Hydraulic fracturing enables the enhanced recovery of hydrocarbons from shale formations while generating large volumes of produced water, i.e. wastewater from hydraulic fracturing. Treatment of produced water for reuse or final disposal is challenged by both high salinity and the presence of organic compounds. This dissertation is focused on the biological treatment of produced water using a mixed-culture biofilm approach to remove the available electron donors and therefore, potentially limit microbial growth, biocide use, and fouling of wells (during reuse) and membranes (during treatment prior to final disposal). Conventional activated sludge treatments are intolerant of high salinity, thus a biofilm approach was proposed to provide a more robust treatment method for high salinity produced waters. First, a preliminary evaluation on COD biodegradation (as acetate and guar gum) in synthetic and real produced waters was performed. Biodegradation was mainly driven by salinity; however, microbial activity was observed at salt concentrations as high as 100,000 mg/L TDS. Next, the effect of glutaraldehyde (GA), a commonly used biocide in hydraulic fracturing, on biodegradation of organic chemicals that are commonly used in fracturing fluids, is investigated. Results demonstrated that glutaraldehyde can affect the observed lag period and half-lives of the compounds, depending on the compound. Finally, the biodegradation of produced waters were evaluated in seven samples from different wells. Results showed a negative correlation between salinity and biodegradation rates. Moreover, variable biodegradation rates were observed at the same salt concentration. Finally, a Ra-226 biosorption was evaluated in synthetic and real produced waters to determine the efficacy of Ra-226 removal by a halophilic microalga D. salina.udThis study contributes to the understanding of biological treatment applicability in produced water management. The proposed biofilm approach could further encourage the use of similar approaches in produced water treatment and possibly in other industrial wastewaters containing high salinity and toxic chemicals. The evaluation of the biocide effect on biodegradation can enhance the understanding and accuracy of environmental model predictions for bio-treatment, bio-remediation, and pollution transport. Ultimately, this dissertation will contribute to more sustainable and economical produced water management strategies.
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机译:水力压裂能够增强页岩地层中碳氢化合物的采收率,同时产生大量采出水,即水力压裂产生的废水。高盐度和有机化合物的存在都对生产用水的再利用或最终处理提出了挑战。本论文的重点是使用混合培养生物膜方法去除可用的电子供体,从而对采出水进行生物处理,因此有可能限制微生物的生长,使用杀生物剂以及对孔和膜的污染(在重复使用之前的处理)最终处置)。常规的活性污泥处理不能耐受高盐度,因此提出了一种生物膜方法来为高盐度采出水提供更可靠的处理方法。首先,对合成水和实际采出水中的化学需氧量生物降解(如乙酸盐和瓜尔豆胶)进行了初步评估。生物降解主要是由盐分引起的。但是,在盐浓度高达100,000 mg / L TDS时观察到了微生物活性。接下来,研究了水力压裂中常用的杀菌剂戊二醛(GA)对压裂液中常用的有机化学物质的生物降解作用。结果表明,戊二醛可以影响化合物的观察到的延迟期和半衰期,具体取决于化合物。最后,在来自不同井的七个样品中评估了采出水的生物降解。结果显示盐度与生物降解率之间呈负相关。此外,在相同的盐浓度下观察到可变的生物降解速率。最后,在合成水和实际采出水中对Ra-226的生物吸附进行了评估,以确定通过嗜盐微藻D. salina去除Ra-226的功效。 ud这项研究有助于理解采出水管理中生物处理的适用性。拟议的生物膜方法可进一步鼓励在采出水处理以及可能在含高盐度和有毒化学物质的其他工业废水中使用类似方法。评估杀生物剂对生物降解的作用可以增强对用于生物处理,生物修复和污染转移的环境模型预测的理解和准确性。最终,本文将为制定更可持续,更经济的采水管理策略做出贡献。
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