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Article

Green Stability Indicating Organic Solvent-Free HPLC Determination of Remdesivir in Substances and Pharmaceutical Dosage Forms

by
Adel Ehab Ibrahim
1,
Sami El Deeb
2,3,*,
Emad Mahmoud Abdelhalim
4,
Ahmed Al-Harrasi
3 and
Rania Adel Sayed
5
1
Analytical Chemistry Department, Faculty of Pharmacy, Port-Said University, Port Said 42526, Egypt
2
Institute of Medicinal and Pharmaceutical Chemistry, Technische Universitaet Braunschweig, 38106 Braunschweig, Germany
3
Natural and Medical Sciences Research Center, University of Nizwa, P.O. Box 33, Birkat Al Mauz, Nizwa 616, Oman
4
Chemistry Department, Zagazig University, Zagazig 44519, Egypt
5
Analytical Chemistry Department, Faculty of Pharmacy, Zagazig University, Zagazig 44519, Egypt
*
Author to whom correspondence should be addressed.
Separations 2021, 8(12), 243; https://doi.org/10.3390/separations8120243
Submission received: 25 November 2021 / Revised: 8 December 2021 / Accepted: 10 December 2021 / Published: 12 December 2021

Abstract

:
A green liquid chromatographic method is considered in this work to minimize the environmental impact of waste solvents. One important principle is to replace or eliminate the use of hazardous organic solvents. Organic impurities in any active pharmaceutical ingredient could arise either during the process of its synthesis, or as degradation products developed throughout the shelf-life. Remdesivir (RDS) is an antiviral drug, approved by the US Food and Drug Adminstration (-FDA), to treat SARS-Cov-2 virus during its pandemic crisis. We studied the stability of remdesivir against several degradation pathways using the organic solvent-free liquid chromatographic technique. Separation was performed on RP-C18 stationary phase using mixed-micellar mobile phase composed of a mixture of 0.025 M Brij-35, 0.1 M sodium lauryl sulfate (SLS), and 0.02 M disodium hydrogen phosphate, adjusted to pH 6.0. The mobile phase flow rate was 1 mL min−1, and detection was carried out at a wavelength of 244 nm. We profiled the impurities that originated in mild to drastic degradation conditions. The method was then validated according to International Conference of Harmonization (ICH) guidelines within a linearity range of 5–100 μg mL−1 and applied successfully for the determination of the drug in its marketed dosage form. A brief comparison was established with reported chromatographic methods, including a greenness assessment on two new metrics (GAPI and AGREE). This study is the first to be reported as eco-friendly, solvent-free, and stability indicating LC methodology for RDS determination and impurity profiling.

1. Introduction

In December 2019, COVID-19 was discovered; since then, a pandemic infection has spread all over the world, causing patients pneumonia and acute respiratory distress syndrome that potentially progresses to death [1]. The causative organism was discovered to be SARS-Cov-2 virus, for which scientists have not yet discovered a specified regimen. Since the process of discovery, development and evaluation of any new active pharmaceutical ingredient (API) is tedious and requires a long time for safety and clinical profiling, older, clinically profiled antivirals were extensively tested against the new causative virus. Among these molecules, remdesivir (RDS) emerged as a promising active nucleus against the virus [1,2].
Remdesivir (structure depicted in Figure 1) is an adenosine nucleotide analogue that is activated in vivo into an active viral RNA polymerase inhibitor. During the Ebola virus outbreak (2014–2016), RDS was discovered and developed against Ebola virus. Although RDS by then had reached phase III of its clinical trials, it was over-performed by monoclonal antibodies against Ebola [3]. RDS showed increased intracellular concentration of its active triphosphate metabolite after single-dose administration, as well as inhibition of viral RNA polymerase that led to shortened recovery times and decreased mortality rates [4]. Therefore, RDS was recently approved by the US FDA and Japan for the treatment of severe COVID-19 cases [4], and since then it has been extensively formulated and produced by several countries all over the world.
The process of quality control (QC) of any API in its crude raw powder form, as well as during several steps of its formulation, is crucial, in order to maintain good manufacturing practices (GMP). Pharmaceutical QC laboratories profile APIs for assessing the presence any organic impurities. These organic impurities can originate either during the synthesis process of the API, as degradation molecules during transport, storage, and manufacturing, or even during the product’s shelf-life. An individual API product batch can be tested tens of times from its birth until expiry. This is how millions of analyses are performed daily in research and QC laboratories.
Meanwhile, the ecological impact of analytical methodologies must be controlled in order to decrease their environmental hazards. Ongoing greener in chromatography, reversed phase liquid chromatography (RPLC) is the best choice since it requires significantly fewer organic solvents than other stationary phases [5]. Organic solvents are used by chromatographers in RPLC to promote the analytes’ elution and to improve their peak shape. However, given that each conventional LC system can generate around 0.5 L of organic waste daily [6], other techniques needed to be developed to decrease the dependence on these organic solvents, which are difficult both to produce and to dispose. Among the developed techniques, mixed-micellar mobile phases demonstrated adequate performance at replacing hazardous organic solvents [7,8]. The combination of the non-ionic polyoxyethylene surfactant (Brij-35) and the anionic sodium lauryl sulfate (SLS) surfactant improved the elution power in RP stationary phases without the loss of their separation efficiency [9]. This technique involves much lower cost, toxicity and environmental harm; moreover, it offers unique selectivity and power of solubilization. These advantages encourage economic pharmaceutical corporations to utilize methodologies related to such techniques that avoid the disadvantages of expensive and ecologically harmful solvents in their routine inspections.
A literature review revealed that only a small number of methodologies were validated for the determination of RDS. Most methods were based on HPLC or ultrahigh performance liquid chromatography (UHPLC) coupled with MS/MS detection [10,11,12,13,14,15]. Some detailed data regarding these cited references are discussed and compared for their advantages and disadvantages in the Discussion section. Except for one reported method [13], other methods validated a gradient LC technique. Formic acid, sodium formate and ammonium acetate were the main buffers of the mobile phases. The flow rates of the reported methodologies ranged from 0.4–0.6 mL min−1, with a run time range of 4.0–10.0 min per run. The method described in [11] used anion exchange stationary phase, while the other reported methods used an RP-C18 column as stationary phase. All the reported techniques utilized organic solvents, such as acetonitrile (ACN) and methanol (MeOH), to improve elution and chromatographic efficiencies. No solvent-free HPLC method was reported for the determination of RDS. Moreover, all the reported methods until now quantified the drug in plasma or body tissues using HPLC or UHPLC coupled with an MS/MS detector. Although UHPLC-MS/MS utilizes low amounts of reagents, its high maintenance cost and short column life are worrying issues for low-budget laboratories. Therefore, as expensive tools, they are not readily present in most of QC laboratories [6]. Another electrochemical for the determination of RDS was also reported [16].
The aim of this research article is to validate a simple, conventional and green LC method for the determination of RDS in its pure form, as well as in pharmaceutical product forms. The method is the first to be reported as stability indicating method that can profile existing organic degradation impurities. The method is sustainable since it is solvent free and was assessed for greenness against recent metrics and compared to previously reported analytical methodologies in order to prove its efficiency and desirable ecological safety.

2. Materials and Methods

2.1. Materials

All the reagents used were of analytical grades. The Brij-L23 was purchased from Alfa Aesar GmbH, Tewksbury, MA, USA. The phosphoric acid, SLS, disodium hydrogen phosphate and methanol were purchased from Merck, Darmstadt, Germany. The de-ionized water was freshly produced in-house (using a Millipore water system for purification).
The RDS was kindly supplied by EIPICo., tenth of Ramadan city, Egypt. The pharmaceutical dosage form Remdesivir-Rameda® I.V. infusion (lot. No. 203526, 100 mg RDS per 20 mL vial), and Betacyclodextrin sulfobutyl ether sodium (BCD-SE) were kindly supplied by Rameda, October, Egypt.

2.2. Instrumentation

The study was performed on an Agilent-1200 chromatographic system (Rocklin, CA, USA) equipped with a quaternary pump, an auto-sampler, a PDA detector, and a mobile phase degasser (models G1311A, G1329B, G1315B and G1322A, respectively). A Mettler–Toledo meter, SevenCompact® model S210 (Columbus, MN, USA), was utilized for pH adjustment. A Core-shell RP-C18 column Kinetix® (5 μm, 150 × 4.6 mm) was purchased from Phenomenex, CA, USA.

2.3. Chromatographic Separation Conditions

The mobile phase was prepared by dissolving 0.025 M Brij, 0.1 M SLS and 0.02 M of disodium hydrogen phosphate in 1 L of de-ionized water and the pH was adjusted to 6.0 using dilute phosphoric acid. The mobile phase was filtered, degassed and eluted isocratically on a chromatographic column, at a flow rate of 1 mL min−1 for 9 min during the method validation. The detection wavelength was adjusted to 244 nm.
To enhance the sustainability of the analytical procedure, the mobile phase was recycled in between the chromatographic runs. To maintain the column efficiency and remove all the surfactants that were adsorbed on the stationary phase, the system needed to be purged for fifteen minutes using a regenerating mobile phase composed of water, MeOH (50:50, v/v), at the end of each working day.

2.4. Preparation of Stock Solutions, Standard Solutions and Pharmaceutical Dosage Form

The RDS stock solution was prepared by dissolving 50.0 mg of pure powder in 10 mL of MeOH with sonication for 2 min. The volume was then increased to 50 mL using the mobile phase. The stock solution was stored in a refrigerator (at 2–8 °C) in amber glass bottles and was stable for more than 2 weeks.
The linearity was established by diluting the stock solution with the mobile phase to obtain six standard solutions at (5, 20, 40, 60, 80 and 100 μg mL−1). Quality control (QC) standards were prepared by spiking the RDS stock solution into a placebo solution containing 1 mg mL−1 of (BCD-SE), adjusted to pH 4.0 using phosphoric acid in order to simulate the drug delivery system of Remdesivir-Rameda® I.V. infusion, to obtain four QC standards at (10, 25, 50 and 75 μg mL−1).
The validated method was applied for the determination of RDS in its marketed pharmaceutical dosage form. The assay was performed through the direct dilution of the Remdesivir-Rameda® I.V. infusion using the mobile phase to concentration (50.0 μg mL−1).

2.5. Drug Forced Degradation

In the proposed study, the stress protocol was chosen to effect acid/base hydrolysis, oxidative and thermal degradation to RDS [17]. The RDS was prepared at a concentration of 1 mg mL−1 and was then subjected to degradation according the following protocol. Alkaline hydrolysis was performed in 0.1 N NaOH at (25 °C/0.5 h), (25 °C/3 h) and (45 °C/1 h). Acidic hydrolysis was performed in 0.1 N HCl at 40 °C and 50 °C in a calibrated water bath for 1 h, respectively. Oxidative degradation was carried out in hydrogen peroxide 4.5% at 40 °C and 50 °C for 1 h, respectively. Photolytic degradation was done by exposing the drug solution to Ultra-violet (UV) lamp at 365 nm for 1 day. Finally, after acid/base hydrolysis, the process must be stopped by neutralizing acidic/basic solutions. The oxidative degradation was stopped by adding sodium persulfate powder to remove excess remaining hydrogen peroxide.

3. Results

3.1. Analytical Method Validation

The developed method was validated according to ICH guidelines [18]. The linearity was established using six linearity standards across the specified range. The standards were injected in triplicates and the average corresponding areas under the curve were plotted against their corresponding drug concentrations. Table 1 outlines the retention time and regression equation statistics.
Specificity is the ability of the analytical method to determine the analyte in the presence of interferences. The absence of interferences from any present excipients is demonstrated by the chromatograms obtained from pure RDS and RDS Remdesivir-Rameda® in dosage form (Figure 2). Both RDS peaks were identical and indicated that no interferences from the excipients were found.
The system’s suitability was evaluated using the proposed mobile phase in the absence of organic solvents, which are important for the enhancement of peak shape. The parameters tested included repeatability of retention time, column efficiency in terms of number of theoretical plates and peak symmetry. The results (Table 1) for the higher-concentration linearity standard (80 µg mL−1) established the system’s adequacy for the analysis using the solvent-free mobile phase without a considerable loss of efficiency.
The limits of detection (LOD) and quantification (LOQ) were calculated based on signal-to-noise ratios (Table 1), where descending concentrations of RDS were injected and ratios were considered. The LOD and LOQ were determined using drug concentrations that produced signal-to-noise ratios 3 and 10, respectively.
The accuracy of the developed method was proven by injecting four QC standards in triplicates and calculating the percentage recoveries obtained from the regression equation. Table 2 presents the accuracy results, which proved the close agreement between the expected and true values.
The precision was tested by evaluating the repeatability and intermediate precision. The repeatability of the triplicate injections of linearity standards under the same operating conditions resulted in low relative standard deviation (RSD). The intermediate precision was tested using the four QC standards, which were injected at three different times during the same day (Intra-day) and on three different days (Inter-day). Table 2 presents the intermediate precision, where the standard deviations of the results prove the agreement between the different measurements.

3.2. Stability Indicating Capability of the Proposed Method

In order to specify the stability-indicating capability of any analytical methodology, forced degradation must be performed for the analyte under conditions more drastic than normal or even accelerated conditions [17]. Drug degradation became an essential step for regulatory approval during the development of new API formulas. Although regulatory documents do not specify exact details for degradation studies, stress conditions must be chosen to simulate possible pathways to decompose APIs during manufacture, transport, storage or shelf-life [19].
Alkaline hydrolysis exerted the most drastic effect on the RDS nucleus (Supplementary Material Figure S1), where complete hydrolysis occurred. Even at the mildest alkaline degradation (0.1 N NaOH, 25 °C/0.5 h), RDS degradation was up to nearly 95% (Figure 3). The RDS nucleus withstood the acidic degradation more than the peroxide oxidation, as demonstrated in the Supplementary Material (Figure S1). Photolytic degradation did not produce a significant change on the RDS nucleus. In all cases, none of the formed impurities interfered with the RDS peak (Supplementary Material Figure S1)

3.3. Method Application

The validated method was applied for the assay of RSD in its marketed dosage form (Remdesivir-Rameda®). The IV solution was diluted and injected within the working range of the method in triplicates. The concentrations were calculated using the calibration equation. The results were then compared to those obtained by a reference method obtained from a dosage form formulator EIPICo., tenth of Ramadan city, Egypt. The formulator describes a HPLC method for its determination using mobile phase consisting of 0.1% phosphoric acid in water: methanol (35:65, v/v) eluting at flow rate 1 mL min−1 on a C18-RP column and a detection wavelength of 237 nm. Table 3 presents the obtained results and their evaluation on the student t-test and F-test. The results prove the absence of any significant differences between the reported and validated methods.

3.4. Comparison and Evaluation to Previously Reported Methods

As mentioned in the Introduction section, according to our knowledge, only a small number of chromatographic methods were reported for the determination of RDS, mainly in plasma, which were based mainly on UHPLC coupled with MS/MS detection. UHPLC is an expensive tool that cannot be used economically in routine QC procedures due to its high maintenance cost and short column life-time [20]. Table 4 presents a thorough comparison between the proposed method and five other reported methodologies. The present study is the only one to depend on a conventional LC, which is widely available in most pharmaceutical QC laboratories. All other methodologies are related to UHPLC, of which one reported method presented 2D UHPLC separation [14]. Although UHPLC systems are the most efficient separation tools, utilizing only a small amount of reagents and presenting higher sensitivities, they feature some well-known drawbacks. The low reproducibility they offer, their short column life-time and the high cost of their maintenance discourage their use in economical pharmaceutical facilities for routine daily QC tasks [20]. This study is the only solvent-free tool, in which the compared methodologies mostly use acetonitrile as organic solvent, except one method which uses a methanol-based mobile phase ready kit [14]. ACN features a unique selectivity; however, several reports refer to its high toxicity and environmental hazardousness, added to its expensive production and tedious disposal [21].
The comparison presents an assessment of the reported methods on two recent assessment metrics: the Green Analytical Procedure Index (GAPI) [22] and AGREE [23]. GAPI is a color-coded index that features a figure composed of 15 pentagrams, each representing a step in the analytical procedure. It assesses the analytical method using three colors; red indicates high environmental impact, yellow indicates moderate and green indicates a low hazardous effect. Another recent metric was reported, AGREE [23], which is based on Green Analytical Chemistry (GAC) principles. AGREE features a clock-shaped figure. The perimeter of the clock is divided into 12 sectors, each representing one GAC principle. The same color coding is preserved for both GAPI and AGREE. However, AGREE introduces a numerical evaluation for the assessed method in the core of its graph, ranging from (0.0–1.0). As demonstrated in Table 4, the proposed method has the greenest impact on both GAPI and AGREE for several reasons. Firstly, it is the only reported solvent-free method. Furthermore, this study uses biodegradable mobile phase micellar constituents. Since the previously reported methods were applied in biological tissues, they require extraction steps that range from simple protein precipitation to complex advanced extraction. The only red zones in the GAPI pictogram for the proposed study (also present in other reported methods) correspond to the off-line sampling and positioning of analytical instrumentation in QC laboratories, which is a regulatory requirement in pharmaceutical establishments.
In the assessment of the GAPI and AGREE metrics, GAPI failed to distinguish between four of the five comparison references. These methods were based on UHPLC-MS/MS, using ACN as organic modifier; since they are UHPLC, they utilized and produced less than 10 mL of organic solvents and waste, respectively. On the other hand, AGREE was able to differentiate between these methods based on the consideration of some other factors. AGREE considers the total run time and procedure through the output expressed by the number of runs per working hour. Along with presenting a numerical estimating figure for assessment, AGREE can demonstrate its superiority. However, AGREE features an important drawback in that it does not differentiate between reagents and solvents to the same extent as GAPI, which uses the National Fire Protection Association (NFPA)’s health and safety hazard codes for used reagents and solvents.
The proposed method offers a low ecological impact on both metrics, together with cost-effectiveness, robust design and high predictability. It is therefore recommended to be applied in the quality control quantification of any combination of the tested analytes as a green alternative to any reported methodology.

4. Conclusions

A new, simple, fast and economical method was developed and validated for the determination of remdesivir, one of the currently used medications for the treatment of COVID-19 infections. The developed method can profile the drug in the presence of its stress degradation impurities without interferences. Moreover, the proposed method is green and cost-effective, so it can be applied for the routine quality control analyses of remdesivir with high predictability. The method was found to have the lowest ecological impact, as assessed on both GAPI and AGREE greenness metrics.

Supplementary Materials

The following are available online at https://www.mdpi.com/article/10.3390/separations8120243/s1, Figure S1. Chromatograms showing degradation of RDS in (A) 0.1N NaOH, 25 °C/ 3 h (B) 0.1N HCl, 40 °C/ 1 h, (C) 4.5% hydrogen peroxide, 50 °C/1 h, (D) Photolytic degradation; under the proposed chromatographic conditions

Author Contributions

Conceptualization, A.E.I. and S.E.D.; methodology, E.M.A. and R.A.S.; validation, R.A.S. and A.E.I.; formal analysis, A.E.I. and R.A.S.; investigation, A.E.I. and S.E.D.; resources, A.E.I. and S.E.D.; writing—original draft preparation, A.E.I. and R.A.S.; writing—review and editing, S.E.D. and A.A.-H.; visualization, A.E.I. and E.M.A.; supervision, S.E.D.; project administration, S.E.D. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding to declare.

Conflicts of Interest

The authors declare that there is no conflict of interest. This article does not contain any studies with animals or human volunteers.

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Figure 1. Chemical structure of RDS.
Figure 1. Chemical structure of RDS.
Separations 08 00243 g001
Figure 2. Chromatograms presenting elution of RDS (A) pure form (80 µg mL−1), (B) diluted Remdesivir-Rameda® IV infusion under the proposed chromatographic conditions.
Figure 2. Chromatograms presenting elution of RDS (A) pure form (80 µg mL−1), (B) diluted Remdesivir-Rameda® IV infusion under the proposed chromatographic conditions.
Separations 08 00243 g002
Figure 3. Chromatogram presenting stress degradation results of RDS in 0.1 N NqOH, 25 °C/0.5 h under the proposed chromatographic conditions.
Figure 3. Chromatogram presenting stress degradation results of RDS in 0.1 N NqOH, 25 °C/0.5 h under the proposed chromatographic conditions.
Separations 08 00243 g003
Table 1. Linearity and regression results for determination of RDS using the proposed LC method.
Table 1. Linearity and regression results for determination of RDS using the proposed LC method.
ParameterResult
Retention time (min ± SD)8.5 ± 0.4
Number of theoretical plates9550 m−1
Symmetry factor0.83
Linearity range (μg mL−1)5.0–100.0
Linearity equationY = 64.4 X − 42.5
Correlation coefficient (r)0.999
LOD (S/N ratio = 3)0.5 μg mL−1
LOQ (S/N ratio = 10)2.0 μg mL−1
Table 2. Accuracy and precision results for determination of RDS using the proposed method.
Table 2. Accuracy and precision results for determination of RDS using the proposed method.
Concentration
(µg mL−1)
Accuracy *Inter-Day Precision *Intra-Day Precision *
10.0102.6 ± 0.4101.8 ± 1.4101.3 ± 1.7
25.0100.3 ± 1.7100.2 ± 0.9100.1 ± 0.6
50.097.8 ± 0.698.4 ± 1.398.5 ± 1.1
75.0101.9 ± 2.4
Mean; 100.7 ± 2.0
102.5 ± 1.4101.6 ± 1.9
* Results: %Recovery ± standard deviation, Average of triplicate injections per quality control concentration (n = 3).
Table 3. Application of the proposed method for the determination of RDS in Remdesivir-Rameda®.
Table 3. Application of the proposed method for the determination of RDS in Remdesivir-Rameda®.
Proposed Method *Reference Method *t-TestF-Test
100.8 ± 1.4101.4 ± 0.80.531 (2.776)3.213 (19)
* Results = %Recovery ± relative standard deviation, (n = 3).
Table 4. Comparison of the proposed analytical methods to chosen reported methodologies.
Table 4. Comparison of the proposed analytical methods to chosen reported methodologies.
Proposed MethodReported Method [11] Reported Method [12] Reported Method [14] Reported Method [13] Reported Method [15]
TechniqueHPLC-UVUHPLC-MS/MSHPLC-MS/MSUHPLC-MS/MSUHPLC-MS/MSUHPLC-MS/MS
Matrix; Application Bulk powder; Drug QCMouse tissue, Clinical studiesPlasma; Clinical studiesPlasma; Clinical studiesPlasma; Clinical studiesPlasma; Clinical studies
Linearity range5–100 µg mL−16.0–60260 ng mL−11–5000 ng mL−11–1000 ng mL−11–5000 ng mL−185–5450 ng mL−1
LOD500 ng mL−10.3 ng mL−10.3 ng mL−1Not available0.24 ng mL−1Not available
LOQ2000 ng mL−11.0 ng mL−11.0 ng mL−1Not available0.98 ng mL−14.0 ng mL−1
Organic phaseNilACNACNACNACNMethanol-based
Run time (min)9.06.55.04.010.05.0
ColumnC18 (5 μm, 150 × 4.6 mm)Anion exchange BioBasic AX column (2.1 μm, 50 × 4.6 mm)C18 (2.6 μm, 100 × 2.1 mm)C18 (1.8 μm, 50 × 2.1 mm)C18 (3 μm, 150 × 4.6 mm)Separation on C18 (MassTox® TDM column) after solid phase extraction
Mobile phaseIsocratic;Gradient;Gradient;Gradient;Isocratic;Gradient;
Mixed mode of Brij and SLS.Ammonium acetate buffer and ACNSodium formate buffer and ACN0.05% formic acid and ACN0.05% formic acid: ACN (52:48)MassTox® series A mobile phase
Flow; 1 mL min−1Flow: 0.6 mL min−1Flow; 0.5 mL min−1Flow; 0.4 mL min−1Flow; 0.5 mL min−1Flow; 0.6 mL min−1
GAPI assessment Separations 08 00243 i001 Separations 08 00243 i002 Separations 08 00243 i003 Separations 08 00243 i004 Separations 08 00243 i005 Separations 08 00243 i006
AGREE assessment Separations 08 00243 i007 Separations 08 00243 i008 Separations 08 00243 i009 Separations 08 00243 i010 Separations 08 00243 i011 Separations 08 00243 i012
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MDPI and ACS Style

Ibrahim, A.E.; Deeb, S.E.; Abdelhalim, E.M.; Al-Harrasi, A.; Sayed, R.A. Green Stability Indicating Organic Solvent-Free HPLC Determination of Remdesivir in Substances and Pharmaceutical Dosage Forms. Separations 2021, 8, 243. https://doi.org/10.3390/separations8120243

AMA Style

Ibrahim AE, Deeb SE, Abdelhalim EM, Al-Harrasi A, Sayed RA. Green Stability Indicating Organic Solvent-Free HPLC Determination of Remdesivir in Substances and Pharmaceutical Dosage Forms. Separations. 2021; 8(12):243. https://doi.org/10.3390/separations8120243

Chicago/Turabian Style

Ibrahim, Adel Ehab, Sami El Deeb, Emad Mahmoud Abdelhalim, Ahmed Al-Harrasi, and Rania Adel Sayed. 2021. "Green Stability Indicating Organic Solvent-Free HPLC Determination of Remdesivir in Substances and Pharmaceutical Dosage Forms" Separations 8, no. 12: 243. https://doi.org/10.3390/separations8120243

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