In this paper, a delay differential equation model is investigated, which describes the biodegradation of microcystins (MCs) by Sphingomonas sp. and its degrading enzymes. First, the local stability of the positive equilibrium and the existence of the Hopf bifurcation are obtained. Second, the global attractivity of the positive equilibrium is obtained by constructing suitable Lyapunov functionals, which implies that the biodegradation of microcystins is sustainable under appropriate conditions. In addition, some numerical simulations of the model are carried out to illustrate the theoretical results. Finally, the parameters of the model are determined from the experimental data and fitted to the data. The results show that the trajectories of the model fit well with the trend of the experimental data.
Citation: Luyao Zhao, Mou Li, Wanbiao Ma. Hopf bifurcation and stability analysis of a delay differential equation model for biodegradation of a class of microcystins[J]. AIMS Mathematics, 2024, 9(7): 18440-18474. doi: 10.3934/math.2024899
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Abstract
In this paper, a delay differential equation model is investigated, which describes the biodegradation of microcystins (MCs) by Sphingomonas sp. and its degrading enzymes. First, the local stability of the positive equilibrium and the existence of the Hopf bifurcation are obtained. Second, the global attractivity of the positive equilibrium is obtained by constructing suitable Lyapunov functionals, which implies that the biodegradation of microcystins is sustainable under appropriate conditions. In addition, some numerical simulations of the model are carried out to illustrate the theoretical results. Finally, the parameters of the model are determined from the experimental data and fitted to the data. The results show that the trajectories of the model fit well with the trend of the experimental data.
1.
Introduction
With global warming and increasing eutrophication [1], the frequency and distribution of harmful cyanobacterial blooms in lake ecosystems are increasing worldwide [2,3,4]. When cyanobacteria, also known as "blue-green algae", congregate in large numbers in freshwater lakes, they form harmful algal blooms. These blooms produce a variety of secondary toxic metabolites called cyanotoxins [5]. Harmful algal blooms can have negative impacts on various aspects, including food security, tourism, local economies, human health, drinking water, and aquatic food [6,7].
Among the many different types of cyanotoxins produced by cyanobacteria, the most abundant, widespread, and harmful cyanotoxins are microcystins (MCs) [8,9]. MCs comprise a set of cyclic heptapeptide hepatotoxins produced by freshwater species of cyanobacteria, which share the common structure cyclo (-Adda-D-Glu-M-dha-D-Ala-L-X-D-MeAsp-L-Z), where X and Z represent variable amino acids [10,11]. MCs can form many different isomers due to the variation of amino acid species in the peptide composition. The most common variants detected in China are MC-LR, MC-RR, and MC-YR [12]. MCs can inhibit the activity of phosphoproteases, causing disruption of physiological and biochemical reactions in the human body and seriously endangering health. Long-term and frequent exposure to low-concentration MCs can lead to chronic apoptosis or uncontrolled cell proliferation of hepatocytes, which in turn promotes the occurrence and development of tumors, leading to primary hepatocellular carcinoma [13,14]. The International Agency for Research on Cancer (IARC) classified MC-LR as a class 2B carcinogen. The World Health Organization (WHO) recommends that the concentration of MC-LR in drinking water should not exceed 1 μg/L [15]. Therefore, effective removal of MCs is the key to drinking water treatment.
Since MCs have harmful effects on humans and the environment, research on their degradation has important practical significance. The degradation pathways of MCs mainly comprise physical, chemical, and biological methods. Physical degradation methods mainly include coagulation and precipitation, filtration, activated carbon adsorption, and membrane treatment. However, physical degradation methods are generally inefficient, costly, and difficult to recycle [16]. Chemical degradation methods, such as chemical reagents, ozone oxidation, and photodegradation, can effectively reduce MCs in water bodies. However, these methods can introduce toxic byproducts, causing secondary pollution. Furthermore, the photocatalytic degradation process has complex operational requirements [17]. Therefore, the limitations of physical and chemical degradation methods have restricted their further application in degrading MCs. However, biodegradation has proven to be highly efficient, cost-effective, and free from secondary pollution, making it the safest and most effective method for degrading MCs [18].
Microorganisms are capable of reducing or losing the toxicity of MCs by modifying the structure of the Adda active group in the side chain of MCs or by breaking down the ring structure. In 1994, Jones et al. first isolated a strain of Sphingomonas sp. ACM-3962 from natural water bodies, which could degrade MC-LR [19]. Subsequently, Bourne et al. showed for the first time that the microcystinases MlrA, MlrB, MlrC, and transport protein (MlrD) encoded by four genes, mlrA, mlrB, mlrC, and mlrD, respectively, were involved in the degradation of MC-LR in Sphingomonas sp. ACM-3962. The cyclic MC-LR was sequentially degraded to linear MC-LR (Adda-Glu-M-dha-Ala-Leu-MaspArg-OH), tetra-compound (Adda-Glu-M-dha-Ala-OH), poly-compound, and amino acid by the catalytic action of MlrA, MlrB, and MlrC. MlrA peptidase activity has been shown to be the most efficient enzymatic process and the most specific catalyst in all known detoxification pathways of MCs [20]. Since then, various strains capable of degrading MCs have been isolated, such as Pseudomonas aeruginosa [21], Paucibacter toxinivorans [22], and Brevibacterium sp. [23]. However, the degrading bacteria are still mainly concentrated in the genus Sphingomonas [24,25,26]. Yan et al. [27] successfully extracted the Sphingopyxis sp. USTB-05, which can effectively degrade MCs. They studied the biodegradation of MCs by USTB-05 at both cellular and enzymatic levels.
On the other hand, the studies of the dynamics of the chemostat models and their variants have achieved rich results [28,29]. Tai et al. [30] proposed a time-delayed microorganism flocculation model. They studied the existence and local stability of the equilibria of the presented model and found that the model can display forward or backward bifurcation. Guo et al. [31] further studied the uniform persistence of the model and global stability of the equilibria. Building upon the research in [31], Guo et al. [32] considered a time-delayed microorganism flocculation model with saturated functional responses. Using the generalized Lyapunov-LaSalle theorem, they established some conditions for the global stability of the equilibria. Song et al. [33] proposed a dynamic model for microbial flocculant with nutrient competition and metabolic products, and analyzed the global dynamic properties of the model.
For the flocculation and microbial degradation of MCs, Yang et al. [34] proposed the following model:
Here, x1(t), x2(t), and x3(t) represent the concentrations of MCs, Sphingomonas sp., and the degrading enzymes produced by Sphingomonas sp. at time t. The constant a10>0 is the input concentration of MCs. The constant D>0 is the continuous input rate of MCs, Sphingomonas sp. and the degrading enzymes into the chemostat. The constant a12≥0 is the consumption rate of MCs. The constant a21≥0 is the maximum growth rate of Sphingomonas sp. The constant a20≥0 is the consumption rate of Sphingomonas sp. The constant a30≥0 is the rate at which Sphingomonas sp. produce the degrading enzymes that can be used for the degradation of MCs. The constant a13≥0 is the degradation rate of MCs. The constant a31≥0 is the consumption rate of the degrading enzymes. The constants d1, d2, and d3 represent the death rates of MCs, Sphingomonas sp., and the degrading enzymes, respectively. Yang et al. [34] studied the local stability of the equilibria and the global stability of the boundary equilibrium of model (1.1), as well as the uniform persistence of model (1.1). Furthermore, Song et al. [35] studied the global stability of the positive equilibrium of model (1.1) by constructing suitable Lyapunov functions. They also found that, under certain conditions, the parameter a13/D can cause Hopf bifurcation.
Model (1.1) is a set of ordinary differential equations that is valid under the assumption that the process of nutrient (MCs) storage by the organism (Sphingomonas sp.) is instantaneous. However, during the continuous cultivation of microorganisms, the growth of microorganisms and the consumption of nutrients often show a time delay. Time delay is caused by factors such as the storage of nutrients by microorganisms and their metabolic processes. Therefore, time delay becomes an important factor in accurately characterizing microbial culture processes [36,37,38,39]. In reference [40], Song et al. rewrote the second equation of model (1.1) into the following form:
where the constant τ1≥0 represents the time that the organism (Sphingomonas sp.) stores the nutrient (MCs). The term e−δ1τ1 represents the approximate proportion of individuals remaining in the chemostat during the conversion process. Considering that there may be time delay in the production of degrading enzymes by microorganisms [41,42], and under the experimental conditions of model (1.1), in order to obtain the degrading enzymes produced by Sphingomonas sp., it is necessary to separate the degrading enzymes from the chemostat by centrifugation and sonicate the Sphingomonas sp. to release the degrading enzymes. This process is not instantaneous. Therefore, we construct the following time-delayed model:
Here, the constant τ2≥0 represents the time required for Sphingomonas sp. to produce degrading enzymes that can be used for the degradation of MCs. The term e−δ2τ2 represents the approximate proportion of the degrading enzymes produced by Sphingomonas sp. that remains in the chemostat during the conversion process. For clarity, the biological meanings of the parameters of model (1.2) are summarized in Table 1.
Table 1.
Descriptions of parameters in model (1.2).
Parameters
Descriptions
x1(t)
the concentration of MCs at time t
x2(t)
the concentration of Sphingomonas sp. at time t
x3(t)
the concentration of the degrading enzymes produced by Sphingomonas sp. at time t
D
the continuous input rate of MCs, Sphingomonas sp., and the degrading enzymes
into the chemostat
a10
the input concentration of MCs
a12
the consumption rate of MCs
a13
the degradation rate of MCs
d1
the death rate of MCs
a21
the maximum growth rate of Sphingomonas sp.
a20
the consumption rate of Sphingomonas sp.
d2
the death rate of Sphingomonas sp.
a30
the rate at which Sphingomonas sp. produces the degrading enzymes that can be
used for the degradation of MCs.
a31
the consumption rate of the degrading enzymes
d3
the death rate of the degrading enzymes
τ1
the time that the organism (Sphingomonas sp.) stores the nutrient (MCs)
e−δ1τ1
the approximate proportion of individuals remaining in the chemostat during
the conversion process
τ2
the time required for Sphingomonas sp. to produce degrading enzymes
that can be used for the degradation of MCs
e−δ2τ2
the approximate proportion of the degrading enzymes produced by Sphingomonas sp.
that remains in the chemostat during the conversion process.
In model (1.2), for τ1>0 and τ2=0, Song et al. [40] studied the local and global stability of the boundary equilibrium, local stability of the positive equilibrium, and the existence of Hopf bifurcations caused by the time delay τ1. However, they did not obtain global stability results for the positive equilibrium of model (1.2) for τ1>0 and τ2=0. The global stability or attractivity of the positive equilibrium of model (1.2) deserves further study. The main purpose of this paper is to study the effect of the time delay τ2 on the dynamical properties of model (1.2) and to obtain sufficient conditions for the global attractivity of the positive equilibrium of model (1.2).
The rest of this paper is organized as follows. In Section 2, the dimensionless model for model (1.2) is first obtained. Further, the classification of equilibria and the global stability of the boundary equilibrium are obtained for model (2.1). In Section 3, if τ1=0,τ2>0, or τ1=τ2>0, we study the local stability of the positive equilibrium and the existence of Hopf bifurcations of model (2.1). In Section 4, by constructing suitable Lyapunov functionals and applying some inequality analysis techniques, we establish some sufficient conditions for the global attractivity of the positive equilibrium. In Section 5, we provide several specific examples and perform numerical simulations to validate our conclusions. Finally, using experimental data from reference [43], we estimate the specific values of model parameters through the least squares method and perform numerical simulations.
2.
Preliminaties
First, we make the following dimensionless transformations of model (1.2):
Let C=C([−ˆτ,0],R3) be the Banach space of continuous functions mapping [−ˆτ,0] to R3, equipped with the sup-norm, where ˆτ=max{τ1,τ2}. We assume that model (2.1) always satisfies the initial condition
x(θ)=ϕ1(θ),y(θ)=ϕ2(θ),z(θ)=ϕ3(θ),θ∈[−ˆτ,0],
(2.2)
where
ϕ=(ϕ1,ϕ2,ϕ3)T∈C+:={ϕ∈C|ϕi≥0,i=1,2,3}.
Then, we have the following lemma.
Lemma 2.1.The solution (x(t),y(t),z(t))T of model (2.1) with initial condition (2.2) is existent, unique, and nonnegative on [0,+∞), which satisfies
By a similar argument as in the proof of Theorem 2.1 in [40], we obtain the following result.
Theorem 2.1.(i) If R0<1, then the boundary equilibrium E0 is globally asymptotically stable.
(ii) If R0=1, then the boundary equilibrium E0 is linearly stable.
(iii)If R0>1, then the boundary equilibrium E0 is unstable.
3.
Local stability of the positive equilibrium and Hopf bifurcation analysis
In this section, we assume that R0>1. The method provided in references [44,45] for studying the stability of the models with coefficient-dependent time delays is employed here. We utilize the stability criteria discussed in Section 2.4 of reference [45] to analyze the local stability of the positive equilibrium.
The characteristic equation of model (2.1) at the positive equilibrium E∗ can be written as
According to the Routh-Hurwitz criterion, if condition (H1) holds, then all the roots of Eq (3.1) have negative real parts and the positive equilibrium E∗ is locally asymptotically stable if τ1=τ2=0.
Remark 3.1.From reference [35], we state the following two facts.
(i) If Π≥0, then condition (H1) holds.
(ii) If Π<0, then there exists a positive constant a∗2 such that if a2<a∗2, then condition (H1) holds, and if a2≥a∗2, then condition (H1) does not hold.
Case Ⅰ.τ1=0, τ2≥0.
For the convenience of analysis, we first assume τ1=0 and choose τ2 as the bifucation parameter.
In this case, the characteristic equation of model (2.1) at the positive equilibrium E∗ can be written as
If τ2=0 and condition (H1) holds, then all the roots of Eq (3.2) have negative real parts, and the positive equilibrium E∗ is locally asymptotically stable.
When τ2>0, stability switching may occur when the existence of a pair of pure imaginary roots λ=±iω exist in Eq (3.2) that crosses the imaginary axis as the value of τ2 increases. It can be easily proven that P(λ,τ2) and Q(λ,τ2) in Eq (3.2) satisfy the following properties:
(ⅰ) P(0,τ2)+Q(0,τ2)≠0;
(ⅱ) P(iω,τ2)+Q(iω,τ2)≠0;
(ⅲ) lim|λ|→∞|Q(λ,τ2)P(λ,τ2)|=0;
(ⅳ) F(ω,τ2)=|P(ω,τ2)|2−|Q(ω,τ2|2 has a finite number of zero roots;
(ⅴ) The equation F(ω,τ2)=0 has positive roots ω(τ2), and each positive root is continuously differentiable.
Let λ=iω be a purely imaginary root of Eq (3.2). Then we have
Letting Δ(τ2)=P22(τ2)−3P1(τ2). If Δ(τ2)≥0, we define v+=−P2(τ2)+√Δ(τ2)3. According to reference [46], the following conclusion holds.
Lemma 3.1.(i) When P0(τ2)<0, Eq (3.4) has at least one positive real root;
(i) When P0(τ2)≥0, Eq (3.4) has positive roots if and only if v+=−P2(τ2)+√Δ(τ2)3>0 and h(v+)≤0;
(i) When conditions (i) or (ii) are not satisfied, Eq (3.4) has no positive real roots.
For convenience, in our subsequent discussions, we assume that Eq (3.4) has only one positive root. There exists a set I such that, when τ2∈I, the equation
F(ω(τ2),τ2)=0
has a positive real root ω=ω(τ2)>0. Furthermore, for τ2∈I, we can define an angle θ(τ2)∈[0,2π) as the solution of (3.3):
For τ2∈I, the angle θ in the above equation must satisfy the following relationship with ωτ2 in Eq (3.3):
ωτ2=θ(τ2)+2nπ,n∈N0.
Define
Sn(τ2)=τ2−θ(τ2)+2nπω(τ2),n∈N0,τ2∈I,
(3.5)
where Sn(τ2) is continuously differentiable with respect to τ2.
Theorem 3.1.Suppose that τ1=0, R0>1, and condition (H1) hold. When τ2=τ∗2∈I such that Sn(τ∗2)=0 for some n∈N0 hold, the characteristic equation (3.2) has a pair of purely imaginary roots ±iω(τ∗2). If δ(τ∗2)>0 (<0), then the roots ±iω(τ∗2) cross the imaginary axis from left to right (from right to left), where
Theorem 3.2.Suppose that τ1=0 and R0>1. If condition (H1) holds, the following conclusions hold.
(i) When the function S0(τ2) has no positive roots for τ2∈I, the positive equilibrium E∗ is locally asymptotically stable for any τ2≥0;
(ii) When the function Sn(τ2) has roots such that τ02<τ12<⋯<τm2∈I and S′n(τj2)≠0(j=0,1,2,⋯,m), then the positive equilibrium E∗ is locally asymptotically stable on [0,τ02)∪(τm2,+∞)∩I.
Case Ⅱ.τ1=τ2=τ.
We assume τ1=τ2=τ, and we increase the value of τ from 0 to observe possible bifurcations. In this situation, the characteristic equation becomes
We choose θ(τ)∈[0,2π), and sinθ(τ) and cosθ(τ) are given by Eq (3.7). Similar to Case Ⅰ, there exists a set ˉI⊂(0,τ1max) such that, when τ∈ˉI, Eq (3.8) has a positive real root. Then we have Sn(τ)=τ−θ(τ)+2nπω(τ), where n∈N0 and τ∈ˉI.
Theorem 3.3.Suppose that τ1=τ2=τ, R0>1, and condition (H1) hold. When τ=τ∗∈ˉI such that Sn(τ∗)=0 for some n∈N0 hold, the characteristic Eq (3.6) has a pair of purely imaginary roots ±iω(τ∗). If Δ(τ∗)>0 (<0), then the roots ±iω(τ∗) cross the imaginary axis from left to right (from right to left), where
Theorem 3.4.Suppose that τ1=τ2=τ and R0>1. If condition (H1) holds, the following conclusions hold.
(i) When the function S0(τ) has no positive roots for τ∈ˉI, the positive equilibrium E∗ is locally asymptotically stable for τ∈ˉI;
(ii) When the function Sn(τ) has roots such that τ0<τ1<⋯<τm∈ˉI and S′n(τj)≠0(j=0,1,2,⋯,m), then the positive equilibrium E∗ is locally asymptotically stable on [0,τ0)∪(τm,τ1max)∩ˉI.
4.
Global attractivity of the positive equilibrium
Similar to the method used to prove the uniform persistence in reference [40], we have the following result.
Theorem 4.1.If R0>1, then model (2.1) is uniformly persistent, and the solution (x(t),y(t),z(t))T of model (2.1) with initial condition (2.2) satisfies
where ρ>0 and d>0 satisfy q≡1a1ρy∗+a2c1e−δ2τ2ρy∗D3+D1>x∗andxΔ≡q(1−e−dq)>x∗.
Next, similar to the method used to prove the global stability of equilibria using Barbalat's lemma in references [47,48], we consider the global stability of the positive equilibrium E∗ when R0>1.
For convenience of description, let ϵ be any sufficiently small positive number such that 0<ϵ<min{ν1,ν2,ν3}. We define
Theorem 4.2.If R0>1 and the symmetric matrix J(0) is positive definite, then the positive equilibrium E∗ is globally attractive in C1:={ϕ∈C+:ϕ(0)>0}.
Proof. If R0>1, then there exists a sufficiently small ϵ such that 0<ϵ<min{ν1,ν2,ν3} and J(ϵ) is a positive definite matrix. For this chosen ϵ, there exists a sufficiently large T(ϵ)>ˆτ such that when t≥T(ϵ),
Therefore, the positive equilibrium E∗ is globally attractive. □
Remark 4.1.Suppose that τ1=τ2=0 and R0>1. If we choose θ1=a1D2+a1D1b21 and θ2=a1a2x∗b1c1, then matrix J(0) in our Theorem 4.2 becomes J, where J can be found in the proof of Theorem 3.1 in reference [35]. Therefore, our Theorem 4.2 extends Theorem 3.1 in reference [35].
5.
Numerical simulations
In this section, we run simulations in two parts.
Part Ⅰ. In this part, we give some numerical examples to summarize the applications of the main results. These include the global stability of the boundary equilibrium E0, the local stability, and global attractivity of the positive equilibrium E∗, and the existence of a Hopf bifurcation.
First, we determine the values of the parameters a1, a2, D1, and D3 to be a1=1, a2=2, D1=1.01, and D3=1.02.
Then, we choose b1=5, c1=5, c2=15, D2=8.01, δ1=2, τ1=2, δ2=2, and τ2=2. These values satisfy the condition R0=0.0113<1. According to Theorem 2.1 and Figure 1, the boundary equilibrium E0(0.9901,0,0) is globally asymptotically stable.
Figure 1.
The solution curves and phase trajectory of model (2.1) for R0<1 with different initial values. Here, the boundary equilibrium E0(0.9901,0,0) is globally asymptotically stable.
Next, we choose b1=5, c1=15, c2=5, D2=4.01, and δ2=0.1. Under these parameters, it can be checked that Eq (3.3) has only one positive real root. Based on Theorem 3.1, the picture of S0(τ2) can be drawn clearly. It follows from Figure 2 that there exists 2 roots denoted by τ02=1.5704 and τ12=17.6442. Then we have ω(τ02)=0.6661 and ω(τ12)=0.1547, and the transversality condition is determined by the sign of S′0(τ2).
Additionally, when τ2∈[0,τ02), the positive equilibrium E∗ is locally asymptotically stable. For example (see Figure 3), when τ2=1∈[0,τ02), we have the positive equilibrium E∗=(0.8020,0.0370,0.0999). As the time delay increases, a Hopf bifurcation occurs at τ2=τ02, and the positive equilibrium E∗ loses stability for τ2∈(τ02,τ12). For example (see Figure 4), when τ2=14∈(τ02,τ12). As τ2 continues to increase, when τ2∈(τ12,+∞)∩I, the positive equilibrium E∗ is locally asymptotically stable. For example (see Figure 5), when τ2=17.79∈(τ12,+∞)∩I, we have the positive equilibrium E∗=(0.8020,0.1179,0.0595).
Figure 3.
The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=1<τ02. Here, the positive equilibrium E∗(0.8020,0.0370,0.0999) is locally asymptotically stable.
Figure 4.
The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=14∈(τ02,τ12). Here, the positive equilibrium E∗ is unstable and periodic oscillations occur.
Figure 5.
The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=17.79∈(τ12,+∞)∩I. Here, the positive equilibrium E∗(0.8020,0.1179,0.0595) is locally asymptotically stable.
Next, we choose b1=16.1, c1=3.1, c2=14.1, D2=7.1, and δ2=0.1. Under these parameters, it can be checked that Eq (3.3) has two positive real roots. The picture of S0(τ2) follows from Figure 6, and there exist 2 roots denoted by τ022=0.6617 and τ021=1.2539. Then we have ω(τ022)=2.0852 and ω(τ021)=1.6120.
Additionally, when τ2∈[0,τ022), the positive equilibrium E∗ is locally asymptotically stable. For example (see Figure 7), when τ2=0.5∈[0,τ022), we have the positive equilibrium E∗=(0.4410,0.6930,0.2823). As the time delay increases, a Hopf bifurcation occurs at τ2=τ022, and the positive equilibrium E∗ loses stability for τ2∈(τ022,τ021). For example (see Figure 8), when τ2=1.2∈(τ022,τ021). As τ2 continues to increase, when τ2∈(τ021,+∞)∩I, the positive equilibrium E∗ is locally asymptotically stable. For example (see Figure 9), when τ2=1.35∈(τ021,+∞)∩I, we have the positive equilibrium E∗=(0.4410,0.7193,0.2692).
Figure 7.
The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=0.5<τ022. Here, the positive equilibrium E∗(0.4410,0.6930,0.2823) is locally asymptotically stable.
Figure 8.
The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=1.2∈(τ022,τ021). Here, the positive equilibrium E∗ is unstable and periodic oscillations occur.
Figure 9.
The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=1.35∈(τ021,+∞)∩I. Here, the positive equilibrium E∗(0.4410,0.7193,0.2692) is locally asymptotically stable.
Lastly, based on reference [48], Theorem 4.2 gives some sufficient conditions for the global attractivity of the positive equilibrium E∗ in model (2.1) with time delays. For example (see Figure 10), let us choose the parameter values a1=0.8890, a2=0.0970, b1=37.2064, c1=6.1465, c2=1.0287, D1=1.0300, D2=1.0100, D3=19.9259, δ1=1, τ1=3.3007e−6, δ2=1, and τ2=4.0184e−6. Then we have R0=36.4839>1, and model (2.1) has a positive equilibrium E∗=(0.0271,40.2768,0.0011). By selecting θ1=0.9601 and θ2=0.0018, it can be easily verified that J(0) is positive definite. Therefore, the conditions of Theorem 4.2 are satisfied, and the positive equilibrium E∗ is globally attractive. Without changing any other parameters, when we increase τ1 to τ1=6.3000e−6 and perform calculations, it does not satisfy the conditions of Theorem 4.2. However, through numerical simulations, it is observed that under the set of parameters, the positive equilibrium E∗ is globally attractive. Theorem 4.2 only provides a sufficient condition for the global attractivity of the positive equilibrium E∗ and is somewhat conservative.
Figure 10.
The solution curves and phase trajectory of model (2.1) for R0>1 with different initial values and τ1=3.3007e−6, τ2=4.0184e−6. Here, the positive equilibrium E∗(0.0271,40.2768,0.0011) is globally attractive.
Furthermore, we choose the parameter values a1=1.8883, a2=0.6644, b1=40.0752, c1=6.1465e−4, c2=98.1660, D1=1.0300, D2=1.0100, D3=14.1512, δ1=1, δ2=1, θ1=0.2429, and θ2=7.4998e−4. When τ1=0, for any τ2>0, the positive equilibrium E∗ is locally asymptotically stable. Using a genetic algorithm and MATLAB simulation, we determine the global attractivity region of model (2.1) with the specified parameter values, as shown by the blue dashed region in Figure 11(a). Further, we can observe that under the parameter values, τ2 has a relatively small impact on the global attractivity compared to τ1. To ensure that the equilibrium is globally attractive, we can observe from Figure 11 that the range of variation in τ1 is much smaller compared to the range of variation in τ2. Therefore, even small changes in τ1 can lead to instability of the equilibrium, while changes in τ2 seem to have a minor impact. From a biological perspective, the time delay (τ1) that the organism (Sphingomonas sp.) stores the nutrient (MCs) is more significant than the time delay (τ2) it takes for Sphingomonas sp. to produce degrading enzymes for the sustained degradation of MCs. When τ1=τ2=τ, within the range τ∈[0,3.65), the positive equilibrium E∗ is locally asymptotically stable, as represented by the red line in Figure 11(b). Therefore, the red dashed line falling within the blue region indicates that the positive equilibrium E∗ is globally asymptotically stable.
Figure 11.
The global attractivity region of the positive equilibrium E∗ with respect to τ1 and τ2.
Part Ⅱ. In this part, based on the MCs degradation experiments by Sphingopyxis sp. USTB-05 and enzymes of USTB-05, as described in reference [43], we modify model (1.2) into the following two models:
The biological meanings of the parameters in models (5.1) and (5.2) are provided in Tables 2–4. The experimental data for Figures 2 and 4 in reference [43] are provided in Table 5. However, since reference [43] has not provided the accurate experimental data for 48 hours in Table 5(a) and 10 hours in Table 5(b), and from a mathematical point of view, it is unlikely that the experimental values at these two-time points are zero. Therefore, for simulations, we only use the first four experimental data sets as the parameter values.
Table 2.
Parameter estimation values for model (5.1) when τ1>0.
Parameters
MC-RR
MC-LR
MC-YR
Unit
Descriptions
Source
a12
1.44e−4
3.53e−4
1.58e−3
L×mg−1×h−1
the consumption rate of MCs
LSM
d1
0.006
0.006
0.006
h−1
the death rate of MCs
LSM
a21
4.82e−3
7.98e−3
3.00e−3
L×mg−1×h−1
the maximum growth rate of USTB-05
LSM
d2
4.25e−6
2.72e−5
2.00e−6
h−1
the death rate of USTB-05
LSM
τ1
13.60
18.44
14.61
h−1
the time that the organism (USTB-05) stores the nutrient (MCs)
Firstly, according to the experimental procedure described in reference [43], we set the initial concentration of USTB-05 to be 10ml/L and the initial concentration of enzymes of USTB-05 to be 100ml/L. Furthermore, using the experimental data of Table 5 and the least squares method (LSM), the remaining parameter values in models (5.1) and (5.2) are determined as shown in Tables 2–4. Since δ1 is related to d2, for simplicity let us assume δ1=d2. Based on the parameter values provided in Tables 2–5, we have Figures 12 and 13. These figures demonstrate that under the condition where MCs are the sole carbon and nitrogen source, models (5.1) and (5.2) fit well with the MCs degradation experiments by USTB-05 and enzymes of USTB-05.
Figure 12.
Experimental data and fitting curve of USTB-05 degradation of MCs. The green dots and pink dots in the figure represent the fitted data values at 48 hours in model (5.1) when τ1>0 and τ1=0, respectively.
Furthermore, Table 6 provides the fitted values of MCs in Figures 12 and 13. We use mean squared error (MSE) and root mean squared error (RMSE) to evaluate the reliability of the data fitting for models (5.1) and (5.2) (for example, see [50,51]). For convenience, let us introduce the definitions of MSE and RMSE as follows:
Here, yi and y′i represent the experimental data and fitted data, respectively. The positive integer n represents the number of fitted data points. Using the data from Table 6, we obtain Table 7. Since the initial values of the experimental data in Table 5 and fitted data are consistent, they are not included in the evaluation. According to Table 7, we can observe that for model (5.1), the fitted results of model (5.1) with time delay are always better than those of model (5.1) without time delay. From a biological point of view, model (5.1) with time delay is more reasonable.
Based on the simulation results for the experiments described in reference [43], it can be observed that when the degradation of MCs by USTB-05 is at 48 hours, the remaining amounts of MC-RR, MC-LR, and MC-YR are approximately 6.93mg/L, 1.74mg/L, and 2.18mg/L, respectively. Furthermore, USTB-05 degrades MC-RR, MC-LR, and MC-YR to 1% of their initial values at approximately 57.5 hours, 54.2 hours, and 78.6 hours, respectively.
6.
Conclusions
This paper is mainly based on references [34,40]. We proposed and analyzed the time-delayed model (2.1). Model (2.1) describes the biodegradation process of MCs by Sphingomonas sp. and its degrading enzyme. Theorem 2.1 provides the condition (R0<1) for global asymptotic stability of the boundary equilibrium E0 in model (2.1). It implies that, in the chemostat, Sphingomonas sp. cannot sustainably degrade MCs, when R0<1.
Theorems 3.1–3.4 provide some conditions for local asymptotic stability of the positive equilibrium E∗ and the existence of Hopf bifurcation in model (2.1). According to Theorem 3.1 and the results of simulations, when τ2<τ02, the positive equilibrium E∗ is locally asymptotically stable. When τ2∈(τ02,τm2), the positive equilibrium E∗ may becomes unstable. When τ2>τm2, the positive equilibrium E∗ becomes stable again. This indicates that time delay τ2 has a significant impact on the stability of the positive equilibrium E∗. From a biological point of view, it means time delay (τ2) in the production of degrading enzymes by Sphingomonas sp. makes it more difficult to stably degrade MCs.
Theorem 4.1 provides the condition (R0<1) for uniform persistence in model (2.1). From a biological point of view, under some conditions, the biodegradation of MCs is sustainable. Time delays τ1 and τ2 do not affect the sustained degradation of MCs. Theorem 4.2 provides some sufficient conditions for global attractivity of the positive equilibrium E∗ in model (2.1) by constructing appropriate Lyapunov functionals and analyzing inequalities. Considering numerical simulations, from a biological perspective, the time delay (τ1) that the organism (Sphingomonas sp.) stores the nutrient (MCs) is more significant than the time delay (τ2) it takes for Sphingomonas sp. to produce degrading enzymes for the sustained degradation of MCs.
Finally, based on experimental data from reference [43], a least squares fitting is performed, and the fitting results demonstrate the rationality of models (5.1) and (5.2) to some extent. Furthermore, as future work to make the model (2.1) more biologically plausible, the addition of some diffusion terms may have significant theoretical and practical implications.
Author contributions
L.Z.: Writing–original draft, Methodology, Software, Writing–review and editing; M.L.: Writing–original draft, Methodology, Software, Writing–review and editing; W.M.: Writing–original draft, Methodology, Writing–review and editing, Funding acquisition, Supervision. All authors have read and agreed to the published version of the manuscript.
Use of AI tools declaration
The authors declare they have not used Artificial Intelligence (AI) tools in the creation of this article.
Acknowledgments
The authors would like to thank the reviewers and the editors for their careful reading, helpful comments, and suggestions that greatly improved the paper. This paper has been supported by the National Natural Science Foundation of China (No. 12371481) and the Beijing Natural Science Fundation (No. 1202019).
Conflict of interest
The authors declare there is no conflict of interest.
References
[1]
C. J. Gobler, Climate change and harmful algal blooms: insights and perspective, Harmful Algae, 91 (2020), 101731. https://doi.org/10.1016/j.hal.2019.101731 doi: 10.1016/j.hal.2019.101731
[2]
R. I. Woolway, S. Sharma, J. P. Smol, Lakes in hot water: the impacts of a changing climate on aquatic ecosystems, BioScience, 72 (2022), 1050–1061. https://doi.org/10.1093/biosci/biac052 doi: 10.1093/biosci/biac052
[3]
J. C. Ho, A. M. Michalak, N. Pahlevan, Widespread global increase in intense lake phytoplankton blooms since the 1980s, Nature, 574 (2019), 667–670. https://doi.org/10.1038/s41586-019-1648-7 doi: 10.1038/s41586-019-1648-7
[4]
X. Hou, L. Feng, Y. Dai, C. Hu, L. Gibson, J. Tang, et al., Global mapping reveals increase in lacustrine algal blooms over the past decade, Nat. Geosci., 15 (2022), 130–134. https://doi.org/10.1038/s41561-021-00887-x doi: 10.1038/s41561-021-00887-x
[5]
J. Huisman, G. A. Codd, H. W. Paerl, B. W. Ibelings, J. M. H. Verspagen, P. M. Visser, Cyanobacterial blooms, Nat. Rev. Microbiol., 16 (2018), 471–483. https://doi.org/10.1038/s41579-018-0040-1 doi: 10.1038/s41579-018-0040-1
[6]
R. Cavicchioli, W. J. Ripple, K. N. Timmis, F. Azam, L. R. Bakken, M. Baylis, et al., Scientists' warning to humanity: microorganisms and climate change, Nat. Rev. Microbiol., 17 (2019), 569–586. https://doi.org/10.1038/s41579-019-0222-5 doi: 10.1038/s41579-019-0222-5
[7]
W. A. Wurtsbaugh, H. W. Paerl, W. K. Dodds, Nutrients, eutrophication and harmful algal blooms along the freshwater to marine continuum, WIREs Water, 6 (2019), e1373. https://doi.org/10.1002/wat2.1373 doi: 10.1002/wat2.1373
[8]
L. Chen, J. Chen, X. Zhang, P. Xie, A review of reproductive toxicity of microcystins, J. Hazard. Mater., 301 (2016), 381–399. https://doi.org/10.1016/j.jhazmat.2015.08.041 doi: 10.1016/j.jhazmat.2015.08.041
[9]
X. Wan, A. D. Steinman, Y. Gu, G. Zhu, X. Shu, Q. Xue, et al., Occurrence and risk assessment of microcystin and its relationship with environmental factors in lakes of the eastern plain ecoregion, China, Environ. Sci. Pollut. Res., 27 (2020), 45095–45107. https://doi.org/10.1007/s11356-020-10384-0 doi: 10.1007/s11356-020-10384-0
[10]
R. E. Honkanen, J. Zwiller, R. E. Moore, S. L. Daily, B. S. Khatra, M. Dukelow, et al., Characterization of microcystin-LR, a potent inhibitor of type 1 and type 2A protein phosphatases, J. Biol. Chem., 265 (1990), 19401–19404. https://doi.org/10.1016/S0021-9258(17)45384-1 doi: 10.1016/S0021-9258(17)45384-1
[11]
D. Huo, N. Gan, R. Geng, Q. Cao, L. Song, G. Yu, et al., Cyanobacterial blooms in China: diversity, distribution, and cyanotoxins, Harmful Algae, 109 (2021), 102106. https://doi.org/10.1016/j.hal.2021.102106 doi: 10.1016/j.hal.2021.102106
[12]
Q. Cao, A. D. Steinman, X. Wan, L. Xie, Bioaccumulation of microcystin congeners in soil-plant system and human health risk assessment: a field study from Lake Taihu region of China, Environ. Pollut., 240 (2018), 44–50. https://doi.org/10.1016/j.envpol.2018.04.067 doi: 10.1016/j.envpol.2018.04.067
[13]
E. M. Jochimsen, W. W. Carmichael, J. S. An, D. M. Cardo, S. T. Cookson, C. E. M. Holmes, et al., Liver failure and death after exposure to microcystins at a hemodialysis center in Brazil, New Engl. J. Med., 338 (1998), 873–878. https://doi.org/10.1056/NEJM199803263381304 doi: 10.1056/NEJM199803263381304
[14]
L. Díez-Quijada, M. Puerto, D. Gutiérrez-Praena, M. Liana-Ruiz-Cabello, A. Jos, A. M. Camean, Microcystin-RR: occurrence, content in water and food and toxicological studies, Environ. Res., 168 (2019), 467–489. https://doi.org/10.1016/j.envres.2018.07.019 doi: 10.1016/j.envres.2018.07.019
T. W. Lambert, C. F. B. Holmes, S. E. Hrudey, Adsorption of microcystin-LR by activated carbon and removal in full scale water treatment, Water Res., 30 (1996), 1411–1422. https://doi.org/10.1016/0043-1354(96)00026-7 doi: 10.1016/0043-1354(96)00026-7
[17]
B. L. Yuan, J. H. Qu, M. L. Fu, Removal of cyanobacterial microcystin-LR by ferrate oxidation–coagulation, Toxicon, 40 (2002), 1129–1134. https://doi.org/10.1016/S0041-0101(02)00112-5 doi: 10.1016/S0041-0101(02)00112-5
[18]
A. K. Y. Lam, P. M. Fedorak, E. E. Prepas, Biotransformation of the cyanobacterial hepatotoxin microcystin-LR, as determined by HPLC and protein phosphatase bioassay, Environ. Sci. Technol., 29 (1995), 242–246. https://doi.org/10.1021/es00001a030 doi: 10.1021/es00001a030
[19]
G. J. Jones, D. G. Bourne, R. L. Blakeley, H. Doelle, Degradation of the cyanobacteria hepatotoxin microcystin by aquatic bacteria, Natural Toxins, 2 (1994), 228–235. https://doi.org/10.1002/nt.2620020412 doi: 10.1002/nt.2620020412
[20]
D. G. Bourne, G. J. Jones, R. L. Blakeley, A. Jones, A. P. Negri, P. Riddles, Enzymatic pathway for the bacterial degradation of the cyanobacterial cyclic peptide toxin microcystin LR, Appl. Environ. Microbiol., 62 (1996), 4086–4094. https://doi.org/10.1128/aem.62.11.4086-4094.1996 doi: 10.1128/aem.62.11.4086-4094.1996
[21]
S. Takenaka, M. F. Watanabe, Microcystin LR degradation by Pseudomonas aeruginosa alkaline protease, Chemosphere, 34 (1997), 749–757. https://doi.org/10.1016/S0045-6535(97)00002-7 doi: 10.1016/S0045-6535(97)00002-7
[22]
J. Rapala, K. A. Berg, C. Lyra, R. M. Niemi, W. Manz, S. Suomalainen, et al., Paucibacter toxinivorans gen. nov., sp. nov., a bacterium that degrades cyclic cyanobacterial hepatotoxins microcystins and nodularin, Int. J. Syst. Evol. Microbiol., 55 (2005), 1563–1568. https://doi.org/10.1099/ijs.0.63599-0 doi: 10.1099/ijs.0.63599-0
[23]
L. A. Lawton, A. Welgamage, P. M. Manage, C. Edwards, Novel bacterial strains for the removal of microcystins from drinking water, Water Sci. Technol., 63 (2011), 1137–1142. https://doi.org/10.2166/wst.2011.352 doi: 10.2166/wst.2011.352
[24]
H. D. Park, Y. Sasaki, T. Maruyama, E. Yanagisawa, A. Hiraishi, K. Kato, Degradation of the cyanobacterial hepatotoxin microcystin by a new bacterium isolated from a hypertrophic lake, Environ. Toxicol., 16 (2001), 337–343. https://doi.org/10.1002/tox.1041 doi: 10.1002/tox.1041
[25]
Q. Ding, K. Liu, K. Xu, R. Sun, J. Zhang, L. Yin, et al., Further understanding of degradation pathways of microcystin-LR by an indigenous Sphingopyxis sp. in environmentally relevant pollution concentrations, Toxins, 10 (2018), 536. https://doi.org/10.3390/toxins10120536 doi: 10.3390/toxins10120536
[26]
F. Yang, F. Huang, H. Feng, J. Wei, I. Y. Massey, G. Liang, et al., A complete route for biodegradation of potentially carcinogenic cyanotoxin microcystin-LR in a novel indigenous bacterium, Water Res., 174 (2020), 115638. https://doi.org/10.1016/j.watres.2020.115638 doi: 10.1016/j.watres.2020.115638
[27]
H. Yan, Y. Deng, H. Zou, X. Li, C. Ye, Isolation and activity of bacteria for the biodegradation of microcystins, (Chinese), Environmental Science, 25 (2004), 49–53. https://doi.org/10.13227/j.hjkx.2004.06.010 doi: 10.13227/j.hjkx.2004.06.010
[28]
H. L. Smith, P. Waltman, The theory of the chemostat: dynamics of microbial competition, Cambridge University Press, 1995. https://doi.org/10.1017/CBO9780511530043
[29]
Y. Kuang, Delay differential equations with applications in population dynamics, New York: Academic Press, 1993.
[30]
X. Tai, W. Ma, S. Guo, H. Yan, C. Yin, A class of dynamic delayed model describing flocculation of microorganism and its theoretical analysis, (Chinese), Mathametics in Practice and Theory, 13 (2015), 198–209.
[31]
S. Guo, W. Ma, Global dynamics of a microorganism flocculation model with time delay, Commun. Pure Appl. Anal., 16 (2017), 1883–1891. https://doi.org/10.3934/cpaa.2017091 doi: 10.3934/cpaa.2017091
[32]
S. Guo, W. Ma, X. Q. Zhao, Global dynamics of a time-delayed microorganism flocculation model with saturated functional responses, J. Dyn. Diff. Equat., 30 (2018), 1247–1271. https://doi.org/10.1007/s10884-017-9605-3 doi: 10.1007/s10884-017-9605-3
[33]
K. Song, S. Guo, W. Ma, H. Yan, A class of dynamic models describing microbial flocculant with nutrient competition and metabolic products in wastewater treatment, Adv. Differ. Equ., 2018 (2018), 33. https://doi.org/10.1186/s13662-018-1473-6 doi: 10.1186/s13662-018-1473-6
[34]
K. Yang, W. Ma, Z. Jiang, H. Yan, Differential equation model describing degradation of microcystins (MCs) and its theoretical analysis, (Chinese), Mathematics in Practice and Theory, 51 (2021), 231–247.
[35]
K. Song, W. Ma, S. Guo, Global behavior of a dynamic model with biodegradation of Microcystins, J. Appl. Anal. Comput., 9 (2019), 1261–1276. https://doi.org/10.11948/2156-907X.20180215 doi: 10.11948/2156-907X.20180215
[36]
M. R. Droop, Vitamin B12 and marine ecology. IV. The kinetics of uptake, growth and inhibition in Monochrysis lutheri, J. Mar. Biol. Assoc. UK, 48 (1968), 689–733. https://doi.org/10.1017/S0025315400019238 doi: 10.1017/S0025315400019238
[37]
J. Caperon, Time lag in population growth response of isochrysis galbana to a variable nitrate environment, Ecology, 50 (1969), 188–192. https://doi.org/10.2307/1934845 doi: 10.2307/1934845
[38]
H. I. Freedman, J. W. H. So, P. Waltman, Coexistence in a model of competition in the chemostat incorporating discrete delays, SIAM J. Appl. Math., 49 (1989), 859–870. https://doi.org/10.1137/0149050 doi: 10.1137/0149050
[39]
T. F. Thingstad, T. I. Langeland, Dynamics of chemostat culture: the effect of a delay in cell response, J. Theor. Biol., 48 (1974), 149–159. https://doi.org/10.1016/0022-5193(74)90186-6 doi: 10.1016/0022-5193(74)90186-6
[40]
K. Song, W. Ma, Z. Jiang, Bifurcation analysis of modeling biodegradation of microcystins, Int. J. Biomath., 12 (2019), 1950028. https://doi.org/10.1142/S1793524519500281 doi: 10.1142/S1793524519500281
[41]
J. Yang, S. Ding, J. Yang, Advances in process for microbial enzymes separation and purification, (Chinese), Modern Chemical Industry, 2007 (2007), 19–23. https://doi.org/10.16606/j.cnki.issn0253-4320.2007.06.005 doi: 10.16606/j.cnki.issn0253-4320.2007.06.005
[42]
H. Chen, W. Liu, Y. Du, G. Chen, B. Fang, Progress of operation of NADPH metabolism in industrial strains, (Chinese), Chemical Industry and Engineering Progress, 31 (2012), 2535–2541. https://doi.org/10.16085/j.issn.1000-6613.2012.11.035 doi: 10.16085/j.issn.1000-6613.2012.11.035
[43]
H. Yan, J. Wang, J. Chen, W. Wei, H, Wang, H. Wang, Characterization of the first step involved in enzymatic pathway for microcystin-RR biodegraded by Sphingopyxis sp. USTB-05, Chemosphere, 87 (2012), 12–18. https://doi.org/10.1016/j.chemosphere.2011.11.030 doi: 10.1016/j.chemosphere.2011.11.030
[44]
Z. Jiang, W. Ma, Y. Takeuchi, Dynamics for phytoplankton-zooplankton system with time delays, Funkcialaj Ekvacioj, 60 (2017), 279–304. https://doi.org/10.1619/fesi.60.279 doi: 10.1619/fesi.60.279
[45]
E. Beretta, Y. Kuang, Geometric stability switch criteria in delay differential systems with delay dependent parameters, SIAM J. Math. Anal., 33 (2002), 1144–1165. https://doi.org/10.1137/S0036141000376086 doi: 10.1137/S0036141000376086
[46]
S. Ruan, J. Wei, On the zeros of a third degree exponential polynomial with applications to a delayed model for the control of testosterone secretion, Math. Med. Biol., 18 (2001), 41–52. https://doi.org/10.1093/imammb/18.1.41 doi: 10.1093/imammb/18.1.41
[47]
K. Guo, W. Ma, Global dynamics of an SI epidemic model with nonlinear incidence rate, feedback controls and time delays, Math. Biosci. Eng., 18 (2021), 643–672. https://doi.org/10.3934/mbe.2021035 doi: 10.3934/mbe.2021035
[48]
M. Li, K. Guo, W. Ma, Uniform persistence and global attractivity in a delayed virus dynamic model with apoptosis and both virus-to-cell and cell-to-cell infections, Mathematics, 10 (2022), 975. https://doi.org/10.3390/math10060975 doi: 10.3390/math10060975
[49]
I. Barbǎlat, Systèmes d'équations différentielles d'oscillations non linéaires, (French), Revue de Mathématiques Pures et Appliquées, 4 (1959), 267–270.
[50]
S. A. DeLurgio, Forecasting principles and applications, Boston: Iwin McGraw-Hill, 1998.
[51]
C. D. Lewis, Industrial and business forecasting methods: a practical guide to exponential smoothing and curve fitting, Boston: Butterworth Scientific, 1982.
Luyao Zhao, Mou Li, Wanbiao Ma. Hopf bifurcation and stability analysis of a delay differential equation model for biodegradation of a class of microcystins[J]. AIMS Mathematics, 2024, 9(7): 18440-18474. doi: 10.3934/math.2024899
Luyao Zhao, Mou Li, Wanbiao Ma. Hopf bifurcation and stability analysis of a delay differential equation model for biodegradation of a class of microcystins[J]. AIMS Mathematics, 2024, 9(7): 18440-18474. doi: 10.3934/math.2024899
the concentration of the degrading enzymes produced by Sphingomonas sp. at time t
D
the continuous input rate of MCs, Sphingomonas sp., and the degrading enzymes
into the chemostat
a10
the input concentration of MCs
a12
the consumption rate of MCs
a13
the degradation rate of MCs
d1
the death rate of MCs
a21
the maximum growth rate of Sphingomonas sp.
a20
the consumption rate of Sphingomonas sp.
d2
the death rate of Sphingomonas sp.
a30
the rate at which Sphingomonas sp. produces the degrading enzymes that can be
used for the degradation of MCs.
a31
the consumption rate of the degrading enzymes
d3
the death rate of the degrading enzymes
τ1
the time that the organism (Sphingomonas sp.) stores the nutrient (MCs)
e−δ1τ1
the approximate proportion of individuals remaining in the chemostat during
the conversion process
τ2
the time required for Sphingomonas sp. to produce degrading enzymes
that can be used for the degradation of MCs
e−δ2τ2
the approximate proportion of the degrading enzymes produced by Sphingomonas sp.
that remains in the chemostat during the conversion process.
Parameters
MC-RR
MC-LR
MC-YR
Unit
Descriptions
Source
a12
1.44e−4
3.53e−4
1.58e−3
L×mg−1×h−1
the consumption rate of MCs
LSM
d1
0.006
0.006
0.006
h−1
the death rate of MCs
LSM
a21
4.82e−3
7.98e−3
3.00e−3
L×mg−1×h−1
the maximum growth rate of USTB-05
LSM
d2
4.25e−6
2.72e−5
2.00e−6
h−1
the death rate of USTB-05
LSM
τ1
13.60
18.44
14.61
h−1
the time that the organism (USTB-05) stores the nutrient (MCs)
LSM
Parameters
MC-RR
MC-LR
MC-YR
Unit
Descriptions
Source
a12
1.72e−4
4.84e−4
1.55e−3
L×mg−1×h−1
the consumption rate of MCs
LSM
d1
0.006
0.006
0.006
h−1
the death rate of MCs
LSM
a21
1.65e−3
2.62e−3
2.76e−3
L×mg−1×h−1
the maximum growth rate of USTB-05
LSM
d2
2.00e−7
2.68e−5
4.87e−6
h−1
the death rate of USTB-05
LSM
Parameters
MC-RR
MC-LR
MC-YR
Unit
Descriptions
Source
a13
2.23e−3
2.66e−3
2.81e−3
L×mg−1×h−1
the degradation rate of MCs
LSM
d1
5.75e−3
5.77e−3
5.72e−3
h−1
the death rate of MCs
LSM
a31
2.13e−8
7.07e−9
8.24e−8
L×mg−1×h−1
the consumption rate of USTB-05 enzymes
LSM
d3
3.73e−7
7.04e−8
7.82e−7
h−1
the death rate of USTB-05 enzymes
LSM
Figure 1. The solution curves and phase trajectory of model (2.1) for R0<1 with different initial values. Here, the boundary equilibrium E0(0.9901,0,0) is globally asymptotically stable
Figure 2. The plot of the function (τ2,S0(τ2))
Figure 3. The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=1<τ02. Here, the positive equilibrium E∗(0.8020,0.0370,0.0999) is locally asymptotically stable
Figure 4. The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=14∈(τ02,τ12). Here, the positive equilibrium E∗ is unstable and periodic oscillations occur
Figure 5. The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=17.79∈(τ12,+∞)∩I. Here, the positive equilibrium E∗(0.8020,0.1179,0.0595) is locally asymptotically stable
Figure 6. The plot of the function (τ2,S0(τ2))
Figure 7. The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=0.5<τ022. Here, the positive equilibrium E∗(0.4410,0.6930,0.2823) is locally asymptotically stable
Figure 8. The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=1.2∈(τ022,τ021). Here, the positive equilibrium E∗ is unstable and periodic oscillations occur
Figure 9. The solution curves and phase trajectory of model (2.1) for R0>1 with the initial value (0.5, 0.7, 0.5) and τ2=1.35∈(τ021,+∞)∩I. Here, the positive equilibrium E∗(0.4410,0.7193,0.2692) is locally asymptotically stable
Figure 10. The solution curves and phase trajectory of model (2.1) for R0>1 with different initial values and τ1=3.3007e−6, τ2=4.0184e−6. Here, the positive equilibrium E∗(0.0271,40.2768,0.0011) is globally attractive
Figure 11. The global attractivity region of the positive equilibrium E∗ with respect to τ1 and τ2
Figure 12. Experimental data and fitting curve of USTB-05 degradation of MCs. The green dots and pink dots in the figure represent the fitted data values at 48 hours in model (5.1) when τ1>0 and τ1=0, respectively
Figure 13. Experimental data and fitting curve of enzymes of USTB-05 degradation of MCs
Catalog
Abstract
1.
Introduction
2.
Preliminaties
3.
Local stability of the positive equilibrium and Hopf bifurcation analysis
4.
Global attractivity of the positive equilibrium