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Assessing nitrous oxide emissions from European peatlands at variable degradation status and land use to improve national GHG inventories
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<p>Nitrous oxide (N<sub>2</sub>O) is 300 times more potent than carbon dioxide in atmospheric warming and it is the main driver of stratospheric ozone depletion. The N<sub>2</sub>O emissions from peatlands are often estimated by applying published IPCC default emission factors, neglecting the stages of peat degradation. Here, we introduce soil bulk density (BD) as a proxy for peat degradation to estimate N<sub>2</sub>O emissions.&#160;A&#160;synthesis of soil physical and geochemical&#160;data from global boreal and temperate peatlands revealed a strong relationship between BD and annual N<sub>2</sub>O emissions (R2=0.56, p<0.001), and the BD&#160;was&#160;superior to other parameters (C/N, pH) in estimating annual N<sub>2</sub>O emissions. The results indicate that the more a peat soil is degraded, and the&#160;larger&#160;the values for BD are the&#160;larger&#160;the risk of&#160;N<sub>2</sub>O emission&#160;in peaty landscapes. Even after rewetting, highly degraded soils may exhibit&#160;large&#160;N<sub>2</sub>O release rates.&#160;A&#160;BD distribution map of European peatlands was generated and the estimated annual N<sub>2</sub>O-N emissions from European peatlands sum up to approximately 46.9 Gg. In conclusion, this research shows that explicitly accounting for the stage of peat degradation as expressed in measured BD values gives reliable N<sub>2</sub>O emission estimates from peatlands on a national scale.</p>
Title: Assessing nitrous oxide emissions from European peatlands at variable degradation status and land use to improve national GHG inventories
Description:
<p>Nitrous oxide (N<sub>2</sub>O) is 300 times more potent than carbon dioxide in atmospheric warming and it is the main driver of stratospheric ozone depletion.
The N<sub>2</sub>O emissions from peatlands are often estimated by applying published IPCC default emission factors, neglecting the stages of peat degradation.
Here, we introduce soil bulk density (BD) as a proxy for peat degradation to estimate N<sub>2</sub>O emissions.
&#160;A&#160;synthesis of soil physical and geochemical&#160;data from global boreal and temperate peatlands revealed a strong relationship between BD and annual N<sub>2</sub>O emissions (R2=0.
56, p<0.
001), and the BD&#160;was&#160;superior to other parameters (C/N, pH) in estimating annual N<sub>2</sub>O emissions.
The results indicate that the more a peat soil is degraded, and the&#160;larger&#160;the values for BD are the&#160;larger&#160;the risk of&#160;N<sub>2</sub>O emission&#160;in peaty landscapes.
Even after rewetting, highly degraded soils may exhibit&#160;large&#160;N<sub>2</sub>O release rates.
&#160;A&#160;BD distribution map of European peatlands was generated and the estimated annual N<sub>2</sub>O-N emissions from European peatlands sum up to approximately 46.
9 Gg.
In conclusion, this research shows that explicitly accounting for the stage of peat degradation as expressed in measured BD values gives reliable N<sub>2</sub>O emission estimates from peatlands on a national scale.
</p>.
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