Usha K Aravind

Prof. Dr. Usha K Aravind

School of Environmental Studies, Cochin University of Science and Technology, Kochi 682022, India

Research Focus & Metrics

Academic Career Length

20Years (2007-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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20 April 2023 in Water
Verified
Journal Article
Open access
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MRManoj Rayaroth
Manoj Rayaroth
Grzegorz BoczkajGrzegorz Boczkaj
Grzegorz Boczkaj
Olivier AubryOlivier Aubry
Olivier Aubry
UAUsha K Aravind
Usha K Aravind
CACharuvila T. Aravindakumar
Charuvila T. Aravindakumar
Advanced oxidation processes (AOPs) hold great promise in the removal of organic contaminants. Reactive oxygen species (ROS) produced in AOPs react with target pollutants to initially form several intermediate compounds that finally undergo complete mineralization. Such observations are reported, especially for laboratory-scale experiments performed in pure water. On the other hand, while considering real contaminated wastewater matrices, particularly industrial effluents, there are many co-existing ions. Carbonate ions are one of the major inorganic ions commonly existing in water resources. Hence, these ions have a significant impact on the respective water treatment processes. This review focused on the effect of carbonate ions on the degradation of pollutants in AOPs. In AOPs, carbonate radicals are formed by the scavenging reaction of the respective ions with ROS. The reactivity of these radicals towards the pollutant varies with respect to the structure and functionality. Therefore, depending on the functionalities of the contaminants, these ions show both positive and negative effects. Thus, this review aims to summarize the effects of carbonate species on the degradation of organic contaminants during AOPs and their environmental impacts. The carbonates enhanced the degradation of several emerging organic pollutants, including aniline, bisphenol A, rhodamine B, acid orange 7, naphthalene, and phenol derivatives. Carbonate presence was also revealed to have a positive contribution in cases of drug degradation, including sulfamethoxazole, propranolol, sulfamethazine, salbutamol, trimethoprim, azithromycin, naproxen, oxcarbazepine, and oxytetracycline.

1 December 2015 in Journal of Hazardous Materials
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Journal Article
Closed access
SSSubha Sasi
Subha Sasi
MRManoj Rayaroth
Manoj Rayaroth
DDDineep Devadasan
Dineep Devadasan
UAUsha K Aravind
Usha K Aravind
CACharuvila T. Aravindakumar
Charuvila T. Aravindakumar

4 May 2007 in Journal of Membrane Science
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Journal Article
Closed access
UAUsha K Aravind
Usha K Aravind
JMJissy Mathew
Jissy Mathew
CAC.T. Aravindakumar
C.T. Aravindakumar

1 March 2019 in Journal of Hazardous Materials
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Journal Article
Closed access
MMMary Lidiya Mathew
Mary Lidiya Mathew
AGAkhil Gopalakrishnan
Akhil Gopalakrishnan
CACharuvila T. Aravindakumar
Charuvila T. Aravindakumar
UAUsha K Aravind
Usha K Aravind

15 December 2021 in ACS Omega
Verified
Journal Article
Open access
RJReshmi John
Reshmi John
JMJissy Mathew
Jissy Mathew
AMAnu Mathew
Anu Mathew
CACharuvila T. Aravindakumar
Charuvila T. Aravindakumar
UAUsha K Aravind
Usha K Aravind
Copper is an essential trace element for human biology where its metal dyshomeostasis accounts for an increased level of serum copper, which accelerates protein aggregation. Protein aggregation is a notable feature for many neurodegenerative disorders. Herein, we report an experimental study using two model proteins, bovine serum albumin (BSA) and human serum albumin (HSA), to elucidate the mechanistic pathway by which serum albumins get converted from a fully folded globular protein to a fibril and an amorphous aggregate upon interaction with copper. Steady-state fluorescence, time-resolved fluorescence studies, and Raman spectroscopy were used to monitor the unfolding of serum albumin with increasing copper concentrations. Steady-state fluorescence studies have revealed that the fluorescence quenching of BSA/HSA by Cu(II) has occurred through a static quenching mechanism, and we have evaluated both the quenching constants individually. The binding constants of BSA–Cu(II) and HSA–Cu(II) were found to be 2.42 × 104 and 0.05 × 104 M–1, respectively. Further nanoscale morphological changes of BSA mediated by oligomers to fibril and HSA to amorphous aggregate formation were studied using atomic force microscopy. This aggregation process correlates with the Stern–Volmer plots in the absence of discernible lag phase. Raman spectroscopy results obtained are in good agreement with the increase in antiparallel β-sheet structures formed during the aggregation of BSA in the presence of Cu(II) ions. However, an increase in α-helical fractions is observed for the amorphous aggregate formed from HSA.

20 August 2012 in Langmuir
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Journal Article
Closed access
VDV. J. Disha
V. J. Disha
CACharuvila T. Aravindakumar
Charuvila T. Aravindakumar
UAUsha K Aravind
Usha K Aravind