Team:KU Leuven/Project/Ecological/Modelling

From 2013.igem.org

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<p align="justify">
As can be noticed, the wind speed decreases exponentially with extinction factor a when approaching ground level and thus going deeper into the canopy. u<sub>c</sub> is the speed at height z<sub>c</sub> and can easily be calculated by the formula of the logarithmic wind profile.<br /><br />
As can be noticed, the wind speed decreases exponentially with extinction factor a when approaching ground level and thus going deeper into the canopy. u<sub>c</sub> is the speed at height z<sub>c</sub> and can easily be calculated by the formula of the logarithmic wind profile.<br /><br />
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Evidently, the wind direction changes in time. Most regions however tend to have a dominant wind (“Prevailing winds,” 2013), at least during a certain time period. This is the reason our model only incorporates convection in one direction, which greatly simplifies calculation.  Furthermore we can also find average wind speeds, measured by KMI in Belgium (“Maandelijkse normalen - KMI,” 2013). These are measured at 10 m above the ground, making it possible to calculate u*/k used in the log law. Now, all parameters for convection are known when the crop height is given. The wind profile was entered in the software using a piecewise function and self-defined parameters, making it easy to change wind speed and crop height. An example of the profile is plotted in Figure 1.</p>
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Evidently, the wind direction changes in time. Most regions however tend to have a dominant wind (“Prevailing winds,” Wikipedia, 2013), at least during a certain time period. This is the reason our model only incorporates convection in one direction, which greatly simplifies calculation.  Furthermore, average wind speeds are measured and published monthly by the Royal Meteorological Institute (KMI) in Belgium (“Maandelijkse normalen - KMI,” 2013). These are measured at 10 m above the ground, making it possible to calculate u*/k used in the log law. Now, all parameters for convection are known when the crop height is given. The wind profile was entered in the software using a piecewise function and self-defined parameters, making it easy to change wind speed and crop height. An example of the profile is plotted in Figure 1.</p>
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     <h3>Boundary conditions</h3>
     <h3>Boundary conditions</h3>
     <p align="justify">
     <p align="justify">
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     In order to solve our model, boundary conditions need to be specified.
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     In order to solve our model, boundary conditions need to be specified. We'll represent the environment as a square box (5X5X5m) with 6 faces. Within this environment box, we assume a bacterium box (5X5X1cm), suspended in "mid air", with its own 6 (smaller) faces.
     </p>
     </p>
     <h4>Inflow and outflow</h4>
     <h4>Inflow and outflow</h4>
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     <p align="justify">The faces perpendicular to the wind direction were specified as an inflow (with a concentration of 0 mol/m<sup>3</sup>) respectively an outflow.</p>
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     <p align="justify">For the environment box, the faces perpendicular to the wind direction were specified as an inflow (with a concentration of 0 mol/m<sup>3</sup>), respectively an outflow.</p>
     <h4>No flux</h4>
     <h4>No flux</h4>
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     <p align="justify">The face representing the ground will have no flux through it, because we assume that the diffusion coefficient of our pheromones is much larger in soil than in air. Furthermore, all faces but one of the volume representing a container with bacteria are given zero flux as well.</p>
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     <p align="justify">Within the environment box, the face representing the ground will have no flux through it, because we assume that the diffusion coefficient of our pheromones is much larger in soil than in air. Within the bacterium box, all faces but one (pheromone outlet) are given zero flux as well.
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    <h4>Flux</h4>
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</p>
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     <p align="justify">The upper face of this container is the only place where pheromones are released in the air. Under the assumption that the pheromone production and vaporization is at steady state, we can set the flux at this surface equal to the production rate of the entire colony.<br /><br />
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<h4>Open boundaries</h4>
 +
<p align="justify">The remaining 3 faces of the environment box remain "open" since the pheromone flux needs to be calculated.</p>
 +
     <h4>Specified Flux</h4>    <p align="justify">The upper face of the bacterium container is the only place where pheromones are released in the air. Under the assumption that the pheromone production and vaporization is at steady state, we can set the flux at this surface equal to the production rate of the entire colony.<br /><br />
Once we know the production per cell (by the procedure in &lt;PART SANDER&gt;) it is straightforward to calculate the output of the whole colony by using an average cell density in the appropriate growth phase. This output represented as an amount per time can then be converted to a flux through the contact surface with the air, which can be entered in the simulation program. </p>
Once we know the production per cell (by the procedure in &lt;PART SANDER&gt;) it is straightforward to calculate the output of the whole colony by using an average cell density in the appropriate growth phase. This output represented as an amount per time can then be converted to a flux through the contact surface with the air, which can be entered in the simulation program. </p>

Revision as of 19:39, 2 October 2013

iGem

Secret garden

Congratulations! You've found our secret garden! Follow the instructions below and win a great prize at the World jamboree!


  • A video shows that two of our team members are having great fun at our favourite company. Do you know the name of the second member that appears in the video?
  • For one of our models we had to do very extensive computations. To prevent our own computers from overheating and to keep the temperature in our iGEM room at a normal level, we used a supercomputer. Which centre maintains this supercomputer? (Dutch abbreviation)
  • We organised a symposium with a debate, some seminars and 2 iGEM project presentations. An iGEM team came all the way from the Netherlands to present their project. What is the name of their city?

Now put all of these in this URL:https://2013.igem.org/Team:KU_Leuven/(firstname)(abbreviation)(city), (loose the brackets and put everything in lowercase) and follow the very last instruction to get your special jamboree prize!

tree ladybugcartoon

Ultimately our project aims to reduce crop loss because of aphid infestation. Given the time span of the competition, it is impossible to conduct a field experiment for this. Therefore we attempt to predict the effect of our pheromones on the ecology through a series of modelling steps.

The first step is to calculate the concentration of the pheromones released in the environment. When a colony of E. coligy is placed in a field, the produced substances (pheromones, ...) will be transported in the air by diffusion and convection. Diffusion is always present, whereas the source of the convection term is the wind. To establish a realistic model, certain parameters are needed. Therefore, approximate diffusion coefficients and air velocity were searched. Production of the pheromones by the colony was coupled with the other modelling approach <link to Sander’s text>.

Convection-diffusion equation

Diffusion coefficients

Because we found no measured diffusion coefficients of the pheromones in literature, estimations were made with a calculator based on methods described in (Lyman, Reehl, & Rosenblatt, 1982). Using the average supplied by the calculator, the results are 4.62 x 10-6 m2/s for E-beta-farnesene and 6.33 x 10-6 m2/s for methyl salicylate. The conditions supplied were a pressure of 1 atm and a temperature of 15 °C.


Plot of the wind profile

Figure 1 ǀ Wind profile for a crop height of 2 m and a wind speed of 3.39 m/s at a height of 10 m.

Wind speed

Because of friction and obstacles on the earth’s surface, wind speed varies with altitude. Generally, the velocity decreases with increasing altitude. A logarithmic wind profile is appropriate for the part above the crops (Goudriaan, 1977, p. 96). The formula for this profile is

Wind profile

with u representing the velocity. Here d accounts for an upward shift above a vegetative cover. The relation d=0.63 x zc is suggested, where zc is the height of the crops. The length z0 is called the roughness length and is often supposed to be about one tenth of zc.

For the part inside the canopy, the profile is exponential.

Wind profile inside canopy

As can be noticed, the wind speed decreases exponentially with extinction factor a when approaching ground level and thus going deeper into the canopy. uc is the speed at height zc and can easily be calculated by the formula of the logarithmic wind profile.

Evidently, the wind direction changes in time. Most regions however tend to have a dominant wind (“Prevailing winds,” Wikipedia, 2013), at least during a certain time period. This is the reason our model only incorporates convection in one direction, which greatly simplifies calculation. Furthermore, average wind speeds are measured and published monthly by the Royal Meteorological Institute (KMI) in Belgium (“Maandelijkse normalen - KMI,” 2013). These are measured at 10 m above the ground, making it possible to calculate u*/k used in the log law. Now, all parameters for convection are known when the crop height is given. The wind profile was entered in the software using a piecewise function and self-defined parameters, making it easy to change wind speed and crop height. An example of the profile is plotted in Figure 1.

Boundary conditions

In order to solve our model, boundary conditions need to be specified. We'll represent the environment as a square box (5X5X5m) with 6 faces. Within this environment box, we assume a bacterium box (5X5X1cm), suspended in "mid air", with its own 6 (smaller) faces.

Inflow and outflow

For the environment box, the faces perpendicular to the wind direction were specified as an inflow (with a concentration of 0 mol/m3), respectively an outflow.

No flux

Within the environment box, the face representing the ground will have no flux through it, because we assume that the diffusion coefficient of our pheromones is much larger in soil than in air. Within the bacterium box, all faces but one (pheromone outlet) are given zero flux as well.

Open boundaries

The remaining 3 faces of the environment box remain "open" since the pheromone flux needs to be calculated.

Specified Flux

The upper face of the bacterium container is the only place where pheromones are released in the air. Under the assumption that the pheromone production and vaporization is at steady state, we can set the flux at this surface equal to the production rate of the entire colony.

Once we know the production per cell (by the procedure in <PART SANDER>) it is straightforward to calculate the output of the whole colony by using an average cell density in the appropriate growth phase. This output represented as an amount per time can then be converted to a flux through the contact surface with the air, which can be entered in the simulation program.


Geometry for the model

Figure 2 ǀ Geometry for the model: the blue dot is the container with E. coligy, a is an influx plane, b an open boundary and c a face with no flux.

Results

Although we lacked real values for the production rates of the pheromones, we ran the model with an arbitrary (although in the ballpark) flux of 1 mmol/(m2s) to get an idea of the shape of the solution. We used a simple raised cosine function to capture the oscillating behaviour of the <OSCILLATOR MODEL> with a period of 1 hour. As can be seen in the animated figure below, convection by wind is the dominant effect on the pheromones. Therefore the solution follows the oscillations quite well and lag or local accumulation of pheromones is not a problem. Note that the solution has negative values at some points, which is physically impossible of course. This is solely due to numerical errors and can be avoided by the use of a finer mesh (at a much larger computational cost).

Vertical slice of the geometry showing the concentration of methyl salicylate

Figure 3 ǀ Vertical slice of the geometry showing the concentration of methyl salicylate.

Software

At first, we used Mathworks Matlab with the Partial Differential Equations Toolbox, but this software was limited to 2D geometries and more stringent boundary conditions. Later on, we noticed that the Department of Engineering of our university provided COMSOL Multiphysics. This program was very suitable for our purposes, as it provides a model for “Transport of Diluted Species”. Our complete model can be downloaded here.


COMSOL Multiphysics

Goudriaan, J. (1977). Crop micrometeorology : a simulation study. Wageningen University, Wageningen.
Lyman, W. J., Reehl, W. F., & Rosenblatt, D. H. (1982). Handbook of chemical property estimation methods: environmental behavior of organic compounds. McGraw-Hill.
Maandelijkse normalen - KMI. (n.d.). Meteo. Retrieved August 22, 2013, from http://www.meteo.be/meteo/view/nl/65239-Home.html
Prevailing winds. (2013, August 21). In Wikipedia, the free encyclopedia. Retrieved from http://en.wikipedia.org/w/index.php?title=Prevailing_winds&oldid=569524163