CBET Research Group, Department of Zoology and Cell Biology, Faculty of Science and Technology and Research Center for Marine Biology and Biotechnology (PiE-UPV/EHU) University of the Basque Country, Areatza z/g, 48620, Plentzia, Bizkaia, Basque Country, Spain; Universite de Pau et des Pays de l'Adour, E2S/UPPA, IPREM5254, 64000, Pau, France.
CBET Research Group, Department of Zoology and Cell Biology, Faculty of Science and Technology and Research Center for Marine Biology and Biotechnology (PiE-UPV/EHU) University of the Basque Country, Areatza z/g, 48620, Plentzia, Bizkaia, Basque Country, Spain.
Environ Res. 2022 Sep;212(Pt D):113467. doi: 10.1016/j.envres.2022.113467. Epub 2022 May 16.
Dispersants, used for combating oil spills, increase hydrocarbon bioavailability promoting their biodegradation. Oil weathering process introduces harmful soluble hydrocarbons, such as polycyclic aromatic hydrocarbons (PAHs), into the water column, resulting in water-accommodated fraction (WAF). The presence of dispersants can influence the weathering process by increasing PAHs solubility, toxicity and biodegradability. However, little is known on how dispersants affect microbial communities and their degradation capacities, especially in cold environment where low temperature decreases microbial activity and thus hydrocarbon degradation. Here, we investigated the microbial community dynamics in cold water contaminated by WAF prepared from crude oil with or without a commercial dispersant (Finasol OSR52). The WAFs, prepared with Naphthenic North Atlantic crude oil, were used to contaminate seawater from Norwegian cold sites, one oil-contaminated and the other pristine. The WAF-contaminated seawaters were maintained in microcosms at 4 °C for 21 days. The content of PAHs and microbial compositions (16S rRNA gene sequencing) were determined at days 0, 7, 14 and 21. In addition, the 96 h toxicity assay with adult Acartia tonsa revealed WAFs toxicity at days 0 and 21. The toxicity of WAF mixtures, with and without dispersant, against Acartia tonsa was reduced during the experiment, but PAHs removal was not increased. The water from the oil-contaminated site showed the highest PAHs removal revealing legacy effect (presence of microorganisms adapted to PAHs). Additionally, our results reveal: i) microbial community plasticity allowing the adaptation to the presence of PAHs and dispersant, ii) specific bacteria taxa probably involved in PAHs degradation, and iii) dispersants shape the microbial communities dynamics by stimulating potential dispersant-degrading taxa, such as Fusibacter. Thus, our results provide valuable insights on the role of microbial community in determining the fate of water-solubilized hydrocarbon in cold environment while questioning the role of dispersant used for fighting oil spill.
分散剂用于应对溢油事故,可提高烃类物质的生物利用度,促进其生物降解。石油风化过程将有害的可溶性烃类物质(如多环芳烃,PAHs)带入水柱中,形成水可容纳部分(WAF)。分散剂的存在会通过增加 PAHs 的溶解度、毒性和生物降解性来影响风化过程。然而,对于分散剂如何影响微生物群落及其降解能力,人们知之甚少,特别是在低温会降低微生物活性从而影响烃类物质降解的寒冷环境中。在这里,我们研究了来自含有或不含有商业分散剂(Finasol OSR52)的北大西洋粗油制备的 WAF 污染的冷水微生物群落动态。用 WAF 污染取自挪威寒冷站点的海水,一个是石油污染的,另一个是原始的。将 WAF 污染的海水在 4°C 的微环境中保持 21 天。在第 0、7、14 和 21 天分别测定了 PAHs 的含量和微生物组成(16S rRNA 基因测序)。此外,还进行了含有和不含有分散剂的 WAF 对成体桡足类生物 Acartia tonsa 的 96 小时毒性试验。在第 0 天和第 21 天,WAF 混合物对 Acartia tonsa 的毒性。没有分散剂的 WAF 混合物的毒性在实验过程中降低,但去除 PAHs 的效果并没有增加。石油污染场地的水显示出最高的 PAHs 去除率,这表明存在适应 PAHs 的微生物(遗留效应)。此外,我们的结果揭示:i)微生物群落的可塑性允许它们适应 PAHs 和分散剂的存在,ii)可能参与 PAHs 降解的特定细菌类群,iii)分散剂通过刺激潜在的分散剂降解类群(如 Fusibacter)来塑造微生物群落动态。因此,我们的研究结果为寒冷环境下水溶性烃类的归宿中微生物群落的作用提供了有价值的见解,同时也对用于应对溢油事故的分散剂的作用提出了质疑。