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土壤微塑料与丛枝菌根真菌的相互作用

王发园, 张莘, 陈保冬   

  1. 青岛科技大学环境与安全工程学院, 266042
    中国科学院生态环境研究中心区域与城市生态安全全国重点实验室, 北京 100085 中国
    中国科学院大学, 100049
  • 收稿日期:2025-05-16 修回日期:2025-09-07 接受日期:2025-10-20
  • 基金资助:
    山东省自然科学基金面上项目(ZR2020MD120, ZR2024QD253); 国家自然科学基金项目(42177019,42377299); 政府间国际科技创新合作项目(2022YFE0114000)

Interactions between soil microplastics and arbuscular mycorrhizal fungi

CHEN Bao-Dong   

  1. College of Environment and Safety Engineering, Qingdao University of Science and Technology 266042,
    State Key Laboratory of Regional and Urban Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences 100085, China
    , University of Chinese Academy of Sciences 100049,
  • Received:2025-05-16 Revised:2025-09-07 Accepted:2025-10-20
  • Supported by:
    Inter-government International Science and Technology Innovation Cooperation Project(2022YFE0114000)

摘要: 微塑料是全球性分布的一类新污染物,常见于包括农田在内的陆地生态系统。已有证据显示,微塑料会改变土壤理化性质,影响土壤生物、植物性状及生态系统功能。作为土壤中最常见的植物共生真菌,丛枝菌根(arbuscular mycorrhizal, AM)真菌通过多种机制增强宿主植物的抗逆能力,对于维持生态系统稳定具有重要作用。结合当前最新研究进展,本文综述了土壤微塑料与AM真菌的相互作用。一方面微塑料可以通过吸附固持作用,以及释放所携带的污染物直接影响AM真菌,也可以通过改变土壤性质(如pH、养分有效性)、污染物形态及毒性、土壤微生物群落组成及其活性、植物性状等间接影响AM真菌的侵染能力和群落结构。另一方面,AM真菌对微塑料具有较强的耐性,可能通过多种途径缓解微塑料对植物和土壤环境的不利影响,包括改善土壤结构、缓解微塑料引起的植物营养限制、通过菌根结构(如根外菌丝)固持微塑料,减少植物对微塑料的吸收和转运等。总体上,微塑料与AM真菌之间的相互作用依赖于微塑料的特性(如种类、剂量、尺寸、形状)、植物种类、土壤性质及暴露条件,研究结果尚难统一。最后,基于对当前研究中存在的问题和不足的分析,展望了未来研究方向,提出建立可靠的土壤植物体系中微塑料定量分析方法,加强微塑料代谢产物和复合污染对AM真菌的生态毒理效应研究,揭示AM真菌对微塑料环境行为的影响及其生态效应,从而为应用菌根技术解决土壤微塑料污染问题提供理论和技术支撑。

关键词: 新污染物, 生态功能, 全球变化, 环境胁迫, 土壤污染

Abstract: As a category of emerging contaminants with global distribution, microplastics occur frequently in terrestrial ecosystems, including agricultural soils. Available evidence indicates that microplastics can alter soil physicochemical properties, and affect soil biota, plant performance, and ecosystem functions. As the most ubiquitous plant symbiotic fungi in soils, arbuscular mycorrhizal (AM) fungi can enhance host plant stress resistance through multiple mechanisms and play a critical role in maintaining ecosystem stability. This review synthesizes current research advances in the interactions between microplastics and AM fungi. Microplastics in soil can directly affect AM fungi through adsorption and absorption, or by releasing co-contaminants, and indirectly influence fungal colonization and community structure by altering soil properties (e.g., pH, nutrient availability), pollutant speciation and toxicity, microbial community composition and activity, and plant performance. On the other side, AM fungi exhibit strong tolerance and resilience to microplastics, and may alleviate negative impacts of microplastic contamination on plant and soil environment through multiple pathways, such as improving soil structure,mitigating plant nutrient limitations caused by microplastics, immobilizing microplastics via fungal structures (e.g., extraradical hyphae) to reduce their uptake and translocation by plants. Overall, the interactions between microplastics and AM fungi vary with microplastic characteristics (e.g., type, dose, size, and shape), plant species, soil properties, and exposure conditions, as a result it is still difficult to reach general conclusions. Finally, based on identification of current knowledge gaps, future research priorities are proposed to establish reliable quantitative method for microplastics in the soil plant systems, to assess the ecotoxicological effects of microplastic metabolites and composite pollution on AM fungi, and to reveal the influences of AM fungi on environmental behavior of soil microplastic and its ecological impacts, which will provide theoretical and technical support for the application of mycorrhizal technology to tackle soil microplastic pollution problems.

Key words: emerging contaminants, ecological functions, global change, environmental stress, soil pollution