Department of Civil, Environmental and Architectural Engineering, University of Padova, Via Marzolo 9, 35131, Padova, Italy.
Department of Environmental Sciences, Informatics and Statistics, Ca' Foscari University of Venice, Via Torino 155, I-30172 Venice, Italy; Società Estense Servizi Ambientali S.E.S.A., Este, PD, Via Comuna, 5/B, 35042 Este, Padova, Italy.
Chemosphere. 2024 Apr;353:141594. doi: 10.1016/j.chemosphere.2024.141594. Epub 2024 Mar 1.
The uptake and translocation of four polybrominated diphenyl ethers (PBDEs) and four novel brominated flame retardants (NBFRs) in tomato plants (Solanum lycopersicum L.) were investigated via the RHIZOtest, a standard soil-based biotest, optimized for organic compounds. Tomato plants were exposed to soil samples spiked with 0 (i.e. control), 5.00 or 50.00 ng gdw of each compound. Compared of those of the control, exposure to increasing spiking concentrations resulted in average reductions of 13% and 26% (w/w) in tomato plant biomass. Higher concentrations of NBFRs were analyzed both in roots, ranging from 0.23 to 8.01 ng gdw for PBDEs and from 1.25 to 18.51 ng gdw for NBFRs, and in shoots, ranging from 0.09 to 5.58 ng gdw and from 0.47 to 7.78 ng gdw for PBDEs and NBFRs, respectively. This corresponded to an average soil uptake of 5% for PBDEs and 9% for NBFRs at the lower soil-spiking level, and 3% for PBDEs and 6% for NBFRs at the higher soil spiking level. Consequently, among both initial spiking levels, the soil-root concentration factor (RCF) values were lower on average for PBDEs (0.13 ± 0.05 g dw soil gdw roots) than for NBFRs (0.33 ± 0.16 g dw soil gdw roots). Conversely, nondifferent values of the root-shoot transfer factor (TF) were calculated for both PBDEs (0.54 ± 0.13 g dw roots gdw shoots) and NBFRs (0.49 ± 0.24 g dw roots gdw shoots). The differences and similarities reported in the RCF and TF between and within the two groups of compounds can be explained by their properties. The calculated RCF and TF values of the PBDEs exhibited a decreasing trend as the number of bromine atoms increased. Additionally, a robust negative linear correlation was observed between RCF values and the respective logK values for the PBDEs, at both soil-spiking levels. The root uptake of NBFRs exhibited a negative correlation with their hydrophobicity; however, this was not observed in the context of root-to-shoot transfer. The presence of a second aromatic ring appears to be the key factor influencing the observed variations in NBFRs, with biphenyl NBFRs (BTBPE and DBDPE) characterized by lower uptake and reduced translocation potential than monophenyl PBEB and HBB. Understanding the transfer of these compounds to crops, especially near plastic recycling waste sites, is crucial for understanding the risks of their potential inclusion in the human food chain.
采用 RHIZOtest 研究了四种多溴二苯醚(PBDEs)和四种新型溴化阻燃剂(NBFRs)在番茄植物(Solanum lycopersicum L.)中的吸收和迁移情况。RHIZOtest 是一种优化用于有机化合物的标准土壤生物测试。与对照组相比,暴露于 5.00 或 50.00ng gdw 浓度的每种化合物的土壤样本中,番茄植物的生物量平均分别降低了 13%和 26%。在根部分析了更高浓度的 NBFRs,范围从 0.23 到 8.01ng gdw 用于 PBDEs 和从 1.25 到 18.51ng gdw 用于 NBFRs,在茎中,范围从 0.09 到 5.58ng gdw 和从 0.47 到 7.78ng gdw 用于 PBDEs 和 NBFRs。这对应于在较低土壤喷注水平下 PBDEs 为 5%和 NBFRs 为 9%的平均土壤吸收,在较高土壤喷注水平下 PBDEs 为 3%和 NBFRs 为 6%。因此,在两个初始喷注水平中,PBDEs 的土壤-根浓度因子(RCF)值(0.13±0.05g dw 土壤 gdw 根)平均低于 NBFRs(0.33±0.16g dw 土壤 gdw 根)。相反,对于 PBDEs(0.54±0.13g dw 根 gdw 茎)和 NBFRs(0.49±0.24g dw 根 gdw 茎),计算出的根-茎转移因子(TF)值相同。可以用两种化合物的性质来解释报告的 RCF 和 TF 之间和内部的差异和相似之处。随着溴原子数量的增加,计算出的 PBDEs 的 RCF 和 TF 值呈下降趋势。此外,在两个土壤喷注水平下,都观察到 PBDEs 的 RCF 值与相应的 logK 值之间存在强负线性相关性。NBFRs 的根吸收与疏水性呈负相关;然而,在根到茎的转移中没有观察到这种情况。第二个芳环的存在似乎是影响 NBFRs 观察到的变化的关键因素,双苯 NBFRs(BTBPE 和 DBDPE)的摄取量较低,迁移潜力降低,而单苯 PBEB 和 HBB 则不是。了解这些化合物向作物的转移,特别是在塑料回收废物场附近,对于了解它们可能包含在人类食物链中的潜在风险至关重要。