How do sand addition, soil moisture and nutrient status influence greenhouse gas fluxes from drained organic soils?

Publikation: Beitrag in FachzeitschriftArtikelForschungPeer-Review

Autoren

  • Annelie Säurich
  • Bärbel Tiemeyer
  • Ullrich Dettmann
  • Axel Don

Organisationseinheiten

Externe Organisationen

  • Johann Heinrich von Thünen-Institut, Bundesforschungsinstitut für Ländliche Räume, Wald und Fischerei
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Details

OriginalspracheEnglisch
Seiten (von - bis)71-84
Seitenumfang14
FachzeitschriftSoil Biology and Biochemistry
Jahrgang135
Frühes Online-Datum22 Apr. 2019
PublikationsstatusVeröffentlicht - Aug. 2019

Abstract

Drainage turns peatlands from natural carbon sinks into hotspots of greenhouse gas (GHG)emissions from soils due to alterations in hydrological and biogeochemical processes. As a consequence of drainage-induced mineralisation and anthropogenic sand addition, large areas of former peatlands under agricultural use have soil organic carbon (SOC)contents at the boundary between mineral and organic soils. Previous research has shown that the variability of GHG emissions increases with anthropogenic disturbance. However, how and whether sand addition affects GHG emissions remains a controversial issue. The aim of this long-term incubation experiment was to assess the influence of hydrological and biogeochemical soil properties on emissions of carbon dioxide (CO2), nitrous oxide (N2O)and methane (CH4). Strongly degraded peat with sand addition (peat-sand mixtures)and without sand addition (earthified peat)was systematically compared under different moisture conditions for fen and bog peat. Soil columns originating from both the topsoil and the subsoil of ten different peatlands under grassland use were investigated. Over a period of six months the almost saturated soil columns were drained stepwise via suction to −300 hPa. The CO2 fluxes were lowest at water-saturated and dry soil moisture conditions, resulting in a parabolic dependence of CO2 fluxes on the water-filled pore space (WFPS)peaking at 56–92% WFPS. The highest N2O fluxes were found at between 73 and 95% WFPS. Maximum CO2 fluxes were highest from topsoils, ranging from 21 to 77 mg C m−2 h−1, while the maximum CO2 fluxes from subsoils ranged from 3 to 14 mg C m−2 h−1. No systematic influence of peat type or sand addition on GHG emissions was found in topsoils, but CO2 fluxes from subsoils below peat-sand mixtures were higher than from subsoils below earthified peat. Maximum N2O fluxes were highly variable between sites and ranged from 18.5 to 234.9 and from 0.2 to 22.9 μg N m−2 h−1 for topsoils and subsoils, respectively. CH4 fluxes were negligible even under water-saturated conditions. The highest GHG emissions occurred at a WFPS that relates – under equilibrium conditions – to a water table of 20–60 cm below the surface in the field. High maximum CO2 and N2O fluxes were linked to high densities of plant-available phosphorus and potassium. The results of this study highlight that nutrient status plays a more important role in GHG emissions than peat type or sand addition, and do not support the idea of peat-sand mixtures as a mitigation option for GHG emissions.

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How do sand addition, soil moisture and nutrient status influence greenhouse gas fluxes from drained organic soils? / Säurich, Annelie; Tiemeyer, Bärbel; Dettmann, Ullrich et al.
in: Soil Biology and Biochemistry, Jahrgang 135, 08.2019, S. 71-84.

Publikation: Beitrag in FachzeitschriftArtikelForschungPeer-Review

Säurich A, Tiemeyer B, Dettmann U, Don A. How do sand addition, soil moisture and nutrient status influence greenhouse gas fluxes from drained organic soils? Soil Biology and Biochemistry. 2019 Aug;135:71-84. Epub 2019 Apr 22. doi: 10.1016/j.soilbio.2019.04.013, 10.15488/5064
Säurich, Annelie ; Tiemeyer, Bärbel ; Dettmann, Ullrich et al. / How do sand addition, soil moisture and nutrient status influence greenhouse gas fluxes from drained organic soils?. in: Soil Biology and Biochemistry. 2019 ; Jahrgang 135. S. 71-84.
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title = "How do sand addition, soil moisture and nutrient status influence greenhouse gas fluxes from drained organic soils?",
abstract = "Drainage turns peatlands from natural carbon sinks into hotspots of greenhouse gas (GHG)emissions from soils due to alterations in hydrological and biogeochemical processes. As a consequence of drainage-induced mineralisation and anthropogenic sand addition, large areas of former peatlands under agricultural use have soil organic carbon (SOC)contents at the boundary between mineral and organic soils. Previous research has shown that the variability of GHG emissions increases with anthropogenic disturbance. However, how and whether sand addition affects GHG emissions remains a controversial issue. The aim of this long-term incubation experiment was to assess the influence of hydrological and biogeochemical soil properties on emissions of carbon dioxide (CO2), nitrous oxide (N2O)and methane (CH4). Strongly degraded peat with sand addition (peat-sand mixtures)and without sand addition (earthified peat)was systematically compared under different moisture conditions for fen and bog peat. Soil columns originating from both the topsoil and the subsoil of ten different peatlands under grassland use were investigated. Over a period of six months the almost saturated soil columns were drained stepwise via suction to −300 hPa. The CO2 fluxes were lowest at water-saturated and dry soil moisture conditions, resulting in a parabolic dependence of CO2 fluxes on the water-filled pore space (WFPS)peaking at 56–92% WFPS. The highest N2O fluxes were found at between 73 and 95% WFPS. Maximum CO2 fluxes were highest from topsoils, ranging from 21 to 77 mg C m−2 h−1, while the maximum CO2 fluxes from subsoils ranged from 3 to 14 mg C m−2 h−1. No systematic influence of peat type or sand addition on GHG emissions was found in topsoils, but CO2 fluxes from subsoils below peat-sand mixtures were higher than from subsoils below earthified peat. Maximum N2O fluxes were highly variable between sites and ranged from 18.5 to 234.9 and from 0.2 to 22.9 μg N m−2 h−1 for topsoils and subsoils, respectively. CH4 fluxes were negligible even under water-saturated conditions. The highest GHG emissions occurred at a WFPS that relates – under equilibrium conditions – to a water table of 20–60 cm below the surface in the field. High maximum CO2 and N2O fluxes were linked to high densities of plant-available phosphorus and potassium. The results of this study highlight that nutrient status plays a more important role in GHG emissions than peat type or sand addition, and do not support the idea of peat-sand mixtures as a mitigation option for GHG emissions.",
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Download

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T1 - How do sand addition, soil moisture and nutrient status influence greenhouse gas fluxes from drained organic soils?

AU - Säurich, Annelie

AU - Tiemeyer, Bärbel

AU - Dettmann, Ullrich

AU - Don, Axel

N1 - Funding information: This work would not have been possible without the help of Frank Hegewald, Stefan Burkart, Thomas Viohl, Arndt Piayda, Mareille Wittnebel, Sebastian Willi Oehmke, Peter Braunisch, Viridiana Alcántara, Roland Prietz, Arne Heidkamp, Anna Jacobs, Angélica Jaconi, Ute Tambor, Nicole Altwein, Daniel Ziehe and Sabine Wathsack. The study was carried out as part of the German Agricultural Soil Inventory, which was funded by the German Federal Ministry of Food and Agriculture. This work would not have been possible without the help of Frank Hegewald, Stefan Burkart, Thomas Viohl, Arndt Piayda, Mareille Wittnebel, Sebastian Willi Oehmke, Peter Braunisch, Viridiana Alcántara, Roland Prietz, Arne Heidkamp, Anna Jacobs, Angélica Jaconi, Ute Tambor, Nicole Altwein, Daniel Ziehe and Sabine Wathsack. The study was carried out as part of the German Agricultural Soil Inventory, which was funded by the German Federal Ministry of Food and Agriculture .

PY - 2019/8

Y1 - 2019/8

N2 - Drainage turns peatlands from natural carbon sinks into hotspots of greenhouse gas (GHG)emissions from soils due to alterations in hydrological and biogeochemical processes. As a consequence of drainage-induced mineralisation and anthropogenic sand addition, large areas of former peatlands under agricultural use have soil organic carbon (SOC)contents at the boundary between mineral and organic soils. Previous research has shown that the variability of GHG emissions increases with anthropogenic disturbance. However, how and whether sand addition affects GHG emissions remains a controversial issue. The aim of this long-term incubation experiment was to assess the influence of hydrological and biogeochemical soil properties on emissions of carbon dioxide (CO2), nitrous oxide (N2O)and methane (CH4). Strongly degraded peat with sand addition (peat-sand mixtures)and without sand addition (earthified peat)was systematically compared under different moisture conditions for fen and bog peat. Soil columns originating from both the topsoil and the subsoil of ten different peatlands under grassland use were investigated. Over a period of six months the almost saturated soil columns were drained stepwise via suction to −300 hPa. The CO2 fluxes were lowest at water-saturated and dry soil moisture conditions, resulting in a parabolic dependence of CO2 fluxes on the water-filled pore space (WFPS)peaking at 56–92% WFPS. The highest N2O fluxes were found at between 73 and 95% WFPS. Maximum CO2 fluxes were highest from topsoils, ranging from 21 to 77 mg C m−2 h−1, while the maximum CO2 fluxes from subsoils ranged from 3 to 14 mg C m−2 h−1. No systematic influence of peat type or sand addition on GHG emissions was found in topsoils, but CO2 fluxes from subsoils below peat-sand mixtures were higher than from subsoils below earthified peat. Maximum N2O fluxes were highly variable between sites and ranged from 18.5 to 234.9 and from 0.2 to 22.9 μg N m−2 h−1 for topsoils and subsoils, respectively. CH4 fluxes were negligible even under water-saturated conditions. The highest GHG emissions occurred at a WFPS that relates – under equilibrium conditions – to a water table of 20–60 cm below the surface in the field. High maximum CO2 and N2O fluxes were linked to high densities of plant-available phosphorus and potassium. The results of this study highlight that nutrient status plays a more important role in GHG emissions than peat type or sand addition, and do not support the idea of peat-sand mixtures as a mitigation option for GHG emissions.

AB - Drainage turns peatlands from natural carbon sinks into hotspots of greenhouse gas (GHG)emissions from soils due to alterations in hydrological and biogeochemical processes. As a consequence of drainage-induced mineralisation and anthropogenic sand addition, large areas of former peatlands under agricultural use have soil organic carbon (SOC)contents at the boundary between mineral and organic soils. Previous research has shown that the variability of GHG emissions increases with anthropogenic disturbance. However, how and whether sand addition affects GHG emissions remains a controversial issue. The aim of this long-term incubation experiment was to assess the influence of hydrological and biogeochemical soil properties on emissions of carbon dioxide (CO2), nitrous oxide (N2O)and methane (CH4). Strongly degraded peat with sand addition (peat-sand mixtures)and without sand addition (earthified peat)was systematically compared under different moisture conditions for fen and bog peat. Soil columns originating from both the topsoil and the subsoil of ten different peatlands under grassland use were investigated. Over a period of six months the almost saturated soil columns were drained stepwise via suction to −300 hPa. The CO2 fluxes were lowest at water-saturated and dry soil moisture conditions, resulting in a parabolic dependence of CO2 fluxes on the water-filled pore space (WFPS)peaking at 56–92% WFPS. The highest N2O fluxes were found at between 73 and 95% WFPS. Maximum CO2 fluxes were highest from topsoils, ranging from 21 to 77 mg C m−2 h−1, while the maximum CO2 fluxes from subsoils ranged from 3 to 14 mg C m−2 h−1. No systematic influence of peat type or sand addition on GHG emissions was found in topsoils, but CO2 fluxes from subsoils below peat-sand mixtures were higher than from subsoils below earthified peat. Maximum N2O fluxes were highly variable between sites and ranged from 18.5 to 234.9 and from 0.2 to 22.9 μg N m−2 h−1 for topsoils and subsoils, respectively. CH4 fluxes were negligible even under water-saturated conditions. The highest GHG emissions occurred at a WFPS that relates – under equilibrium conditions – to a water table of 20–60 cm below the surface in the field. High maximum CO2 and N2O fluxes were linked to high densities of plant-available phosphorus and potassium. The results of this study highlight that nutrient status plays a more important role in GHG emissions than peat type or sand addition, and do not support the idea of peat-sand mixtures as a mitigation option for GHG emissions.

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KW - Microcosm incubation

KW - Mitigation measures

KW - Nitrous oxide

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