†Engineering School of Sustainable Infrastructure and Environment, Dept. of Environmental Engineering Sciences, University of Florida, Gainesville, Florida 32611, United States.
‡Department of Chemical Engineering, University of Florida, Gainesville, Florida 32611, United States.
Environ Sci Technol. 2015 Mar 17;49(6):3913-21. doi: 10.1021/es505925m. Epub 2015 Mar 4.
Over the past decade, extensive research has been completed on the potential threats of single-wall carbon nanotubes (SWCNTs) to living organisms upon release to aquatic systems. However, these studies have focused primarily on the link between adverse biological effects in exposed test organisms on the length, diameter, and metallic impurity content of SWCNTs. In contrast, few studies have focused on the bioeffects of the different SWCNTs in the as-produced mixture, which contain both metallic (m-SWCNT) and semiconducting (s-SWCNT) species. Using selective adsorption onto hydrogels, high purity m-SWCNT and s-SWCNT fractions were produced and their biological impacts determined in dose-response studies with Pseudokirchneriella subcapitata as test organism. The results show significant differences in the biological responses of P. subcapitata exposed to high purity m- and s-SWCNT fractions. Contrary to the biological response observed using SWCNTs separated by density gradient ultracentrifugation, it is found that the high-pressure CO conversion (HiPco) s-SWCNT fraction separated by selective adsorption causes increased biological impact. These findings suggest that s-SWCNTs are the primary factor driving the adverse biological responses observed from P. subcapitata cells exposed to our as-produced suspensions. Finally, the toxicity of the s-SWCNT fraction is mitigated by increasing the concentration of biocompatible surfactant in the suspensions, likely altering the nature of surfactant coverage along SWCNT sidewalls, thereby reducing potential physical interaction with algal cells. These findings highlight the need to couple sample processing and toxicity response studies.
在过去的十年中,人们对单壁碳纳米管(SWCNTs)释放到水生系统后对生物体的潜在威胁进行了广泛的研究。然而,这些研究主要集中在暴露于 SWCNTs 的受试生物的不良生物效应与 SWCNTs 的长度、直径和金属杂质含量之间的联系上。相比之下,很少有研究关注生产混合物中不同 SWCNTs 的生物效应,这些混合物中包含金属(m-SWCNT)和半导体(s-SWCNT)物种。通过选择性吸附到水凝胶上,产生了高纯度的 m-SWCNT 和 s-SWCNT 馏分,并在以假鱼腥藻为受试生物的剂量反应研究中确定了它们的生物影响。结果表明,暴露于高纯度 m-SWCNT 和 s-SWCNT 馏分的假鱼腥藻的生物反应存在显著差异。与通过密度梯度超速离心分离的 SWCNTs 观察到的生物反应相反,发现通过选择性吸附分离的高压 CO 转化(HiPco)s-SWCNT 馏分导致生物影响增加。这些发现表明,s-SWCNTs 是导致暴露于我们生产的悬浮液中的假鱼腥藻细胞观察到的不良生物反应的主要因素。最后,通过增加悬浮液中生物相容性表面活性剂的浓度来减轻 s-SWCNT 馏分的毒性,这可能改变表面活性剂沿 SWCNT 侧壁的覆盖性质,从而减少与藻类细胞的潜在物理相互作用。这些发现强调了需要将样品处理和毒性反应研究结合起来。