Abstract

The accurate assessment of racemic pharmaceuticals requires enantioselective analytical methods. This study presents the development and validation of an enantioselective liquid chromatography with a fluorescence detection method for the concomitant quantification of the enantiomers of tramadol and their metabolites, N-desmethyltramadol and O-desmethyltramadol, in wastewater samples. Optimized conditions were achieved using a Lux Cellulose-4 column 150 × 4.6 mm, 3 µm isocratic elution, and 0.1% diethylamine in hexane and ethanol (96:4, v/v) at 0.7 mL min−1. The samples were extracted using 150 mg Oasis® mixed-mode cation exchange (MCX) cartridges. The method was validated using a synthetic effluent of a laboratory-scale aerobic granular sludge sequencing batch reactor. The method demonstrated to be selective, accurate, and linear (r2 > 0.99) over the range of 56 ng L−1 to 392 ng L−1. The detection and the quantification limits of each enantiomer were 8 ng L−1 and 28 ng L−1 for tramadol and N-desmethyltramadol, and 20 ng L−1 and 56 ng L−1 for O-desmethyltramadol. The feasibility of the method was demonstrated in a screening study in influent and effluent samples from a wastewater treatment plant. The results demonstrated the occurrence of tramadol enantiomers up to 325.1 ng L−1 and 357.9 ng L−1, in the effluent and influent samples, respectively. Both metabolites were detected in influents and effluents.

Highlights

  • Pharmaceutical compounds are an important group of emergent environmental pollutants due to their high consumption and continuous discharge

  • In a tentative attempt to obtain the best result of chemo and enantioseparation of the enantiomers of tramadol and its metabolites (O-DT and N-DT), chiral stationary phases (CSP) based on macrocyclic glycopeptides antibiotics and polysaccharide derivates were evaluated in normal, polar, and reversed elution modes

  • The separation of the enantiomers of tramadol was reported in Chirobiotic V CSP [40]

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Summary

Introduction

Pharmaceutical compounds are an important group of emergent environmental pollutants due to their high consumption and continuous discharge. These pollutants can enter the environment through various routes, including the direct discharge of sewage from health institutions, industries, agriculture, aquaculture, and households [1,2]. Many pharmaceuticals are chiral and are found in environmental matrices as single enantiomers or as enantiomeric mixtures [5]. These aspects produce additional environmental problems due to the potential diverse behavior of the enantiomers concerning their toxicological and ecotoxicological properties [4]

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