Laboratoire de Phytoplanctonologie, Faculté des Sciences de Bizerte, Université de Carthage, Zarzouna, 7021 Bizerte, Tunisia; MARBEC, Univ Montpellier, IRD, Ifremer, CNRS, Sète, France.
Department of Biology, University of Ottawa, Ottawa K1N 6N5, Canada.
J Hazard Mater. 2023 Jan 5;441:129869. doi: 10.1016/j.jhazmat.2022.129869. Epub 2022 Aug 30.
The first synthetic review of the PAHs effects on microalgae in experimental studies and aquatic ecosystems is provided. Phytoplankton and phytobenthos from marine and freshwaters show a wide range of sensitivities to PAHs, and can accumulate, transfer and degrade PAHs. Different toxicological endpoints including growth, chlorophyll a, in vivo fluorescence yield, membrane integrity, lipid content, anti-oxidant responses and gene expression are reported for both freshwater and marine microalgal species exposed to PAHs in culture and in natural assemblages. Photosynthesis, the key process carried out by microalgae appears to be the most impacted by PAH exposure. The effect of PAHs is both dose- and species-dependent and influenced by environmental factors such as UV radiation, temperature, and salinity. Under natural conditions, PAHs are typically present in mixtures and the toxic effects induced by single PAHs are not necessarily extrapolated to mixtures. Natural microalgal communities appear more sensitive to PAH contamination than microalgae in monospecific culture. To further refine the ecological risks linked to PAH exposure, species-sensitivity distributions (SSD) were analyzed based on published ECs (half-maximal effective concentrations during exposure). HC (harmful concentration for 5% of the species assessed) was derived from SSD to provide a toxicity ranking for each of nine PAHs. The most water-soluble PAHs naphthalene (HC = 650 µg/L), acenaphthene (HC = 274 µg/L), and fluorene (HC = 76.8 µg/L) are the least toxic to microalgae, whereas benzo[a]pyrene (HC = 0.834 µg/L) appeared as the more toxic. No relationship between EC and cell biovolume was established, which does not support assumptions that larger microalgal cells are less sensitive to PAHs, and calls for further experimental evidence. The global PAHs HC for marine species was on average higher than for freshwater species (26.3 and 1.09 µg/L, respectively), suggesting a greater tolerance of marine phytoplankton towards PAHs. Nevertheless, an important number of experimental exposure concentrations and reported toxicity thresholds are above known PAHs solubility in water. The precise and accurate assessment of PAHs toxicity to microalgae will continue to benefit from more rigorously designed experimental studies, including control of exposure duration and biometric data on test microalgae.
提供了对实验研究和水生生态系统中多环芳烃(PAHs)对微藻影响的首次综合综述。来自海洋和淡水的浮游植物和底栖植物对 PAHs 的敏感性范围很广,并且可以积累、转移和降解 PAHs。报道了不同的毒理学终点,包括生长、叶绿素 a、体内荧光产率、膜完整性、脂质含量、抗氧化反应和基因表达,这些终点适用于在培养和自然组合中暴露于 PAHs 的淡水和海洋微藻物种。光合作用是微藻进行的关键过程,似乎受到 PAH 暴露的影响最大。PAHs 的影响既取决于剂量又取决于物种,并且受环境因素(如紫外线辐射、温度和盐度)的影响。在自然条件下,PAHs 通常以混合物的形式存在,并且单一 PAHs 引起的毒性效应不一定可以推断到混合物。自然微藻群落比单一培养的微藻对 PAH 污染更为敏感。为了进一步细化与 PAH 暴露相关的生态风险,根据已发表的 EC(暴露期间的半最大有效浓度)分析了物种敏感性分布(SSD)。从 SSD 中得出 HC(评估的 5%物种的有害浓度),以提供对 9 种 PAHs 中每一种的毒性排名。最易溶于水的 PAHs 萘(HC = 650 µg/L)、苊(HC = 274 µg/L)和芴(HC = 76.8 µg/L)对微藻的毒性最小,而苯并[a]芘(HC = 0.834 µg/L)的毒性最大。没有建立 EC 与细胞生物量之间的关系,这并不支持较大的微藻细胞对 PAHs 的敏感性较低的假设,需要进一步的实验证据。海洋物种的全球 PAHs HC 平均值高于淡水物种(分别为 26.3 和 1.09 µg/L),这表明海洋浮游植物对 PAHs 的耐受性更强。尽管如此,许多实验暴露浓度和报告的毒性阈值都高于水中已知的 PAHs 溶解度。要更准确地评估 PAHs 对微藻的毒性,将继续受益于设计更严格的实验研究,包括控制暴露持续时间和测试微藻的生物计量数据。