Monitoring changes in boreal peatland vegetation after restoration with optical satellite imagery.
Autor: | Isoaho A; Natural Resources Institute Finland (Luke), Paavo Havaksen tie 3, FI-90570 Oulu, Finland; Water, Energy and Environmental Engineering Research Unit, Faculty of Technology, University of Oulu, FI-90014 Oulu, Finland. Electronic address: aleksi.isoaho@luke.fi., Elo M; Finnish Environment Institute, Survontie 9A, FI-40500 Jyväskylä, Finland; Department of Biological and Environmental Science, University of Jyvaskyla, FI-40014 Jyväskylä, Finland; School of Resource Wisdom, University of Jyvaskyla, FI-40014 Jyväskylä, Finland., Marttila H; Water, Energy and Environmental Engineering Research Unit, Faculty of Technology, University of Oulu, FI-90014 Oulu, Finland., Rana P; Natural Resources Institute Finland (Luke), Paavo Havaksen tie 3, FI-90570 Oulu, Finland., Lensu A; Department of Biological and Environmental Science, University of Jyvaskyla, FI-40014 Jyväskylä, Finland., Räsänen A; Natural Resources Institute Finland (Luke), Paavo Havaksen tie 3, FI-90570 Oulu, Finland; Geography Research Unit, Faculty of Science, University of Oulu, P.O. Box 8000, Oulu, Finland. |
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Jazyk: | angličtina |
Zdroj: | The Science of the total environment [Sci Total Environ] 2024 Dec 20; Vol. 957, pp. 177697. Date of Electronic Publication: 2024 Nov 26. |
DOI: | 10.1016/j.scitotenv.2024.177697 |
Abstrakt: | Restoration can initiate a succession of plant communities towards those of pristine peatlands. Field inventory-based vegetation monitoring is labour-intensive and not feasible for every restored site. While remote sensing has been used to monitor hydrological changes in peatlands, it has been less used to monitor post-restoration changes in vegetation composition. We utilised vegetation inventories from Finnish peatland monitoring network containing 10-year before-after-control-impact monitoring data from 150 peatland sites, representing three peatland types (spruce mire forests, pine mire forests, open mires), and optical observations from Landsat 5-9 and Sentinel-2 satellites. We employed non-metric multidimensional scaling (NMDS) to produce floristic gradients, representing wetness and productivity, from the vegetation data. We constructed random forest regression models with NMDS dimensions, i.e. floristic gradients, as response variables and satellite imagery variables as the predictors. Our results show that the floristic gradients in different peatland types should be monitored with different satellite imagery variables. However, midsummer NIR and red band consistently explain variation in the gradients in all peatland types. Our results indicate that the gradients and the post-restoration changes in them can be modelled with reasonable accuracy in open mires and sparsely treed pine mire forests but not in densely treed spruce mire forests. We suggest that optical satellite imagery can serve as a proxy for assessing the post-restoration vegetation changes in peatlands with little or no trees. Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. (Copyright © 2024 The Authors. Published by Elsevier B.V. All rights reserved.) |
Databáze: | MEDLINE |
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