| Literature DB >> 29404043 |
Prashant S Devrukhakar1, M Shiva Shankar1, G Shankar2, R Srinivas2.
Abstract
Zidvovudine (AZT) is a nucleoside analogue reverse transcriptase inhibitor (NRTI), a class of anti-retroviral drug. A stability-indicating assay method for AZT was developed in line with ICH guideline. Successful separation of AZT and its degradation products was achieved by gradient elution mode on reverse phase C18 column using 10 mM ammonium acetate: acetonitrile as the mobile phase at 0.8 mL/min flow rate, 25 µL injection volume, 30 °C column temperature and 285 nm detection wavelength. Two major acid degradation products were identified and characterized by liquid chromatography-electrospray ionization mass spectrometry (LC-ESI/MS/MS) and accurate mass measurements. The probable mechanisms for the formation of degradation products were identified based on a comparison of the fragmentation pattern of the [M + H] + ions of AZT and its degradation products. One of the degradation products, DP-1, was isolated by semi-preparative high performance liquid chromatography (HPLC) using Waters XBridge Prep C18 (250 mm×10 mm, 5 µm). Degradation products showed higher toxicity compared to the drug in some models assessed by TOPKAT software. The method validation was performed with respect to robustness, specificity, linearity, precision and accuracy as per ICH guideline Q2 (R1).Entities:
Keywords: Degradation pathway; Degradation products; In-silico toxicity prediction; LC–ESI/MS/MS; Stability study; Zidvovudine
Year: 2017 PMID: 29404043 PMCID: PMC5790685 DOI: 10.1016/j.jpha.2017.01.006
Source DB: PubMed Journal: J Pharm Anal ISSN: 2214-0883
Recovery data of AZT (n=3).
| Spiked concentration (ng/mL) | Found concentration | RSD | Recovery |
|---|---|---|---|
| (ng/mL, Mean±SD) | (%) | (%) | |
| 10 | 10.10±0.193 | 1.91 | 101.0 |
| 30 | 29.81±0.493 | 1.65 | 99.4 |
| 50 | 50.32±0.650 | 1.29 | 100.6 |
Precision study of the developed method for AZT (n=3).
| Concentration (ng/mL) | Intra-day precision | Inter-day precision | ||
|---|---|---|---|---|
| Found concentration | RSD | Found concentration | RSD | |
| (ng/mL, Mean±SD) | (%) | (ng/mL, Mean±SD) | (%) | |
| 10 | 9.83±0.05 | 0.51 | 9.80±0.10 | 1.02 |
| 20 | 19.70±0.10 | 0.51 | 19.80±0.10 | 0.51 |
| 40 | 39.69±0.21 | 0.53 | 39.84±0.16 | 0.40 |
| 80 | 79.87±0.22 | 0.28 | 79.65±0.10 | 0.13 |
| 100 | 99.87±0.29 | 0.29 | 99.74±0.22 | 0.22 |
Fig. 1Chromatogram of AZT (2 mg/mL).
Fig. 2Chromatogram of acid degradation products.
Scheme 1Proposed structures of protonated degradation products of AZT formed under various stress conditions.
Elemental compositions of AZT and its degradation products.
| Degradation product | Retention time (min) | Molecular formula [M+H] | Calculated | Observed | Error (ppm) | MS/MS fragment ions |
|---|---|---|---|---|---|---|
| AZT | 11.7 | C10H14N5O4+ | 268.1040 | 268.1052 | −4.5 | 227, 127 |
| DP−1 | 2.8 | C5H17N2O2+ | 127.0502 | 127.0498 | 3.1 | 127 |
| DP−2 | 12.0 | C10H15N2O4+ | 227.1026 | 227.1016 | 4.4 | 127 |
Scheme 2Proposed fragmentation pathway of protonated AZT.
Fig. 3ESI/MS/MS spectrum of AZT.
Fig. 4ESI/MS/MS spectrum of degradation product 1 (m/z 127).
Scheme 3Probable mechanism of formation of degradation product 2 (m/z 227).
Scheme 4Proposed fragmentation pathway of protonated degradation product 2 (m/z 227).
Fig. 5ESI/MS/MS spectrum of degradation product 2 (m/z 227).
Fig. 61H NMR of degradation product 1 (m/z 127).
Probable values of degradation products in different toxicity models by TOPKAT analysis.
| Model | DP-1 | DP-2 |
|---|---|---|
| NTP Carcinogenicity Call (Male Rat) (v3.2) | ||
| NTP Carcinogenicity Call (Female Rat) (v3.2) | 0.063 | 0.004 |
| NTP Carcinogenicity Call (Male Mouse) (v3.2) | ||
| NTP Carcinogenicity Call (Female Mouse) (v3.2) | 0.00 | 0.040 |
| FDA Carcinogenicity Male Rat Non vsCarc (v3.1) | 0.000 | |
| FDA Carcinogenicity Male Rat Single vsMult (v3.1) | ||
| FDA Carcinogenicity Female Rat Non vsCarc (v3.1) | 0.001 | 0.00 |
| FDA Carcinogenicity Female Rat Single vsMult (v3.1) | 0.001 | |
| FDA Carcinogenicity Male Mouse Non vsCarc (v3.1) | 0.002 | 0.004 |
| FDA Carcinogenicity Male Mouse Single vsMult (v3.1) | 0.000 | |
| FDA Carcinogenicity Female Mouse Non vsCarc (v3.1) | ||
| FDA Carcinogenicity Female Mouse Single vsMult (v3.1) | ||
| Weight of Evidence Carcinogenicity Call (v5.1) | 0.303 | |
| Ames Mutagenicity (v3.1) | 0.000 | |
| Developmental Toxicity Potential (DTP) (v3.1) | ||
| Rat Oral LD 50 (v3.1) (g/kg) | 1.8 | 391.0 |
| Rat Maximum Tolerated Dose - Feed/Water (v6.1) | 6.7 mg/kg | 4.4 g/kg |
| Rat Inhalational LC 50 (v6.1) (g/m3/H) | 4.7 | 10 |
| Chronic LOAEL (v3.1) (mg/kg) | 891.2 | 292.9 |
| Skin Irritation (v6.1) | 0.422 | 0.954 |
| Skin Sensitization NEG v SENS (v6.1) | ||
| Skin Sensitization MLD/MOD v SEV (v6.1) | 0.002 | 0.000 |
| Ocular Irritancy SEV/MOD vs MLD/NON (v5.1) | 0.046 | 0.000 |
| Ocular Irritancy SEV vs MOD (v5.1) | 0.000 | 0.000 |
| Ocular Irritancy MLD vs NON (v5.1) | 0.150 | 0.000 |
| Aerobic Biodegradability (v6.1) | 0.000 | |
| Daphnia EC50 (v3.1) | 147.8 mg/L | 39.7 g/L |
Note: Data in bold indicate the severity of toxicity for both degradation products in respective model.