Department of Civil Engineering, Indian Institute of Technology, New Delhi, India.
Department of Civil Engineering, Indian Institute of Technology, New Delhi, India.
Sci Total Environ. 2020 Oct 20;740:140140. doi: 10.1016/j.scitotenv.2020.140140. Epub 2020 Jun 11.
This study proposed a framework (termed as "nanoHealthRisk" hereafter) for incorporating i) interaction of nanoparticles (NPs) with fishes, ii) availability of NPs to the human digestive system, and iii) estimation of health risk due to fish consumption and inadvertent ingestion of NP-contaminated surface water, for the first time as per the literature review. The framework was applied for estimating health risks due to hypothetical exposures of pristine ZnO, CuO, and TiO NPs (without any surface functionalization) from fish tissues. Values of bio- concentration factors (BCF) of ZnO, CuO, and TiO NPs in fish and model distributions of bio-assimilation factor of ZnO, CuO and TiO NPs in the human digestive system were incorporated explicitly in the risk assessment of NPs for the first time. ZnO NP was observed to be transferred more to the human digestive system from aqueous matrix than the other two NPs. Maximum allowable values of NP posing no risk were found to be 0.115 mg/L, 0.152 mg/L, and 1.77 × 10 mg/L for pristine ZnO, CuO and TiO NP, respectively. At the environmental concentration range, exposures of studied NPs from aquatic environment under the assumptions used did not pose any health risk under the conditions studied in this study. More work is required to (1) Estimate bio-concentration factors of a mixture of NPs with other constituents in fish tissues, (2) Estimate dissolution of NP from fish tissue in human digestive media, (3) Generate new data to develop reference dose of NP for human health risk assessment, and (4) Study effect of NP fate in the water on health risk through fish consumption pathway. Until all above-mentioned aspects are not explicitly incorporated in the risk assessment framework, risk estimates do not represent the risk from environment completely. Thus, continuous monitoring of these NPs in the environment is required to protect health due to chronic exposure of small concentrations of NPs from an aqueous matrix.
本研究提出了一个框架(以下简称“nanoHealthRisk”),首次将以下三个方面纳入其中:i)纳米颗粒(NPs)与鱼类的相互作用,ii)NPs 对人类消化系统的可利用性,以及 iii)由于食用鱼类和误食受 NP 污染的地表水而导致的健康风险评估。该框架用于评估假设的纯 ZnO、CuO 和 TiO NPs(无任何表面功能化)从鱼类组织中暴露的健康风险。首次在风险评估中明确纳入了鱼类中 ZnO、CuO 和 TiO NPs 的生物浓缩因子(BCF)值和人体消化系统中 ZnO、CuO 和 TiO NPs 的生物同化因子的模型分布。结果表明,与其他两种 NPs 相比,ZnO NP 更易从水基质转移到人体消化系统。发现对于 pristine ZnO、CuO 和 TiO NP,不会造成风险的 NP 最大允许值分别为 0.115 mg/L、0.152 mg/L 和 1.77 × 10 mg/L。在环境浓度范围内,在所假设的条件下,从水生环境中暴露于研究中的 NPs 不会在本研究条件下造成任何健康风险。需要开展更多工作来:(1)估算鱼类组织中 NP 与其他成分混合物的生物浓缩因子;(2)估算 NP 从鱼类组织到人体消化介质中的溶解;(3)生成新数据以制定用于人类健康风险评估的 NP 参考剂量;(4)通过鱼类消费途径研究 NP 在水中的命运对健康风险的影响。在将所有上述方面明确纳入风险评估框架之前,风险评估并不能完全代表环境风险。因此,由于从水基质中以低浓度持续暴露,需要对这些 NPs 进行持续监测,以保护健康。