Electro-oxidation of tetracycline in ethanol-water mixture using DSA-Cl2 anode and stimulating/monitoring the formation of organic radicals
Graphical abstract
Introduction
Over the past few decades, there has been an increasingly growing interest in the detection of emerging pollutants (EPs) in environmental matrices due to the threats posed by the presence of these contaminants in the environment and the risks to human health caused by the exposure to these pollutants. A wide range of substances which are disposed of into the environment are considered EPs; these substances include pharmaceutical products, personal care products, pesticides, surfactants, among others. EPs can contaminate the soil, water and atmosphere, and have been found to pose serious threats to the ecosystem and to human health (Deblonde et al., 2011; Galindo-Miranda et al., 2019). In fact, most of these EPs are considered endocrine disruptors as they alter the endocrine functions of the body, causing a wide range of chronic diseases (Diamanti-Kandarakis et al., 2009). Considering that EPs are present in the environment in extremely low concentrations (of the order of μg L−1), their removal process is often complex, and this has become a matter of grave concern to researchers and other stakeholders due to the aforementioned risks posed by these contaminants (Brillas, 2014; Montagner et al., 2017; Silva et al., 2016).
Pharmaceutical substances have become one of the main pollutants of water. Among these substances, antibiotics are the pollutants class seen to be of the greatest concern in the scientific community because of their widespread use by humans and animals for the treatment of infections and other illnesses (Santos et al., 2021). The human organism is incapable of fully metabolizing antibiotics; as such, the unmetabolized contents are eliminated through feces and urine, which are eventually disposed of into the environment via domestic sewage (Rivera-Utrilla et al., 2013; Parra et al., 2016; Fent et al., 2006). Tetracyclines are the second group of antibiotics that are most widely used in the world due to their low cost and broad spectrum of antibacterial activities; these antibiotics are commonly used for the treatment of various infections. Disturbingly though, when TC is ingested, the human body is only able to absorb 60% of the drug (Parra et al., 2016).
Because of the low concentrations of EPs found in aquatic environments, conventional wastewater treatments are unable to efficiently degrade these contaminants. In view of that, alternative advanced treatment techniques, such as electrochemical advanced oxidation processes (EAOP), have been developed with a view to addressing the inefficiencies of conventional treatment processes. EAOPs have been successfully employed for the removal of EPs from water and wastewater matrices (Malpass et al., 2012; Mello et al., 2021; Muñoz-Morales et al., 2019; Dionisio et al., 2020; Ding et al., 2020). In fact, several studies reported in the literature have demonstrated the high removal efficiency of EAOPs when applied for the treatment of different effluents (Monteil et al., 2019; Barrera-Díaz et al., 2014; Sirés et al., 2014); however, the high energy costs involved in the application of EAOPs have tended to limit their use in some cases. Recently, Muñoz-Morales et al. (2018) proposed an efficient alternative strategy to overcome this limitation; where the pollutants are initially concentrated through adsorption with activated carbon and then desorbed using organic solvent such as methanol, obtaining a concentrated solution of the target pollutant in low volume of methanol. This concentrated solution is subjected to electro-oxidation, where higher treatment efficiency is obtained with diminished energy consumption (Muñoz-Morales et al., 2019, 2020).
Since this is a novel strategy for the removal of micropollutants from wastewater, several studies still need to be carried out in order to fully understand the technique to effectively validate or evaluate its efficiency. More recently, Mello et al. (2021) studied the degradation of TC in methanol media where they compared the efficiencies of two commercial anodes: boron-doped diamond reactor (BDD) and dimensionally stable anode (DSA-Cl2), as well as different supporting electrolytes: acid sulfuric and chloride anions. The degradation process was found to be more efficient when the DSA-Cl2 electrode was applied in chloride medium. There are some research studies on the degradation of pollutants in methanol (Muñoz-Morales et al., 2018, 2019, 2020), nonetheless, methanol is a kind of toxic solvent, which is not favorable from an environmental and health perspective. As an alternative to this problem, this article proposes the use of ethanol in these processes. There are published articles that board the use of ethanol as a solvent for desorption of pollutants (Zhou et al., 2015; Reif et al., 2020; Larasati et al., 2020), however, there are no reports of the use of this solvent in pollutant degradation processes, being an innovative topic.
Bearing this in mind, the objective of this study was to analyze the degradation of tetracycline in ethanol/water. Under the technique proposed in this study, DSA-Cl2 was used as anode and NaCl as electrolyte in the electrooxidation of TC. The study analyzed the behavior of ethanol during the degradation process while the formation of radical species was also investigated by electron paramagnetic resonance (EPR).
Section snippets
Chemical products
Tetracycline hydrochloride (C22H24N2O8, 95%) was acquire from Sigma-Aldrich. Ethanol (99.9%) and methanol (99.9%) were both obtained from Exodo. 0.04 mol L−1 sodium chloride (99.9%) - acquired from Synth, was used as supporting electrolyte. 0.1 mol L−1 solutions of HCl (37% - Synth) and NaOH (99% - Merck) were used for pH adjustment. DMPO (5,5-dimethyl-1-pyrroline-N-oxide), acquired from Sigma-Aldrich, was used as trapping agent in the EPR analysis. Deionized water (Millipore Milli-Q system,
Effect of organic solvent
Fig. 1 shows the removal of TC from an initial 100 mg L−1 solution. The degradation experiments were carried out in different solvents (EtOH–H2O and MeOH–H2O mixture - both in the ratio of 85:15%, and aqueous solution) using DSA-Cl2 anode and 0.04 mol L−1 NaCl as supporting electrolyte. The pollutant was quickly removed in all solutions in the first 15 min of electrolysis. The application of current density of 10 mA cm−2 led the same pollutant removal of 95% in H2O and MeOH–H2O solutions,
Conclusions
Based on the results obtained in this study, the following conclusions can be drawn:
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TC can be degraded in ethanol-water mixture using a DSA-Cl2 reactor.
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TC removal in ethanol-water mixture occurred most efficiently at pH = 6 (neutral) and at current density of 10 mA cm−2 achieving 90% of TC removal after 15 min of electrolysis.
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Owing to its lower toxicity, ethanol can be used for pollutants degradation; besides that, the use of ethanol leads to efficient oxidation.
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Through EPR analysis, the
Author contributions
Isabela Fiori: Conceptualization, Methodology, Formal analysis, Investigation, Data curation, Visualization, Writing – original draft. William Santacruz: Investigation, Formal analysis, Writing – review and editing. (Supporting). Dawany Dionísio: Formal analysis, Visualization, Writing – review and editing. (Supporting). Artur J. Motheo: Conceptualization, Methodology, Resources, Supervision, Validation, Project administration, Writing – review and editing. (Lead).
Declaration of competing interest
The authors declare the following financial interests/personal relationships which may be considered as potential competing interests.
Artur de Jesus Motheo reports financial support was provided by State of Sao Paulo Research Foundation. Isabela Fiori reports financial support was provided by Coordination of Higher Education Personnel Improvement. William Santacruz reports financial support was provided by Coordination of Higher Education Personnel Improvement.
Acknowledgments
The authors are grateful to the following Brazilian research funding agencies: Coordination of the Improvement of Higher Education Personnel (CAPES - 2020/88887.480668 and 2020/88887.502308), the National Council for Scientific and Technological Development (CNPq - 160590/2019-1), and the São Paulo Research Foundation (FAPESP - 2017/10118-0) for the financial assistance granted in support of this work. The authors are also grateful to Daniel R. Cardoso, Antonio Roveda and Jennifer Chauca for
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