledge, and youth and women’s organizations, with
result-based payments
triggered by verified carbon gains or erosion cuts.
A key strength of this integrated framework is its ability to align global goals with local priorities.
The pursuit of soil carbon sequestration for climate mitigation, for instance, need not conflict with
local food sovereignty or economic development. Through inclusive, place-based planning and
tailored tools, conservation practices can be designed to generate multiple co-benefits. No-till
farming with residue return not only stores carbon but also enhances soil water retention and
lowers fertilizer needs, thereby simultaneously advancing climate, productivity, and farm-income
objectives. Iterative planning and monitoring cycles allow interventions to be adapted to local
agro-ecological and socio-economic conditions, transforming potential trade-offs into sustained
synergies.
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Mobilizing alliance with finance and force
Technical networks alone lack the muscle and money to move markets. The INBS convenes
webinars and issues white papers but has no mandate to mobilize finance, and the Global Soil
Partnership’s resolutions remain largely exhortatory. We therefore call for an FAO-hosted Global
Black Soil Protection Alliance (GBSPA), which would be a multi-stakeholder platform that fuses
science, finance, and diplomacy.
The Alliance’s first task is to finalize global indicators and report protocols, locking the monitoring
architecture into place. Its second task is to broker technology exchange: pairing Ukraine’s 30-cm
chernozem depth maps with Brazil’s advanced residue-management rigs or adapting China’s
customization dashboards to Kazakh steppe districts. The third pillar is finance. A dedicated
window blending Green Climate Fund grants, Global Environment Facility co-finance, and
concessional loans, and outcome-based payments could underwrite sensor grids, machinery banks,
and Black-Soil Academies in low-income regions. This blended finance mechanism is designed to
de-risk investment and mobilize additional private capital, establishing a sustainable funding
model that extends beyond public grants. Donor appetite exists: the global environment facility
approved a US$68 million soil-restoration package in 2024 that explicitly earmarks black-soil
landscapes
27
.
Governance must be inclusive. Seats on the Alliance steering committee should be reserved for
indigenous peoples, women farmers, and youth representatives, and every funded project should
report sex-disaggregated benefits. Embedding such safeguards prevents capture by large
agribusinesses and aligns with FAO’s voluntary guidelines on gender equality
21
.
Mainstreaming black soils in global pacts
Policy alignment unlocks scale. A recent stock-take found that only five NDCs mention black
soils
15
, and soils appear merely as a footnote in the Kunming–Montreal Global Biodiversity
Framework. Parties to the Paris Agreement could register black-soil projects under Article 6.2
cooperative approaches, opening a tradable stream of soil-based carbon credits. The biodiversity
“30 × 30” target could prioritize remnant prairie and steppe chernozems as twin carbon–
biodiversity hotspots, while World Trade Organization green-trade talks could fast-track tariff
reductions for “black-soil-friendly” commodities—grains certified as produced under residue
cover and reduced tillage.
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Moving from pledge to practice demands people. A regional Black Soil Academies is proposed,
building on FAO’s Soil Doctors but adding accredited diplomas that national ministries recognize
for credit access and career advancement. Each academy would blend modern soil science with
traditional ecological knowledge and gender-responsive extension. By establishing a pilot "black-
soil research institute", Heilongjiang has successfully promoted strip-till and residue-return
techniques and proven effective in retaining more young people in farming. South–South
scholarships—say, pairing Argentine agronomists with Ukrainian extension agents—can multiply
such results.
Outlook
Coordinating real-time data, inclusive technology, participatory planning, multilateral finance, and
capacity building transforms today’s scattered pilot projects into a coherent global campaign. A
monitoring backbone tells us where to act; locally calibrated tools and land-use plans direct how
to act; an Alliance secures money and diplomacy; and mainstreaming embeds black-soil targets in
the rules that govern trade, climate, and biodiversity.
The implementation of this framework will face several predictable challenges. These include
concerns over data sovereignty in global monitoring, political constraints to cross-border
technology transfer and the practical barriers to meaningful smallholder participation in alliance
governance. To address these, a federated data governance model can allow countries to retain
sovereignty while contributing to a shared knowledge graph. Technology exchange can be
facilitated through multilateral licensing agreements and open-source digital toolboxes to lower
access barriers. Moreover, the governance structure of the GBSPA should formally reserve seats
for smallholder and women farmer representatives, supported by targeted capacity-building
programs, to ensure equitable and inclusive decision-making.
By being implemented as a package and backed by sustained political will, this framework can
halt the erosion of the planet’s most productive soils, turning them from a silent casualty of modern
agriculture into a linchpin of food security, rural prosperity, and climate stability for decades to
come. Black soils are rare, non-renewable on human timescales, and irreplaceable in its ecosystem
services; protecting it is no longer optional but essential planetary insurance.
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Acknowledgement
The study was financially supported by the National Natural Science Foundation of China
(42225707) and the Strategic Priority Research Program of the Chinese Academy of Sciences (No.
XDA28130000). We also thank Dr. Yifeng Cui for his contributions to part of the data collection.
Author contributions
Conceptualization: X.L.; Writing
—
original draft: X.L., Y. L., J. D. Q. Y.; Writing
—
review &
editing: X.L., Y. L., J. W., J. D., Q. Y., J. L., R. H., Z. L., Y. Z., X. J., G. L.; Funding acquisition:
X.L.
Competing interests
The authors declare no competing interests.
Additional information
Correspondence
and requests for materials should be addressed to Xiaoyong Liao