Effects of nitrogen addition on soil faunal abundance: A global meta‐analysis. Issue 8 (13th May 2022)

• Record Type: Journal Article
• Authors: Hu, Junxi; Zhou, Shixing; Tie, Liehua; Liu, Xiong; Liu, Xing; Zhao, Anjiu; Lai, Jiaming; Xiao, Lin; You, Chengming; Huang, Congde
• Is Part Of: Global ecology & biogeography. Volume 31:Issue 8(2022)
• Page Start: 1655
• Page End: 1666
• Publication Date: 2022-05-13
• Subjects: abundance -- meta‐analysis -- nematodes -- nitrogen deposition -- soil arthropods -- terrestrial ecosystems; Ecology -- Periodicals; Biogeography -- Periodicals; Biodiversity -- Periodicals; Macroevolution -- Periodicals; 577
• DOI: 10.1111/geb.13528
• Languages: English
• ISSNs: 1466-822X

Abstract

Abstract: Aim: Soil fauna has a wide range of ecosystem functions. Anthropogenic atmospheric nitrogen (N) deposition affects the structure and function of soil fauna by changing the microenvironment and resources. Given that soil faunal responses can vary considerably among taxonomic groups, N deposition rate, and ecosystems, however, there is little consensus. We aimed to evaluate the effects of N deposition on different soil faunal taxa across different terrestrial ecosystems. Location: Global. Time period: 1970–2021. Major taxa studied: Soil fauna. Methods: We conducted a meta‐analysis that yielded 264 observations from 43 publications. We evaluated the responses to N addition of soil faunal abundance for three different taxa (nematodes, mites, collembolans) in three ecosystem types (cropland, forest, and grassland). Results: Our results showed an overall negative effect of N addition on soil fauna. However, the effect varied among soil faunal taxa. Specifically, N addition had no significant effects on the abundance of collembolans and mites in any ecosystem. On the other hand, N addition significantly reduced the abundance of all nematode trophic groups except bacterivores. The overall reduction of soil fauna is likely driven by the nematode response. The negative effects of N addition on nematode abundance were contingent on the N addition rate, N addition form, and ecosystem type. N addition decreased nematode abundance at N addition rates of more than 100 kg/ha/year. Inorganic N addition negatively affected nematode abundance. Finally, N addition had a greater adverse effect on nematodes in cropland and grassland compared to forest ecosystems. Main conclusions: Our results demonstrate the overall negative effects of N addition on nematode abundance. Excessive N addition should be avoided in cropland and grassland management. Further, we suggest the application of organic fertilizer instead of inorganic fertilizer to minimize the N‐induced negative effects on soil nematodes.