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Plant diversity in giant panda habitat

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NIAID Data Ecosystem2026-03-12 收录
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http://datadryad.org/dataset/doi%253A10.5061%252Fdryad.rjdfn2z6b
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Understanding the relative importance of the factors driving the patterns of biodi- versity is a key research topic in community ecology and biogeography. However, the  main drivers of plant species diversity in montane forests are still not clear. In addi- tion, most existing studies make no distinction between direct and indirect effects of  environmental factors and spatial constraints on plant biodiversity. Using data from  107 montane forest plots in Sichuan Giant Panda habitat, China, we quantified the  direct and indirect effects of abiotic environmental factors, spatial constraints, and  plant functional traits on plant community diversity. Our results showed significant  correlations between abiotic environmental factors and trees (r = .10, p value = .001),  shrubs (r = .19, p value = .001), or overall plant diversity (r = .18, p value = .001) in mon- tane forests. Spatial constraints also showed significant correlations with trees and  shrubs. However, no significant correlations were found between functional traits  and plant community diversity. Moreover, the diversity (richness and abundance) of  shrubs, trees, and plant communities was directly affected by precipitation, latitude,  and altitude. Mean annual temperature (MAT) had no direct effect on the richness of  tree and plant communities. Further, MAT and precipitation indirectly affected plant  communities  via  the  tree  canopy.  The  results  revealed  a  stronger  direct  effect  on  montane plant diversity than indirect effect, suggesting that single-species models  may be adequate for forecasting the impacts of climate factors in these communities.  The shifting of tree canopy coverage might be a potential indicator for trends of plant  diversity under climate change. Methods In 2017, 107 random sampling plots in montane forests were collected  from north to south, spanning the entire Sichuan Giant Panda habi- tat. The sampling strategy and field site information are shown in Li et  al. (2019). The elevation within the sampling plots varied significantly  (from ca. 2,000 to 3,600 m a.s.l.) (Li et al., 2019). The main vegetation  types in those plots were coniferous and broad-leaved mixed forests,  and evergreen and deciduous broad-leaved mixed forests. Using ques- tionnaires, we surveyed 72 local people from Minshan, Xiaoxiangling,  and Qionglai in the Sichuan Giant Panda habitat in 2017. Those local  villagers mainly participated in the local Giant Panda habitat conser- vation.  The  survey  information  included  if  there  was  any  interfer- ence in the sampling plots. In addition, we observed the plant species  composition and environment in the montane forests to choose only  mature forests. We finally screened 107 mature forest sampling plots  without human interventions. Vegetation surveys were conducted be- tween July and September 2017 (the peak period of plant growth). All  plots were located at least 150 m from the road to avoid edge effects.  Within each plot, trees in a 20 m × 30 m subplot and shrubs from three  5 m × 5 m subplots were studied. Data from the three subplots within  each plot were then pooled. The plant species, number of individu- als (abundance), and coverage of each layer (e.g., tree, shrub) were re- corded (Table S1).
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2021-09-18
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