| Literature DB >> 32046727 |
Patharapol Piamsomboon1, Janthima Jaresitthikunchai2, Tran Quang Hung3, Sittiruk Roytrakul2, Janenuj Wongtavatchai4.
Abstract
BACKGROUND: The majority of infectious diseases of cultured fish is caused by bacteria. Rapid identification of bacterial pathogens is necessary for immediate management. The present study developed a custom Main Spectra Profile (MSP) database and validate the method using matrix-assisted laser desorption/ionization time-of-flight mass spectrometry (MALDI-TOF MS) for rapid identification of fish bacterial pathogens. Streptococcus agalactiae, Streptococcus iniae, Aeromonas hydrophila, Aeromonas veronii, and Edwardsiella tarda obtained from diseased fish were used as representative bacterial pathogens in this study. Bacterial peptides were extracted to create a Main Spectra Profile (MSP), and the MSPs of each bacterial species was added into the MALDI Biotyper database. Fifteen additional isolates of each bacterial species were tested to validate the utilized technique.Entities:
Keywords: Biotyper; Fish disease; Mass spectrometry; Proteomic
Year: 2020 PMID: 32046727 PMCID: PMC7014616 DOI: 10.1186/s12917-020-2274-1
Source DB: PubMed Journal: BMC Vet Res ISSN: 1746-6148 Impact factor: 2.741
Fig. 1Mass peptide fingerprints of five bacterial pathogens (S. agalactiae, S. iniae, A. hydrophila, A. veronii and E. tarda) isolated from cultured fish
Fig. 2Cluster analysis of the five bacterial pathogens (S. agalactiae, S. iniae, A. hydrophila, A. veronii and E. tarda) isolated from cultured fish. a The 3D-PCA scatterplot representing clusters of each species (dashed circles) and the (b) MSP dendrogram of the representative bacterial isolates analyzed in the present study with the reference ATCC strains
Method validation of the MALDI Biotyper of five bacterial pathogens showing the matching results with the 16 s rDNA sequencing, custom MSP and Bruker MSP database. The identity was calculated against NCBI database
| Isolate number | Source | 16S rDNA sequencing | MALDI-TOF | ||||
|---|---|---|---|---|---|---|---|
| Custom MSP database | Bruker MSP database | ||||||
| Organism best match | % identity | Organism best match | Log score | Organism best match | Log score | ||
| S147-Ja | Nile tilapia | 100 | 2.999 | 1.877 | |||
| S183-Ja | Red tilapia | 100 | 2.897 | 1.665 | |||
| S187-Ja | Nile tilapia | 99 | 2.988 | 1.545 | |||
| S190-Ja | Red tilapia | 99 | 2.856 | 1.998 | |||
| SV1/1-Ja | Nile tilapia | 100 | 2.945 | 2.019 | |||
| S71 | Red tilapia | 99 | 2.244 | 1.666 | |||
| S96 | Red tilapia | 100 | 2.377 | 1.756 | |||
| S100 | Nile tilapia | 99 | 2.442 | 1.582 | |||
| S101 | Nile tilapia | 99 | 2.375 | 1.829 | |||
| S102 | Nile tilapia | 98 | 2.544 | 1.876 | |||
| S183 | Red tilapia | 100 | 2.388 | 1.716 | |||
| S184 | Red tilapia | 100 | 2.591 | 1.749 | |||
| S191 | Red tilapia | 99 | 2.347 | 1.564 | |||
| S195 | Nile tilapia | 97 | 2.455 | 1.632 | |||
| S198 | Nile tilapia | 99 | 2.544 | 1.908 | |||
| NS12-Ja | Red tilapia | 100 | 2.898 | 1.432 | |||
| NS70-Ja | Nile tilapia | 100 | 2.988 | 1.688 | |||
| NS74-Ja | Barramundi | 100 | 2.878 | 1.987 | |||
| NS76-Ja | Barramundi | 99 | 2.999 | 1.555 | |||
| NS185-Ja | Barramundi | 99 | 2.778 | 1.654 | |||
| NS11 | Nile tilapia | 98 | 2.376 | 1.997 | |||
| NS18 | Nile tilapia | 100 | 2.419 | 1.707 | |||
| NS26 | Red tilapia | 99 | 2.534 | 1.728 | |||
| NS34 | Barramundi | 96 | 2.544 | 1.886 | |||
| NS50 | Barramundi | 97 | 2.308 | 1.679 | |||
| NS84 | Barramundi | 98 | 2.118 | 1.679 | |||
| NS85 | Barramundi | 98 | 2.445 | 1.864 | |||
| NS89 | Red tilapia | 99 | 2.342 | 1.975 | |||
| NS90 | Red tilapia | 100 | 2.221 | 1.873 | |||
| NS91 | Nile tilapia | 100 | 2.464 | 1.593 | |||
| A28-Ja | Nile tilapia | 100 | 2.978 | 1.495 | |||
| A29-Ja | Hybrid catfish | 100 | 2.991 | 1.767 | |||
| A49-Ja | Red tilapia | 100 | 2.965 | 1.869 | |||
| A50-Ja | Nile tilapia | 100 | 2.889 | 2.094 | |||
| A84-Ja | Snakehead fish | 100 | 2.945 | 1.755 | |||
| A90 | Nile tilapia | 99 | 2.312 | 2.018 | |||
| A108 | Hybrid catfish | 100 | 2.464 | 1.956 | |||
| A109 | Red tilapia | 100 | 2.115 | 1.848 | |||
| A110 | Snakehead fish | 98 | 2.394 | 2.181 | |||
| A112 | Snakehead fish | 98 | 2.601 | 2.011 | |||
| A114 | Nile tilapia | 97 | 2.451 | 1.995 | |||
| A115 | Nile tilapia | 97 | 2.551 | 2.045 | |||
| A120 | Hybrid catfish | 99 | 2.009 | 1.454 | |||
| A126 | Snakehead fish | 100 | 2.567 | 1.777 | |||
| A127 | Snakehead fish | 99 | 2.301 | 1.985 | |||
| SB1-Ja | Nile tilapia | 100 | 2.969 | 1.559 | |||
| SB2-Ja | Nile tilapia | 99 | 3.000 | 1.997 | |||
| SB3-Ja | Barramundi | 99 | 2.897 | 1.787 | |||
| SB4-Ja | Barramundi | 100 | 2.888 | 1.945 | |||
| SB7-Ja | Red tilapia | 98 | 2.899 | 1.658 | |||
| SB5 | Nile tilapia | 98 | 2.327 | 2.027 | |||
| SB6 | Nile tilapia | 100 | 2.454 | 1.787 | |||
| SB8 | Barramundi | 98 | 2.382 | 1.844 | |||
| SB9 | Barramundi | 98 | 2.511 | 1.906 | |||
| SB10 | Barramundi | 97 | 2.377 | 1.733 | |||
| SB12 | Barramundi | 100 | 2.401 | 1.667 | |||
| SB13 | Barramundi | 99 | 2.359 | 1.872 | |||
| SB14 | Barramundi | 97 | 2.228 | 1.560 | |||
| SB15 | Barramundi | 100 | 2.553 | 1.924 | |||
| SB17 | Barramundi | 100 | 2.198 | 1.855 | |||
| Ed10-Ja | Hybrid catfish | 100 | 2.899 | 2.000 | |||
| Ed12-Ja | Hybrid catfish | 100 | 2.932 | 1.887 | |||
| Ed14-Ja | Nile tilapia | 99 | 2.984 | 1.666 | |||
| Ed16-Ja | Nile tilapia | 98 | 3.000 | 1.669 | |||
| Ed18-Ja | Nile tilapia | 100 | 2.999 | 1.842 | |||
| Ed8 | Hybrid catfish | 99 | 2.382 | 1.584 | |||
| Ed9 | Hybrid catfish | 100 | 2.367 | 1.624 | |||
| Ed11 | Hybrid catfish | 98 | 2.203 | 1.782 | |||
| Ed17 | Nile tilapia | 99 | 2.471 | 1.977 | |||
| Ed20 | Nile tilapia | 100 | 2.457 | 1.945 | |||
| Ed23 | Hybrid catfish | 98 | 2.457 | 2.254 | |||
| Ed25 | Hybrid catfish | 100 | 2.342 | 1.963 | |||
| Ed27 | Nile tilapia | 100 | 2.264 | 2.014 | |||
| Ed30 | Nile tilapia | 100 | 2.445 | 2.002 | |||
| Ed31 | Nile tilapia | 100 | 2.116 | 1.956 | |||
aIsolate used for MSP database construction
log score values: < 1.700 = no reliable identification, ≥ 1.700–1.999 = probable genus-level identification, 2.000–2.229 = a secure genus-level identification and a probable species-level identification, and 2.300–3.000 = a secure species-level identification and highly probable species-level identification
Comparison of the test results for bacterial species identification using a custom MSP database and Bruker database
| Pathogen | MSP database | No. of isolate matched with 16 s rDNA sequencing (%) | Mean log score ± SD (Min - Max) |
|---|---|---|---|
| Custom | 15/15 (100%) | 2.599 ± 0.26 (2.244–2.999) | |
| Bruker | 9/15 (60%) | 1.758 ± 0.15 (2.545–2.019) | |
| Custom | 15/15 (100%) | 2.554 ± 0.25 (2.118–2.999) | |
| Bruker | 0/15 (0%) | 1.753 ± 0.17 (1.432–1.997) | |
| Custom | 15/15 (100%) | 2.568 ± 0.22 (2.009–2.991) | |
| Bruker | 6/15 (40%) | 1.883 ± 0.20 (1.454–2.181) | |
| Custom | 15/15 (100%) | 2.562 ± 0.25 (2.198–3.000) | |
| Bruker | 7/15 (46.67%) | 1.808 ± 0.14 (1.559–2.027) | |
| Custom | 15/15 (100%) | 2.554 ± 0.24 (2.116–3.000) | |
| Bruker | 10/15 (66.67%) | 1.877 ± 0.18 (1.584–2.254) | |
| Total | Custom | 75/75 (100%) | 2.568 ± 0.25 (2.009–3.000) |
| Bruker | 32/75 (42.67%) | 1.816 ± 0.17 (1.432–2.254) |
Bacterial pathogens used for the development the custom MSP database. The isolates were obtained from cultured Nile tilapia Oreochromis niloticus, red tilapia Oreochromis spp., barramundi Lates calcarifer, hybrid catfish Clarias macrocephalus × C. gariepinus, and Snakehead fish Channa striata
| Bacterial species | Isolate number | Year | Source | Region |
|---|---|---|---|---|
| S147-J | 2013 | Nile tilapia | Western Thailand | |
| S183-J | 2015 | Red tilapia | Central Thailand | |
| S187-J | 2017 | Nile tilapia | Eastern Thailand | |
| S190-J | 2018 | Red tilapia | Southern Thailand | |
| SV1/1-J | 2018 | Nile tilapia | Northern Vietnam | |
| NS12-J | 2007 | Red tilapia | Northeastern Thailand | |
| NS70-J | 2012 | Nile tilapia | Northeastern Thailand | |
| NS74-J | 2014 | Barramundi | Eastern Thailand | |
| NS76-J | 2014 | Barramundi | Eastern Thailand | |
| NS185-J | 2018 | Barramundi | Eastern Thailand | |
| A28-J | 2011 | Nile tilapia | Eastern Thailand | |
| A29-J | 2011 | Hybrid catfish | Eastern Thailand | |
| A49-J | 2013 | Red tilapia | Central Thailand | |
| A50-J | 2015 | Nile tilapia | Eastern Thailand | |
| A84-J | 2017 | Snakehead fish | Central Thailand | |
| SB1-J | 2017 | Nile tilapia | Eastern Thailand | |
| SB2-J | 2017 | Nile tilapia | Eastern Thailand | |
| SB3-J | 2018 | Barramundi | Eastern Thailand | |
| SB4-J | 2019 | Barramundi | Eastern Thailand | |
| SB7-J | 2019 | Red tilapia | Eastern Thailand | |
| Ed10-J | 2012 | Hybrid catfish | Central Thailand | |
| Ed12-J | 2013 | Hybrid catfish | Central Thailand | |
| Ed14-J | 2015 | Nile tilapia | Eastern Thailand | |
| Ed16-J | 2016 | Nile tilapia | Eastern Thailand | |
| Ed18-J | 2017 | Nile tilapia | Central Thailand |