Team:University College London/Module 2/Modelling
From 2012.igem.org
Erinoerton (Talk | contribs) (→Modelling) |
Erinoerton (Talk | contribs) (→References) |
||
Line 70: | Line 70: | ||
2. Andrady AL (2011) Microplastics in the marine environment. Marine Pollution Bulletin 62: 1596-1605 | 2. Andrady AL (2011) Microplastics in the marine environment. Marine Pollution Bulletin 62: 1596-1605 | ||
- | |||
3. To follow | 3. To follow | ||
Line 82: | Line 81: | ||
Walsh DM, Lomakin A, Benedek GB, Condron MM, Teplow DB (1997) Amyloid b-Protein Fibrillogenesis: Detection of a protofibrillar intermediate. <i> The Journal of Biological Chemistry </i> 272: 22364–22372 | Walsh DM, Lomakin A, Benedek GB, Condron MM, Teplow DB (1997) Amyloid b-Protein Fibrillogenesis: Detection of a protofibrillar intermediate. <i> The Journal of Biological Chemistry </i> 272: 22364–22372 | ||
+ | |||
+ | Shala AA, Restrepo S, Gonzalez Barrios AF (2011) A network model for biofilm development in Escherichia coli K-12. <i> Theoretical Biology and Medical Modelling </i> 8: 34 doi:10.1186/1742-4682-8-34 |
Revision as of 16:35, 21 September 2012
Contents |
Module 2: Aggregation
Description | Design | Construction | Characterisation | Shear Device | Modelling | Results | Conclusions
Modelling
In addition to our gene network model for this module, we have come up with a system of equations which describe the strength of our adhesive biofilms under shear force stress.
Species
Species | Initial value (molecules) | Notes |
---|---|---|
PE | 0.044 | Polyethylene found in North Pacific Gyre (value per cubic metre)1,2 |
POPex | 0.0 | Persistent organic pollutants (ex = extracellular) that are not adhered to plastic surface |
PEPOPex | 9.24E-5 | Persistent organic pollutants (ex = extracellular) that are adhered to the plastic surface3 |
POPin | 0.5 | Persistent organic pollutants (in = intracellular) assumed from E. coli membrane permeability 4 |
mRNANahR | 0.0 | NahR mRNA product |
POPinNahR | 0.0 | Complex of the above two molecules |
POPinNahRpSal | 0.0 | Complex of the above molecule and pSal (promoter that induces laccase transcription) |
mRNACurli | 0.0 | Polycistronic mRNA as it codes for more than one protein, in reality curli cluster contains five or more proteins, in our model mRNA is present as ??CsgE??5 |
CsgA | 0.0 | One of the polypeptides that is coded for in curli cluster, it is a structural component secreted in subunits outside of the cell |
CsgB | 0.0 | One of the polypeptides that is coded for in curli cluster, it is secreted outside of the cell allowing polymerization of CsgA |
Fibril | Result of CsgA and CsgB interaction |
Reactions taking place in the model
Number | Reaction | Reaction rate (molecules/sec) | Notes |
---|---|---|---|
R1 | PE + POPex ↔ PEPOPex | Forward: 1000 Backward: 1 | Pops have 1000 to 10000 times greater tendency to adhere to plastic than float free in the ocean6 |
R2 | POPex ↔ POPin | Forward: 0.6 Backward: 0.4 | Based on membrane permeability4: diffusion gradient |
R3 | POPin + mRNA.Nahr → POPin.mRNA.Nahr | Forward: 1 Backward: 0.0001 | Based on the assumption that the chemical structure/size of POPs is similar to salycilate6. Salycilate binds to the NahR mRNA product, which complex then binds to the pSal promoter. |
R7 | 0 → mRNA.Nahr | Forward: 0.088 Backward: 0.6 | Transcription rate of NahR in molecules/sec (for NahR size 909 bp7, transcription rate in E.coli 80bp/sec8) under constitutive promoter control |
R4 | POPinmRNANahr → POPinmRNANahr.Psal | Forward: 78200 Backward: 0.191 9 | NahR to pSal binding based on the assumption that POP-NahR binding has no effect on NahR-pSal binding |
R5 | POPexmRNANahr.Psal → GFP.mRNA | 0.11 | Transcription rate of GFP in molecules/sec (for GFP size 720bp10, transcription rate in E.coli 80bp/sec8) |
R6 | GFP.mRNA → GFP | 0.084 | Translation rate of GFP in molecules/sec (for GFP size 240aa10, translation rate in E.coli 20aa/sec8) |
R9 | GFP.mRNA → 0 | 0.03 | Degradation rate of GFP mRNA product11 must be taken into account due to suboptimal conditions |
Results
To follow
References
1. Goldstein M, Rosenberg M, Cheng L (2012) Increased oceanic microplastic debris enhances oviposition in an endemic pelagic insect. Biology Letters 10.1098
2. Andrady AL (2011) Microplastics in the marine environment. Marine Pollution Bulletin 62: 1596-1605
3. To follow
4. To follow
5. Nenninger AA, Robinson LS, Hammer ND, Epstein EA, Badtke MP, Hultgren SJ, Chapman MR (2011) CsgE is a curli secretion specificity factor that prevents amyloid fibre aggregation. Mol Microbiol 81: 486-499
6. Mato Y, Isobe T, Takada H, Kanehiro H, Ohtake C, Kaminuma T (2001) Plastic Resin Pellets as a Transport Medium for Toxic Chemicals in the Marine Environment. Environ. Sci. Technol. 35: 318-324
Walsh DM, Lomakin A, Benedek GB, Condron MM, Teplow DB (1997) Amyloid b-Protein Fibrillogenesis: Detection of a protofibrillar intermediate. The Journal of Biological Chemistry 272: 22364–22372
Shala AA, Restrepo S, Gonzalez Barrios AF (2011) A network model for biofilm development in Escherichia coli K-12. Theoretical Biology and Medical Modelling 8: 34 doi:10.1186/1742-4682-8-34