14539 10 77063 3 212992 document 77063 forests-08-00114.pdf application/pdf f87798015da9cf911572818463ef7c3f MD5 1154711 2017-04-20 13:34:25 https://pure.iiasa.ac.at/id/eprint/14539/1/forests-08-00114.pdf 14539 1 1 application/pdf text en public cc_by

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http://eprints.org/relation/isVersionOf https://pure.iiasa.ac.at/id/document/77063 http://eprints.org/relation/isVolatileVersionOf https://pure.iiasa.ac.at/id/document/77063 http://eprints.org/relation/ismediumThumbnailVersionOf https://pure.iiasa.ac.at/id/document/77063 77068 2 213001 document 77068 small.jpg image/png d46f657d330605b519fba75ff36cc559 MD5 1716 2017-04-20 13:44:51 https://pure.iiasa.ac.at/id/eprint/14539/6/small.jpg 14539 6 6 image/png other Thumbnails conversion from text to thumbnail_small en public

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http://eprints.org/relation/isVersionOf https://pure.iiasa.ac.at/id/document/77063 http://eprints.org/relation/isVolatileVersionOf https://pure.iiasa.ac.at/id/document/77063 http://eprints.org/relation/issmallThumbnailVersionOf https://pure.iiasa.ac.at/id/document/77063 archive 5 disk0/00/01/45/39 2017-04-20 13:36:36 2021-08-27 17:28:51 2017-04-20 13:36:36 article show Lee J. 8934 Lee S. Han S.H. Kim S. Roh Y. Salim K.A. Pietsch S.A. 2054 0000-0001-6431-2212 Son Y. pub prog_esm carbon dynamics; net ecosystem production; forest carbon model; intact dipterocarp forest Intact dipterocarp forests in Asia act as crucial carbon (C) reservoirs, and it is therefore important to investigate the C dynamics in these forests. We estimated C dynamics, together with net ecosystem production (NEP), in an intact tropical dipterocarp forest of Brunei Darussalam. Fifty-four simulation units (plots; 20 m × 20 m) were established and initial C stocks were determined via direct field measurement. The C dynamics were annually simulated with a regression model and the Forest Biomass and Dead organic matter Carbon (FBDC) model. The initial C stock (Mg C·ha−1) of biomass, litter, dead wood and mineral soil were 213.1 ± 104.8, 2.0 ± 0.8, 31.3 ± 38.8, and 80.7 ± 15.5, respectively. Their annual changes (Mg C·ha−1·year−1) were 3.2 ± 1.1, 0.2 ± 0.2, −3.7 ± 6.1, and −0.3 ± 1.1, respectively. NEP was −0.6 ± 6.1 Mg C·ha−1·year−1, showing large heterogeneity among the plots. The initial C stocks of biomass and dead wood, biomass turnover rates and dead wood decay rates were elucidated as dominant factors determining NEP in a sensitivity analysis. Accordingly, investigation on those input data can constrain an uncertainty in determining NEP in the intact tropical forests. 2017 published MDPI AG 10.3390/f8040114 178 232 public Forests 8 4 114-114 TRUE 1999-4907 FALSE no info:eu-repo/semantics/article