
Reduce soil tillage
System: Arable Crops
Applicability
Not applicable or effective for: Already compacted soils as here a reduced or no tillage can increase soil compaction and thus pest and disease pressure. In crop rotations with many root crops the effect of reduced tillage will be very limited due to soil distrubance at the harvest of the crops
Description
Cultivating a permanent vegetation that covers the soil underneath and in alleys between the olive trees. The vegetation can be used as cover crops to cover and protect bare ground, and/or as inter crops where additional plants are grown parallel to the olive trees. The additional soil cover reduces erosion, increases biodiversity and provides additional carbon, which potentially increases soil organic carbon (SOC). On the other side, the additional vegetation might increase evapotranspiration, which might be critical as olive orchards are often situated in water scarce regions.
Mechanism of effect
By growing additional crops on the ground, more atmospheric carbon is removed and stored in the form of biomass. This additional biomass will potentially increase carbon inputs into the soil and, therefore, increase the SOC. Beside the increase of SOC, ground vegetation reduces soil and SOC loss by erosion. A study of Marquez-Garcia et al. (2024) shows that conservation management (ground cover vegetation and no tillage) can reduce erosion by up to 85 % and accordingly reduce SOC losses by 76 %. Torrus-Castillo et al. (2022) found that ground vegetation can help to improve the nutrient use efficiency by reducing nutrient losses.
Effect on organic carbon stocks
Reference situation: Conventional tillage (up to 30 cm) or reduced tillage
Soil organic carbon (SOC)
| Relative change (%) in SOC%: | Relative change | ||
| Mean | (min-max) | Level of evidence | |
| Conservation tillage vs. conventional tillage | ●● | ●–●●● | High |
| No tillage vs. conventional tillage | ● | o-●●● | High |
| Reduced tillage vs. conventional tillage | ? | ●–●● | High |
| No tillage vs reduced tillage | ● | ●–●● | High |
| ● – small increase (<10%) | ● – small decrease (<5%) | o – no effect |
| ●● – medium increase (10-25%) | ●●– large decrease (≥5%) | ? – unknown effect |
| ●●● – large increase (>25%) | ● – ● – Variable effect (depending on farm characteristics or way/level of implementation) |
Explanation of variable effect
All measures
Changes in tillage management—such as shifting from conventional tillage to reduced tillage or no-till—produce highly variable SOC sequestration outcomes in Europe (Fohrafellner et al. 2023) because their effectiveness depends on a wide range of environmental and agronomic factors. The impact of conservation tillage on GHG emissions and SOC is influenced by climate (temperature and precipitation), soil texture, soil pH, crop species, microbial activity, and especially the duration of the practice.
Soil properties are a major driver of variation. Clay-rich soils generally show greater SOC gains because clay particles protect organic matter from decomposition, while sandy soils offer limited physical protection and therefore store less carbon. Soils with high microbial diversity and activity can better stabilize organic carbon, but microbial responses differ by soil type and climate. Warmer and wetter regions often show higher SOC sequestration potential under conservation tillage because microbial processes that build stable carbon are more active—although these same conditions can also increase decomposition, adding further variability.
The duration of conservation tillage is equally important: long-term adoption tends to deliver more SOC gain than short-term changes, and results improve when combined with complementary practices like residue retention, diverse rotations, or cover crops. Tillage reductions alone often yield modest or inconsistent gains.
No-till in particular tends to increase SOC mainly in the upper soil layers, while deeper layers often show no change or losses of SOC. This uneven distribution makes the overall SOC impact across the full soil profile very uncertain. Studies such as Haddaway et al. (2017) and Mary et al. (2020) report limited or no long-term SOC increases, although integrating no-till with other carbon-enhancing practices can improve outcomes (Chenu et al. 2019; Dignac et al. 2017).
Because these interacting factors vary widely across Europe’s diverse soils and climates, SOC responses to conservation tillage range from minimal to substantial. As a result, no-till and reduced tillage are often most valuable as measures for reducing erosion and improving climate resilience, with SOC sequestration considered a potential but uncertain secondary benefit (Ogle et al. 2019).
| Literature references | Maintain permanent pasture |
|---|---|
| Nicoloso et al., 2021 | Intensification of no-till agricultural systems: An opportunity for carbon sequestration |
| Gao et al., 2017 | Evaluation of the Agronomic Impacts on Yield-Scaled N2O Emission from Wheat and Maize Fields in China |
| Kan et al., 2021 | Effects of experiment duration on carbon mineralization and accumulation under no-till |
| Li et al., 2020 | Residue retention promotes soil carbon accumulation in minimum tillage systems: Implications for conservation agriculture |
| Mondal et al., 2020 | A global analysis of the impact of zero-tillage on soil physical condition, organic carbon content, and plant root response |
| Bai et al., 2019 | Responses of soil carbon sequestration to climate-smart agriculture practices: A meta-analysis |
| Mukumbuta et al., 2019 | Do tillage and conversion of grassland to cropland always deplete soil organic carbon? |
| Beillouin et al., 2023 | A globalmeta-analysis of soil organic carbon in the Anthropocene |
| Haddaway et al., 2017 | How does tillage intensity affect soil organic carbon? A systematic review. Environmental Evidence, 6, 1-48. |
| Sainju, 2016 | A Global Meta-Analysis on the Impact of Management Practices on Net Global Warming Potential and Greenhouse Gas Intensity from Cropland Soils |
| Mary et al., 2020 | Soil carbon storage and mineralization rates are affected by carbon inputs rather than physical disturbance: Evidence from a 47-year tillage experiment. Agriculture, Ecosystems & Environment 299, 106972. |
| Chenu et al., 2019 | Increasing organic stocks in agricultural soils: Knowledge gaps and potential innovations.Soil Till. Res. 188, 41–52, doi:10.1016/j.still.2018.04.011 |
| Dimassi et al., 2014 | Long-term effect of contrasted tillage and crop management on soil carbon dynamics during 41 years. Agric. Ecosyst. Environ. 188, 134–146 doi:10.1016/j.agee.2014.02.014 |
| Ogle et al., 2019 | Determine Where No-Till Management Can Store Carbon in Soils and Mitigate Greenhouse Gas Emissions. Sci Rep 9, 11665. doi:10.1038/s41598-019-47861-7 |
| Fohrafellner et al., 2023 | Quality assessment of meta-analyses on soil organic carbon |
| Haddawayet al., 2017 | How does tillage intensity affect soil organic carbon? A systematic review. Environmental Evidence, 6, 1-48. |