Environment and Sustainability Department, CSIR-IMMT, Bhubaneshwar, 751013, India.
Academy of Scientific and Innovative Research (AcSIR), Ghaziabad, 201002, India.
Environ Monit Assess. 2023 May 22;195(6):703. doi: 10.1007/s10661-023-11304-8.
The habitation and environment are affected by the stable isotopes of caesium (Cs) and strontium (Sr), as well as by their radioactive isotopes. The current work gives insight on Alstonia scholaris' capacity to phytoextract stable caesium (Cs) and strontium (Sr), as well as the plant's ability to protect against the toxicity of both elements. Experiments with Cs [0-5 mM (CsCl)] and Sr [0-3 mM (SrCl. 6HO)] dosing in controlled light, temperature, and humidity condition in greenhouse for 21 days were undertaken. Cs and Sr accumulation in different plant parts was quantified with atomic absorption spectroscopy (AAS) and inductively coupled plasma-optical emission spectrometry (ICP-OES) respectively. Hyper-accumulation capacity for Cs and Sr was estimated with indices like transfer factor (TF) and translocation factors (TrF). The uptake pattern of caesium in Alstonia scholaris is 5452.8-24,771.4 mg/kg DW (TF = 85.2-57.6) and in the case of Sr is 1307.4-8705.7 mg/kg DW (TF = 85.3-1.46). The findings demonstrated the plant's ability to transfer Cs and Sr to aboveground biomass on the basis of dry weight, with the majority of the metals being deposited in the shoot rather than the root portion of the plant. For Cs and Sr, with increasing concentration, the plants exhibited the enzymatic expression for defence against metal toxicity by free radicals compared to control. Field emission electron microscopy with energy-dispersive spectroscopy (FESEM with EDS) was employed to assess the spatial distribution of Cs and Sr in plant leaf, indicating the accumulation of Cs, Sr, and their homologous components.
居所和环境会受到铯 (Cs) 和锶 (Sr) 的稳定同位素以及它们的放射性同位素的影响。目前的工作深入了解了阿斯顿尼亚学者(Alstonia scholaris)植物吸收稳定的铯 (Cs) 和锶 (Sr) 的能力,以及该植物抵御这两种元素毒性的能力。在温室中,在受控的光照、温度和湿度条件下,进行了 Cs [0-5 mM (CsCl)] 和 Sr [0-3 mM (SrCl. 6HO)] 剂量的 21 天实验。采用原子吸收光谱法(AAS)和电感耦合等离子体发射光谱法(ICP-OES)分别定量测定不同植物部位的 Cs 和 Sr 积累量。采用转移因子(TF)和转运因子(TrF)等指数估算 Cs 和 Sr 的超积累能力。在 Alstonia scholaris 中,铯的摄取模式为 5452.8-24771.4 mg/kg DW(TF=85.2-57.6),而 Sr 的摄取模式为 1307.4-8705.7 mg/kg DW(TF=85.3-1.46)。研究结果表明,植物有能力将 Cs 和 Sr 转移到地上生物量中,基于干重,大部分金属沉积在植物的地上部分,而不是根部。对于 Cs 和 Sr,随着浓度的增加,与对照相比,植物表现出对自由基引起的金属毒性的酶表达防御能力。采用场发射电子显微镜与能谱(FESEM with EDS)评估 Cs 和 Sr 在植物叶片中的空间分布,表明 Cs、Sr 及其同源成分的积累。