{"type": "FeatureCollection", "features": [{"id": "10.5061/dryad.cjsxksncn", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:33Z", "type": "Dataset", "created": "2023-10-13", "title": "Tillage agriculture and afforestation threaten tropical savanna plant communities across a broad rainfall gradient in India", "description": "unspecifiedThe consequences of land-use change for savanna biodiversity remain  undocumented in most regions of tropical Asia. One such region is western  Maharashtra, India, where old-growth savannas occupy a broad rainfall  gradient and are increasingly rare due to agricultural conversion and  afforestation. To understand the consequences of land-use change, we  sampled herbaceous plant communities of old-growth savannas and three  alternative land-use types: tree plantations, tillage agriculture, and  agricultural fallows (n=15 sites per type). Study sites spanned 457 to  1954 mm of mean annual precipitation\u2014corresponding to the typical rainfall  range of mesic savannas globally. Across the rainfall gradient, we found  consistent declines in old-growth savanna plant communities due to  land-use change. Local-scale native species richness dropped from a mean  of 12 species/m2 in old-growth savannas to 8, 6, and 3 species/m2 in tree  plantations, fallows, and tillage agriculture, respectively. Cover of  native plants declined from a mean of 49% in old-growth savannas to 27% in  both tree plantations and fallows, and 4% in tillage agriculture.  Reductions in native cover coincided with increased cover of invasive  species in tree plantations (18%), fallows (18%), and tillage agriculture  (3%). In analyses of community composition, tillage agriculture was most  dissimilar to old-growth savannas, while tree plantations and fallows  showed intermediate dissimilarity. These compositional changes were driven  partly by the loss of characteristic savanna species: 65 species recorded  in old-growth savannas were absent in other land uses. Indicator analysis  revealed 21 old-growth species, comprised mostly of native savanna  specialists. Indicators of tree plantations (9 species) and fallows (13  species) were both invasive and native species, while the 2 indicators of  tillage agriculture were invasive. As reflective of declines in savanna  communities, mean native perennial graminoid cover of 27% in old-growth  savannas dropped to 9%, 7%, and 0.1% in tree plantations, fallows, and  tillage agriculture, respectively. Synthesis: Agricultural conversion and  afforestation of old-growth savannas in India destroys and degrades  herbaceous plant communities that do not spontaneously recover on fallowed  land. Efforts to conserve India\u2019s native biodiversity should encompass the  country\u2019s widespread savanna biome and seek to limit conversion of  irreplaceable old-growth savannas.", "keywords": ["2. Zero hunger", "land use change", "13. Climate action", "plant species richness", "India", "Biodiversity", "15. Life on land", "grassland", "herbivores", "fire", "FOS: Natural sciences"], "contacts": [{"organization": "Nerlekar, Ashish, Munje, Avishkar, Mhaisalkar, Pranav, Hiremath, Ankila, Veldman, Joseph,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.cjsxksncn"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.cjsxksncn", "name": "item", "description": "10.5061/dryad.cjsxksncn", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.cjsxksncn"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-10-17T00:00:00Z"}}, {"id": "10.25338/B8P92J", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:21:31Z", "type": "Dataset", "created": "2023-07-13", "title": "Spatio-temporal dynamics of insect communities in constructed and natural tidal marshes with distinct landscape positions", "description": "unspecified| | | | | | | | |  ------------------------------------------------------------------------------------------------------------------------------------------------------------------- | ----------------------------------------------------------------------------------------------------------------------------------------------------------------- | ---------------------------------------------------------- | ------------------------------------------------- | ------------------------------------------------------------------------------------------------------------- | ------- | ------------------------------------------------------ | | This readme file was generated on 2023-07-05 by Emily Fromenthal | | | | | | | | | | | | | | | | GENERAL INFORMATION | | | | | | | | | | | | | | | | Title of Dataset: Beyond the Marsh: Tidal Marsh Landscape Position Influences Insect Community Structure | | | | | | | | | | | | | | | | Author/Principal Investigator Information | | | | | | | | Name: Emily Fromenthal | | | | | | | | Institution: University of Alabama | | | | | | | | Email:[efromenthal@crimson.ua.edu](mailto:efromenthal@crimson.ua.edu) | | | | | | | | Author/Associate or Co-investigator Information | | | | | | | | Name: Shelby Rinehart | | | | | | | | ORCID:0000-0001-9820-1350 | | | | | | | | Institution: University of Alabama &amp; Drexel University | | | | | | | | Email: [srinehart@ucdavis.edu](mailto:srinehart@ucdavis.edu) OR [sarinehart@ua.edu](mailto:sarinehart@ua.edu) | | | | | | | | Author/Associate or Co-investigator Information | | | | | | | | Name: Jacob M Dybiec | | | | | | | | Institution: University of Alabama | | | | | | | | Email: [jmdybiec@crimson.ua.edu](mailto:jmdybiec@crimson.ua.edu) | | | | | | | | Author/Associate or Co-investigator Information | | | | | | | | Name: Julia A Cherry | | | | | | | | Institution: University of Alabama | | | | | | | | Email: [cherr002@ua.edu](mailto:cherr002@ua.edu) | | | | | | | | | | | | | | | | Date of data collection: 2021-04 through 2021-10 | | | | | | | | | | | | | | | | Geographic location of data collection: West Fowl River | Coden | Alabama | USA | | | | | CON-1: 30.368 N | -88.152 W | | | | | | | CON-2: 30.367 N | -88.151 W | | | | | | | NAT: 30.368 N | -88.160 W | | | | | | | | | | | | | | | Information about funding sources that supported the collection of the data: | | | | | | | | The Society of Wetland Scientists | | | | | | | | University of Alabama | Department of Biological Sciences | | | | | | | | | | | | | | | | | | | | | | | SHARING/ACCESS INFORMATION | | | | | | | | | | | | | | | | Licenses/restrictions placed on the data: None | | | | | | | | | | | | | | | | Links to publications that cite or use the data: Please see the publication associated with these data in XXXXXXXX (doi: XXXXXX) | | | | | | | | | | | | | | | | Recommended citation for this dataset: | | | | | | | | | | | | | | | | Fromenthal | E | S. Rinehart | J.M. Dybiec | and J.A Cherry. Beyond the Marsh: Tidal Marsh Landscape Position Influences Insect Community Structure. Dryad | Dataset | [https://doi.org/XXXXXXXXX](https://doi.org/XXXXXXXXX) | | | | | | | | | | | | | | | | | | DATA &amp; FILE OVERVIEW | | | | | | | | | | | | | | | | File List: | | | | | | | | Taxa- count data for each insect taxon observed at study sites | | | | | | | | Biodiversity- total individuals | taxa richness | and Shannon-Weiner diversity (H') indeces for each quadrat | | | | | | FloralCounts- total count | average count | standard deviation | and variance of Juncus roemerianus inflorescences | | | | | Herbivory- percent area of herbivory damage on J. roemerianus shoots collected from each quadrat in each marsh. | | | | | | | | | | | | | | | | METHODOLOGICAL INFORMATION | | | | | | | | | | | | | | | | Description of methods used for collection/generation of data: See the publication associated with these data in XXXXXXXX (doi: XXXXXX) for details on methods. | | | | | | | | | | | | | | | | Methods for processing the data: See the publication associated with these data in XXXXXXXX (doi: XXXXXX) for details on methods. | | | | | | | | | | | | | | | | Instrument- or software-specific information needed to interpret the data: Microsoft Excel | | | | | | | | | | | | | | | | Environmental/experimental conditions: CON-1 and CON-2 are two constructed tidal marshes hydrologically connected via canal to the West Fowl River in Mobile County | Alabama. NAT is a reference marsh directly connected to the West Fowl River. All marshes are located in a sub-tropical estuary along the northern Gulf fo Mexico. | | | | | | | | | | | | | | | Describe any quality-assurance procedures performed on the data: | | | | | | | | General QA/QC done by all co-authors. | | | | | | | | | | | | | | | | People involved with sample collection | processing | analysis | and/or submission: | | | | | Emily Fromenthal was involved in sample collection | processing | analysis | and submission. | | | | | Shelby Rinehart was involved in sample collection | analysis | and submission. | | | | | | Jacob M Dybiec was involved in sample collection and analysis. | | | | | | | | Julia A Cherry was involved in analysis and submission. | | | | | | | | | | | | | | | | DATA-SPECIFIC INFORMATION FOR: Taxa | | | | | | | | Number of variables: 86 | | | | | | | | Number of cases/rows: 146 | | | | | | | | Missing data codes: No data missing. | | | | | | | | Specialized formats or other abbreviations used: N/A. | | | | | | | | | | | | | | | | Variable List: | | | | | | | | Marsh-indicates the marsh (CON1 | CON2 | or NAT) that data was collected from | | | | | | Month- month that data was collected | | | | | | | | Method- method used to collect data (Pan | Net | Light | FC) | | | | | Quadrat- indicates the replicate quadrat (i.e. | CON1-1 | CON1-2 | etc.) that data was collected from | | | | | Variables E-CH (5-86) represent counts of indiviual taxa identified to the lowest possible taxa (family | in most cases). | | | | | | | | | | | | | | | DATA-SPECIFIC INFORMATION FOR: Biodiversity | | | | | | | | Number of variables: 5 | | | | | | | | Number of cases/rows: 12 | | | | | | | | | | | | | | | | Missing data codes: No missing data. | | | | | | | | Specialized formats or other abbreviations used: | | | | | | | | H'- Shannon-Wiener diversity index; calculated using the formula H^'= - _(i=1)^Rp _i ln p _i | | | | | | | | | | | | | | | | Variable List: | | | | | | | | Marsh- indicates the marsh (CON1 | CON2 | or NAT) that data was collected from | | | | | | Quadrat- indicates the replicate quadrat (i.e. | CON1-1 | CON1-2 | etc.) that data was collected from | | | | | Total Individuals- total count of individual insects per quadrat across all sampling strategies. | | | | | | | | Taxa Richness- number of unique taxa identified per quadrat across all sampling stratagies. | | | | | | | | H'- Shannon-Wiener diversity calculated for each quadrat across all sampling stratagies. | | | | | | | | | | | | | | | | DATA-SPECIFIC INFORMATION FOR: FloralCounts | | | | | | | | Number of variables: 4 | | | | | | | | Number of cases/rows: 37 | | | | | | | | | | | | | | | | Missing data codes: No missing data. | | | | | | | | Specialized formats or other abbreviations used: None | | | | | | | | | | | | | | | | Variable List: | | | | | | | | Marsh- indicates the marsh (CON1 | CON2 | or NAT) that data was collected from | | | | | | Quadrat- indicates the replicate quadrat (i.e. | CON1-1 | CON1-2 | etc.) that data was collected from | | | | | Replicate- inducates which sub-sample from each quadrat is associated with each observation | | | | | | | | Floral count- the number of flowering J. roemerianus shoots in each observation. | | | | | | | | | | | | | | | | DATA-SPECIFIC INFORMATION FOR: Herbivory | | | | | | | | Number of variables: 7 | | | | | | | | Number of cases/rows: 12 | | | | | | | | | | | | | | | | Missing data codes: No missing data. | | | | | | | | Specialized formats or other abbreviations used: N/A | | | | | | | | | | | | | | | | Variable List: | | | | | | | | Quadrat- indicates the replicate quadrat (i.e. | CON1-1 | CON1-2 | etc.) that data was collected from. | | | | | Marsh- notes which tidal wetland site the sample was collected from. | | | | | | | | Herbivory (sq inch)- area of insect herbivory damage/scars in square inches | | | | | | | | Herbivory (cm2)- area of insect herbivory damage/scars per cm2 | | | | | | | | Total area (sq inch)- total size (area) of J. roemerianus shoots in square inches | | | | | | | | Total area (cm2)- total size (area) of of J. roemerianus shoots in cm2. | | | | | | | | % Herbivory- the percent area of J. roemerianus shoots with insect herbivory damage | | | | | | |", "keywords": ["coastal wetlands", "Gulf of Mexico", "Restoration ecology", "insect ecology", "Seasonal variations", "Spatial and landscape ecology", "FOS: Natural sciences", "Species diversity"], "contacts": [{"organization": "Rinehart, Shelby, Fromenthal, Emily, Dybiec, Jacob, Cherry, Julia,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.25338/B8P92J"}, {"rel": "self", "type": "application/geo+json", "title": "10.25338/B8P92J", "name": "item", "description": "10.25338/B8P92J", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.25338/B8P92J"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2024-04-26T00:00:00Z"}}, {"id": "10.5061/dryad.rn8pk0ph1", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:38Z", "type": "Dataset", "title": "Long-term nitrogen deposition inhibits soil priming effects by enhancing phosphorus limitation in a subtropical forest", "description": "unspecifiedThis dataset was collected by sampling soils  exposed to 9 years of manipulative N inputs in situ in a subtropical  forest and then incubating them in a 30-day incubation experiment. The CO2  flux and PE were measured by NaOH trapping. Soil variables were measured  at the end of incubation.", "keywords": ["2. Zero hunger", "SOM decomposition", "13. Climate action", "P limitation", "15. Life on land", "priming effects", "Microbial metabolism", "FOS: Natural sciences", "N deposition"], "contacts": [{"organization": "Wang, Xiaohong, Li, Shiyining, Zhu, Biao, Homyak, Peter M., Chen, Guangshui, Yao, Xiaodong, Wu, Dongmei, Yang, Zhijie, Lyu, Maokui, Yang, Yusheng,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.rn8pk0ph1"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.rn8pk0ph1", "name": "item", "description": "10.5061/dryad.rn8pk0ph1", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.rn8pk0ph1"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-04-19T00:00:00Z"}}, {"id": "10.3929/ethz-b-000640921", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:18Z", "type": "Journal Article", "title": "Mineral transformations of ferrihydrite and lepidocrocite in suspension and in paddy soil: A closer look at the effects of silicate, phosphate, and the soil matrix", "description": "unspecifiedIron (Fe) (oxyhydr)oxides, such as ferrihydrite and lepidocrocite, are ubiquitous in soils. Due to their high surface area, Fe (oxyhydr)oxides constitute important sorbents for nutrients and contaminants in the soil, including silicate and phosphate. Under sub- or anoxic conditions in water-saturated or submerged soils, Fe(III) acts as an alternative electron acceptor during the microbial metabolization of organic matter. This leads to the reductive dissolution of Fe (oxyhydr)oxides, the formation of Fe(II) and the potential release of adsorbed components. The presence of Fe(II) accelerates the transformation of ferrihydrite and lepidocrocite to more crystalline Fe minerals, such as goethite or magnetite. Silicate and phosphate can interfere with these mineral transformations. However, how silicate and phosphate impact the trajectory and mineral products of ferrihydrite and lepidocrocite transformation has not been fully resolved yet. Up to now, Fe mineral transformations have mainly been studied in simplified model systems, such as mineral suspensions, but rarely in soil. Further, transformations of ferrihydrite and lepidocrocite in soils during redox cycles, including the recurring reduction and oxidation of Fe, remain obscure. Redox active soils include paddy soils which are crucial for the global production of rice as a staple food. This thesis investigated factors that govern Fe (oxyhydr)oxide transformations in redox active paddy soils. The doctoral project was designed to move consecutively from controlled laboratory to in-situ field experiments. In all experiments, the stable isotope 57Fe was used as a tracer in combination with isotope analysis of dissolved and solid phases and/or 57Fe M\u00f6ssbauer spectroscopy.  In the first part of this thesis, the effect of silicate on Fe(II)-catalyzed transformation of ferrihydrite and lepidocrocite was examined in mineral suspensions spiked with 57Fe(II) at two Fe(II):Fe(III) molar ratios. The reactivity of ferrihydrite towards 57Fe(II) adsorption and Fe atom exchange with dissolved 57Fe(II) was only marginally impacted by coprecipitated silicate. Silicate hindered ferrihydrite transformation to goethite and magnetite as compared to silicate-free ferrihydrite. During mineral transformation, coprecipitated silicate led to the formation of thicker lepidocrocite crystallites from ferrihydrite and silicate was redistributed in the solid phase. For lepidocrocite, magnetite formed at the higher Fe(II):Fe(III) molar ratio. This contrasts the decreased Fe atom exchange and inhibited mineral transformation in the presence of surface-adsorbed silicate on lepidocrocite surfaces. The results demonstrate that silicate strongly interferes with Fe mineral transformations whereas the mineral reactivity towards Fe(II) adsorption and Fe atom exchange can remain high.  In a following experiment, the transformation of ferrihydrite and lepidocrocite during three redox cycles was studied in laboratory mesocosms filled with paddy soil. To understand the effect of the soil matrix on mineral transformations, minerals were incubated either as minerals without the addition of soil or as 57Fe-labeled mineral-soil mixes in mesh bags. The results showed that ferrihydrite and lepidocrocite transformed to goethite and/or magnetite when incubated as mineral mesh bags without soil. When ferrihydrite and lepidocrocite were mixed with soil, a mixed valent and highly disordered Fe phase formed. Goethite additionally formed in lepidocrocite-soil mixes. Throughout repeated redox cycles, solid-associated Fe(II) fractions in mineral-soil mixes during anoxic periods increased, suggesting an increasing extent of Fe mineral reduction. The outcomes of this study showed that Fe mineral transformations are strongly impacted when minerals are exposed to the soil matrix, which can lead to highly disordered instead of crystalline Fe mineral transformation products.  In a final experiment, the in-situ transformation of Fe oxyhydroxides and the effect of phosphate were investigated in a field-incubation of minerals in a flooded rice paddy soil in Thailand. Ferrihydrite, lepidocrocite and phosphate-adsorbed ferrihydrite were incubated using mesh bags, containing the minerals without soil or 57Fe-labeled mineral-soil mixes. The field-incubation of ferrihydrite and lepidocrocite in mineral mesh bags without soil resulted in goethite formation with a much larger transformation extent in ferrihydrite. With pre-adsorbed phosphate, the transformation of ferrihydrite was strongly hindered. In mineral-soil mixes ferrihydrite and lepidocrocite transformed to goethite to a similar extent. Pre-adsorbed phosphate on ferrihydrite surfaces strongly hindered mineral transformation in the mineral-soil mixes but enhanced Fe reduction compared to phosphate-free ferrihydrite. These findings demonstrate the dual role of phosphate during mineral transformations when minerals are closely associated or in direct contact with the soil matrix.  The outcomes of this thesis highlight the importance of considering silicate and phosphate interactions with Fe (oxyhydr)oxides, by demonstrating their strong impact on the trajectory of mineral transformations. Mineral transformations in soil have been shown in this thesis to be much slower compared to mineral suspension experiments. Further, when minerals are closely associated or in direct contact with the soil matrix, highly disordered Fe phases can form instead of crystalline Fe minerals. Such disordered Fe phases can be highly reactive, as this work demonstrated for the exposure to redox cycles. Collectively, the gained insights contribute to a better assessment of Fe cycling in redox-active soils which can control nutrient and contaminant mobility in the environment.", "keywords": ["Transformations", "Field study", "iron reduction", "15. Life on land", "laboratory study", "6. Clean water", "Lepidocrocite", "Natural sciences", "Ferrihydrite", "Rice paddy", "Redox reactions", "iron minerals", "FOS: Natural sciences", "info:eu-repo/classification/ddc/500"], "contacts": [{"organization": "Schulz, Katrin", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.3929/ethz-b-000640921"}, {"rel": "related", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/Thesis/Dissertation", "name": "related record", "description": "related record", "type": "application/json"}, {"rel": "self", "type": "application/geo+json", "title": "10.3929/ethz-b-000640921", "name": "item", "description": "10.3929/ethz-b-000640921", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.3929/ethz-b-000640921"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-01-01T00:00:00Z"}}, {"id": "10.5061/dryad.1g1jwsv29", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:27Z", "type": "Dataset", "created": "2023-06-26", "title": "Summer litter decomposition is moderated by scale-dependent microenvironmental variation in tundra ecosystems", "description": "unspecifiedTundra soils are one of the world\u2019s largest organic carbon stores, yet  this carbon is vulnerable to accelerated decomposition as climate warming  progresses. The landscape-scale controls of litter decomposition are  poorly understood in tundra ecosystems, which hinders our understanding of  the global carbon cycle. We examined the extent to which the thermal sum  of surface air temperature, soil moisture and permafrost thaw depth  influenced litter mass loss and decomposition rates (k), and at which  spatial thresholds an environmental variable becomes a reliable predictor  of decomposition, using the Tea Bag Index protocol across a heterogeneous  tundra landscape on Qikiqtaruk - Herschel Island, Yukon, Canada. We found  greater green tea litter mass loss and faster decomposition rates (k) in  wetter areas within the landscape, and to a lesser extent in areas with  deeper permafrost active layer thickness and higher surface thermal sums.  We also found higher decomposition rates (k) on north-facing relative to  south-facing aspects at microsites that were wetter rather than warmer.  Spatially heterogeneous belowground conditions (soil moisture and active  layer depth) explained variation in decomposition metrics at local scales  (&lt; 50 m2) better than thermal sum. Surprisingly, there was no  strong control of elevation or slope on litter decomposition. Our results  reveal that there is considerable scale dependency in the environmental  controls of tundra litter decomposition, with moisture playing a greater  role than the thermal sum at &lt; 50 m2 scales. Our findings highlight  the importance and complexity of microenvironmental controls on litter  decomposition in estimates of carbon cycling in a rapidly warming tundra  biome.", "keywords": ["Decomposition", "litter", "13. Climate action", "moisture", "ecosystem change", "tea bag index", "Temperature", "Climate change", "carbon cycling", "15. Life on land", "Tundra", "FOS: Natural sciences", "microclimate"], "contacts": [{"organization": "Gallois, Elise", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.1g1jwsv29"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.1g1jwsv29", "name": "item", "description": "10.5061/dryad.1g1jwsv29", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.1g1jwsv29"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-07-03T00:00:00Z"}}, {"id": "10.5061/dryad.3n5tb2rmr", "type": "Feature", "geometry": null, "properties": {"license": "unspecified", "updated": "2026-04-13T16:22:28Z", "type": "Dataset", "title": "Data for: Inundation depth stimulates plant-mediated CH4 emissions by increasing ecosystem carbon uptake and plant height in an estuarine wetland", "description": "Plant-mediated CH4 emission is an important part of the ecosystem CH4  emission from vegetated wetlands. Inundation depth may alter the potential  magnitude of CH4\u00a0releases by changing CH4\u00a0production and  plant transport, but the relationships between plant-mediated  CH4\u00a0emissions and inundation depth are still uncertain,  especially for estuarine wetlands with changeable hydrological processes.  Besides, there are conflicting results regarding the role of inundation  depth in plant-mediated CH4\u00a0emissions. Here we conducted a novel  inundation depth experiment (0, 5, 10, 20, 30 and 40 cm inundation depth)  dominated by Phragmites australis in the Yellow River estuary, China. Soil  CH4\u00a0emissions, ecosystem CH4\u00a0emissions, net ecosystem  CO2 exchange (NEE), soil organic carbon (SOC) and plant traits were  measured during the growing seasons of 2018, 2019 and 2020. Plant-mediated  CH4\u00a0emissions were the difference between ecosystem  CH4\u00a0emissions and soil CH4\u00a0emissions. The results showed  that inundation depth decreased soil CH4\u00a0emissions but increased  ecosystem CH4\u00a0emissions. Plant-mediated CH4\u00a0transport  from Phragmites australis accounted for 99% of total ecosystem  CH4\u00a0emissions under different inundation depths. Inundation depth  strongly stimulated plant-mediated CH4\u00a0emission from 0 to 20 cm  during the growing seasons. The increased net ecosystem CO2 exchange  enhanced plant-mediated CH4\u00a0emissions by altering production,  suggesting that carbon components derived from photosynthetic carbon input  may benefit CH4\u00a0production. Additionally, the increased plant  height promoted CH4\u00a0emission by regulating plant transport,  indicating that plant traits may play an important role in transport of  CH4. Our findings indicated that NEE and plant height play an important  role in plant-mediated CH4\u00a0emissions under different inundation  depths in estuarine wetland. This study also highlights that hydrological  regimes and plant traits are essential for the estimation of  CH4\u00a0emissions in future projections of global wetland changes.", "keywords": ["13. Climate action", "15. Life on land", "6. Clean water", "FOS: Natural sciences"], "contacts": [{"organization": "Zhao, Mingliang, Li, Peiguang, Song, Weimin, Chu, Xiaojing, Eller, Franziska, Wang, Xiaojie, Liu, Jingtao, Xiao, Leilei, Wei, Siyu, Li, Xinge, Han, Guang-Xuan,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.3n5tb2rmr"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.3n5tb2rmr", "name": "item", "description": "10.5061/dryad.3n5tb2rmr", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.3n5tb2rmr"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-12-19T00:00:00Z"}}, {"id": "10.5061/dryad.66t1g1k7n", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:30Z", "type": "Dataset", "created": "2023-12-05", "title": "Biotic and abiotic properties of biocrus", "description": "unspecifiedEukaryotic algae, as the primary group of photosynthetic autotrophs, exert  a significant influence on the development and functions of biological  crusts in dryland ecosystems. Despite their importance, there are  substantial knowledge gaps on the composition of eukaryotic algal  communities and their effects on the distributions of bacteria and fungi  in dryland soils. This study examined the eukaryotic algal community along  a successional sequence of biocrusts in the Gurbantunggut desert, while  also investigating their patterns of co-occurrence with bacteria and fungi  through high-throughput sequencing and bioinformatic analyses. The results  showed that nitrogen and phosphorus levels played a crucial role in the  regulation of changes in the abundance and composition of the algal  community. In particular, changes in the structure of the algal community  arise primarily from fluctuations in the main species, rather than from  loss and appearance of species during the biocrust succession. The  accumulation of nitrogen and phosphorus in the biocrust led to increases  in the relative abundance of algal species in the Chlorophyta. The results  also indicated that eukaryotic algae played an important role in affecting  bacterial and fungal communities and significantly improved the stability  of the microbial community, reflected by the robustness of co-occurrence  networks. The network analysis further indicated that eukaryotic algae  affected the stability of microbial co-occurrence networks either by  acting as keystone taxa or associating with the keystone bacterial and  fungal taxa. These findings reveal a clear mechanism by which soil  nitrogen and phosphorus levels affected the composition of eukaryotic  algae communities and further regulated bacterial and fungal communities  during biocrust development, providing valuable information on the  development and functional execution of biocrusts in dryland ecosystems.", "keywords": ["2. Zero hunger", "Microbial ecology", "Succession of biocrusts", "13. Climate action", "Physicochemical properties", "15. Life on land", "FOS: Natural sciences"], "contacts": [{"organization": "Zhao, Kang", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.66t1g1k7n"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.66t1g1k7n", "name": "item", "description": "10.5061/dryad.66t1g1k7n", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.66t1g1k7n"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-12-12T00:00:00Z"}}, {"id": "10.5061/dryad.8931zcrwj", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:31Z", "type": "Dataset", "created": "2023-07-04", "title": "Data from: Litter quality controls tradeoffs in soil carbon decomposition and replenishment in a subtropical forest", "description": "Species-rich forests can produce litter of varying carbon (C) and nitrogen  (N) composition (i.e., quality), which can affect decomposition and play a  central role in long-term soil organic carbon (SOC) accumulation. However,  how differences in litter quality affect SOC decomposition and formation  remains unclear over the full litter decomposition trajectory.\u00a0  We followed the in-situ complete decomposition of added 13C-labelled high-  (low C:N) and low-quality (high C:N) leaf-litter and its effect on  particulate (POM) and mineral-associated (MAOM) organic matter fractions  over two years in a natural subtropical forest. We found that during early  stages of decomposition, low-quality litter inputs decreased SOC via a  positive priming effect (i.e., new C inputs favored decomposition of  native SOC), but these SOC losses were offset by SOC gains observed via a  negative priming effect during decomposition of high-quality litter. In  contrast, this pattern reversed during late stages of decomposition\u2014SOC  losses via a positive priming effect induced by high-quality litter were  offset by SOC gains via a negative priming effect induced by low-quality  litter. Over the full decomposition of litter, both high- and low-quality  litter stimulated microbial breakdown of SOC tied to POM, but also  replenished more persistent SOC that associated with soil minerals (MAOM).  Altogether, we observed that low-quality litter formed twice as much new  SOC as high-quality litter (24% vs. 12% of added litter-C). We extend the  notion of the priming effect\u00a0from primarily a negative role  promoting losses of native SOC, to a functional role that can replenish  persistent SOC. Synthesis. Our measurements raise the possibility that, in  species-rich forests, high- and low-quality litter decomposition play  opposite but dynamically complementary roles in renewing POM\u2014both by  inducing its decomposition and formation\u2014while exclusively favoring MAOM  formation, which can help explain how differences in litter quality favor  SOC accumulation and persistence. Global change factors that shift plant  community composition may ultimately affect the fate of soil C, as changes  in litter quality may force soil transitions from sinks to sources or  sources to sinks of atmospheric CO2.", "keywords": ["complementary effect", "species-rich forests", "13C-labelled tree litter", "isotope tracer field experiment", "15. Life on land", "Priming effect", "litter-quality", "FOS: Natural sciences"], "contacts": [{"organization": "Lyu, Maokui, Homyak, Peter, Xie, Jinsheng, Pe\u00f1uelas, Josep, Ryan, Michael, Xiong, Xiaoling, Sardans, Jordi, Lin, Weisheng, Wang, Minhuang, Chen, Guangshui, Yang, Yusheng,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.8931zcrwj"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.8931zcrwj", "name": "item", "description": "10.5061/dryad.8931zcrwj", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.8931zcrwj"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-07-10T00:00:00Z"}}, {"id": "10.5061/dryad.7wm37pw23", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:31Z", "type": "Dataset", "created": "2024-06-13", "title": "Data from: Patterns and drivers of atmospheric nitrogen deposition retention in global forests", "description": "unspecified# Patterns and drivers of atmospheric nitrogen deposition retention in  global forests We searched the Web of Science Database for peer-reviewed  papers prior to February 22, 2023, using \u201cretention\u201d and \u201cN-15\u201d as the  keywords. The following criteria were applied to filter the peer-reviewed  papers: (1) Selection of 15N tracer experiments in forest ecosystems  conducted in the field, excluding laboratory incubation or greenhouse  experiments; (2) Selection of the absolute value of 15N retention obtained  from the 15N tracer experiment, excluding the relative value; (3)  Selection of 15N tracer experiments including N addition treatments,  excluding other treatments such as fire, phosphorus (P) addition,  potassium addition, etc. Due to limited data on litter layers and  understory vegetation components (i.e., shrubs, herbs, and grasses), the  15N retention of litter layers was combined into organic soil 15N  retention. Within the entire forest ecosystem, the 15N retention of  understory vegetation was not consider, focusing instead on the 15N  allocation among different plant organs (i.e., leaves, branches, stems,  roots). Ultimately, 408 observations were obtained from 56 peer-reviewed  papers, totaling 62 sites and 92 site-years. The study sites were  distributed across North America (25 sites), Europe (14 sites), Asia (14  sites), South America (3 sites), Oceania (4 sites), and Africa (2 sites),  covering tropical forests (5 sites), subtropical forests (10 sites),  temperate forests (42 sites), and boreal forests (5 sites). Raw data for  15N retention of different ecosystem compartments were obtained from  tables, figures, results, or supplementary information in the  peer-reviewed papers. When data were presented in figures, specific values  were extracted using Getdata software 2.22 (GetData, Kogarah, NSW, AUS).  Note: N_retention_data_v2 is based on N_retention_data_v1, with the  addition of raw data. 'XX' in the 'forest_type' and  '15N_tracer_type' sheets represents the 15N retention in  different ecosystem compartments (i.e., plant, leaf, branch, stem, root,  soil, organic soil, mineral soil, and total ecosystem).\u00a0'XX_n'  in the 'forest_type' and '15N_tracer_type' sheets  represents the sample size of 'XX'.\u00a0'XX_mean' in the  'forest_type' and '15N_tracer_type' sheets represents  the mean value of 'XX'.\u00a0'XX_se' in the  'forest_type' and '15N_tracer_type' sheet represents  the standard error of the mean value of 'XX'. 'NA' in  the 'raw_data' sheet represents unavailable observed data.  'MAT_CRU' and 'MAP_CRU' columns of the  'raw_data' sheet indicate that the missing values in the  references are extracted from the CRU.", "keywords": ["ammonium", "nitrogen retention", "15N tracer", "plant organs", "nitrate", "nitrogen allocation", "Forest", "FOS: Natural sciences"], "contacts": [{"organization": "Lin, Quanhong, Zhu, Jianxing, Wang, Qiufeng, Zhang, Qiongyu, Yu, Guirui,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.7wm37pw23"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.7wm37pw23", "name": "item", "description": "10.5061/dryad.7wm37pw23", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.7wm37pw23"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2024-06-23T00:00:00Z"}}, {"id": "10.5061/dryad.931zcrjtp", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:31Z", "type": "Dataset", "created": "2024-06-03", "title": "Carbon sequestration in intact rare ecosystems and their encroaching forests (Michigan, USA)", "description": "unspecifiedRising atmospheric carbon dioxide levels are impacting global  temperatures, ecological systems, and human societies. Natural carbon  sequestration through the conservation of soil and native ecosystems may  slow or reduce the amount of CO2 in the atmosphere, and thus slow or  mitigate the rate of global warming. Most of the research investigating  carbon sequestration in natural systems occurs in forested ecosystems,  however rare ecosystems such as coastal plain marshes and wet-mesic sand  prairie collectively may serve as significant carbon sinks. Our objectives  were to measure and assess the importance of carbon sequestration in three  rare ecosystems (oak-pine barrens, coastal plain marsh, and wet-mesic sand  prairie) in western Lower Michigan. We measured carbon in standing  vegetation, dead organic matter, and soils within each ecosystem and  adjacent encroaching forested areas. Driven by tree carbon, total carbon  stocks in encroaching areas were greater than in intact rare ecosystems.  Soil organic carbon was greater in all intact ecosystems, though only  significantly so in coastal plain marsh.\u00a0 Principal components  analysis explained 72% of the variation and revealed differences between  intact ecosystems and their encroaching areas. Linear models using the  ratio of red to green light reflectance successfully predicted SOC in  intact coastal plain marsh and wet-mesic sand prairie. Our results infer  the importance of these rare ecosystems in sequestering carbon in soils  and support the need to establish federal or state management practices  for the conservation of these systems.", "keywords": ["Carbon sequestration", "rare ecosystems", "coastal plain marsh", "Climate change", "oak-pine barrens", "FOS: Natural sciences", "wet-mesic sand prairie"], "contacts": [{"organization": "Woller-Skar, Meg, Locher, Alexandra, Audia, Ellen,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.931zcrjtp"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.931zcrjtp", "name": "item", "description": "10.5061/dryad.931zcrjtp", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.931zcrjtp"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2024-06-17T00:00:00Z"}}, {"id": "10.5061/dryad.9s4mw6mks", "type": "Feature", "geometry": null, "properties": {"license": "unspecified", "updated": "2026-04-13T16:22:32Z", "type": "Dataset", "title": "Soil microbes respond to four-year warming and precipitation alteration", "description": "unspecifiedSoil temperature and moisture were  automatically monitored by 5-TM probe sensors at the soil depth of 5 cm  with an EM-to data logger (Meter, Inc., Pullman, WA, USA) in each  plot.\u00a0 Soil aerobic respiration (soil CO<sub>2</sub>  flux) was automatically measured once an hour by the LI-8150 Multiplexer  composed of LI -8100-104 long-term chambers (Li-Cor Inc., Lincoln, NE,  USA) and a LI-8100 Automated soil CO<sub>2</sub> flux system  (Wang<em> et al.</em>,  2014). As for soil CH<sub>4</sub> fluxes, gas  samples were collected from all plots twice or three times per month  between 9:00 a.m. and 12:00 p.m. on sunny days (Qi et al., 2021).  Specifically, a stainless steel collar was inserted 10 cm into the soil in  each plot and a static opaque chamber (40 cm in length  \u00b4 40 cm in width \u00b4 40 cm in height) was used to collect gas samples from soil at this site (Yuan<em> et al.</em>, 2021). At each measurement, 60 mL gas sample was collected in each plot and analyzed within 24 hours using gas chromatography (Agilent 7890A; Agilent Technologies, Santa Clara, CA, USA) to present a one-day average flux. Similar with soil CH<sub>4</sub> fluxes, ecosystem C fluxes were also measured twice or three times per month between 9:00 a.m. and 12:00 p.m. on sunny days (Qi<em> et al.</em>, 2021). We used a LI-6400 infrared gas analyzer (LI-COR, Inc., Lincoln, NE, USA) with a transparent chamber (0.4 m in length \u00d7 0.4 m in width \u00d7 0.6 m in height) to measure net ecosystem CO<sub>2</sub> exchange (NEE). Ecosystem respiration (ER) was measured by using the similar method with the transparent chamber covered by an opaque cloth. Gross ecosystem production (GEP) was estimated as the difference between NEE and ER (Qi<em> et al.</em>, 2021). In this study, the more negative NEE represents more CO<sub>2</sub> sequestration by terrestrial ecosystem.", "keywords": ["2. Zero hunger", "13. Climate action", "soil microbes", "Global warming", "15. Life on land", "FOS: Natural sciences"], "contacts": [{"organization": "Qi, Qi, Zhao, Jianshu, Tian, Renmao, Zeng, Yufei, Xie, Changyi, Gao, Qun, Dai, Tianjiao, Wang, Hao, He, Jin-Sheng, Konstantinidis, Konstantinos, Yang, Yunfeng, Zhou, Jizhong, Guo, Xue,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.9s4mw6mks"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.9s4mw6mks", "name": "item", "description": "10.5061/dryad.9s4mw6mks", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.9s4mw6mks"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-09-25T00:00:00Z"}}, {"id": "10.5061/dryad.c59zw3rf9", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:33Z", "type": "Dataset", "created": "2023-09-28", "title": "Fungal necromass is reduced by intensive drought in subsoil but not in topsoil", "description": "unspecifiedFungal necromass is reduced by intensive drought in subsoil but not in  topsoil [Access this dataset on Dryad] (DOI: 10.5061/dryad.c59zw3rf9) A  drought simulation experiment was conducted on a poplar plantations in  Jiangsu, China. In this study, the precipitation input was controlled by  the rain canopy to simulate different drought conditions. We established  three treatments, including a control without throughfall reduction (CK);  moderate treatment with a 30% throughfall reduction (D30%); and intensive  treatment with a 50% throughfall reduction (D50%). Each treatment was set  up with three replicates for a total of nine plots. Soil samples were  extracted from all nine plots in 2021 (January in Winter, April in Spring,  July in Summer, and October in Autumn). The soil samples collected for  each plot are divided into 0-15cm topsoil and 15-30cm subsoil. We measured  the content of microbial necromass in these soil samples as well as soil  properties. Based on these data, we analyzed the ecological correlations  between soil depth, drought intensity, soil properties and microbial  necromass. ## Description of the data and file structure This dataset  showed the raw data we used in the manuscript. [Treatments] CK means soil  samples without throughfall removal, D30% means soil samples with 30%  throughfall removal, and D50% implies soil samples with 50% throughfall  removal. [Variables] Temp means soil temperature, Mois means soil  moisture, FNC means fungal necromass carbon , BNC means beterial necromass  carbon and TNC means total necromass carbon. The TNC=FNC+BNC. [Seasons]  Win: Winter (January, 2021); Spr: Spring (April, 2021); Sum: Summer (July,  2021); Aut: Auntumn (October, 2021).  *These data is aggregated in an  Excel file that can be accessed and observed in the corresponding tabs. ##  Code/Software This data file can be opened and accessed using Microsoft  Excel.", "keywords": ["2. Zero hunger", "soil organic carbon", "fungal necromass", "13. Climate action", "soil depth", "bacterial necromass", "15. Life on land", "throughfall removal", "6. Clean water", "FOS: Natural sciences"], "contacts": [{"organization": "Liu, Yuwei, Zou, Xiaoming, Chen, Han, Baquerizo, Manuel Delgado, Wang, Cuiting, Zhang, Chen, Ruan, Honghua,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.c59zw3rf9"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.c59zw3rf9", "name": "item", "description": "10.5061/dryad.c59zw3rf9", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.c59zw3rf9"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-10-02T00:00:00Z"}}, {"id": "10.5061/dryad.dncjsxm31", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:33Z", "type": "Dataset", "title": "Local temperature increases reduce soil microbial residues and carbon stocks", "description": "Warming is known to reduce soil carbon (C) stocks by promoting microbial  respiration, which is associated with the decomposition of microbial  residue C (MRC). However, the relative contribution of MRC to soil organic  C (SOC) across temperature gradients\u00a0is poorly understood. Here,  we investigated the contribution of MRC to SOC along two independent  elevation gradients\u00a0of our model system (i.e., the Tibetan  Plateau and Shennongjia Mountain in China). Our results showed that local  temperature increases were negatively correlated with MRC and SOC. Further  analyses revealed that rising temperature reduced SOC via decreasing  MRC,\u00a0which helps to explain future reductions in SOC under  climate warming. Our findings\u00a0demonstrate that climate warming  has the potential to reduce C sequestration\u00a0by  increasing\u00a0the decomposition\u00a0of MRC, exacerbating the  positive feedback between rising temperature and CO2\u00a0efflux. Our  study also considered the influence of multiple environmental factors such  as soil pH and moisture, which were more important in controlling SOC than  microbial traits such as microbial life-style strategies and metabolic  efficiency. Together, our work suggests an important mechanism underlying  long-term soil C sequestration, which has important implications for the  microbial-mediated C process in the face of global climate change.", "keywords": ["13. Climate action", "15. Life on land", "FOS: Natural sciences"], "contacts": [{"organization": "Zeng, Xiao-Min, Feng, Jiao, Yu, Dai-Lin, Wen, Shu-Hai, Zhang, Qianggong, Huang, Qiaoyun, Delgado-Baquerizo, Manuel, Liu, Yu-Rong,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.dncjsxm31"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.dncjsxm31", "name": "item", "description": "10.5061/dryad.dncjsxm31", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.dncjsxm31"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-07-26T00:00:00Z"}}, {"id": "10.5061/dryad.gtht76hqs", "type": "Feature", "geometry": null, "properties": {"license": "unspecified", "updated": "2026-04-13T16:22:34Z", "type": "Dataset", "title": "Soil microbial biomass C, N in biocrust: A meta-analysis", "description": "The biological soil crust (biocrust) has many crucial ecological functions  in dryland ecosystems. Differentiation of soil microbial biomass in  different ecosystems\u2019 biocrust under various climatic and soil conditions  remains unknown, restricting our knowledge of biocrust microbiomes  regulating terrestrial carbon and nitrogen cycling globally. We selected  255 paired observations from 45 global study sites for meta-analysis to  quantify the effect of biocrust type, soil texture, and ecosystem type on  soil microbial biomass in biocrust and identify the underlying impact  factors. The results showed that biocrust had significantly higher soil  microbial carbon and nitrogen contents (SMBC and SMBN, respectively) than  bare (non-crust) soil (P &lt; 0.05). Biocrust also significantly  increased total nitrogen (TN) (143.68%), soil organic carbon (SOC) and TN  ratio (C: N) (9.93%), and soil water content (SWC) (60.18%), and decreased  pH (0.72%) (P &lt; 0.05). Overall, the SMBC significantly differed  between biocrust type, ecosystem type, and soil texture (P &lt; 0.05).  Compared with other biocrust types, lichen crust had the strongest  positive effect on SMBC (822.48%). Grassland ecosystems had stronger  positive effects on SMBC in biocrust than forest ecosystems, and sand and  sandy loam soils had higher SMBC in biocrust than loam soils. Notably,  altitude drives the positive effects of biocrust on SMBN and the negative  effects of biocrust on SMBC and SMBC and SMBN ratio (SMBC: SMBN). Mean  annual temperature (MAT) positively affected SMBC based on regression  analysis. Further analysis revealed that SMBC and SMBN positively  correlated with SOC, C: N, SWC, and urease activity and negatively  correlated with pH. The random forest analysis confirmed that SOC, C: N,  and altitude could be considered determinants of SMBC, SMBN, and SMBC:  SMBN, respectively. Climatic factors and soil nutrients differently  affected soil microbial biomass C, N and their ratio in biocrust. The high  contribution of lichen crust to SMBC should be incorporated into regional  and global models to predict the effects of climate change on soil carbon  budgets in ecosystems worldwide.", "keywords": ["2. Zero hunger", "13. Climate action", "15. Life on land", "FOS: Natural sciences"], "contacts": [{"organization": "Tian, Chang", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.gtht76hqs"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.gtht76hqs", "name": "item", "description": "10.5061/dryad.gtht76hqs", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.gtht76hqs"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-12-02T00:00:00Z"}}, {"id": "10.5061/dryad.jwstqjqc0", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:36Z", "type": "Dataset", "title": "More soil organic carbon is sequestered through the mycelium-pathway than through the root-pathway under nitrogen enrichment in an alpine forest", "description": "Open AccessPeer reviewed", "keywords": ["roots", "SOC sequestration", "ectomycorrhizal mycelia", "Alpine forests", "15. Life on land", "Roots", "alpine forests", "6. Clean water", "N deposition", "Ectomycorrhizal mycelia", "Natural sciences", "microbial C pump", "Microbial C pump", "FOS: Natural sciences"], "contacts": [{"organization": "Zhu, Xiaomin, Zhang, Ziliang, Wang, Qitong, Pe\u00f1uelas, Josep, Sardans, Jordi, Li, Na, Liu, Qing, Yin, Huajun, Liu, Zhanfeng, Lambers, Hans,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.jwstqjqc0"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.jwstqjqc0", "name": "item", "description": "10.5061/dryad.jwstqjqc0", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.jwstqjqc0"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-01-01T00:00:00Z"}}, {"id": "10.5061/dryad.mgqnk992r", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:36Z", "type": "Dataset", "title": "Effects of land clearing for agriculture on soil organic carbon stocks in drylands: A meta-analysis", "description": "To improve our understanding of clearing natural ecosystems for cropland  on soil organic carbon stocks in drylands, we searched for related  peer-reviewed research papers published from 1980 to 2022 on the Web of  Science (https://www.webofscience.com) and the Scopus Database  (https://www.scopus.com) (accessed on 30th April 2022). Then, we screened  papers for integrity, relevance, and scientific merit under the following  criteria: (1) We made sure all studies were independent and based on  field-measured data; (2) Each study had to report paired SOC stocks of  cropland and adjacent natural ecosystems with the same or a similar suite  of environmental factors; (3) Studies need to explicitly present results  on SOC stocks or concentrations for certain depths and areas; (4) Studies  have specified the types of natural ecosystems that were converted to  cropland, which are used as criteria for defining CNEC types. Finally, we  winnowed results to a total of 159 scientific journal articles, comprising  242 sites with 1379 paired soil layer observations from 601 paired soil  profiles.", "keywords": ["2. Zero hunger", "soil organic carbon", "meta-analysis", "drylands", "13. Climate action", "cropland", "15. Life on land", "Clearing natural ecosystems", "FOS: Natural sciences"], "contacts": [{"organization": "Wang, Yuangang, Luo, Geping, Li, Chaofan, Ye, Hui, Shi, Haiyang, Fan, Binbin, Zhang, Wenqiang, Zhang, Chen, Xie, Mingjuan, Zhang, Yu,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.mgqnk992r"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.mgqnk992r", "name": "item", "description": "10.5061/dryad.mgqnk992r", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.mgqnk992r"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-10-24T00:00:00Z"}}, {"id": "10.5061/dryad.mpg4f4r3b", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:36Z", "type": "Dataset", "title": "Changing plant species composition and richness benefit soil carbon sequestration under climate warming", "description": "Anthropogenic warming and land-use change are expected to accelerate  global soil organic carbon (SOC) losses and change plant species  composition and richness. However, how changes in plant composition and  species richness mediate SOC responses to climate warming and land-use  change remains poorly understood. Using data from a 7-year warming and  clipping field experiment in an alpine meadow on the Qinghai-Tibetan  Plateau, we examined the direct effects of warming and clipping on SOC  storage versus their indirect effects mediated by plant functional type  and species richness. We found that warming significantly increased SOC  storage by 8.1% and clipping decreased it by 6.4%, which was closely  correlated with the corresponding response of below-ground net primary  productivity (BNPP). We also found a negative correlation between SOC  storage and species richness, which was ascribed to the increased BNPP via  enhancing the dominance of grasses and decreasing species richness under  warming. The lower SOC storage under clipping was caused by the  clipping-induced decrease in BNPP via weakening the dominance of grasses  and increasing species richness. Our findings highlight that the SOC  storage in this alpine meadow under climate warming and clipping was  primarily governed by BNPP, which was mediated by changes in the dominance  of grasses and species richness. Overall, our study demonstrates that  shifting to the dominance of grasses and changing species richness would  benefit soil C sequestration under climate warming, but this positive  effect would be dampened by grazing or hay harvest.", "keywords": ["2. Zero hunger", "soil organic carbon", "dominant functional type", "13. Climate action", "Land-use change", "14. Life underwater", "15. Life on land", "species richness", "FOS: Natural sciences", "climate warming"], "contacts": [{"organization": "Yan, Yingjie, Niu, Shuli, He, Yicheng, Wang, Song, Song, Lei, Peng, Jinlong, Chen, Xinli, Quan, Quan, Meng, Cheng, Zhou, Qingping, Wang, Jinsong,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.mpg4f4r3b"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.mpg4f4r3b", "name": "item", "description": "10.5061/dryad.mpg4f4r3b", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.mpg4f4r3b"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-10-11T00:00:00Z"}}, {"id": "10.5061/dryad.sbcc2frbh", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:38Z", "type": "Dataset", "title": "Root functional traits determine the magnitude of the rhizosphere priming effect among eight tree species", "description": "Rhizosphere priming effect\u00a0can accelerate or decelerate the  decomposition of soil organic matter.\u00a0Using a natural abundance  13C tracer method allowing partitioning of native soil organic carbon  (SOC) decomposition and plant rhizosphere respiration, we studied the  effects of eight tree species on the strength of the rhizosphere priming.  All tree species enhanced the rate of SOC decomposition, by 82% on  average.\u00a0Mean diameter of first-order roots and root  exudate-derived respiration were positively correlated with the RPE,  together explaining a large part of the observed variation in the RPE (R2  = 0.72), whereas root branching density was negatively associated with the  RPE. Path analyses further suggested that mean diameter of first-order  roots was the main driver of the RPE owing to its positive direct effect  on the RPE and its indirect effects via root exudate-derived respiration  and root branching density. These results demonstrate that the magnitude  of the RPE is regulated by complementary aspects of root morphology,  architecture and physiology, implying that comprehensive approaches are  needed to reveal the multiple mechanisms driving plant effects on the RPE.", "keywords": ["13C natural abundance", "Plant functional traits", "rhizosphere priming effect", "Fine roots", "15. Life on land", "FOS: Natural sciences"], "contacts": [{"organization": "Chao, Lin, Liu, Yanyan, Zhang, Weidong, Wang, Qingkui, Guan, Xin, Yang, Qingpeng, Chen, Longchi, Zhang, Jianbing, Hu, Baoqing, Liu, Zhanfeng, Wang, Silong, Freschet, Gr\u00e9goire T.,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.sbcc2frbh"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.sbcc2frbh", "name": "item", "description": "10.5061/dryad.sbcc2frbh", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.sbcc2frbh"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-02-20T00:00:00Z"}}, {"id": "10.5061/dryad.s4mw6m9bc", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:38Z", "type": "Dataset", "title": "Divergent responses of grassland productivity and plant diversity to intra-annual precipitation variability across climate regions: A global synthesis", "description": "Global warming intensifies the hydrological cycle and may result in  changes in the frequency and intensity of precipitation events. Although  the effects of changes in precipitation amount and inter-annual  precipitation variability on terrestrial plant productivity and carbon  sequestration have been well studied, how intra-annual precipitation  variability affects terrestrial ecosystem function remains unclear. Here,  we synthesized field manipulative experiments from 71 publications to  quantify the effects of intra-annual precipitation variability increases  (IPVI) on community biomass and plant diversity in grasslands worldwide.  \u00a0At the global scale, we found that IPVI generally increased  grassland community aboveground biomass (AGB) by 6%, and decreased grass  biomass and soil ammonium nitrogen by 12% and 31%, respectively. IPVI  stimulated AGB, belowground biomass, and plant species richness in arid  regions, but not changed them in humid regions. Changes in AGB under IPVI  were related to changes in the biomass of plant functional groups, species  richness, and soil moisture. Structural equation modelling demonstrated  that that climate conditions (mean annual temperature and mean annual  precipitation) and background soil properties (soil sand content and soil  organic carbon content) jointly regulated grassland AGB responses to IPVI  across climate types. Synthesis: Overall, our study shows that grassland  productivity and diversity may increase under IPVI in arid climates, and  that humid grasslands may be highly resistant to the effects of IPVI.  These findings have important implications for understanding ecosystem  carbon cycling under global precipitation change scenarios.", "keywords": ["2. Zero hunger", "meta-analysis", "13. Climate action", "soil properties", "intra-annual precipitation variability increase", "15. Life on land", "grassland", "species richness", "aboveground biomass", "Soil water availability", "FOS: Natural sciences"], "contacts": [{"organization": "Su, Jishuai, Zhang, Yi, Xu, Fengwei,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.s4mw6m9bc"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.s4mw6m9bc", "name": "item", "description": "10.5061/dryad.s4mw6m9bc", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.s4mw6m9bc"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-05-16T00:00:00Z"}}, {"id": "10.5061/dryad.z08kprrnc", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:40Z", "type": "Dataset", "created": "2024-04-19", "title": "Data from: Water level drawdown induces a legacy effect on the seed bank and retains sediment chemistry in a eutrophic clay wetland", "description": "Open Access<strong>2.1 Study site</strong>  The study was conducted in Oostvaardersplassen in the Netherlands  (coordinates: 52.456857, 5.355935). This eutrophic clay wetland of about  5600 ha consists of a 3600 ha marsh and a 2000 ha dryer border zone. This  study took place in the marsh part. The marsh is characterized by large  water bodies, reed vegetation and willow forests. Oostvaardersplassen is  part of the polder Zuidelijk Flevoland, which is located in the former  Zuiderzee estuary, a marine habitat (see van Leeuwen et al., 2021 for a  detailed description). For water safety reasons the decision was made to  separate the inland Zuiderzee from the North Sea through the construction  of a dike, named the Afsluitdijk. After completion of the construction and  within five years, the Zuiderzee transformed into a freshwater lake,  IJsselmeer. In this freshwater lake, several polders were established to  create land for agriculture; Zuidelijk Flevoland was reclaimed in 1968.  Since Oostvaardersplassen is located in, what was then, the lowest part of  the polder, it remained wet during the first years after reclamation and  no actions were taken to develop this area into the industrial site as it  was planned to be (Cornelissen et al., 2014). The  marine clay soil and its associated high nutrient concentrations  (eutrophic) in combination with the unmanaged and wet conditions, led  nature to develop quickly. This made the area into an important breeding  and resting area for many wetland birds and therefore became a protected  wetland nature reserve in 1974. In 1989 it became a protected area within  the European Bird directive and under the Ramsar agreement. Additionally,  it was qualified as a Natura 2000 area in 2009. Later on, the relatively  high water levels at the end of winter, due to the height of the weir, in  combination with high grazing pressure by moulting greylag geese  (<em>Anser anser</em>) from May to July, resulted in the loss  of reed cover (<em>Phragmites australis</em>) (Vulink and Van  Eerden, 1998). This in turn resulted in decreasing bird numbers due to  lower food and habitat availability (Beemster et al., 2010). To restore  reed-dominated wetlands and to increase food and habitat availability for  birds, a complete multi-year water level drawdown was induced in the  western part of the marsh from 1987 till 1991\u00a0(Vulink and Van Eerden,  1998). The eastern part was hydrologically separated from the western part  by a low dike\u00a0and water levels and dynamics remained unchanged in this  area. The implemented water level drawdown resulted in the development of  c. 600 ha of reed-dominated vegetation in the western part, after which  typical wetland birds, e.g., bearded reedling (<em>Paranrus  biarmicus</em>), marsh harrier (<em>Circus  aeruginosus</em>) and Eurasian bittern (<em>Botaurus  stellaris</em>), increased in numbers (Beemster et al., 2012; Vulink  and Van Eerden, 1998). The study area experiences  seasonal variation in water level, but lacks long-term dynamics in water  level that would be caused by extreme climatological periods. As the marsh  is rainwater fed, natural water level dynamics occur with a high water  level at the end of winter (March) and low levels at the end of summer  (September;). The surplus of water in winter leaves the marsh via a weir.  The average difference in water level between summer and winter is  approximately 30 cm. During \u2018dry\u2019 summers the water level can drop 50 cm  at the end of the growing season. Due to both the climate conditions in  combination with the height of the weir, set as to pertain high water  levels in the reed beds during late winter and spring, these naturally  occurring \u2018dry\u2019 summers did not result in enough mudflat exposure  throughout the area to allow extensive marsh recovery. At the time of  sampling, both the water level drawdown and the non-water level drawdown  area were characterized by a sharp border between vegetation and open  water. The vegetation on the shores was similar in both areas and  dominated by <em>Phragmites australis</em>, <em>Salix  spp. </em>and, to a lesser extent, <em>Convolvulus  spp.</em>. At drier sites, with greater proximity to the lake,  <em>Urtica dioica</em> and <em>Carduus spp.  </em>were present in higher abundances.\u00a0The shores of the lake, that  sometimes fall dry during dry summers, are colonized quickly by species  among which <em>Tephroseris palustris </em>(also known as  <em>Senecio congestus</em>), <em>Epilobium  hirsutum</em> and<strong> </strong><em>Ranunculus  sceleratus</em>.  <strong>2.2 Experimental  design</strong> We examined the legacy effects of  a water level drawdown, a water level gradient and water level  fluctuations on seed bank germination and nutrient availability using  field sampling and mesocosm experiment. The unique field situation  consisting of areas with and without a water level drawdown history allows  to explore legacy effects on seed bank properties (Part 1.1) and nutrient  availability (Part 2.1). This approach focusses on the long-term effects  of inducing a four-year water level drawdown, in this case 30 years after  the event, by sampling 20 locations in each subarea that have been  inundated since the last water level drawdown. In addition, soil samples  have been taken in these two hydrologically distinct areas, along a water  level gradient that is dictated by elevational differences of about 20 cm.  With this approach, we used the elevational gradient to distinguish  between higher locations, that would fall dry more often due to for  example dry summers, and lower locations. The latter had not fallen dry  for 30 years in case of the water level drawdown area and 50 years in case  of the non\u2013water level drawdown area. By taking soil samples on 7  (germination) or 5 (nutrient) locations along this water level gradient,  we were able to research how changes in water level alter seed bank  properties (Part 2.1) and nutrient availability (Part 2.2) on a smaller  seasonal time scale. In addition to the above two sampling campaigns, a  mesocosm experiment was conducted to study the effects of water level on  germination (Part 3.1) and nutrient availability (Part 3.2) . With this  approach it was possible to determine effects of a specified water level  (inundated, saturated, dry) on an even smaller time scale of weeks/months  and how such a response might be influenced by events in the past, in this  case drawdown history.\u00a0 <strong>2.2.1 Part 1:  Water level drawdown history </strong> To  investigate the legacy effects of a previously induced water level  drawdown on the seed bank (part 1.1) and on nutrient availability (part  1.2), we compared seed bank properties (density, diversity, species  composition) and sediment nutrient concentrations between an area with  water level drawdown history and an area without. For the method on  sediment nutrient concentrations we would like to refer to the section on  water level gradient (2.2.2) for field sampling and lab  protocols. <em>2.2.1.1 Seed bank properties (part  1.1)</em> We collected sediment samples from both  areas in Oostvaardersplassen in June 2021, when both areas were still  inundated. To cover the spatial heterogeneity of the area, 40 locations  were sampled. 20 Sample points were located in the area that was  continuously inundated for 50 years (non-water level drawdown history,  <em>n = 20</em>) and 20 in the area that had undergone a water  level drawdown from 1987 till 1991 and was subsequently inundated for 30  years (water level drawdown history, <em>n =  20</em>). In June 2021, we took ten sediment  cores of 23.8 cm<sup>2</sup> (diameter = 5.5 cm) to a depth of  10 cm and pooled the 0-5 cm and 5-10 cm depth in separate plastic bags at  each location (Verhofstad et al., 2017). The bags were stored in the dark  at 4\u00b0C for approximately one month to allow seed stratification, after  which the sediment was sieved (mesh width: 150 \u00b5m) and the residue,  containing the seeds, was spread across a tray (37\u00d727 cm) containing  sediment for propagation and germination (Lensli substrates; pH = ~5.3;  electrical conductivity = ~0.5mS/cm). The trays were placed in a  greenhouse with supplementary light from 6:00-22:00h so that light  conditions on plant level corresponded with 250  \u03bcmol.m<sup>2</sup>/s. The temperature in the greenhouse was on  average 21\u00b0C between 6:00-22:00 and 16\u00b0C between 22:00-6:00. The relative  humidity (Rh) in the greenhouse was on average 60% (-5/+5%). To ensure  optimal sediment moisture, the trays were watered at least once a week  with rainwater. The germinating plants were then identified to species  level and removed afterwards. This was done to minimize possible  competition effects between seedlings. Unidentified plants were  transferred from the trays to individual pots, providing the space for  them to grow and/or flower until their identification could be determined.  When germination stopped, the sediment was mixed to allow seeds deeper in  the sediment to germinate. The trays were kept in the greenhouse until  germination stopped again, which lasted up to 5 months.  <strong>2.2.2 Part 2: Water level  gradient</strong> To determine how a water level  gradient, induced through a gradient in soil elevation of around 20 cm,  affects seed bank properties (density, diversity, species composition;  Part 2.1) and nutrient availability (part 2.2), we collected sediment  samples in the field. Sample collection occurred at seven locations (seed  bank) and five locations (nutrient availability) along four transects  perpendicular to the border of the reed vegetation. The indicated  direction was chosen to cover differences in soil elevation, with  locations on a relatively higher elevation falling dry more often due to  small fluctuations in the water level and locations on a lower elevation  falling dry less often. <em>2.2.2.1 Seed bank  properties (part 2.1)</em> To assess how a water  level gradient alters seed bank properties, we collected sediment samples  in June 2021 along four transects, each consisting of seven sampling  points (<em>n</em> = 28). The sampling points cover a gradient  of soil elevation, where the locations indicated by a 1 are located at the  highest elevation, and thus fall dry the most, while locations indicated  by a higher number (2-7) are decreasing in soil elevation and thus fall  dry less often or never. Each transect covered around 777.5 \u00b1 418.7 meter.  Two transects were located in the area without water level drawdown  history and two in the area with water level drawdown history. The  sampling and germination protocol was identical to the one described in  section 2.2.1. <em>2.2.2.2 Nutrient availability  (part 2.2)</em> To examine how a water level  gradient affect nutrient availability, sediment samples were collected  along four transects (different from the transects in 2.2.2.1) in November  2021. Each transect consists of five sampling points that were sampled in  duplicate (<em>n</em> = 40). The sampling points cover a  gradient of soil elevation, where the locations indicated by a 1 are  located at the highest elevation, and thus fall dry the most, while  locations indicated by a higher number (2-5) are decreasing in soil  elevation and thus fall dry less often or never. Each transect covered  around 237.5 \u00b1 17.9 meter. Two transects were situated in the area without  water level drawdown history and two in the area with water level drawdown  history. At each sampling location, four sediment cores of 23.8  cm<sup>2</sup> (diameter = 5.5 cm) to a depth of 0-10 cm and  20-30 cm were collected for pore-water extraction and one sediment core of  23.8 cm<sup>2</sup> (diameter = 5.5 cm) to a depth of 0-10 and  20-30 cm was collected for sediment nutrient analyses. Soil elevation  measurements were conducted with a dGPS (Topcon, HiPer SR). At each  location, we took three measurements which were averaged.  Pore-water extraction was initiated in the lab on the same day as  sediment collection and collected the next morning. Pore-water samples  were extracted using vacuum syringes attached to rhizons (Rhizon SMS;  Rhizosphere Research Products; Eijkelkamp Agrisearch Equipment, Giesbeek,  The Netherlands). The pore-water was analyzed for pH, alkalinity (Metrohm,  877 Titrino plus), total inorganic carbon (TIC; infrared carbon Analyser,  IRGA; ABB Analytical, Frankfurt, Germany) and nutrient  concentrations. Sediment samples were analyzed on water  content, bulk density loss of ignition (LOI; proxy for organic matter  content) and bioavailable phosphorus and  NH<sub>4</sub><sup>+</sup> and  NO<sub>3</sub><sup>-</sup>. The elaborated method  can be found in the supplementary material S1. Nitrite  (NO<sub>2</sub><sup>-</sup>) concentrations were  barely detectable and therefore left out of the analysis.  <strong>2.2.3 Part 3: Water level  fluctuations</strong> <strong>Experimental  setup</strong> To unravel how water level  influences germination (part 3.1) and nutrient availability (part 3.2), we  performed a mesocosm experiment with different water levels on intact  sediment cores from sites with and without water level drawdown history  from Oostvaardersplassen. The different water levels reflect the different  stages the system goes through during the first phase (drying) of a water  level drawdown cycle: (1) Dry, the water level was 20 cm below sediment  surface level (\u2018dry\u2019 for brevity), (2) saturated, the water level was  equal to the sediment surface level (\u2018saturated\u2019 for brevity), and (3)  wet, the water level was eight cm above sediment surface level (\u2018wet\u2019 for  brevity). The experiment ran for eight consecutive weeks in which each  core experienced one of the water level treatments (inundated, saturated  or dry) following Vonk et al. (2017). In November 2020, intact sediment  cores were collected from Oostvaardersplassen at ten locations that were  inundated. Half of these locations were situated in an area with a water  level drawdown history (<em>n</em> = 5, water level = 13.8 +/-  3.9 cm), while the other half were situated in a continuously inundated  area (<em>n</em> = 5, water level = 17 +/- 5.4 cm). At each  location, four sediment cores with a diameter of 16 cm and a depth of 40  cm were collected by pressing a PVC-tube in the sediment and sealing it  with a cap on the bottom. Three of the intact cores for each location were  placed in a climate room for an acclimation period of six days, after  which the experiment started. The cores were placed in the climate room  with a temperature regime of 20\u00b0C from 6:00-22:00 and 15\u00b0C from  22:00-6:00. The average humidity in the climate chamber was 45% and the  average light conditions at sediment level were 554  \u03bcmol.m<sup>2</sup>/s (LI-COR LI-250 photometer) with 16 hours  light and 8 hours dark. The cores were placed using a randomized block  design (<em>n</em> = 5), each block consisted of six sediment  cores. The treatments were applied by drilling holes in the PVC-tube at  the corresponding water level treatment height (-20 cm, 0 cm, +8 cm  relative to the sediment height). To regulate the water level in the core,  we placed the PVC-tube in a larger water-proof PVC-core (diameter = 20 cm,  length = 50 cm). Water collected from the Oostvaardersplassen was used to  initiate the treatments. During the experiment, water was replenished till  treatment level with rainwater (pH = 5.18, alkalinity = 0.33 mEQ/L). The  fourth core was used to determine sediment nutrient starting conditions by  taking two sediment samples of 40 cm deep (23.8  cm<sup>2</sup>) after which it was split in two sections of 10  cm (0-10, 20-30). The two sediment samples from the sediment core were  pooled per location and per depth and stored in the freezer at -20\u00b0C until  further analyses. The same analysis protocol was used as in approach 2  (section 2.2.2.2). <em>2.2.3.1 Seed bank  properties(part 3.1)</em> Through the use of  intact soil cores in an experimental setup, we could identify possible  environmental filters that would exert selection on the type of plants  that were able to germinate during different phases of a water level  drawdown cycle. During the 8-week experiment, the mesocosms were checked  weekly for plant germination. Germinated plants were counted and  identified to species level if possible. Plants were not removed during  the experiment. <em>2.2.3.2 Nutrient availability  (part 3.2)</em> The experimental setup allowed us  to assess how a certain water level regime impacts nutrient availability  in the system, in this case, we selected three water levels to mimic  different phases of the water level drawdown cycle. By monitoring these  changes it would be possible to identify possible nutrient depletion in  the system upon repeated water level drawdown implementation. Nutrient  concentrations were determined in both the pore-water and the sediment. To  collect pore-water samples during the experiment, rhizons (Rhizon SMS;  Rhizosphere Research Products; Eijkelkamp Agrisearch Equipment, Giesbeek,  The Netherlands) were installed in the sediment core at a depth of 10 cm  and a vacuum syringe could be attached to extract pore-water. This was  done at the start of the experiment (day 0), and repeated five times on  day 7, 14, 21, 35 and 56. Pore-water samples were analyzed in the same way  as in approach 2. At the end of the experiment, sediment samples were  taken from the sediment cores at two different depths (0-10 cm and 20-30  cm) following the same sampling strategy as at the start of the  experiment. These samples were stored in the freezer at -20\u00b0C until  further analyses, following the analysis protocol as described in approach  2 (section 2.2.2.2). <strong>2.3 Statistical  analyses </strong> Data were analyzed in RStudio  version 4.0.3 (R Core Team, 2023). For all hypotheses testing procedures  the significance level was set at \u03b1 = 0.05. All data are shown with their  average \u00b1 standard deviation (sd). <strong>Part  1: Water level drawdown history</strong>  <em>Part 1.1 Seed bank properties</em>  To determine the effect of water level drawdown history (Yes or  No) on mean Shannon-Wiener diversity, mean species richness, and mean  germination densities (log transformed), we used mixed linear models from  the GlmmTMB package (Mollie et al., 2017), using location ID as a random  effect. Differences in the total sum of germinated individuals between the  water level drawdown and non-water level drawdown area were tested using a  Chi-Square test. Shannon-Wiener diversity was calculated using the \u2018vegan  package\u2019 (Oksanen et al., 2022). To assess the effect of water level  drawdown history on species composition a permanova analysis with a  Bray-Curtis dissimilarity index was used, in combination with non-metric  multidimensional scaling (NMDS) (vegan package: Oksanen et al.,  2022). <em>Part 1.2 Nutrient  availability</em> To determine the effect of  water level drawdown history and sampling depth (independent variables) on  the nutrient availability (dependent variables) along the transect survey  (method section 2.2.2.2), we used mixed linear models from the GlmmTMB  package (Mollie et al., 2017). The model was performed for both the  sediment- and the pore-water nutrient concentrations. Location ID was used  as a random effect to correct for the duplicate measurements.  Tukey-adjusted comparisons were done using \u201cemmeans\u201d (Russell, 2022).  Normality and heterogeneity of the residuals of the models were assessed  using histograms, and transformed if necessary.  Additionally, we used the nutrient starting concentrations from  the experimental water level experiment (part 3) to determine differences  in nutrient concentrations due to the water level drawdown history. To  determine the effect of water level drawdown history (independent  variable) on nutrient availability (dependent variables), we used mixed  linear models from the GlmmTMB package (Mollie et al., 2017). Starting  nutrient concentrations (day 0; field conditions) were used as the  dependent variable. Field location ID was used as a random effect to  correct for samples taken at the same location.  <strong>Part 2: Water level  gradient</strong> <em>Part 2.1 Seed bank  properties</em> To determine the best fit of the  relation between germination and distance to the reed border, we compared  the AIC of linear, parabolic, hyperbolic and exponential decay functions.  An \u0394AIC \u2265 2 was used to differentiate models ( \u2018stats\u2019 package (R Core  Team, 2023). To assess the effect of water level drawdown history and  location along soil elevation gradient on species composition, a permanova  analysis with a Bray-Curtis dissimilarity index was used in combination  with non-metric multidimensional scaling (NMDS) (Oksanen et al.,  2022). To determine differences in Shannon-Wiener  diversity, species richness and germination densities (dependent  variables) along the transect survey (location within transect as  independent variable), we used mixed linear models from the GlmmTMB  package with location ID as a random effect (Mollie et al., 2017). Species  richness was fitted with a Poisson distribution. This approach was done  separately for the water level drawdown and the non-water level drawdown  area. Tukey-adjusted comparisons were done using \u201cemmeans\u201d (Russell,  2022). Shannon-Wiener diversity was calculated using the \u2018vegan package\u2019  (Oksanen et al., 2022). Differences in the sum of germinated individuals  per location along the water level gradient were tested using a Chi-Square  test. <em>Part 2.2 Nutrient  availability</em> To test for differences in  nutrient availability along the elevational gradient of current water  level fluctuations in the transect survey, we performed Spearman  correlations. The Spearman correlations were done between nutrient  concentration as the dependent variable and elevation in meters NAP as the  independent variable. <strong>Part 3: Water level  fluctuations</strong> <em>Part 3.1: Seed  bank properties</em> Due to the low germination  rate, no statistical analysis were performed on seed bank properties in  relation to any of the water level treatments.  <em>Part 3.2: Nutrient availability</em>  To determine the effect of water level treatment (independent  variable) on nutrient availability (dependent variables), we used mixed  linear models from the GlmmTMB package (Mollie et al., 2017). Nutrient  concentrations from the end of the experiment (day 56) were used as  dependent variable. Nutrient starting concentrations were used as a  covariate into the model and the blocking factor was used as a random  effect. Additionally, nutrient concentrations were tested for changes over  time during the eight-week experiment using mixed linear models from the  GlmmTMB package (Mollie et al., 2017). Nutrient concentrations were used  as the dependent variable, the blocking factor was used as a covariate in  the model and date was used as the independent variable. To test for  differences among the independent variables, Tukey-adjusted comparisons  were done using \u201cemmeans\u201d for all models (Russell, 2022). All models were  fitted with a Gaussian-error distribution. Normality and heterogeneity of  the residuals of the models were assessed using histograms, and were  transformed if necessary. For more details we would  like to refer to\u00a0<strong>Figure 1</strong> in the related  manuscript.", "keywords": ["fluctuating water level", "nutrients", "Seedlings", "Wetlands", "seedlings", "Fluctuating water level", "Nutrients", "mesocosms", "natural sciences", "Mesocosms", "FOS: Natural sciences", "wetlands"]}, "links": [{"href": "https://doi.org/10.5061/dryad.z08kprrnc"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.z08kprrnc", "name": "item", "description": "10.5061/dryad.z08kprrnc", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.z08kprrnc"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2024-01-01T00:00:00Z"}}, {"id": "10.5061/dryad.wm37pvmt3", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:22:39Z", "type": "Dataset", "created": "2023-06-28", "title": "Tree biomass does not correlate with soil carbon stocks in forest-tundra ecotones along a 1100 km latitudinal gradient in Norway", "description": "Due to climate warming, forests are expanding to higher elevations and  latitudes at the expense of tundra vegetation. While the subsequent  increase in aboveground biomass is well-documented, there is much  speculation regarding the effects on soil organic carbon (SOC) stocks. To  provide insight into the consequences of tree encroachment into treeless  tundra, we sampled SOC stocks across 36 forest-tundra ecotones along a  1100 km latitudinal gradient in Norway. Our results show that SOC stocks  vary greatly within, as well as among treeline ecotones, and that SOC  stocks do not correlate with tree biomass and tree species. SOC stocks do  increase with temperature, and vary with slope steepness, slope aspect,  and soil parent material. Applying a \u2018space-for-time substitution\u2019  perspective, our findings suggest that tree encroachment into tundra is  unlikely to have immediate consequences for SOC stocks.", "keywords": ["treeline", "13. Climate action", "Norway", "Forest-tundra ecotone", "boreal forest", "15. Life on land", "Tundra", "Soil carbon", "FOS: Natural sciences"], "contacts": [{"organization": "Devos, Claire C\u00e9line, Ohlson, Mikael, N\u00e6sset, Erik, Klanderud, Kari, Bollands\u00e5s, Ole Martin,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.wm37pvmt3"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.wm37pvmt3", "name": "item", "description": "10.5061/dryad.wm37pvmt3", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.wm37pvmt3"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2023-07-10T00:00:00Z"}}, {"id": "10.5061/dryad.zs7h44jb4", "type": "Feature", "geometry": null, "properties": {"license": "unspecified", "updated": "2026-04-13T16:22:40Z", "type": "Dataset", "title": "Decay by ectomycorrhizal fungi couples soil organic matter to nitrogen availability", "description": "Interactions between soil nitrogen (N) availability, fungal community  composition, and soil organic matter (SOM) regulate soil carbon (C)  dynamics in many forest ecosystems, but context dependency in these  relationships has precluded general predictive theory. We found that  ectomycorrhizal (ECM) fungi with peroxidases decreased with increasing  inorganic N availability across a natural inorganic N gradient in northern  temperate forests, whereas ligninolytic fungal saprotrophs exhibited no  response. Lignin-derived SOM and soil C were negatively correlated with  ECM fungi with peroxidases and were positively correlated with inorganic N  availability, suggesting decay of lignin-derived SOM by these ECM fungi  reduced soil C storage. The correlations we observed link SOM decay in  temperate forests to tradeoffs in tree N nutrition and ECM composition,  and we propose SOM varies along a single continuum across temperate and  boreal ecosystems depending upon how tree allocation to functionally  distinct ECM taxa and environmental stress covary with soil N  availability.", "keywords": ["15. Life on land", "FOS: Natural sciences"], "contacts": [{"organization": "Argiroff, William A., Zak, Donald R., Pellitier, Peter T., Upchurch, Rima A., Belke, Julia P.,", "roles": ["creator"]}]}, "links": [{"href": "https://doi.org/10.5061/dryad.zs7h44jb4"}, {"rel": "self", "type": "application/geo+json", "title": "10.5061/dryad.zs7h44jb4", "name": "item", "description": "10.5061/dryad.zs7h44jb4", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main/items/10.5061/dryad.zs7h44jb4"}, {"rel": "collection", "type": "application/json", "title": "Collection", "name": "collection", "description": "Collection", "href": "https://repository.soilwise-he.eu/cat/collections/metadata:main"}], "time": {"date": "2022-01-24T00:00:00Z"}}, {"id": "10.6078/D1DD85", "type": "Feature", "geometry": null, "properties": {"updated": "2026-04-13T16:25:32Z", "type": "Dataset", "title": "DayCent simulations for California annual grasslands: Monthly data outputs", "description": "unspecifiedComposted manure and green waste amendments have been shown to increase  net carbon (C) sequestration in rangeland soils and have been proposed as  a means to help lower atmospheric CO2 concentrations. However, the effect  of climate change on soil organic C (SOC) stocks and greenhouse gas  emissions in rangelands is not well understood, and the viability of  climate change mitigation strategies under future conditions is even less  certain. We used a process-based biogeochemical model (DayCent) at a daily  timestep to explore the long-term effects of potential future climate  changes on C and greenhouse gas dynamics in annual grassland ecosystems.  We then used the model to explore how the same ecosystems might respond to  climate change following compost amendments to soils and determined the  long-term viability of net SOC sequestration under changing climates. We  simulated net primary productivity (NPP), SOC, and greenhouse gas fluxes  across seven California annual grasslands with and without compost  amendments. We drove the DayCent simulations with field data and with  site-specific daily climate data from two Earth system models (CanESM2 and  HadGEM-ES) and two representative concentration pathways (RCP4.5 and  RCP8.5) through 2100. Net primary productivity and SOC stocks in unamended  and amended ecosystems were surprisingly insensitive to projected climate  changes. A one-time amendment of compost to rangeland acted as a  slow-release organic fertilizer and increased NPP by up to 390\u2013814 kg C  ha-1 y-1 across sites. The amendment effect on NPP was not sensitive to  Earth system model or emissions scenario and endured through the end of  the century. Net SOC sequestration amounted to 1.96 \u00b1 0.02 Mg C ha-1  relative to unamended soils at the maximum amendment effect. Averaged  across sites and scenarios, SOC sequestration peaked 22 \u00b1 1 years after  amendment and declined but remained positive throughout the century. While  compost stimulated nitrous oxide (N2O) emissions, the cumulative net  emissions (in CO2 equivalents) due to compost were far less than the  amount of SOC sequestered. Compost amendments resulted in a net climate  benefit of 69.6 \u00b1 0.5 Tg CO2e 20 \u00b1 1 years after amendment if applied to  similar ecosystems across the state, amounting to 39% of California\u2019s  rangeland. These results suggest that the biogeochemical benefits of a  single amendment of compost to rangelands in California is insensitive to  future climate change and could contribute to decadal-scale climate  mitigation goals alongside emissions reductions.", "keywords": ["2. Zero hunger", "compost", "HadGEM2-ES", "15. Life on land", "California", "12. Responsible consumption", "soil organic carbon", "DayCent", "CanESM2", "RCP8.5", "13. 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