The species richness pattern and its component dependence of two typical secondary forests in central China
Secondary forests dominated by Masson pine (Pinus massoniana, MPF) and Chinese fir (Cunninghamia lanceolata, CFF) are widespread in the subtropical areas of China, whereas their biodiversity patterns receive far less attention than biomass patterns. This study aimed to gain insights into the species...
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Elsevier
2022-10-01
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Series: | Ecological Indicators |
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Online Access: | http://www.sciencedirect.com/science/article/pii/S1470160X22008433 |
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author | Guang Feng Jihong Huang Wenxing Long Xunru Ai Junqing Li Runguo Zang |
author_facet | Guang Feng Jihong Huang Wenxing Long Xunru Ai Junqing Li Runguo Zang |
author_sort | Guang Feng |
collection | DOAJ |
description | Secondary forests dominated by Masson pine (Pinus massoniana, MPF) and Chinese fir (Cunninghamia lanceolata, CFF) are widespread in the subtropical areas of China, whereas their biodiversity patterns receive far less attention than biomass patterns. This study aimed to gain insights into the species richness (SR) patterns of the typical natural secondary MPF and CFF in central China, with the old-growth zonal vegetation (evergreen-deciduous broadleaved mixed forest, EDBMF) used as reference. We established 45 plots across the three forest types and surveyed all the stems with a diameter at breast height ≥ 1 cm in each plot. Specifically, we compared the local (plot-level) and rarefied SR among the three forest types; at the metacommunity level, we examined the dependence of the rarefied SR difference between MPF and CFF on the number of individuals (N), species abundance distribution (SAD), and conspecific spatial aggregation (CSA); and we also assessed how local SR changed with N and species dominance within MPF and CFF. Our results showed that MPF had local and rarefied SR levels higher than CFF and closer to EDBMF. Both N and SAD had positive contributions to the high rarefied SR level of MPF (relative to CFF), while CSA had negative contributions. The N contributions were significant and dominated at most scale, the SAD contributions were considerable and significant at large scales, and the CSA contributions were significant at small and intermediate scales. Moreover, within MPF and CFF, local SR changed with N more generally than with species dominance. In conclusion, at both local and metacommunity level, MPF was generally more species-rich than CFF, and this difference remarkably depended on N, suggesting that the habitat conditions of CFF may be stressful for species persistence. Our findings also have several implications for biodiversity research and ecosystem management. |
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id | doaj.art-811c9165a3a943d59ac825819f8b66ea |
institution | Directory Open Access Journal |
issn | 1470-160X |
language | English |
last_indexed | 2024-04-12T21:16:09Z |
publishDate | 2022-10-01 |
publisher | Elsevier |
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series | Ecological Indicators |
spelling | doaj.art-811c9165a3a943d59ac825819f8b66ea2022-12-22T03:16:26ZengElsevierEcological Indicators1470-160X2022-10-01143109370The species richness pattern and its component dependence of two typical secondary forests in central ChinaGuang Feng0Jihong Huang1Wenxing Long2Xunru Ai3Junqing Li4Runguo Zang5Hainan Wuzhishan Forest Ecosystem Observation and Research Station, College of Forestry, Hainan University, Haikou, China; Key Laboratory of Tropical Forest Flower Genetics and Germplasm Innovation, Ministry of Education, Hainan University, Haikou, ChinaKey Laboratory of Forest Ecology and Environment of National Forestry and Grassland Administration, Ecology and Nature Conservation Institute, Chinese Academy of Forestry, Beijing, China; Co-Innovation Center for Sustainable Forestry in Southern China, Nanjing Forestry University, Nanjing, China; Corresponding author at: Key Laboratory of Forest Ecology and Environment of National Forestry and Grassland Administration, Ecology and Nature Conservation Institute, Chinese Academy of Forestry, Beijing, China.Hainan Wuzhishan Forest Ecosystem Observation and Research Station, College of Forestry, Hainan University, Haikou, China; Key Laboratory of Tropical Forest Flower Genetics and Germplasm Innovation, Ministry of Education, Hainan University, Haikou, ChinaEnshi Xingdoushan Forest Ecosystem Observation and Research Station, School of Forestry and Horticulture, Hubei Minzu University, Enshi, ChinaKey Laboratory for Silviculture and Conservation, Ministry of Education, Beijing Forestry University, Beijing, ChinaKey Laboratory of Forest Ecology and Environment of National Forestry and Grassland Administration, Ecology and Nature Conservation Institute, Chinese Academy of Forestry, Beijing, China; Co-Innovation Center for Sustainable Forestry in Southern China, Nanjing Forestry University, Nanjing, ChinaSecondary forests dominated by Masson pine (Pinus massoniana, MPF) and Chinese fir (Cunninghamia lanceolata, CFF) are widespread in the subtropical areas of China, whereas their biodiversity patterns receive far less attention than biomass patterns. This study aimed to gain insights into the species richness (SR) patterns of the typical natural secondary MPF and CFF in central China, with the old-growth zonal vegetation (evergreen-deciduous broadleaved mixed forest, EDBMF) used as reference. We established 45 plots across the three forest types and surveyed all the stems with a diameter at breast height ≥ 1 cm in each plot. Specifically, we compared the local (plot-level) and rarefied SR among the three forest types; at the metacommunity level, we examined the dependence of the rarefied SR difference between MPF and CFF on the number of individuals (N), species abundance distribution (SAD), and conspecific spatial aggregation (CSA); and we also assessed how local SR changed with N and species dominance within MPF and CFF. Our results showed that MPF had local and rarefied SR levels higher than CFF and closer to EDBMF. Both N and SAD had positive contributions to the high rarefied SR level of MPF (relative to CFF), while CSA had negative contributions. The N contributions were significant and dominated at most scale, the SAD contributions were considerable and significant at large scales, and the CSA contributions were significant at small and intermediate scales. Moreover, within MPF and CFF, local SR changed with N more generally than with species dominance. In conclusion, at both local and metacommunity level, MPF was generally more species-rich than CFF, and this difference remarkably depended on N, suggesting that the habitat conditions of CFF may be stressful for species persistence. Our findings also have several implications for biodiversity research and ecosystem management.http://www.sciencedirect.com/science/article/pii/S1470160X22008433Secondary forestNumber of individualsConspecific aggregationScaleSpecies abundance distributionSpecies richness |
spellingShingle | Guang Feng Jihong Huang Wenxing Long Xunru Ai Junqing Li Runguo Zang The species richness pattern and its component dependence of two typical secondary forests in central China Ecological Indicators Secondary forest Number of individuals Conspecific aggregation Scale Species abundance distribution Species richness |
title | The species richness pattern and its component dependence of two typical secondary forests in central China |
title_full | The species richness pattern and its component dependence of two typical secondary forests in central China |
title_fullStr | The species richness pattern and its component dependence of two typical secondary forests in central China |
title_full_unstemmed | The species richness pattern and its component dependence of two typical secondary forests in central China |
title_short | The species richness pattern and its component dependence of two typical secondary forests in central China |
title_sort | species richness pattern and its component dependence of two typical secondary forests in central china |
topic | Secondary forest Number of individuals Conspecific aggregation Scale Species abundance distribution Species richness |
url | http://www.sciencedirect.com/science/article/pii/S1470160X22008433 |
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