Department of Soil Science and Agricultural Chemistry, Institute of Agricultural Sciences, Banaras Hindu University, Varanasi, Uttar Pradesh, 221005, India.
ICAR-National Research Centre for Grapes, Pune, Maharashtra, 412307, India.
Environ Geochem Health. 2022 Jan;44(1):221-234. doi: 10.1007/s10653-021-00929-8. Epub 2021 Apr 17.
Widespread use of zinc oxide nanoparticles (ZnO-NPs) threatens soil, plants, terrestrial and aquatic animals. Thus, it is essential to explore the fate and behavior of NPs in soil and also its mechanism of interaction with soil microbial biodiversity to maintain soil health and quality to accomplish essential ecosystem services. With this background, the model experiment was conducted in the greenhouse to study the impact of ZnO-NPs on soil taking maize as a test crop. The X-ray diffraction, Fourier transform infrared spectroscopy, Scanning electron microscopy and Particles size analysis of engineered NPs confirmed that the material was ZnO-NPs (particle size--65.82 nm). The application of ZnO-NPs resulted in a significant decrease in soil pH. Significantly high EC (0.13 dS m) was recorded where ZnO-NPs were applied at the rate of 2.5 mg Zn kg soil over control (0.12 dS m). A significant increase in soil available phosphorus was observed on applying ZnO-NPs (15.29 mg kg of soil) as compared to control (11.84 mg kg of soil). Maximum soil available Zn (2.09 mg kg) was recorded in ZnO-NPs-amended soil (T) which was significantly higher than control (0.33 mg kg) as well as treatments containing conventional zincatic fertilizers. The inhibition rates of dehydrogenase enzyme activity in the presence of 0.5 mg, 1.25 mg and 2.5 mg ZnO-NPs per kg soil were 31.3, 46.2 and 49.7%, respectively. Soil microbial biomass carbon was significantly reduced (103.33 µg g soil) in soils treated with ZnO-NPs over control (111.33 µg g soil). Soil bacterial count was also significantly lesser (12.33 × 10 CFU) in the case where 2.5 mg kg ZnO-NPs were applied as compared to control (21.33 × 10 CFU). The corresponding decrease in fungal and actinomycetes colony count was 24.16, 37.35, 46.15% and 14.59, 17.97, 22.45% with the application of 0.5 mg, 1.25 mg and 2.5 mg ZnO-NPs per kg soil, respectively, as compared to control. Thus, the use of ZnO-NPs resulted in an increase in soil available Zn but inhibited soil microbial activity.
氧化锌纳米颗粒(ZnO-NPs)的广泛使用威胁到土壤、植物、陆地和水生动物。因此,探索纳米颗粒在土壤中的归宿和行为及其与土壤微生物生物多样性相互作用的机制,对于维持土壤健康和质量以实现基本生态系统服务至关重要。在此背景下,本研究以玉米为供试作物,在温室中进行了模型实验,以研究 ZnO-NPs 对土壤的影响。X 射线衍射、傅里叶变换红外光谱、扫描电子显微镜和工程纳米颗粒的粒径分析证实,该材料为 ZnO-NPs(粒径为 65.82nm)。施加 ZnO-NPs 可显著降低土壤 pH 值。在 2.5mg Zn kg 土壤的 ZnO-NPs 处理下,电导率(EC)(0.13dS m)显著升高,而对照(0.12dS m)。与对照(11.84mg kg 土壤)相比,施加 ZnO-NPs 后土壤有效磷显著增加(15.29mg kg 土壤)。在 ZnO-NPs 处理土壤中,最大土壤有效锌(2.09mg kg)记录为 2.09mg kg,明显高于对照(0.33mg kg)和含有常规锌肥的处理。在 0.5mg、1.25mg 和 2.5mg ZnO-NPs kg 土壤中存在的脱氢酶活性抑制率分别为 31.3%、46.2%和 49.7%。土壤微生物生物量碳在施用 ZnO-NPs 的土壤中(103.33µg g 土壤)显著低于对照(111.33µg g 土壤)。在 2.5mg kg ZnO-NPs 处理的土壤中,土壤细菌计数也明显减少(12.33×10 CFU),而对照(21.33×10 CFU)。在施用 0.5mg、1.25mg 和 2.5mg ZnO-NPs kg 土壤时,真菌和放线菌菌落计数分别相应减少 24.16%、37.35%、46.15%和 14.59%、17.97%、22.45%。因此,ZnO-NPs 的使用增加了土壤中有效锌的含量,但抑制了土壤微生物的活性。