| Literature DB >> 31192021 |
Chunxiu Gu1,2, Yanling Cheng1,2, Xin Zhen1, Xiaoxuan Chen1, Kaowen Zhou1,2.
Abstract
A novel method was developed for simultaneous determination of 10 progestin residues in fish by ultra-performance liquid chromatography-quadrupole-time-of-flight mass spectrometry (UPLC-Q-TOF/MS) combined with a modified quick, easy, cheap, effective, rugged, and safe (QuEChERS) method. The homogenized samples were dispersed by water, extracted with acetonitrile, and then purified by QuEChERS reagent. The concentrated analytes were detected by UPLC-Q-TOF/MS. High linearities (R 2 > 0.995) and recoveries (85.71-117.08%) at three spiked levels (5, 10, and 20 ng/g) and low relative standard deviation values (<8.83%, n = 7) and limits of detection (0.23-0.66 ng/g) were obtained. This method is simple, rapid, reliable, sensitive, and efficient and can be used for monitoring of progestin residues in fish. This method provides a strong guarantee to deal with food emergencies for the laboratory, provides technical support for the screening and quantitative detection of progesterone in fish, and provides technical support for the food safety of aquatic products.Entities:
Year: 2019 PMID: 31192021 PMCID: PMC6525950 DOI: 10.1155/2019/6426958
Source DB: PubMed Journal: J Anal Methods Chem ISSN: 2090-8873 Impact factor: 2.193
TOF parameters of 10 progestins.
| Compounds | Formula | Exact mass | Mother ions (m/z) | Daughter ions (m/z) | RT (min) |
|---|---|---|---|---|---|
| Norethisterone | C20H26O2 | 298.1933 | 299.1981 | 231.1714, 281.1876 | 4.15 |
| 17 | C21H30O3 | 330.2195 | 331.2245 | 313.2140, 295.200 | 4.64 |
| D-methylnorethindrone | C21H28O2 | 312.2089 | 313.2142 | 245.1871, 295.2029 | 4.76 |
| 17 | C23H32O4 | 372.2301 | 373.2391 | 313.2151, 271.2095 | 4.87 |
| Megestrol | C22H30O3 | 342.2195 | 343.2242 | 325.2208, 267.1788 | 5.00 |
| Medroxyprogesterone | C22H32O3 | 344.2351 | 345.2393 | 123.0765, 327.2294 | 5.28 |
| Chlorprogestone acetate | C23H29ClO4 | 404.1754 | 405.1806 | 309.1852, 267.1704 | 5.43 |
| Medroxyprogesterone acetate | C24H34O4 | 386.2454 | 387.2521 | 327.2306, 123.0820 | 5.50 |
| Melengestrol acetate | C25H32O4 | 396.2301 | 397.2343 | 279.1719, 337.2200 | 5.59 |
| Progesterone | C21H30O2 | 314.2246 | 315.2287 | 109.0609, 297.2179 | 5.64 |
Figure 1TOF mass spectrogram of 10 progestin standard solutions.
Regression equations, correlation coefficients (R2), LOD, and LOQ of 10 progestins.
| Compounds | Linear equations |
| LOD (ng/g) | LOQ (ng/g) |
|---|---|---|---|---|
| Norethisterone |
| 0.995 | 0.23 | 0.77 |
| 17 |
| 0.999 | 0403 | 1.77 |
| D-methylnorethindrone |
| 0.995 | 0.52 | 1.72 |
| 17 |
| 0.997 | 0.34 | 1.12 |
| Megestrol |
| 0.999 | 0.66 | 2.20 |
| Medroxyprogesterone |
| 0.999 | 0.27 | 0.91 |
| Chlorprogestone acetate |
| 0.997 | 0.32 | 1.05 |
| Medroxyprogesterone acetate |
| 0.998 | 0.37 | 1.22 |
| Melengestrol acetate |
| 0.998 | 0.52 | 1.73 |
| Progesterone |
| 0.999 | 0.28 | 0.92 |
Recoveries and relative standard deviations (%) of 10 progestins in fish (n = 7).
| Spiked level compounds | 5 ng/g | 10 ng/g | 20 ng/g | |||
|---|---|---|---|---|---|---|
| Recoveries | RSDs | Recoveries | RSDs | Recoveries | RSDs | |
| Norethisterone | 88.55 | 5.49 | 85.85 | 4.12 | 87.97 | 5.25 |
| 17 | 88.15 | 5.02 | 85.71 | 6.81 | 102.43 | 7.95 |
| D-methylnorethindrone | 105.44 | 5.68 | 88.40 | 4.30 | 90.16 | 6.48 |
| 17 | 91.73 | 3.83 | 95.71 | 4.01 | 108.96 | 6.18 |
| Megestrol | 88.66 | 7.60 | 86.58 | 6.88 | 87.79 | 6.60 |
| Medroxyprogesterone | 104.84 | 4.69 | 103.81 | 3.40 | 89.77 | 6.30 |
| Chlorprogestone acetate | 96.42 | 7.95 | 109.65 | 2.66 | 97.18 | 7.59 |
| Medroxyprogesterone acetate | 87.97 | 8.30 | 91.24 | 7.31 | 107.59 | 6.33 |
| Melengestrol acetate | 89.56 | 8.59 | 99.97 | 7.22 | 91.40 | 8.83 |
| Progesterone | 106.36 | 8.28 | 91.58 | 4.63 | 117.08 | 7.76 |