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<h1><b>Specificity of Bee T's toxin</b></h1> | <h1><b>Specificity of Bee T's toxin</b></h1> | ||
− | <p> To improve on existing methods, BeeT should affect Varroa mites only. This means it should be harmless to bees, humans and other organisms. In our search for a suitable toxin we looked into Bt toxins | + | <p> To improve on existing methods, BeeT should affect <i>Varroa<i> mites only. This means it should be harmless to bees, humans and other organisms. In our search for a suitable toxin we looked into Bt toxins, which are produced by <i>Bacillus thuringiensis<i>. Due to interaction with species specific receptors in the gut membrane, these toxins are known to be very species specific. To find a suitable Bt toxin we tried isolating <i>B. thuringiensis<i> from dead mites, as well as mutating an existing Bt toxin. For testing the potential toxins that were obtained, we employed an in vitro toxicity assay with brush-border membrane vesicles made from Varroa mite gut. The vesicles contain fluorophores. When a Bt toxin is applied that is toxic to <i>Varroa<i> mites, it recognizes the receptors on the vesicles, rupturing them and releasing the fluorophores. </p> |
Revision as of 16:41, 8 October 2016
Specificity of Bee T's toxin
To improve on existing methods, BeeT should affect Varroa mites only. This means it should be harmless to bees, humans and other organisms. In our search for a suitable toxin we looked into Bt toxins, which are produced by Bacillus thuringiensis. Due to interaction with species specific receptors in the gut membrane, these toxins are known to be very species specific. To find a suitable Bt toxin we tried isolating B. thuringiensis from dead mites, as well as mutating an existing Bt toxin. For testing the potential toxins that were obtained, we employed an in vitro toxicity assay with brush-border membrane vesicles made from Varroa mite gut. The vesicles contain fluorophores. When a Bt toxin is applied that is toxic to Varroa mites, it recognizes the receptors on the vesicles, rupturing them and releasing the fluorophores.
Toxin Engineering
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In Vitro Assay
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Varroa Isolates
Cry toxins and mites
To provide an alternative to currently available pesticides, we wanted to adopt Cry toxins. Cry toxins, also known as Bt toxins, have been used commercially for decades and can limit the environmental impact of pesticide use 1. Cry toxins are produced by the insect pathogen Bacillus thuringiensis. Their mode of action can make them highly specific to certain species of insects. They are activated by the alkaline conditions of the insect gut, after which the protoxin is cleaved off. The toxin can then recognize receptors on the gut membrane and bind to them. It will form oligomers with other toxin molecules and make a pore in the gut membrane. This is what causes the insect’s death 2.
While over 800 Cry toxins are known, research on the workings of these toxins mainly focuses on conventional pests such as coleopterans, lepidopterans and some dipteran species. Field experiments on non-target invertebrates show that Acari (mites and ticks) are not significantly affected by Bt crops3, but these use only a few known Cry toxins. Other studies have shown that there are strains of B. thuringiensis which are harmful to Acari. While most of these strains or toxins were tested against herbivorous species of mites use 4,5,6,7, some are known to kill species of ticks8,9,10,11. In fact, two strains have been discovered which show toxicity to V. destructor12,13! Unfortunately, they did not identify a particular Cry toxin.
To find our own Cry toxin, we adapted a procedure from Rampersad et al.14 and Alquisira-Ramírez et al12. We gathered over 800 dead mites from the Dutch foundation “De Duurzame Bij”15 with the help of Henk Kok, their secretary.
Our method of sample preparation selected for spore formation, but not the B. thuringiensis rod-shaped morphology. Therefore, 106 colonies from the mites were investigated with brightfield microscopy. They were stained with Coomassie Brilliant Blue to make Cry toxins more visible. Five isolates were identified as Bacillus-like species. Some of them, including Bacillus thuringiensis HD-350, are shown in Figure 1.
Testing strains for toxicity
We wanted to test the strains we identified for their toxicity to Varroa destructor. Protein extracts and SDS-PAGE were performed. The toxicity assay was based on the assay used by Alquisira-Ramírez et al.12, but we faced one major problem: the assay, including the negative control, killed all of the Varroa mites. Therefore, it was not a reliable indicator of the isolates’ toxicity to Varroa. An alternative would be to use an assay where we dip honeybee larvae in protein extracts from the strains; a Varroa mite which feeds on the larvae should then ingest any toxins. Unfortunately, Varroa mites tend to share feeding sites and use them repeatedly16, which means that not all mites would consume the protein extract.
A sample-size calculation was performed in R with the following code to assess the feasibility of such an assay.
> p=0.66
> p0=0.5
> alpha=0.05
> beta=0.1
> (n=p*(1-p)*((qnorm(1-alpha)+qnorm(1-beta))/(p-p0))^2)
Here, p is the alternative hypothesis, p0 the null hypothesis, alpha the type I error and beta the type II error. The values of these variables were based on the following assumptions:
- The null hypothesis is 50% mite mortality. Natural mite mortality is very high in the laboratory.
- Linea Muhsal estimated during feeding experiments that approximately 16% of mites ingested the fluorophores she had dipped honeybee larvae in.
- If an effective Cry toxin is ingested, we expect to see 100% mite mortality. This is a very optimistic assumption.
- 16% of mites eat a toxin which causes 100% mite mortality, so if there is a toxin, we should see 66% mite mortality.
With these assumptions, a sample size of 75 was calculated. In a very good week, we were generally able to gather 40 mites. Gathering enough mites to test all our samples was deemed unfeasible. Therefore, pursuit of this type of toxicity assay was cancelled in favour of further development of an in vitro assay.
16s rRNA sequencing and SDS-PAGE results
All five isolates with Bacillus-like morphology had their 16s rRNA sequenced. A search of NCBI’s 16S ribosomal RNA sequences database resulted in the following alignments, each with approximately 99% identity of their best match:
Isolate | Best alignment |
---|---|
V46 | Bacillus licheniformis |
V47 | Paenibacillus amylolyticus |
V82 | Lysinibacillus meyeri |
V88 | Paenibacillus chitinolyticus |
V106 | Bacillus sp. |
It can be difficult to tell Bacillus species apart with just a 16s rRNA sequence17, so an SDS-PAGE gel of the protein extracts was prepared to further analyse them. This gel is shown in Figure 2.
Proteomics analysis of isolate V82
Based on the previous results, our Lysinibacillus isolate V82 was the most interesting to study. It is relatively closely related to a known insect pathogen, Lysinibacillus sphaericus, a species which is known to make a 100 kDa mosquiticidal toxin 18. Our isolate also showed a strong band at the 100 kDa region (Figure 2). A new SDS-PAGE gel was prepared with independently grown V82 cultures and bands were cut out for peptide extraction, so the 100 kDa protein could be analysed with LC-MS/MS. MaxQuant was used to analyze the data.
Analysis of the LC-MS/MS results resulted in Figure 4. Figure 4 is a vulcano plot; the x-axis plots the protein abundance ratio between the 100 kDa band and its respective control band, while the y-axis plots the p-value of this difference in protein abundance. Therefore, a protein in the left half of the plot is more abundant in the control bands, while the opposite goes for proteins in the right half of the plot. The higher it is on the y-axis, the more significant this difference is.
Contaminations such as keratins and the trypsin used to digest the samples should not differ significantly between the samples. This is also shown in Figure 4 as most contaminants (the blue points) are present in the bottom half of the vulcano plot. The relative label-free quantification (LFQ) intensity of the significant proteins shown in Figure 4 was very low, in all cases lower than the LFQ intensity of trypsin. From a biological perspective, this makes sense; there is no reason for an organism to produce mass amounts of alanine tRNA ligase. However, this and the fact that only 3% of peptides could be matched indicates that the 100 kDa protein was not present in the prepared Lysinibacillus sequence database. Therefore, the peptides were also matched against a Bacillus database, but this yielded similar results. Genomic DNA was extracted from V82 and sent for sequencing so the LC-MS/MS data could be run against the isolate's own DNA. This genomic DNA was also analyzed with the Toxin Scanner.
References
References for Varroa isolates
1. Lacey, L. A., Grzywacz, D., Shapiro-Ilan, D. I., Frutos, R., Brownbridge, M., & Goettel, M. S. (2015). Insect pathogens as biological control agents: back to the future. Journal of invertebrate pathology, 132, 1-41. ↩2. de Maagd, R. A., Bravo, A., & Crickmore, N. (2001). How Bacillus thuringiensis has evolved specific toxins to colonize the insect world.TRENDS in Genetics, 17(4), 193-199. ↩
3. Marvier, M., McCreedy, C., Regetz, J., & Kareiva, P. (2007). A meta-analysis of effects of Bt cotton and maize on nontarget invertebrates.science, 316(5830), 1475-1477. ↩
4. Ahmed, N., Wang, M., & Shu, S. (2016). Effect of commercial Bacillus thuringiensis toxins on Tyrophagus putrescentiae (Schrank) fed on wolfberry (Lycium barbarum L.). International Journal of Acarology, 42(1), 1-6. ↩
5. Chapman, M. H., & Hoy, M. A. (1991). Relative toxicity of Bacillus thuringiensis var. tenebrionis to the two‐spotted spider mite (Tetranychus urticae Koch) and its predator Metaseiulus occidentalis (Nesbitt)(Acari, Tetranychidae and Phytoseiidae). Journal of Applied Entomology, 111(1‐5), 147-154. ↩
6. Dunstand-Guzmán, E., Peña-Chora, G., Hallal-Calleros, C., Pérez-Martínez, M., Hernández-Velazquez, V. M., Morales-Montor, J., & Flores-Pérez, F. I. (2015). Acaricidal effect and histological damage induced by Bacillus thuringiensis protein extracts on the mite Psoroptes cuniculi. Parasites & vectors, 8(1), 1. ↩
7. Erban, T., Nesvorna, M., Erbanova, M., & Hubert, J. (2009). Bacillus thuringiensis var. tenebrionis control of synanthropic mites (Acari: Acaridida) under laboratory conditions. Experimental and Applied Acarology, 49(4), 339-346. ↩
8. Fernández-Ruvalcaba, M., Peña-Chora, G., Romo-Martínez, A., Hernández-Velázquez, V., de la Parra, A. B., & De La Rosa, D. P. (2010). Evaluation of Bacillus thuringiensis pathogenicity for a strain of the tick, Rhipicephalus microplus, resistant to chemical pesticides. Journal of Insect Science, 10(1), 186. ↩
9. Hassanain, M. A., Garhy, M. E., Abdel-Ghaffar, F. A., El-Sharaby, A., & Megeed, K. N. A. (1997). Biological control studies of soft and hard ticks in Egypt. Parasitology research, 83(3), 209-213. ↩
10. Neethu, K. B., Priji, P., Unni, K. N., Sajith, S., Sreedevi, S., Ramani, N., ... & Benjamin, S. (2015). New Bacillus thuringiensis strain isolated from the gut of Malabari goat is effective against Tetranychus macfarlanei. Journal of Applied Entomology. ↩
11. Zhioua, E., Heyer, K., Browning, M., Ginsberg, H. S., & LeBrun, R. A. (1999). Pathogenicity of Bacillus thuringiensis variety kurstaki to Ixodes scapularis (Acari: Ixodidae). Journal of medical entomology, 36(6), 900-902. ↩
12. Neethu, K. Alquisira-Ramírez, E. V., Paredes-Gonzalez, J. R., Hernández-Velázquez, V. M., Ramírez-Trujillo, J. A., & Peña-Chora, G. (2014). In vitro susceptibility of varroa destructor and Apis mellifera to native strains of Bacillus thuringiensis. Apidologie, 45(6), 707-718. ↩
13. Tsagou, V., Lianou, A., Lazarakis, D., Emmanouel, N., & Aggelis, G. (2004). Newly isolated bacterial strains belonging to Bacillaceae (Bacillus sp.) and Micrococcaceae accelerate death of the honey bee mite, varroa destructor (V. jacobsoni), in laboratory assays. Biotechnology letters, 26(6), 529-532. ↩
14. Rampersad, J., & Ammons, D. (2005). A Bacillus thuringiensis isolation method utilizing a novel stain, low selection and high throughput produced atypical results. BMC microbiology, 5(1), 1. ↩
15. This is the homepage of “De Duurzame Bij”. They want to stop treating Varroa with pesticides. ↩
16. Kanbar, G., & Engels, W. (2005). Communal use of integumental wounds in honey bee (Apis mellifera) pupae multiply infested by the ectoparasitic mite Varroa destructor. Genetics and Molecular Research, 4(3), 465-472. ↩
17. Bavykin, S. G., Lysov, Y. P., Zakhariev, V., Kelly, J. J., Jackman, J., Stahl, D. A., & Cherni, A. (2004). Use of 16S rRNA, 23S rRNA, and gyrB gene sequence analysis to determine phylogenetic relationships of Bacillus cereus group microorganisms. Journal of clinical microbiology, 42(8), 3711-3730. ↩
18. Berry, C. (2012). The bacterium, Lysinibacillus sphaericus, as an insect pathogen. Journal of invertebrate pathology, 109(1), 1-10. ↩