Team:Paris/Network analysis and design/Core system/Model construction/Detailed justification

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We shall present here a more detailed presentation of the choice we made as far as our model is concerned

Contents

Sum effect and linear modelling

  • The flagella gene network has been thoroughly studied in [1]. We used two major results presented in this study. Firstly, Shiraz Kalir and Uri Alon came up with the fact that the promoters of class 2 genes, among which fliL, flgA and flhB, behaved like SUM-gate functions with flhDC and fliA inputs. Secondly, their experiments proved that these influences could be considered as linear. Thus the following model:


Promoter Activity.jpg


β and β’ represent the relative influence of flhDC and fliA respectively, the units of β and β’ being time-1.

  • Furthermore, they came up with numerical values of β and β’ for each gene, which fitted quite well to their experiments. We then decided that we could use those values as well in our model.
  • Thus the resulting equations
FliA dynamics.jpg
CFP.jpg
YFP.jpg
Eqn EnvZ-RFP.jpg

Hill function

When we had no relevant information, we decided to model the promoter activity by a Hill function. This was the case for the effect of envZ over FlhDC :

Prom act flhDC.jpg

Thus the dynamic equation for [FlhDC] :

Eqn flhDC.jpg

As for the parameters, we decided to chose coherent values, that is nEnvZ=4 and θEnvZ=0.5.

Normalization

FliA, CFP, YFP, EnvZ-RFP

We kept the β and β’ values found by S. Kalir and U. Alon, since they showed the relative influence of flhDC and fliA. To have the same order of magnitude between each specie, we normalized those parameters between 0 and 1 as following. We reasoned independently for each equation, wishing to set the equilibrium values of the concentration to 1 given input values of 1. This gave:

Beta Resize.jpg


Beta p Resize.jpg


  • In fact, if we take CFP for example:
CFP.jpg

The maximum of [CFP] is reached when [fliA] = 1 and [flhDC] = 1 ; when we solve with these condidtions, we obtain :

CFP Solve.jpg

Then setting the equilibrium value of [CFP] to 1 corresponds to setting

Beta Gamma resize.jpg
  • The analysis of fliA is different, but not the result:
FliA Analysis.jpg

With an input of flhDC equal to 1, the solution of the differential equation is:

FliA Solve.jpg

And the condition on the equilibrium imposes

Beta Gamma Resize FliA.jpg
  • To conclude, we see that we always get the same condition:
Final Resize.jpg
  • Finally, since we had imposed γ=1 we resulted with β+β'=1.

FlhDC

  • Likewise the previous analysis, we set γFlhDC to 1. Then, since FlhDC is fully expressed when envZ is not, we see that when solving under this conditions, we get
FlhDC norm.jpg

hence the need to set

Beta flhDC.jpg
  • This is highly interesting since we do not need to find a value for βFlhDC
  • Furthermore, since [EnvZ] has been normalized, we have to do so for θEnvZ as well, since its role is to stand as a reference concentration for EnvZ. Therefore, we have to normalize it in the same way we did for [EnvZ]:
we had
Norm envZ.jpg
which means we have to impose :
Norm Theta EnvZ.jpg

Determining the degradation rate

We evaluated in the wet lab the half life time for our cells, and then calculated the degradation constants using :

Gamma Expression.jpg

The value for half-life time we found and used is 35min.

Parameters table

Parameter Table
Parameter Meaning Original Value Normalized Value Unit Source


γ Degradation rate 0.0198 1 min-1 wet-lab
βFliA FlhDC activation coefficient 50 0.1429 min-1 [1]
β'FliA FliA activation coefficient 300 0.8571 min-1 [1]
βCFP FlhDC activation coefficient 1200 0.8276 min-1 [1]
β'CFP FliA activation coefficient 250 0.1724 min-1 [1]
βYFP FlhDC activation coefficient 150 0.3333 min-1 [1]
β'YFP FliA activation coefficient 300 0.6667 min-1 [1]
βEnvZ-RFP FlhDC activation coefficient 100 0.2222 min-1 [1]
β'EnvZ-RFP FliA activation coefficient 350 0.7778 min-1 [1]
βFlhDC Maximum production rate 1 min-1
nenvZ Hill coefficient 4 ¤
θenvZ Hill characteristic concentration 0.5 c.u

c.u. being an arbitrary concentration unit.