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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2019, Vol. 13 Issue (4) : 63    https://doi.org/10.1007/s11783-019-1147-y
REVIEW ARTICLE
Membrane-based treatment of shale oil and gas wastewater: The current state of knowledge
Tiezheng Tong(), Kenneth H. Carlson, Cristian A. Robbins, Zuoyou Zhang, Xuewei Du
Department of Civil and Environmental Engineering, Colorado State University, Fort Collins, CO 80523, USA
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Abstract

• Shale oil and gas production generates wastewater with complex composition.

• Membrane technologies emerged for the treatment of shale oil and gas wastewater.

• Membrane technologies should tolerate high TDS and consume low primary energy.

• Pretreatment is a key component of integrated wastewater treatment systems.

• Full-scale implementation of membrane technologies is highly desirable.

Shale oil and gas exploitation not only consumes substantial amounts of freshwater but also generates large quantities of hazardous wastewater. Tremendous research efforts have been invested in developing membrane-based technologies for the treatment of shale oil and gas wastewater. Despite their success at the laboratory scale, membrane processes have not been implemented at full scale in the oil and gas fields. In this article, we analyze the growing demands of wastewater treatment in shale oil and gas production, and then critically review the current stage of membrane technologies applied to the treatment of shale oil and gas wastewater. We focus on the unique niche of those technologies due to their advantages and limitations, and use mechanical vapor compression as the benchmark for comparison. We also highlight the importance of pretreatment as a key component of integrated treatment trains, in order to improve the performance of downstream membrane processes and water product quality. We emphasize the lack of sufficient efforts to scale up existing membrane technologies, and suggest that a stronger collaboration between academia and industry is of paramount importance to translate membrane technologies developed in the laboratory to the practical applications by the shale oil and gas industry.

Keywords Shale oil and gas production      Wastewater treatment and reuse      Membrane technology      Pretreatment      Academia-industry collaboration     
Corresponding Author(s): Tiezheng Tong   
Issue Date: 01 July 2019
 Cite this article:   
Tiezheng Tong,Kenneth H. Carlson,Cristian A. Robbins, et al. Membrane-based treatment of shale oil and gas wastewater: The current state of knowledge[J]. Front. Environ. Sci. Eng., 2019, 13(4): 63.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-019-1147-y
https://academic.hep.com.cn/fese/EN/Y2019/V13/I4/63
Fig.1  Wastewater  production volume per well during the first 12 months after hydraulic fracturing from (A) Permian Basin, (B) Eagle Ford Shale, (C) Marcellus Shale, and (D) Niobrara Shale. The data marked in red indicate gas-producing regions while those marked in blue indicate oil-producing regions. The data used in this figure are extracted from Kondash et al. (2018).
Fig.2  Three  periods of wastewater production from shale oil and gas wells, as well as variation of total dissolved salts (TDS) and organics with time. The TDS and organics from formation brines typically increases with well age, whereas the organics associated with fracturing fluids decrease with time. The shape of wastewater production volume is adopted from Bai et al. (2015).
Fig.3  Pilot-scale  treatment facilities employed for the treatment of shale oil and gas wastewater using (A) MVC (Hayes et al., 2014), (B) UF coupled with RO (Miller et al., 2013), and (C and D) thermolytic FO (McGinnis et al., 2013).
Fig.4  (A) The  specific energy consumption of RO and MVC. Although RO is much more energy efficient than MVC, the salinity of shale oil and gas wastewater often exceeds the salinity limit of RO (typically 70,000 mg/L), constraining the use of RO in the treatment of shale oil and gas wastewater. This gap necessitates the development of technologies that tolerate higher salinity than RO and consume less energy than MVC. These technologies include (B) forward osmosis and (C) membrane distillation, both of which are able to utilize low-grade thermal energy and reduce the consumption of primary electric energy. The style of this figure is adopted from Tong et al. (Tong and Elimelech, 2016)
Feature MVC MF/UF NF/RO FO MD
Technical Maturity
Energy Efficiency
Product Quality
Salinity Limit
Utilize Low-grade Thermal Energy
Capital Cost
On-site Treatment
Tab.1  Qualitative  comparison of technologies used as main step for shale oil and gas wastewater treatment. A higher number of stars indicate of more favorable features
Fig.5  Schematic  description of an on-site wastewater treatment train for shale oil and gas production, which utilizes precipitative softening and walnut shell filtration as the pretreatment steps, as well as membrane distillation as the main treatment step. CNG boiler stands for compressed natural gas boiler. This figure is adopted from Zhang et al. (2019).
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