Ge Jingke, Yang Qiongying, Fang Zhouxi, Liu Shuqi, Zhu Yue, Yao Jiang, Ma Zengling, Gonçalves Rodrigo J, Guan Wanchun
School of Laboratory Medicine and Life Science, Wenzhou Medical University, Wenzhou, Zhejiang, 325035, China; Wenzhou Key Laboratory of Sanitary Microbiology, Key Laboratory of Laboratory Medicine, Ministry of Education, Wenzhou Medical University, China; State Key Laboratory of Marine Environmental Science, College of Ocean and Earth Sciences, Xiamen University, Xiamen, Fujian, 361005, China.
School of Laboratory Medicine and Life Science, Wenzhou Medical University, Wenzhou, Zhejiang, 325035, China; Wenzhou Key Laboratory of Sanitary Microbiology, Key Laboratory of Laboratory Medicine, Ministry of Education, Wenzhou Medical University, China.
Environ Res. 2022 Apr 15;206:112598. doi: 10.1016/j.envres.2021.112598. Epub 2021 Dec 23.
The toxicity of microplastic particles (MPs) on aquatic environments has been widely reported; however, their effects on protists are still contradictory. For example, it is unclear if cell size and cell wall have a role in shaping the response of flagellates to MPs. In this study, seven marine flagellated microalgae (six Dinoflagellates and one Raphidophyceae) were incubated with 10 mg L MPs (polystyrene plastic micro-spheres, 1 μm diameter) to address the above question by measuring different response variables, i.e., growth, optimal photochemical efficiency (F/F), chlorophyll-a (Chl-a) content, superoxide dismutase (SOD) activity, and cell morphology. The effect of MPs on growth and F/F showed species-specificity effects. Maximum and minimum MPs-induced inhibitions were detected in Karenia mikimotoi (76.43%) and Akashiwo sanguinea (10.16%), respectively, while the rest of the species showed intermediate responses. The presence of MPs was associated with an average reduction of Chl-a content in most cases and with a higher superoxide dismutase activity in all cases. Seven species were classified into two groups by the variation of Chl-a under MPs treatment. One group (Prorocentrum minimum and Karenia mikimotoi) showed increased Chl-a, while the other (P. donghaiense, P. micans, Alexandrium tamarense, Akashiwo sanguinea, Heterosigma akashiwo) showed decreased Chl-a content. The MPs-induced growth inhibition was negatively correlated with cell size in the latter group. SEM images further indicated that MPs-induced malformation in the smaller cells (e.g., P. donghaiense and K. mikimotoi) was more severe than the bigger cells (e.g., A. sanguinea and P. micans), probably due to a relatively higher ratio of the cell surface to cell volume in the former. These results implicate that the effect of MPs on marine flagellated microalgae was related to the cell size among most species but not cell wall. Thus plastic pollution may have size-dependent effects on phytoplankton in future scenarios.
微塑料颗粒(MPs)对水生环境的毒性已有广泛报道;然而,它们对原生生物的影响仍存在矛盾。例如,尚不清楚细胞大小和细胞壁在塑造鞭毛虫对微塑料颗粒的反应中是否起作用。在本研究中,将七种海洋鞭毛微藻(六种甲藻和一种硅藻)与10 mg/L的微塑料颗粒(聚苯乙烯塑料微球,直径1μm)一起培养,通过测量不同的反应变量,即生长、最佳光化学效率(F/F)、叶绿素a(Chl-a)含量、超氧化物歧化酶(SOD)活性和细胞形态,来解决上述问题。微塑料颗粒对生长和F/F的影响表现出物种特异性效应。在米氏凯伦藻(76.43%)和血红哈卡藻(10.16%)中分别检测到微塑料颗粒诱导的最大和最小抑制,而其余物种表现出中间反应。在大多数情况下,微塑料颗粒的存在与Chl-a含量的平均降低有关,并且在所有情况下都与较高的超氧化物歧化酶活性有关。根据微塑料颗粒处理下Chl-a的变化,七种物种被分为两组。一组(微小原甲藻和米氏凯伦藻)Chl-a增加,而另一组(东海原甲藻、海洋原甲藻、塔玛亚历山大藻、血红哈卡藻、赤潮异弯藻)Chl-a含量降低。在后者中,微塑料颗粒诱导的生长抑制与细胞大小呈负相关。扫描电子显微镜图像进一步表明,微塑料颗粒对较小细胞(如东海原甲藻和米氏凯伦藻)诱导的畸形比大细胞(如血红哈卡藻和海洋原甲藻)更严重,这可能是由于前者细胞表面与细胞体积的比例相对较高。这些结果表明,微塑料颗粒对海洋鞭毛微藻的影响在大多数物种中与细胞大小有关,而与细胞壁无关。因此,在未来情况下,塑料污染可能对浮游植物产生大小依赖性影响。