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dc.contributor.authorAmoakoh, Alex Owusu
dc.contributor.authorAplin, Paul
dc.contributor.authorRodríguez-Veiga, Pedro
dc.contributor.authorMoses, Cherith
dc.contributor.authorPeña Alonso, Carolina
dc.contributor.authorCortés, Joaquín A.
dc.contributor.authorDelgado Fernández, Irene 
dc.contributor.authorKankam, Stephen
dc.contributor.authorMensah, Justice Camillus
dc.contributor.authorNortey, Daniel Doku Ni
dc.contributor.otherCiencias de la Tierraes_ES
dc.date.accessioned2025-04-03T08:07:33Z
dc.date.available2025-04-03T08:07:33Z
dc.date.issued2024
dc.identifier.issn2072-4292
dc.identifier.urihttp://hdl.handle.net/10498/36059
dc.description.abstractThe Greater Amanzule Peatlands (GAP) in Ghana is an important biodiversity hotspot facing increasing pressure from anthropogenic land-use activities driven by rapid agricultural plantation expansion, urbanisation, and the burgeoning oil and gas industry. Accurate measurement of how these pressures alter land cover over time, along with the projection of future changes, is crucial for sustainable management. This study aims to analyse these changes from 2010 to 2020 and predict future scenarios up to 2040 using multi-source remote sensing and machine learning techniques. Optical, radar, and topographical remote sensing data from Landsat-7, Landsat-8, ALOS/PALSAR, and Shuttle Radar Topography Mission derived digital elevation models (DEMs) were integrated to perform land cover change analysis using Random Forest (RF), while Cellular Automata Artificial Neural Networks (CA-ANNs) were employed for predictive modelling. The classification model achieved overall accuracies of 93% in 2010 and 94% in both 2015 and 2020, with weighted F1 scores of 80.0%, 75.8%, and 75.7%, respectively. Validation of the predictive model yielded a Kappa value of 0.70, with an overall accuracy rate of 80%, ensuring reliable spatial predictions of future land cover dynamics. Findings reveal a 12% expansion in peatland cover, equivalent to approximately 6570 ± 308.59 hectares, despite declines in specific peatland types. Concurrently, anthropogenic land uses have increased, evidenced by an 85% rise in rubber plantations (from 30,530 ± 110.96 hectares to 56,617 ± 220.90 hectares) and a 6% reduction in natural forest cover (5965 ± 353.72 hectares). Sparse vegetation, including smallholder farms, decreased by 35% from 45,064 ± 163.79 hectares to 29,424 ± 114.81 hectares. Projections for 2030 and 2040 indicate minimal changes based on current trends; however, they do not consider potential impacts from climate change, large-scale development projects, and demographic shifts, necessitating cautious interpretation. The results highlight areas of stability and vulnerability within the understudied GAP region, offering critical insights for developing targeted conservation strategies. Additionally, the methodological framework, which combines optical, radar, and topographical data with machine learning, provides a robust approach for accurate and detailed landscape-scale monitoring of tropical peatlands that is applicable to other regions facing similar environmental challenges.es_ES
dc.formatapplication/pdfes_ES
dc.language.isoenges_ES
dc.publisherMultidisciplinary Digital Publishing Institute (MDPI)es_ES
dc.rightsAtribución 4.0 Internacional*
dc.rights.urihttp://creativecommons.org/licenses/by/4.0/*
dc.sourceRemote Sensing - Vol. 16 n. 21, artículo n. 4013es_ES
dc.subjectenvironmental conservationes_ES
dc.subjectland cover dynamicses_ES
dc.subjectmachine learning classificationes_ES
dc.subjectmodellinges_ES
dc.subjectpeatlandses_ES
dc.subjectremote sensinges_ES
dc.titlePredictive Modelling of Land Cover Changes in the Greater Amanzule Peatlands Using Multi-Source Remote Sensing and Machine Learning Techniqueses_ES
dc.typejournal articlees_ES
dc.rights.accessRightsopen accesses_ES
dc.identifier.doi10.3390/RS16214013
dc.type.hasVersionVoRes_ES


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This work is under a Creative Commons License Atribución 4.0 Internacional