Jing Xin-Xin, Su Zhi-Zhong, Xing Hong-En, Wang Fa-Yuan, Shi Zhao-Yong, Liu Xue-Qin
College of Agriculture, Henan University of Science and Technology, Luoyang 471003, China.
College of Life Science, Luoyang Normal University, Luoyang 471022, China.
Huan Jing Ke Xue. 2016 Aug 8;37(8):3208-3215. doi: 10.13277/j.hjkx.2016.08.049.
ZnO nanoparticles (NPs) are widely used in many applications, such as plastics, ceramics, glass, cement, rubber, lubricants, paints, pigments, batteries, fire retardants, catalysts, and anti-microbial agents. They directly or indirectly enter aquatic and terrestrial environments through application, accidental release, contaminated soil/sediments, or atmospheric fallouts. When present in excess, ZnO NPs can induce phytotoxicity and reduce plant growth and yields. ZnO NPs can also cause Zn accumulation in edible parts of food crops, and then subsequently enter human bodies and pose a significant health risk. Arbuscular mycorrhizae are ubiquitous symbiotic associations in nature formed between arbuscular mycorrhizal (AM) fungi and most higher plants in terrestrial ecosystems. In addition to their well-known contribution to plant nutrient acquisition and growth, AM fungi can improve plant tolerance to various environmental stresses, but mycorrhizal effects vary with environmental conditions such as phosphorus status in both soil and plants. AM fungi have been shown to alleviate the negative effects of ZnO NPs and zinc accumulation in plants, however, the role of phosphorus fertilization has been neglected. A greenhouse pot culture experiment was conducted using maize as the test plant inoculated with or without AM fungus . Four levels of phosphorus (0, 20, 50 or 100 mg·kg) and two levels of ZnO NPs (0 or 500 mg·kg) were applied to pots. Shoots and roots were harvested separately after two months of growth. Mycorrhizal infection, plant biomass, P and Zn concentrations and uptake in plants, and soil DTPA-extractable zinc and pH were determined. The results showed that ZnO NPs did not significantly affect the growth of maize, but inhibited root mycorrhizal infection and plant phosphorus uptake, and led to the accumulation of zinc in plants. ZnO NPs and high phosphorus supply decreased root mycorrhizal infection, but AM inoculation significantly promoted plant growth under all phosphorus supply levels. Phosphorus application and AM inoculation increased soil pH, but reduced the bioavailability of Zn derived from ZnO NPs, decreased the translocation and accumulation of zinc in maize shoots, and thus produced beneficial effects on plants. In general, AM inoculation showed positive mycorrhizal effect, especially under low phosphorus conditions and addition of ZnO NPs. Our results showed for the first time that both AM fungi and phosphate fertilizer could help to mitigate soil pollution and the ecological and health risks posed by ZnO NPs.
氧化锌纳米颗粒(NPs)广泛应用于许多领域,如塑料、陶瓷、玻璃、水泥、橡胶、润滑剂、涂料、颜料、电池、阻燃剂、催化剂和抗菌剂等。它们通过应用、意外释放、受污染的土壤/沉积物或大气沉降直接或间接进入水生和陆地环境。当过量存在时,氧化锌纳米颗粒会诱导植物毒性,降低植物生长和产量。氧化锌纳米颗粒还会导致粮食作物可食用部分锌的积累,进而进入人体并构成重大健康风险。丛枝菌根是自然界中普遍存在的共生关系,由丛枝菌根(AM)真菌与陆地生态系统中的大多数高等植物形成。除了其对植物养分获取和生长的众所周知的贡献外,AM真菌还可以提高植物对各种环境胁迫的耐受性,但菌根效应会因环境条件而异,如土壤和植物中的磷状况。已表明AM真菌可减轻氧化锌纳米颗粒对植物的负面影响以及锌在植物中的积累,然而,磷肥的作用却被忽视了。以玉米为试验植物进行了温室盆栽试验,接种或不接种AM真菌。向花盆中施加四个磷水平(0、20、50或100毫克·千克)和两个氧化锌纳米颗粒水平(0或500毫克·千克)。生长两个月后分别收获地上部和根部。测定了菌根侵染、植物生物量、植物中磷和锌的浓度及吸收量,以及土壤中DTPA可提取锌和pH值。结果表明,氧化锌纳米颗粒对玉米生长没有显著影响,但抑制了根部菌根侵染和植物对磷的吸收,并导致植物中锌的积累。氧化锌纳米颗粒和高磷供应降低了根部菌根侵染,但接种AM真菌在所有磷供应水平下均显著促进了植物生长。施磷和接种AM真菌提高了土壤pH值,但降低了源自氧化锌纳米颗粒的锌的生物有效性,减少了锌在玉米地上部的转运和积累,从而对植物产生了有益影响。总体而言,接种AM真菌显示出积极的菌根效应,尤其是在低磷条件下和添加氧化锌纳米颗粒的情况下。我们的结果首次表明,AM真菌和磷肥都有助于减轻土壤污染以及氧化锌纳米颗粒带来的生态和健康风险。