Model header image

Overview

Our model serves two main purposes:

Quantitative Description of Project Design: Our dual-microbe system involves complex processes spanning lignin degradation, metabolic conversion, and microbial population dynamics. Through mathematical modeling, we can quantitatively describe these intricate interactions, providing crucial insights into system behavior that would be challenging to obtain through wet lab experiments alone.

Computational Methods for Project Engineering: The models help determine key parameters for system optimization, reduce experimental trial-and-error, connect different wet lab modules, and mathematically encapsulate biological components for predictable engineering.

Our modeling framework consists of three interconnected parts:

  1. ODE models - Simulate the kinetic processes of lignin decomposition and metabolic conversion, providing dynamic insights into reaction rates.
  2. Flux Balance Analysis (FBA) - Predicts optimal metabolic fluxes and theoretical succinate yields at genome scale.
  3. Dual-Species System Dynamics - Explore population interactions and system stability.

These models provide a comprehensive understanding of our project and yield valuable computational results for both fundamental research and industrial application.

Model for Lignin Decomposition and Succinate Synthesis

I. Model Design

We examine the reaction equations and enzyme parameters of the four main parts in the project design: “Lignin decomposition by laccase”, “Metabolic entry of decomposition products into TCA”, “TCA cycle”, and “Succinate extraction”, and characterize the system’s metabolism through ordinary differential equations. We hope to deepen our understanding of the project system and provide guidance for further improvements in wet lab experiments.

II. Pre-assumptions

  • The system is well-mixed in compartments, ignoring diffusion limitations inside the culture medium and cytoplasm, but considering the separation between culture medium and cytoplasm.
  • Oxygen concentration is suitable and not a limiting factor.
  • pH and temperature remain constant during the reaction.
  • The total concentration of various enzymes remains constant.
  • Products of non-equilibrium reactions do not inhibit the reactions.
  • Complex free radical chain reactions are simplified as depolymerization.
  • The baseline production of various substances in the engineered bacteria is stable.
  • Parameters for some enzymes that were not queried are given by referring to parameters of similar enzymes.
  • The total cellular protein concentration is estimated as 250g/L.

III. Lignin Decomposition by Laccase

1.Model Variables

Variable Unit Meaning
Lp mM/L Phenolic Lignin concentration (based on oxidizable phenolic hydroxyl units)
Lnp mM/L Non-phenolic Lignin concentration (based on units oxidizable by mediators)
Mred mM/L Reduced Mediator concentration
Mox mM/L Oxidized Mediator radical concentration
Syr mM/L Concentration of Syringate in the fermentation system
Van mM/L Concentration of Vanillic in the fermentation system
pHB mM/L Concentration of p-Hydroxybenzoic in the fermentation system

2.Metabolic Reactions

Reaction 1: Direct oxidation of phenolic lignin (Lp) by laccase

$$E + L_p \xrightarrow{k_1} E:L_p \xrightarrow{k_{cat,p}} E_{red} + L_p^{\bullet}\quad (phenolic\text{ }lignin\text{ }radical)$$ $$E_{red} + O_2 \xrightarrow{k_{ox}} E + H_2O\quad (enzyme\text{ }regeneration)$$ $$L_p^{\bullet} \xrightarrow{k_{depoly,p}} a\cdot Syr+b\cdot Van+c\cdot pHB\quad(radical-initiated\text{ }depolymerization)$$ Lignin is composed of three types of monomers: S, G, and H. When lignin is completely decomposed by laccase, these three monomers form syringate, vanillic, and p-Hydroxybenzoic, respectively.

Assuming enzyme regeneration and radical depolymerization are relatively fast, the entire process can be viewed as the consumption of Lp. Since Lp and Mred compete for the enzyme E, the consumption rate v1 of Lp is described using the competitive inhibition Michaelis-Menten equation: $$v_1 = \frac{V_{max,p} [L_p]}{K_{m,p}(1 + \frac{[M_{red}]}{K_{m,m}}) + [L_p]}$$

Reaction 2: Oxidation of mediator (Mred) by laccase

$$E + M_{red} \xrightarrow{k_2} E:M_{red} \xrightarrow{k_{cat,m}} E_{red} + M_{ox}$$ $$E_{red} + O_2 \xrightarrow{k_{ox}} E + H_2O\quad(enzyme\text{ }regeneration)$$

Similarly, considering the competition between Lp and Mred, the generation rate of Mox (i.e., the consumption rate of Mred) v2 is described as: $$v_2 = \frac{V_{max,m} [M_{red}]}{K_{m,m}(1 + \frac{[L_p]}{K_{m,p}}) + [M_{red}]}$$

Reaction 3: Oxidation of non-phenolic lignin (Lnp) by oxidized mediator (Mox)

$$M_{ox} + L_{np} \xrightarrow{k_3} M_{red} + L_{np}^{\bullet}\quad(non-phenolic\text{ }lignin\text{ }radical)$$ $$L_{np}^{\bullet} \xrightarrow{k_{depoly,np}} d\cdot Syr+e\cdot Van+f\cdot pHB\quad(radical-initiated\text{ }depolymerization)$$

Simplification: Assuming radical depolymerization is fast, the reaction rate v3 is mainly determined by the concentrations of Mox and Lnp: $$\begin{align}v_3 = k_3 [M_{ox}] [L_{np}]\end{align}$$

3.Parameter List:

Parameter Symbol Parameter Description Value Data Source
vLp Feeding rate of phenolic lignin 0.01mM/L * min Estimated value
vLnp Feeding rate of non-phenolic lignin 0.05mM/L * min Estimated value
[Etotal] Total laccase concentration 1U/mL [1]
[Mtotal] Total mediator concentration (ABTS, HBT, etc.) 1mM [3]
Km, p Michaelis constant for phenolic lignin 0.8mM [2]
Km, m Michaelis constant for mediator (e.g., ABTS) 0.32mM [9]
Vmax, p Maximum reaction rate for lignin substrate 0.025mM/L * min [1]
a Proportion of syringate produced after complete decomposition of phenolic lignin 0.4 [10][11]
b Proportion of vanillic produced after complete decomposition of phenolic lignin 0.5 [10][11]
c Proportion of p-Hydroxybenzoic produced after complete decomposition of phenolic lignin 0.1 [10][11]
d Proportion of syringate produced after complete decomposition of non-phenolic lignin 0.85 [10]
e Proportion of vanillic produced after complete decomposition of non-phenolic lignin 0.15 [10]
f Proportion of p-Hydroxybenzoic produced after complete decomposition of non-phenolic lignin 0 [10]

4.Ordinary Differential Equations:

$$\frac{d[L_p]}{dt} = v_{L_{p}}-v_1 $$ $$\frac{d[L_{np}]}{dt} = v_{L_{np}}-v_3 $$ $$\frac{d[M_{ox}]}{dt} = v_2 - v_3 $$ $$ \begin{align} [M_{red}] = [M_{total}] - [M_{ox}] \end{align} $$ $$\frac{d[\text{Syr}]}{dt}=a\cdot v_1+d\cdot v_3$$ $$\frac{d[\text{Van}]}{dt}=b\cdot v_1+e\cdot v_3$$ $$\frac{d[\text{pHB}]}{dt}=c\cdot v_1+f\cdot v_3$$

5.Result Presentation:

fig 1. Lignin degradation rate
fig 2. Degradation product generation rate

IV.Metabolic Entry of Decomposition Products into TCA

1.Model Variables

Variable Unit Meaning
Syr mM/L Concentration of Syringate in the fermentation system
Van mM/L Concentration of Vanillic in the fermentation system
pHB mM/L Concentration of p-Hydroxybenzoic in the fermentation system
OAA mM/L Concentration of oxaloacetate in the engineered bacteria
Pyr mM/L Concentration of Pyruvate in the engineered bacteria
AcCoA mM/L Concentration of Acetyl-CoA in the engineered bacteria
Succ mM/L Concentration of Succinate in the engineered bacteria

2.Metabolic Reactions

Reaction 4: Entry of Syringate into the TCA cycle

Syringate will be gradually metabolized into pyruvate and oxaloacetate via the gallate metabolic pathway in Pseudomonas putida. $$\begin{align}Syr \longrightarrow Pyr + OAA\end{align}$$ To maintain model interpretability, we equate the metabolic rate of Syringate inside Pseudomonas putida to the rate catalyzed by a certain step enzyme, thus using the Michaelis-Menten equation for description: $$v_4=\frac{V_{max}^{Syr}\cdot [Syr]}{K_m^{Syr}+[Syr]}$$ In the fermentation system, since the laccase decomposition process occurs in the total liquid, subsequent metabolic steps occur in the bacterial cells. However, the bacterial volume only accounts for a small part of the total liquid volume, so the consumption rate of Syringate is corrected by multiplying by a coefficient rt. But the generation rates of pyruvate and oxaloacetate are not multiplied by the coefficient rt, as they describe concentrations inside the engineered bacteria, not in the fermentation system.

Reaction 5: Entry of Vanillic into the TCA cycle

Vanillic will be gradually metabolized into succinate and acetyl-CoA via the Protocatechuate metabolic pathway in Pseudomonas putida. $$Van \xrightarrow[+CoA]{} Succ + Ac_{CoA}$$ To maintain model interpretability, we use the simplification method of Reaction 4 for description, and similarly multiply the consumption rate of vanillic by the coefficient rt, but not the generation rates of succinate and acetyl-CoA: $$v_5=\frac{V_{max}^{Van}\cdot [Van]}{K_m^{Van}+[Van]}$$

Reaction 6: Entry of p-Hydroxybenzoic into the TCA cycle

p-Hydroxybenzoic will also be gradually metabolized into succinate and acetyl-CoA via the Protocatechuate metabolic pathway in Pseudomonas putida. $$pHB \xrightarrow[+CoA]{} Succ + Ac_{CoA}$$ To maintain model interpretability, we use the simplification method of Reaction 4 for description, and similarly multiply the consumption rate of p-Hydroxybenzoic by the coefficient rt, but not the generation rates of succinate and acetyl-CoA: $$v_6=\frac{V_{max}^{pHB}\cdot [pHB]}{K_m^{pHB}+[pHB]}$$

3.Parameter List:

Parameter Symbol Parameter Description Value Data Source
rt Ratio of bacterial volume to total liquid volume in the fermentation system 1% Estimated value
KmSyr Michaelis constant of the key enzyme in syringate metabolism 15mM Estimated value
VmaxSyr Maximum reaction rate of the key enzyme in syringate metabolism 10mM/L * min Estimated value
KmVan Michaelis constant of the key enzyme in Vanillic metabolism 15mM Estimated value
VmaxVan Maximum reaction rate of the key enzyme in Vanillic metabolism 100mM/L * min Estimated value
KmpHB Michaelis constant of the key enzyme in p-Hydroxybenzoic metabolism 15mM Estimated value
VmaxpHB Maximum reaction rate of the key enzyme in p-Hydroxybenzoic metabolism 50mM/L * min Estimated value

4.Ordinary Differential Equations

$$\frac{d[\text{Syr}]}{dt}=a\cdot v_1+d\cdot v_3-v_4\cdot rt$$ $$\frac{d[\text{Van}]}{dt}=b\cdot v_1+e\cdot v_3-v_5\cdot rt$$ $$\frac{d[\text{pHB}]}{dt}=c\cdot v_1+f\cdot v_3-v_6\cdot rt$$

$$\frac{d[\text{OAA}]}{dt}=v_{OAA}+v_4$$ $$\frac{d[\text{Pyr}]}{dt}=v_{Pyr}+v_4$$ $$\frac{d[\text{Ac}_\text{{CoA}}]}{dt}=v_{Ac_{CoA}}+v_5+v_6$$ $$\frac{d[\text{Succ}]}{dt}=v_{Succ}+v_5+v_6$$

5.Result Presentation:

fig 3. Concentration of lignin degradation products
fig 4. Rate of degradation product entering into the TCA cycle

V.TCA Cycle:

1.Model Variables

Variable Unit Meaning
ATP mM/L ATP production in the engineered bacteria
OAA mM/L Concentration of oxaloacetate in the engineered bacteria
Pyr mM/L Concentration of Pyruvate in the engineered bacteria
AcCoA mM/L Concentration of Acetyl-CoA in the engineered bacteria
Cit mM/L Concentration of Citrate in the engineered bacteria
Icit mM/L Concentration of Isocitrate in the engineered bacteria
αKG mM/L Concentration of α-Ketoglutarate in the engineered bacteria
SuccinylCoA mM/L Concentration of Succinyl-CoA in the engineered bacteria
Succ mM/L Concentration of Succinate in the engineered bacteria
Fum mM/L Concentration of Fumarate in the engineered bacteria
Mal mM/L Concentration of L-Malate in the engineered bacteria
CoA mM/L Concentration of CoA in the engineered bacteria

2.Metabolic Reactions

Reaction 7: Conversion of Pyruvate to Acetyl-CoA

$$Pyr \xrightarrow[+CoA-2.5ATP]{PDHc} Ac_{CoA}$$ The reaction mechanism is a ping-pong mechanism, so its reaction rate is described using the corresponding Michaelis-Menten equation variant: $$v_7=\frac{V_{max}^{PDHc}\cdot [Pyr]\cdot [CoA]}{K_m^{PDHc,Pyr}\cdot [CoA]+K_m^{PDHc,CoA}\cdot [Pyr]+[Pyr]\cdot [CoA]}$$

Reaction 8: TCA cycle (part1)

$$Ac_{CoA} + OAA \xrightarrow[-CoA]{CS} Cit \xleftrightarrow{ACO} Icit \xrightarrow[-2.5ATP]{IDH} \alpha KG \xrightarrow[+CoA-2.5ATP]{\alpha KGDHC} Succinyl_{CoA} \xrightarrow[-CoA-ATP]{SCS} Succ $$ For most enzyme-catalyzed reactions in the TCA cycle, we use the Michaelis-Menten equation to describe their reaction rates. Specifically, for the step $Ac_{CoA} + OAA \xrightarrow[-CoA]{CS} Cit$, the reaction mechanism is an ordered sequential mechanism; for the step $\alpha KG \xrightarrow[+CoA-2.5ATP]{\alpha KGDHC} Succinyl_{CoA}$, the reaction mechanism is a ping-pong mechanism; their reaction rates are described using the corresponding Michaelis-Menten equation variants. For the step $Cit \xleftrightarrow{ACO} Icit$, the forward and reverse reaction rates are both described using the standard Michaelis-Menten equation. $$v_{8.1}= \frac{V_{max}^{CS}\cdot [OAA]\cdot [Ac_{CoA}]}{K_m^{CS,Ac_{CoA}}\cdot [OAA] + K_m^{CS,OAA}\cdot [Ac_{CoA}] + [OAA]\cdot [Ac_{CoA}] + K_s^{CS,OAA}\cdot K_m^{CS,Ac_{CoA}}}$$ $$v_{8.2+}=\frac{V_{max}^{+ACO}\cdot [Cit]}{K_m^{+ACO}+[Cit]}$$ $$v_{8.2-}=\frac{V_{max}^{-ACO}\cdot [Icit]}{K_m^{-ACO}+[Icit]}$$ $$v_{8.3}=\frac{V_{max}^{IDH}\cdot [Icit]}{K_m^{IDH}+[Icit]}$$ $$v_{8.4}=\frac{V_{max}^{\alpha KGDHC}\cdot [\alpha KG]\cdot [CoA]}{K_m^{\alpha KGDHC,CoA}\cdot [\alpha KG] + K_m^{\alpha KGDHC,\alpha KG}\cdot [CoA] + [\alpha KG]\cdot [CoA]}$$ $$v_{8.5}=\frac{V_{max}^{SCS}\cdot [Succinyl_{CoA}]}{K_m^{SCS}+[Succinyl_{CoA}]}$$

Reaction 9: TCA cycle (part2)

$$OAA \xleftrightarrow[+2.5ATP]{MDH} Mal \xleftrightarrow{FH} Fum \xrightarrow[+1.5ATP]{FRD} Succ$$ For the step $Fum \xrightarrow[+1.5ATP]{FRD} Succ$, the Michaelis-Menten equation is used to describe its reaction rate. For the steps $OAA \xleftrightarrow[+2.5ATP]{MDH} Mal$ and $Mal \xleftrightarrow{FH} Fum$, the forward and reverse reaction rates are both described using the standard Michaelis-Menten equation. $$v_{9.1+}=\frac{V_{max}^{+MDH}\cdot [OAA]}{K_m^{+MDH}+[OAA]}$$ $$v_{9.1-}=\frac{V_{max}^{-MDH}\cdot [Mal]}{K_m^{-MDH}+[Mal]}$$ $$v_{9.2+}=\frac{V_{max}^{+FH}\cdot [Mal]}{K_m^{+FH}+[Mal]}$$ $$v_{9.2-}=\frac{V_{max}^{-FH}\cdot [Fum]}{K_m^{-FH}+[Fum]}$$ $$v_{9.3}=\frac{V_{max}^{FRD}\cdot [Fum]}{K_m^{FRD}+[Fum]}$$

Reaction 10: Regeneration of OAA

$$Pyr\xrightarrow[+ATP]{PC} OAA$$ Due to the break in the TCA cycle, OAA cannot be regenerated through the TCA cycle, so the pyruvate carboxylation catalyzed by PC becomes the main generation pathway for OAA. The standard Michaelis-Menten equation is used to describe its reaction rate. $$v_{10}=\frac{V_{max}^{PC}\cdot [Pyr]}{K_m^{PC}+[Pyr]}$$

3.Parameter List:

Parameter Symbol Parameter Description Value Data Source
KmPDHc, Pyr Michaelis constant of PDHc enzyme for Pyr 0.037mM [12]
KmPDHc, CoA Michaelis constant of PDHc enzyme for CoA 0 Ideal value
KcatPDHc Kcat of PDHc enzyme 0.0071mM/min * mg [12]
EPDHc Concentration of PDHc enzyme 3169ppm [13]
VmaxPDHc Maximum reaction rate of PDHc enzyme 5.62mM/L * min [12][13]
KmCS, AcCoA Michaelis constant of CS enzyme for AcCoA 0.0013mM [14]
KmCS, OAA Michaelis constant of CS enzyme for OAA 25.5mM [14]
KsCS, OAA Dissociation constant of CS enzyme and OAA 140mM [14]
KcatCS Kcat of CS enzyme 18/min [14]
ECS Concentration of CS enzyme 1266ppm [13]
VmaxCS Maximum reaction rate of CS enzyme 0.108mM/L * min [13][14]
Km+ACO Michaelis constant of ACO enzyme in the forward reaction for Cit 11mM [15]
Kcat+ACO Kcat of ACO enzyme in the forward reaction 0.024mM/min * mg [15]
EACO Concentration of ACO enzyme 3481ppm [13]
Vmax+ACO Maximum reaction rate of ACO enzyme in the forward reaction 2.088mM/L * min [13][15]
KmACO Michaelis constant of ACO enzyme in the reverse reaction for Icit 0.015mM [15]
KcatACO Kcat of ACO enzyme in the reverse reaction 0.0035mM/min * mg [15]
VmaxACO Maximum reaction rate of ACO enzyme in the reverse reaction 3.045mM/L * min [13][15]
KmIDH Michaelis constant of IDH enzyme for Icit 0.0114mM [16]
KcatIDH Kcat of IDH enzyme 4572/min [16]
EIDH Concentration of IDH enzyme 3054ppm [13]
VmaxIDH Maximum reaction rate of IDH enzyme 34.56mM/L * min [13][16]
KmαKGDHC, CoA Michaelis constant of αKGDHC enzyme for CoA 0 Ideal value
KmαKGDHC, αKG Michaelis constant of αKGDHC enzyme for αKG 0.22mM [16]
KcatαKGDHC Kcat of αKGDHC enzyme 1236/min [16]
EαKGDHC Concentration of αKGDHC enzyme 2828ppm [13]
VmaxαKGDHC Maximum reaction rate of αKGDHC enzyme 8.738mM/L * min [13][16]
KmSCS Michaelis constant of SCS enzyme for SuccinylCoA 0.06mM [17]
KcatSCS Kcat of SCS enzyme 0.00002mM/min * mg [18]
ESCS Concentration of SCS enzyme 2759ppm [13]
VmaxSCS Maximum reaction rate of SCS enzyme 0.0138mM/L * min [13][18]
Km+MDH Michaelis constant of MDH enzyme in the forward reaction for OAA 0.049mM [19]
Kcat+MDH Kcat of MDH enzyme in the forward reaction 5400/min [19]
EMDH Concentration of MDH enzyme 6597ppm [20]
Vmax+MDH Maximum reaction rate of MDH enzyme in the forward reaction 137.16mM/L * min [19][20]
KmMDH Michaelis constant of MDH enzyme in the reverse reaction for Mal 2.6mM [19]
KcatMDH Kcat of MDH enzyme in the reverse reaction 1260/min [19]
VmaxMDH Maximum reaction rate of MDH enzyme in the reverse reaction 32mM/L * min [19][20]
Km+FH Michaelis constant of FH enzyme in the forward reaction for Mal 1.1mM [21]
Kcat+FH Kcat of FH enzyme in the forward reaction 0.059mM/min * mg [21]
EFH Concentration of FH enzyme 1613ppm [13]
Vmax+FH Maximum reaction rate of FH enzyme in the forward reaction 23.777mM/L * min [13][21]
KmFH Michaelis constant of FH enzyme in the reverse reaction for Fum 0.15mM [21]
KcatFH Kcat of FH enzyme in the reverse reaction 0.0066mM/min * mg [21]
VmaxFH Maximum reaction rate of FH enzyme in the reverse reaction 2.6598mM/L * min [13][21]
KmFRD Michaelis constant of FRD enzyme for Fum 0.028mM [22]
KcatFRD Kcat of FRD enzyme 22200/min [22]
EFRD Concentration of FRD enzyme 5000ppm Estimated value
VmaxFRD Maximum reaction rate of FRD enzyme 426.9mM/L * min [22]
KmPC Michaelis constant of PC enzyme for OAA 1.36mM [23]
KcatPC Kcat of PC enzyme 3570/min [23]
EPC Concentration of PC enzyme 5000ppm Estimated value
VmaxPC Maximum reaction rate of PC enzyme 89.25mL/L * min [23]
vATP Non-TCA cycle production rate of ATP 0mM/L * min Ideal value
vOAA Non-TCA cycle production rate of OAA 0mM/L * min Ideal value
vPyr Non-TCA cycle production rate of Pyr 0mM/L * min Ideal value
vAcCoA Non-TCA cycle production rate of AcCoA (−0.9 * AcCoA)mM/L * min Estimated value
vCit Non-TCA cycle production rate of Cit 0mM/L * min Ideal value
vIcit Non-TCA cycle production rate of Icit 0mM/L * min Ideal value
vαKG Non-TCA cycle production rate of αKG 0mM/L * min Ideal value
vSuccinylCoA Non-TCA cycle production rate of SuccinylCoA 0mM/L * min Ideal value
vSucc Non-TCA cycle production rate of Succ 0mM/L * min Ideal value
vFum Non-TCA cycle production rate of Fum 0mM/L * min Ideal value
vMal Non-TCA cycle production rate of Mal 0mM/L * min Ideal value
vCoA Non-TCA cycle production rate of CoA 0mM/L * min Ideal value

4.Ordinary Differential Equations

$$\frac{d[\text{ATP}]}{dt}=v_{ATP}+v_{8.5}+2.5\cdot (v_7+ v_{8.3}+ v_{8.4}+v_{9.1-}-v_{9.1+})-1.5\cdot v_{9.3}$$ $$\frac{d[\text{OAA}]}{dt}=v_{OAA}+v_4-v_{8.1}-v_{9.1+}+v_{9.1-}$$ $$\frac{d[\text{Pyr}]}{dt}=v_{Pyr}+v_4-v_7$$ $$\frac{d[\text{Ac}_\text{{CoA}}]}{dt}=v_{Ac_{CoA}}+v_5+v_6+v_7-v_{8.1}$$ $$\frac{d[\text{Cit}]}{dt}=v_{Cit}+v_{8.1}-v_{8.2+}+v_{8.2-}$$ $$\frac{d[\text{Icit}]}{dt}=v_{Icit}+v_{8.2+}-v_{8.2-}-v_{8.3}$$ $$\frac{d[\alpha \text{KG}]}{dt}=v_{\alpha KG}+v_{8.3}-v_{8.4}$$ $$\frac{d[\text{Succinyl}_\text{CoA}]}{dt}=v_{Succinyl_{CoA}}+v_{8.4}-v_{8.5}$$ $$\frac{d[\text{Succ}]}{dt}=v_{Succ}+v_5+v_6+v_{8.5}+v_{9.3}$$ $$\frac{d[\text{Fum}]}{dt}=v_{Fum}+v_{9.2+}-v_{9.2-}-v_{9.3}$$ $$\frac{d[\text{Mal}]}{dt}=v_{Mal}+v_{9.1+}-v_{9.1-}-v_{9.2+}+v_{9.2-}$$ $$\frac{d[\text{CoA}]}{dt}=v_{CoA}-v_5-v_6-v_7+v_{8.1}-v_{8.4}+v_{8.5}$$

5.Result Presentation:

fig 5. Rate of TCA cycle branch one
fig 6. Rate of TCA cycle branch two

VI.Succinate Extraction

1.Model Variables

Variable Unit Meaning
Succ mM/L Concentration of Succinate in the engineered bacteria
Produc mM/L Cumulative production of extracted Succinate

2.Metabolic Reactions

Reaction 11: Extraction of Succinate

$$\begin{align}Succ \rightarrow Produc\end{align}$$ Since we have introduced a plasmid containing the succinate efflux carrier protein gene into the engineered bacteria, we assume that the produced Succinate is stably and quickly excreted from the engineered bacteria and extracted in the system. The extraction rate is analogous to a first-order reaction rate formula. Meanwhile, since the bacterial volume only accounts for a small part of the total liquid volume, the Succinate concentration is multiplied by the coefficient rt to represent the Succinate concentration in the fermentation system. $$\begin{align}v_{11}=K_{Succ}\cdot [Succ]\cdot rt\end{align}$$

3.Parameter List:

Parameter Symbol Parameter Description Value Data Source
KSucc Extraction rate coefficient of Succ 0.5 Estimated value (slightly higher for a quicker balance)

4.Ordinary Differential Equations:

$$\frac{d[\text{Succ}]}{dt}=v_{Succ}+v_5+v_6+v_{8.5}+v_{9.3}-v_{11}$$ $$\frac{d[\text{Produc}]}{dt}=v_{11}$$

5.Result Presentation:

fig 7. Succinate production rate
fig 8. ATP consumption rate

VII.Model Conclusions and Guidance for Wet Lab Experiments:

  1. The rate of laccase decomposition of phenolic lignin is faster than that of non-phenolic lignin.
  2. Syringate has the highest proportion among lignin decomposition products, but its further metabolism is more difficult.
  3. After further metabolism, most decomposition products enter the TCA cycle via oxaloacetate and pyruvate, while a small part enters via Acetyl-CoA and directly generates the product Succinate.
  4. For the broken TCA cycle, Succinate is mainly produced through the equilibrium reaction in branch two (oxaloacetate, malate, fumarate) consuming energy.
  5. The production rate of Succinate is approximately 7mmol/L * min, where /L corresponds to per liter of fermentation system.
  6. ATP is consumed at a rate of about 20mmol/L * min, where /L corresponds to per liter of engineered bacterial cytoplasm, requiring supply of appropriate energy substances to maintain fermentation.
  7. Based on the rate bottlenecks revealed by the model, methods such as increasing the content of Syringate degradation enzymes, TCA cycle branch two enzymes, or constructing pathways to recycle Acetyl-CoA can be considered to further improve the system’s Succinate production.
fig 9. Rate after normalize

VIII.Complete List of Variables, Parameters, and Ordinary Differential Equations:

Complete Variable List:
Variable Unit Meaning
Lp: mM/L Phenolic Lignin concentration (based on oxidizable phenolic hydroxyl units)
Lnp mM/L Non-phenolic Lignin concentration (based on units oxidizable by mediators)
Mred mM/L Reduced Mediator concentration
Mox mM/L Oxidized Mediator radical concentration
Syr mM/L Concentration of Syringate in the fermentation system
Van mM/L Concentration of Vanillic in the fermentation system
pHB mM/L Concentration of p-Hydroxybenzoic in the fermentation system
ATP mM/L ATP production in the engineered bacteria
OAA mM/L Concentration of oxaloacetate in the engineered bacteria
Pyr mM/L Concentration of Pyruvate in the engineered bacteria
AcCoA mM/L Concentration of Acetyl-CoA in the engineered bacteria
Cit mM/L Concentration of Citrate in the engineered bacteria
Icit mM/L Concentration of Isocitrate in the engineered bacteria
αKG mM/L Concentration of α-Ketoglutarate in the engineered bacteria
SuccinylCoA mM/L Concentration of Succinyl-CoA in the engineered bacteria
Succ mM/L Concentration of Succinate in the engineered bacteria
Fum mM/L Concentration of Fumarate in the engineered bacteria
Mal mM/L Concentration of L-Malate in the engineered bacteria
CoA mM/L Concentration of CoA in the engineered bacteria
Produc mM/L Cumulative production of extracted Succinate
Complete Parameter List:
Parameter Symbol Parameter Description Value Data Source
vLp Feeding rate of phenolic lignin 0.01mM/L * min Estimated value
vLnp Feeding rate of non-phenolic lignin 0.05mM/L * min Estimated value
[Etotal] Total laccase concentration 1U/mL [1]
[Mtotal] Total mediator concentration (ABTS, HBT, etc.) 1mM [3]
Km, p Michaelis constant for phenolic lignin 0.8mM [2]
Km, m Michaelis constant for mediator (e.g., ABTS) 0.32mM [9]
Vmax, p Maximum reaction rate for lignin substrate 0.025mM/L * min [1]
a Proportion of syringate produced after complete decomposition of phenolic lignin 0.4 [10][11]
b Proportion of vanillic produced after complete decomposition of phenolic lignin 0.5 [10][11]
c Proportion of p-Hydroxybenzoic produced after complete decomposition of phenolic lignin 0.1 [10][11]
d Proportion of syringate produced after complete decomposition of non-phenolic lignin 0.85 [10]
e Proportion of vanillic produced after complete decomposition of non-phenolic lignin 0.15 [10]
f Proportion of p-Hydroxybenzoic produced after complete decomposition of non-phenolic lignin 0 [10]
rt Ratio of bacterial volume to total liquid volume in the fermentation system 1% Estimated value
KmSyr Michaelis constant of the key enzyme in syringate metabolism 15mM Estimated value
VmaxSyr Maximum reaction rate of the key enzyme in syringate metabolism 10mM/L * min Estimated value
KmVan Michaelis constant of the key enzyme in Vanillic metabolism 15mM Estimated value
VmaxVan Maximum reaction rate of the key enzyme in Vanillic metabolism 100mM/L * min Estimated value
KmpHB Michaelis constant of the key enzyme in p-Hydroxybenzoic metabolism 15mM Estimated value
VmaxpHB Maximum reaction rate of the key enzyme in p-Hydroxybenzoic metabolism 50mM/L * min Estimated value
KmPDHc, Pyr Michaelis constant of PDHc enzyme for Pyr 0.037mM [12]
KmPDHc, CoA Michaelis constant of PDHc enzyme for CoA 0 Ideal value
KcatPDHc Kcat of PDHc enzyme 0.0071mM/min * mg [12]
EPDHc Concentration of PDHc enzyme 3169ppm [13]
VmaxPDHc Maximum reaction rate of PDHc enzyme 5.62mM/L * min [12][13]
KmCS, AcCoA Michaelis constant of CS enzyme for AcCoA 0.0013mM [14]
KmCS, OAA Michaelis constant of CS enzyme for OAA 25.5mM [14]
KsCS, OAA Dissociation constant of CS enzyme and OAA 140mM [14]
KcatCS Kcat of CS enzyme 18/min [14]
ECS Concentration of CS enzyme 1266ppm [13]
VmaxCS Maximum reaction rate of CS enzyme 0.108mM/L * min [13][14]
Km+ACO Michaelis constant of ACO enzyme in the forward reaction for Cit 11mM [15]
Kcat+ACO Kcat of ACO enzyme in the forward reaction 0.024mM/min * mg [15]
EACO Concentration of ACO enzyme 3481ppm [13]
Vmax+ACO Maximum reaction rate of ACO enzyme in the forward reaction 2.088mM/L * min [13][15]
KmACO Michaelis constant of ACO enzyme in the reverse reaction for Icit 0.015mM [15]
KcatACO Kcat of ACO enzyme in the reverse reaction 0.0035mM/min * mg [15]
VmaxACO Maximum reaction rate of ACO enzyme in the reverse reaction 3.045mM/L * min [13][15]
KmIDH Michaelis constant of IDH enzyme for Icit 0.0114mM [16]
KcatIDH Kcat of IDH enzyme 4572/min [16]
EIDH Concentration of IDH enzyme 3054ppm [13]
VmaxIDH Maximum reaction rate of IDH enzyme 34.56mM/L * min [13][16]
KmαKGDHC, CoA Michaelis constant of αKGDHC enzyme for CoA 0 Ideal value
KmαKGDHC, αKG Michaelis constant of αKGDHC enzyme for αKG 0.22mM [16]
KcatαKGDHC Kcat of αKGDHC enzyme 1236/min [16]
EαKGDHC Concentration of αKGDHC enzyme 2828ppm [13]
VmaxαKGDHC Maximum reaction rate of αKGDHC enzyme 8.738mM/L * min [13][16]
KmSCS Michaelis constant of SCS enzyme for SuccinylCoA 0.06mM [17]
KcatSCS Kcat of SCS enzyme 0.00002mM/min * mg [18]
ESCS Concentration of SCS enzyme 2759ppm [13]
VmaxSCS Maximum reaction rate of SCS enzyme 0.0138mM/L * min [13][18]
Km+MDH Michaelis constant of MDH enzyme in the forward reaction for OAA 0.049mM [19]
Kcat+MDH Kcat of MDH enzyme in the forward reaction 5400/min [19]
EMDH Concentration of MDH enzyme 6597ppm [20]
Vmax+MDH Maximum reaction rate of MDH enzyme in the forward reaction 137.16mM/L * min [19][20]
KmMDH Michaelis constant of MDH enzyme in the reverse reaction for Mal 2.6mM [19]
KcatMDH Kcat of MDH enzyme in the reverse reaction 1260/min [19]
VmaxMDH Maximum reaction rate of MDH enzyme in the reverse reaction 32mM/L * min [19][20]
Km+FH Michaelis constant of FH enzyme in the forward reaction for Mal 1.1mM [21]
Kcat+FH Kcat of FH enzyme in the forward reaction 0.059mM/min * mg [21]
EFH Concentration of FH enzyme 1613ppm [13]
Vmax+FH Maximum reaction rate of FH enzyme in the forward reaction 23.777mM/L * min [13][21]
KmFH Michaelis constant of FH enzyme in the reverse reaction for Fum 0.15mM [21]
KcatFH Kcat of FH enzyme in the reverse reaction 0.0066mM/min * mg [21]
VmaxFH Maximum reaction rate of FH enzyme in the reverse reaction 2.6598mM/L * min [13][21]
KmFRD Michaelis constant of FRD enzyme for Fum 0.028mM [22]
KcatFRD Kcat of FRD enzyme 22200/min [22]
EFRD Concentration of FRD enzyme 5000ppm Estimated value
VmaxFRD Maximum reaction rate of FRD enzyme 426.9mM/L * min [22]
KmPC Michaelis constant of PC enzyme for OAA 1.36mM [23]
KcatPC Kcat of PC enzyme 3570/min [23]
EPC Concentration of PC enzyme 5000ppm Estimated value
VmaxPC Maximum reaction rate of PC enzyme 89.25mL/L * min [23]
vATP Non-TCA cycle production rate of ATP 0mM/L * min Ideal value
vOAA Non-TCA cycle production rate of OAA 0mM/L * min Ideal value
vPyr Non-TCA cycle production rate of Pyr 0mM/L * min Ideal value
vAcCoA Non-TCA cycle production rate of AcCoA (−0.9 * AcCoA)mM/L * min Estimated value
vCit Non-TCA cycle production rate of Cit 0mM/L * min Ideal value
vIcit Non-TCA cycle production rate of Icit 0mM/L * min Ideal value
vαKG Non-TCA cycle production rate of αKG 0mM/L * min Ideal value
vSuccinylCoA Non-TCA cycle production rate of SuccinylCoA 0mM/L * min Ideal value
vSucc Non-TCA cycle production rate of Succ 0mM/L * min Ideal value
vFum Non-TCA cycle production rate of Fum 0mM/L * min Ideal value
vMal Non-TCA cycle production rate of Mal 0mM/L * min Ideal value
vCoA Non-TCA cycle production rate of CoA 0mM/L * min Ideal value
KSucc Extraction rate coefficient of Succ 0.5 Estimated value (slightly higher for a quicker balance)
Complete Ordinary Differential Equations:

$$\frac{d[L_p]}{dt} = v_{L_{p}}-v_1 $$ $$\frac{d[L_{np}]}{dt} = v_{L_{np}}-v_3 $$ $$\frac{d[M_{ox}]}{dt} = v_2 - v_3 $$ $$\begin{align}[M_{red}] = [M_{total}] - [M_{ox}]\end{align}$$ $$\frac{d[\text{Syr}]}{dt}=a\cdot v_1+d\cdot v_3-v_4\cdot rt$$ $$\frac{d[\text{Van}]}{dt}=b\cdot v_1+e\cdot v_3-v_5\cdot rt$$ $$\frac{d[\text{pHB}]}{dt}=c\cdot v_1+f\cdot v_3-v_6\cdot rt$$ $$\frac{d[\text{ATP}]}{dt}=v_{ATP}+v_{8.5}+2.5\cdot (v_7+ v_{8.3}+ v_{8.4}+v_{9.1-}-v_{9.1+})-1.5\cdot v_{9.3}$$ $$\frac{d[\text{OAA}]}{dt}=v_{OAA}+v_4-v_{8.1}-v_{9.1+}+v_{9.1-}$$ $$\frac{d[\text{Pyr}]}{dt}=v_{Pyr}+v_4-v_7$$ $$\frac{d[\text{Ac}_\text{{CoA}}]}{dt}=v_{Ac_{CoA}}+v_5+v_6+v_7-v_{8.1}$$ $$\frac{d[\text{Cit}]}{dt}=v_{Cit}+v_{8.1}-v_{8.2+}+v_{8.2-}$$ $$\frac{d[\text{Icit}]}{dt}=v_{Icit}+v_{8.2+}-v_{8.2-}-v_{8.3}$$ $$\frac{d[\alpha \text{KG}]}{dt}=v_{\alpha KG}+v_{8.3}-v_{8.4}$$ $$\frac{d[\text{Succinyl}_\text{CoA}]}{dt}=v_{Succinyl_{CoA}}+v_{8.4}-v_{8.5}$$ $$\frac{d[\text{Succ}]}{dt}=v_{Succ}+v_5+v_6+v_{8.5}+v_{9.3}-v_{11}$$ $$\frac{d[\text{Fum}]}{dt}=v_{Fum}+v_{9.2+}-v_{9.2-}-v_{9.3}$$ $$\frac{d[\text{Mal}]}{dt}=v_{Mal}+v_{9.1+}-v_{9.1-}-v_{9.2+}+v_{9.2-}$$ $$\frac{d[\text{CoA}]}{dt}=v_{CoA}-v_5-v_6-v_7+v_{8.1}-v_{8.4}+v_{8.5}$$ $$\frac{d[\text{Produc}]}{dt}=v_{11}$$

IX.Complete MATLAB code:

clear
clc

%%

first=[0.700;0.0008;0; 0;0;0; 0;0;0;
       0;0;0; 0;0;0; 0;0;-100; 0];

% 1 :Lp
% 2 :Lnp
% 3 :Mox
% 4 :Syr
% 5 :Van
% 6 :pHB
% 7 :ATP
% 8 :OAA
% 9 :Pyr
% 10:AcCoA
% 11:Cit
% 12:Icit
% 13:akG
% 14:SucCoA
% 15:Succ
% 16:Fum
% 17:Mal
% 18:CoA
% 19:Produc

function d=fuc(t,y)

Etotal  =2;
Mtotal  =1;
Kp      =0.8;
Km      =0.32;
Vp      =0.025;
Vm      =0.25;
k3      =60;
a       =0.4;
b       =0.5;
c       =0.1;
d       =0.85;
e       =0.15;
f       =0;
rt      =0.01;

KSyr    =15;
VSyr    =10;
KVan    =15;
VVan    =100;
KpHB    =15;
VpHB    =50;

KPDHcPyr    =0.037;
KPDHcCoA    =0;
VPDHc       =5.62;
KCSAcCoA    =0.0013;
KCSOAAm     =25.5;
KCSOAAs     =140;
VCS         =0.108;%%%%%%%
KACO1       =11;
VACO1       =2.088;
KACO0       =0.015;
VACO0       =3.045;
KIDH        =0.0114;
VIDH        =34.56;
KaKGCoA     =0;
KaKGaKG     =0.22;
VaKG        =8.738;
KSUCL       =0.06;
VSUCL       =0.0138;
KMDH1       =0.049;
VMDH1       =137.16;
KMDH0       =2.6;
VMDH0       =32;
KFH1        =1.1;
VFH1        =23.777;
KFH0        =0.15;
VFH0        =2.6598;
KFRD        =0.028;
VFRD        =426.9;
KPC         =1.36;
VPC         =89.25;
vATP        =0;
vOAA        =0;
vPyr        =0;
vAcCoA      =-0.9*y(10);
vCit        =0;
vIcit       =0;
vaKG        =0;
vSucCoA     =0;
vSucc       =0;
vFum        =0;
vMal        =0;
vCoA        =0;
KSucc       =0.5;

v1=Vp*y(1)/(Kp*(1+(Mtotal-y(3))/Km)+y(1));
v2=Vm*(Mtotal-y(3))/(Km*(1+y(1)/Kp)+Mtotal-y(3));
v3=k3*y(3)*y(2);

v4=VSyr*y(4)/(KSyr+y(4));
v5=VVan*y(5)/(KVan+y(5));
v6=VpHB*y(6)/(KpHB+y(6));
v7=VPDHc*y(9)*y(18)/( KPDHcPyr*y(18)+ KPDHcCoA*y(9)+ y(9)*y(18) );

v81=VCS*y(8)*y(10)/( KCSAcCoA*y(8)+ KCSOAAm*y(10)+ y(8)*y(10)+ KCSOAAs*KCSAcCoA );
v821=VACO1*y(11)/(KACO1+y(11));
v820=VACO0*y(12)/(KACO0+y(12));
v83=VIDH*y(12)/(KIDH+y(12));
v84=VaKG*y(13)*y(18)/( KaKGCoA*y(13)+ KaKGaKG*y(18)+ y(13)*y(18) );
v85=VSUCL*y(14)/(KSUCL+y(14));

v911=VMDH1*y(8)/(KMDH1+y(8));
v910=VMDH0*y(17)/(KMDH0+y(17));
v921=VFH1*y(17)/(KFH1+y(17));
v920=VFH0*y(16)/(KFH0+y(16));
v93=VFRD*y(16)/(KFRD+y(16));

v10=VPC*y(9)/(KPC+y(9));

v11=KSucc*y(15)*rt;

Lp=-v1+0.01;
Lnp=-v3+0.05;
Mox=v2-v3;
Syr=a*v1+d*v3-v4*rt;
Van=b*v1+e*v3-v5*rt;
pHB=c*v1+f*v3-v6*rt;
ATP=vATP+v85+2.5*(v7+v83+v84+v910-v911)-1.5*v93-v10;
OAA=vOAA+v4-v81-v911+v910+v10;
Pyr=vPyr+v4-v7-v10;
AcCoA=vAcCoA+v5+v6+v7-v81;
Cit=vCit+v81-v821+v820;
Icit=vIcit+v821-v820-v83;
aKG=vaKG+v83-v84;
SucCoA=vSucCoA+v84-v85;
Succ=vSucc+v5+v6+v85+v93-v11;
Fum=vFum+v921-v920-v93;
Mal=vMal+v911-v910-v921+v920;
CoA=vCoA-v5-v6-v7+v81-v84+v85;
Produc=v11;

d=[Lp;Lnp;Mox;Syr;Van;pHB;ATP;OAA;
    Pyr;AcCoA;Cit;Icit;aKG;SucCoA;
    Succ;Fum;Mal;CoA;Produc];
end

options = odeset('NonNegative', [1,2,3,4,5,6,8,9,10,11,12,13,14,15,16,17,19]);

[t0,y0] = ode45(@fuc,[0 900],first,options);

t=t0(1:10000:end, :);
y=y0(1:10000:end, :);

%% Obtain the process of variable changes
Etotal  =2;
Mtotal  =1;
Kp      =0.8;
Km      =0.05;
Vp      =0.025;
Vm      =0.25;
k3      =60;
a       =0.4;
b       =0.5;
c       =0.1;
d       =0.85;
e       =0.15;
f       =0;
rt      =0.01;

KSyr    =15;
VSyr    =10;
KVan    =15;
VVan    =100;
KpHB    =15;
VpHB    =50;

KPDHcPyr    =0.037;
KPDHcCoA    =0;
VPDHc       =5.62;
KCSAcCoA    =0.0013;
KCSOAAm     =25.5;
KCSOAAs     =140;
VCS         =0.108;
KACO1       =11;
VACO1       =2.088;
KACO0       =0.015;
VACO0       =3.045;
KIDH        =0.0114;
VIDH        =34.56;
KaKGCoA     =0;
KaKGaKG     =0.22;
VaKG        =8.738;
KSUCL       =0.06;
VSUCL       =0.0138;
KMDH1       =0.049;
VMDH1       =137.16;
KMDH0       =2.6;
VMDH0       =32;
KFH1        =1.1;
VFH1        =23.777;
KFH0        =0.15;
VFH0        =2.6598;
KFRD        =0.028;
VFRD        =426.9;
KPC         =1.36;
VPC         =89.25;
vATP        =0;
vOAA        =0;
vPyr        =0;
vAcCoA      =-0.9*y(10);
vCit        =0;
vIcit       =0;
vaKG        =0;
vSucCoA     =0;
vSucc       =0;
vFum        =0;
vMal        =0;
vCoA        =100;
KSucc       =0.5;

v1=Vp.*y(:,1)./(Kp*(1+(Mtotal-y(:,3))/Km)+y(:,1));
v2=Vm*(Mtotal-y(:,3))./(Km*(1+y(:,1)/Kp)+Mtotal-y(:,3));
v3=k3.*y(:,3).*y(:,2);

v4=VSyr.*y(:,4)./(KSyr+y(:,4));
v5=VVan.*y(:,5)./(KVan+y(:,5));
v6=VpHB.*y(:,6)./(KpHB+y(:,6));
v7=VPDHc.*y(:,9).*y(:,18)./( KPDHcPyr.*y(:,18)+ KPDHcCoA.*y(:,9)+ y(:,9).*y(:,18) );

v81=VCS.*y(:,8).*y(:,10)./( KCSAcCoA.*y(:,8)+ KCSOAAm.*y(:,10)+ y(:,8).*y(:,10)+ KCSOAAs*KCSAcCoA );
v821=VACO1.*y(:,11)./(KACO1+y(:,11));
v820=VACO0.*y(:,12)./(KACO0+y(:,12));
v83=VIDH.*y(:,12)./(KIDH+y(:,12));
v84=VaKG.*y(:,13).*y(:,18)./( KaKGCoA.*y(:,13)+ KaKGaKG.*y(:,18)+ y(:,13).*y(:,18) );
v85=VSUCL.*y(:,14)./(KSUCL+y(:,14));

v911=VMDH1.*y(:,8)./(KMDH1+y(:,8));
v910=VMDH0.*y(:,17)./(KMDH0+y(:,17));
v921=VFH1.*y(:,17)./(KFH1+y(:,17));
v920=VFH0.*y(:,16)./(KFH0+y(:,16));
v93=VFRD.*y(:,16)./(KFRD+y(:,16));

v10=VPC.*y(:,9)./(KPC+y(:,9));

v11=KSucc.*y(:,15)*rt;

Lp=-v1+0.01;
Lnp=-v3+0.05;
Mox=v2-v3;
Syr=a*v1+d*v3-v4*rt;
Van=b*v1+e*v3-v5*rt;
pHB=c*v1+f*v3-v6*rt;
ATP=vATP+v85+2.5*(v7+v83+v84+v910-v911)-1.5*v93-v10;
OAA=vOAA+v4-v81-v911+v910+v10;
Pyr=vPyr+v4-v7-v10;
AcCoA=vAcCoA+v5+v6+v7-v81;
Cit=vCit+v81-v821+v820;
Icit=vIcit+v821-v820-v83;
aKG=vaKG+v83-v84;
SucCoA=vSucCoA+v84-v85;
Succ=vSucc+v5+v6+v85+v93-v11;
Fum0=vFum+v921-v920-v93;
Fum = movmean(Fum0, 3);
Mal=vMal+v911-v910-v921+v920;
CoA=vCoA-v5-v6-v7+v81-v84+v85;
Produc=v11;


%% Figure sum:
figure;
vP=v1+v3;
vin=vOAA+v4+vSucc+v5+v6;
vout=v11;
vA=vATP+v85+2.5*(v7+v83+v84+v910-v911)-1.5*v93-v10;
vP=normalize(vP,'range');
vin=normalize(vin,'range');
vout=normalize(vout,'range');
vA=normalize(-vA,'range');
hold on;
plot(t,vP,'LineWidth',2);
plot(t,vin,'LineWidth',2);
plot(t,vout,'LineWidth',2);
plot(t,vA,'LineWidth',2);
legend('Lignin','Metabolic Entry into TCA','Succinate production','ATP consumption');
title('Rate after normalize');
xlabel('Time /min');
ylabel('Velocity');
hold off;

%% Other plottings have been omitted

FBA Model: Model for Succinate Yield Prediction

The model aims at predicting the succinate production with the dual-microbes system in industry. According to the model, each 1 g biomass can produce 5.343 g succinate each hour.

Principle & Design

The model is based on the COnstraint-Based Reconstruction and Analysis (COBRA) methods which has been wildly used to model the metabolic networks in both prokaryotes and eukaryotes on the genome-scale. This model does not require difficult-to-measure kinetic parameters. Instead, it lists the stoichiometric coefficients of each metabolic reaction in the form of a numerical matrix as constraints. Each row represents a metabolite and each column represents a reaction. Under steady state, the flux of each reaction is given by Sv = 0, which defines a linear equation system. Then, linear programming is used to determine the flux distribution, which is optimized or minimized by maximizing or minimizing the objective function within the allowable flux space defined by the mass balance equation and the reaction boundaries[24].

fig 10. Formulation of an FBA problem (Bernhard Ø Palsson, Nature Biotechnology, 2010)

With the model, the hourly succinate production and biomass by 1 g biomass can be roughly calculated. Then, with integration, we might get the total production required in the industrial design. With proper construction of the matebolism network, it might be a method to offer opimized prediction in absence of experimental data on a large scale.

Realization

The constrcution of the model started from a exist model downloaded from BIGG for wild type P.Putida. Although exist model for T.reesei was unvailable, the core metabolism was similar. Therefore, this model served as the base for the dual-microbes system and extra reactions of both engineered microbses were added to it later[25].

# import model of wild P.Putida from IBGG
import cobra
model = cobra.io.read_sbml_model('iJN746.xml')

# create a new reaction for succinate output
from cobra import Model, Reaction, Metabolite

reaction = Reaction('SUCCt')
reaction.name = 'succinate transport'
reaction.subsystem = 'succinate transport'
reaction.lower_bound = 0.0
reaction.upper_bound = 999999.9

succ_c = Metabolite(
    'succ_c',
    formula = 'C4H4O4',
    name='Succinate',
    compartment='c')
succ_e = Metabolite(
    'succ_e',
    formula = 'C4H4O4',
    name='Succinate',
    compartment='c')

reaction.add_metabolites({
    succ_c: -1.0,
    succ_e: 1.0,
})  

reaction.reaction

model.add_reactions([reaction])

Table.1. the Reactions added in the final model

Reaction Stoichiometry Usage
FRD7 Fumarate + Ubiquinol-8 –> Ubiquinone-8 + Succinate fumarate reductase
SUCCt Succinate_c –> Succinate_e succinate output
CELASE Cellobiose + H2O H2O –> 2.0 D-Glucose cellulose degradation
DECOU p-Coumaryl alcohol –> ethylene + 4-hydroxybenzaldehyde p-Coumaryl alcohol degradation
DECON coniferyl alcohol –> ethylene + Vanillin Coniferyl alcohol degradation
DESIN sinapyl alcohol –> ethylene + syringaldehyde Sinapyl alcohol degradation
SYRDEM H+ + Nicotinamide adenine dinucleotide phosphate - reduced + O2 O2 + syringate –> Formaldehyde + H2O + Nicotinamide adenine dinucleotide phosphate + 3-O-methylgallate syringate demethylation
OMGDEM H+ + Nicotinamide adenine dinucleotide phosphate - reduced + O2 + 3-O-methylgallate –> Formaldehyde + Gallic acid + H2O + Nicotinamide adenine dinucleotide phosphate 3-O-methylgallate demethylation
SYRO H2O+ syringaldehyde –> 2.0 H+ + Nicotinamide adenine dinucleotide + syringate syringaldehyde oxidation
SYRDEtex Syringaldehyde <=> Syringaldehyde Syringaldehyde transport
SYRDEpp H+ + Syringaldehyde <=> H+ + syringaldehyde Syringaldehyde transport
4HBALDtex 4-Hydroxybenzaldehyde <=> 4-Hydroxybenzaldehyde 4-Hydroxybenzaldehyde transport
4HBALDpp H+ + 4-Hydroxybenzaldehyde <=> H+ + 4-hydroxybenzaldehyde 4-Hydroxybenzaldehyde transport
CELLBtex cellobiose <=> 4-Hydroxybenzaldehyde cellobiose transport
CELLBpp H+ + 4-Hydroxybenzaldehyde <=> Cellobiose + H+ cellobiose transport
COUMARYLtex p-Coumaryl alcohol <=> 4-Hydroxybenzaldehyde coumaryl alcohol transport
COUMARYLpp H+ + 4-Hydroxybenzaldehyde <=> p-Coumaryl alcohol + H+ coumaryl alcohol transport
CONIFERYLtex coniferyl alcohol <=> coniferyl alcohol coniferyl alcohol transport
CONIFERYLpp coniferyl alcohol + H+ <=> Coniferyl alcohol + H+ coniferyl alcohol transport
SINAPYLtex sinapyl alcohol <=> sinapyl alcohol sinapyl alcohol transport
SINAPYLpp sinapyl alcohol + H+ <=> Sinapyl alcohol + H+ sinapyl alcohol transport

Then, the bounds of the reactions controled by the genes to be blocked were set as “(0,0)”. In this model, the reactions where succinate is transferd to fumarate was blocked. After that, the medium was set according to the composition of the broth after the first fermentation.

# block transformation of succinate to fumarate
model.reactions.get_by_id('SUCD1').bounds = (-9999.9,0)
model.reactions.get_by_id('SUCDi').bounds = (0,0)

Table.2. the medium composition

Component Max Flux Source
Glucose 1.01 cellulose and hemicellulose degration
Syringaldehyde 0.15 lignin degration
Vanillin 0.16 lignin degradation
4-Hydroxybenzaldehyde 0.15 lignin degration
Cellobiose 2.53 cellulose & hemicellulose
Coumaryl Alcohol 0.32 coumaryl alcohol degradation
Coniferyl Alcohol 0.33 coniferyl Alcohol degration
Sinapyl Alcohol 0.32 Sinapyl degration
# change your medium
medium['EX_glc__D_e'] = 1.01
model.medium = medium

Result & Discussion

Solve the model with the optimizing projective as the reaction where succinate is produced in the Kreb’s cycle, and then the uptake and secrection can be print out as listed below. These data were used in the prediction of succinate production which can be found on the page for hardware.

# solve the model and output
model.objective = "SUCOAS"
model.optimize()
model.summary()
fig 11. The output of the FBA model

The model also has something to be improved or noticed:

  • The basic model of wild types isn’t the same as what they should be in live microbes. There’s surely some reactions missing.
  • The time and the conversion rate of each reaction isn’t considered.
  • A steady state is assumed so that it’s not the same as the real fermentation process.
  • The model can only provide the ideal case, and for industry, a large-scale experiment is always neccesary.

Dual-Species Microbial System: Mathematical Modeling and Simulation

Model Description

This document describes a mathematical model of a dual-species microbial system consisting of Trichoderma reesei and Pseudomonas putida. The model captures the synergistic interaction where T. reesei degrades lignin to produce aromatic compounds that serve as growth substrates for P. putida, which in turn produces succinate as a valuable metabolic product[26].

The system represents a typical syntrophic relationship in microbial communities, where the metabolic activities of one species create favorable conditions for another. This model provides a quantitative framework for understanding and optimizing such cooperative systems for industrial applications like lignocellulosic biomass conversion[27].

Basic Assumptions

  1. Spatial Homogeneity: The system is well-mixed with uniform distribution of all components.

  2. Monod Kinetics: Microbial growth follows Monod kinetics, where growth rate depends on limiting substrate concentration.

  3. Enzyme-Mediated Reactions: Lignin degradation is catalyzed by laccase enzymes produced by T. reesei, following Michaelis-Menten kinetics.

  4. Product Inhibition: High concentrations of metabolic products (particularly succinate) can inhibit microbial growth.

  5. Mass Conservation: Substrate consumption, biomass production, and product formation are connected through yield coefficients.

  6. Dynamic Enzyme Production: Enzyme synthesis is regulated by substrate induction and follows first-order kinetics.

  7. Non-growth Associated Maintenance: Microbial populations experience natural decay rates.

Model Equations

State Variables

Variable Description Units
N1 Trichoderma reesei population density g/L
N2 Pseudomonas putida population density g/L
S1 Lignin concentration g/L
E Laccase enzyme concentration U/L
S2 Succinate concentration g/L
P Aromatic compounds concentration g/L
F1 Nutrient 1 concentration (for T. reesei) g/L
F2 Nutrient 2 concentration (for P. putida) g/L

Growth Rate Functions

Trichoderma reesei growth rate: $$ \mu_1 = \mu_{1,max} \cdot \frac{F_1}{K_{F1} + F_1} \cdot \frac{1}{1 + S_2/K_{i1}} $$

Pseudomonas putida growth rate: $$ \mu_2 = \mu_{2,max} \cdot \frac{P}{K_P + P} $$

Enzyme Production and Metabolic Reactions

Laccase production: $$ r_E = k_{E1} + k_{E2} \cdot \frac{S_1}{K_E + S_1} $$

Aromatic compounds production: $$ r_P = v_{P1} \cdot E \cdot \frac{S_1}{K_{S1} + S_1} $$

Ordinary Differential Equations

The system dynamics are described by the following set of ordinary differential equations:

Microbial Population Dynamics

Trichoderma reesei: $$ \frac{dN_1}{dt} = \mu_1 \cdot N_1 - k_{d1} \cdot N_1 $$

Pseudomonas putida: $$ \frac{dN_2}{dt} = \mu_2 \cdot N_2 - k_{d2} \cdot N_2 $$

Substrate and Metabolite Dynamics

Lignin consumption: $$ \frac{dS_1}{dt} = -\frac{1}{Y_{P1}} \cdot r_P \cdot N_1 $$

Laccase enzyme dynamics: $$ \frac{dE}{dt} = r_E \cdot N_1 - k_{dE} \cdot E $$

Succinate production: $$ \frac{dS_2}{dt} = Y_{S2P} \cdot \frac{1}{Y_{X2P}} \cdot \mu_2 \cdot N_2 $$

Aromatic compounds dynamics: $$ \frac{dP}{dt} = r_P \cdot N_1 - \frac{1}{Y_{X2P}} \cdot \mu_2 \cdot N_2 - k_{dP} \cdot P $$

Nutrient Consumption

Nutrient 1 (for T. reesei): $$ \frac{dF_1}{dt} = -\frac{1}{Y_{X1F1}} \cdot \mu_1 \cdot N_1 $$

Nutrient 2 (for P. putida): $$ \frac{dF_2}{dt} = -\frac{1}{Y_{X2F2}} \cdot \mu_2 \cdot N_2 $$

Parameter Definitions

Parameter Description Typical Value Units
μ1, max Maximum growth rate of T. reesei 0.8 h⁻¹
μ2, max Maximum growth rate of P. putida 0.7 h⁻¹
KF1 Half-saturation constant for F1 2.0 g/L
KP Half-saturation constant for P 1.0 g/L
Ki1 Inhibition constant of S2 on N1 15.0 g/L
kd1, kd2 Microbial decay rates 0.05, 0.04 h⁻¹
YX1F1 Yield of N1 on F1 0.4 g/g
YX2P Yield of N2 on P 0.35 g/g
YX2F2 Yield of N2 on F2 0.5 g/g
YP1 Yield of P from S1 0.3 g/g
YS2P Yield of S2 from P 0.6 g/g
vP1 Maximum P production rate 0.25 g/(U·h)
KS1 Half-saturation for S1 degradation 1.5 g/L
kE1 Basal laccase production 0.02 U/(g·h)
kE2 Induced laccase production 0.15 U/(g·h)
KE Half-saturation for S1 induction 1.0 g/L
kdE Laccase degradation rate 0.1 h⁻¹
kdP P degradation rate 0.08 h⁻¹

Results

fig 13. General results of the dual species microbial system

System Dynamics

The model predicts several characteristic phases in the dual-species system:

  1. Lag Phase: Initial period where T. reesei adapts and begins producing laccase enzymes.

  2. Lignin Degradation Phase: Exponential production of aromatic compounds as laccase concentration increases and lignin is degraded.

  3. P. putida Growth Phase: Delayed growth of P. putida as aromatic compounds accumulate to sufficient concentrations.

  4. Succinate Production: Significant succinate accumulation occurs during the stationary phase of P. putida growth.

  5. System Decline: Nutrient depletion and accumulation of inhibitory products lead to population decline.

Key Features

  • Cross-feeding Dynamics: The time-delayed growth of P. putida demonstrates the dependency on T. reesei for metabolic intermediates.

  • Enzyme Induction: Laccase production shows induction kinetics in response to lignin presence.

  • Product Inhibition: The inhibitory effect of succinate on T. reesei creates feedback regulation in the system.

  • Resource Competition: Both species compete for general nutrients while maintaining their specialized metabolic roles.

Biological Significance

This model captures essential features of microbial syntrophy where:

  • Metabolic specialization enables efficient resource utilization
  • Cross-feeding creates stable cooperative interactions
  • Enzyme regulation allows adaptation to changing environmental conditions
  • Product inhibition provides natural population control mechanisms

The mathematical framework serves as a valuable tool for optimizing bioprocess conditions, predicting system behavior under different scenarios, and understanding the fundamental principles governing microbial community interactions.

Alternative Scenarios

Scenario 1:Base Model

This scenario is the baseline scenario described above, with no modifications.

fig 14. Scenario 1:Base Model

Scenario 2:Mutual Nutritional Dependency

Model Description

In this scenario, the growth rate of Trichoderma reesei (μ₁) from Scenario 1, originally defined as: $$ \mu_1 = \mu_{1,max} \cdot \frac{F_1}{K_{F1} + F_1} \cdot \frac{1}{1 + S_2/K_{i1}} $$ is modified to: $$ \mu_1 = \mu_{1,max} \cdot \frac{F_1}{K_{F1} + F_1} \cdot \frac{S_2}{K_{S2} + S_2} $$

A new constant, KS2 , is introduced:

Parameter Description Typical Value Units
KS2 Half-saturation for S2 dependency 1.5 g/L

We establish a mutual dependency relationship where Trichoderma reesei requires succinate produced by Pseudomonas putida for optimal growth. This creates a true syntrophic relationship where both species depend on each other’s metabolic activities.

Key Modifications
  • Added succinate dependency to T. reesei growth
  • Maintained aromatic compound dependency for P. putida
  • Creates a tightly coupled system with mutual benefits
Model Results
fig 15. Scenario 2:Mutual Nutritional Dependency

Scenario 3:Aromatic Compound Toxicity and Detoxification

Model Description

In this scenario, the growth rate of Trichoderma reesei (μ₁) from Scenario 1, originally defined as: $$ \mu_1 = \mu_{1,max} \cdot \frac{F_1}{K_{F1} + F_1} \cdot \frac{1}{1 + S_2/K_{i1}} $$ is modified to: $$ \mu_1 = \mu_{1,max} \cdot \frac{F_1}{K_{F1} + F_1} \cdot \frac{1}{1 + P/K_{iP}} $$

A new constant, KiP , is introduced:

Parameter Description Typical Value Units
KiP Inhibition constant for P toxicity 3.0 g/L

This scenario introduces toxicity dynamics where aromatic compounds (P) produced by T. reesei inhibit its own growth, creating a dependency on P. putida for detoxification through consumption of these compounds.

Key Modifications
  • Added inhibitory effect of P on T. reesei growth
  • P. putida serves as detoxifier by consuming P
  • Creates a detoxification-based mutualism
Model Results
fig 16. Scenario 3:Aromatic Compound Toxicity and Detoxification

Scenario 4:Batch Fermentation (Separate Cultivation)

Model Description

In this scenario, we assume that the growth rates of T. reesei and P. putida are independent of each other. Furthermore, the fermentation process is designed as a two-stage, separated cultivation:

  • Stage 1: Only T. reesei is cultivated.
  • Stage 2: Only P. putida is cultivated, utilizing the products from Stage 1.

This scenario implements a two-stage batch fermentation process where T. reesei and P. putida are cultivated separately. This represents industrial processes where cross-contamination must be avoided or where optimal conditions differ significantly between species.

Key Features
  • Stage 1: T. reesei cultivation for lignin degradation and P production
  • Stage 2: P. putida cultivation using Stage 1 products
  • No direct microbial interaction
  • Sequential optimization of each process
fig 17. Scenario 4:Batch Fermentation (Separate Cultivation)

Comparative Analysis

Performance Metrics Comparison

Scenario Final N₁ Final N₂ S₂ Production Process Efficiency Stability
Baseline Medium Medium Medium Medium Medium
Mutual Dependency High High High High High
Toxicity-Detox Low-Medium High High Medium High
Batch Process High (Stage1) High (Stage2) Very High Highest Very High

Biological Implications

  1. Mutual Dependency (Scenario 2): Creates the most stable cooperative system but requires careful balancing of growth rates.

  2. Toxicity-Detoxification (Scenario 3): Provides strong evolutionary pressure for cooperation but may limit maximum population densities.

  3. Batch Process (Scenario 4): Offers highest product yields and process control but requires additional operational steps and infrastructure.

Feeding Strategy Analysis

fig 18. Feeding Strategy Analysis

In industrial settings, optimization efforts typically focus on maximizing final product yield while minimizing input costs. Accordingly, this study investigates the impact of the initial concentrations of substrates F₁ and F₂ on the final yield of product S₂ across the baseline scenario. Our simulations reveal that a lower initial concentration of F₁ consistently enhances S₂ yield, whereas the initial concentration of F₂ has no discernible impact. The underlying mechanism can be explained as follows: a lower initial F₁ concentration suppresses the growth rate of N₁, which in turn slows the production of S₂, resulting in a lower S₂ concentration. This reduced S₂ level alleviates its inhibitory effect on N₁ (since g₁ is inhibited by S₂), thereby enabling N₁ to sustain its growth for an extended duration. This prolonged growth phase consequently extends the production period for P and the growth phase for N₂. Conversely, the consumption of F₂ is an independent process, decoupled from both S₂ generation and its own initial concentration, thus rendering the initial F₂ level irrelevant to the final S₂ yield. The identification of key control points and the optimal allocation of resources in a production system are crucial. They can provide a universal optimization strategy for enhancing efficiency and reducing consumption in complex industrial processes. These results may offer a valuable reference for future industrial production.

Industrial Application Recommendations

  • For maximum stability: Mutual dependency scenario
  • For maximum product yield: Batch process
  • For evolutionary robustness: Toxicity-detoxification scenario
  • For simplicity: Baseline scenario

Each scenario offers distinct advantages depending on the specific industrial constraints and objectives, allowing for tailored implementation based on production goals and available resources.

4 Reference

  1. Salem, M.M., Mohamed, T.M., Shaban, A.M. et al. Optimization, purification and characterization of laccase from a new endophytic Trichoderma harzianum AUMC14897 isolated from Opuntia ficus-indica and its applications in dye decolorization and wastewater treatment. Microb Cell Fact 23, 266 (2024). https://doi.org/10.1186/s12934-024-02530-x ↩︎
  2. Rawal, R.S., Mehant, A. & Suman, S.K. Deciphering ligninolytic enzymes in the secretome of Pycnoporus sp. and their potential in degradation of 2-chlorophenol. Environ Sci Pollut Res 30, 92830–92841 (2023). https://doi.org/10.1007/s11356-023-28932-9 ↩︎
  3. Cheng, C.-M., Patel, A. K., Singhania, R. R., Tsai, C.-H., Chen, S.-Y., Chen, C.-W., & Dong, C. D. (2021). Heterologous expression of bacterial CotA-laccase, characterization and its application for biodegradation of malachite green. Bioresource Technology, 340, 125708. https://doi.org/10.1016/j.biortech.2021.125708 ↩︎
  4. Gujjala, L. K. S., Bandyopadhyay, T. K., & Banerjee, R. (2016). Kinetic modelling of laccase mediated delignification of Lantana camara. Bioresource technology, 212, 47–54. https://doi.org/10.1016/j.biortech.2016.04.006 ↩︎
  5. Sampaio, L. M. P., Padrão, J., Faria, J., Silva, J. P., Silva, C. J., Dourado, F., & Zille, A. (2016). Laccase immobilization on bacterial nanocellulose membranes: Antimicrobial, kinetic and stability properties. Carbohydrate Polymers, 145, 1–12. https://doi.org/10.1016/j.carbpol.2016.03.009 ↩︎
  6. Asgher, M., Kamal, S., & Iqbal, H. M. N. (2012). Improvement of Catalytic Efficiency, Thermo-stability and Dye Decolorization Capability of Pleurotus ostreatus IBL-02 laccase by Hydrophobic Sol Gel Entrapment. Chemistry Central Journal, 6(1), 110. https://doi.org/10.1186/1752-153X-6-110 ↩︎
  7. Claro, F. C., de Lima, G. G., de Lima, T. A. M., et al. (2025). Characterisation of laccase-mediated lignin polymerisation: implications for molecular weight, thermal stability, and electrical properties. Biomass Conversion and Biorefinery, 15, 2479–2494. https://doi.org/10.1007/s13399-023-05040-9 ↩︎
  8. Wang, G., Post, W. M., Mayes, M. A., Frerichs, J. T., & Sindhu, J. (2012). Parameter estimation for models of ligninolytic and cellulolytic enzyme kinetics. Soil Biology and Biochemistry, 48, 28-38. https://doi.org/10.1016/j.soilbio.2012.01.011 ↩︎
  9. Floch, C., Alarcon-Gutiérrez, E., & Criquet, S. (2007). ABTS assay of phenol oxidase activity in soil. Journal of Microbiological Methods, 71(3), 319–324. https://doi.org/10.1016/j.mimet.2007.09.020 ↩︎
  10. Martínez, Á. T., Rencoret, J., Marques, G., Gutiérrez, A., Ibarra, D., Jiménez-Barbero, J., & del Río, J. C. (2008). Monolignol acylation and lignin structure in some nonwoody plants: A 2D NMR study. Phytochemistry, 69(16), 2831–2843. https://doi.org/10.1016/j.phytochem.2008.08.009 ↩︎
  11. Kurek, B., Martinez-inigo, M. J., Artaud, I., Hames, B. R., Lequart, C., & Monties, B. (1998). Structural features of lignin determining its biodegradation by oxidative enzymes and related systems. Polymer Degradation and Stability, 59(1–3), 359–364. https://doi.org/10.1016/S0141-3910(97)00155-2 ↩︎
  12. Liu, X., & Bisswanger, H. (2003). Solvent isotope effect on the reaction catalysed by the pyruvate dehydrogenase complex from Escherichia coli. Biological chemistry, 384(4), 673–679. https://doi.org/10.1515/BC.2003.075 ↩︎
  13. https://pax-db.org/dataset/160488/1991256584 ↩︎
  14. Andi, B., West, A. H., & Cook, P. F. (2004). Kinetic mechanism of histidine-tagged homocitrate synthase from Saccharomyces cerevisiae. Biochemistry, 43(37), 11790–11795. https://doi.org/10.1021/bi048766p ↩︎
  15. Jordan, P. A., Tang, Y., Bradbury, A. J., Thomson, A. J., & Guest, J. R. (1999). Biochemical and spectroscopic characterization of Escherichia coli aconitases (AcnA and AcnB). The Biochemical journal, 344 Pt 3(Pt 3), 739–746. ↩︎
  16. Lee, M. E., Dyer, D. H., Klein, O. D., Bolduc, J. M., Stoddard, B. L., & Koshland, D. E., Jr (1995). Mutational analysis of the catalytic residues lysine 230 and tyrosine 160 in the NADP(+)-dependent isocitrate dehydrogenase from Escherichia coli. Biochemistry, 34(1), 378–384. https://doi.org/10.1021/bi00001a046 ↩︎
  17. Simcock, D. C., Walker, L. R., Pedley, K. C., Simpson, H. V., & Brown, S. (2011). The tricarboxylic acid cycle in L₃ Teladorsagia circumcincta: metabolism of acetyl CoA to succinyl CoA. Experimental parasitology, 128(1), 68–75. https://doi.org/10.1016/j.exppara.2011.02.008 ↩︎
  18. Tian, J., Bryk, R., Itoh, M., Suematsu, M., & Nathan, C. (2005). Variant tricarboxylic acid cycle in Mycobacterium tuberculosis: identification of alpha-ketoglutarate decarboxylase. Proceedings of the National Academy of Sciences of the United States of America, 102(30), 10670–10675. https://doi.org/10.1073/pnas.0501605102 ↩︎
  19. Muslin, E. H., Li, D., Stevens, F. J., Donnelly, M., Schiffer, M., & Anderson, L. E. (1995). Engineering a domain-locking disulfide into a bacterial malate dehydrogenase produces a redox-sensitive enzyme. Biophysical journal, 68(6), 2218–2223. https://doi.org/10.1016/S0006-3495(95)80430-3 ↩︎
  20. https://pax-db.org/dataset/511145/2297923011 ↩︎
  21. Woods, S. A., Schwartzbach, S. D., & Guest, J. R. (1988). Two biochemically distinct classes of fumarase in Escherichia coli. Biochimica et biophysica acta, 954(1), 14–26. https://doi.org/10.1016/0167-4838(88)90050-7 ↩︎
  22. Rothery, E. L., Mowat, C. G., Miles, C. S., Mott, S., Walkinshaw, M. D., Reid, G. A., & Chapman, S. K. (2004). Probing domain mobility in a flavocytochrome. Biochemistry, 43(17), 4983–4989. https://doi.org/10.1021/bi030261w ↩︎
  23. Branson, J. P., Nezic, M., Jitrapakdee, S., Wallace, J. C., & Attwood, P. V. (2004). Kinetic characterization of yeast pyruvate carboxylase isozyme Pyc1 and the Pyc1 mutant, C249A. Biochemistry, 43(4), 1075–1081. https://doi.org/10.1021/bi035575y ↩︎
  24. Orth, J., Thiele, I. & Palsson, B. What is flux balance analysis?[J]. Nat Biotechnol 28, 245–248 (2010). https://doi.org/10.1038/nbt.1614 ↩︎
  25. Ebrahim, A., Lerman, J.A., Palsson, B.O. et al. COBRApy: COnstraints-Based Reconstruction and Analysis for Python[J]. BMC Syst Biol 7, 74 (2013). https://doi.org/10.1186/1752-0509-7-74 ↩︎
  26. Kong, W., Meldgin, D. R., Collins, J. J., & Lu, T. (2018). Designing microbial consortia with defined social interactions. Nature chemical biology, 14(8), 821–829. https://doi.org/10.1038/s41589-018-0091-7 ↩︎
  27. Yuan, S. F., Yi, X., Johnston, T. G., & Alper, H. S. (2020). De novo resveratrol production through modular engineering of an Escherichia coli-Saccharomyces cerevisiae co-culture. Microbial cell factories, 19(1), 143. https://doi.org/10.1186/s12934-020-01401-5 ↩︎