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Management effects on nitrate and ammonium leaching in temperate grasslands
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<p>Grassland management can influence nitrogen leaching by changing respective inputs (like fertilization) and outputs (e.g. harvest) from the ecosystem but also through changes in plant and microbial communities and their interactions with the soil. Yet the mechanisms of these processes and their importance for nitrate (NO<sub>3</sub><sup>-</sup>) and ammonium (NH<sub>4</sub><sup>+</sup>) are poorly researched. Although temperate grassland management can cause a high leaching risk, studies measuring annual soil nitrogen fluxes and covering a high number of sites are limited. Using a resin method, we measured annual leaching fluxes of NO<sub>3</sub>-N and NH<sub>4</sub>-N in 150 grassland sites in three German regions from spring 2018 to spring 2019 at a depth of 10 cm. We used Structural Equation Modeling to identify direct and indirect management effects on nitrogen leaching. Both fertilization and grazing intensities increased NO<sub>3</sub>-N leaching to almost the same extent. Fertilization intensity increased NO<sub>3</sub>-N leaching directly and indirectly i) by decreasing the negative effect of plant richness on NO<sub>3</sub>-N leaching and ii) by increasing the positive effect of legume cover on NO<sub>3</sub>-N leaching. Similarly, grazing intensity increased NO<sub>3</sub>-N directly and indirectly i) by increasing the positive effect of legume cover on NO<sub>3</sub>-N leaching and ii) by decreasing the negative effect of grass cover on NO<sub>3</sub>-N leaching. Microbial biomass (nitrogen) increased NO<sub>3</sub>-N leaching and it was not controlled by management. Fertilization strongly increased NH<sub>4</sub>-N leaching, both by a direct effect and indirectly by increasing the positive effect of plant nitrogen on NH<sub>4</sub>-N. Grazing intensity and plant richness had no direct effects on NH<sub>4</sub>-N leaching. We have shown that grassland management considerably influences inorganic nitrogen leaching in the annual basis, and that fertilization intensity is more important than grazing, especially for NH<sub>4</sub>-N leaching. Moreover, we found that plant diversity decreases NO<sub>3</sub>-N leaching, but this effect is controlled by fertilization leading to increased leaching risks. Thus, reducing the management intensity, both in meadows and pastures, can be used as a mitigation tool for inorganic nitrogen leaching.</p>
Copernicus GmbH
Title: Management effects on nitrate and ammonium leaching in temperate grasslands
Description:
<p>Grassland management can influence nitrogen leaching by changing respective inputs (like fertilization) and outputs (e.
g.
harvest) from the ecosystem but also through changes in plant and microbial communities and their interactions with the soil.
Yet the mechanisms of these processes and their importance for nitrate (NO<sub>3</sub><sup>-</sup>) and ammonium (NH<sub>4</sub><sup>+</sup>) are poorly researched.
Although temperate grassland management can cause a high leaching risk, studies measuring annual soil nitrogen fluxes and covering a high number of sites are limited.
Using a resin method, we measured annual leaching fluxes of NO<sub>3</sub>-N and NH<sub>4</sub>-N in 150 grassland sites in three German regions from spring 2018 to spring 2019 at a depth of 10 cm.
We used Structural Equation Modeling to identify direct and indirect management effects on nitrogen leaching.
Both fertilization and grazing intensities increased NO<sub>3</sub>-N leaching to almost the same extent.
Fertilization intensity increased NO<sub>3</sub>-N leaching directly and indirectly i) by decreasing the negative effect of plant richness on NO<sub>3</sub>-N leaching and ii) by increasing the positive effect of legume cover on NO<sub>3</sub>-N leaching.
Similarly, grazing intensity increased NO<sub>3</sub>-N directly and indirectly i) by increasing the positive effect of legume cover on NO<sub>3</sub>-N leaching and ii) by decreasing the negative effect of grass cover on NO<sub>3</sub>-N leaching.
Microbial biomass (nitrogen) increased NO<sub>3</sub>-N leaching and it was not controlled by management.
Fertilization strongly increased NH<sub>4</sub>-N leaching, both by a direct effect and indirectly by increasing the positive effect of plant nitrogen on NH<sub>4</sub>-N.
Grazing intensity and plant richness had no direct effects on NH<sub>4</sub>-N leaching.
We have shown that grassland management considerably influences inorganic nitrogen leaching in the annual basis, and that fertilization intensity is more important than grazing, especially for NH<sub>4</sub>-N leaching.
Moreover, we found that plant diversity decreases NO<sub>3</sub>-N leaching, but this effect is controlled by fertilization leading to increased leaching risks.
Thus, reducing the management intensity, both in meadows and pastures, can be used as a mitigation tool for inorganic nitrogen leaching.
</p>.
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