Suares-Rocha Paula, Braunbeck Thomas, de Angelis Dejanira de Francheschi, Marin-Morales Maria Aparecida
Laboratory of Environmental Mutagenesis, Institute of Biosciences, University of São Paulo State (UNESP), Av. 24A, 1515, Bela Vista, Rio Claro, Brazil,
Environ Sci Pollut Res Int. 2015 Aug;22(16):12566-75. doi: 10.1007/s11356-015-4431-9. Epub 2015 Apr 25.
Oil refinery effluents contain many chemicals at variable concentrations. Therefore, it is difficult to predict potential effects on the environment. The Atibaia River (SP, Brazil), which serves as a source of water supply for many municipalities, receives the effluents of one of the biggest oil refinery of this country. The aim of this study was to identify the (eco)toxicity of fresh water sediments under the influence of this oil refinery through neutral red (cytotoxicity) and ethoxyresorufin-O-deethylase (EROD) assays (AhR-mediated toxicity) in RTL-W1 cells (derived from fish liver). Once the refinery captures the waters of Jaguarí River for the development of its activities and discharges its effluents after treatment into the Atibaia River, which then flows into Piracicaba River, sediments from both river systems were also investigated. The samples showed a high cytotoxic potential, even when compared to well-known pollution sites. However, the cytotoxicity of samples collected downstream the effluent was not higher than that of sediments collected upstream, which suggested that the refinery discharges are not the main source of pollution in those areas. No EROD activity could be recorded, which could be confirmed by chemical analyses of polycyclic aromatic hydrocarbons (PAHs) that revealed a high concentration of phenanthrene, anthracene, fluoranthene, and pyrene, which are not EROD inducers in RTL-W1 cells. In contrast, high concentrations of PAHs were found upstream the refinery effluent, corroborating cytotoxicity results from the neutral red assay. A decrease of PAHs was recorded from upstream to downstream the refinery effluent, probably due to dilution of compounds following water discharges. On the other hand, these discharges apparently contribute specifically to the amount of anthracene in the river, since an increase of anthracene concentrations could be recorded downstream the effluent. Since the extrapolation of results from acute toxicity to specific toxic effects with different modes of action is a complex task, complementary bioassays covering additional specific effects should be applied in future studies for better understanding of the overall ecotoxicity of those environments.
炼油厂废水含有多种浓度各异的化学物质。因此,很难预测其对环境的潜在影响。阿蒂巴亚河(巴西圣保罗州)是多个城市的供水水源,接纳了该国最大炼油厂之一的废水。本研究的目的是通过在RTL-W1细胞(源自鱼肝)中进行中性红(细胞毒性)和乙氧异吩唑酮-O-脱乙基酶(EROD)测定(芳烃受体介导的毒性),确定受该炼油厂影响的淡水沉积物的(生态)毒性。由于炼油厂取水于雅瓜里河用于其生产活动,并在处理后将废水排放到阿蒂巴亚河,阿蒂巴亚河随后流入皮拉西卡巴河,因此对这两个河流系统的沉积物也进行了调查。这些样本显示出很高的细胞毒性潜力,即使与著名的污染场地相比也是如此。然而,在废水排放下游采集的样本的细胞毒性并不高于上游采集的沉积物,这表明炼油厂的排放并非这些区域的主要污染源。未记录到EROD活性,这可以通过多环芳烃(PAHs)的化学分析得到证实,分析显示菲、蒽、荧蒽和芘的浓度很高,而这些物质在RTL-W1细胞中并非EROD诱导剂。相反,在炼油厂废水排放上游发现了高浓度的PAHs,这与中性红测定的细胞毒性结果相符。从炼油厂废水排放的上游到下游,PAHs浓度有所下降,这可能是由于废水排放后化合物被稀释。另一方面,这些排放显然特别增加了河流中蒽的含量,因为在废水排放下游可以记录到蒽浓度的增加。由于将急性毒性结果外推到具有不同作用方式的特定毒性效应是一项复杂的任务,未来的研究应采用涵盖其他特定效应的补充生物测定法,以便更好地了解这些环境的整体生态毒性。