Abstract

Summary An increased awareness of the environmental impact and operational costs associated with freshwater usage and wastewater disposal in energy production has shifted industry interest toward replacing freshwater sources with lower-quality or recycled water in oilfield applications, and has highlighted the importance of addressing toxicity as part of a successful waste-management plan. Poor-quality and recycled waters often contain high concentrations of bacterial assemblages, which can cause operational challenges such as corrosion, slime formation, and souring. Microbial-control agents, such as biocides, are subsequently necessary to manage bacteriological problems. However, these chemicals are highly reactive and can react indiscriminately with biological targets, making their toxicity both a performance metric and an ecological, human-health, and disposal concern. The luminescent-bacteria toxicity test presented in this work, for instance, is a key regulatory parameter in the pumpoff and landspray disposal of drilling fluids in Alberta, Canada. Considering the necessary toxicity of biocides, controlled detoxification following use is a pertinent factor in responsible hazard management. Formaldehyde-releasing agents are the most widely used category of microbial-control additives that slowly and continuously release small amounts of formaldehyde, a toxic environmental pollutant and known human carcinogen. This research evaluated the acute (short-term) aquatic toxicity of two liquid formaldehyde-releasing biocides, identified necessary parameters for their detoxification, measured the resulting change in their toxicity over time, and used regulatory requirements for toxicity testing set by the Alberta Energy Regulator (AER) for drilling-waste management to evaluate the practical relevance of this detoxification to waste-management practices. The additives investigated were a tetrakis(hydroxymethyl)phosphonium sulfate (THPS)-based product, and a 1,3-dimethylol-5,5-dimethylhydantoin (DMDMH)-based product. Laboratory results suggest that the THPS-based additive was more toxic than the DMDMH-based additive on a percent volume basis, and pH was an important factor in THPS toxicity. Aeration alone decreased the toxicity of DMDMH over the course of the experiment, while a combination of aeration and pH increase were necessary to decrease the toxicity of THPS over the same time period. This work presents a proof of concept for a relatively simple and cost-effective detoxification of the evaluated additives, highlights the key parameters for this process, and uses toxicity-threshold levels referenced by the AER drilling-waste-management directive to evaluate their application in waste-assessment practices.

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