Central composite design driven optimization of sustainable stability indicating HPLC method for the determination of Tigecycline and greenness assessment

Reagents and chemicals

TGC was donated by the QPS laboratory (Egypt). Ammonium acetate, triethylamine (TEA), ammonium hydroxide, ethylene diamine tetra-acetic acid disodium salt dihydrate (EDTA), and acetic acid were obtained from Merck (Germany). Without additional purification, HPLC-grade ethanol from Merck (Germany) was utilized. A Milli-pore analytical deionization system collected deionized water (Bedford, MA). Tygacil^® (Pfizer, U.S.A.) lyophilized vial containing fifty milligrams of TGC was purchased from wholesale suppliers during the product's shelf life.

Instrumentation

A quaternary pump and a solvent chamber with an auto-sampler injection system were both parts of the Alliance HPLC instrumentation (Waters, U.S.A.) used in this study. A conventional flow cell was coupled to a Waters photodiode array for detection. The data was gathered with the help of the Empower 3 program. All results were calculated in Design Expert 13 software from Stat-Ease Inc. (Minneapolis, U.S.A.) and Microsoft Excel 2016 (Microsoft Corporation, U.S.A.). Lab pH meter model AD1030 from ADWA in Romania was used to adjust the mobile phase's pH to the desired level. The accurate weighing was accomplished using an analytical balance of SA 210 D (Scientech, U.S.A.).

Chromatographic conditions

Preparing an ammonium acetate pH 6.0 buffer

Transfer 3.85 g ammonium acetate (50 mM), 5.82 g EDTA (20 mM), and 0.2 mL TEA(0.2% v:v) to 1000 mL HPLC grade water, sonicated to dissolve, and then adjust to pH 6.25with glacial acetic acid.

Optimized chromatographic conditions

The assessment of TGC in pharmaceutical drug products and degradation investigations was performed on a reversed-phase symmetry C18 column (10* 0.46 centimetre, 3.5 micrometres), Waters (Ireland). For the liquid chromatography, a mobile phase of 85 volumes of buffer solution (50 mM ammonium acetate, 20 mM disodium edetate, 0.2% triethylamine) and 15 volume ethanol was used at a temperature of 40 degrees Celsius. It was filtered with a membrane filter from a Millipore of 0.45-micrometre pore size. The analysis was carried out at a flow rate of 1.0 millilitres per minute utilizing UV detection at 275 nanometers. The reference material and the samples were injected with a volume of 40 μL, which was the same.

Preparing reference substance solutions

Water is considered the most suitable solvent for TGC because of its high solubility in water.^5,6 The standard stock solution was produced by accurately weighing 25 mg of the TGC reference substance, moving it to a twenty-five millilitres flask, and diluting it with distilled water until it reached a TGC concentration of 1000 μg mL^-1. The freshly prepared stock standard solution was then diluted with water to the desired concentration before being filtered through a membrane filter with a pore size of 0.45 micrometres (Millipore).

Construction of calibration graphs for the linearity test

Aliquots were taken from TGC standard stock solutions and transferred into appropriate volumetric flasks to prepare concentrations of 8-60 μg mL^-1 for TGC to complete each flask, and distilled water was utilized. The calibration graphs were created by graphing the area under the peak versus TGC concentration in μg mL^-1 and calculating the regression equations.

Preparation of solution for accuracy and precision tests

The stock solution should be diluted for the precision test to produce solutions containing 32, 40, and 48 μg mL^-1. These solutions will be evaluated using three separate measurements of TGC samples on the same day (intra-day). Then, it was performed over two more days to assess the investigation's intermediate precision than initially planned (inter-day). For the objective of the accuracy test, exactly known quantities of TGC were successively transferred to a placebo solution to generate solutions with concentration levels of 32, 40, and 48 μg mL^-1, equivalent to 80, 100, and 120 percent of the actual analytical level.

The preparation of test samples

To make the sample solution, weighing and mixing Tygacil^® vials with 50 milligrams of TGC in each twenty-five millilitres flask was necessary. A suitable volume of the solution was added and mixed to the volume with distilled water (40 μg mL^-1) and injected.

Forced degradation tests of TGC

An analytical method that successfully evaluates and assesses the active constituents without interfering with degradation products, process contaminants, inactive ingredients, or any other possible impurities is known as a stability-indicating procedure.^5,10,47 A standard reference solution and pharmaceutical preparations of 1 mg mL^-1 concentration were submitted to rapid forced degradation under acidic, basic, neutral, oxidative, and photolytic conditions to study the interference in the measurement of TGC. The ICH guidelines Q1A (R2) and Q1B were used for these degradation investigations, including solid and solution phases.^5,10

Acidic forced degradation

Ten milliliters of the TGC stock solution were treated with 100 mM HCl to hasten acidic degradation. Subsequently, the solution was examined at 25 and 60°C for an hour.^5,10

Alkaline forced degradation

To initiate alkaline degradation, a portion of ten milliliters of TGC stock solution was exposed to ten milliliters of 100 mM sodium hydroxide at 25°C for two hours.^5,10

Oxidative forced degradation

To commence the oxidative degradation, a portion of ten milliliters of TGC stock solution was maintained at 25°C for two hours, shielded from illumination, with ten milliliters of 5 percent H₂O_2.^5,10

Thermal forced degradation

Under neutral conditions, both TGC powder and solution were thermally degraded. TGC powder was maintained in a 60°C oven. A portion of the treated material was weighed and diluted in a 25-millilitre flask. A TGC stock solution was mixed with distilled water and heated to 60°C.^5,10

Photolytic forced degradation

TGC powder and solution were tested for photolytic degeneration after twenty-four hours of exposure to near-ultraviolet radiation. There was enough TGC powder weighed and tested under ultraviolet radiation. In addition, an amount of TGC stock solution equal to ten milliliters of distilled water was treated with ultraviolet light for testing.^5,10,47 Therefore, every sample was taken at the intervals that were specified above. If necessary, it was treated before being injected to stop the degradation, and then it was diluted with distilled water to the target concentration (40 μg mL^-1).

Experimental design (ED)

Initially, a trial and error approach was used to learn about the method's efficacy and to identify critical, independent parameters and their impacts on dependent responses or parameters. Establishing a separation between TGC and its degradants with a resolution of more than 2.0 is the primary goal of the RP-HPLC method development, in addition to other important parameters that affect the accuracy and precision of the method. For example, the ED of the proposed method was set, and the central composite design (CCD) with the response surface method (RSM) was used.⁴⁶

The ED initially begins with the pre-determination of the principle parameter crucial to the method efficacy; therefore, it should be measured during the ED (critical quality attributes (CQA)). The next step was determining the acceptable value of the CQA according to universal pharmacopoeias such as USP and BP, defined as analytical target profile (ATP). The optimum resolution (Rs) between peaks is considered the principle CQA. The peak symmetry, capacity factor, and other CQAs were also investigated (Table 1). The proposed ATPs had to be determined (Table 1) to achieve good reliability of the results. The next step is to define the main variables of the proposed chromatographic method that affect the CQAs and ATPs values which are defined as critical method parameters (CMPs) (Table 1).⁴⁴

Furthermore, the RSM with a three-level CCD was selected for the ED. In other words, the design comprises 3 important factors independently acting to build the design. The independent factors investigated were the ratio of green solvent (% Ethanol), the pH value of aqueous mobile phase (pH), and the concentration of additives EDTA and TEA.

Twenty runs, each with a unique condition, made up the CCD (Table 2). The aqueous portion of the mobile phase, 100 mL in volume, was made for each run. Once the pH was adjusted, the mobile phase was eluted at a rate of 1.0 mL min^-1 in each run. TGC and its degradation products were measured at 275 nm. After collecting and analyzing all responses, models were created in design expert 13 to determine the interactive effects between the CQAs and the CMPs. The optimization process was designed to find the optimal Rs between the peaks of TGC and its degradation products without surrendering the other parameters that eventually determine the system's efficacy. Throughout this process, optimization was carried out both numerically and graphically.

Optimization

Preliminary tests for screening

The HPLC approach was selected to separate and quantify TGC and its degradation products. To establish a method for monitoring the stability of a product, the proposed chromatographic conditions must be developed and optimized. The impact of the relevant factors was screened using the preliminary experiments. TGC has a molecular weight of 585.65, log P values of -3.86, and pKa values of 3.19, 6.4, 7.54, and 9.14, respectively.^6,49 For example, water was selected as the appropriate solvent for TGC due to its high water solubility.^5,6 In addition, all stock solutions in water were refrigerated for optimal drug stability in amber containers.

Furthermore, an ultraviolet spectrophotometer scans 10 μg mL^-1 TGC solution to find appropriate wavelengths. The wavelength of the measurement must be 20 nanometers longer than the ultra-violet cutoff of the solvent.⁵⁰ The ultraviolet cutoff of ammonium formate containing EDTA and TEA mixed with ethanol (which were used in reversed-phase liquid chromatography trials) was 210 nm.⁵⁰ Consequently, the UV detector can be set at 275 nm for TGC detection. According to Figure 2, the latter wavelength would show acceptable sensitivity for the TGC peak with good peak shape and baseline in the HPLC chromatogram compared to a wavelength of 245 nm, so it was chosen for ED examinations (Figure 2).

Figure 2. 3D plot of the UV spectrum of TGC in distilled water.

Two columns were employed to perform performance investigations. These columns were a VDSpher C18-E column (25*0.46 cm, 5 μm) from Nouryon (Sweden) and symmetry C18 Columns (10*0.46 cm, 3.5 μm) from Waters (Ireland). TGC is an antibiotic that resembles the chemical properties of tetracycline. TGC causes tailing peaks in a reversed-phase column by forming chelate complexes with metal ions and binding to the silanol group (Si-O-R). Experiments demonstrated that the column, symmetry C18 Column, was more suitable because it had excellent chromatographic performance, ideal resolution, sensitivity, and peak symmetry while maintaining a shorter run time. A preliminary trial showed that mobile phase pH greater than 4 improves the peak shape of TGC but still needs improvement. As a result, some additives for mobile phases were tested for improving TGC peak shape and the resolution with its degradation products.

Higher pH values (4 or higher) combined with different concentrations of ethanol, EDTA, or TEA led to greater interference between the peaks of TGC and degradation products and a faster elution. These methods were developed to prevent adsorption on reversed-phase columns and chelate complexes formation. Therefore, the variables' minimum and maximum values were set at (10 and 20%), (5 and 7.5 mM), (10 and 40 mM), and (0.1 and 0.3%) for the percent of ethanol, mobile phase pH, EDTA molar concentration and percent of TEA, respectively. These values were utilized to figure out the possible range of the variables.

RSM and CCD study

Design Expert 13 software was used to make the ED, and RSM was used to explore the influence of the variables.⁵¹ The model uses a CCD design, combining the independent factors in 20 different and five-centric runs. Our optimization study focused on the following factors: ethanol concentration, mobile phase pH, EDTA molar concentration, and percent of TEA. This study aimed to explore the sweet spot for these four factors. In addition, three distinct degrees of evaluation were carried out for each variable: -α, 0, and +α in Table 2.

As a result, the quadratic model can determine which parameters are most crucial. CCD is used for response modelling and optimization because it can comprehend the interactions between multiple variables.^44–46 the rotatable CCD was chosen because of its high consistency and relatively low variability. This experiment consisted of 20 randomized iterations that were used to assess the factor effects using (-α), (-1), (0), (+1), and (+α) values of examined variables.

Response analysis and optimization

The five selected responses were evaluated based on the criteria (ATP). Coded prediction models or equations allow one to compute the importance of various factors in light of the data at hand.⁴⁵ For instance, an artificial model selection approach used the Akaike information criterion (AIC) to improve accuracy. The P value is used in statistical analysis to determine the degree of significance (Table 3). Compared to the threshold for statistical significance set at (P value = 0.05), all proposed models have minor P values (0.0001), indicating their significance. However, higher P values for the lack of fit indicate that they are not statistically significant (<0.05) (Table 3). A positive coefficient in Table 3 positively impacts the corresponding response, whereas a negative coefficient indicates the opposite.⁵¹ Therefore, to ensure model validity, other CCD aspects must be investigated. Finally, strong linearity between the adjusted and expected regression coefficient (R2) was proved if the difference was smaller than 0.2 (Table 3).

There was also the signal-to-noise ratio, which had to be high and was approved if a value greater than 4 indicated appropriate precision. Based on previously existing data, it was possible to determine the relevance of the examined factors to the selected CQAs. The adequate precision allows for evaluating the signal-to-noise ratio, which should be greater than 4.0. Consequently, as shown in Table 3, the findings demonstrate that this model can explore the design space.

In Figure 3 and Figure 4, contour and 3D surface plots depict the optimal responses against numerous combinations of essential variables. Finally, optimization was performed using both graphical and numerical approaches. In this stage, solutions are developed for the ideal chromatography settings with the best levels of desire by utilizing the limitations of the variables and their responses, as shown in Figure 5.

Figure 3. Contour Plots for the effect of dependent variables on all responses.

Figure 4. Plots of the 3D response surface for dependent variables, including (A) the resolution (Res 1), (B) (Res 2), and (C) run time.

Figure 5. Overlay plot showing the sweet spot for the selected chromatographic parameters in response to acceptable factor settings.

The primary objective of the optimizations was to attain a reasonable value for Resolution (>2). Other parameters, including peak symmetry, theoretical plates, capacity factor, and the shortness of analysis time (run time), were also considered. With graphical optimization, it's possible to put these limitations into practice. Finding the “sweet spot” (optimal value) between design space and robustness requires adjusting factor values (yellow area) (Figure 5). However, results that fall into the gray area are generally undesirable. The pH varied between 6.0 and 6.4, the molar concentration of EDTA was between 10 and 40 mM, and the quantity of TEA was between 0.1 and 0.3 percent. The acceptable ranges are illustrated in Figure 5. When using the post-analysis procedure, the computed mean was inside the 95% confidence interval (CI) of the possible values.

Method validation

The method was validated by establishing its specificity, linearity, precision, accuracy, and robustness. The validation was done following the ICH requirements.⁴⁷

Specificity

Testing for excipient interference was performed by injecting a placebo (house-made solution of lyophilized powder excipient), and a known TGC concentration (40 μg mL^-1) was added to the placebo solution. The ability of the method to identify degradation products from the TGC peak is shown to have been successfully demonstrated by the excellent separation of the peaks, as shown in Figure 6.

Figure 6. Proposed method is composed of a mobile phase containing ammonium acetate (50 mM), disodium edetate (20 mM), and triethylamine (0.2% v: v) (pH 6.25) - ethanol (85:15, v/v) running on Symmetry C18 column at a flow rate = 1 mL per minute.

Linearity and range

The linearity was confirmed by creating three different analytical graphs based on water, each with six different TGC levels in the 8–60 μg mL^-1. Before the injection of the solutions, the column was first allowed to become equilibrated for at least twenty minutes while the mobile phase was being passed via the system. As a point of reference, the area of peaks of the chromatograms and the concentrations of TGC were plotted on the analytical graph to construct the calibration graphs of TGC. Table 4 and Figure 7 state that the results, calibration equation, and determination coefficient were calculated using regression analysis with the least-squares method.

Figure 7. Calibration curve of TGC.

Precision and accuracy

The precision of the approach was assessed based on its repeatability and intermediate precision. Six determinations were performed on the same day and under the same conditions to test the repeatability (intra-day) using the same TGC concentration sample. Analyses performed on three separate days (inter-day) and by other analysts in the same laboratory helped determine the method's intermediate precision (between analysts). The accuracy of the proposed method was assessed by adding 32, 40, and 48 μg mL^-1 to a sample solution equivalent to 80, 100, and 120 percent of the actual analytical level. As can be seen in Table 5, the percentage of sample recovery was utilized to calculate the percent bias (% error) between the recorded average concentrations and those that were added.

LOD and LOQ

The LOQ and LOD values were calculated using ICH,⁴⁷ and the results are presented in Table 4. Calculating LOQ and LOD was accomplished by determining the standard deviation of the intercept and slope ratio over three different analytical graphs. These values were obtained using a linear regression model and multiplying the latter percentage by their respective detection and quantitation limit factors of 3.3 and 10. In addition, the LOQ was tested in an experiment.

Robustness

For routine analysis, the robustness of the suggested procedure can be judged by its capacity to withstand modest and purposeful changes in method parameters. For example, using the same samples (40 μg mL^-1 TGC) under five different analytical parameters, the robustness assessment of the chromatographic procedure for TGC quantification is illustrated in Table 6.

System suitability test

A system suitability test was also performed to verify the system's repeatability and resolution for the analysis. This test consisted of 6 replicate injections of a standard solution containing 40 μg mL^-1 TGC. Measurements were taken of peak symmetry, theoretical plates, and capacity factor. Observe and record the relative standard deviation of the peak area of injected standard samples and the retention times of all injections.

Measurement of TGC in drug products

After diluting the lyophilized TGC vial with water (40 μg mL^-1), filtering, and injecting in triplicate, the percent recoveries of the TGC against the pure compound were determined.

Degradation kinetic study

ICH Q1A (R1) and Q1B recommendations were applied further to study the degradation of TGC under various stress conditions.^10,48

Reactions of degradation

When no information regarding potential degradation products was available, stress degradation tests were employed to test the method's stability-indicating aspects. In addition, all stress degradation investigations generated probable degradation products. It was found that TGC was labile to all forced degradation conditions, including acidic, alkaline oxidative, thermal hydrolysis, and UV degradation. TGC showed significant decreases in the area under all conditions, ranging from 30 to 70% (Table 7). Furthermore, each type of forced degradation scenario produced a distinct pattern of degradation products corresponding to specific degradation pathways. The TGC reference material and Tygacil had nearly identical findings and practices.

Greenness evaluation of the suggested method

To determine whether the proposed method was environmentally friendly, we used the analytical eco-scale to calculate the penalty points gained by each analysis step. A grade of over 75 suggests a special green assessment, while a degree of over 50 shows an acceptable green evaluation, and a grade of 50 indicates inadequate green assessment.⁴⁰ Analytical procedures can be evaluated using the Green Analytical Procedure Index (GAPI), a new tool that assesses the environmental friendliness of the entire process. Using a unique symbol with five pentagrams, it is possible to use GAPI to analyze and quantify the ecological impact of each phase of an analytical technique. The colors green, yellow, plus red in the GAPI pentagram each stand for a different level of impact: low, middle, as well as high, respectively.

The number of Globally Harmonized System (GHS) of Classification and Labeling of Chemicals hazard pictograms was multiplied by the degree of hazard warning, which was multiplied by 1, and danger, which was multiplied by 2, to calculate the number of penalty counts that should be assigned to each reagent. Because the GHS risk pictograms are printed on the bottles of the reagents, it is easy to determine the level of danger connected with using the chemicals.^41–43,52 The interpretation of the GAPI pentagrams for the proposed chromatographic approach and its comparison with the reported methods^33–35 are described in Table 8 and illustrated in Figure 8. The recommended procedure was more environmentally friendly than the reported methods. As a result, it can be used for routine analysis without causing harm to the environment.

Figure 8. GAPI evaluation of the green character of the reported method 1 (A), reported method 2 (B), reported method 3 (C) and developed HPLC method (D).