Solar remediation of wastewater and saline water with concurrent production of value-added chemicals
Graphical Abstract
Section snippets
Sun-water-energy nexus
Over the past five decades, solar conversion technologies have received growing attention as an environmental-friendly and carbon–neutral process for producing value-added chemicals (H2, carbon chemicals, and hydrogen peroxide) in aqueous systems [1], [2], [3], [4]. The solar potential is excellent. The standard terrestrial sunlight (air mass 1.5 G, 1 kW m−2) can generate an average daily power of ~250 W m−2 yearly [5]. With this power density, a solar conversion process with 10% efficiency
Solar conversion systems
Three primary solar conversion systems have been developed so far for oxidizing water and producing value-added chemicals: photocatalysis (PC), photoelectrocatalysis (PEC), and photovoltaic-assisted electrocatalysis (PV-EC) (Fig. 1). This classification is rather arbitrary because various versions of hybrid systems have been reported. The uniqueness and relative features of the systems were compared and discussed elsewhere in detail [1], [3], [4], [7], [13] and this article briefly introduces
Production of reactive oxygen species for wastewater oxidation
The primary feature in solar wastewater splitting is production of single or many different reactive oxygen species (ROSs), such as hydroxyl radical (OH•), superoxide anion radical (O2•−), hydroperoxyl radical (HOO•), and ozone (O3). Most ROSs are quickly transformed into one another (Figs. 2a and 2b) [65]. The aqueous (in)organic substrates are also oxidized via direct inner-sphere charge transfer. However, the direct charge transfer usually proceeds only for strongly adsorbed substrates
Solar treatment of saline water
Chloride is one of the most abundant, ubiquitous inorganic ions in most water types. Its concentration is ~0.3 mM in unpolluted water, 1 mM in rivers, ~5 mM in agricultural and contaminated water, 10–100 mM in brackish water, ~0.5 mM in seawater, and > 0.5 mM in brine water. Besides, wastewater contains a large amount of chloride (maximum ~30 mM in dairy wastewater, ~450 mM in textile wastewater, and 20–40 mM in human urine) [24]. Accordingly, the effects and use of chloride in treating
Summary
This article introduced the solar splitting of wastewater and saline water and classified them into PC, PEC, and PV-EC systems. For each system, the oxidation reactions (generation of ROSs and RCSs) and reduction reactions (HER, HPR, and CO2RR) were separately discussed and their coupled reactions were examined for mechanisms and efficiency. Despite the same configuration, the wastewater and saline water splitting systems further consider the effect of (in)organic substrates in redox reactions.
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
This research was supported by the National Research Foundation (NRF-2018R1A6A1A03024962, NRF-2019R1A2C2002602, NRF-2021M3I3A1082880, and NRF-2021K1A4A7A02102598).
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