青藏高原灌丛化与氮添加对土壤线虫群落及功能性状的交互作用

doi:10.17521/cjpe.2025.0119

植物生态学报 ›› 2026, Vol. 50 ›› Issue (4): 859-869.DOI: 10.17521/cjpe.2025.0119 cstr: 32100.14.cjpe.2025.0119

青藏高原灌丛化与氮添加对土壤线虫群落及功能性状的交互作用

张安宁¹, 肖亚宁², 赵霞², 张淼¹, 崔瀚文², 陈书燕¹^,^*(), 安黎哲¹^,³^,^*()

¹ 兰州大学生命科学学院, 兰州 730000
² 兰州大学生态学院, 兰州 730000
³ 北京林业大学林木资源高效生产全国重点实验室, 北京 100083

收稿日期:2025-04-02 接受日期:2025-09-09 出版日期:2026-04-20 发布日期:2026-06-25
通讯作者: *陈书燕, chenshy@lzu.edu.cn;
安黎哲, anlizhe@bjfu.edu.cn
基金资助:
国家自然科学基金(41830321);国家自然科学基金(32471559);国家自然科学基金(32460262和325B2066);甘肃省自然科学基金(24JRRA433);甘肃省自然科学基金(25JRRE015)

Interactions between shrub encroachment and nitrogen addition on nematode community and functional traits on Qingzang Plateau

ZHANG An-Ning¹, XIAO Ya-Ning², ZHAO Xia², ZHANG Miao¹, CUI Han-Wen², CHEN Shu-Yan¹^,^*(), AN Li-Zhe¹^,³^,^*()

¹ School of Life Sciences, Lanzhou University, Lanzhou 730000, China
² College of Ecology, Lanzhou University, Lanzhou 730000, China
³ State Key Laboratory of Efficient Production of Forest Resources, Beijing Forestry University, Beijing 100083, China

Received:2025-04-02 Accepted:2025-09-09 Online:2026-04-20 Published:2026-06-25
Contact: *CHEN Shu-Yan, chenshy@lzu.edu.cn;
AN Li-Zhe, anlizhe@bjfu.edu.cn
Supported by:
National Natural Science Foundation of China(41830321);National Natural Science Foundation of China(32471559);National Natural Science Foundation of China(32460262);National Natural Science Foundation of China(325B2066);Natural Science Foundation of Gansu Province(24JRRA433);Natural Science Foundation of Gansu Province(25JRRE015)

摘要/Abstract

摘要： 线虫是地下生物群落的重要组成部分, 在维持生态系统结构与功能中起着至关重要的作用。全球环境变化, 如灌丛化和氮沉降, 已成为生物群落结构和功能变化的重要驱动因素。不同环境因子会共同影响生物多样性, 而灌丛化和氮沉降间的交互作用对土壤线虫功能多样性的影响尚不清晰。该研究在青藏高原东缘开展了灌木移除和氮添加的控制实验, 使用核密度N维超体积法计算线虫功能多样性, 探究线虫对灌木、氮沉降及其交互作用的响应。结果表明: (1)灌木显著增加了线虫物种多样性并改变了其群落组成, 但该效应受氮添加影响较小。(2)灌木显著增加了线虫功能多样性, 而氮添加将削弱灌木对功能多样性的促进作用。(3)灌木改变了不同食性线虫多度占比, 显著增加了植食性、食细菌性和食真菌性线虫占比, 但显著降低了捕食性线虫占比。此外, 氮添加加剧了灌木对低营养级线虫的促进作用和对高营养级线虫的抑制作用。(4)相关性和冗余分析(RDA)表明, 植物生物量和土壤水分含量是影响线虫群落组成和功能性状的关键驱动因子。在灌丛化和大气氮沉降背景下, 线虫功能多样性将更加相似。

关键词: 土壤线虫, 功能多样性, 功能性状, 灌木效应, 氮添加, 青藏高原

Abstract:

Aims Nematodes are a key component of belowground communities that maintain ecosystem structure and function. Global environmental changes, such as shrub encroachment and nitrogen deposition, have become key drivers of changes in belowground community structure and function. While multiple environmental factors may jointly influence biodiversity, the interactive effects of shrub encroachment and nitrogen deposition on soil nematode functional diversity remain poorly understood.

Methods In this study, we conducted a controlled experiment involving shrub removal and nitrogen addition on the eastern edge of Qingzang Plateau. We used the kernel density N-dimensional hypervolumes method to calculate nematode functional diversity and explore the response of nematodes to shrubs, nitrogen deposition, and their interactions.

Important findings Shrubs significantly increased nematode taxonomic diversity and altered their community composition, but these effects were less affected by nitrogen addition. Shrubs significantly increased nematode functional diversity, while nitrogen addition mitigated this positive effect. Shrubs altered the abundance proportion of nematodes with different diets, significantly increasing the proportion of herbivorous, bacterivorous, and fungivorous nematodes, but significantly decreasing the proportion of predatory nematodes. Moreover, nitrogen addition exacerbated the positive effects of shrub on lower trophic level nematodes and the negative effects on higher trophic level nematodes. Correlation and redundancy analysis (RDA) indicated that plant biomass and soil moisture were key factors driving nematode community composition and functional traits. Our findings suggest that under future nitrogen deposition and shrub encroachment, nematode functional diversity will become more homogenized.

Key words: soil nematode, functional diversity, functional trait, shrub effect, nitrogen addition, Qingzang Plateau

张安宁, 肖亚宁, 赵霞, 张淼, 崔瀚文, 陈书燕, 安黎哲. 青藏高原灌丛化与氮添加对土壤线虫群落及功能性状的交互作用. 植物生态学报, 2026, 50(4): 859-869. DOI: 10.17521/cjpe.2025.0119

ZHANG An-Ning, XIAO Ya-Ning, ZHAO Xia, ZHANG Miao, CUI Han-Wen, CHEN Shu-Yan, AN Li-Zhe. Interactions between shrub encroachment and nitrogen addition on nematode community and functional traits on Qingzang Plateau. Chinese Journal of Plant Ecology, 2026, 50(4): 859-869. DOI: 10.17521/cjpe.2025.0119

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://www.plant-ecology.com/CN/10.17521/cjpe.2025.0119

https://www.plant-ecology.com/CN/Y2026/V50/I4/859

图/表 9

图1 灌木移除、氮添加及其交互作用对线虫物种多样性的影响。不同小写字母表示差异显著(p < 0.05)。

Fig. 1 Effects of shrub removal, nitrogen (N) addition, and their interaction on the nematode taxonomic diversity. Different lowercase letters indicate significant difference (p < 0.05).

图2 灌木移除、氮添加及其交互作用对土壤线虫群落组成的影响。CC, 灌木移除及不添加氮; CN, 灌木移除及添加氮; SC, 灌木存在及不添加氮; SN, 灌木存在及添加氮。NMDS, 非度量多维尺度分析。

Fig. 2 Effects of shrub removal, nitrogen (N) addition, and their interaction on the nematode community composition. CC, shrub removal and no N addition; CN, shrub removal and N addition; SC, with shrub and no N addition; SN, with shrub and N addition. NMDS, non-metric multidimensional scaling analysis.

图3 灌木移除、氮添加及其交互作用对线虫属相对丰度影响的堆积图。CC, 灌木移除及不添加氮; CN, 灌木移除及添加氮; SC, 灌木存在及不添加氮; SN, 灌木存在及添加氮。

Fig. 3 Stacked bar of the effects of shrub removal, nitrogen addition, and their interaction on the relative abundance of nematode genera. CC, shrub removal and no nitrogen addition; CN, shrub removal and nitrogen addition; SC, with shrub and no nitrogen addition; SN, with shrub and nitrogen addition.

表1 灌木移除、氮添加及其交互作用对前15个线虫属丰度的影响(平均值±标准误)

Table 1 Effects of shrub removal, nitrogen addition, and their interaction on the abundance of first 15 nematode genera (mean ± SE)

线虫属 Nematode	对照 Control		氮添加 Nitrogen addition		p
线虫属 Nematode	灌木存在 With shrub	灌木移除 Shrub removal	灌木存在 With shrub	灌木移除 Shrub removal	灌木效应 Shrub	氮效应 Nitrogen	交互作用 Shrub × nitrogen
拟丽突属 Acrobeloides	12.44 ± 3.69^a	23.43 ± 4.99^a	15.64 ± 4.16^a	2.40 ± 1.17^b	0.075	<0.001	<0.001
中杆属 Mesorhabditis	10.31 ± 4.30^ab	1.94 ± 1.16^b	10.94 ± 24.45^a	3.08 ± 1.82^ab	0.012	0.464	0.635
原矛属 Prodorylaimium	4.82 ± 2.28^b	1.82 ± 1.04^b	0.91 ± 0.53^b	15.21 ± 4.37^a	0.946	0.076	0.002
垫刃属 Tylenchus	7.95 ± 3.44^a	2.81 ± 1.68^a	9.27 ± 3.63^a	2.50 ± 1.36^a	0.167	0.864	0.746
真矛属 Eudorylaimus	3.47 ± 1.91^ab	0.84 ± 0.58^b	3.51 ± 1.92^ab	9.45 ± 4.45^a	0.034	<0.001	0.004
类滑刃属 Aphelenchoides	4.26 ± 2.87^a	4.30 ± 2.57^a	3.66 ± 2.31^a	1.58 ± 1.10^a	0.986	0.083	0.279
滑刃属 Aphelenchus	7.04 ± 1.86^a	0.46 ± 0.26^b	9.86 ± 2.21^a	0.22 ± 0.13^b	<0.001	0.258	0.138
盘旋属 Rotylenchus	8.72 ± 3.55^a	1.38 ± 0.82^b	2.98 ± 1.62^ab	2.57 ± 1.43^ab	0.002	0.318	0.045
单齿属 Mononchus	1.26 ± 0.76^b	1.27 ± 0.76^b	2.42 ± 1.35^ab	10.08 ± 3.73^a	0.998	<0.001	0.086
盆咽属 Panagrolaimus	2.77 ± 1.52^a	2.66 ± 1.36^a	1.80 ± 0.97^a	4.30 ± 2.21^a	0.937	0.341	0.246
异头叶属 Pseudacrobeles	5.80 ± 1.36^a	0.57 ± 0.29^b	7.61 ± 1.56^a	0.11 ± 0.07^c	<0.001	0.010	0.007
锉齿属 Mylonchulus	1.81 ± 1.16^a	5.50 ± 2.83^a	2.27 ± 1.25^a	2.36 ± 1.30^a	0.097	0.184	0.219
钵盘属 Mylodiscus	2.12 ± 1.19^ab	7.22 ± 2.95^a	1.13 ± 0.69^b	1.22 ± 0.73^b	0.035	0.003	0.167
大矛属 Enchodelus	0.33 ± 0.22^b	0.41 ± 0.28^b	0.41 ± 0.28^b	10.51 ± 3.12^a	0.733	<0.001	<0.001
绕线属 Plectus	5.01 ± 1.00^a	0.12 ± 0.07^b	6.42 ± 1.14^a	0.07 ± 0.04^b	<0.001	0.373	0.231

表1 灌木移除、氮添加及其交互作用对前15个线虫属丰度的影响(平均值±标准误)

Table 1 Effects of shrub removal, nitrogen addition, and their interaction on the abundance of first 15 nematode genera (mean ± SE)

线虫属 Nematode	对照 Control		氮添加 Nitrogen addition		p
线虫属 Nematode	灌木存在 With shrub	灌木移除 Shrub removal	灌木存在 With shrub	灌木移除 Shrub removal	灌木效应 Shrub	氮效应 Nitrogen	交互作用 Shrub × nitrogen
拟丽突属 Acrobeloides	12.44 ± 3.69^a	23.43 ± 4.99^a	15.64 ± 4.16^a	2.40 ± 1.17^b	0.075	<0.001	<0.001
中杆属 Mesorhabditis	10.31 ± 4.30^ab	1.94 ± 1.16^b	10.94 ± 24.45^a	3.08 ± 1.82^ab	0.012	0.464	0.635
原矛属 Prodorylaimium	4.82 ± 2.28^b	1.82 ± 1.04^b	0.91 ± 0.53^b	15.21 ± 4.37^a	0.946	0.076	0.002
垫刃属 Tylenchus	7.95 ± 3.44^a	2.81 ± 1.68^a	9.27 ± 3.63^a	2.50 ± 1.36^a	0.167	0.864	0.746
真矛属 Eudorylaimus	3.47 ± 1.91^ab	0.84 ± 0.58^b	3.51 ± 1.92^ab	9.45 ± 4.45^a	0.034	<0.001	0.004
类滑刃属 Aphelenchoides	4.26 ± 2.87^a	4.30 ± 2.57^a	3.66 ± 2.31^a	1.58 ± 1.10^a	0.986	0.083	0.279
滑刃属 Aphelenchus	7.04 ± 1.86^a	0.46 ± 0.26^b	9.86 ± 2.21^a	0.22 ± 0.13^b	<0.001	0.258	0.138
盘旋属 Rotylenchus	8.72 ± 3.55^a	1.38 ± 0.82^b	2.98 ± 1.62^ab	2.57 ± 1.43^ab	0.002	0.318	0.045
单齿属 Mononchus	1.26 ± 0.76^b	1.27 ± 0.76^b	2.42 ± 1.35^ab	10.08 ± 3.73^a	0.998	<0.001	0.086
盆咽属 Panagrolaimus	2.77 ± 1.52^a	2.66 ± 1.36^a	1.80 ± 0.97^a	4.30 ± 2.21^a	0.937	0.341	0.246
异头叶属 Pseudacrobeles	5.80 ± 1.36^a	0.57 ± 0.29^b	7.61 ± 1.56^a	0.11 ± 0.07^c	<0.001	0.010	0.007
锉齿属 Mylonchulus	1.81 ± 1.16^a	5.50 ± 2.83^a	2.27 ± 1.25^a	2.36 ± 1.30^a	0.097	0.184	0.219
钵盘属 Mylodiscus	2.12 ± 1.19^ab	7.22 ± 2.95^a	1.13 ± 0.69^b	1.22 ± 0.73^b	0.035	0.003	0.167
大矛属 Enchodelus	0.33 ± 0.22^b	0.41 ± 0.28^b	0.41 ± 0.28^b	10.51 ± 3.12^a	0.733	<0.001	<0.001
绕线属 Plectus	5.01 ± 1.00^a	0.12 ± 0.07^b	6.42 ± 1.14^a	0.07 ± 0.04^b	<0.001	0.373	0.231

图4 灌木移除、氮添加及其交互作用对土壤线虫功能多样性的影响。不同小写字母表示差异显著(p < 0.05)。

Fig. 4 Effects of shrub removal, nitrogen (N) addition, and their interaction on the nematode functional diversity. Different lowercase letters indicate significant difference (p < 0.05).

图5 灌木移除、氮添加及其交互作用对土壤线虫群落功能性状的影响。A, 线虫C-P值的群落加权平均值。B, 线虫生物量的群落加权平均值。C, 食细菌性线虫占比。D, 食真菌性线虫占比。E, 植食性线虫占比。F, 捕食性线虫占比。G, 杂食性线虫占比。占比为多度占比。不同小写字母表示差异显著(p < 0.05)。

Fig. 5 Effects of shrub removal, nitrogen (N) addition, and their interaction on the functional traits of nematode communities. A, Community weighted mean of nematode C-P value. B, Community weighted mean of nematode biomass. C, Bacterivore nematode proportion. D, Fungivore nematode proportion. E, Herbivore nematode proportion. F, Predator nematode proportion. G, Omnivore nematode proportion. Proportion refers to abundance proportion. Different lowercase letters indicate significant difference (p < 0.05).

表2 土壤线虫多样性及功能性状与环境因子间的相关关系

Table 2 Correlation between the diversity and functional traits of soil nematodes and environmental factors

线虫指标 Nematode indicator	土壤 pH	电导率 Electrical conductivity	含水量 Soil moisture	土壤总磷含量 Total phosphorus content	土壤硝态氮含量 Ammonium nitrogen content	土壤铵态氮含量 Nitrate nitrogen content	植物生物量 Plant biomass	植物丰富度 Plant richness
物种多样性 Taxonomic diversity	-0.096	0.168	0.083	-0.535^*	0.043	0.025	-0.253	-0.032
功能多样性 Functional diversity	-0.001	0.090	0.184	-0.342	0.072	-0.145	-0.171	-0.020
C-P值 C-P value	0.139	-0.125	0.412	0.108	-0.498^*	0.089	0.350	0.275
线虫生物量 Biomass	0.233	0.195	0.554^*	-0.458^*	-0.394	0.060	-0.055	0.094
食细菌性占比 Bacterivore proportion	-0.068	0.199	-0.341	-0.044	0.462^*	-0.131	-0.301	-0.154
食真菌性占比 Fungivore proportion	-0.047	0.072	-0.175	-0.321	0.216	0.063	0.486^*	-0.356
植食性占比 Herbivore proportion	-0.136	0.136	-0.372	-0.134	0.168	0.013	-0.278	-0.227
杂食性占比 Omnivore proportion	-0.103	-0.170	0.165	0.091	-0.226	0.206	0.397	0.078
捕食性占比 Predator proportion	0.269	-0.191	0.546^*	0.224	-0.522^*	-0.076	0.415	0.427

图6 土壤线虫群落分布与环境因子关系的冗余分析(RDA)二维排序图。红线表示线虫属, 蓝线表示环境因子。EC, 电导率; NH+4-N, 土壤铵态氮含量; NO-3-N, 土壤硝态氮含量; PB, 植物生物量; pH, 土壤pH; PR, 植物丰富度; SM, 土壤含水量; TP, 土壤总磷含量。Acrobeloides, 拟丽突属; Alaimus, 无咽属; Allodorylaimus, 异矛线属; Anaplectus, 似绕线属; Aphelenchoides, 类滑刃属; Aphelenchus, 滑刃属; Aporcelaimus, 孔咽属; Cephalobus, 头叶属; Enchodelus, 大矛属; Filenchus, 丝垫刃属; Iotonchus, 基齿属; Labronema, 厚唇属; Miconchus, 等齿属; Mononchus, 单齿属; Mylodiscus, 钵盘属; Mylonchulus, 锉齿属; Plectus, 绕线属; Prodorylaimium, 原矛线属; Protorhabditis, 原杆属; Pseudacrobeles, 异头叶属; Rotylenchus, 盘旋属; Panagrolaimus, 盆咽属; Paratimminema, 库氏线属; Tylenchorhynchus, 矮化属; Tylenchus, 垫刃属; Tylopharynx, 瘤咽属。部分属名位于原点附近, 被遮盖, 有Coomansus, 库曼属; Criconemoides, 轮属; Dorylaimoides, 拟矛线属; Dorylaimus, 矛线属; Epidorylaimus, 附矛线属; Eudorylaimus, 真矛属; Helicotylenchus, 螺旋属; Laimydorus, 咽矛线属; Mesodorylaimus, 中矛线属; Mesorhabditis, 中杆属; Mononchoides, 拟独齿属。

Fig. 6 Redundancy analysis (RDA) of two-dimensional diagram of the relationship between soil nematode community distribution and environment factors. Red lines represent nematode genera, and blue lines represent environmental factors. EC, electrical conductivity; NH+4-N, ammonium nitrogen content; NO-3-N, nitrate nitrogen content; PB, plant biomass; pH, soil pH; PR, plant richness; SM, soil moisture; TP, total phosphorus content.

表3 环境因子对土壤线虫群落组成影响的冗余分析

Table 3 Redundancy analysis of the effect of environment factors on the nematode community composition

变量 Variable	df	F	p
土壤含水量 Soil moisture	1	2.505	0.010
植物生物量 Plant biomass	1	2.180	0.027
土壤总磷含量 Soil total phosphorus content	1	1.622	0.092
电导率 Electrical conductivity	1	1.211	0.247
土壤pH Soil pH	1	0.891	0.547
土壤硝态氮含量 Soil ammonium nitrogen content	1	1.313	0.191
土壤铵态氮含量 Soil nitrate nitrogen content	1	1.254	0.223
植物丰富度 Plant richness	1	0.838	0.581
残差 Residual	11

参考文献 30

[1]	An XL, Zhang ZH, Yang JP (2024). Expansion dynamics of the alpine shrub Potentilla fruticosa. Pratacultural Science, 41, 2823-2832.
	[安栩立, 张振华, 杨建平 (2024). 青藏高原高寒灌木金露梅扩张态势分析. 草业科学, 41, 2823-2832.]
[2]	Andriuzzi WS, Franco ALC, Ankrom KE, Cui SY, de Tomasel CM, Guan PT, Gherardi LA, Sala OE, Wall DH (2020). Body size structure of soil fauna along geographic and temporal gradients of precipitation in grasslands. Soil Biology & Biochemistry, 140, 107638. DOI: 10.1016/j.soilbio.2019.107638.
[3]	Aranibar JN, Otter L, Macko SA, Feral CJW, Epstein HE, Dowty PR, Eckardt F, Shugart HH, Swap RJ (2004). Nitrogen cycling in the soil-plant system along a precipitation gradient in the Kalahari sands: nitrogen cycling in the Kalahari. Global Change Biology, 10, 359-373. DOI URL
[4]	Bao SD (2000). Soil and Agrochemistry Analysis. 3 rd ed. China Agriculture Press, Beijing.
	[鲍士旦 (2000) 土壤农化分析(第三版). 中国农业出版社, 北京.]
[5]	Biederman LA, Boutton TW (2009). Biodiversity and trophic structure of soil nematode communities are altered following woody plant invasion of grassland. Soil Biology & Biochemistry, 41, 1943-1950. DOI URL
[6]	Blonder B (2016). Do hypervolumes have holes? The American Naturalist, 187, E93-E105.
[7]	Collins CG, Stajich JE, Weber SE, Pombubpa N, Diez JM (2018). Shrub range expansion alters diversity and distribution of soil fungal communities across an alpine elevation gradient. Molecular Ecology, 27, 2461-2476. DOI PMID
[8]	Erktan A, Or D, Scheu S (2020). The physical structure of soil: determinant and consequence of trophic interactions. Soil Biology & Biochemistry, 148, 107876. DOI: 10.1016/j.soilbio.2020.107876
[9]	Fitoussi N, Pen-Mouratov S, Steinberger Y (2016). Soil free-living nematodes as bio-indicators for assaying the invasive effect of the alien plant Heterotheca subaxillaris in a coastal dune ecosystem. Applied Soil Ecology, 102, 1-9. DOI URL
[10]	Franco ALC, Gherardi LA, de Tomasel CM, Andriuzzi WS, Ankrom KE, Shaw EA, Bach EM, Sala OE, Wall DH (2019). Drought suppresses soil predators and promotes root herbivores in mesic, but not in xeric grasslands. Proceedings of the National Academy of Sciences of the United States of America, 116, 12883-12888. DOI PMID
[11]	Gao Z, Huang J, Gao W, Jia MQ, Li XD, Han GD, Zhang GG (2023). Exploring the effects of warming and nitrogen deposition on desert steppe based on soil nematodes. Land Degradation & Development, 34, 682-697. DOI URL
[12]	He X, Bai MM, Xu CL, Song MJ, Wang PB, Yu XJ (2021). Soil and vegetation successional responses in natural restoration of mixed Potentilla parvifolia-Salix cupularis shrubland in the Eastern Qilian Mountains. Acta Prataculturae Sinica, 30(8), 12-24.
	[贺翔, 白梅梅, 徐长林, 宋美娟, 汪鹏斌, 鱼小军 (2021). 东祁连山小叶金露梅+杯腺柳灌丛草地植被和土壤对其自然恢复演替的响应. 草业学报, 30(8), 12-24.] DOI
[13]	Hodson AK, Ferris H, Hollander AD, Jackson LE (2014). Nematode food webs associated with native perennial plant species and soil nutrient pools in California riparian oak woodlands. Geoderma, 228, 182-191.
[14]	Li XP, Zhu HM, Geisen S, Bellard C, Hu F, Li HX, Chen XY, Liu MQ (2020). Agriculture erases climate constraints on soil nematode communities across large spatial scales. Global Change Biology, 26, 919-930. DOI PMID
[15]	Liu T, Guo R, Ran W, Whalen JK, Li HX (2015). Body size is a sensitive trait-based indicator of soil nematode community response to fertilization in rice and wheat agroecosystems. Soil Biology & Biochemistry, 88, 275-281. DOI URL
[16]	Liu WX, Liu LL, Yang X, Deng MF, Wang Z, Wang PD, Yang S, Li P, Peng ZY, Yang L, Jiang L (2021). Long-term nitrogen input alters plant and soil bacterial, but not fungal beta diversity in a semiarid grassland. Global Change Biology, 27, 3939-3950. DOI URL
[17]	Mammola S, Cardoso P (2020). Functional diversity metrics using kernel density n-dimensional hypervolumes. Methods in Ecology and Evolution, 11, 986-995. DOI URL
[18]	Wang GX, Mao TX, Chang J, Du JZ (2014). Impacts of surface soil organic content on the soil thermal dynamics of alpine meadows in permafrost regions: data from field observations. Geoderma, 232, 414-425.
[19]	Wang HY, Wu JQ, Li G, Yan LJ, Wei XX, Ma WW (2022). Effects of simulated nitrogen deposition on soil active carbon fractions in a wet meadow in the Qinghai-Tibet Plateau. Journal of Soil Science and Plant Nutrition, 22, 2943-2954. DOI
[20]	Wang XT, Xiao S, Yang XL, Liu ZY, Zhou XH, Du GZ, Zhang LM, Guo AF, Chen SY, Nielsen UN (2019). Dominant plant species influence nematode richness by moderating understory diversity and microbial assemblages. Soil Biology & Biochemistry, 137, 107566. DOI: 10.1016/j.soilbio.2019.107566.
[21]	Wang YF, Liang EY, Lu XM, Camarero JJ, Babst F, Shen MG, Peñuelas J (2021). Warming-induced shrubline advance stalled by moisture limitation on the Tibetan Plateau. Ecography, 44, 1631-1641. DOI URL
[22]	Wang YY, Xiao JF, Ma YM, Ding JZ, Chen XL, Ding ZY, Luo YQ (2023). Persistent and enhanced carbon sequestration capacity of alpine grasslands on Earth’s Third Pole. Science Advances, 9, eade6875. DOI: 10.1126/sciadv.ade6875.
[23]	Xing W, Lu XM, Niu SL, Chen DM, Wang JS, Liu Y, Wang BX, Zhang S, Li ZL, Yao XJ, Yu Q, Tian DS (2022). Global patterns and drivers of soil nematodes in response to nitrogen enrichment. Catena, 213, 106235. DOI: 10.1016/j.catena.2022.106235.
[24]	Xu QM, Gu XM, Wang YY, Du YG (2023). Simulated nitrogen deposition significantly increases nitrous oxide emission rate from alpine grassland on the Tibetan Plateau. Acta Agrestia Sinica, 31, 3785-3792.
	[许庆民, 顾晓梦, 王云英, 杜岩功 (2023). 模拟氮沉降显著提高青藏高原高寒草地氧化亚氮排放速率. 草地学报, 31, 3785-3792.] DOI
[25]	Yang LC, Li CB, Ning Y, Nie XQ, Xu WH, Zhou GY (2017). Carbon density and its spatial distribution in the Potentilla fruticosa dominated alpine shrub in Qinghai, China. Chinese Journal of Plant Ecology, 41, 62-70.
	[杨路存, 李长斌, 宁祎, 聂秀青, 徐文华, 周国英 (2017). 青海高寒金露梅灌丛碳密度及其分配格局. 植物生态学报, 41, 62-70.] DOI
[26]	Yang XX, Ren F, Zhou HK, He JS (2014). Responses of plant community biomass to nitrogen and phosphorus additions in an alpine meadow on the Qinghai-Xizang Plateau. Chinese Journal of Plant Ecology, 38, 159-166. DOI URL
	[杨晓霞, 任飞, 周华坤, 贺金生 (2014). 青藏高原高寒草甸植物群落生物量对氮、磷添加的响应. 植物生态学报, 38, 159-166.] DOI
[27]	Yin WY (2000). Pictorial Keys to Soil Animal of China. Science Press, Beijing.
	[尹文英 (2000). 中国土壤动物检索图鉴. 科学出版社, 北京.]
[28]	Zhang AN, Chen SY, Chen JW, Cui HW, Jiang XX, Xiao S, Wang JJ, Gao HN, An LZ, Cardoso P (2023). Shrub and precipitation interactions shape functional diversity of nematode communities on the Qinghai-Tibet Plateau. Global Change Biology, 29, 2746-2758. DOI URL
[29]	Zhang AN, Song HX, Liu ZY, Cui HW, Ding HT, Chen SY, Xiao S, An LZ, Cardoso P (2024). Effects of plant taxonomic position on soil nematode communities in Antarctica. Conservation Biology, 38, e14264. DOI: 10.1111/cobi.14264.
[30]	Zhao F, Zhang MW, Wang CW, Mei XF, Xie LN, Ma CC (2022). Effects of Caragana shrub encroachment on soil nematode community composition and metabolic footprints in steppe desert region. Acta Ecologica Sinica, 42, 4124-4136.
	[赵芳, 张明伟, 王春雯, 梅续芳, 解李娜, 马成仓 (2022). 锦鸡儿属灌丛化对草原化荒漠区土壤线虫群落组成和代谢足迹的影响. 生态学报, 42, 4124-4136.]

青藏高原灌丛化与氮添加对土壤线虫群落及功能性状的交互作用

Interactions between shrub encroachment and nitrogen addition on nematode community and functional traits on Qingzang Plateau

全文

PDF (PC)

可视化

摘要/Abstract

引用本文

使用本文

图/表 9

参考文献 30

相关文章 15

编辑推荐

Metrics

本文评价

[1]	陈佳乐, 赵颖菲, 昌海超, 董必成, 于飞海. 基于大语言模型的植物性状自动提取框架构建与评价体系[J]. , 2026, 50(生态统计方法专题): 0-.
[2]	丁明利, 魏瑶, 马健妤, 兰玉婷, 刘慧颖, 张振华. 典型高寒植物抗氧化与渗透调节系统对季节性干旱的响应及光合调控[J]. 植物生态学报, 2026, 50(5): 1187-1201.
[3]	卜欣雅, 王秀伟. 不同形态氮素添加对四个温带树种幼苗叶性状和生长的影响[J]. 植物生态学报, 2026, 50(5): 1092-1104.
[4]	封逸凡, 朱时应, 周淑荣, 江乐乐, 陈隆, 王苗, 邓国芳, 刘兰. 热带次生林恢复过程中土壤微生物对不同菌根类型树苗存活和生长性状的影响[J]. 植物生态学报, 2026, 50(4): 846-858.
[5]	洪翎桂, 安琦, 张佛军, 任宇飞, 任正炜, 周小龙. 氮磷添加增强天山高寒草地群落构建中确定性过程[J]. 植物生态学报, 2026, 50(4): 883-894.
[6]	饶朝康, 唐亮. 不同潮位红树植物叶际微生物群落特征及其影响因素[J]. 植物生态学报, 2026, 50(4): 987-1002.
[7]	林琳琳, 肖劲祥, 黄深深, 赵杨梅, 张德旭, 程毅康, 龙文兴. 磷添加对热带云雾林幼苗及幼树功能性状的影响[J]. 植物生态学报, 2026, 50(4): 917-928.
[8]	段建林, 孟晟, 陈仁利, 熊林峰, 卢春洋, 席念勋. 全球变化因子数量对菌根植物性状的影响[J]. 植物生态学报, 2026, 50(4): 907-916.
[9]	李燚, 黄欢, 赵艳超, 陈立同. 养分添加对不同海拔高寒草甸物种多样性及组成的影响[J]. 植物生态学报, 2026, 50(4): 870-882.
[10]	张永军, 李敬东, 安琦, 洪翎桂, 任正炜, 张蕊, 周小龙. 氮添加和增温对天山高寒草地群落性状的影响[J]. 植物生态学报, 2026, 50(2): 417-428.
[11]	张静, 陈洁, 李艳朋, 盘李军, 许涵, 李意德, 何海生. 南亚热带针阔混交人工林植物生物量比较及其影响因子分析[J]. 植物生态学报, 2026, 50(2): 400-416.
[12]	戴丽君, 向玲艺, 蹇陈, 王晓锋. 三峡回水扰动增强入库小流域河岸带典型草本植物功能性状的局域分化[J]. 植物生态学报, 2026, 50(2): 442-460.
[13]	王爽, 陈雅轩, 陈艳梅, 王佳乐, 刘倩愿. 太行山典型区不同生境酸枣根系资源获取策略[J]. 植物生态学报, 2026, 50(2): 374-387.
[14]	陈雅轩, 韩雨音, 陈艳梅, 刘倩愿. 华北不同林龄人工林植物功能性状与碳氮化学计量[J]. 植物生态学报, 2026, 50(2): 318-333.
[15]	梁天豪, 吴帆, 黄锦学, 景陈鸿, 傅贺菁, 杨智杰, 熊德成. 增温对中亚热带格氏栲天然林细根生长量及形态特征的影响[J]. 植物生态学报, 2026, 50(1): 94-106.