Pilot-scale treatment of hypersaline coal chemical wastewater with zero liquid discharge
Graphical abstract
Introduction
Coal is an essential raw material to many chemicals and fuels [1]. However, in the coal-to-chemical industry, converting 1 ton of coal to other chemicals may produce 1 m3 of hypersaline organic wastewater, which poses a serious threat to water security [2]. Besides inorganic ions, coal chemical wastewater contains a large amount of hazardous substances such as ammonia nitrogen, polycyclic aromatic, and phenols etc. [1]. Zero liquid discharge (ZLD) is a wastewater management strategy that advocates minimizing wastewater discharge and maximizing water reuse. To realize ZLD, advanced water treatment techniques are integrated to purify and reuse wastewater, as well as recover valuable byproducts.
Ultrafiltration (UF) and reverse osmosis (RO) integrated process is a mature technology that has been successfully applied in the reuse of hypersaline industrial wastewater in coal chemical industry, in which the UF process functions as a pretreatment step for removal of suspended particles and colloids, while the RO membrane rejects salt ions and organic contaminants [3], [4]. However, high-concentration organic contaminants and severe concentration polarization (CP) causes fouling/scaling of the RO membrane, especially in conventional spiral-wound configuration; this leads to a reduction in water recovery and requires frequent membrane cleaning, eventually hindering the efficiency and reliability of the system [5]. Compared to the spiral-wound configuration, the disc-tube RO (DTRO) provides shorter flow channel and more uniform flow distribution, thus generating higher turbulence and inhibiting CP effects along the membrane surface. The DTRO is hence more appropriate for treating hypersaline organic wastewater [6], [7], in which the water recovery can be elevated to 80% with a permeate flux of 34 L m−2 h−1 [8]. The flux of DTRO system can be easily recovered with periodic water flushing in long-term operation. In addition, an electrochemical oxidation (EO) process without addition of any other chemicals that oxidizes organic containments using electrochemically-generated hydroxyl radicals [9], was employed for removing ammonia nitrogen and COD (>90%) in the RO concentrate of coal gasification wastewater and coal tar wastewater under mild current density (30–50 mA cm−2) [10], [11].
Besides, other techniques are utilized for recovering salts from the RO concentrate stream to achieve maximum water reuse. NF has a unique characteristic of selective separating multivalent ions and organic compounds from monovalent ions [12]. Thus, a NF unit is capable of removing most chemical oxygen demand (COD) and sulfates (e.g. rejection rate of >99% for sodium sulfate) in the highly concentrated RO brine, only leaving chlorides (e.g. rejection rate of <20% for sodium chloride) in the permeate [13]. In order to ensure the purity of recovered salts, a pretreatment technique for completely eliminating hardness and organics in the NF concentrate is demanded prior to the evaporative crystallization process [14]. Chemical precipitation is an effective softening approach to remove the mineral scalants, as well as other trace constituents (e.g., strontium and silica et al.) via co-precipitation processes [15]. Even though the aforementioned technologies have been established, the technical and particularly economic feasibility of their industrial-scale integration have not been demonstrated so far.
The key objective of this study is to construct a pilot system for treating the RO concentrate from coal chemical industry at a maximum rate of 3 m3 h−1 for water reclamation and salt recovery (i.e., NaCl and Na2SO4). To achieve ZLD condition, the treatment chain includes nanofiltration (NF), disc tube reverse osmosis (DTRO), chemical softening, electro-oxidation (EO), and evaporation-crystallization. We experimentally test the filtration performance and stability of the proposed hybrid system, assess the fouling tendency of the DTRO and NF modules, and provide the energy and cost analysis in a long-term operation. The outcome of this study would serve as a valuable guide for ZLD process design and practical operation in subsequent large-scale industrial applications.
Section snippets
Raw water characteristics
This pilot-scale test was conducted in a wastewater reclamation plant for a coal chemistry industry located in Ningxia Hui autonomous region, China. Chemical softening and fiber filtration were employed for the pre-treatment. Ultrafiltration and two-stage reverse osmosis were used for the water reclamation (Fig. S1). The raw water fed into our ZLD process was collected from the secondary RO concentrate in the wastewater reclamation plant, and its characteristics were shown in Table 1.
Performance of the NF and DTRO systems
The NF system with a high recovery of 85% is first employed to effectively separate divalent ions from monovalent ions for facilitating salt recovery in this study. The transmembrane pressure across the pilot-scale NF system experiences some fluctuations first but stabilizes at approximately 2.3 bar after 25-days operation and remains constant for the rest operation (Fig. 2a). The stable transmembrane pressure indicates that almost no measurable membrane fouling occurred during the pilot-scale
Implications
Establishing a zero-liquid discharge approach is imperative for the coal chemical industry to overcome the imbalance between the supply shortage and huge demand of water resources. In this study, a pilot-scale ZLD plant was successfully developed to consistently recover huge quantity of water for reuse and to produce industrial-grade salts from hypersaline organic wastewater. However, ZLD technology applied in the treatment of industrial concentrate still faces two major challenges: large
Conclusions
This pilot study was carried out to evaluate the treatment and reuse of hypersaline coal chemical wastewater using a ZLD system that combines a NF-DTRO hybrid membrane system with a multiple-effect evaporator/crystallizer. The results indicated that the hybrid ZLD process achieves water recovery of about 98%. This plant was also equipped with a chemical softening and EO system to remove hardness and organic substances. Finally, through an evaporator-crystallizer, industrial-grade salts of Na2SO4
CRediT authorship contribution statement
Fayuan Chen: Investigation, Methodology, Writing - Original draft preparation. Zhong Zhang: Formal analysis. Fengmi Zeng: Graph editing. Yang Yang: Reviewing, and Editing. Xianhui Li: Writing - Reviewing and editing, Conceptualization.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
The study is jointly supported by the Program for Guangdong Introducing Innovative and Entrepreneurial Teams (2019ZT08L213), Postdoctoral Research Foundation of China (2019M662816), and Guangdong Basic and Applied Basic Research Foundation (2020A1515110716). Key Special Project for Introduced Talents Team of Southern Marine Science and Engineering Guangdong Laboratory (Guangzhou) (GML2019ZD0403), Guangdong Provincial Key Laboratory Project (2019B121203011), and “One hundred Youth” Science and
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