3.2. Chemical Degradation of Glutides (GLP-1 RAs) and the Methods Used for Elucidate Their Degradation Pathways
Similarly to low-mass drug (small drug) molecules, regulatory agencies recommend characterizing the chemical stability and related impurities of peptide drugs. These impurities may occur as a result of degradation during manufacture or storage and decrease product efficacy or even exert some toxic effects. It is reported that some impurities derived from the degradation of peptide drugs can even provoke anaphylactic shock
[14]. It is also obvious that impurities from degradation processes in peptide drugs should be controlled using the appropriate strategies
[13].
In the study from the literature
[21], a few analytical methods to examine the degradation of exenatide (EXE) in solutions of different pH were described. Firstly, EXE and its impurities were separated on a C4-Pack column using PDA detection and analyzed by a mass spectrometer with a Q-TOF with a dual ESI system. The total ion chromatogram (TIC) was obtained at 280 nm. Secondly, impurities in EXE were separated using HPLC-SEC using a dedicated Superdex Increase 75 GL column from Cytiva (Marlborough, MA, USA) (10 × 300 mm) and recorded using an UV detector. Samples were separated with phosphate buffered saline as the mobile phase at a flow rate of 1.0 mL/min using isocratic elution. In addition, the intrinsic fluorescence of proteins was used to determine the tertiary structure of EXE. Analysis was performed at the wavelength range of 280–450 nm for emission and at wavelength 270 nm for excitation.
4. Gliflozins (SGLT2 Inhibitors)
Gliflozins are members of a group of relatively new SGLT2 inhibitors that increase glucosuria by inhibiting glucose reabsorption in the kidney. Since the approval of dapagliflozin (DAPA, (2S,3R,4R,5S,6R)-2-[4-chloro-3-[(4-ethoxyphenyl)methyl]phenyl]-6-(hydroxymethyl)oxane-3,4,5-triol) as the first SGLT2 inhibitor in 2012, many other drugs have been developed and approved, including canagliflozin (CANA, (2S,3R,4R,5S,6R)-2-[3-[[5-(4-fluorophenyl)thiophen-2-yl]methyl]-4-methylphenyl]-6-(hydroxymethyl)oxane-3,4,5-triol), empagliflozin (EMPA, (2S,3R,4R,5S,6R)-2-[4-chloro-3-[[4-[(3S)-oxolan-3-yl]oxyphenyl]methyl]phenyl]-6-(hydroxymethyl)oxane-3,4,5-triol), ertugliflozin (ERTU, (1S,2S,3S,4R,5S)-5-[4-chloro-3-[(4-ethoxyphenyl)methyl]phenyl]-1-(hydroxymethyl)-6,8-dioxabicyclo[3.2.1]octane-2,3,4-triol), ipragliflozin (IPRA, (2S,3R,4R,5S,6R)-2-[3-(1-benzothiophen-2-ylmethyl)-4-fluorophenyl]-6-(hydroxymethyl)oxane-3,4,5-triol), tofogliflozin (TOFO, (3S,3′R,4′S,5′S,6′R)-5-[(4-ethylphenyl)methyl]-6′-(hydroxymethyl)spiro [1H-2-benzofuran-3,2′-oxane]-3′,4′,5′-triol), luseogliflozin (LUSE, (2S,3R,4R,5S,6R)-2-[5-[(4-ethoxyphenyl)methyl]-2-methoxy-4-methylphenyl]-6-(hydroxy me thyl)thiane-3,4,5-triol) and bexagliflozin (BEXA, (2S,3R,4R,5S,6R)-2-[4-chloro-3-[[4-(2-cyclopropyloxyethoxy)phenyl]methyl]phenyl]-6-(hydroxymethyl)oxane-3,4,5-triol)
[1].
By targeting the kidney, gliflozins have a unique mechanism of action that results in enhanced glucosuria, osmotic diuresis, and natriuresis. Thereby, they improve glucose control with a limited risk of hypoglycemia. In addition, they have shown favorable effects on cardiovascular risk factors such as body weight, blood pressure, lipid profile, arterial stiffness, and endothelial functions
[3][5]. The predominant pathophysiological mechanisms that may explain the cardiovascular benefits of SGLT2 include plasma volume and diuresis, cardiac fibrosis, myocardial metabolism, and adipokine kinetics. Therefore, the current guidelines propose a new procedure in the management of T2DM with a preferential place for SGLT2, even before metformin, especially in patients with atherosclerotic cardiovascular disease, heart failure, and progressive kidney disease
[1].
4.1. Metabolic Transformations of Gliflozins (SGLT2 Inhibitors) and the Methods Used to Examine Their Metabolic Pathways
In the study of Zhang et al.
[22], the samples from humans and animals receiving bexagliflozin (BEXA) were fractionated by an HPLC system and examined using a radioactivity flow monitor. Radioactivity in bulk samples was determined using a liquid scintillation analyzer. Quench correction was checked using quenched radioactive reference standards. In the next step, unlabeled rat plasma samples were analyzed using the next HPLC system with detection on a triple quadrupole mass spectrometer equipped with an atmospheric pressure chemical ionization (APCI) interface. For the analysis of unlabeled monkey samples, an LC-MS/MS mass spectrometer equipped with a turbo ion spray with an ESI interface was applied.
Based on the results obtained by the Authors, BEXA was shown to be metabolized via glucuronidation and oxidation to form six principal metabolites, i.e., three non-active metabolites through glucuronidation and three through oxidation, i.e., BEXA-M1, BEXA-M2, and BEXA-M3. In vitro studies identified CYP3A4 and UDP-glucuronosyltransferase UGT1A9 as the major enzymes acting on the BEXA moiety. Following oral dosing of humans with [14C]-BEXA, the 3-O-glucuronide contributed 32% of the parent drug, and all other metabolites contributed < 10%. The input of recovered radioactivity was ca. 90%, and of this, ca. 50% was present in feces, predominantly as BEXA, and ca. 40% was present in urine, mainly as 3-O-glucuronide. At the same time, BEXA-M2 was shown as a major metabolite in vivo in all species examined. The pharmacological activity of these metabolites was assessed by measuring the sodium-dependent uptake of the particular substrate, methyl-a-D-[U-14C]-glucopyranoside, that was not metabolized, by cells expressing recombinant human SGLT2 protein. All metabolites had less than 10% of the activity of the parent BEXA
[22].
In the study of Francke et al.
[23], separation of canagliflozin (CANA) and its metabolites was achieved using a Waters XBridge RP-HPLC column (4.6 × 250 mm, 5 µm) at 25 °C. A flow rate of the mobile phase of 1 mL/min was used throughout the analysis. Sample components were eluted with a gradient elution consisting of solvent A (0.025 mM ammonium acetate, pH 9) and solvent B (10/45/45, 0.25 M ammonium acetate of pH 9/MeOH/ACN). The eluates from the HPLC column were steered to both a PDA detector and a radioactivity detector. Finally, the amount of the unchanged CANA was calculated from the radioactivity peaks. The main goal of this study was to examine the formation of CANA O-glucuronides in microsomes from human liver, intestinal, and kidney tissues using [14C]-CANA. Furthermore, the impact of genetic variations in UGTs on the pharmacokinetics of CANA was studied in detail
[23].
Separation of glucuronides of CANA was also performed in the study of Algeelani et al.
[24], using a HPLC method on a Waters μBondaPak C18 column (3.9 × 300 mm) with fluorescence detection. The elution was isocratic, with the mobile phase at pH 3.2 consisting of ACN and 20 mM phosphate buffer (55:45,
v/
v) with a flow rate of 1 mL/min. For detecting respective eluents, the wavelength 280 nm was used for excitation, and the wavelength 325 nm was used for emission.
4.2. Chemical Degradation of Gliflozins (SGLT2 Inhibitors) and the Methods Used for Elucidate Their Degradation Pathways
In the study of Emam and Abdelwaham
[25], CANA was quantified along with its oxidative degradation product by an eco-friendly HPLC method. Separation and quantitation were performed on a Zorbax Eclipse C18 column from Agilent Technologies (4.6 × 250 mm, 5 μm) with the mobile phase consisting of MeOH-H
2O (98:2,
v/
v) at a flow rate of 1 mL/min and UV detection at 225 nm. The column temperature was maintained at 25 °C. The main oxidative degradation product was obtained by refluxing CANA with 3% hydrogen peroxide at high temperatures. The structure of the prepared degradation product showed the presence of a carboxylic group (CANA-D1) that was confirmed using IR analysis
[25].
The degradation processes of CANA were also studied using UPLC and LC/ESI-QTOF-MS/MS analysis
[26]. Separation of the drug and its degradants was monitored at 291 nm. The same UPLC conditions were applied for LC/HRMS analysis. Degradation of CANA was observed under oxidative and acidic stress conditions, whereas it was stable under base and neutral hydrolysis as well as photolytic and thermal stress. The oxidative degradants were identified as CANA-D2 and CANA-D3. Formation of CANA-D2 can be explained by S-oxidation of the thiophene ring and hydroxylation of the fluorobenzene ring of the parent drug, bearing in mind that thiophene sulfur is rather prone to oxidation. The elemental compositions of CANA-D2 and its product ions in MS were confirmed by accurate mass measurements. Based on these data, CANA-D2 was identified as (2S,3R,4S,5S,6R)-2-(3-((5-(4-fluoro-2-hydroxyphenyl)thiophen-1-oxide-2-yl)methyl)-4-methylphenyl)-6-(hydroxymethyl)tetrahydro-2H-pyran-3,4,5-triol. As far as CANA-D3 is concerned, the addition of an oxygen atom on the thiophene ring and the formation of 5-(4-fluorophenyl)-2-methylenethiophen-3(2H)-one were suggested. Based on these data, the name for CANA-D3 was proposed as (E)-5-(4-fluorophenyl)-2-(2-methyl-5-((2S,3R,4S,5S,6R)-3,4,5-trihydroxy-6-(hydroxymethyl)tetrahydro-2Hpyran-2-yl)benzylidene)thiophen-3(2H)-one
[26].
In silico toxicity prediction of DAPA and its degradation products was also performed with ProTox-II software (
https:/tox.charite.de) that classified toxicity with different targets, such as oral, hepatic, carcinogenic, immunotoxicity, mutagenicity, and cytotoxicity. Various Tox21-Nuclear receptor signaling pathways, Tox21-stress response pathways, and toxicity targets were included in this study. Prediction tools identified that there is no binding of DAPA and its degradation products to any of the toxicity targets, and similarly, most of the toxicity end points and pathways are inactive. However, immunotoxicity end point and aryl hydrocarbon receptor signaling pathways are active in the case of DAPA-D2, and mitochondrial membrane potential stress response pathways are active in the cases of DAPA-D2 and DAPA-D1
[27].
Forced degradation studies were performed under different stress conditions, and then the degraded samples were analyzed by the developed method. In acidic conditions EMPA, showed 28.76% degradation with the formation of 3 degradants, namely, EMPA-D1, EMPA-D2, and EMPA-D3. Based on LC-MS/MS studies, the probable structures of these degradants were proposed. EMPA-D1 was identified as 6-(4-chloro-3-{[4-(oxalan-3yloxy)phenyl]methyl}phenyl)-2-(hydroxymethyl)-3,4-dihydro-2H-pyran-3,4-diol. The structure of 6-(4-chloro-3{[4-(oxalan-3 yloxy)phenyl]methyl}phenyl)-2-(hydroxymethyl)-2H-pyran-3-ol was proposed for EMPA-D2 while EMPA-D3 was specified as 6-(4-chloro-3{[4-(oxalan-3-yloxy)phenyl]methyl}phenyl)-2-methylidene-2H-pyran-3-ol. Under alkaline conditions, EMPA showed degradation of 15.48%, and the formation of the next 2 degradants was reported. From the LC-MS/MS data, the probable structure of one of them, i.e., EMPA-D4 was proposed as 2-(4-hydroxy-3{[4-(oxalan-3-yloxy)phenyl]methyl}phenyl)-6-(hydroxymethyl)-oxane-3,4,5-triol). By analyzing the obtained spectra, the substitution of the chlorine atom by the OH group was proposed. Under oxidative conditions, EMPA was found to generate one more degradant, i.e., EMPA-D5, that could be formed by oxidation of the primary alcoholic group to carboxylic acid to form 6-(4-chloro-3{[4-(oxalan-3-yloxy)phenyl]methyl}phenyl)-3,4,5-trihydroxyoxane-2-carboxylic acid
[28].
5. Conclusions
The main analytical tools for the analysis of glutides and gliflozins are undoubtely LC-MS or LC-HRMS methods. LC-HRMS is especially important for peptide drugs such as glutides. Mass spectrometers are frequently combined with a quadrupole such as a Q-TOF system, an ion trap, or orbitrap mass analyzers that deliver excellent resolution and mass accuracy, which are essential in drug metabolism and drug degradation studies
[11]. In addition, radiometric methods using stable isotopes as well as chromatographic methods with deuterated standards could be used for the determination of the mentioned drugs in biological fluids or excreta. As was described above, [14C] and [13C] technology was widely applied for tracking glutides as well as gliflozins and providing their metabolic profiles.
It was also demonstrated that several SGLT2 inhibitors, including BEXA, CANA, DAPA, EMPA, and ERTU, share a similar metabolic pathway in humans and animals, primarily through O-glucuronidation. Their major non-active metabolites were identified as 1-O, 2-O, and 3-O-glucuronides. These SGLT2 inhibitors that metabolize through glucuronidation can be subsequently eliminated with urine. Such an excretion process can be facilitated by organic anion transporters, which are responsible for the uptake of various organic anionic compounds such as glucuronidation and sulfation drug metabolites
[29].
Furthermore, the more or less important metabolic pathway of SGLT2 inhibitors via oxidative reactions occurred, e.g., for BEXA, DAPA, ERTU, LUSE, and TOFO. Such metabolic pathways, e.g., ω-hydroxylation at the ethoxy group followed by oxidation to form the corresponding carboxylic acid, were shown for LUSE, leading to the formation of LUSE-M4. The metabolic pathway via oxidation of the substituents at the 4-phenyl position of BEXA, DAPA, ERTU, LUSE, and TOFO seems to also be the characteristic pattern of their metabolism. The hydroxyl metabolite TOFO-M1 undergoes further oxidation to the respective ketone metabolite TOFO-M2. The next hydroxyl metabolite, TOFO-M3, is further oxidized to the corresponding phenyl acetic acid metabolite, TOFO-M4.
Generally, both drug metabolism and drug degradation (during drug manufacturing and/or storage) can undergo similar chemical transformations. Consequently, many impurities that are generated during degradation could also be respective metabolites. Sometimes, individual metabolites as well as particular degradation products are formed or detected in small amounts, potentially with no toxicity risk. However, the goal of the present paper was to find as many such overlapping products of metabolism and chemical degradation of gliflozins as possible Thus, the metabolites and degradants formed in smaller amounts were also included. Further studies on possible degradation products of gliflozins based on their metabolic pathways should give a definitive assessment of their safety for patients. As far as such detected similarities between metabolites and degradants are concerned, the process of hydroxylation of the benzyl-phenyl or benzyl-thiophen moieties that was characteristic for metabolites of BEXA-M3, CANA-M2, DAPA-M1 and ERTU-M1 was observed during degradation of EMPA to form EMPA-D6.