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Adapt N fertiliser application (doses or methods)

System: Arable crops

Mainly applicable for: Applicable for most crops. Regarding split application, this is already a common practice for several crops such as cereals. Placement of fertilisers by banding fertilisers is most applicable for crops grown at wider row spacings (e.g. maize, sugar beet).

Description

Reducing and optimizing mineral nitrogen fertiliser application in cropping systems through precision fertilisation, which matches fertiliser use to crop needs by adjusting rate, timing, type, and placement. The reduction of N fertiliser rate can be either : 1) a reduction due to higher uptake efficiency while maintaining yield (e.g. better timing and placement) and 2) further reduction (suboptimal fertilisation situation) with risks for yield decreases.

Adapting N fertiliser application involves:
• Adjusting fertiliser doses by considering existing nutrient inputs and setting realistic yield targets (right rate).
• Timing applications based on crop needs and climatic conditions, for example by splitting doses during the growing season (right time).
• Placing fertilisers strategically, such as banding or incorporating them near zones with most intensive rooting instead of broadcasting on the soil surface (right place).
• Using decision-support tools or nutrient management software to guide fertiliser strategies.

For best results, combining several of these practices is recommended, as a single action may have limited effect. This strategy can be combined with the solution “Apply low emission fertilisers.”
The techniques aiming at a higher NUE can be reinforced by agronomic practices that favour soil fertility or enhanced root health for nitrogen uptake efficiency , such as application of organic fertilisers and diversification of crop systems with legumes (both break crops and sources of nitrogen issued from symbiotic fixation); see factsheets “Cultivate more legumes crops” or “Grow cover crops”.

Mechanism of effect

More efficient mineral fertiliser application reduces nitrous oxide (N₂O) emissions by minimizing excess nitrogen in the soil, which drives microbial processes like denitrification. Applying fertiliser closer to the active root zone, especially with slight incorporation, helps to:
• Reduce ammonia (NH₃) emission, a common nitrogen loss when fertilizers are surface-applied (e.g., urea), lowering indirect N₂O emissions.
• Improve nitrogen use efficiency (NUE) by making nitrogen more available to plants and less to microbes, enabling lower fertilizer rates without reducing yields, and thereby lowering N₂O emissions and lowering nitrate leaching (linked to indirect emissions). Reducing fertilizer rates also reduces CO₂ emissions from manufacturing and transportation of purchased synthetic fertilizers.

Reference situation

Usual N fertiliser application practices

Legend

– Small effect (<5%)o – No effecto – no effect
●● – Medium effect (5-20%) – Unfavourable effectN/A – unknown effect
●●● – Large effect (>20%) – Variable effect (depending on farm characteristics or way/level of implementation)
Effect on total greenhouse gas (GHG) emissions (kg CO2-eq)
Mean effect and range in kg CO2-equivalentsper haLevel of evidence
Meanmin-max
Adapt N dose to crop requirements in a given situation (right rate)●●●●High
Split N application (vs. one-time)Medium
Banded application (vs. broadcasting)Medium
Effect per emission source
SoilInputsEnergy use
N2Omin-maxCO2min-maxCO2min-max
Adapt N dose to crop requirements in a given situation (right rate)●●●●●●●●o
Split N application (vs. one-time)
Banded application (vs. broadcasting)●●●●?
Effect on soil organic carbon (SOC) stocks
Relative change (%) in SOC%:
Mean(min-max)Level of evidence
Synthetic fertilizer vs. no fertilizer ●●●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

Reduce N fertilization rate

The effect of reducing N fertilization rate on GHG emissions depends on the reference situation, with a larger degree of reduction resulting in a larger reduction of N2O and CO2 emission per hectare. If the current fertilization rate is lower than recommended rates, reducing the application rate may reduce crop yields which can result in higher GHG emissions per kg of crop produced. That is why this solution is facilitated by agronomic strategies to increase nitrogen sources from recycling organic matter (rebuilding soil fertility) and increasing legume in cropping systems (to get nitrogen issued from symbiotic N fixation therefore renewable nitrogen).

Split N application (vs. one-time)

Split application of fertilizer often results in lower nitrous oxide (N₂O) emissions because it aligns better with crop nitrogen uptake, reducing the amount of nitrogen available for microbial processes that produce N₂O. The effectiveness depends on the proper timing of split applications, weather conditions, and other management practices to enhance benefits of spit application, such as precision techniques. In some cases, adverse weather conditions can still lead to higher emissions despite split applications.

Banded application (vs. broadcasting)

The effect of banded application on nitrous oxide (N₂O) emissions depends on (i) local soil and environmental conditions, (ii) proper placement and proper concentration of the nitrogen in the band, and (iii) other management practices that can enhance benefits of banded applications, such as enhanced efficiency fertilizer or nitrification inhibitors. Banded application may lead to increased emissions if the soil conditions (soil type, moisture, temperature) favor rapid nitrification and denitrification processes. In water-saturated or poorly drained soils, localized band placement of nitrogen can create anaerobic zones with high nitrogen and moisture levels, promoting denitrification “hotspots” and thus increased N₂O emissions. Concentrating fertilizer in a small area also encourages microbial activity that produces more N₂O due to excess available nitrogen. Applying a large amount of nitrogen in a narrow band without adapting/reducing the dose compare to broadcast fertilisation, can exceed root uptake capacity, leaving excess nitrogen available for microbes and leading to greater N₂O losses. That is why this technique requires adapted management practices to use it properly.

Synthetic fertilizer vs. no fertilizer

The carbon sequestration potential of reducing synthetic fertilizer spans a wide range because it depends on whether N reductions limit biomass inputs (small effect) or eliminate unnecessary fertilizer without harming productivity (large effect), and on how strongly N₂O emissions respond to improved nitrogen management. Further, the carbon sequestration potentials in European soils range from very small to very high because they depend on multiple interacting factors that differ widely across landscapes, climates, and farming systems.

Literature referencesOptimize N fertilization rate
Han et al., 2017N2O emissions from grain cropping systems: a meta-analysis of the impacts of fertilizer-based and ecologically-based nutrient management strategies
Guo et al., 2022A global meta-analysis of crop yield and agricultural greenhouse gas emissions under nitrogen fertilizer application
Literature referencesSplit N application (vs. one-time)
Guo et al., 2022A global meta-analysis of crop yield and agricultural greenhouse gas emissions under nitrogen fertilizer application
Literature referencesBanded application (vs. broadcasting)
Guo et al., 2022A global meta-analysis of crop yield and agricultural greenhouse gas emissions under nitrogen fertilizer application
Literature referencesSynthetic fertilizer vs. no fertilizer
Beillouin et al., 2023A globalmeta-analysis of soil organic carbon in the Anthropocene