Cover crop biomass production as a predictor of nitrogen fertilizer replacement value - legumes secure positive effects

Cover crops can contribute to climate change mitigation by promoting soil organic carbon sequestration, retaining nitrogen (N) in soil and lower greenhouse gas emissions from reduced fertilization of following crops. Their N fertilizer replacement value (NFRV) varies based on cover crop type and management. This study aimed at identifying factors affecting cover crop NFRV as a means to guide N fertilizers reduction. Ryegrass ( Lolium perenne L.; RG), plantain ( Plantago lanceolata L.; PL), red clover ( Trifolium pratense L.; RC), and two mixtures (RG+PL and RG+PL+RC) were sown in May 2020 and 2021 in an organic field trial, and terminated by either rotovation+ploughing or ploughing. Spring barley ( Hordeum vulgaris L.) was used as a test crop to quantify NFRV. Before sowing spring barley, cover crop plots were not fertilized and control plots received 0, 50 and 100 kg mineral N ha −1 . In both years, RG+PL+RC had the greatest aboveground biomass and biomass N yield in autumn (5.5 Mg ha −1 , 128 kg N ha −1 ), while RG had the lowest (0.7 Mg ha −1 , 21 kg N ha −1 ). Before termination in spring, differences among cover crop types were less pronounced with no effect of termination method on NFRV. However, the NFRV was significantly correlated to cover crop biomass (p < 0.001) in autumn (r = 0.83) and spring (r = 0.66). NFRV was as high as 100 kg N ha −1 with RC and RG+PL+RC, while negative values were obtained with autumn biomass below 1 Mg ha −1 . We found a strong correlation between cover crop biomass and NFRV, which can guide N fertilization reduction if autumn cover crop biomass can be estimated. The threshold between positive and negative residual N effects at 1 Mg ha −1 confirms the need for a minimum cover crop biomass for providing desired ecosystem services. • The nitrogen fertilizer replacement value (NFRV) of cover crops was tested. • NFRV was positively correlated to autumn cover crop biomass. • Cover crop biomass above 1 Mg DM ha −1 gave positive residual N effects. • Legume-based cover crop mixtures secured high NFRV (50–100 kg N ha −1 ). • Cover crop spring termination method did not affect residual N effects.

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Publication Details

Journal
Agriculture Ecosystems & Environment
Published
2024-12-19
DOI
https://doi.org/10.1016/j.agee.2024.109446
Citations
11
Primary Topic
Agronomic Practices and Intercropping Systems
Type
article
Field-Weighted Citation Impact
6.24

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article

Cover crop biomass production as a predictor of nitrogen fertilizer replacement value - legumes secure positive effects

Jim Rasmussen, Leanne Peixoto, Esben Øster Mortensen, Chiara De Notaris
11 citations
Agriculture Ecosystems & Environment
Agronomic Practices and Intercropping Systems
6.24
article

Cover crop biomass production as a predictor of nitrogen fertilizer replacement value - legumes secure positive effects

Jim Rasmussen, Leanne Peixoto, Esben Øster Mortensen, Chiara De Notaris
article en
11 citations

Abstract

Cover crops can contribute to climate change mitigation by promoting soil organic carbon sequestration, retaining nitrogen (N) in soil and lower greenhouse gas emissions from reduced fertilization of following crops. Their N fertilizer replacement value (NFRV) varies based on cover crop type and management. This study aimed at identifying factors affecting cover crop NFRV as a means to guide N fertilizers reduction. Ryegrass ( Lolium perenne L.; RG), plantain ( Plantago lanceolata L.; PL), red clover ( Trifolium pratense L.; RC), and two mixtures (RG+PL and RG+PL+RC) were sown in May 2020 and 2021 in an organic field trial, and terminated by either rotovation+ploughing or ploughing. Spring barley ( Hordeum vulgaris L.) was used as a test crop to quantify NFRV. Before sowing spring barley, cover crop plots were not fertilized and control plots received 0, 50 and 100 kg mineral N ha −1 . In both years, RG+PL+RC had the greatest aboveground biomass and biomass N yield in autumn (5.5 Mg ha −1 , 128 kg N ha −1 ), while RG had the lowest (0.7 Mg ha −1 , 21 kg N ha −1 ). Before termination in spring, differences among cover crop types were less pronounced with no effect of termination method on NFRV. However, the NFRV was significantly correlated to cover crop biomass (p < 0.001) in autumn (r = 0.83) and spring (r = 0.66). NFRV was as high as 100 kg N ha −1 with RC and RG+PL+RC, while negative values were obtained with autumn biomass below 1 Mg ha −1 . We found a strong correlation between cover crop biomass and NFRV, which can guide N fertilization reduction if autumn cover crop biomass can be estimated. The threshold between positive and negative residual N effects at 1 Mg ha −1 confirms the need for a minimum cover crop biomass for providing desired ecosystem services. • The nitrogen fertilizer replacement value (NFRV) of cover crops was tested. • NFRV was positively correlated to autumn cover crop biomass. • Cover crop biomass above 1 Mg DM ha −1 gave positive residual N effects. • Legume-based cover crop mixtures secured high NFRV (50–100 kg N ha −1 ). • Cover crop spring termination method did not affect residual N effects.

Agriculture Ecosystems & EnvironmentVol. 381
Aarhus University (DK), CMCC Foundation - Euro-Mediterranean Center on Climate Change (IT)
Ministeriet for Fø devarer, Landbrug og Fiskeri, Internationalt Center for Forskning i Økologisk Jordbrug og Fødevaresystemer, Grønt Udviklings- og Demonstrations Program
Zero hunger
Openalex Percentile: Top 3%
Agronomic Practices and Intercropping Systems
6.24
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