Simultaneous Determination of Some Selected Hypertension Drugs in Hospital Effluents by Using LCMS

Research Article

Austin J Anal Pharm Chem. 2019; 6(1): 1113.

Simultaneous Determination of Some Selected Hypertension Drugs in Hospital Effluents by Using LCMS

Elhag DE*, Abdallah BS and Suliman SA

¹Institute of Research, UMST University, Khartoum, Sudan

*Corresponding author: Dhia Eldin Elhag, Institute of Research, UMST University, Khartoum, Sudan

Received: February 14, 2019; Accepted: April 19, 2019; Published: April 26, 2019

Abstract

A robust method was developed and validated for the determination of Bisoprolol, Losartan, Amlodipine, Atorvastatin and Candesartan antihypertension drugs in hospital wastewater. The method employs acetonitrile/formic acid as a mobile phase in a gradient mode, flow rate 1ml/min. The column used was ODS Shimpack 4.6*150*5μm and the injected volume was 5μL. Solid phase extraction was used for sample cleaning before analysis. Analysis time was less than seven minutes. The limits of quantitation (LOQ) ranges were 0.001-0.003 and 0.003-0.014 ug/ml, respectively. Acceptable recoveries were achieved for the drug standards. This new method proved to be simple, robust, precise and accurate.

Keywords: LCMS; Method development; Hypertension drugs

Introduction

Pharmaceuticals are emerging as potential pollutants of the environment and have become a considerable source of environmental contamination [1–4]. A number of therapeutic pharmaceuticals are used in large quantities and may be present in effluents at varying concentrations. The health impact of long-term exposure to mixtures of these compounds is unknown. Sources of pharmaceutical pollution of the environment include humans, hospitals, livestock and pharmaceutical industry. They can enter the waterways through their disposal and as a result can become a serious and persisting health hazard to human health, as well as to the life of the flora and fauna. The presence of pharmaceuticals in the environment raised great concern in the recent years regarding their potential impact as they can affect water quality by the increasing discharge of drugs. This issue has prompted numerous monitoring and assessment programs and studies [5–9].

The determination of pharmaceuticals at trace levels in various environmental matrices, especially water, is mainly attributable to the advancement of the sensitivity and accuracy of the new generations of analytical instrumentation. For instance, high performance liquid chromatography (HPLC) coupled to mass spectrometry, is a common technique of choice for various drug residues and pharmaceuticals [2,10–15]. Anti-Hypertensive drugs are pharmaceutical used to help control blood pressure. Untreated high blood pressure can lead to diseases of the heart, arteries, kidney damage, or stroke [16–18]. In this study, we report the development and validation of an HPLCMS method enabling to quantify simultaneously some selected antihypertensive drugs i.e. Bisoprolol, Losartan, Amlodipine, Atorvastatin and Candesartan.

Materials and Methods

Drugs standard Bisoprolol, Losartan, Amlodipine, Atorvastatin and Candesartan were kindly donated by Kingstone Pharmaceuticals, Sudan, Acetonitrile, (Carlo Erba, France), formic acid, acetone 99% triethylamine methanol (99%) sulphoric acid (98%), ethanol (99%) (SDFCL, India). Deionized water, filter paper (Watman 100 and 0.45 micron filter paper. All chemical were analytical or HPLC grade.

Preparation of standard stock solution

Exactly 0.01g from each standard was weighed separately in a beaker (50mL) and 10ml of the diluent was added. The standard was transferred to ultrasonic bath for 5min and then was completed to the mark to obtain a concentration of 200mg/ml. From this standard solution, 0.5ml were pipetted into 10ml volumetric flask and then completed to the mark by the diluent to obtain a final solution of a concentration of 10ug/ml. Further dilutions were made from this solutions for the different validation tests.

Samples pretreatment and clean up

Initially, 500 ml of each sample of wastewater was filtered through Watman filter paper (100) and then through 0.45 micron, then acidified to pH 3.0 by adding sulphuric acid. The sample was passed through C-18 cartridge activated with 5ml of methanol, 5ml methanol/water 50/50 (v/v) and 5ml of water at (pH 3). The cartridge was washed further with 5ml of acidified water (pH 3).The cartridge was eluted with 5ml of triethylamine (5% v/v) in methanol. The eluted solution was evaporated at normal room temperature (200C). Finally, sample volume was completed to 1ml by adding water/acetonitrile 95/5 (v/v).

Mobile phase preparation of mobile phase

Gradient elution mode was used in the analysis. Mobile phase A (1% formic acid) and mobile phase B was acetonitrile. The gradient program is shown in Table 1.