†Department of Plant and Soil Sciences, University of Kentucky, Lexington Kentucky 40546, United States.
‡Transatlantic Initiative for Nanotechnology and the Environment (TINE), University of Kentucky, Lexington, Kentucky 40546, Unites States.
Environ Sci Technol. 2015 Jul 21;49(14):8759-68. doi: 10.1021/acs.est.5b01211. Epub 2015 Jul 2.
Toxicogenomic responses in Medicago truncatula A17 were monitored following exposure to biosolids-amended soils. Treatments included biosolids produced using a pilot wastewater treatment plant with either no metal introduced into the influent (control); bulk/ionic TiO2, ZnO, and AgNO3 added to influent (bulk/dissolved treatment); or Ag, ZnO, and TiO2 engineered nanomaterials added to influent (ENM treatment) and then added to soil, which was aged in the field for 6 months. In our companion study, we found inhibition of nodulation in the ENM but not in the bulk/dissolved treatment. Gene expression profiling revealed highly distinct profiles with more than 10-fold down-regulation in 239 genes in M. truncatula roots from the ENM treatment, while gene expression patterns were similar between bulk/dissolved and control treatments. In response to ENM exposure, many of the identified biological pathways, gene ontologies, and individual genes are associated with nitrogen metabolism, nodulation, metal homeostasis, and stress responses. Expression levels of nine genes were independently confirmed with qRT-PCR. Exposure to ENMs induced unique shifts in expression profiles and biological pathways compared with bulk/dissolved treatment, despite the lack of difference in bioavailable metal fractions, metal oxidation state, and coordination environment between ENM and bulk/dissolved biosolids. As populations of Sinorhizobium meliloti Rm2011 were similar in bulk/dissolved and ENM treatments, our results suggest that inhibition of nodulation in the ENM treatment was primarily due to phytotoxicity, likely caused by enhanced bioavailability of Zn ions.
在将生物固体添加到土壤中后,监测了 Medicago truncatula A17 的毒理基因组反应。处理包括使用没有金属引入进水的中试废水处理厂生产的生物固体(对照);将大量/离子 TiO2、ZnO 和 AgNO3 添加到进水(大量/溶解处理);或向进水添加 Ag、ZnO 和 TiO2 工程纳米材料(ENM 处理),然后将其添加到土壤中,在田间老化 6 个月。在我们的配套研究中,我们发现 ENM 处理抑制了根瘤的形成,但在大量/溶解处理中没有。基因表达谱分析显示,ENM 处理的 M. truncatula 根中有 239 个基因的表达水平下调了 10 倍以上,而大量/溶解和对照处理之间的基因表达模式相似。暴露于 ENM 后,许多已识别的生物途径、基因本体和单个基因与氮代谢、根瘤形成、金属稳态和应激反应有关。使用 qRT-PCR 独立验证了九个基因的表达水平。与大量/溶解处理相比,尽管 ENM 和大量/溶解生物固体之间的生物可利用金属分数、金属氧化态和配位环境没有差异,但 ENM 暴露引起了独特的表达谱和生物途径的变化。由于 Sinorhizobium meliloti Rm2011 的种群在大量/溶解和 ENM 处理中相似,我们的结果表明,ENM 处理中根瘤形成的抑制主要是由于植物毒性,可能是由于 Zn 离子的生物利用度增强所致。