
Biodiv Sci ›› 2025, Vol. 33 ›› Issue (11): 25275. DOI: 10.17520/biods.2025275 cstr: 32101.14.biods.2025275
• Original Papers: Plant Diversity • Previous Articles Next Articles
Jihong Huang1(
), Erfan Akberjan2,3, Ruiming Cheng1, Wendong Wang4, Yue Xu1(
), Jie Yao1(
), Yi Ding1,*(
)(
)
Received:2025-07-17
Accepted:2025-10-21
Online:2025-11-20
Published:2025-12-26
Contact:
Yi Ding
Supported by:Jihong Huang, Erfan Akberjan, Ruiming Cheng, Wendong Wang, Yue Xu, Jie Yao, Yi Ding. Dynamics of the Picea schrenkiana community in the west Tianshan Mountains of Xinjiang and their influencing factors[J]. Biodiv Sci, 2025, 33(11): 25275.
Fig. 1 Location (A), contour map (B), and photographs of a typical Picea schrenkiana forest (C) in the 6-ha forest dynamics plot in the west Tianshan Mountains, Xinjiang
| 变量 Variables | 平均值 ± 标准差 Mean ± SD |
|---|---|
| 地形因子 Topographic factor | |
| 凹凸度 Convexity (Convex) | -0.11 ± 2.21 |
| 坡度 Slope | 21.56° ± 7.79° |
| 坡向 Aspect | 189.77° ± 50.18° |
| 土壤因子 Soil factor | |
| pH | 6.19 ± 0.37 |
| 土壤有机质含量 Soil organic matter content (g/kg) | 173.39 ± 64.08 |
| 有效氮含量 Available nitrogen content (mg/kg) | 191.47 ± 122.10 |
| 全氮含量 Total nitrogen content (g/kg) | 8.67 ± 2.66 |
| 有效磷含量 Available phosphorus content (mg/kg) | 37.56 ± 21.35 |
| 全磷含量 Total phosphorus content (g/kg) | 0.21 ± 0.04 |
Table 1 Basic information of topographic and soil factors of the 6-ha forest dynamics plot in the west Tianshan Mountains, Xinjiang
| 变量 Variables | 平均值 ± 标准差 Mean ± SD |
|---|---|
| 地形因子 Topographic factor | |
| 凹凸度 Convexity (Convex) | -0.11 ± 2.21 |
| 坡度 Slope | 21.56° ± 7.79° |
| 坡向 Aspect | 189.77° ± 50.18° |
| 土壤因子 Soil factor | |
| pH | 6.19 ± 0.37 |
| 土壤有机质含量 Soil organic matter content (g/kg) | 173.39 ± 64.08 |
| 有效氮含量 Available nitrogen content (mg/kg) | 191.47 ± 122.10 |
| 全氮含量 Total nitrogen content (g/kg) | 8.67 ± 2.66 |
| 有效磷含量 Available phosphorus content (mg/kg) | 37.56 ± 21.35 |
| 全磷含量 Total phosphorus content (g/kg) | 0.21 ± 0.04 |
| 物种 Species | 2008 | 2014 | 2019 | 2024 |
|---|---|---|---|---|
| 雪岭云杉 Picea schrenkiana | 1,310 (91.54%) | 1,341 (90.73%) | 1,210 (91.74%) | 1,123 (93.58%) |
| 天山桦 Betula tianschanica | 91 (6.36%) | 92 (6.22%) | 62 (4.70%) | 50 (4.17%) |
| 天山花楸 Sorbus tianschanica | 11 (0.77%) | 11 (0.74 %) | 7 (0.53%) | 3 (0.25%) |
| 新疆忍冬 Lonicera tatarica | 10 (0.70%) | 13 (0.88%) | 17 (1.29%) | 10 (0.83%) |
| 山楂 Crataegus pinnatifida | 3 (0.21%) | 3 (0.20%) | 3 (0.23%) | 3 (0.25%) |
| 黄花柳 Salix caprea | 3 (0.21%) | 3 (0.20%) | 4 (0.30%) | 4 (0.33%) |
| 伊犁小檗 Berberis iliensis | 2 (0.14%) | 14 (0.95%) | 16 (1.21%) | 7 (0.58%) |
| 新疆野苹果 Malus sieversii | 1 (0.07%) | 1 (0.07%) | 0 (0.00%) | 0 (0.00%) |
| 合计 Total | 1,431 (100.00%) | 1,478 (100.00%) | 1,319 (100.00%) | 1,200 (100.00%) |
Table 2 Changes in the number of living trees across different years (2008-2024) in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang
| 物种 Species | 2008 | 2014 | 2019 | 2024 |
|---|---|---|---|---|
| 雪岭云杉 Picea schrenkiana | 1,310 (91.54%) | 1,341 (90.73%) | 1,210 (91.74%) | 1,123 (93.58%) |
| 天山桦 Betula tianschanica | 91 (6.36%) | 92 (6.22%) | 62 (4.70%) | 50 (4.17%) |
| 天山花楸 Sorbus tianschanica | 11 (0.77%) | 11 (0.74 %) | 7 (0.53%) | 3 (0.25%) |
| 新疆忍冬 Lonicera tatarica | 10 (0.70%) | 13 (0.88%) | 17 (1.29%) | 10 (0.83%) |
| 山楂 Crataegus pinnatifida | 3 (0.21%) | 3 (0.20%) | 3 (0.23%) | 3 (0.25%) |
| 黄花柳 Salix caprea | 3 (0.21%) | 3 (0.20%) | 4 (0.30%) | 4 (0.33%) |
| 伊犁小檗 Berberis iliensis | 2 (0.14%) | 14 (0.95%) | 16 (1.21%) | 7 (0.58%) |
| 新疆野苹果 Malus sieversii | 1 (0.07%) | 1 (0.07%) | 0 (0.00%) | 0 (0.00%) |
| 合计 Total | 1,431 (100.00%) | 1,478 (100.00%) | 1,319 (100.00%) | 1,200 (100.00%) |
Fig. 2 Interannual variation (2008-2024) in DBH-classes distribution of living stems in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang. The bar shows the number of individuals corresponding to different DBH-classes across survey years. The line represents the fitted curves of individual numbers varying with DBH-classes in different survey years.
Fig. 3 Interannual (2008-2024) mortality distribution across DBH-classes in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang. The bar displays the number of dead individuals across different DBH-classes in various time periods. The line graph represents the fitted curve of dead individual numbers varying by DBH-classes over different time periods.
Fig. 4 Interannual (2008-2024) change rates of tree individual number (A) and aboveground biomass (AGB) (B) in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang
Fig. 5 Proportional contributions of biological, soil, and topographic factors to the recruitment rate (A), mortality rate (B), and turnover rate (C) in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang
Fig. 6 Factors influencing recruitment rate (A), mortality rate (B), and turnover rate (C) in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang. Convex, Convexity; SOM, Soil organic matter content; AN, Available nitrogen content; TN, Total nitrogen content; AP, Available phosphorus content; TP, Total phosphorus content. * P < 0.05; ** P < 0.01.
Fig. 7 The proportional contributions of biological, soil, and topographic factors to the aboveground biomass (AGB) recruitment (A), loss (B), growth (C), and net change (D) in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang
Fig. 8 Factors influencing to the aboveground biomass (AGB) recruitment (A), loss (B), growth (C), and net change (D) in the Picea schrenkiana community in the west Tianshan Mountains, Xinjiang. Convex, Convexity; SOM, Soil organic matter content; AN, Available nitrogen content; TN, Total nitrogen content; AP, Available phosphorus content; TP, Total phosphorus content. * P < 0.05; ** P < 0.01; *** P < 0.001.
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