| Literature DB >> 35884259 |
Yi-Kuan Lu1,2,3, Di Xu1,2,3, Wen-Yue Liu1,2,3, Jing Xie1,2,3, Ying Lu1,2,3.
Abstract
In this research, we designed a rapid tricolour immunochromatographic test strip with double test lines (TS-DTL) and two-colour AuNP probes, which realised the simultaneous detection of tricaine mesylate (TMS) and malachite green (MG). Through a distinct tricolour system (red T1 line, blue T2 line and purple C line), a visual identification of TMS (0.2 μg/mL) and MG (0.5 μg/mL) was quickly achieved on site, which improved the accuracy of naked eye observations. The LODs of TMS in aquaculture water, fish and shrimp were 11.0, 29.6 and 61.4 ng/mL, respectively. MG LODs were 47.0 ng/mL (aquaculture water), 82.8 ng/mL (fish) and 152.4 ng/mL (shrimp). The LOD of MG was close to the similar TS methods. However, visual detection of TMS could meet the requirements of the residue limit (1 μg/mL) of TMS in the USA, and the quantitative detection of TMS was over 16 times lower than the USA standard. The developed platform was rapid (~20 min, HPLC~3 h) and accurate, which was verified using a traditional HPLC method. The recovery rates ranged from 82.2% to 108.6% in three types of real samples, indicating a potential application in on-site fast screening or multiple detection for TMS and MG residues in aquatic products.Entities:
Keywords: Au nanoparticles; malachite green; simultaneous detection; tricaine mesylate; tricolour test strip
Mesh:
Substances:
Year: 2022 PMID: 35884259 PMCID: PMC9312490 DOI: 10.3390/bios12070456
Source DB: PubMed Journal: Biosensors (Basel) ISSN: 2079-6374
Scheme 1Schematic diagram of simultaneous detection for TMS and MG based on a test strip with double T lines (TS-DTL). (A) Schematic illustration of two-colour AuNP probes and TS-DTL. (B) Working principles for the tricolour test strip platform for simultaneous qualitative and quantitative detection of TMS and MG.
Figure 1Characterisation of the optical properties, shapes and sizes of red and blue AuNPs. (A,B) UV–vis absorption spectra of two-colour AuNPs. Inset: the relevant photographic images of the synthesised AuNP solution. (C,D) TEM images. Inset: the structural diagrammatic presentation of synthesised AuNPs. (E,F) Hydrodynamic diameter. PDI indicates the polydispersity index.
Figure 2Optimisation results of different conditions. (A) Loading buffer solution. (B) Concentration of coating antigens of TMS-BSA and MG-BSA. (C) The amount of mAbs used to prepare AuNP probes for TMS and MG. (D) Single detection sensitivity of TS-DTL, (left) for TMS, (right) for MG. ★: Red and blue pentagrams indicate the qualitative limit of TMS and MG, respectively.
Figure 3Specificity evaluation of TS-DTL for the detection of TMS and MG. (A) Specificity test of TMS and 6 other anaesthetics; (B) Specificity test of MG and 6 other dyes.
Figure 4Simultaneous detection of TMS and MG in spiked samples with TS-DTL. Qualitative detection for aquaculture water (A), fish (B) and shrimp (C). Calibration curves of TMS and MG in aquaculture water (D), fish (E) and shrimp (F).
Comparison of various methods for the quantitative detection of TMS and MG.
| Analyte | Method | Label Material | LOD | Cost-Time | Sample | Reference |
|---|---|---|---|---|---|---|
| TMS | HPLC | / | 25 ng/mL | 6 h | fish | [ |
| HPLC–MS/MS | / | 2.5 ng/mL | 3.0 h | fish | [ | |
| HPLC–MS/MS | / | 0.01 ng/mL | 1.0 h | water | [ | |
| ICTS | AuNPs | <0.1 μg/mL | 15 min | fish | [ | |
| TS-DTL | Two-colour AuNPs | 11.0 ng/mL | 15~20 min | aquaculture water | This work | |
| 29.6 ng/g | fish | |||||
| 61.4 ng/g | shrimp | |||||
| MG | ICTS | Orange carbon dots | 58.4 ng/g | 10 min | fish | [ |
| ICTS | AuNPs | 1 ng/mL | 8 min | fish | [ | |
| Fluorescence | Se,N,Cl-doped carbon dots | 339.37 ng/mL | 1.5 h | fish | [ | |
| assay | ||||||
| ELISA | / | 0.31 ng/mL | 6 h | fish | [ | |
| Colorimetry | AuNPs | 5 ng/mL | 25 min | fish | [ | |
| L-Aptamer | / | 17.4 ng/mL | 2 h | fish | [ | |
| TS-DTL | Two-colour AuNPs | 47.0 ng/mL | 15~20 min | aquaculture water | This work | |
| 82.8 ng/mL | fish | |||||
| 152.4 ng/mL | shrimp |
Recovery evaluation of aquaculture water by the developed TS-DTL and HPLC methods.
| Sample | Target | Spiked | TS-DTL | HPLC | ||||
|---|---|---|---|---|---|---|---|---|
| Found (μg/mL) | Recovery | CV | Found | Recovery | CV | |||
| aquaculture water | TMS | 0.1 | 0.094 | 94.2 | 7.51 | 0.11 | 110.0 | 3.56 |
| 1 | 1.07 | 107.3 | 8.43 | 1.05 | 105.3 | 4.23 | ||
| 2 | 1.91 | 95.5 | 6.44 | 2.06 | 103.0 | 3.51 | ||
| 5 | 4.62 | 92.4 | 9.68 | 5.11 | 102.2 | 4.22 | ||
| MG | 0.1 | 0.082 | 82.3 | 7.02 | 0.11 | 110.1 | 5.16 | |
| 1 | 0.92 | 92.4 | 7.93 | 1.01 | 101.4 | 3.92 | ||
| 2 | 1.83 | 91.5 | 5.48 | 1.96 | 98.0 | 4.10 | ||
| 5 | 4.67 | 93.4 | 8.70 | 4.79 | 95.8 | 3.95 |
Recovery evaluation in aquatic products by the developed TS-DTL and HPLC methods.
| Sample | Target | Spiked | TS-DTL | HPLC | ||||
|---|---|---|---|---|---|---|---|---|
| Found | Recovery | CV | Found | Recovery | CV | |||
| fish | TMS | 0.1 | 0.094 | 94.2 | 7.51 | 0.11 | 110.0 | 3.56 |
| 1 | 1.07 | 107.3 | 8.43 | 1.05 | 105.3 | 4.23 | ||
| 2 | 1.91 | 95.5 | 6.44 | 2.06 | 103.0 | 3.51 | ||
| 5 | 4.62 | 92.4 | 9.68 | 5.11 | 102.2 | 4.22 | ||
| MG | 0.1 | 0.082 | 82.3 | 7.02 | 0.11 | 110.1 | 5.16 | |
| 1 | 0.92 | 92.4 | 7.93 | 1.01 | 101.4 | 3.92 | ||
| 2 | 1.83 | 91.5 | 5.48 | 1.96 | 98.0 | 4.10 | ||
| 5 | 4.67 | 93.4 | 8.70 | 4.79 | 95.8 | 3.95 | ||
| shrimp | TMS | 0.1 | 0.085 | 85.4 | 13.27 | 0.102 | 102.0 | 4.76 |
| 1 | 0.94 | 94.0 | 9.23 | 0.936 | 93.6 | 5.37 | ||
| 2 | 2.07 | 103.5 | 8.63 | 1.89 | 94.5 | 4.87 | ||
| 5 | 5.43 | 108.6 | 8.37 | 4.77 | 95.4 | 5.21 | ||
| MG | 0.1 | 0.082 | 82.3 | 11.41 | 0.88 | 88.8 | 5.67 | |
| 1 | 0.88 | 87.6 | 12.56 | 0.92 | 92.0 | 4.88 | ||
| 2 | 1.85 | 92.5 | 9.24 | 1.96 | 97.9 | 3.96 | ||
| 5 | 4.24 | 84.8 | 7.31 | 4.22 | 84.3 | 4.63 | ||