Biodiv Sci ›› 2020, Vol. 28 ›› Issue (6): 707-717. DOI: 10.17520/biods.2020042
Special Issue: 土壤生物与土壤健康; 青藏高原生物多样性与生态安全
• Original Papers: Animal Diversity • Previous Articles Next Articles
Received:
2020-02-16
Accepted:
2020-04-10
Online:
2020-06-20
Published:
2020-05-15
Contact:
Kechang Niu
Yutong Wang, Kechang Niu. Effect of soil environment on functional diversity of soil nematodes in Tibetan alpine meadows[J]. Biodiv Sci, 2020, 28(6): 707-717.
变异度 Variability (%) | 以研究点A为参照的研究点间差异 Direction and strength of site effect (relative to site A) | 以沟底平地为参照的生境间差异 Direction and strength of terrain effect (relative to plots at valleys) | |||||
---|---|---|---|---|---|---|---|
研究点 Sites | 生境 Terrain | B研究点 Site B | C研究点 Site C | 阴坡 Northern | 阳坡 Southern | 山顶 Top | |
线虫α多样性 Nematode α diversity | |||||||
线虫丰富度 Nematode richness | 2.44 | 23.3 | 0.07 | 0.13 | 0.09 | 0.27* | -0.14 |
线虫Shannon多样性 Nematode Shannon diversity | 8.67 | 39.36* | 0.07 | 0.24* | 0.06 | 0.46* | -0.05 |
线虫均匀度 Nematode evenness diversity | 8.59 | 25.02* | -0.02 | 0.03 | 0.02 | 0.09* | 0.05 |
线虫个体多度 Nematode individual abundance | 2.77 | 25.39* | 17.51* | 3.65 | -1.27 | 18.47* | -45.83* |
基于个体大小的土壤线虫功能多样性 Body-size based functional diversity of soil nematodes | |||||||
群落水平个体大小 CWM for body-size | 9.44 | 7.19 | -4.25 | 1.89 | 2.83 | 0.80 | 5.96 |
个体大小多样性 FDRao for body-size | 8.6 | 9.5 | -2.03 | 2.5 | 0.38 | 1.53 | 5.18 |
不同线虫功能类群个体多度 Individual abundance of each functional group | |||||||
食细菌线虫 Bacterivores | 22.22* | 15.0 | 0.85* | 0.86* | -0.41* | -0.46* | -0.68* |
食真菌线虫 Fungivores | 2.19 | 6.43 | 0.01 | -0.15 | -0.04 | -0.20* | -0.26* |
植食线虫 Herbivores | 6.45 | 3.42 | 0.44* | 0.01 | 0.44* | 0.13 | 0.24 |
捕食杂食线虫 Omnivores-Predators | 3.38 | 20.03 | -0.32* | -0.06 | 0.86* | 0.71* | 0.19 |
植物物种丰富度 Plant species richness | 5.60 | 45.93* | 0.09 | 0.08 | -0.15 | -0.25* | -0.25* |
土壤理化因子 Edaphic factors | |||||||
土壤pH值 Soil pH | 3.17* | 89.6* | 0.21* | 0.13* | 0.26* | 1.17* | 0.15* |
土壤有机质 Soil organic matter | 0.23 | 34.8* | 2.51 | 1.61 | -25.6* | 3.05 | 7.53 |
土壤总磷 Soil total P | 2.63 | 50.5* | -0.01 | -0.37 | -0.46 | -1.86* | -1.53 |
土壤速效磷 Soil available P | 10.3* | 70.2* | 1.19* | 1.77* | -2.42* | -2.95* | -5.42* |
土壤总氮 Soil total N | 17.7* | 38.9* | 0.42* | 0.48* | -0.02 | -0.50* | -0.74* |
土壤速效氮 Soil available N | 14.6* | 79.1* | 7.3 | 36.9 | 60.4 | -26.1* | -34.7 |
Table 1 Summary of site and terrain effect on variation in soil nematode diversity tested by generalized linear mixed effect model
变异度 Variability (%) | 以研究点A为参照的研究点间差异 Direction and strength of site effect (relative to site A) | 以沟底平地为参照的生境间差异 Direction and strength of terrain effect (relative to plots at valleys) | |||||
---|---|---|---|---|---|---|---|
研究点 Sites | 生境 Terrain | B研究点 Site B | C研究点 Site C | 阴坡 Northern | 阳坡 Southern | 山顶 Top | |
线虫α多样性 Nematode α diversity | |||||||
线虫丰富度 Nematode richness | 2.44 | 23.3 | 0.07 | 0.13 | 0.09 | 0.27* | -0.14 |
线虫Shannon多样性 Nematode Shannon diversity | 8.67 | 39.36* | 0.07 | 0.24* | 0.06 | 0.46* | -0.05 |
线虫均匀度 Nematode evenness diversity | 8.59 | 25.02* | -0.02 | 0.03 | 0.02 | 0.09* | 0.05 |
线虫个体多度 Nematode individual abundance | 2.77 | 25.39* | 17.51* | 3.65 | -1.27 | 18.47* | -45.83* |
基于个体大小的土壤线虫功能多样性 Body-size based functional diversity of soil nematodes | |||||||
群落水平个体大小 CWM for body-size | 9.44 | 7.19 | -4.25 | 1.89 | 2.83 | 0.80 | 5.96 |
个体大小多样性 FDRao for body-size | 8.6 | 9.5 | -2.03 | 2.5 | 0.38 | 1.53 | 5.18 |
不同线虫功能类群个体多度 Individual abundance of each functional group | |||||||
食细菌线虫 Bacterivores | 22.22* | 15.0 | 0.85* | 0.86* | -0.41* | -0.46* | -0.68* |
食真菌线虫 Fungivores | 2.19 | 6.43 | 0.01 | -0.15 | -0.04 | -0.20* | -0.26* |
植食线虫 Herbivores | 6.45 | 3.42 | 0.44* | 0.01 | 0.44* | 0.13 | 0.24 |
捕食杂食线虫 Omnivores-Predators | 3.38 | 20.03 | -0.32* | -0.06 | 0.86* | 0.71* | 0.19 |
植物物种丰富度 Plant species richness | 5.60 | 45.93* | 0.09 | 0.08 | -0.15 | -0.25* | -0.25* |
土壤理化因子 Edaphic factors | |||||||
土壤pH值 Soil pH | 3.17* | 89.6* | 0.21* | 0.13* | 0.26* | 1.17* | 0.15* |
土壤有机质 Soil organic matter | 0.23 | 34.8* | 2.51 | 1.61 | -25.6* | 3.05 | 7.53 |
土壤总磷 Soil total P | 2.63 | 50.5* | -0.01 | -0.37 | -0.46 | -1.86* | -1.53 |
土壤速效磷 Soil available P | 10.3* | 70.2* | 1.19* | 1.77* | -2.42* | -2.95* | -5.42* |
土壤总氮 Soil total N | 17.7* | 38.9* | 0.42* | 0.48* | -0.02 | -0.50* | -0.74* |
土壤速效氮 Soil available N | 14.6* | 79.1* | 7.3 | 36.9 | 60.4 | -26.1* | -34.7 |
Fig. 1 Relationship between edaphic factors and soil nematodes diversity (a), and individual abundance of each functional group (b) over four terrains at each of three sites. SOM, Soil organic matter; SAP, Soil available P; STN, Soil total N; SAN, Soil available N; STP, Soil total P; PSR, Plant species richness; CWM, Community-weighted mean; FDRao, Functional diversity in term of Rao index.
Fig. 2 Effect of soil environment on soil nematode diversity assessed by Bayesian regression model. The effect of edaphic factors and plant species richness on soil nematode diversity assessed by distribution of estimated slopes, with significant effects indicated by 95% credible intervals that do not overlap zero. CWM, Community-weighted mean; FDRao, Functional diversity in term of Rao index.
Fig. 3 Effect of soil environment on individual abundance of each functional group of soil nematodes assessed by Bayesian regression model. The effect of edaphic factors and plant species richness on individual abundance of each functional group of soil nematodes assessed by distribution of estimated slopes, with significant effects indicated by 95% credible intervals that do not overlap zero.
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