Guoxi Shi , Zhonghua Zhang , Li Ma , Yongjun Liu , Yibo Wang , Jean Yves Uwamungu , Huyuan Feng , Shikui Dong , Buqing Yao , Huakun Zhou
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By itself, Ni addition of 20 g N m<sup>−2</sup> year<sup>−1</sup> (Ni20) reduced both plant and AM fungal richness, while Am addition of 20 g N m<sup>−2</sup> year<sup>−1</sup> (Am20) had no significant effect on them. However, when Ni and Am were combined, only Ni20 plus Am20 among all combinations reduced both plant and AM fungal richness. Both soil nitrate-N and plant species richness jointly drove changes in AM fungal richness, but plant species richness was the main factor affecting AM fungal richness under N addition. Our results suggest that minimizing the loss of AM fungi caused by plant species loss resulting from N addition is a key means to sustainably restore degraded grasslands.</p></div>","PeriodicalId":55136,"journal":{"name":"Fungal Ecology","volume":"67 ","pages":"Article 101303"},"PeriodicalIF":1.9000,"publicationDate":"2023-11-16","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://www.sciencedirect.com/science/article/pii/S1754504823000806/pdfft?md5=58a8b9d8d1dd080ebecfd323ed9119c3&pid=1-s2.0-S1754504823000806-main.pdf","citationCount":"0","resultStr":"{\"title\":\"Nitrogen addition drives changes in arbuscular mycorrhizal fungal richness through changes in plant species richness in revegetated alpine grassland\",\"authors\":\"Guoxi Shi , Zhonghua Zhang , Li Ma , Yongjun Liu , Yibo Wang , Jean Yves Uwamungu , Huyuan Feng , Shikui Dong , Buqing Yao , Huakun Zhou\",\"doi\":\"10.1016/j.funeco.2023.101303\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><p>Nitrogen (N) addition not only promotes the restoration of degraded grasslands, but also threatens ecosystem functioning through the loss of species richness. Thus, a deep understanding of the effect of N addition on the richness of key organisms in restored grasslands is critical to sustainably restoring degraded grasslands. We conducted a 4-year N addition experiment to investigate the response of both plant and arbuscular mycorrhizal (AM) fungal richness to the combined addition of ammonium (Am) and nitrate (Ni) in a revegetated grassland rehabilitated (with a focus on restoration) on the Qinghai–Tibet Plateau. Both nitrogen forms were added at three levels: 0, 10, and 20 g N m<sup>−2</sup> year<sup>−1</sup>. By itself, Ni addition of 20 g N m<sup>−2</sup> year<sup>−1</sup> (Ni20) reduced both plant and AM fungal richness, while Am addition of 20 g N m<sup>−2</sup> year<sup>−1</sup> (Am20) had no significant effect on them. However, when Ni and Am were combined, only Ni20 plus Am20 among all combinations reduced both plant and AM fungal richness. Both soil nitrate-N and plant species richness jointly drove changes in AM fungal richness, but plant species richness was the main factor affecting AM fungal richness under N addition. 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引用次数: 0
摘要
氮素的添加不仅能促进退化草地的恢复,还会通过物种丰富度的丧失威胁生态系统的功能。因此,深入了解N添加对恢复草地关键生物丰富度的影响,对退化草地的可持续恢复至关重要。通过为期4年的N添加试验,研究了青藏高原恢复草地植物和丛枝菌根真菌丰富度对铵态氮和硝态氮联合添加的响应。两种形式的氮均以3个水平添加:0、10和20 g N m−2 year−1。添加20 g N m−2 year−1 (Ni20)的Ni本身降低了植物和AM真菌的丰富度,而添加20 g N m−2 year−1 (Am20)的AM对它们没有显著影响。然而,当Ni和Am组合时,所有组合中只有Ni20 + Am20降低了植物和Am的真菌丰富度。土壤硝态氮和植物物种丰富度共同驱动AM真菌丰富度的变化,但植物物种丰富度是N添加下影响AM真菌丰富度的主要因素。综上所述,尽量减少氮素对植物物种损失造成的AM真菌损失是实现退化草地可持续恢复的关键手段。
Nitrogen addition drives changes in arbuscular mycorrhizal fungal richness through changes in plant species richness in revegetated alpine grassland
Nitrogen (N) addition not only promotes the restoration of degraded grasslands, but also threatens ecosystem functioning through the loss of species richness. Thus, a deep understanding of the effect of N addition on the richness of key organisms in restored grasslands is critical to sustainably restoring degraded grasslands. We conducted a 4-year N addition experiment to investigate the response of both plant and arbuscular mycorrhizal (AM) fungal richness to the combined addition of ammonium (Am) and nitrate (Ni) in a revegetated grassland rehabilitated (with a focus on restoration) on the Qinghai–Tibet Plateau. Both nitrogen forms were added at three levels: 0, 10, and 20 g N m−2 year−1. By itself, Ni addition of 20 g N m−2 year−1 (Ni20) reduced both plant and AM fungal richness, while Am addition of 20 g N m−2 year−1 (Am20) had no significant effect on them. However, when Ni and Am were combined, only Ni20 plus Am20 among all combinations reduced both plant and AM fungal richness. Both soil nitrate-N and plant species richness jointly drove changes in AM fungal richness, but plant species richness was the main factor affecting AM fungal richness under N addition. Our results suggest that minimizing the loss of AM fungi caused by plant species loss resulting from N addition is a key means to sustainably restore degraded grasslands.
期刊介绍:
Fungal Ecology publishes investigations into all aspects of fungal ecology, including the following (not exclusive): population dynamics; adaptation; evolution; role in ecosystem functioning, nutrient cycling, decomposition, carbon allocation; ecophysiology; intra- and inter-specific mycelial interactions, fungus-plant (pathogens, mycorrhizas, lichens, endophytes), fungus-invertebrate and fungus-microbe interaction; genomics and (evolutionary) genetics; conservation and biodiversity; remote sensing; bioremediation and biodegradation; quantitative and computational aspects - modelling, indicators, complexity, informatics. The usual prerequisites for publication will be originality, clarity, and significance as relevant to a better understanding of the ecology of fungi.