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Large-diameter trees buffer monsoonal changes to tree biomass over two decades
Forest carbon storage inherently depends on the frequency and severity of characteristic disturbances and long-term changes in climate. The tropical forest of Lanjenchi, Taiwan is affected by the northeast monsoon wind, resulting in a varying vegetation structure depending on wind exposure. However,...
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| Published in: | Plant ecology 2023-11, Vol.224 (11), p.1037-1048 |
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| cites | cdi_FETCH-LOGICAL-c419t-e6b68558608b02b1fadb08d4ed6a0e589a67a9cfc1e1eaa7aabf774dfac2d9ba3 |
| container_end_page | 1048 |
| container_issue | 11 |
| container_start_page | 1037 |
| container_title | Plant ecology |
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| creator | Ku, Chen-Chia Tang, Jianwu Chao, Wei-Chun Chao, Kuo-Jung Song, Guo-Zhang Michael Lin, Huan-Yu Lutz, James A. |
| description | Forest carbon storage inherently depends on the frequency and severity of characteristic disturbances and long-term changes in climate. The tropical forest of Lanjenchi, Taiwan is affected by the northeast monsoon wind, resulting in a varying vegetation structure depending on wind exposure. However, the northeast monsoon winds have been decreasing due to the climate change. We used four censuses over 22 years (1997, 2005, 2013, and 2019) to examine how tree density and aboveground biomass change under different levels of wind stress. We assessed tree density, aboveground biomass, aboveground woody productivity, and aboveground woody mortality from trees with diameter at breast height (DBH) ≥ 1 cm across 5.28 ha subdivided into 10 × 10 m quadrats. We tested for differences in tree density and aboveground biomass among three habitat types (windward, intermediate, and leeward), among small-diameter (1 cm ≤ DBH |
| doi_str_mv | 10.1007/s11258-023-01360-y |
| format | article |
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−1
) of 140 species held 129.37 ± 51.95 Mg ha
−1
of aboveground biomass. From 1997 to 2019, tree density decreased and aboveground biomass was stable in the whole forest. However, changes in density and aboveground biomass were apparent among different habitat types and among different diameter classes. Specifically, in the windward habitat, aboveground biomass of small-diameter trees declined over time (from 35.34 Mg ha
−1
to 26.29 Mg ha
−1
), and that of large-diameter trees increased (from 48.62 Mg ha
−1
to 57.78 Mg ha
−1
). In the leeward habitat, large-diameter trees exhibited both high biomass productivity (1.04 Mg ha
−1
year
−1
) and mortality (1.43 Mg ha
−1
year
−1
). Although the overall state of the forest appears to possess multi-decadal stability, differences in dynamics among diameter classes and habitats may lead to forest changes if trees in those habitats continue to respond differentially to shifting magnitudes of monsoon wind speed.</description><identifier>ISSN: 1385-0237</identifier><identifier>EISSN: 1573-5052</identifier><identifier>DOI: 10.1007/s11258-023-01360-y</identifier><language>eng</language><publisher>Dordrecht: Springer Netherlands</publisher><subject>aboveground biomass ; Applied Ecology ; Biodiversity ; Biomass ; biomass production ; Biomedical and Life Sciences ; Carbon sequestration ; climate ; Climate change ; Community & Population Ecology ; Density ; Dynamic stability ; Ecology ; Global temperature changes ; Habitats ; Health aspects ; Life Sciences ; monsoon season ; Monsoons ; Mortality ; Natural resources ; Plant Ecology ; Productivity ; Taiwan ; Terrestial Ecology ; tree and stand measurements ; Trees ; Tropical forests ; Vegetation ; vegetation structure ; Wind ; Wind speed ; Wind stress</subject><ispartof>Plant ecology, 2023-11, Vol.224 (11), p.1037-1048</ispartof><rights>The Author(s), under exclusive licence to Springer Nature B.V. 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.</rights><rights>COPYRIGHT 2023 Springer</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c419t-e6b68558608b02b1fadb08d4ed6a0e589a67a9cfc1e1eaa7aabf774dfac2d9ba3</citedby><cites>FETCH-LOGICAL-c419t-e6b68558608b02b1fadb08d4ed6a0e589a67a9cfc1e1eaa7aabf774dfac2d9ba3</cites><orcidid>0000-0001-7630-8018 ; 0000-0003-4063-0421 ; 0000-0002-7419-2282 ; 0000-0002-9266-3690 ; 0000-0002-2560-0710 ; 0000-0002-7340-0713 ; 0000-0003-2498-9012</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27900,27901</link.rule.ids></links><search><creatorcontrib>Ku, Chen-Chia</creatorcontrib><creatorcontrib>Tang, Jianwu</creatorcontrib><creatorcontrib>Chao, Wei-Chun</creatorcontrib><creatorcontrib>Chao, Kuo-Jung</creatorcontrib><creatorcontrib>Song, Guo-Zhang Michael</creatorcontrib><creatorcontrib>Lin, Huan-Yu</creatorcontrib><creatorcontrib>Lutz, James A.</creatorcontrib><title>Large-diameter trees buffer monsoonal changes to tree biomass over two decades</title><title>Plant ecology</title><addtitle>Plant Ecol</addtitle><description>Forest carbon storage inherently depends on the frequency and severity of characteristic disturbances and long-term changes in climate. The tropical forest of Lanjenchi, Taiwan is affected by the northeast monsoon wind, resulting in a varying vegetation structure depending on wind exposure. However, the northeast monsoon winds have been decreasing due to the climate change. We used four censuses over 22 years (1997, 2005, 2013, and 2019) to examine how tree density and aboveground biomass change under different levels of wind stress. We assessed tree density, aboveground biomass, aboveground woody productivity, and aboveground woody mortality from trees with diameter at breast height (DBH) ≥ 1 cm across 5.28 ha subdivided into 10 × 10 m quadrats. We tested for differences in tree density and aboveground biomass among three habitat types (windward, intermediate, and leeward), among small-diameter (1 cm ≤ DBH < 10 cm), medium-diameter (10 cm ≤ DBH < 17.2 cm) and large-diameter trees (DBH ≥ 17.2 cm). The 49,481 trees (density 9,272 ± 3612 trees ha
−1
) of 140 species held 129.37 ± 51.95 Mg ha
−1
of aboveground biomass. From 1997 to 2019, tree density decreased and aboveground biomass was stable in the whole forest. However, changes in density and aboveground biomass were apparent among different habitat types and among different diameter classes. Specifically, in the windward habitat, aboveground biomass of small-diameter trees declined over time (from 35.34 Mg ha
−1
to 26.29 Mg ha
−1
), and that of large-diameter trees increased (from 48.62 Mg ha
−1
to 57.78 Mg ha
−1
). In the leeward habitat, large-diameter trees exhibited both high biomass productivity (1.04 Mg ha
−1
year
−1
) and mortality (1.43 Mg ha
−1
year
−1
). Although the overall state of the forest appears to possess multi-decadal stability, differences in dynamics among diameter classes and habitats may lead to forest changes if trees in those habitats continue to respond differentially to shifting magnitudes of monsoon wind speed.</description><subject>aboveground biomass</subject><subject>Applied Ecology</subject><subject>Biodiversity</subject><subject>Biomass</subject><subject>biomass production</subject><subject>Biomedical and Life Sciences</subject><subject>Carbon sequestration</subject><subject>climate</subject><subject>Climate change</subject><subject>Community & Population Ecology</subject><subject>Density</subject><subject>Dynamic stability</subject><subject>Ecology</subject><subject>Global temperature changes</subject><subject>Habitats</subject><subject>Health aspects</subject><subject>Life Sciences</subject><subject>monsoon season</subject><subject>Monsoons</subject><subject>Mortality</subject><subject>Natural resources</subject><subject>Plant Ecology</subject><subject>Productivity</subject><subject>Taiwan</subject><subject>Terrestial Ecology</subject><subject>tree and stand measurements</subject><subject>Trees</subject><subject>Tropical forests</subject><subject>Vegetation</subject><subject>vegetation structure</subject><subject>Wind</subject><subject>Wind speed</subject><subject>Wind stress</subject><issn>1385-0237</issn><issn>1573-5052</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><recordid>eNp9kctOwzAQRSMEEqXwA6wisWGT4kdtJ8uq4iVVsIG1NXHGJVUSFzsF9e9xWqQKhFj5MeeMPL5JcknJhBKibgKlTOQZYTwjlEuSbY-SERWKZ4IIdhz3PBdDWZ0mZyGsCIkaF6PkaQF-iVlVQ4s9-rT3iCEtN9bGQ-u64FwHTWreoFvGQu92RFrWroUQUvcxOJ8urdBAheE8ObHQBLz4XsfJ693ty_whWzzfP85ni8xMadFnKEuZC5FLkpeEldRCVZK8mmIlgaDIC5AKCmMNRYoACqC0Sk0rC4ZVRQl8nFzv-669e99g6HVbB4NNAx26TdCcCi4EVZRE9OoXunIbH4cKmuUFlZKxQh2oJTSo68663oMZmuqZUlxOJeE0UpM_KBhGb2vjOrR1vP8hsL1gvAvBo9VrX7fgt5oSPSSn98npGI3eJae3UeJ7KUQ4frs_vPgf6wsg8Zt8</recordid><startdate>20231101</startdate><enddate>20231101</enddate><creator>Ku, Chen-Chia</creator><creator>Tang, Jianwu</creator><creator>Chao, Wei-Chun</creator><creator>Chao, Kuo-Jung</creator><creator>Song, Guo-Zhang Michael</creator><creator>Lin, Huan-Yu</creator><creator>Lutz, James A.</creator><general>Springer 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trees buffer monsoonal changes to tree biomass over two decades</title><author>Ku, Chen-Chia ; Tang, Jianwu ; Chao, Wei-Chun ; Chao, Kuo-Jung ; Song, Guo-Zhang Michael ; Lin, Huan-Yu ; Lutz, James A.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c419t-e6b68558608b02b1fadb08d4ed6a0e589a67a9cfc1e1eaa7aabf774dfac2d9ba3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2023</creationdate><topic>aboveground biomass</topic><topic>Applied Ecology</topic><topic>Biodiversity</topic><topic>Biomass</topic><topic>biomass production</topic><topic>Biomedical and Life Sciences</topic><topic>Carbon sequestration</topic><topic>climate</topic><topic>Climate change</topic><topic>Community & Population Ecology</topic><topic>Density</topic><topic>Dynamic stability</topic><topic>Ecology</topic><topic>Global temperature changes</topic><topic>Habitats</topic><topic>Health aspects</topic><topic>Life Sciences</topic><topic>monsoon season</topic><topic>Monsoons</topic><topic>Mortality</topic><topic>Natural resources</topic><topic>Plant Ecology</topic><topic>Productivity</topic><topic>Taiwan</topic><topic>Terrestial Ecology</topic><topic>tree and stand measurements</topic><topic>Trees</topic><topic>Tropical forests</topic><topic>Vegetation</topic><topic>vegetation structure</topic><topic>Wind</topic><topic>Wind speed</topic><topic>Wind stress</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Ku, Chen-Chia</creatorcontrib><creatorcontrib>Tang, Jianwu</creatorcontrib><creatorcontrib>Chao, Wei-Chun</creatorcontrib><creatorcontrib>Chao, Kuo-Jung</creatorcontrib><creatorcontrib>Song, Guo-Zhang Michael</creatorcontrib><creatorcontrib>Lin, Huan-Yu</creatorcontrib><creatorcontrib>Lutz, James A.</creatorcontrib><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Bacteriology Abstracts (Microbiology 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Ecol</stitle><date>2023-11-01</date><risdate>2023</risdate><volume>224</volume><issue>11</issue><spage>1037</spage><epage>1048</epage><pages>1037-1048</pages><issn>1385-0237</issn><eissn>1573-5052</eissn><abstract>Forest carbon storage inherently depends on the frequency and severity of characteristic disturbances and long-term changes in climate. The tropical forest of Lanjenchi, Taiwan is affected by the northeast monsoon wind, resulting in a varying vegetation structure depending on wind exposure. However, the northeast monsoon winds have been decreasing due to the climate change. We used four censuses over 22 years (1997, 2005, 2013, and 2019) to examine how tree density and aboveground biomass change under different levels of wind stress. We assessed tree density, aboveground biomass, aboveground woody productivity, and aboveground woody mortality from trees with diameter at breast height (DBH) ≥ 1 cm across 5.28 ha subdivided into 10 × 10 m quadrats. We tested for differences in tree density and aboveground biomass among three habitat types (windward, intermediate, and leeward), among small-diameter (1 cm ≤ DBH < 10 cm), medium-diameter (10 cm ≤ DBH < 17.2 cm) and large-diameter trees (DBH ≥ 17.2 cm). The 49,481 trees (density 9,272 ± 3612 trees ha
−1
) of 140 species held 129.37 ± 51.95 Mg ha
−1
of aboveground biomass. From 1997 to 2019, tree density decreased and aboveground biomass was stable in the whole forest. However, changes in density and aboveground biomass were apparent among different habitat types and among different diameter classes. Specifically, in the windward habitat, aboveground biomass of small-diameter trees declined over time (from 35.34 Mg ha
−1
to 26.29 Mg ha
−1
), and that of large-diameter trees increased (from 48.62 Mg ha
−1
to 57.78 Mg ha
−1
). In the leeward habitat, large-diameter trees exhibited both high biomass productivity (1.04 Mg ha
−1
year
−1
) and mortality (1.43 Mg ha
−1
year
−1
). Although the overall state of the forest appears to possess multi-decadal stability, differences in dynamics among diameter classes and habitats may lead to forest changes if trees in those habitats continue to respond differentially to shifting magnitudes of monsoon wind speed.</abstract><cop>Dordrecht</cop><pub>Springer Netherlands</pub><doi>10.1007/s11258-023-01360-y</doi><tpages>12</tpages><orcidid>https://orcid.org/0000-0001-7630-8018</orcidid><orcidid>https://orcid.org/0000-0003-4063-0421</orcidid><orcidid>https://orcid.org/0000-0002-7419-2282</orcidid><orcidid>https://orcid.org/0000-0002-9266-3690</orcidid><orcidid>https://orcid.org/0000-0002-2560-0710</orcidid><orcidid>https://orcid.org/0000-0002-7340-0713</orcidid><orcidid>https://orcid.org/0000-0003-2498-9012</orcidid></addata></record> |
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| ispartof | Plant ecology, 2023-11, Vol.224 (11), p.1037-1048 |
| issn | 1385-0237 1573-5052 |
| language | eng |
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| source | Springer Link |
| subjects | aboveground biomass Applied Ecology Biodiversity Biomass biomass production Biomedical and Life Sciences Carbon sequestration climate Climate change Community & Population Ecology Density Dynamic stability Ecology Global temperature changes Habitats Health aspects Life Sciences monsoon season Monsoons Mortality Natural resources Plant Ecology Productivity Taiwan Terrestial Ecology tree and stand measurements Trees Tropical forests Vegetation vegetation structure Wind Wind speed Wind stress |
| title | Large-diameter trees buffer monsoonal changes to tree biomass over two decades |
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