Removal of heat stable salts from N-methyldiethanolamine wastewater by anion exchange resin coupled three-compartment electrodialysis
Introduction
The Gas Exporting Countries Forum expects global production and consumption of natural gas to increase from 3.9 trillion to 6 trillion m3 by 2050. This growth will boost the role of gas in the global energy balance from 27% to 34% in the same period [1]. In the process of natural gas exploitation and coal synthesis gas production, some hydrogen sulfide (H2S), carbon dioxide (CO2), and other organic sulfides, such as carbon disulfide (CS2) and carbonyl sulfide (COS), will inevitably be mixed. The high content of sulfides will not only corrode equipment and pipelines but also pollute the environment and threaten human health and safety. Further, a large amount of CO2 will reduce the calorific value of both natural gas and synthesis gas (syngas), and CO2 is also one of the main gases responsible for the greenhouse effect.
In industry, N-methyldiethanolamine (MDEA) is the most commonly used solvent for removing H2S, CO2, and other acidic compounds from natural gas and coal syngas because of its highly selective removal of acidic gases and its high capture efficiency. However, chemical degradation, thermal degradation, and oxidative degradation gradually occur during long-term desulfurization, along with the formation of heat stable salts (HSS). The formation of HSS is caused by the chemically irreversible reactions between these degradation products and other impurities, such as sulfur dioxide (SO2), nitrogen dioxide (NO2), CO2, and oxygen (O2), in the feed gas stream [2]. The composition of HSS is very complex; it includes organic acids, such as acetic and oxalic acid, as well as chloride and a variety of sulfates, sulfites, and nitrates [3]. The accumulation of these salts and other impurities can cause problems, such as excessive foaming and the capacity reduction of MDEA solution. Corrosion of the operating units, which reduces the equipment’s lifetime, has also been reported [4], [5]. The traditional method used to preserve the absorbent activity of MDEA is to partially remove degraded MDEA from the system and replace it with fresh MDEA solution. However, this leads to the discharge of a large amount of wastewater and an increase in the total cost of acidic gas removal of at least 10% [6]. Other options for preserving the absorbent activity include distilling the free amine away from the HSS and neutralizing MDEA with sodium or potassium caustic to reclaim MDEA from the HSS [7], [8]. However, because of a phase transition that occurs in the distillation process, the high energy consumption is a practical shortcoming of this method. Neutralization only solve amine loss, without getting rid of HSS from the spent MDEA wastewater. In addition, the number of sodium ions introduced negatively affects the absorption of H2S by the MDEA solution [9].
In recent years, several efforts have been made to develop new technologies to solve this issue concerning HSS and reclaim MDEA. The two most prominent and widely used types of technique among these are electrodialysis (ED) [6], [10], [11], and ion exchange resin techniques [12], [13]. ED has the advantages of having a low energy consumption, having a small area, and not requiring additional chemicals [14], [15]. However, because of the hydrolysis of MDEA in aqueous solution, MDEAH+ inevitably migrates to the concentrate compartment under the direct-current (DC) electric field, resulting in a 10–30% loss of MDEA during the ED process [10], [11]. Ion exchange resin techniques provide an effective and economical way to reduce MDEA loss with lowering energy consumption [16]. However, a low efficiency (approximately 50–65%) in the regeneration of exhausted exchange resin means that the process requires a high consumption of sodium or potassium hydroxide. Additionally, the alkaline wastewater produced by regeneration causes a secondary pollution that places a heavy burden on the environment [10], [13], [17].
From the above, it can be seen that the neutralization method, ED method, and ion exchange resin method all have advantages and disadvantages. In this study, we attempted to combine them to unite their advantages and eliminate their disadvantages. The first step was to reduce the loss of MDEA in the ED process by combining the ED and neutralization methods. To achieve this goal, a sodium hydroxide (NaOH) compartment was added to an ED stack to create a three-compartment electrodialysis (TED) stack. To further accelerate the HSS removal efficiency of the ED process, especially for the MDEA solution with low HSS concentration, an anion exchange resin was added into the dilute compartment of the TED stack to form an anion exchange resin coupled three-compartment electrodialysis (RTED) stack, which finally combined the ED process, neutralization method, and anion exchange resin method. Altogether, the aims of this research were to (1) investigate and compare the desalination mechanism, HSS removal efficiency, and MDEA loss of ED, TED, and RTED processes; (2) investigate the effect of NaOH concentration on the HSS removal efficiency and the MDEA loss of TED and RTED; (3) investigate the anion exchange membrane fouling of ED and RTED; and (4) investigate the economic viability of ED, TED, and RTED.
Section snippets
Materials
Spent MDEA wastewater was collected from the H2S desulfurization stripper in an integrated gasification combined cycle power plant in Tianjin, China. The feed solution contained 21.06 wt% MDEA and 5.19 wt% HSS. The pH and conductivity of the feed solution were 9.40 and 12.32 mS/cm, respectively. The specific water quality of the spent MDEA wastewater is shown in Table 1. For all three electrodialyzers, LCM (Liaoning Yichen, China) cation exchange membranes and LAM (Liaoning Yichen, China) anion
Comparison of conductivity in dilute compartment
Fig. 2 shows the conductivity in the dilute compartments of three electrodialyzers over time. For ED, the conductivity in the dilute compartment decreased over time because of continuous ion migration from the dilute compartment to the concentrate compartment. For RTED and TED, when the ions in the dilute compartment migrated to the concentrate compartment, the OH− in the concentrate compartment also migrated to the dilute compartment. Therefore, the ion concentration and the conductivity
Conclusion
- (1)
Through adding anion exchange resin and NaOH compartments in ED, RTED is able to effectively improve HSS removal efficiency and reduce the loss of MDEA.
- (2)
A relatively high NaOH concentration in the NaOH compartment, but no more than 3%, is beneficial for both improving the HSS removal efficiency and decreasing the loss of MDEA in TED and RTED.
- (3)
The RTED is able to effectively reduce the anion exchange membrane fouling.
- (4)
Compared with ED and RED, RTED is a cost-effective and environmentally friendly
CRediT authorship contribution statement
Fuqiang Chen: Conceptualization, Writing - original draft. Yongzhi Chi: Conceptualization, Methodology. Mengyi Zhang: Formal analysis. Zhiyuan Liu: Data curation. Xuening Fei: Writing - review & editing, Resources. Kun Yang: Supervision. Cuilian Fu: Project administration.
Acknowledgements
This work was supported by the National Water Pollution Control and Treatment Science and Technology Major Project (NO. 2017ZX07107) and Tianjin Enterprise Science and Technology Commissioner Project (NO. 18JCTPJC60800).
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