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dc.contributor.authorSani-Mohammed, Abubakar
dc.contributor.authorYao, Wei
dc.contributor.authorWong, Tsz Chung
dc.contributor.authorFekry, Reda
dc.contributor.authorHeurich, Marco Dietmar
dc.coverage.spatialEuropeen_US
dc.date.accessioned2025-02-12T09:20:56Z
dc.date.available2025-02-12T09:20:56Z
dc.date.created2024-08-26T12:43:40Z
dc.date.issued2024
dc.identifier.citationRemote Sensing. 2024, 16 (15), .en_US
dc.identifier.issn2072-4292
dc.identifier.urihttps://hdl.handle.net/11250/3177647
dc.description.abstractEffective forest management is essential for mitigating climate change effects. This is why understanding forest growth dynamics is critical for its sustainable management. Thus, characterizing forest plot deadwood levels is vital for understanding forest dynamics, and for assessments of biomass, carbon stock, and biodiversity. For the first time, this study used the leaf area index (LAI) and L-moments to characterize and model forest plot deadwood levels in the Bavarian Forest National Park from airborne laser scanning (ALS) data. This study proposes methods that can be tested for forests, especially those in temperate climates with frequent cloud coverage and limited access. The proposed method is practically significant for effective planning and management of forest resources. First, plot decay levels were characterized based on their canopy leaf area density (LAD). Then, the deadwood levels were modeled to assess the relationships between the vegetation area index (VAI), gap fraction (GF), and the third L-moment ratio (T3). Finally, we tested the rule-based methods for classifying plot decay levels based on their biophysical structures. Our results per the LAD vertical profiles clearly showed the declining levels of decay from Level 1 to 5. Our findings from the models indicate that at a 95% confidence interval, 96% of the variation in GF was explained by the VAI with a significant negative association (VAIslope = −0.047; R2 = 0.96; (p < 0.001)), while the VAI explained 92% of the variation in T3 with a significant negative association (VAIslope = −0.50; R2 = 0.92; (p < 0.001)). Testing the rule-based methods, we found that the first rule (Lcv = 0.5) classified Levels 1 and 2 at (Lcv < 0.5) against Levels 3 to 5 at (Lcv > 0.5). However, the second rule (Lskew = 0) classified Level 1 (healthy plots) as closed canopy areas (Lskew < 0) against Levels 2 to 5 (deadwood) as open canopy areas (Lskew > 0). This approach is simple and more convenient for forest managers to exploit for mapping large forest gap areas for planning and managing forest resources for improved and effective forest management.en_US
dc.language.isoengen_US
dc.rightsNavngivelse 4.0 Internasjonal*
dc.rights.urihttp://creativecommons.org/licenses/by/4.0/deed.no*
dc.subjectplot decay levelsen_US
dc.subjectALS metricsen_US
dc.subjectleaf area indexen_US
dc.subjectleaf area densityen_US
dc.subjectL-momentsen_US
dc.subjectforest managementen_US
dc.subjectdeadwooden_US
dc.titleCharacterizing Forest Plot Decay Levels Based on Leaf Area Index, Gap Fraction, and L-Moments from Airborne LiDARen_US
dc.title.alternativeCharacterizing Forest Plot Decay Levels Based on Leaf Area Index, Gap Fraction, and L-Moments from Airborne LiDARen_US
dc.typePeer revieweden_US
dc.typeJournal articleen_US
dc.description.versionpublishedVersionen_US
dc.rights.holder© 2024 by the authorsen_US
dc.subject.nsiVDP::Matematikk og Naturvitenskap: 400::Geofag: 450::Geometrikk: 468en_US
dc.subject.nsiVDP::Landbruks- og Fiskerifag: 900::Landbruksfag: 910::Naturressursforvaltning: 914en_US
dc.source.pagenumber19en_US
dc.source.volume16en_US
dc.source.journalRemote Sensingen_US
dc.source.issue15en_US
dc.identifier.doi10.3390/rs16152824
dc.identifier.cristin2289404
cristin.ispublishedtrue
cristin.fulltextoriginal
cristin.qualitycode1


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