Abstract:Fens belong to the most threatened ecosystems in Europe. Maintaining a high water table through rewetting is an effective measure to rehabilitate many of their ecosystem functions. However, the impact of meteorological conditions such as vapor pressure deficit (VPD) and precipitation on water tables is still unclear for rewetted fens. Here, we compare the impact of meteorological factors on water table dynamics in a drained and a rewetted fen, using multiple regression with data from continuous high-resolution… Show more
“…Biodiversity loss is a critical threat, and preserving natural habitats, expanding protected areas, and restoring the degraded landscapes are crucial steps in biodiversity improvement. If the authors' findings [2] are followed, it becomes evident that the current consumption of land and resources by humans, alongside the corresponding environmental changes, has a predominantly negative impact on biodiversity at all levels, ranging from genetic diversity Land 2024, 13, 581 2 of 29 to the biome. Reintroducing degraded lands into new green infrastructures for urban areas [3,4], or areas close to the natural state habitats, is supported by ecological engineering approaches to reduce the land consumption pressures of built-up environments.…”
Section: Introductionmentioning
confidence: 99%
“…However, intact peatlands mitigate the effects of global warming by manipulating the water cycle in two ways. According to Ahmad, Liu, and Alam et al [13], there is a connection between the meteorological influences, the groundwater level, and the latent heat flow. This comparison between a drained and a rewetted moor (same area) showed that on the one hand, the groundwater fluctuations were less pronounced; therefore, the daily evaporation for the rewetted moor could be increased by around 2.5 times.…”
Draining peatlands to create agricultural land has been the norm in Europe, but in the context of climate change and the loss of biodiversity, these rich ecosystems may reactivate their functions as greenhouse gas sinks and retreat spaces for animals and plants. Against this background, the National Moor Rewetting Strategy was put into effect in Germany in 2023, together with the Natural Climate Protection Action Plan. This article examines the methodology of peatland rewetting from scientific, administrative, social, and technical perspectives. The article focuses on an example of moor rewetting in central Germany: the Rathsbruch moor near the municipality of Zerbst, Saxony-Anhalt. To illustrate the importance of rewetting projects for degraded peatlands, five scenarios with different target soil water levels were considered, and the associated greenhouse gas emissions were calculated for a period of five years. For the planning solution, an estimate of the medium-to-long-term development of the habitat types was made based on current use and the dynamics typical of the habitat. The results for the Rathsbruch moor area showed that increasing the water level in steps of 1, 0.8, or 0.5 m has no significant influence on reducing the CO2 emissions situation, while a depth of 0.3 m has a slight influence. When the water was raised to 0.1 m below the surface (Scenario 5), a significant CO2 reduction was observed. The calculated avoided CO2 costs due to environmental damage show that the environmental benefits multiply with every decimeter of water level increase. The rising groundwater levels and extensification favor the establishment of local biotopes. This means that two of the biggest man-made problems (extinction of species and climate change) can be reduced. Therefore, this research is applicable to the development and planning of recultivation work at municipal and regional levels in Germany and beyond within the framework of EU restoration policy.
“…Biodiversity loss is a critical threat, and preserving natural habitats, expanding protected areas, and restoring the degraded landscapes are crucial steps in biodiversity improvement. If the authors' findings [2] are followed, it becomes evident that the current consumption of land and resources by humans, alongside the corresponding environmental changes, has a predominantly negative impact on biodiversity at all levels, ranging from genetic diversity Land 2024, 13, 581 2 of 29 to the biome. Reintroducing degraded lands into new green infrastructures for urban areas [3,4], or areas close to the natural state habitats, is supported by ecological engineering approaches to reduce the land consumption pressures of built-up environments.…”
Section: Introductionmentioning
confidence: 99%
“…However, intact peatlands mitigate the effects of global warming by manipulating the water cycle in two ways. According to Ahmad, Liu, and Alam et al [13], there is a connection between the meteorological influences, the groundwater level, and the latent heat flow. This comparison between a drained and a rewetted moor (same area) showed that on the one hand, the groundwater fluctuations were less pronounced; therefore, the daily evaporation for the rewetted moor could be increased by around 2.5 times.…”
Draining peatlands to create agricultural land has been the norm in Europe, but in the context of climate change and the loss of biodiversity, these rich ecosystems may reactivate their functions as greenhouse gas sinks and retreat spaces for animals and plants. Against this background, the National Moor Rewetting Strategy was put into effect in Germany in 2023, together with the Natural Climate Protection Action Plan. This article examines the methodology of peatland rewetting from scientific, administrative, social, and technical perspectives. The article focuses on an example of moor rewetting in central Germany: the Rathsbruch moor near the municipality of Zerbst, Saxony-Anhalt. To illustrate the importance of rewetting projects for degraded peatlands, five scenarios with different target soil water levels were considered, and the associated greenhouse gas emissions were calculated for a period of five years. For the planning solution, an estimate of the medium-to-long-term development of the habitat types was made based on current use and the dynamics typical of the habitat. The results for the Rathsbruch moor area showed that increasing the water level in steps of 1, 0.8, or 0.5 m has no significant influence on reducing the CO2 emissions situation, while a depth of 0.3 m has a slight influence. When the water was raised to 0.1 m below the surface (Scenario 5), a significant CO2 reduction was observed. The calculated avoided CO2 costs due to environmental damage show that the environmental benefits multiply with every decimeter of water level increase. The rising groundwater levels and extensification favor the establishment of local biotopes. This means that two of the biggest man-made problems (extinction of species and climate change) can be reduced. Therefore, this research is applicable to the development and planning of recultivation work at municipal and regional levels in Germany and beyond within the framework of EU restoration policy.
“…The depth to water table in peatlands is not homogeneous and depends on spatial location (Joris & Feyen, 2003), soil physical parameters (Ahmad et al, 2021), vegetation cover (Volik et al, 2020), and of course seasonal atmospheric forcings. As a consequence, its effect on the concentrations of chemical elements varies both spatially and temporally.…”
Section: Introductionmentioning
confidence: 99%
“…Although chloride behaviour is affected by several processes that indicate topsoil transformation, the depth to water table remains a crucial factor for the chloride concentrations in shallow groundwater. The depth to water table in peatlands is not homogeneous and depends on spatial location (Joris & Feyen, 2003), soil physical parameters (Ahmad et al, 2021), vegetation cover (Volik et al, 2020), and of course seasonal atmospheric forcings. As a consequence, its effect on the concentrations of chemical elements varies both spatially and temporally.…”
Peatlands are environments that rely mainly on high water levels to accumulate organic matter. Depending on the chemical species observed, the lowering of the water table can change biogeochemical equilibriums, with various impacts. This paper aims to understand the effect of shallow groundwater seasonality on chloride concentrations in a French riparian peatland by combining water table monitoring, geochemical and stable water isotopes analysis. Water table levels and groundwater samples were recorded and collected for 3 years, every 2 months, in nine observation wells and the nearby river. Chloride concentrations were highly variable in space and time, ranging from 10 to 100 mg L−1. They are shown to be related to the water table dynamics, which are closely linked to the life cycle of the local vegetation. These dynamics were characterized by a significant drawdown between June and October due to plant transpiration and a fast recovering period just after its senescence. Results show that the chloride accumulates within the unsaturated zone during the drying phase and is solubilized back into the groundwater during the rewetting phase, increasing its concentration. Moreover, the water table rises in autumn with various dynamics according to the location in the peatland, which induces some special differences in hydraulic gradients. Such gradients allow lateral transfers from zones of fast recovery to zones of slow recovery, where year‐to‐year chloride accumulation was observed. These complex 3D processes preclude the use of chloride to constrain how the peatland hydrogeological system functions. Conversely, the use of stable water isotopes in this work emphasizes the importance of the river's role during the summer as a water supplier to counterbalance vegetation transpiration.
“…Despite the importance of these near‐surface controls on peatland hydrology and carbon sequestration, historically the quantification of peatland hydrophysical properties and the hydrological simulation of the ecosystems has focused on peat properties at depth (Wang et al, 2021), linking surface ecological dynamics with the water table depth (WTD) (Ahmad et al, 2021). However, more recently, notably Canadian, peatland studies evaluated moss moistures stresses via known ecohydrological thresholds by quantifying bulk densities, hydrophysical properties, water table depths and peat moistures of very near‐surface layers regrowing or recolonizing onto the cutover surface (Cagampan & Waddington, 2008; Gauthier et al, 2018; Golubev et al, 2021; McCarter & Price, 2015; Turetsky et al, 2008; Waddington et al, 2011) This focus on near‐surface properties and hydrological dynamics is important.…”
Northern peatlands faced compounding disturbances that transformed such critical ecosystems from long‐term carbon sinks into carbon sources. Considerable investment is therefore directed for restoring their carbon sequestration potential through large‐scale rewetting/rehabilitation. However, rapid need to transform their carbon dynamics contrasts with millennial timescales over which peat profiles that control key ecohydrological processes within these ecosystems have developed. This study demonstrates the sensitivity of vadose zone hydrology of northern peatlands to hydrophysical properties of the very near‐surface peat layer and therefore the potential capability of at least some ecohydrological processes to respond rapidly to developments in peat properties as a result of restoration. HYDRUS 1‐D Monte Carlo simulations were undertaken of near‐surface peat layers of various species and depths overlying degraded peat layer during periods of sustained drying. The modelling results showed that shallow additions of newly developed Sphagnum peat, just a couple of centimetres in depth, substantially modified near‐surface hydrology of peat profiles and significantly altered the time taken for reaching important ecohydrological pressure heads. Whilst a degraded peat layer reached threshold pressure head (TP) of −100 cm in 119 h, addition of 2.5‐cm layer of S. magellancium reduced the average time to TP by 18 hours, whilst S. fuscum and amalgamated Sphagnum overlying degraded peat across initial WTDs (5, 10, 15 and 20 cm) increased average time to TP by 304 and 540 h, respectively. This demonstrates that whilst peat hydrophysical properties have developed over millennia, ecohydrological dynamics of these systems rapidly adjusted through restoration approaches in response to disturbances.
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