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RESEARCH ARTICLE

Oxidative degradation of ranitidine by UV and ultrasound: identification of transformation products using LC-Q-ToF-MS

Misha T. Elias A , Jisha Chandran B , Usha K. Aravind A and Charuvila T. Aravindakumar https://orcid.org/0000-0002-9157-7539 B C D
+ Author Affiliations
- Author Affiliations

A Advanced Centre of Environmental Studies and Sustainable Development, Mahatma Gandhi University, Kottayam, 686560, Kerala, India.

B Inter University Instrumentation Centre, Mahatma Gandhi University, Kottayam, 686560, Kerala, India.

C School of Environmental Sciences, Mahatma Gandhi University, Kottayam, 686560, Kerala, India.

D Corresponding author. Email: cta@mgu.ac.in

Environmental Chemistry 16(1) 41-54 https://doi.org/10.1071/EN18155
Submitted: 16 July 2018  Accepted: 17 October 2018   Published: 3 December 2018

Environmental context. Ranitidine, a widely prescribed antiulcer drug commonly found in surface waters, has been identified as an emerging contaminant due to its toxicity and the enhanced toxicity displayed by its transformation products. Mechanisms for the formation of ranitidine transformation products and their degradation pathways induced by UV oxidation processes are presented. This work provides insight into treatment processes to remove these toxic chemicals from environmental water bodies.

Abstract. The transformation products (TPs) of pharmaceuticals formed during advanced oxidation processes (AOPs) are of great significance, but there are still gaps in our knowledge regarding the persistence of such compounds in the water matrices, their impact on human health and the applicability of such techniques during water treatment processes. Ranitidine (RAN), a highly prescribed gastrointestinal drug, has been widely detected in various surface waters and experiments, along with its TPs, which show enhanced toxicity. The present study analyses the TPs formed from the degradation of RAN in aqueous solution induced by three AOPs; namely UV-photolysis, UV/peroxodisulfate (PDS) and sonolysis. The degradations followed pseudo first-order kinetics, with removal efficiencies of 99.8, 100 and 98.8 % after 60 min under UV photolysis, UV/PDS, and sonolysis, respectively, with a corresponding decrease in chemical oxygen demand (COD) of 25, 100 and 75 %. Structures of the main TPs were elucidated by using LC-Q-ToF-MS in positive mode, and possible degradation pathways are proposed which mainly involved C-N and C-H bond cleavage, hydroxylation and reduction of nitro groups. Possible mechanisms for the formation of the identified TPs (elucidated by using electrospray ionisation–collisionally induced dissociation) support their structural assignments. Seven out of the 11 TPs presented here (namely TP-1, TP-4, TP-5, TP-6, TP-7, TP-9 and TP-10) were not reported in previous studies of RAN using any other AOPs, while four (m/z 331, 270, 288 and 286) were found to retain the NO2 group, which might contribute to the formation of halonitromethanes (HNMs) during chlorination of drinking water. Interestingly, we identified an additional sonolysis product, TP-3, whose formation can only be rationalised by invoking ozone.

Additional keywords: advanced oxidation processes, ESI-CID, halonitromethanes, pharmaceutical pollution, photodegradation.


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