High-throughput chemometrically assisted flow-injection method for the simultaneous determination of multi-antiretrovirals in water
Introduction
The acquired immune deficiency syndrome (AIDS) caused by the human immunodeficiency virus (HIV) is one of the greatest lethal diseases in the world. It is estimated that causes about 1 million deaths per year worldwide [1,2]. The most widely used treatment, known as highly active antiretroviral therapy, combines at least two nucleoside analogue reverse transcriptase inhibitors, such as lamivudine (3TC), abacavir (ABC) or zidovudine (AZT), with one non-nucleoside reverse transcriptase inhibitor, such as nevirapine (NVP) or efavirenz (EFV), in a fixed dose combination [3]. The synergistic action provided by this therapy has allowed reducing both mortality and morbidity rates among HIV-infected people, improving their life quality.
Antiretroviral drugs are considered emerging contaminants since they were found in the environment and can cause adverse ecological and/or human health effects. However, they are not usually monitored due to the lack of regulations [4]. Although these drugs are generally present at rather low levels (from ng L−1 to μg L−1) in wastewater and surface waters [[5], [6], [7]], the continuous input can increase the concentrations bringing potential negative effects on the environment, e.g., antimicrobial resistance and toxicity to sensitive aquatic organisms. Their simultaneous determination in environmental samples, as well as in pharmaceutical dosage, biological fluids, animal tissue, synthetic mixtures, has been performed by near-infrared spectroscopy [8], high performance liquid chromatography with diode array detection (HPLC-DAD) [9], U-HPLC with tandem mass spectrometry detection (MS/MS) [10] and pH-gradient flow injection analysis (FIA) with DAD [11].
The aforementioned antiretrovirals (3TC, ABC, AZT, NVP and EFV) exhibit acid-base properties that cause UV spectral changes when variations in the pH of the medium are produced. It is known that the pKa of the analytes plays an important role from an analytical point of view. Therefore, prior to the development of a pH-gradient with spectral detection method, an in-depth bibliographic search related to the pKa values of the five herein analyzed drugs was conducted and summarized in Table 1. It is clear that the available information is scarce or incomplete, especially due to the lack of description of the experimental conditions in which they were determined.
Analytical methods used for pKa determinations of several drugs include potentiometry [12,13], capillary electrophoresis (CE) with DAD [14], UV–Vis spectroscopy [15] and FIA-DAD [11], among others. The most commonly used estimator for the pKa is the well-known Henderson-Hasselbalch equation [16], whereas chemometric resolution of spectrophotometric second-order data constitutes an alternative way of calculation. In this sense, MCR-ALS [[17], [18], [19]] has been widely applied to calculate pKa from second-order data gathered by different instrumentations in several research fields, i.e. UV spectroscopy [20,21], FIA-DAD [22,23], CE-DAD [24] and fluorescence spectroscopy [20,25].
In this work, the apparent pKa values of 3TC, ABC, AZT, NVP and EFV were determined by spectrophotometric titrations and chemometric data analysis. Then, based on this physicochemical information, a FIA-DAD method with MCR-ALS modeling for the simultaneous quantitation of these five drugs in aqueous environmental samples was developed.
Section snippets
Reagents and solutions
3TC, ABC, AZT, NVP and EFV were kindly supplied by Laboratorio DOSA S.A (Buenos Aires, Argentina). Potassium chloride (KCl) was purchased from Merck (New York, USA). Hydrochloric acid (37%, HCl), potassium hydroxide (KOH), sodium hydroxide (NaOH), phosphoric acid (85%, H3PO4) and sodium phosphate dibasic (Na2HPO4) were purchased from Anedra (San Fernando, Argentina). All reagents were of analytical grade. HPLC grade methanol (MeOH) was purchased from Biopack (Buenos Aires, Argentina). Ultrapure
General considerations
It is well-known that the pKa strongly depends on the temperature, ionic strength and dielectric constant of the solution [30]. Nevertheless, some works reporting the determination of the pKa values of antiretroviral drugs avoid maintaining these parameters controlled during the experiments (or did not informed them), as can be seen in Table 1. It is worth noting that determinations at constant ionic strength require the preparation of different solutions for each measurement, which is
Conclusions
The spectral behavior of the antiretroviral drugs against pH allowed determining their pKa by spectrophotometric titration and MCR-ALS analysis. All the pKa values were consistent with the literature data and for the case of NVP a second pKa value, which was not previously reported, was established.
Taking into account that the presence of emerging contaminants in highly complex environmental samples is of current concern due to the potential occurrence of adverse effects on humans and animals,
Acknowledgements
The authors are grateful to Laboratorios DOSA S.A for supplying the antiretroviral drugs to conduct this study, Universidad Nacional del Litoral (Projects CAI+D 2016-50120150100110LI and 50020150100063LI), CONICET (Consejo Nacional de Investigaciones Científicas y Técnicas, Project PIP-2015 N° 0111) and ANPCyT (Agencia Nacional de Promoción Científica y Tecnológica, Project PICT 2014-0347) for financial support. LPF and MRA thank CONICET for their fellowship.
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2022, ChemosphereCitation Excerpt :In fact, ABC and EFV were detected in different types of water bodies (wastewater influents and effluents, surface waters, groundwater and even drinking water) at concentrations of 0.5 ng L−1 to 34 μg L−1 (Aminot et al., 2015; Funke et al., 2016; K'oreje et al., 2012; Schoeman et al., 2017; Swanepoel et al., 2015), and in estuary sediments at concentrations ranging between 0.1 and 3.0 μg kg−1 (Aminot et al., 2015; Rimayi et al., 2018). Several analytical methods, such as high performance liquid chromatography with diode array detection (HPLC-DAD) (Paradina Fernández et al., 2020a; Pynnönen and Tuhkanen, 2014), ultra HPLC with tandem mass spectrometry detection (MS/MS) (Mu et al., 2016; Schoeman et al., 2017), pH-gradient flow injection analysis (FIA) with DAD (Checa et al., 2006; Paradina Fernández et al., 2018) and, more recently, molecular fluorescence spectroscopy (Paradina Fernández et al., 2020b), have been used for the quantitation of ARVs in biological and environmental matrices. Since these pharmaceuticals are found at low concentrations in the environment, the analytical methodology should have high sensitivity, which can be achieved not only by analytical instrumentation, but also using chemometric tools, such as experimental design, to optimize and maximize the responses of the target analytes (Paradina Fernández et al., 2020b).
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