School of Water Conservancy and Environment, University of Jinan, Jinan, 250022, China.
Bull Environ Contam Toxicol. 2024 Apr 2;112(4):52. doi: 10.1007/s00128-024-03882-1.
The increasing use of copper oxide nano particles (nCuO) as nano-fertilizers and pesticides have raised concerns over their impact on soil environment and agricultural products. In this study, two nCuO with different shapes, namely spherical nCuO (CuO NPs) and tubular nCuO (CuO NTs), were selected to investigate their bioavailability and toxicity to pakchoi in two soils with different properties. At the meantime, CuO bulk particles (CuO BPs) and Cu(NO) were used for comparison. Results showed that all the Cu treatments increased the DTPA extractable (DTPA-Cu) concentrations in GD soil (acidic) more than in HN soil (alkaline). The DTPA-Cu concentrations increased in the order of Cu(NO) ≈ CuO NPs > CuO BPs ≈ CuO NTs in GD soil and Cu(NO) > CuO NPs > CuO BPs ≈ CuO NTs in HN soil. While for the contents of Cu in the aerial parts of pakchoi, the order is CuO NPs > Cu(NO) > CuO NTs ≈ CuO BPs in GD soil and CuO NPs ≈ Cu(NO) > CuO BPs ≈ CuO NTs in HN soil. Only CuO NPs reduced pakchoi biomass in GD soil. There are no significant difference among CuO NPs, CuO BPs, and Cu(NO) in reducing the chlorophyll contents in pakchoi in HN soil, whereas in GD soil, CuO NPs and CuO BPs led to significantly lower chlorophyll contents in pakchoi compared to Cu(NO). Additionally, CuO NPs and Cu(NO) increased Mn and Mo in pakchoi leaf in HN soil, while increased Zn in pakchoi leaf in GD soil. These results indicated that CuO NPs showed higher or comparable toxicity and bioavailability to pakchoi compared with Cu(NO) depending on soil properties, and nCuO are more easily to be transferred from roots to the aerial parts than CuO BPs and Cu(NO).
纳米氧化铜(nCuO)作为纳米肥料和农药的使用日益增多,引起了人们对其对土壤环境和农产品影响的关注。本研究选择了两种不同形状的 nCuO,即球形 nCuO(CuO NPs)和管状 nCuO(CuO NTs),以研究它们在两种性质不同的土壤中的生物有效性和对小白菜的毒性。同时,还使用了氧化铜块状颗粒(CuO BPs)和硝酸铜(Cu(NO₃)₂)进行比较。结果表明,所有的 Cu 处理都增加了酸性 GD 土壤中可 DTPA 提取的(DTPA-Cu)浓度,而碱性 HN 土壤中则增加较少。在 GD 土壤中,DTPA-Cu 浓度的顺序为 Cu(NO₃)₂≈CuO NPs>CuO BPs≈CuO NTs,而在 HN 土壤中则为 Cu(NO₃)₂>CuO NPs>CuO BPs≈CuO NTs。而对于小白菜地上部分的 Cu 含量,顺序为 CuO NPs>Cu(NO₃)₂>CuO NTs≈CuO BPs 在 GD 土壤中,CuO NPs≈Cu(NO₃)₂>CuO BPs≈CuO NTs 在 HN 土壤中。只有 CuO NPs 在 GD 土壤中降低了小白菜的生物量。在 HN 土壤中,CuO NPs、CuO BPs 和 Cu(NO₃)₂对小白菜叶绿素含量的降低没有显著差异,而在 GD 土壤中,CuO NPs 和 CuO BPs 导致小白菜叶绿素含量明显低于 Cu(NO₃)₂。此外,CuO NPs 和 Cu(NO₃)₂在 HN 土壤中增加了小白菜叶片中的 Mn 和 Mo,而在 GD 土壤中增加了 Zn。这些结果表明,取决于土壤性质,与 Cu(NO₃)₂相比,CuO NPs 对小白菜表现出更高或相当的毒性和生物有效性,并且 nCuO 比 CuO BPs 和 Cu(NO₃)₂更容易从根部转移到地上部分。