Flux Based Analysis
Flux Balance Analysis (FBA) is a constraint-based modeling approach that allows us to predict metabolic flux distributions in our engineered bacteria. This is crucial for optimizing L-DOPA production and understanding the metabolic constraints that may limit therapeutic efficacy.
Why we chose FBA
Our initial goal was to model Pseudomonas alcaligenes; we wanted to find a way to predict L-DOPA output to adjust our practical work and to know what to expect from our in-vitro experiments. FBA modelling was chosen for said task.
FBA - flux based analysis, is a common technique that is used to look at how an organism in a steady state distributes its resources or fluxes across its metabolic network. Since such models are not available for our bacteria we took a metabolic model of Pseudomonas putida (iJN1463), which is a close relative with a similar metabolic network. Both species of Pseudomonas also show similar ability to process aromatic compounds, which is important since both catechol and L-dopa are aromatic. As our experimental approach included adding a gene for tyrosine-phenyl lyase (TPL) which is the enzyme that produces L-DOPA we added this enzyme and its related reactions to the model.
Setting the constraints and limitations of the model
We first had to set the major limitations of the FBA: it being state-state and its constraints. FBA is known as a constraint based model since it assumes optimal usage of resources. So we researched and set constraints that we found in literature for uptake of catechol, ammonia and pyruvate; precursors for the TPL L-DOPA reaction. Leonie van Steijn told us in an interview that the uptake rates are the most important constraints of the model, so we spend additional effort to make sure we could argue for reasonable rates.
Balance between biomass growth and L-DOPA production
We were wondering what the effect of our L-DOPA production could be on biomass growth. So first we let our FBA find the maximum L-DOPA production possible, which was determined to be 0.821 minimol per gram dry weight per hour (mmol/gDW/h). We then wanted to calculate the cost of producing a certain amount of L-DOPA. So we set the limits of L-DOPA production at 0 to the max, in intervals of 0.1 mmol/gDW/h, and then have the model find the maximum biomass growth rate for each value. From this we found that every 0.1mmol/gDW/h reduces the biomass growth rate by 0.0131 (Fig 1.).
Figure 1. Biomass growth reduction per produced volume of L-DOPA.
Then we wanted to better understand what this meant on the relation between L-DOPA yield and biomass growth. Therefore we set L-DOPA production at 0-100% of the maximum in intervals of 10%, and made the model calculate what the effect was on growth for each level of L-DOPA production. Through this we found out that the effect of L-DOPA production on biomass growth follows a linear relationship, with 100% L-DOPA production reducing biomass growth rate by 13.3% (Fig. 2). The biomass growth is in mmol/gDW/h, but is calculated for 1gDW. This means it can be seen as the fraction of its own mass it gains per hour.
Figure 2. Biomass growth rate for different L-DOPA yields.
Now we understand the cost of L-DOPA production and optimizing yield on biomass growth rate. However, Leonie van Steijn told us that the model should optimize biomass first instead of L-DOPA production if we wanted it to be more biologically relevant. So we optimized the biomass growth rate, and then manually lowered it in steps of 10% to see what level of growth rate would allow L-DOPA production. Consistent with our earlier finding we found that L-DOPA production was maximed at a biomass growth rate at 86.7% (Fig. 3).
Figure 3: L-dopa vs biomass production trade off curve. We set biomass growth rate at specific percentages of its maximum rate in increments of 10%, and extracted the predicted L-DOPA production rate. We also included the point of 86.7% growth rate as we found that max L-DOPA production capped growth at this rate.
Discovering the limiting metabolites: catechol
Given the chemical pathway we expected that pyruvate and catechol could potentially be limiting factors in L-DOPA production. As pyruvate uptake is around 5 times that of catechol, we started by investigating the impact of catechol on L-DOPA production. However, given the earlier finding that biomass growth rate is partially sacrificed to synthesize L-DOPA we also took this into account. So we changed the catechol uptake rates from 0 to 1.2, which is about 0-1.5 times the normal uptake rate. Then we set biomass growth at different levels. For each catechol uptake and biomass growth rate we then extracted the L-DOPA production (Fig. 4).
Our analysis shows that at maximum biomass growth rate L-DOPA production starts only if the uptake rate of catechol is higher 0.8 mmol/gDW/h. However, we are surprised there is any L-DOPA production at all. This means that catechol is not the only limiting factor, but that an initial proportion of catechol is essential for maintaining optimal growth. Additionally, we found that at a growth rate of 50%, virtually all catechol is used for L-DOPA production, until values higher than 0.8 mmol/gDW/h are reached. At this point they diverge, indicating that above this value catechol again becomes necessary to maintain growth. This shows a delicate metabolic balance of catechol, where an initial portion of catechol is necessary for optimal growth, but also that an over-supply will eventually not directly translate to increased L-DOPA production.
Figure 4: catechol necessary for maintaining growth and L-DOPA production. We set catechol uptake rates at different values and determined the L-DOPA production for different relative growth rates at that catechol uptake rate.
Because of the interesting divergence at high catechol uptake rates we decided we wanted to study this further, so we made the model go from an uptake rate of 0 to 3 mmol/gDW/h. This gave us even further insight. Eventually all growth rates achieve the same increase in L-DOPA production per increase in catechol uptake, no matter what growth rate it is. But high growth rates initially increase less in terms of L-DOPA production than the low growth rate ones. This means that at low growth rates initially all catechol is available to be spent on L-DOPA, but as this requires other resources it eventually converts into L-DOPA only at a certain conversion rate of around 3 units of catechol per 2 units of L-DOPA. For high growth rates, there is initially no catechol available, but as the uptake increases it will eventually get converted into L-DOPA at the same rate.
Figure 5: mapping of the catechol to L-DOPA conversion rate at high rates of catechol uptake. We set catechol uptake rates at different values and determined the L-DOPA production for different relative growth rates at that catechol uptake rate.
Unraveling the effect of pyruvate as a carbon source on biomass growth and its interaction with catechol
Now that we knew that catechol is vital for a balance between optimal growth and L-DOPA production we started to look at the impact of pyruvate. Pyruvate can be used immediately as a primary energy source in the citric acid cycle (PubChem), and is therefore a critical component of cell growth. Therefore we started to wonder if changing the ratio of pyruvate to catechol would change the carbon yield. The carbon yield is what the amount of biomass growth you get per unit of substrate used.
Normally the ratio of pyruvate to catechol uptake is around 5, so we decided to model pyruvate uptake to catechol uptake rates between 0-10, to include both lower and higher than usual ratios. As can be seen in figure 6, increasing the pyruvate to catechol ratio decreases the efficiency with which carbon is incorporated into biomass. We had honestly expected the reverse effect, with increasing pyruvate uptake leading to increased growth. However, this result might indicate that increasing the pyruvate uptake means that other non-carbon components of the cell are undersupplied, reducing carbon-specific yield.
Figure 6: effect of the balance pyruvate to catechol uptake on carbon yield. On the y-axis we plotted the biomass carbon yield, with the ratio of pyruvate to carbon uptake on the x-axis.
Initial modelling of the kill switch through ATP used for maintenance
In addition to that we attempted to simulate a killswitch in our FBA; but the design was very limiting. We tried to mimic the effect of MazF: fast degradation of mRNAs leading to increased metabolic cost of mRNA production and lower levels of proteins and enzymes. We approximated this by manually increasing the maintenance cost of the cell through increasing ATPM by 50%, and approximating the reduction in translation of enzymes by reducing the activity of all enzymatic reactions to 10%. From this we learned that biomass growth rate is reduced to 0.041gDW/h, but L-DOPA synthesis is possible even when the kill switch is activated (Fig. 6).
Figure 7: effect of MazF production on growth rate and L-DOPA production and TPL production. MazF was modeled by increasing ATP used for maintaining cell viability by 50%, and by reducing translation to 10%.
Finding that L-DOPA production happens even when the kill switch was activated was quite surprising, as we did not expect the bacteria to have resources left to produce L-DOPA. So we wanted to understand what part of this was due to the increase in maintenance cost compared to the reduction in translation rates. Therefore we decided to keep the 50% increase in ATP maintenance cost, but vary the ratio of translation (Fig. 7). Interestingly, we found that the reduction in translation rates did not impact biomass growth rate, and that we could actually get a maximum level of L-DOPA production that was equal to the level we could achieve without the increased maintenance costs. This suggests that L-DOPA synthesis does not require energetic input, but is also limited by available metabolites.
Figure 8: Biomass growth rate and L-DOPA production rate as a function of the residual translation rate, when cell maintenance cost is increased by 50%. We set the FBA to increase ATP required for cell maintenance by 50%, then cut translation rates to a fraction of 0-1 in increments of 0.10, as can be seen on the x-axis. Then we determined for each fraction of translation what the maximum biomass growth rate (blue) and L-DOPA production rate (red) was.
Our results made us wonder if the FBA model is limited in its capacity to model processes like transcription and translation effectively. As mentioned before, we modeled reduced translation by cutting enzyme reaction speed as transcription and translation are not processes that are part of the FBA model. So this attempt demonstrated to us some limitations of this simple FBA model. Not only is it in steady state and assuming optimal convergence, it also does not contain a full genome and important cellular processes like transcription and translation. So the accuracy of the model was not ideal.Therefore we decided that it would be better to increase mRNA degradation rates itself, as that more closely resembles the mechanism of action. We decided to attempt to incorporate gene-product reactions in a new model, which we will describe on the next page.
What we learned with the FBA
Our estimates for the L-DOPA production allowed us to attempt to estimate our yields in the wet lab. More importantly, it also allowed us to more intricately understand our model organism and the biosynthesis pathway of L-DOPA. We identified crucial limiting factors like catechol and pyruvate, and showed how the competition for these resources affect the growth of our bacteria.
We learned that L-DOPA production siphons away resources which hampers optimal growth. Supplying additional catechol can remedy this at a specific rate of around 3 units catechol to 2 units L-DOPA. The growth rate of the cell strongly influences how many resources can be shifted towards L-DOPA production and therefore dictates L-DOPA production at low and basal levels of catechol uptake.
Additionally, we found that the ratio of pyruvate to catechol impacts the biomass carbon yield. Although we had expected that increasing pyruvate to catechol ratios would lead to increased usage of pyruvate for cell growth, we found that it actually decreased the yield. This likely means that other resources in our model are relatively less available at the high pyruvate to catechol ratios, leading to reduced efficiency.
Lastly, we learned that biomass growth is almost zero at an increased ATP maintenance of 50%, and that L-DOPA production is not impacted by this. This means that L-DOPA production is not very energetically costly. However, we also learned that this version of the FBA is not suited to model the mazF toxin mechanistically. So we decided to incorporate gene product reactions and expand the capabilities of the model. This would also allow us to screen knock-out genes that would increase yield, and allow us to model the biological effect of our kill switch toxin on transcription and translation.