文章摘要
卢媛,宋琪,许佳瑶,孙红文.纳米氧化物对美托洛尔生物富集的影响研究[J].农业环境科学学报,2022,41(3):455-463.
纳米氧化物对美托洛尔生物富集的影响研究
Bioaccumulation of metoprolol in the presence of oxide nanoparticles
投稿时间:2021-08-14  
DOI:10.11654/jaes.2021-0915
中文关键词: 纳米氧化物  美托洛尔  鲤鱼  生物富集  吸附/解吸
英文关键词: oxide nanoparticle  metoprolol  carp  bioaccumulation  adsorption/desorption
基金项目:国家自然科学基金青年科学基金项目(42107447);南开大学大型仪器实验技术研发项目(21NKSYJS05)
作者单位E-mail
卢媛 南开大学环境科学与工程学院, 环境污染过程与基准教育部重点实验室, 天津 300350  
宋琪 大连理工大学外国语学院盘锦分院, 辽宁 盘锦 124221  
许佳瑶 沈阳大学环境学院, 沈阳 110044  
孙红文 南开大学环境科学与工程学院, 环境污染过程与基准教育部重点实验室, 天津 300350 sunhongwen@nankai.edu.cn 
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中文摘要:
      为揭示氧化物纳米颗粒(NPs)对离子型有机污染物在水生生物体内富集的影响,本研究考察了两种典型的氧化物NPs对鲤鱼富集β-阻断剂美托洛尔的影响以及美托洛尔在鱼体内各部位的分布,并通过批平衡实验进一步探讨了吸附解吸与生物富集的关系。结果表明:NPs共暴露时,在摄取阶段结束时美托洛尔生物浓缩因子(BCF)值增加了2.39倍(TiO2 NPs)和3.49倍(SiO2 NPs)。净化阶段鱼体内的美托洛尔半衰期由20.09d缩短到8.39d(TiO2 NPs)和6.13d(SiO2 NPs),净化结束时鱼体内的美托洛尔残余浓度则略有升高。NPs的共暴露未改变鲤鱼摄取美托洛尔的途径,但显著升高了鱼鳃和内脏中美托洛尔的浓度。相对于TiO2 NPs,SiO2 NPs对美托洛尔具有更强的、且不可逆的吸附,使用Freundlich模型拟合的lg KF值分别为2.21(TiO2 NPs)和4.47(SiO2 NPs)。研究表明NPs能够通过吸附载带促进鱼体对美托洛尔的富集,吸附态美托洛尔主要通过摄食和鳃的呼吸作用随NPs进入鱼体内,由NPs携带进入鱼体内的美托洛尔一部分发生解吸从而被鱼体利用,未发生解吸的部分随NPs的排出被排出体外。
英文摘要:
      To reveal the effect of oxide nanoparticles(NPs) on the bioaccumulation of ionic organic pollutants in aquatic organisms, the effects of two typical oxide NPs on the enrichment and distribution of the β-blocker metoprolol were investigated in carp(Cyprinus carpio). The relationship between adsorption/desorption and bioaccumulation was also examined through batch equilibrium experiments. At the end of the uptake phase, the bioconcentration factor(BCF) value had increased by 2.39 times(TiO2 NPs) and 3.49 times(SiO2 NPs). In the depuration phase, the half-life of metoprolol decreased from 20.09 d to 8.39 d(TiO2 NPs) and 6.13 d(SiO2 NPs). At the end of depuration, the residual concentration of metoprolol in carp increased slightly in the presence of NPs. Co-exposure to various types of NPs did not alter the method of metoprolol uptake by the carp; however, it did significantly increase the concentration of metoprolol in their gills and viscera. SiO2 NPs exhibited a stronger and irreversible adsorption capacity for metoprolol compared to TiO2 NPs; the lg K F values fitted by the Freundlich model were 2.21(TiO2 NPs) and 4.47(SiO2 NPs) respectively. Our results indicate that the presence of NPs promote the bioaccumulation of metoprolol in carp though sorption. Adsorbed metoprolol enters the body of the fish mainly via feeding and gill respiration; however, it is not completely desorbed or absorbed by the carp. Some associated metoprolol may be directly depurated from the body with the discharge of NPs.
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