Chiral separation of propranolol by electrokinetic chromatography using nanodiamonds and human serum albumin as a pseudo‐stationary phase in river water

Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R‐ and S‐propranolol were determined in river samples by electrokinetic chromatography (EKC) using nanodiamonds (NDs) and human serum albumin (HSA) as a pseudo‐stationary phase in order to achieve enantios...

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Published inChirality (New York, N.Y.) Vol. 36; no. 2; pp. e23640 - n/a
Main Authors Lanaro, Verónica M., Sombra, Lorena L., Altamirano, Jorgelina C., Almeida, César A., Stege, Patricia W.
Format Journal Article
LanguageEnglish
Published United States Wiley Subscription Services, Inc 01.02.2024
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Abstract Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R‐ and S‐propranolol were determined in river samples by electrokinetic chromatography (EKC) using nanodiamonds (NDs) and human serum albumin (HSA) as a pseudo‐stationary phase in order to achieve enantioseparation. Previously, river samples were preconcentrated using a column filled with Amberlite® IR‐120 and Dowex® 50WX8 resins. The setting up of influential factors such as temperature, voltage, pH, and HSA and NDs concentration is accurately described along this manuscript. A multivariate study and optimization was carried out to obtain the enantioseparation of propranolol (Rs = 2.91), which was reached under the following experimental conditions: voltage of 16 kV, temperature of 16°C, phosphate buffer pH 9.5, NDs of 0.20%, and HSA of 15 μmol l−1. The recoveries of analytes under optimal conditions were higher than 98%. The limits of detection were 0.85 μg l−1 for R‐ and S‐propranolol. The method was applied to real samples, and the obtained results in three different water sources studied were 1.02, 0.59, and 0.30 μg l−1 for the R‐enantiomer and 0.99, 0.54, and 0.28 μg l−1 for the S‐enantiomer. The accuracy of the proposed methodology (including bias and precision) has allowed us to propose it as a successful tool for the control of water quality. Scheme of the complete proposed procedure for the separation of the two enantiomers of propranolol, using nanodiamonds and albumin, by capillary electrophoresis.
AbstractList Abstract Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R ‐ and S ‐propranolol were determined in river samples by electrokinetic chromatography (EKC) using nanodiamonds (NDs) and human serum albumin (HSA) as a pseudo‐stationary phase in order to achieve enantioseparation. Previously, river samples were preconcentrated using a column filled with Amberlite® IR‐120 and Dowex® 50WX8 resins. The setting up of influential factors such as temperature, voltage, pH, and HSA and NDs concentration is accurately described along this manuscript. A multivariate study and optimization was carried out to obtain the enantioseparation of propranolol (Rs = 2.91), which was reached under the following experimental conditions: voltage of 16 kV, temperature of 16°C, phosphate buffer pH 9.5, NDs of 0.20%, and HSA of 15 μmol l −1 . The recoveries of analytes under optimal conditions were higher than 98%. The limits of detection were 0.85 μg l −1 for R ‐ and S ‐propranolol. The method was applied to real samples, and the obtained results in three different water sources studied were 1.02, 0.59, and 0.30 μg l −1 for the R‐ enantiomer and 0.99, 0.54, and 0.28 μg l −1 for the S‐ enantiomer. The accuracy of the proposed methodology (including bias and precision) has allowed us to propose it as a successful tool for the control of water quality.
Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R- and S-propranolol were determined in river samples by electrokinetic chromatography (EKC) using nanodiamonds (NDs) and human serum albumin (HSA) as a pseudo-stationary phase in order to achieve enantioseparation. Previously, river samples were preconcentrated using a column filled with Amberlite® IR-120 and Dowex® 50WX8 resins. The setting up of influential factors such as temperature, voltage, pH, and HSA and NDs concentration is accurately described along this manuscript. A multivariate study and optimization was carried out to obtain the enantioseparation of propranolol (Rs = 2.91), which was reached under the following experimental conditions: voltage of 16 kV, temperature of 16°C, phosphate buffer pH 9.5, NDs of 0.20%, and HSA of 15 μmol l-1 . The recoveries of analytes under optimal conditions were higher than 98%. The limits of detection were 0.85 μg l-1 for R- and S-propranolol. The method was applied to real samples, and the obtained results in three different water sources studied were 1.02, 0.59, and 0.30 μg l-1 for the R-enantiomer and 0.99, 0.54, and 0.28 μg l-1 for the S-enantiomer. The accuracy of the proposed methodology (including bias and precision) has allowed us to propose it as a successful tool for the control of water quality.
Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R- and S-propranolol were determined in river samples by electrokinetic chromatography (EKC) using nanodiamonds (NDs) and human serum albumin (HSA) as a pseudo-stationary phase in order to achieve enantioseparation. Previously, river samples were preconcentrated using a column filled with Amberlite® IR-120 and Dowex® 50WX8 resins. The setting up of influential factors such as temperature, voltage, pH, and HSA and NDs concentration is accurately described along this manuscript. A multivariate study and optimization was carried out to obtain the enantioseparation of propranolol (Rs = 2.91), which was reached under the following experimental conditions: voltage of 16 kV, temperature of 16°C, phosphate buffer pH 9.5, NDs of 0.20%, and HSA of 15 μmol l . The recoveries of analytes under optimal conditions were higher than 98%. The limits of detection were 0.85 μg l for R- and S-propranolol. The method was applied to real samples, and the obtained results in three different water sources studied were 1.02, 0.59, and 0.30 μg l for the R-enantiomer and 0.99, 0.54, and 0.28 μg l for the S-enantiomer. The accuracy of the proposed methodology (including bias and precision) has allowed us to propose it as a successful tool for the control of water quality.
Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R‐ and S‐propranolol were determined in river samples by electrokinetic chromatography (EKC) using nanodiamonds (NDs) and human serum albumin (HSA) as a pseudo‐stationary phase in order to achieve enantioseparation. Previously, river samples were preconcentrated using a column filled with Amberlite® IR‐120 and Dowex® 50WX8 resins. The setting up of influential factors such as temperature, voltage, pH, and HSA and NDs concentration is accurately described along this manuscript. A multivariate study and optimization was carried out to obtain the enantioseparation of propranolol (Rs = 2.91), which was reached under the following experimental conditions: voltage of 16 kV, temperature of 16°C, phosphate buffer pH 9.5, NDs of 0.20%, and HSA of 15 μmol l−1. The recoveries of analytes under optimal conditions were higher than 98%. The limits of detection were 0.85 μg l−1 for R‐ and S‐propranolol. The method was applied to real samples, and the obtained results in three different water sources studied were 1.02, 0.59, and 0.30 μg l−1 for the R‐enantiomer and 0.99, 0.54, and 0.28 μg l−1 for the S‐enantiomer. The accuracy of the proposed methodology (including bias and precision) has allowed us to propose it as a successful tool for the control of water quality. Scheme of the complete proposed procedure for the separation of the two enantiomers of propranolol, using nanodiamonds and albumin, by capillary electrophoresis.
Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R‐ and S‐propranolol were determined in river samples by electrokinetic chromatography (EKC) using nanodiamonds (NDs) and human serum albumin (HSA) as a pseudo‐stationary phase in order to achieve enantioseparation. Previously, river samples were preconcentrated using a column filled with Amberlite® IR‐120 and Dowex® 50WX8 resins. The setting up of influential factors such as temperature, voltage, pH, and HSA and NDs concentration is accurately described along this manuscript. A multivariate study and optimization was carried out to obtain the enantioseparation of propranolol (Rs = 2.91), which was reached under the following experimental conditions: voltage of 16 kV, temperature of 16°C, phosphate buffer pH 9.5, NDs of 0.20%, and HSA of 15 μmol l−1. The recoveries of analytes under optimal conditions were higher than 98%. The limits of detection were 0.85 μg l−1 for R‐ and S‐propranolol. The method was applied to real samples, and the obtained results in three different water sources studied were 1.02, 0.59, and 0.30 μg l−1 for the R‐enantiomer and 0.99, 0.54, and 0.28 μg l−1 for the S‐enantiomer. The accuracy of the proposed methodology (including bias and precision) has allowed us to propose it as a successful tool for the control of water quality.
Author Lanaro, Verónica M.
Stege, Patricia W.
Almeida, César A.
Altamirano, Jorgelina C.
Sombra, Lorena L.
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Issue 2
Keywords enantioseparation
electrokinetic chromatography
human serum albumin
nanodiamonds
propranolol
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Snippet Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R‐ and S‐propranolol were determined in river samples by...
Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R- and S-propranolol were determined in river samples by...
Abstract Propranolol is currently considered as an emerging contaminant in water bodies. In this study, R ‐ and S ‐propranolol were determined in river samples...
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wiley
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StartPage e23640
SubjectTerms Amberlite (trademark)
Chromatography
Chromatography, Micellar Electrokinetic Capillary - methods
Contaminants
Diamonds
Electric potential
electrokinetic chromatography
Electrokinetics
Enantiomers
enantioseparation
Human serum albumin
Humans
Nanodiamonds
Nanostructure
Propranolol
Resins
Rivers
Serum albumin
Serum Albumin, Human
Stationary phase
Stereoisomerism
Voltage
Water pollution
Water quality
Water quality control
Water sampling
Title Chiral separation of propranolol by electrokinetic chromatography using nanodiamonds and human serum albumin as a pseudo‐stationary phase in river water
URI https://onlinelibrary.wiley.com/doi/abs/10.1002%2Fchir.23640
https://www.ncbi.nlm.nih.gov/pubmed/38384157
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https://search.proquest.com/docview/2930476943
Volume 36
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