Shenzhen Key Laboratory of Environmental Chemistry and Ecological Remediation, College of Chemistry and Environmental Engineering, Shenzhen University, Shenzhen 518060, China.
Shenzhen Key Laboratory of Environmental Chemistry and Ecological Remediation, College of Chemistry and Environmental Engineering, Shenzhen University, Shenzhen 518060, China.
J Hazard Mater. 2022 Mar 5;425:127908. doi: 10.1016/j.jhazmat.2021.127908. Epub 2021 Nov 26.
Microplastics (MPs) have received an increasing attention because of their ubiquitous presence and aquatic toxicity associated with MPs and MP-bound contaminants in the natural water. This review is to critically examine the chemical additives leached from MPs, the altered contaminant behaviors and the resulting changes in their aquatic ecotoxicity. Available data suggest that heavy metals Zn, Cr, Pb, and Cd regulated and present in plastics at the sub-mg g to mg g level can leach a significant amount depending on MPs size, aging, pH, and salinity conditions. MP-bound organic contaminants are primarily additive-derived (e.g., brominated diphenyl ethers, nonylphenol, and bisphenol A) at the µg g to mg g level, and secondarily pyrogenic and legacy origins (e.g., PAHs and PCBs) in the range of ng g and mg g. MPs tend to have higher but more variable sorption capacities for organic compounds than metals (1.77 ± 2.34 vs. 0.82 ± 0.94 mg g). MPs alter the behavior of heavy metals through the electrostatic interactions and surface complexation, while the transport of additive derived organic compounds are altered primarily through hydrophobic effect as supported by a positive correlation (R = 0.71) between the logarithmic MPs-adsorbed concentrations and octanol/water partition coefficients (K) of organic compounds. MPs constitute less than 0.01% of the total mass of aquatic particulates in typical waters, but play a discernible role in the local partitioning and long-distance movement of contaminants. MPs alone exert higher toxicity to invertebrates than algae; however, when MPs co-occur with pollutants, both synergistic and antagonistic toxicities are observed depending mainly on the ingestibility of MPs, the extent of sorption, MPs as a transport vector or a sink to scavenge pollutants. We finally suggest several key areas of future research directions and needed data concerning the role of MPs in mitigating pollutant leaching, transport and risk under conditions mimicking natural and polluted waters.
微塑料(MPs)因其普遍存在和与 MPs 相关的水生毒性以及天然水中 MP 结合的污染物而受到越来越多的关注。本综述旨在批判性地检查从 MPs 浸出的化学添加剂、改变的污染物行为以及由此导致的水生生态毒性变化。现有数据表明,在亚毫克/克至毫克/克水平上受调控和存在于塑料中的重金属 Zn、Cr、Pb 和 Cd 可以根据 MPs 的大小、老化、pH 值和盐度条件浸出大量重金属。MP 结合的有机污染物主要是添加剂衍生的(例如,溴化二苯醚、壬基酚和双酚 A),浓度在微克/克至毫克/克范围内,其次是热生成和遗留来源(例如,多环芳烃和多氯联苯),浓度在纳克/克和毫克/克范围内。MPs 对有机化合物的吸附能力往往高于金属(1.77±2.34 与 0.82±0.94 毫克/克),但更具变异性。MPs 通过静电相互作用和表面络合改变重金属的行为,而添加剂衍生的有机化合物的传输则主要通过疏水性效应改变,这得到了有机化合物的 MPs 吸附浓度的对数与辛醇/水分配系数(K)之间的正相关(R=0.71)的支持。MPs 在典型水中的水相颗粒物质总质量中不到 0.01%,但在污染物的局部分配和远距离迁移中发挥了明显作用。MPs 对无脊椎动物的毒性高于藻类;然而,当 MPs 与污染物共存时,根据 MPs 的可摄取性、吸附程度、MPs 作为污染物传输载体或清除污染物的汇,观察到协同和拮抗毒性。最后,我们建议在模拟天然和污染水条件下,针对 MPs 减轻污染物浸出、迁移和风险的作用,提出几个未来的研究方向和需要的数据。