| Literature DB >> 35062644 |
Binbin Guan1,2, Wencui Kang2, Hao Jiang2, Mi Zhou1, Hao Lin2.
Abstract
Volatile organic compounds (VOCs) could be used as an indicator of the freshness of oysters. However, traditional characterization methods for VOCs have some disadvantages, such as having a high instrument cost, cumbersome pretreatment, and being time consuming. In this work, a fast and non-destructive method based on colorimetric sensor array (CSA) and visible near-infrared spectroscopy (VNIRS) was established to identify the freshness of oysters. Firstly, four color-sensitive dyes, which were sensitive to VOCs of oysters, were selected, and they were printed on a silica gel plate to obtain a CSA. Secondly, a charge coupled device (CCD) camera was used to obtain the "before" and "after" image of CSA. Thirdly, VNIS system obtained the reflected spectrum data of the CSA, which can not only obtain the color change information before and after the reaction of the CSA with the VOCs of oysters, but also reflect the changes in the internal structure of color-sensitive materials after the reaction of oysters' VOCs. The pattern recognition results of VNIS data showed that the fresh oysters and stale oysters could be separated directly from the principal component analysis (PCA) score plot, and linear discriminant analysis (LDA) model based on variables selection methods could obtain a good performance for the freshness detection of oysters, and the recognition rate of the calibration set was 100%, while the recognition rate of the prediction set was 97.22%. The result demonstrated that the CSA, combined with VNIRS, showed great potential for VOCS measurement, and this research result provided a fast and nondestructive identification method for the freshness identification of oysters.Entities:
Keywords: colorimetric sensor array; oysters; storage time; variable screening; visible near-infrared spectroscopy
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Year: 2022 PMID: 35062644 PMCID: PMC8781135 DOI: 10.3390/s22020683
Source DB: PubMed Journal: Sensors (Basel) ISSN: 1424-8220 Impact factor: 3.576
Figure 120 color-sensitive materials were dissolved in DMF (a) and a 4 × 5 colorimetric sensor array (b).
Figure 2The schematic diagram of colorimetric sensor array system (a), visible near-infrared spectroscopy system (b) and difference map acquisition of oysters (c).
The difference value of 20 color-sensitive materials after exposed to the oysters’ VOCs.
| Color-Sensitive Materials | |||
|---|---|---|---|
| 2,3,7,8,12,13,17,18-Octaethyl-21H,23H-porphine manganese(III) chloride | 3.51 ± 2.31 | 13.44 ± 1.66 | 2.28 ± 1.32 |
| 5,10,15,20-Tetrakis(4-methoxyphenyl)-21H,23H-porphine iron(III) chloride | 3.69 ± 3.99 | 3.99 ± 1.46 | 3.12 ± 1.28 |
| 5,10,15,20-Tetraphenyl-21H,23H-porphine iron(III) chloride | 4.17 ± 4.45 | 2.62 ± 0.91 | 2.75 ± 1.38 |
| 5,10,15,20-tetra(4-methoxyphenyl)Porphyrin Fe(II) complex | 4.29 ± 0.81 | 3.41 ± 0.98 | 3.43 ± 1.32 |
| 5,10,15,20-Tetrakis(4-sulfonatophenyl)-21H,23H-porphine manganese(III) chloride | 3.73 ± 0.54 | 4.57 ± 2.12 | 3.04 ± 1.16 |
| 5,10,15,20-Tetraphenyl-21H,23H-porphine nickel(II) | 3.35 ± 2.11 | 4.63 ± 2.47 | 4.45 ± 1.02 |
| 5,10,15,20-Tetraphenyl-21H,23H-porphine palladium(II) | 2.92 ± 0.74 | 4.96 ± 3.52 | 23.50 ± 2.94 |
| 5,10,15,20-Tetraphenyl-21H,23H-porphine palladium(II) | 2.44 ± 0.95 | 2.16 ± 0.90 | 3.36 ± 2.93 |
| meso-tetra(4-sulfonic) porphine tetrasodium dodecahydrate | 2.06 ± 0.74 | 0.78 ± 0.47 | 4.67 ± 0.82 |
| 5,10,15,20-Tetraphenyl-21H,23H-porphine cobalt(II) | 0.87 ± 0.53 | 1.37 ± 0.86 | 11.14 ± 1.07 |
| 4,4′-difluoro-8-(methyl 4-benzoate)-1,7-dimethyl-2,6-diethyl-3,5,-distyryl-(3,5-di-tert-butyl-4-hydroxyphenyl)-4-bora-3a,4a-diaza-s-indacene | 1.52 ± 0.43 | 4.10 ± 1.18 | 29.13 ± 2.24 |
| 8-(4-Carbazolephenyl)-4,4-difluoroboron dipyrromethane | 13.49 ± 1.85 | 7.15 ± 0.97 | 4.43 ± 1.05 |
| 8-(4-Nitrophenyl)-4,4-difluoro-6-bromoborin dipyrromethane | 2.66 ± 1.21 | 3.24 ± 1.73 | 10.89 ± 1.45 |
| 8-(4-Nitrophenyl)-4,4-difluoro-2,6-dibromoborin dipyrrole | 3.44 ± 0.99 | 3.58 ± 0.83 | 30.66 ± 3.20 |
| 8-(6-methoxy-2-naphthyl)-4,4-difluoroboron dipyrromethane | 2.10 ± 1.24 | 15.06 ± 3.09 | 4.26 ± 1.45 |
| Bis (8-phenyldipyrromethane) nickel(II) | 3.83 ± 0.85 | 1.15 ± 0.80 | 5.02 ± 2.19 |
| Bis [8-(4-formylformylphenyl) dipyrromethane] nickel (II) | 2.70 ± 0.62 | 7.22 ± 1.51 | 1.53 ± 2.23 |
| Bis [8-(6-methoxy-2-naphthyl)dipyrromethane] nickel(II) | 3.43 ± 0.85 | 2.72 ± 0.42 | 2.65 ± 1.20 |
| Di [8-(4-carbazolephenyl) dipyrromethane] copper(II) | 0.97 ± 0.54 | 2.34 ± 1.14 | 10.57 ± 4.75 |
| Bis [8-(4-carbazolylphenyl) dipyrromethane] zinc(II) | 1.33 ± 0.49 | 3.09 ± 0.95 | 6.43 ± 2.32 |
1 Mean ± standard.
Figure 3Color difference diagram of colorimetric sensor array before and after the reaction of the oysters’ VOCs with different storage time.
Figure 4Pattern recognition results of PCA (a), LDA (b) and KNN (c), based on colorimetric sensor array.
Figure 5Average spectrum of Doil (a), pCarBDP (b), NO2Br2BDP (c) and NaiOCH3BDP (d) after SNV pretreatment.
LDA and KNN classification results of three variable screening algorithms.
| Variable Screening Algorithms | LDA | KNN | |||||
|---|---|---|---|---|---|---|---|
| PCs | Rc | Rp | PCs | K Value | Rc | Rp | |
| ACO | 11 | 100% | 97.22% | 6 | 1 | 99.07% | 94.44% |
| CARS | 3 | 90.74% | 94.44% | 7 | 1 | 96.30% | 93.06% |
| GA | 9 | 100% | 97.22% | 11 | 1 | 99.07% | 97.22% |
Figure 6Pattern recognition results of PCA (a), LDA (b) and KNN (c) based on visible near-infrared spectroscopy data after SNV preprocessing, siPLS interval screening, and GA variable screening.