Soil Erosion
Erosion is the wearing away of the land surface by water, wind, ice, gravity or other natural or anthropogenic agents that abrade, detach and remove soil particles from one point on the earth's surface, for deposition elsewhere. Four main forms are recognized: water, wind, harvest and tillage. (FAO, 2020).
Primary reference(s)
FAO, 2020. Global Symposium on Soil Erosion. Food and Agriculture Organization of the United Nations (FAO). Accessed 2 October 2024.
Annotations
Additional scientific description
Soil erosion is a slow-onset process that occurs naturally under all climatic conditions and on all continents but is significantly increased and accelerated by unsustainable or inappropriate human activities through intensive agriculture, deforestation, overgrazing and land use changes. The Status of the World's Soil Resources report identified soil erosion as one of the major global soil threats (FAO, 2015). Soil erosion rates are generally much higher than soil formation rates; as soil is a finite resource, its loss and degradation through erosion is not recoverable within a human lifespan (FAO, 2020).
Soil erosion decreases soil quality and functions, agricultural productivity, degrades ecosystem functions, amplifies hydrogeological risk such as landslides or floods, causes significant losses in biodiversity, damage to human infrastructure and, in severe cases, leads to displacement of human populations (FAO, 2020).
Soil erosion poses a major threat to global food security and to the achievement of the Sustainable Development Goals (SDGs) (UN, 2015) on ensuring the well-being of at least 3.2 billion people around the world (FAO, 2020).
Generally, four types of soil erosion are recognized: (1) water; consisting of rain drop or splash, sheet, rill, and gully; (2) wind; (3) harvest; and (4) tillage.
- Splash erosion is caused by raindrops falling onto the soil surfaces causing small particles to move. The detached particles may form a crust that is easily removed by rain or winds.
- Sheet erosion occurs when the thin upper portion of the soil is displaced due to surface runoff after heavy rain. During this process, nutrients and organic matter are lost. This type of soil erosion is gradual and often goes unnoticed until larger portions of soil are displaced through the development of rills or the evidence of exposed roots.
- Rills are shallow drainage channels that form as rainwater flows into depressions in the soil surface. Over time, depressions can widen during subsequent precipitation events, which, in turn, increase susceptibility to erosion.
- Gully erosion occurs when runoff flows strongly and is concentrated in one location. In many cases, gullies begin as a rill that transitions into small channels. As water picks up energy, gully slopes become steeper. This type of soil erosion is very visible and damaging. It often has a drastic effect on the productivity of the soil and can make the land unusable. Gullies can range from 2m to 10-15m in depth.
- Tillage erosion occurs in cultivated fields due to the movement of soil by cultivating the soil (e.g. ploughing). Tillage erosion is often denoted by thinner soils on the upper slopes of cultivated fields or a loss of soil downslope of field boundaries,
- Soil erosion due to crop harvesting generally occurs during harvesting of root crops such as potato, sugar beet, carrot or chicory roots. During the harvest, soil particles stick to the crops and are removed from the field.
Metrics and numeric limits
Approximately 7.5 million km2 (6.1% of the global land surface) exceeds a generic tolerable soil erosion threshold of 10 Mg ha/yr (Borrelli et al., 2022). South America shows the highest prediction of average soil erosion rate (22.0 Mg ha/yr) in 2019, followed by Africa (17.1 Mg ha/yr) and Asia (12.8 Mg ha/yr) (Borrelli et al., 2022). North America, Europe and Oceania show considerably lower predicted values, totalling 11.0, 2.6 and 2.7 Mg ha/yr, respectively (Borrelli et al., 2022). A total of 75 billion tons of fertile soil is removed every year from the global soilscape by erosion. As a result, precious soil resources, which should be preserved for future generations, are continuously reduced. Every year approximately 12 million ha of land are lost (FAO and IAEA, 2017).
Climate projections, for all global dynamics scenarios, indicate a trend moving towards a more vigorous hydrological cycle, which could increase global water erosion (+30 to +66%; Borrelli et al., 2020).
Key relevant UN convention / multilateral treaty
Food and Agriculture Organization of the United Nations (FAO) Global Soil Partnership (GSP) (FAO, 2012,
United Nations Convention to Combat Desertification (UNCCD, 1994).
Drivers
Soil erosion is significantly increased and accelerated by intensive agriculture, deforestation, overgrazing and improper land use changes.
Impacts
Loss of soil body, fertility loss, desertification, off-site effects (e.g., sedimentation, siltation and eutrophication of water ways or enhanced flooding). Disruption of soil carbon and nutrient cycling. Affects climate and water regulation.
Multi-hazard context
The figure below summarises common interactions between soil erosion and other hazards. This information should be used with caution and not be solely relied upon in Disaster Risk Management, particularly as some interactions may not have been included. Note that hazardous events occurring together or locally in space or time may not necessarily cause, amplify or be otherwise related to each other. Specific examples of multi-hazard context can be found in the ‘Hazard drivers’ and ‘Impacts’ sections above.
Multi-hazard diagram
Risk Management
With 95% of the food consumed globally comes from the soil, soil erosion mitigation through the application of sustainable soil management (SSM) is critical for protecting soil while ensuring a sustainable and food secure world (FAO, 2020).
Soil erosion can be reduced through a number of simple measures including maintaining a healthy, perennial plant cover, mulching (leaving crop residues on the soil surface), cover crops and crop rotation, reduced tillage, terraces on steep slopes and water bunds, contour ploughing, addition of wind breaks and/or shelter belts, and the use of buffer strips.
One of the key messages from the Assessment Report on Land Degradation and Restoration prepared by the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services is to eliminate perverse incentives that promote degradation and to devise positive incentives that reward the adoption of sustainable land management practices in order to avoid, reduce and reverse land degradation (IPBES, 2018).
Monitoring
The section and the table below offer an overview of monitoring soil erosion. This information can be used for forecasting within a national early warning system (EWS). Since EWS capacities and processes differ across countries, the most current and specific information regarding EWS should be obtained from the appropriate national or regional agency/authority responsible for disaster management.
| Which institution(s) produce(s) Disaster Risk Data/Information? | Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services. GSP FAO |
| How is the Hazard Observed/Monitored/Forecast? | Measurement of the land surface; mass flux of a river or section |
References
Borrelli, P., Ballabio, C., Yang, J. E., Robinson, D.A., Panagos, P. 2022 GloSEM: High-resolution global estimates of present and future soil displacement in croplands by water erosion. Scientific data 9, 406(2022). 8, 2013 (2017). Accessed 13 February 2025.
Borrelli P., Robinson D.A., Panagos P., Lugato E., Yang J.E., Alewell C., Wuepper D., Montanarella L., Ballabio C. 2020. Land use and climate change impacts on global soil erosion by water (2015-2070). Proceedings of the National Academy of Sciences (PNAS), 117(36), 21994–22001; doi: 10.1073/pnas.2001403117
Food and Agriculture Organization of the United Nations (FAO), 2012. Global Soil Partnership. Food and Agricultural Organization of the United Nations (FAO). Accessed 13 February 2025.
Food and Agriculture Organization of the United Nations (FAO), 2015. Status of the World’s Soil Resources: Main Report. Food and Agricultural Organization of the United Nations (FAO). Accessed 13 February 2025
Food and Agriculture Organization of the United Nations (FAO), 2020. Global Symposium on Soil Erosion. Food and Agricultural Organization of the United Nations (FAO). Accessed 13 February 2025.
Food and Agriculture Organization of the United Nations and International Atomic Energy Agency (FAO and IAEA), 2017. Use of 137Cs for soil erosion assessment. Fulajtar, E., L. Mabit, C.S. Renschler and A. Lee Zhi Yi. Food and Agricultural Organization of the United Nations (FAO) and International Atomic Energy Agency (IAEA). Accessed 13 February 2025.
Gomiero, T., 2016. Soil degradation, land scarcity and food security: Reviewing a complex challenge. Sustainability, 8:281. Accessed 13 February 2025.
Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES), 2018. The assessment report on: Land Degradation and Restoration. Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES). Accessed 13 February 2025.
United Nations (UN), 2015. Sustainable development goals. Department of Economic and Social Affairs, United Nations (UN). Accessed 13 February 2025.
United Nations Convention to Combat Desertification (UNCCD), 1994. About the Convention. United Nations Convention to Combat Desertification. Accessed 13 February 2025.