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dc.contributor.authorHapsari, KA
dc.contributor.authorBorrero Avellaneda, WJ
dc.contributor.authorVan Maanen, B
dc.contributor.authorRestrepo, JC
dc.contributor.authorPolanía, J
dc.contributor.authorSibaja Castillo, DJ
dc.contributor.authorGómez Vargas, LF
dc.contributor.authorRodríguez-Rodríguez, JA
dc.contributor.authorUrrego, DH
dc.date.accessioned2024-06-21T13:35:06Z
dc.date.issued2024-06-21
dc.date.updated2024-06-19T12:32:27Z
dc.description.abstractThis is the dataset used for the Hapsari et al. (2024) article "Structure and carbon stocks of accessible mangroves in the Colombian Caribbean" published in Forest Ecology and Management.en_GB
dc.description.sponsorshipNatural Environment Research Council (NERC)en_GB
dc.formatAll data is in .xlsx format
dc.identifier.doi10.24378/exe.5246
dc.identifier.grantnumberNE/V012800/1en_GB
dc.identifier.urihttp://hdl.handle.net/10871/136372
dc.identifierORCID: 0000-0001-6115-5362 (Van Maanen, Barend)
dc.language.isoenen_GB
dc.publisherUniversity of Exeteren_GB
dc.relation.urlhttp://hdl.handle.net/10871/136319en_GB
dc.rightsCC BY 4.0en_GB
dc.subjectMangroveen_GB
dc.subjectProtected areaen_GB
dc.subjectPADDD risken_GB
dc.subjectUrban ecologyen_GB
dc.subjectForest structureen_GB
dc.subjectCarbon stocken_GB
dc.subjectNeotropicen_GB
dc.titleStructure and carbon stocks of accessible mangroves under different conservation status in the Colombian Caribbean (dataset)en_GB
dc.typeDataseten_GB
dc.date.available2024-06-21T13:35:06Z
dc.descriptionData for: Hapsari et al. 2024. Structure and carbon stocks of accessible mangroves in the Colombian Caribbean. Forest Ecology and Management. The data collection of forest structure and biomass carbon (C) stock was conducted based on modified protocol by Kauffman and Donato (2012). 13 measurement plots were established in Cuatro Bocas, protected mangrove within the Isla Salamanca National Park and 15 measurement plots were established in Mallorquin, unprotected mangrove. Within the larger plots (7-m radius), mangrove trees were identified, and the diameter of each was measured at breast height (dbh), except for Rhizophora spp. (measured at 30 cm above the highest stilt root) (Kauffman and Donato, 2012; Howard et al. 2014) and dead trees (measured immediately below the cut line if remaining stems are lower than 1.3 m) (Scales and Friess, 2019). Mangrove saplings (dbh <5 cm) and seedling (<140 cm height) were recorded within smaller plot sizes (2-m radius). Fallen dead woods or woody debris (large (≥ 7.6 cm) and medium (2.5 ≤ 7.6 cm)) were recorded and measured along 4 planar transects in each plot. Vegetation biomass was estimated using species specific allometric equations developed by Smith and Whelan (2006) for aboveground. For belowground biomass estimation, general equation by Komiyama et al. (2008) was used then adjusted by factoring the proportion of obtained estimated species-specific aboveground biomass with that of the general equation by Komiyama et al. (2005) to reduce overestimation. Vegetation biomass C stock was calculated using species specific wood density and C content published by Rodrigues et al. (2014) and Virgulino-Júnior et al. (2020), and conservative conversion factor (0.46 g of C per 1 g biomass) to convert woody debris C stocks (Murdiyarso et al., 2009). All data does not require specific software to access.en_GB
dc.descriptionThe article associated with this dataset is available in ORE at: http://hdl.handle.net/10871/136319en_GB
dc.rights.urihttps://creativecommons.org/licenses/by/4.0en_GB
rioxxterms.versionNAen_GB
rioxxterms.licenseref.startdate2024-06-21
rioxxterms.typeOtheren_GB
refterms.dateFOA2024-06-21T13:35:24Z


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