
生物多样性 ›› 2026, Vol. 34 ›› Issue (4): 25300. DOI: 10.17520/biods.2025300 cstr: 32101.14.biods.2025300
蒋翠憶1,2(
), 谢致敬1,*(
)(
), 田中平3,*(
)(
), 李玥莹1, 郑明心1, 房帅4(
), 米尔卡米力∙麦麦提5, 依里帆∙艾克拜尔江6,7, 高梅香8(
), 张健2(
)
收稿日期:2025-07-29
接受日期:2026-02-05
出版日期:2026-04-20
发布日期:2026-05-27
通讯作者:
谢致敬,田中平
基金资助:
Cuiyi Jiang1,2(
), Zhijing Xie1,*(
)(
), Zhongping Tian3,*(
)(
), Yueying Li1, Mingxin Zheng1, Shuai Fang4(
), Mierkamili Maimaiti5, Erfan Akberjan6,7, Meixiang Gao8(
), Jian Zhang2(
)
Received:2025-07-29
Accepted:2026-02-05
Online:2026-04-20
Published:2026-05-27
Contact:
Zhijing Xie, Zhongping Tian
Supported by:摘要:
微地形是调控局域物种分布格局和群落结构的关键驱动力之一。然而, 现有研究多集中于植物和微生物, 对土壤动物的研究仍显不足。跳虫作为对环境变化响应敏感的土壤指示生物, 其群落组成和多样性特征可有效反映微环境异质性。本研究以新疆巩留野核桃自然保护区土壤跳虫为研究对象, 选取阴坡、阳坡和沟谷3类典型的微地形生境, 系统调查跳虫群落组成及其环境因子, 分析微地形对土壤跳虫群落结构和多样性的影响。研究共获得跳虫1,548头, 隶属于6科12属19种。结果表明, 不同微地形类型间土壤月均温度、总磷及郁闭度均存在显著差异。微地形类型间跳虫群落组成亦存在显著差异, 而多样性虽差异不显著但呈现一定的空间分布趋势: 阴坡跳虫多样性指数高于阳坡, 而沟谷多样性指数最低; 属水平上呈现特有分布格局, 柳跳属(Willowsia)、长角跳属(Entomobrya)和刺齿跳属(Homidia)仅分布于阴坡, 奇跳属(Xenylla)则为阳坡特有; 土壤月均温度和铵态氮是影响跳虫群落组成的主要因子; 跳虫多度与土壤月均湿度呈显著负相关, 而水热条件与土壤养分间存在紧密耦合关系。研究揭示了微地形通过“植被-微气候-土壤”的耦合效应, 塑造了异质性的微环境条件, 进而驱动了跳虫群落的地理分异。
蒋翠憶, 谢致敬, 田中平, 李玥莹, 郑明心, 房帅, 米尔卡米力∙麦麦提, 依里帆∙艾克拜尔江, 高梅香, 张健 (2026) 微地形生境异质性对新疆西天山森林土壤跳虫群落分异的塑造作用. 生物多样性, 34, 25300. DOI: 10.17520/biods.2025300.
Cuiyi Jiang, Zhijing Xie, Zhongping Tian, Yueying Li, Mingxin Zheng, Shuai Fang, Mierkamili Maimaiti, Erfan Akberjan, Meixiang Gao, Jian Zhang (2026) The role of microtopography in shaping forest soil Collembola community assembly in western Tianshan Mountains of Xinjiang. Biodiversity Science, 34, 25300. DOI: 10.17520/biods.2025300.
| 微地形 Microtopography | 海拔 Elevation (m) | 植被类型 Vegetation type | 郁闭度 Canopy coverage (%) | 优势木本植物 Dominant woody plants |
|---|---|---|---|---|
| 阴坡 Shady | 1,228 | 森林 Forest | 33 | 新疆野苹果, 新疆野核桃 Malus sieversii, Juglans regia |
| 1,305 | 森林 Forest | 28 | 新疆野苹果, 新疆野核桃, 野杏 Malus sieversii, Juglans regia, Prunus armeniaca | |
| 1,454 | 森林 Forest | 51 | 新疆野苹果, 新疆野核桃, 天山柳 Malus sieversii, Juglans regia, Salix tianschanica | |
| 阳坡 Sunny | 1,251 | 灌丛 Shrub | 4 | 野杏, 金丝桃叶绣线菊 Prunus armeniaca, Spiraea hypericifolia |
| 1,328 | 灌丛 Shrub | 5 | 野杏, 准噶尔锦鸡儿 Prunus armeniaca, Caragana soongorica | |
| 1,448 | 灌丛 Shrub | 1 | 野杏, 金丝桃叶绣线菊 Prunus armeniaca, Spiraea hypericifolia | |
| 沟谷 Ravine | 1,225 | 森林 Forest | 53 | 新疆野苹果, 新疆野核桃 Malus sieversii, Juglans regia |
| 1,264 | 森林 Forest | 35 | 新疆野苹果, 新疆野核桃 Malus sieversii, Juglans regia | |
| 1,409 | 森林 Forest | 44 | 新疆野苹果, 新疆野核桃, 天山柳 Malus sieversii, Juglans regia, Salix tianschanica |
表1 新疆巩留野核桃自然保护区的微地形生境和植被概况
Table 1 Microtopographic habitats and vegetation in the Gongliu Wild Walnut Nature Reserve, Xinjiang
| 微地形 Microtopography | 海拔 Elevation (m) | 植被类型 Vegetation type | 郁闭度 Canopy coverage (%) | 优势木本植物 Dominant woody plants |
|---|---|---|---|---|
| 阴坡 Shady | 1,228 | 森林 Forest | 33 | 新疆野苹果, 新疆野核桃 Malus sieversii, Juglans regia |
| 1,305 | 森林 Forest | 28 | 新疆野苹果, 新疆野核桃, 野杏 Malus sieversii, Juglans regia, Prunus armeniaca | |
| 1,454 | 森林 Forest | 51 | 新疆野苹果, 新疆野核桃, 天山柳 Malus sieversii, Juglans regia, Salix tianschanica | |
| 阳坡 Sunny | 1,251 | 灌丛 Shrub | 4 | 野杏, 金丝桃叶绣线菊 Prunus armeniaca, Spiraea hypericifolia |
| 1,328 | 灌丛 Shrub | 5 | 野杏, 准噶尔锦鸡儿 Prunus armeniaca, Caragana soongorica | |
| 1,448 | 灌丛 Shrub | 1 | 野杏, 金丝桃叶绣线菊 Prunus armeniaca, Spiraea hypericifolia | |
| 沟谷 Ravine | 1,225 | 森林 Forest | 53 | 新疆野苹果, 新疆野核桃 Malus sieversii, Juglans regia |
| 1,264 | 森林 Forest | 35 | 新疆野苹果, 新疆野核桃 Malus sieversii, Juglans regia | |
| 1,409 | 森林 Forest | 44 | 新疆野苹果, 新疆野核桃, 天山柳 Malus sieversii, Juglans regia, Salix tianschanica |
| 微地形 Microtopography | 丰富度 Richness | lg多度 lgAbundance | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | Simpson优势度指数 Simpson dominance index | Pielou均匀度指数 Pielou evenness index |
|---|---|---|---|---|---|
| 阴坡 Shady | 6.33±0.33 | 2.68±0.29 | 1.53±0.09 | 0.75±0.03 | 0.58±0.05 |
| 阳坡 Sunny | 6.67±0.33 | 3.19±0.43 | 0.99±0.32 | 0.48±0.17 | 0.37±0.13 |
| 沟谷 Ravine | 4.00±1.53 | 2.66±0.19 | 0.66±0.33 | 0.35±0.18 | 0.27±0.14 |
表2 3种微地形生境的土壤跳虫多样性指数(平均值±标准误)
Table 2 Diversity index of soil Collembola in three microtopographic habitats (mean±SE)
| 微地形 Microtopography | 丰富度 Richness | lg多度 lgAbundance | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | Simpson优势度指数 Simpson dominance index | Pielou均匀度指数 Pielou evenness index |
|---|---|---|---|---|---|
| 阴坡 Shady | 6.33±0.33 | 2.68±0.29 | 1.53±0.09 | 0.75±0.03 | 0.58±0.05 |
| 阳坡 Sunny | 6.67±0.33 | 3.19±0.43 | 0.99±0.32 | 0.48±0.17 | 0.37±0.13 |
| 沟谷 Ravine | 4.00±1.53 | 2.66±0.19 | 0.66±0.33 | 0.35±0.18 | 0.27±0.14 |
| 阴坡 Shady | 阳坡 Sunny | 沟谷 Ravine | |
|---|---|---|---|
| 球角跳科 Hypogastruridae | 106.65±75.81 (15.99%) | 3,810.00±3,614.28 (90.44%) | 205.32±112.65 (37.26%) |
| 棘跳科 Onychiuridae | 253.47±114.08 (38.01%) | 296.69±62.78 (7.04%) | 267.91±147.78 (48.61%) |
| 等节跳科 Isotomidae | 272.75±136.80 (40.90%) | 4.94±2.47 (0.12%) | 54.42±35.07 (9.87%) |
| 疣跳科 Neanuridae | 14.44±14.44 (2.16%) | 94.11±42.66 (2.23%) | 22.22±22.22 (4.03%) |
| 长角跳科 Entomobryidae | 18.33±18.33 (2.75%) | 7.22±7.22 (0.17%) | 0±0 (0.00%) |
| 齿棘圆跳科 Arrhopalitidae | 1.23±1.23 (0.19%) | 0±0 (0.00%) | 1.23±1.23 (0.22%) |
表3 3种微地形生境的土壤跳虫群落科水平多度(ind./m2)及相对多度(%)
Table 3 Family-level abundance (ind./m²) and relative abundance (%) of soil Collembola communities in three microtopographic habitats
| 阴坡 Shady | 阳坡 Sunny | 沟谷 Ravine | |
|---|---|---|---|
| 球角跳科 Hypogastruridae | 106.65±75.81 (15.99%) | 3,810.00±3,614.28 (90.44%) | 205.32±112.65 (37.26%) |
| 棘跳科 Onychiuridae | 253.47±114.08 (38.01%) | 296.69±62.78 (7.04%) | 267.91±147.78 (48.61%) |
| 等节跳科 Isotomidae | 272.75±136.80 (40.90%) | 4.94±2.47 (0.12%) | 54.42±35.07 (9.87%) |
| 疣跳科 Neanuridae | 14.44±14.44 (2.16%) | 94.11±42.66 (2.23%) | 22.22±22.22 (4.03%) |
| 长角跳科 Entomobryidae | 18.33±18.33 (2.75%) | 7.22±7.22 (0.17%) | 0±0 (0.00%) |
| 齿棘圆跳科 Arrhopalitidae | 1.23±1.23 (0.19%) | 0±0 (0.00%) | 1.23±1.23 (0.22%) |
| 阴坡 Shady | 阳坡 Sunny | 沟谷 Ravine | |
|---|---|---|---|
| 奇跳属 Xenylla | 0±0 (0.00%) | 3,497.93±3,475.72 (83.03%) | 0±0 (0.00%) |
| 双棘跳属 Bionychiurus | 253.47±114.08 (38.01%) | 296.69±62.78 (7.04%) | 267.91±147.78 (48.61%) |
| 泡角跳属 Ceratophysella | 106.65±75.81 (15.99%) | 312.07±139.89 (7.41%) | 205.32±112.65 (37.26%) |
| 原等跳属 Proisotoma | 147.20±80.09 (22.07%) | 2.47±2.47 (0.06%) | 39.79±22.03 (7.22%) |
| 符跳属 Folsomia | 125.55±66.16 (18.83%) | 0±0 (0.00%) | 13.39±13.39 (2.43%) |
| 奇刺跳属 Friesea | 14.44±14.44 (2.16%) | 94.11±42.66 (2.23%) | 22.22±22.22 (4.03%) |
| 裸长角跳属 Sinella | 7.22±7.22 (1.08%) | 7.22±7.22 (0.17%) | 0±0 (0.00%) |
| 柳跳属 Willowsia | 6.17±6.17 (0.93%) | 0±0 (0.00%) | 0±0 (0.00%) |
| 德跳属 Desoria | 0±0 (0.00%) | 2.47±2.47 (0.06%) | 1.23±1.23 (0.22%) |
| 长角跳属 Entomobrya | 2.47±2.47 (0.37%) | 0±0 (0.00%) | 0±0 (0.00%) |
| 刺齿跳属 Homidia | 2.47±2.47 (0.37%) | 0±0 (0.00%) | 0±0 (0.00%) |
| 齿棘圆跳属 Arrhopalites | 1.23±1.23 (0.19%) | 0±0 (0.00%) | 1.23±1.23 (0.22%) |
表4 3种微地形生境的土壤跳虫群落属水平多度(ind./m2)及相对多度(%)
Table 4 Genus-level abundance (ind./m2) and relative abundance (%) of soil Collembola communities in three microtopographic habitats
| 阴坡 Shady | 阳坡 Sunny | 沟谷 Ravine | |
|---|---|---|---|
| 奇跳属 Xenylla | 0±0 (0.00%) | 3,497.93±3,475.72 (83.03%) | 0±0 (0.00%) |
| 双棘跳属 Bionychiurus | 253.47±114.08 (38.01%) | 296.69±62.78 (7.04%) | 267.91±147.78 (48.61%) |
| 泡角跳属 Ceratophysella | 106.65±75.81 (15.99%) | 312.07±139.89 (7.41%) | 205.32±112.65 (37.26%) |
| 原等跳属 Proisotoma | 147.20±80.09 (22.07%) | 2.47±2.47 (0.06%) | 39.79±22.03 (7.22%) |
| 符跳属 Folsomia | 125.55±66.16 (18.83%) | 0±0 (0.00%) | 13.39±13.39 (2.43%) |
| 奇刺跳属 Friesea | 14.44±14.44 (2.16%) | 94.11±42.66 (2.23%) | 22.22±22.22 (4.03%) |
| 裸长角跳属 Sinella | 7.22±7.22 (1.08%) | 7.22±7.22 (0.17%) | 0±0 (0.00%) |
| 柳跳属 Willowsia | 6.17±6.17 (0.93%) | 0±0 (0.00%) | 0±0 (0.00%) |
| 德跳属 Desoria | 0±0 (0.00%) | 2.47±2.47 (0.06%) | 1.23±1.23 (0.22%) |
| 长角跳属 Entomobrya | 2.47±2.47 (0.37%) | 0±0 (0.00%) | 0±0 (0.00%) |
| 刺齿跳属 Homidia | 2.47±2.47 (0.37%) | 0±0 (0.00%) | 0±0 (0.00%) |
| 齿棘圆跳属 Arrhopalites | 1.23±1.23 (0.19%) | 0±0 (0.00%) | 1.23±1.23 (0.22%) |
| 微地形 Microtopography | 土壤月均温度 MMST (℃) | 土壤月均湿度 MMSM | 土壤酸碱度 pH | 土壤有机碳 SOC (%) | 土壤铵态氮 NH4+-N (mg/kg) | 土壤总氮 TN (%) | 土壤总磷 TP (g/kg) | 郁闭度 CC |
|---|---|---|---|---|---|---|---|---|
| 阴坡 Shady | 13.78±0.59a | 0.35±0.01a | 7.13±0.13a | 6.61±0.33a | 6.57±1.47a | 0.52±0.06a | 0.98±0.08ab | 0.37±0.07b |
| 阳坡 Sunny | 15.85±0.72b | 0.30±0.05a | 7.23±0.07a | 5.07±0.62a | 4.88±0.61a | 0.72±0.07a | 0.84±0.19a | 0.03±0.01a |
| 沟谷 Ravine | 13.57±0.54a | 0.34±0.03a | 7.18±0.02a | 6.89±0.92a | 5.91±1.41a | 0.70±0.04a | 1.22±0.17b | 0.44±0.05b |
表5 3种微地形生境的环境条件差异(平均值±标准误)
Table 5 Environmental factors for three microtopographic habitats (mean±SE)
| 微地形 Microtopography | 土壤月均温度 MMST (℃) | 土壤月均湿度 MMSM | 土壤酸碱度 pH | 土壤有机碳 SOC (%) | 土壤铵态氮 NH4+-N (mg/kg) | 土壤总氮 TN (%) | 土壤总磷 TP (g/kg) | 郁闭度 CC |
|---|---|---|---|---|---|---|---|---|
| 阴坡 Shady | 13.78±0.59a | 0.35±0.01a | 7.13±0.13a | 6.61±0.33a | 6.57±1.47a | 0.52±0.06a | 0.98±0.08ab | 0.37±0.07b |
| 阳坡 Sunny | 15.85±0.72b | 0.30±0.05a | 7.23±0.07a | 5.07±0.62a | 4.88±0.61a | 0.72±0.07a | 0.84±0.19a | 0.03±0.01a |
| 沟谷 Ravine | 13.57±0.54a | 0.34±0.03a | 7.18±0.02a | 6.89±0.92a | 5.91±1.41a | 0.70±0.04a | 1.22±0.17b | 0.44±0.05b |
图4 土壤跳虫多样性与环境因子间的相关性分析。数字表示Pearson相关系数(r)值; 蓝色代表正相关, 橙色代表负相关; 颜色深浅表示相关性强弱。pH: 土壤酸碱度; SOC: 土壤有机碳; NH4+-N: 土壤铵态氮; TN: 土壤总氮; TP: 土壤总磷; CC: 郁闭度; MMST: 土壤月均温度; MMSM: 土壤月均湿度; Shannon: Shannon-Wiener多样性指数; Simpson: Simpson优势度指数; Richness: 丰富度; Pielou: Pielou均匀度指数; lgAbundance: lg多度。*P<0.05; **P<0.01。
Fig. 4 Correlation analysis of soil Collembola community diversity and environmental factors. The number represents the Pearson correlation coefficient (r) value. Blue represents a positive correlation, and orange represents a negative correlation; The shade of color indicates the strength of the correlation. pH, Soil pH; SOC, Soil organic carbon; NH4+-N, Ammonium nitrogen; TN, Total nitrogen; TP, Total phosphorus; CC, Canopy coverage; MMST, Monthly mean soil temperature; MMSM, Monthly mean soil moisture; Shannon, Shannon-Wiener diversity index; Simpson, Simpson dominance index; Richness, Richness; Pielou, Pielou evenness index. *P<0.05; **P<0.01.
图5 不同微地形生境的土壤跳虫群落结构与环境因子间的冗余分析
Fig. 5 Redundancy analysis of soil Collembola community structure and environmental factors in different microtopographic habitats. MMST, Monthly mean soil temperature; NH4+-N, Ammonium nitrogen.
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