Open Access Article
Alaa Ahmed Mostafa
*a,
Soad S. Abd El-Hay
b,
Youstina Mekhail Metias
b,
Mohamed Adel Said
a and
Michael Gamal Fawzy
a
aPharmaceutical Chemistry Department, Faculty of Pharmacy, Egyptian Russian University, Badr City, Cairo 11829, Egypt. E-mail: alaaazzam30@gmail.com
bPharmaceutical Analytical Chemistry Department, Faculty of Pharmacy, Zagazig University, Zagazig 44519, Egypt
First published on 18th February 2026
The safety of pharmaceutical products is critically influenced by the presence of impurities and degradation products. Aniline (ANN) is a very toxic degradation product of atorvastatin (ATN), which can cause life-threatening diseases such as methemoglobinemia. For the first time, a comprehensive artificial intelligence study using molecular docking was applied to assess the ANN-induced methemoglobinemia by simulating different binding energies in different pockets of cytochrome P450 (CYP 1A2), revealing the most suitable position leading to toxicity. Moreover, environmental concerns have become increasingly important due to the toxic effects of the excessive use of organic solvents in chromatographic separation systems. Accordingly, greener surfactant systems comprising sodium dodecyl sulfate (SDS) and polyoxyethylene-23-lauryl ether (Brij-35) were employed as safer alternatives were used for the quantitation of ANN in the presence of salicylic acid as an aspirin impurity alongside four widely used cardiovascular drugs of aspirin (APN), atenolol (AEN), atorvastatin calcium (ATN), and losartan potassium (LSN) in pure form and pharmaceuticals. The method validation was done according to the International Conference for Harmonisation (ICH) guidelines with linearity ranges of (10–200), (5–140), (5–100), (5–130), (0.5–40), and (0.5–30) µg mL−1 for APN, AEN, ATN, LSN, SAA, and ANN, respectively, and the results obtained were highly accurate. The greenness of the proposed method was ascertained using the green analytical procedure index: score (0.80), blue applicability grade index: score (0.85), and the Analytical GREEnness calculator. A statistical comparison between the results of our study and the reported method showed no significant difference in precision or accuracy.
Managing patients with both hypertension and hypertriglyceridemia often requires a combination of lifestyle modifications and pharmacological interventions.6 Lifestyle changes can include regular physical activity, a diet rich in potassium and low in sodium, and moderate or no alcohol consumption.7
Nearly 95% of hypertension cases that are complicated with hypertriglyceridemia require pharmacological treatment, often involving a combination of drugs with diverse mechanisms of action.2 To improve treatment adherence in these complex cases, fixed-dose combinations of two drugs in a single tablet can be beneficial.3
Atorvastatin calcium (ATN) (Fig. 1A)4,5 works by competitively inhibiting 3-hydroxy-3-methylglutaryl-coenzyme A reductase,6 thereby impeding mevalonate synthesis and subsequently reducing hepatic cholesterol production. This reduction in cholesterol levels triggers an increase in LDL receptor expression in liver cells, leading to enhanced LDL uptake from the bloodstream.7
![]() | ||
| Fig. 1 Chemical structures of (A) atorvastatin calcium, (B) aspirin, (C) losartan potassium, (D) atenolol, (E) salicylic acid, and (F) aniline. | ||
Aspirin (APN) (Fig. 1B)4,5 is an anti-inflammatory drug that inhibits the synthesis of prostaglandins through the deactivation of the cyclooxygenase enzyme pathway.8 APN was utilized in this combination to increase pain tolerance and maintain optimum blood flow.9
Losartan potassium (LSN) (Fig. 1C)4,5 is a selective and competitive blocker of angiotensin receptors, enabling a compensatory elevation of renin and angiotensin I levels.10 LSN effectively lowers blood pressure, reducing the risk of stroke and heart disease. LSN may also improve kidney function in patients with diabetes or other kidney issues.11
Atenolol (AEN) (Fig. 1D)4,5 is a selective inhibitor of β1 adrenergic receptors in vascular smooth muscles and the heart. This selective binding blocks the positive inotropic and chronotropic actions,12 allowing the heart to maintain a regular rhythm with minimum side effects.13 A quaternary combination of ATN, APN, LSN, and AEN, a combination with established medicinal value,14 along with appropriate lifestyle changes, can effectively treat complex cardiovascular conditions.15 These drugs offer different complementary non-interfering mechanisms of action with additional pain-relieving and anti-inflammatory effects. In addition, their minimal adverse effects ensure optimum management of even the most complicated conditions.
Salicylic acid (SAA)5 is a known major APN impurity listed in BP14 with a limit of 0.02% and aniline (ANN)5 is an approved ATN degradation product with a related structure,16 which were studied due to their potential toxicities (Fig. 1E and F). ANN can cause methemoglobinemia by inducing oxidation of the iron center in haemoglobin, leading to several blood complications.17 ANN toxicity was confirmed by simulation of its binding to CYP1A2.18
Micellar liquid chromatography (MLC) is a type of reversed-phase liquid chromatography (RPLC) that employs a mobile phase consisting of an aqueous surfactant solution at concentrations exceeding its CMC. It is a good separation technique that uses environmentally safe and eco-friendly reagents to meet the standards of green chemistry.19 The versatility of the technique stems from the diverse spectrum of interactions that exist between the aqueous phase, stationary phase, eluted solutes, and micelles. The stationary phase in MLC is altered by the adsorption of surfactant monomers, creating an open micelle-like structure. Thus, the silanophilic interactions are diminished. When non-ionic surfactants are used, the polarity of the stationary phase is modified. Ionic surfactants, on the other hand, cause a net positive or negative charge at the surface of the stationary phase, with significant outcomes.20 Sodium dodecyl sulfate (SDS), an anionic surfactant, is widely used in MLC to separate positively charged chemicals by altering the stationary phase. A non-ionic biodegradable surfactant, Brij-35(polyoxyethylene-(23)-dodecyl ether), has also been recently employed. It lowers the polarity of the stationary phase, which decreases the retention of moderately polar compounds and enhances their separation without requiring excessive amounts of organic solvents.21 Therefore, our study employed MLC with Brij-35 and SDS combination to achieve rapid separation of the quaternary combination therapy without the need for highly hazardous organic modifiers.
Chromatographic methodologies were used for the estimation of cardiovascular drugs in their pharmaceutical formulations.22–26 As the safety of pharmaceutical products is critically influenced by the presence of impurities, degradation products like ANN, which is considered a toxic degradation product of ATN, can cause life-threatening diseases like methemoglobinemia. So, a comprehensive artificial intelligence study using both molecular docking and ADMET profiles was applied to assess the ANN-induced methemoglobinemia by simulating different binding energies in different pockets of cytochrome P450 (CYP1A2), revealing the most favourable position leading to toxicity. The safety of pharmaceutical products is critically influenced by the presence of impurities and degradation products.27
Artificial intelligence (AI) integrated into software tools plays a supportive yet powerful role in molecular docking by predicting the mechanism of binding between ANN and CYP, on which induction to CYP was applied and complementary ADME (absorption, distribution, metabolism, and excretion) were conducted to confirm toxicity. In our work, MOE and ADME analyses are AI-assisted, meaning that AI algorithms help improve accuracy and efficiency but do not fully replace human control or scientific interpretation.28,29 AI aids in predicting ligand–receptor binding affinities, analyzing large datasets for pharmacokinetic properties, and optimizing docking simulations. This assistance makes virtual screening faster, more precise, and cost-effective, while expert validation ensures reliability and scientific soundness in drug discovery.30,31
Despite the widespread use of ATN and its known degradation to ANN, there are no comprehensive studies combining in silico toxicity simulation with green analytical quantification of ANN and related impurity in multicomponent cardiovascular drug formulations. Furthermore, the toxicological behaviour of ANN at the molecular level, particularly its interaction with CYP1A2, has not been thoroughly investigated using artificial intelligence-driven approaches. In addition, most previously reported HPLC methods rely on large volumes of organic solvents and do not address the environmental impact or the simultaneous detection of impurities such as ANN and SAA.
Therefore, the proposed method was specifically designed for the simultaneous determination of the studied compounds in the presence of their related impurities and degradation products, differing in scope, analytical matrix, and objectives from previously published methods. Building on this framework, the innovative aspect of this study was to address existing gaps by integrating molecular docking and ADMET analyses to provide predictive insights into aniline-induced toxicity, alongside the development and validation of an eco-friendly micellar HPLC method for the simultaneous determination of ANN, SAA, and four commonly prescribed cardiovascular drugs in bulk materials and pharmaceutical dosage forms. The combined experimental–computational approach represents a key advantage, as it enables efficient toxicity screening, reduces reliance on extensive in vivo testing, and offers a green, cost-effective, and robust analytical solution suitable for routine quality control. This integrated strategy supports informed decision-making when selecting analytical methodologies based on regulatory, environmental, and practical considerations. As a limitation, the toxicity assessment relies on in silico prediction models, which serve as supportive, preliminary risk-assessment tools and do not replace definitive biological or clinical toxicity confirmation. Consequently, the computational findings should be interpreted as complementary to, rather than a substitute for, experimental toxicological evaluation.
A Benchtop pH meter PB3001 (Trans-instruments, India) for precise pH measurements of the mobile phase and sonicator (model DC-80H) were also utilized in this study.
The following available tablets from the Egyptian markets were used for preparing various laboratory ratios: Ator® (10 mg ATN/tablet) with BN 2404319 manufactured by EIPICO, Ezacard® (75 mg APN/tablet) with BN AT240307 produced by multiapex Pharma, Amosar® (50 mg LSN/tablet) with BN 230790 manufactured by AMOUN, and Atelol® (50 mg AEN/tablet) with BN 230450 manufactured by Pharco Pharmaceuticals.
:
1, v/v) for 15 minutes to eliminate the adsorbed surfactants from the stationary phase.
:
75
:
50
:
50 ratio of ATN, APN, LSN, and AEN, respectively, which constitute a medicinally recommended pharmaceutical dosage form. SAA and ANN impurities were also included in the prepared mixtures. SAA impurity was added according to the BP threshold, while the ANN impurity was added based on a calculated ratio relative to its corresponding drug, ATN. The final volume of each prepared mixture was adjusted to 10 mL with a mobile phase.
CYP1A2 is particularly notable for its role in activating procarcinogen substances that become carcinogenic after being metabolized by the enzyme. Its activity can be influenced by genetic factors, lifestyle factors like smoking, and exposure to certain chemicals such as ANN.17
The main compound under investigation (ANN) was installed in MOE in a 3-dimensional model view and its integrity was checked. Energy minimization was applied to ANN and charges were carefully monitored, based on the 2-dimensional depiction. The calculation of charges was automated by MOE. Finally, the ANN was stored as an MDB file to be used in the docking process and calculations.
:
75
:
50
:
50 ratio of these drugs with various aliquots of SAA (as an APN impurity) and ANN (as an ATN degradation product) were prepared. The developed chromatographic condition was applied to analyze the prepared mixtures.To achieve better chromatographic separation of the analytes on the selected column of C18, the trials were applied, testing several parameters, including: first, analysis of the combined mixture at various wavelengths (230, 250, and 285 nm) for the optimal wavelength for the simultaneous detection of all components in different concentration ratios. Second, the mobile phase composition, including micellar eluents of SDS (an anionic surfactant) in the presence of Brij-35 (a non-ionic surfactant) at different ratios, with the possibility to add an organic modifier, was tested.
After adjusting the mobile phase composition and ratio, it was necessary to determine the suitable pH value of the chosen mobile phase and a reasonable flow rate of its isocratic elution. In addition, the tested pH values (3–7) were prepared using 0.05 M phosphate buffer (NaH2PO4) in HPLC water, adjusted with phosphoric acid or NaOH. Finally, a range of flow rates from 0.75 to 1.5 mL min−1 was also investigated thoroughly to achieve a balance between a suitable total run time and good chromatographic separation.
| LOD = 3.3 × SD/S |
| LOQ = 10 × SD/S |
:
50
:
10
:
50) in the presence of different concentrations of SAA and ANN impurities (0.5, 5, 10, 20, and 30 µg mL−1) were evaluated to investigate the selectivity of the proposed method.MOE 2022 was used for molecular docking simulation to comprehend the unique recognition properties of ANN with CYP1A2. To determine the binding characteristics and identify the connections between the ANN's structural properties and affinity profile at the biggest pocket of the protein crystal structure, docking studies were conducted.
1. Green analytical procedure index (GAPI)36 is a green assessment tool that describes 12 green metrics in the shape of 15 geometric parts. GAPI was utilized to establish a thorough green evaluation of the micellar HPLC method, including all in-process steps from the sample, SDS, and Brij-35 preparations to waste disposal. The environmental impact of the employed device, including mobile phase consumption and potential harm, was also studied. According to the color-coding system set by the software provider, each color code indicates a different effect on the environment as follows: green for low, yellow for medium, and red for high impact.
2. Blue applicability grade index (BAGI),37 this green assessment tool consists of various geometrical shapes that assess 10 concepts of greenness. Among the assessed concepts is the quantitative and confirmatory nature of the analysis, the sample throughput of 5–10 samples per hour, and the use of simple, eco-friendly, highly recyclable reagents. Each of these concepts, along with other parameters, is assigned a score on a scale of 2.5 to 10 and a different blue color brightness.
3. Analytical GREEnness calculator (AGREE)38 is an updated system designed to assess the degree of greenness of any analytical methods. It depends mainly on a 10-section scale, and each takes a different or similar color based on its greenness level, calculated according to the basic principles of green chemistry. Assigning a score of 0 to 1 to each section with apparent colors is the main core of AGREE-prep. To encourage more environmentally friendly and secure practices, the calculator primarily evaluates different parameters, including the amount of reagent toxicity, generated waste, energy requirements, number of processes, miniaturization, and automation.
Also, it was found that micellar eluents of SDS in the presence of Brij-35 showed greater elution strength due to their capability of eluting all mixture components completely. However, given the numerous advantages of micellar eluent systems, such as their high elution strength, safe disposability, and favorable ecological profile, the use of a small proportion of a green organic modifier was a necessity for the developed method. The pure micellar mobile phase exhibited unpredictable retention time with significant tailing for some analytes, and it also affected column efficiency. Hence, the introduction of 1-butanol to the eluent system in a lower concentration (10%) as a greener organic modifier, rather than acetonitrile or methanol, was sufficient for significant enhancement of the chromatographic performance within a reasonable runtime.
Several trials employing SDS and Brij-35 at different concentrations of each while maintaining the other at a constant concentration were also conducted, and their effects on the retention times and resolutions of all analytes were monitored, as depicted in Fig. 2 and 3, respectively. For SDS, the concentrations lower than 0.15 M resulted in the peak tailing of certain drugs and affected the retention time greatly as shown in Fig. 2A, where the overlapped and least resolved peaks of APN and LSN were observed upon using 0.13 and 0.14 M of SDS as shown in Fig. 2B. Also, various concentrations of Brij-35 were studied to evaluate the most appropriate concentration. Concentrations below 0.05 M exhibited shorter retention times (Fig. 3A), whereas higher concentrations prolonged the retention times of certain analytes, such as AEN. In addition, Brij-35 concentration had a great impact on peak resolution and symmetry (Fig. 3B). Accordingly, the mobile phase composition was adjusted to 90% (0.15 M SDS and 0.05 M Brij-35) and 10% 1-butanol after extensive optimization of both the 1-butanol: micellar system ratio and the concentrations of SDS and Brij-35.
![]() | ||
| Fig. 2 The impact of the SDS concentrations on the (A) retention time and (B) resolution of the studied mixture with a constant Brij-35 concentration. | ||
![]() | ||
| Fig. 3 The impact of the Brij-35 concentrations on the (A) retention time and (B) resolution of the studied mixture with a constant SDS concentration. | ||
Among the tested pH values (3–7), pH 5 was the most suitable buffer for separating the studied mixture of six substances with different pKa values. The acidic analytes, SAA and APN, at pH 5 are partially ionized while still maintaining sufficient hydrophobicity, resulting in improved retention and well-defined peak shapes. At the same time, the basic drugs, ANN, AEN, and LSN, remain adequately protonated, reducing excessive interaction, minimizing peak tailing and enhancing symmetry. Consequently, this intermediate pH 5 offers the most harmonized ionization profile for both acidic and basic components. It yields superior chromatographic performance with optimal resolution and consistent retention behavior for all investigated drugs across the mixture compared to highly acidic or basic pH values.
During flow rate investigation, it was found that lower flow rates prolonged the separation process, affecting peak symmetry, while flow rates above 1 mL min−1 resulted in peak interference, especially between SAA and ANN, in addition to an undesirable increase in column pressure. Therefore, the suitable flow rate of 1.0 mL min−1 was chosen as it successfully exhibited the necessary separation quality in an efficient timeframe within 8.5 minutes without placing excessive strain on the column pressure.
Finally, Fig. 4 was obtained utilizing the chromatographic conditions described in section (2.4), which includes: isocratic flow system with a ratio of 90% (0.15 M SDS and 0.05 M Brij-35) aqueous solution adjusted to pH 5.0 with 0.05 M sodium dihydrogen phosphate buffer: 10% 1-butanol was found to be the optimal for the mixture separation on a Kinetex C18 column maintained at 30 °C.
![]() | ||
| Fig. 4 Micellar-HPLC chromatogram of SAA (10 µg mL−1), ANN (10 µg mL−1), ATN (10 µg mL−1), ARN (75 µg mL−1), LSN (50 µg mL−1), and AEN (50 µg mL−1) in their pure forms. | ||
Setting the optimized chromatographic conditions was followed by comparison with the scientific literature, which revealed that the proposed method was specifically designed for the simultaneous determination of the studied compounds in the presence of their related impurities/degradation products and that it differs in scope, matrix, and analytical objectives from previously published methods. The relevant literature revealed the novelty, improved selectivity, greener solvent usage, and enhanced analytical performance of the proposed method compared to the reported approach. In addition, the present study incorporates computational toxicity assessment tools, including molecular docking and ADMET prediction models, to provide artificial intelligence–assisted, predictive insight into aniline-induced toxicity. This AI-supported approach complements the experimental chromatographic work by enabling preliminary toxicity screening and informed risk evaluation, which is not addressed in conventional chromatographic methods reported in the literature. The integration of green analytical chemistry with AI-based computational analysis, therefore, represents a distinctive and innovative contribution beyond previously published methods.
| Parameters | HPLC | |||||
|---|---|---|---|---|---|---|
| SAA | ANN | ATN | APN | LSN | AEN | |
| a Mean of three concentrations in triplicate within the same day and in three successive days. | ||||||
| Linearity range (µg mL−1) | 0.5–40 | 0.5–30 | 5–100 | 10–200 | 5–130 | 5–140 |
| LOD (µg mL−1) | 0.13 | 0.06 | 1.63 | 2.46 | 0.48 | 0.44 |
| LOQ (µg mL−1) | 0.40 | 0.19 | 4.94 | 7.45 | 1.48 | 1.33 |
| The determination coefficient (r2) | 0.9999 | 0.9999 | 0.9999 | 0.9999 | 0.9999 | 0.9999 |
| Slope | 9.5828 | 4.5559 | 5.9357 | 6.9191 | 6.3944 | 6.5328 |
| SE of slope | 0.0199 | 0.0051 | 0.0156 | 0.0380 | 0.0116 | 0.0095 |
| Intercept | −0.8626 | −0.0294 | −1.7606 | −4.0579 | −2.3124 | −3.1444 |
| SE of intercept | 0.1840 | 0.08567 | 1.0334 | 5.1526 | 0.9251 | 0.8712 |
| Intraday precisiona | 0.492 | 0.963 | 0.489 | 0.920 | 0.092 | 0.572 |
| Interday precisiona | 0.762 | 0.287 | 0.557 | 0.384 | 0.359 | 0.586 |
| Accuracy (mean ± % SD) | 99.93 ± 1.125 | 100.20 ± 0.080 | 99.98 ± 0.354 | 99.82 ± 1.387 | 100.01 ± 0.515 | 100.09 ± 0.375 |
| Parameters variation | SAA | ANN | ATN | APN | LSN | AEN | |
|---|---|---|---|---|---|---|---|
| (10 µg mL−1) | (10 µg mL−1) | (10 µg mL−1) | (75 µg mL−1) | (50 µg mL−1) | (50 µg mL−1) | ||
| % Recovery | |||||||
| Temperature | 38 °C | 99.95 | 99.81 | 100.36 | 99.63 | 101.11 | 100.57 |
| 40 °C | 100.26 | 100.52 | 101.21 | 99.69 | 101.50 | 100.74 | |
| 42 °C | 100.45 | 99.95 | 99.88 | 99.30 | 101.08 | 101.15 | |
| RSD | 0.253 | 0.378 | 0.672 | 0.210 | 0.227 | 0.296 | |
| pH | 4.9 | 99.60 | 99.69 | 99.68 | 99.39 | 100.60 | 100.78 |
| 5 | 99.53 | 100.16 | 99.98 | 99.59 | 100.13 | 101.16 | |
| 5.1 | 100.08 | 101.38 | 100.23 | 100.02 | 99.86 | 100.78 | |
| RSD | 0.305 | 0.870 | 0.275 | 0.322 | 0.376 | 0.219 | |
| Flow rate | 0.90 | 100.86 | 101.67 | 101.03 | 100.45 | 101.18 | 101.39 |
| 1.0 | 100.21 | 100.37 | 100.86 | 99.50 | 100.53 | 100.58 | |
| 1.1 | 100.70 | 100.03 | 99.59 | 99.25 | 100.88 | 100.09 | |
| RSD | 0.338 | 0.859 | 0.782 | 0.637 | 0.319 | 0.651 | |
| Taken (µg mL−1) | % Recovery | |||||||
|---|---|---|---|---|---|---|---|---|
| SAA | ANN | APNa (75 µg mL−1) | AENa (50 µg mL−1) | ATNa (10 µg mL−1) | LSNa (50 µg mL−1) | SAA | ANN | |
a Determining APN, AEN, ATN, and LSN in a medicinally recommended ratio of 75 : 50 : 10 : 50, respectively, in the presence of varying concentrations of SAA and ANN impurities. |
||||||||
| 0.5 | 0.5 | 99.61 | 99.96 | 99.38 | 101.51 | 101.01 | 100.25 | |
| 5 | 5 | 98.14 | 99.99 | 100.41 | 100.58 | 100.62 | 100.99 | |
| 10 | 10 | 98.47 | 100.41 | 100.97 | 100.94 | 100.67 | 101.14 | |
| 20 | 20 | 98.30 | 100.68 | 98.74 | 100.63 | 100.71 | 100.79 | |
| 30 | 30 | 98.48 | 99.83 | 100.31 | 100.45 | 100.55 | 100.54 | |
| Mean | 98.60 | 100.12 | 99.96 | 100.82 | 100.71 | 100.74 | ||
| SD | 0.579 | 0.413 | 0.891 | 0.427 | 0.069 | 0.256 | ||
| % RSD | 0.588 | 0.413 | 0.891 | 0.424 | 0.069 | 0.255 | ||
| Micellar-HPLC | |||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| ATN | APN | LSN | AEN | ||||||||||||
| Taken (µg mL−1) | % Recovery | Taken (µg mL−1) | % Recovery | Taken (µg mL−1) | % Recovery | Taken (µg mL−1) | % Recovery | Taken (µg mL−1) | % Recovery | ||||||
| Tablet | Added | Tablet | Added | Tablet | Added | Tablet | Added | Tablet | Added | Tablet | Added | Tablet | Added | Tablet | Added |
| 5 | 99.63 | 25 | 101.86 | 25 | 98.97 | 25 | 98.71 | ||||||||
| 10 | 10 | 100.19 | 100.97 | 75 | 75 | 99.08 | 99.92 | 50 | 50 | 100.19 | 100.84 | 50 | 50 | 99.94 | 100.40 |
| 20 | 99.88 | 100 | 99.66 | 75 | 100.35 | 75 | 100.03 | ||||||||
| Mean | 100.16 | 100.48 | 100.05 | 99.71 | |||||||||||
| SD | 0.715 | 1.201 | 0.971 | 0.892 | |||||||||||
| % RSD | 0.714 | 1.195 | 0.971 | 0.894 | |||||||||||
| Parameters | SAA | ANN | ATN | APN | LSN | AEN | Recommended value33 |
|---|---|---|---|---|---|---|---|
| Retention time (tR) (min) | 3.034 | 4.251 | 5.054 | 5.902 | 6.922 | 8.367 | |
| Retention factor (K) | 1.02 | 1.83 | 2.37 | 2.94 | 3.62 | 4.58 | 1–10 |
| Resolution (Rs) | — | 6.21 | 8.11 | 8.77 | 7.36 | 6.85 | ≥2 |
| Symmetry factor (T) | 0.91 | 1.09 | 0.88 | 0.90 | 1.09 | 0.86 | <1.5 |
| Theoretical plate (N) | 4226 | 4899 | 6333 | 7322 | 6698 | 5898 | >2000 |
| Selectivity factor (α′) | — | 7.12 | 7.34 | 7.62 | 6.98 | 7.14 | >1 |
| Form | Statistical parameters | Reported methodb 24 | Micellar-HPLC | ||||||
|---|---|---|---|---|---|---|---|---|---|
| ATN | APN | LSN | AEN | ATN | APN | LSN | AEN | ||
a The tabulated values of the t-test and F-ratio.b The reported HPLC method for the detection of ATN, APN, LSN, and AEN at 236 nm using a mobile phase of acetonitrile: 0.02 M potassium dihydrogen phosphate buffer of pH 3.4 (70 : 30, v/v). |
|||||||||
| Pharmaceutical dosage form | Mean | 99.92 | 99.62 | 100.10 | 99.49 | 100.19 | 99.08 | 100.19 | 99.94 |
| SD | 1.016 | 0.780 | 0.562 | 0.521 | 1.124 | 0.414 | 0.485 | 0.358 | |
| N | 6 | 6 | 6 | 6 | 6 | 6 | 6 | 6 | |
| Variance | 1.040 | 0.608 | 0.314 | 0.270 | 1.254 | 0.168 | 0.240 | 0.130 | |
| t-test (2.23)a | — | — | — | — | 0.44 | 1.50 | 0.30 | 1.74 | |
| F-ratio (5.05)a | — | — | — | — | 1.21 | 3.62 | 1.31 | 2.09 | |
This study establishes a comprehensive and regulatory-compliant analytical framework that delivers high sensitivity, robust linearity across the investigated concentration ranges, and excellent precision and accuracy, as evidenced by validation metrics that consistently meet accepted international guidelines with lower or similar LOD and LOQ values. In addition to achieving analytical performance comparable to or exceeding that of previously reported methods, the proposed approach extends selectivity by enabling the simultaneous quantification of active pharmaceutical ingredients in the presence of related impurities and degradation products. This capability addresses a critical limitation of many existing API-centered methodologies and directly enhances the methodological rigor and practical relevance of the research proposal. Collectively, these findings reinforce the scientific justification for the proposed work, support its applicability in routine quality control, stability studies, and regulatory submissions, and underscore its potential to improve the reliability, efficiency, and regulatory alignment of pharmaceutical analytical workflows.
| Bond type | Bond strength (kcal mol−1) | Amino acid in CYP1A2 |
|---|---|---|
| Hydrogen bond | 1–5 | Phe 125 |
| Covalent bond | 1 | Gly 316 |
| Electrostatic interaction | 5–10 | Asp 313 |
| rseq | 1 | |
| mseq | 1 | |
| S | −4.1921 | |
| Bond type | Bond strength (kcal mol−1) | Amino acid in CYP1A2 |
|---|---|---|
| Hydrogen bond | 1–5 | Serine (Ser), threonine (Thr) |
| Pi–Pi stacking | 2–10 | Phenylalanine (Phe), tyrosine (Tyr) |
| Hydrophobic interaction | 0.5–2 | Leucine (Leu), isoleucine (Ile), valine (Val) |
| van der Waals | <1 | Various amino acids |
| Ionic interaction (if applicable) | 5–10 | Glutamic acid (Glu), aspartic acid (Asp) |
The findings demonstrated that ANN could bind to distinct amino acid residues in the CYP 1A2 compartment either by hydrogen bonding, covalent bond, and electrostatic interaction, as in Phe 125, glycine (Gly 316), and aspartate (Asp 313), respectively. The bond length was 3.00 ± 0.10 Å and its binding energy ranges from 1 to 10 kcal mol−1. The binding was demonstrated by 3D and 2D models, respectively (Fig. 5A and B).
![]() | ||
| Fig. 5 (A) Three-dimensional and (B) two-dimensional molecular simulation of ANN binding with CYP 1A2. | ||
Based on previously reported findings, theoretical docking studies verified that ANN had a higher affinity for CYP1A2 and a greater ability to fit.34 The validity of the results (Table 7) was assured by the reference sequence (rseq), which represents the primary sequence or the first entry in a list and the model sequence (mseq), which represents alignment or pairing with the reference sequence. Both rseq and mseq results confirmed the appropriate docking process, which released an energy (S) of −4.1921.
Validation of the docking protocol is performed via calculation of the root mean square deviation (RMSD). The RMSD is predicted via redocking the co-crystalized ligand on its target enzyme and then superimposing the redocked co-crystalized ligand onto its original co-crystallized bound conformation. During this study, the RMSD of the Human Microsomal P450 1A2 enzyme was within the acceptable range with a value of 1.2356.
Finally, it is crucial to identify the researched medications in the presence of associated hazardous impurities, such as ANN, to ensure the safety of the pharmaceutical product, as frequent and continuous interaction of ANN with CYP1A2 may cause significant hypoxic injury to human beings.
However, ANN had some safety concerns, a carcinogenicity alert, and a risk of drug-induced respiratory toxicity. In terms of clearance and excretion, ANN displayed a clearance rate of 9.025 mL min−1 kg−1, which is considered moderate.
![]() | ||
| Fig. 6 Green assessment using a green analytical procedure index for (A) the proposed and (B) reported HPLC methods. | ||
2. BAGI software generated a final graphic showing the degree of greenness (Fig. 7A), illustrating the overall greenness of the proposed method as evaluated by the BAGI system. With a final BAGI score of 85.0, the suggested technique showed excellent applicability. A comparison with the reported method (Fig. 7B)24 revealed that the proposed HPLC method is more eco-friendly, as the reported method achieved a lower BAGI score of 75.0.
![]() | ||
| Fig. 7 Green assessment using a blue applicability grade index for (A) the proposed and (B) reported HPLC methods. | ||
3. AGREE produced a final estimated greenness score of 0.8 (Fig. 8A) in the middle by allocating different scores to various studied factors. This represents the performance of the greenness approach. The same assessment by AGREE-prep was applied to the reported method24 (Fig. 8B).
| This journal is © The Royal Society of Chemistry 2026 |