砷改变了蜈蚣草土壤根生境的微生物群落组合。

IF 5.1 Q1 ECOLOGY
ISME communications Pub Date : 2024-12-27 eCollection Date: 2025-01-01 DOI:10.1093/ismeco/ycae172
Jiahui Lin, Zhongmin Dai, Mei Lei, Qian Qi, Weijun Zhou, Lena Q Ma, Randy A Dahlgren, Jianming Xu
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引用次数: 0

摘要

vittata Pteris,以其超积累砷的能力而闻名,为全球土壤砷污染升级问题提供了一个有希望的解决方案。这种蕨类植物培育了独特的地下微生物群落,以增强其环境适应性。然而,我们对这种群落的聚集过程和长期生态影响的了解仍然有限,阻碍了有效土壤修复策略的发展。本研究通过调查由砷污染梯度组成的三个地理不同领域的土壤根系栖息地,并辅以时间尺度的温室实验,解决了这一差距。田间调查表明,砷胁迫通过增强同质选择过程影响根际群落组装动态。温室实验进一步揭示,砷暴露通过促进关键微生物模块改变根际群落的组装轨迹。具体来说,在田间和温室环境下,砷暴露增加了根际中一个核心分类群(即根瘤菌科)的富集,使其在植物修复后的土壤中的丰度从无法检测到的水平提高到0.02%。值得注意的是,砷暴露也促进了根际的致病群(即螺旋藻科),将其丰度从无法检测到的水平增加到温室中的0.1%。这引起了人们的关注,值得在未来的植物修复研究中进一步调查。总体而言,本研究阐明了引入修复植物后土壤微生物群落的组装动力学,并强调了植物修复对土壤微生物群落的影响。通过探索修复植物的生态影响,这项工作推进了对植物修复过程中固有的复杂生态影响的更细致的理解。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Arsenic modifies the microbial community assembly of soil-root habitats in Pteris vittata.

Pteris vittata, renowned for its ability to hyperaccumulate arsenic, presents a promising solution to the escalating issue of global soil arsenic contamination. This fern cultivates a unique underground microbial community to enhance its environmental adaptability. However, our understanding of the assembly process and the long-term ecological impacts of this community remains limited, hindering the development of effective soil remediation strategies. This study addresses this gap by investigating soil-root habitats from three geographically diverse fields comprising a gradient of arsenic contamination, complemented by a time-scale greenhouse experiment. Field investigations reveal that arsenic stress influences community assembly dynamics in the rhizosphere by enhancing processes of homogeneous selection. Greenhouse experiments further reveal that arsenic exposure alters the assembly trajectory of rhizosphere communities by promoting key microbial modules. Specifically, arsenic exposure increases the enrichment of a core taxon (i.e. Rhizobiaceae) in the rhizosphere, both in field and greenhouse settings, boosting their abundance from undetectable levels to 0.02% in the soil after phytoremediation. Notably, arsenic exposure also promotes a pathogenic group (i.e. Spirochaetaceae) in the rhizosphere, increasing their abundance from undetectable levels to 0.1% in the greenhouse. This raise concerns that warrant further investigation in future phytoremediation studies. Overall, this study elucidates the assembly dynamics of the soil microbiome following the introduction of a remediation plant and emphasizes the often-overlooked impacts on soil microbial community following phytoremediation. By probing the ecological impacts of remediation plants, this work advances a more nuanced understanding of the complex ecological implications inherent in phytoremediation processes.

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