Abstract
The present study investigated the kinetics and formation of hydroxylated and chlorinated intermediates during electrochemical oxidation of salicylic acid (SA). A chloride (NaCl) and sulfate (Na2SO4) electrolyte were used, along with two different anode materials, boron doped diamond (BDD) and platinum (Pt). Bulk electrolysis of SA confirmed the formation of both hydroxylated and chlorinated intermediates. In line with the density functional theory (DFT) calculations performed in this study, 2,5- and 2,3-dihydroxybenzoic acid, 3- and 5- chlorosalicylic acid and 3,5-dichlorosalicylic acid were the dominating products. In the presence of a chloride electrolyte, the formation of chlorinated intermediates was the predominant oxidation mechanism on both BDD and Pt anodes. In the absence of a chloride electrolyte, hydroxylated intermediates prevailed on the Pt anode and suggested the formation of sulfonated SA intermediates on the BDD anode. Furthermore, direct oxidation at the anode surface only played a subordinate role. First order kinetic models successfully described the degradation of SA and the formation of the observed intermediates. Rate constants provided by the model showed that chlorination of SA can take place at up to more than 60 times faster rates than hydroxylation. In conclusion, the formation of chlorinated intermediates during electrochemical oxidation of the organic model pollutant SA is confirmed and found to be dominant in chloride containing waters.
Highlights
Mono- and polycyclic aromatic compounds present in wastewaters such as landfill leachate, pose a special challenge when it comes to their removal from the water matrix
Studies have shown that advanced oxidation processes (AOP) in general [4], and thereof electrochemical oxidation (EO) [5] are effective treatment processes for the removal of persistent organic
Investigation of electrochemical oxygen transfer reaction (EOTR) and mediated oxidation (MEO) for salicylic acid (SA) was done by bulk electrolysis
Summary
Mono- and polycyclic aromatic compounds present in wastewaters such as landfill leachate, pose a special challenge when it comes to their removal from the water matrix. Greater parts of them are non-biodegradable, persist in the aquatic environment and demand a dedicated treatment step for their removal. Such persistent organic pollutants can be produced intentionally, such as pesticides, or are unintentionally produced during water disinfection [1]. They may enter the human body through the food chain via bioaccumulation [2]. Studies have shown that advanced oxidation processes (AOP) in general [4], and thereof electrochemical oxidation (EO) [5] are effective treatment processes for the removal of persistent organic
Talk to us
Join us for a 30 min session where you can share your feedback and ask us any queries you have
Disclaimer: All third-party content on this website/platform is and will remain the property of their respective owners and is provided on "as is" basis without any warranties, express or implied. Use of third-party content does not indicate any affiliation, sponsorship with or endorsement by them. Any references to third-party content is to identify the corresponding services and shall be considered fair use under The CopyrightLaw.