生物多样性 ›› 2018, Vol. 26 ›› Issue (10): 1034-1050. DOI: 10.17520/biods.2018122
所属专题: 土壤生物与土壤健康
高梅香1,2, 林琳1,2, 常亮3, 孙新3, 刘冬3, 吴东辉3,4,*()
收稿日期:
2018-04-16
接受日期:
2018-07-03
出版日期:
2018-10-20
发布日期:
2019-01-06
通讯作者:
吴东辉
作者简介:
# 共同第一作者
基金资助:
Meixiang Gao1,2, Lin Lin1,2, Liang Chang3, Xin Sun3, Dong Liu3, Donghui Wu3,4,*()
Received:
2018-04-16
Accepted:
2018-07-03
Online:
2018-10-20
Published:
2019-01-06
Contact:
Wu Donghui
About author:
# Co-first authors
摘要:
群落空间格局和构建机制一直是生态学研究的核心内容。在生物多样性严重丧失的背景下, 揭示群落空间格局及其构建机制, 有助于深刻理解生物多样性丧失的原因, 更有助于应对生物多样性保护等重大生态环境问题。然而, 陆地生态系统的研究多集中于地上生物群落, 对地下生态系统, 尤其是土壤动物空间格局和构建机制的研究尚不充分。事实上, 土壤动物多样性是全球生物多样性的关键组成之一, 是地下生态系统结构和功能维持的重要部分。对土壤动物空间格局和构建机制的研究, 能明确不同空间尺度条件下土壤动物多样性的维持机制。土壤动物群落常在多种空间尺度形成复杂的空间分布格局, 因此, 本文首先介绍了不同空间尺度主要土壤动物群落的空间自相关性特征, 阐述了土壤动物群落斑块和孔隙镶嵌分布的复杂空间格局。继而阐明这种空间格局主要受生物间作用、环境过滤和随机扩散的调控, 并说明这三个过程对土壤动物群落的调控能力和作用方式。作者提出, 这三个过程仍是今后土壤动物群落空间格局和构建机制研究的重点内容, 需要进一步加强以土壤动物为研究对象的群落构建理论的验证和发展。我国土壤动物群落空间格局和构建机制起步较晚, 希望本文能够促进我国土壤动物生态学相关领域的研究。
高梅香, 林琳, 常亮, 孙新, 刘冬, 吴东辉 (2018) 土壤动物群落空间格局和构建机制研究进展. 生物多样性, 26, 1034-1050. DOI: 10.17520/biods.2018122.
Meixiang Gao, Lin Lin, Liang Chang, Xin Sun, Dong Liu, Donghui Wu (2018) Spatial patterns and assembly rules in soil fauna communities: A review. Biodiversity Science, 26, 1034-1050. DOI: 10.17520/biods.2018122.
群落 Community | 生境 Habitat | 空间幅度 Spatial extent (m2) | 空间自相关距离 Range (A0, m) | 参考文献 Reference |
---|---|---|---|---|
土壤蚯蚓 Earthworm | 草地 Grassland | - | 1-50 | Decaëns et al, 2009 |
森林 Forest | 10,000 | 17-50 | Gutiérrez-López et al, 2010 | |
土壤跳虫 Soil collembola | 森林 Forest | 10,000 | 20-27 | Gutiérrez-López et al, 2010 |
农田 Cropland | 250 | 5-50 | 高梅香等, 2014c | |
土壤螨类 Soil mite | 森林 Forest | 25 | 0.5-5 | 高梅香等, 2014a |
10,000 | 17-30 | Gutiérrez-López et al, 2010 | ||
农田 Cropland | 250 | 5-40 | 高梅香等, 2014b | |
土壤线虫 Soil nematode | 草地 Grassland | 1,500 | 4-60 | Rossi & Quénéhervé, 1998 |
农田 Cropland | 1,200 | 9-91 | Liang et al, 2005 | |
地表甲虫 Ground beetle | 森林Forest | 25 | 1-2.5 | 胡媛媛等, 2018 |
400 | 5-10 | 朱纪元等, 2017 | ||
900 | 150-450 | 倪娟平等, 2018b | ||
农田 Cropland | 1,600 | 40-150 | 刘洁等, 2017 |
表1 主要土壤动物群落的空间自相关性距离
Table 1 Spatial autocorrelation distances of main soil animal communities
群落 Community | 生境 Habitat | 空间幅度 Spatial extent (m2) | 空间自相关距离 Range (A0, m) | 参考文献 Reference |
---|---|---|---|---|
土壤蚯蚓 Earthworm | 草地 Grassland | - | 1-50 | Decaëns et al, 2009 |
森林 Forest | 10,000 | 17-50 | Gutiérrez-López et al, 2010 | |
土壤跳虫 Soil collembola | 森林 Forest | 10,000 | 20-27 | Gutiérrez-López et al, 2010 |
农田 Cropland | 250 | 5-50 | 高梅香等, 2014c | |
土壤螨类 Soil mite | 森林 Forest | 25 | 0.5-5 | 高梅香等, 2014a |
10,000 | 17-30 | Gutiérrez-López et al, 2010 | ||
农田 Cropland | 250 | 5-40 | 高梅香等, 2014b | |
土壤线虫 Soil nematode | 草地 Grassland | 1,500 | 4-60 | Rossi & Quénéhervé, 1998 |
农田 Cropland | 1,200 | 9-91 | Liang et al, 2005 | |
地表甲虫 Ground beetle | 森林Forest | 25 | 1-2.5 | 胡媛媛等, 2018 |
400 | 5-10 | 朱纪元等, 2017 | ||
900 | 150-450 | 倪娟平等, 2018b | ||
农田 Cropland | 1,600 | 40-150 | 刘洁等, 2017 |
图1 凉水9 ha (300 m × 300 m)阔叶红松林样地地表步行虫群落(2015年8月)和地下土壤跳虫群落(2014年9月)克里格空间插值格局图(高梅香等, 2018)
Fig. 1 Kriging prediction maps for ground carabid (August 2015) and soil collembolan (September 2014) communities (Gao et al, 2018)
图2 群落构建机制的过滤模型(仿Vellend, 2016)。在这个假设的案例中, 一个来自区域物种库的随机物种子集进入局地地点; 只有那些有圆形边缘的物种能够适应局地环境条件; 竞争淘汰了其他物种, 只留下每个功能类型(以不同形状表示)的一个物种。由于资源需求不同, 两个剩余物种才能稳定共存。
Fig. 2 The filter model of community assembly (imitating from Vellend, 2016). In this hypothetical example, a random subset of species in the regional pool has access to a local site; only species with rounded edges can tolerate the environmental conditions; and competition leads to the elimination of all but one species of each functional type (shape). The two remaining species can coexist stably given contrasting resource requirements.
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