钻井废水处理质量毒理学评价

O. M. Krainiukov, I. A. Kryvytska, I. V. Zhytnetskyi
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引用次数: 0

摘要

目的。确定混凝剂和絮凝剂在钻井废水处理中的最佳组合和用量,随后测定所得发光液相的急性致死毒性。方法。采用有机混凝剂“Magnafloc”和“ECOFLOC”作为混凝剂,采用化学混凝法对钻井废弃物的液相进行了初步澄清。在混凝法对钻井废水净化程度不足的情况下,采用了Zetag 8180絮凝剂和纤维素胶的附加净化方法。清洗过程结束后,采用生物测试法对钻井废水进行毒理学分析,以确定水对甲壳类动物切齿蛇(Ceriodaphnia affinis lljeborg)的急性致死毒性。结果。在实验研究过程中,进行了多次实验,确定了处理钻井废水的混凝剂和絮凝剂的最佳用量,并测定了得到的钻井水照明液相的急性致死毒性。首先,对«Magnafloc»混凝剂和Zetag 8180混凝剂的组合进行了测试。所进行的研究表明,在使用有机混凝剂«Magnafloc»和另外使用浓度分别为1.2 g/dm3和1 kg/m3的絮凝剂Zetag 8180对钻井废物的液相进行化学混凝的过程中,最有效的清洁发生在初级澄清阶段。在上述浓度下使用这些化学试剂时,在纯化的钻井废水中测定了二级急性致死毒性(水为微毒)。为了确定混凝剂“ECOFLOC”和絮凝剂纤维素胶的最有效组合,进行了以下实验研究。根据所进行的研究结果,确定了最有效的清洁发生在化学混凝法对钻井废物的液相进行初级澄清时,使用混凝剂“ECOFLOC”和絮凝剂纤维素胶,浓度分别为1.2 g/dm3和1.3 kg/m3。当这些化学试剂在上述浓度下使用时,在纯化的钻井废水中测定了二级急性致死毒性(水为微毒)。结论。一般来说,需要注意的是,这种废水需要更彻底的处理,以防可能排放到水体中,并且只有在重复的钻井工艺过程中才能使用。生物试验的结果必须用于筛选剧毒对环境有害的化学品,并在各类废水形成和排放到水体的所有阶段控制其毒性,作为其质量控制的一个整体指标。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Toxicological assessment of drilling wastewater treatment quality
Purpose. To determine the optimal combination and consumption of coagulants and flocculants in the treatment of drilling wastewater, followed by determination of the acute lethal toxicity of the obtained illuminated liquid phase. Methods. Primary clarification of the liquid phase of drilling waste was carried out by the method of chemical coagulation using the organic coagulants "Magnafloc" and "ECOFLOC" as a coagulant. In case of insufficient degree of purification of drilling wastewater by coagulation method, an additional method of purification with Zetag 8180 flocculants and cellulose gum was used. After the cleaning process, a toxicological analysis of drilling wastewater was carried out using the biotesting method to determine the acute lethal toxicity of the water on the crustacean Ceriodaphnia affinis Lilljeborg. Results. In the process of experimental research, a number of experiments were conducted to determine the optimal consumption of coagulants and flocculant for the treatment of drilling wastewater, followed by the determination of the acute lethal toxicity of the obtained illuminated liquid phase of drilling water. First, combinations of «Magnafloc» coagulant and Zetag 8180 flocculant were tested. The conducted studies showed that the most effective cleaning occurs during the primary clarification of the liquid phase of drilling waste by the method of chemical coagulation using the organic coagulant «Magnafloc» and additionally the flocculant Zetag 8180 in concentrations of 1.2 g/dm3 and 1 kg/m3, respectively. When using these chemical reagents in the above-mentioned concentrations, the 2nd level of acute lethal toxicity was determined in purified drilling wastewater (water is slightly toxic). The following experimental studies were conducted in order to identify the most effective combination of coagulant «ECOFLOC» and flocculant cellulose gum. According to the results of the conducted research, it was established that the most effective cleaning occurs during the primary clarification of the liquid phase of drilling waste by the chemical coagulation method using the coagulant «ECOFLOC» and the flocculant - cellulose gum in concentrations of 1.2 g/dm3 and 1.3 kg/m3, respectively. When using these chemical reagents in the above-mentioned concentrations, the 2nd level of acute lethal toxicity was determined in the purified drilling wastewater (the water is slightly toxic). Conclusions. In general, it should be noted that such wastewater requires more thorough treatment in case of possible discharge to water bodies, and its use is possible only in repeated technological processes of drilling. The results of biotesting must be used for screening highly toxic environmentally hazardous chemicals and controlling the toxicity of various categories of wastewater at all stages of their formation and discharges into water bodies as an integral indicator in their quality control.
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