Abstract
In this work, we investigated a simple mathematical model describing the consumption of virus-infected phytoplankton by zooplankton in a chemostat. The system was studied by calculating the basic reproduction number, the equilibrium points, and their local and global stability. A sensitivity analysis was used to identify key chemostat factors that significantly affected the aquatic system. Additionally, we considered an optimal strategy based on the use of the dilution rate as an operating parameter that helps maintain the ecological balance of the aquatic food web.
Keywords:
chemostat; free virus; zooplankton; phytoplankton; sensitivity; optimal control; Pontryagin’s maximum principle MSC:
34K20; 34D23; 37B25; 49K40; 92D25
1. Introduction
A specific kind of bioreactor called a chemostat permits the continuous culture of microorganisms in a controlled environment. In other words, it allows for the growth of a population of microorganisms (such as phytoplankton, zooplankton, bacteria, yeasts, and unicellular algae) on specific substrates while maintaining the environmental conditions (temperature, brightness, pH, and aeration). It is employed to produce the actual cell mass, to extract and break down specific contaminants in a liquid medium, to produce organic materials as a result of metabolic activity, or to investigate the physiological and metabolic functions of microorganisms in a particular medium. Therefore, we may carefully analyze the impact of each substrate on an organism by changing the limiting substrates in a chemostat. Parasites have a significant impact on the features of the food web and are involved in many trophic interactions. Numerous studies have shown that predators typically hunt animals with a high parasite burden [1]. Several elements that control the complex planktonic food web include grazing by higher predators [2], a nutrient influx [3], and selective predation [4]. Zooplankton are capable of discriminatory feeding [5], and their food selectivity criteria vary to a large extent [6]. Zooplankton can selectively ingest their food depending on a myriad of factors, namely the size [7], digestibility [4], toxicity [8], availability [9], and nutrition value [10] of food. A number of studies have documented that Calanoid copepods can discriminate between toxic and nontoxic dinoflagellates [11], noxious and innoxious blue-greens [12], and live and dead algae of the same species [13]. It has been acknowledged that marine viruses have a significant role in changing the physiological and biochemical makeup of their hosts [14,15]. The feeding behavior and growth rate of zooplankton are influenced by the host cell features that are altered during viral infection, including the cell size, dispersed infochemicals, and cell lipid membrane properties [16,17]. The cocolithophore group of marine phytoplankton, which includes Emiliania huxleyi, is incredibly prevalent and may be found in the majority of marine environments. E. huxleyi burst into massive seasonal blooms when the environment is favorable [18]. Giant physcodnaviruses, also known as E. huxleyi viruses or EhVs, are known to lyse and infect E. huxleyi cells and are closely linked to population control and bloom termination [19]. In comparison to typical bloom circumstances, it has been shown that E. huxleyi produce higher amounts of DMS and DMSP when exposed to EhVs [20,21]. According to some research, the infochemicals that are expelled from infected cells serve as an active chemical signal that causes the grazer zooplankton to feed selectively [17,21,22,23]. Numerous writers have examined the effect of viral infection at the producer trophic level of marine ecosystems [24,25,26,27]. Under the hypothesis that healthy and infected phytoplankton are equally desirable for predation, some model-based studies specifically took into account the role of free viruses in eco-epidemiological systems [28,29]. Predators preferentially feed on both susceptible and diseased prey, according to recent research by Bairagi and Adak [30], who also examined the dynamics between predators and prey. Their results show that knowledge of the effects of a predator’s preference or selectivity may be crucial in determining the ecological characteristics and community structure of parasites. Bairagi et al. [31] have demonstrated that the nutritional value of phytoplankton and the selective predation of zooplankton have a significant influence on the intricate dynamics of plankton, including the bloom phenomenon, by classifying the entire phytoplankton population of a pelagic ecosystem into preferred and nonpreferred phytoplankton. The concept of grazer zooplankton’s selection inclination toward susceptible phytoplankton cells in the presence of infected ones was captured for the first time in this work. Our study’s goal was to find out how selective behavior affects the dominance and persistence of healthy phytoplankton cells. Additionally, we wanted to look into how the dynamics of phytoplankton–zooplankton in the system are affected by free viruses, as well as how the dynamics are regulated by the zooplankton’s selectivity behavior. The model analysis and numerical simulations provide answers to the aforementioned ecological questions.
This article is structured as follows: Section 2 describes a four-dimensional mathematical model that describes the growth of zooplankton on phytoplankton as an essential nutrient in the presence of a free virus affecting only the phytoplankton, with the phytoplankton present in two forms, susceptible and infected phytoplankton, in the chemostat. Section 3 proves the solution’s positivity and boundedness and defines the basic reproduction number and the equilibrium points and gives their local and global stability. In Section 4, a sensitivity analysis of the basic reproduction is discussed. Later, in Section 5, we propose an optimal strategy that it is based on using the dilution rate as a control to adjust the zooplankton concentration to a desired value, minimize the virus concentration inside the chemostat, and keep the dilution costs optimal. Finally, several numerical examples are given in Section 6 to confirm the theoretical findings.
2. Mathematical Modeling
Over the past few decades, there has been concern over the human-caused pollution of freshwater and marine systems. Both inorganic (like heavy metals) [32] and organic (like triazine herbicides) [33] substances may be detrimental to organisms. For instance, contaminants from recreational and industrial sources prevent the green algae Selenastrum capricornutum from photosynthesizing. Copper damages diatoms in a maritime planktonic community that is mostly composed of herbivorous copepods and diatoms in an environment with high copper and low silicate [34]. By preventing photosynthesis, the herbicide triazine also directly impacts primary producers at low doses, but its effects on following trophic levels would only be indirect [34]. The mortality rate of zooplankton is increased when water bodies are contaminated with pesticides like carbaryl, azadirachtin, or cypermetrin. Viral infections in phytoplankton populations do not spread through interaction between infected and susceptible phytoplankton. Virus particles typically bind to their host cells and transfer their genetic material into them. The virus then replicates its genetic material using the host cell’s machinery. The virus particles explode out of the host cell into the extracellular space after replication is finished, killing the host cell. The virus is prepared to infect additional vulnerable phytoplankton after it has fled from the host cell. A portion of the phytoplankton population is immediately transformed into an infected class by this type of transmission [28]. Furthermore, primary consumers such as copepods randomly consume E. huxleyi and other phytoplankton species when there is no viral infection, but zooplankton show some form of grazing preference when there is a viral infection [17,21].
Let , , and Z be the concentrations of susceptible phytoplankton, infected phytoplankton, and zooplankton in a chemostat (a laboratory aquatic ecosystem), and let be the concentrations of free viruses in the chemostat. We consider the following assumptions [35]:
- The susceptible phytoplankton enter into the chemostat at a constant input concentration, .
- The susceptible phytoplankton become infected through direct contact with free viruses, , living in the system, with a transmission rate of .
- The zooplankton grow on susceptible and infected phytoplankton. The susceptible phytoplankton are consumed by the zooplankton Z at a rate of ; however, the infected phytoplankton are consumed by the zooplankton Z at a rate of .
- Let us denote by the virus replication factor in the infected phytoplankton , i.e., the lysis of infected phytoplankton, producing virus particles on average ().
Figure 1 shows a chemostat into which susceptible phytoplankton () is continuously added and the liquid culture () is continuously removed at the same flow rate (D). However, Figure 2 shows a schematic diagram illustrating how all of the dynamical variables under consideration interact.
Figure 1.
A bioreactor with a continuous stirring mechanism that continuously adds susceptible phytoplankton () and continuously removes the liquid culture () at the same flow rate (D) [36,37,38,39].
Figure 2.
Schematic diagram of the desired system. , , Z, and describe the concentrations of susceptible and infected phytoplankton, zooplankton, and free viruses, respectively, in a chemostat.
Based on these ecological assumptions [35], we have the following system of nonlinear differential equations:
with the positive initial condition .
is the concentration of the susceptible phytoplankton in the chemostat at time t. describes the concentration of the infected phytoplankton in the chemostat. reflects the concentration of zooplankton in the chemostat. describes the concentration of free viruses in the chemostat. is the concentration of susceptible phytoplankton input into the chemostat. D is the dilution rate. and describe, respectively, the consumption rates of susceptible and infected phytoplankton by the zooplankton. is the saturated incidence rate. More details regarding the variables and parameters are given in Table 1. Note that the phytoplankton (either infected or not) are essential for the zooplankton’s growth and that the growth rate of zooplankton on susceptible phytoplankton increases with the susceptible phytoplankton concentration. Similarly, the growth rate of zooplankton on infected phytoplankton increases with the infected phytoplankton concentration. Furthermore, no infection can take place without the presence of free viruses in the chemostat. The growth rate of zooplankton on susceptible phytoplankton is more important than the one on the infected phytoplankton. The mortality rate of infected phytoplankton is greater than the mortality rate of susceptible phytoplankton.
Table 1.
Description of the variables, functions, and parameters of system (1).
We assume that
- A1 .
- A2 .
Assumption A1 expresses that the growth rate of the zooplankton on the susceptible phytoplankton is more important than the one on the infected phytoplankton. Assumption A2 expresses that in the absence of the virus, the zooplankton can survive only on the susceptible phytoplankton.
3. Mathematical Results
In order to prove that the system (1) is well designed, it is necessary that the state variables , , , and remain nonnegative for all values of .
Proposition 1.
The compact set is positively invariant for system (1).
Proof.
Since for , for , for , and for , the solution of system (1) is nonnegative. By adding the first four equations of system (1), one obtains, for , a single equation:
Hence, . Thus,
Furthermore, we have . Hence,
Therefore, is positively invariant for model (1) because all the variables are bounded since they are nonnegative. □
3.1. The Ecosystem Without Free Viruses
In the absence of free viruses, we obtain the classical chemostat model that is well studied in [40] and is given hereafter.
This model is similar to the one studied in [41,42]. A modified Beddington type of interaction between phytoplankton and zooplankton is assumed in [41]. In [42], the impact of phytoplankton’s release of toxins on zooplankton and the fish predation of zooplankton are examined. By taking into account that environmental pollutants raise the mortality rate of both phytoplankton and zooplankton, Yu et al. [43] investigated a stochastic model.
The compact attractive set of system (1) is reduced to . System (4) admits a trivial steady state, , and a nonnegative steady state, . Next, the local stability behaviors of the equilibrium points will be discussed.
Theorem 1.
- 1.
- There are no periodic orbits nor polycycles inside .
- 2.
- If (Assumptions A1–A2), then the equilibrium point exists and it is globally asymptotically stable, and is a saddle point.
- 3.
- If , then the equilibrium point is the unique equilibrium point of system (4), and it is globally asymptotically stable.
Proof.
- Let be a solution of (4) inside . By using the change in variables and , we obtain the following equations:The divergence of system (4) is given by
- For (Assumptions A1–A2), exists and the Jacobian matrix at is given bySince trace and det , both eigenvalues have a negative real part, and the equilibrium point is therefore a locally asymptotically stable node. The Jacobian matrix evaluated at is therefore given byadmits two eigenvalues that are given byTherefore, the equilibrium is a saddle point with a stable manifold given by . Let and . By applying the Poincaré–Bendixon Theorem [40], the steady state is found to be globally asymptotically stable.
- If , then is the only steady state and is locally stable. Since any omega limit set is contained in the two-dimensional compact invariant set , and lies on the boundary of , is globally asymptotically stable according to the Poincaré-Bendixson Theorem.
□
3.2. The Complete System
Let us return to the complete system (1). Let us calculate the steady states of system (1) satisfying
- If , then we obtain a pure epidemic model with a steady state satisfyingThen, , and with . Therefore, we obtain two equilibrium points, and .The development of new infections and changes in the status of infected individuals are described by two equations in our example (Equations (2) and (4) in system (1)). We define the matrix F to represent the rate at which new infections develop in these two equations and V to represent the rate at which individuals are transferred into and out of these compartments by all other mechanisms in order to create the next generation matrix. Next, the non-singular matrix V and the nonnegative matrix F are provided by and . Therefore, . The spectral radius of the next generation matrix FV−1, which can be represented as follows, is the basic reproduction number of (1).Note that . Therefore, exists only if .The Jacobian matrix at is given bywhere its characteristic polynomial is given byadmits , , according to Assumptions A1 and A2, and . Therefore, is an unstable equilibrium point.The Jacobian matrix at is given byThe characteristic polynomial is given byNote thatTherefore, if , then exists, and its Jacobian, , admits three negative eigenvalues and one positive eigenvalue, and thus is an unstable equilibrium point.
- If , then we havewith . We obtain two cases: The first case corresponds to the free viruses satisfying , , , and thus . The disease-free equilibrium point is given by . The second case satisfies . Therefore, , , and . We obtain the endemic equilibrium point that is given by . We aim to define the basic reproduction number again. Both the non-singular matrix V and the nonnegative matrix F are provided by and . Therefore, . The spectral radius of (1) is the spectral radius of the next generation matrix FV−1, expressed as follows:Note that in a population where all phytoplankton are vulnerable to infection in the presence of zooplankton, the basic reproduction number, or , is the anticipated number of instances directly caused by one infected phytoplankton.Let be the Jacobian matrix at .The characteristic polynomial of is given byNote that . Therefore, if , then exists, and its Jacobian, , admits three negative eigenvalues (according to Assumptions A1–A2) and one positive eigenvalue, and thus is an unstable equilibrium point. is a stable equilibrium point only if .Let us discuss the existence and stability of the endemic equilibrium point . Note that means that . Furthermore, we have and . Therefore, if , then , and thus exists. Let be the Jacobian matrix at , which is given byThe characteristic polynomial of is given bywhere ,, , and . In order to use the Routh–Hurwitz criteria, one must see that and deduce that because . The calculation of the two other conditions was too large, so we used Maple 12 software to verify that and , and thus we obtained the local stability of the equilibrium point once it exists ().
For the following subsection, we aimed to study the global analysis for model (1), and we considered only the more important case where , which leads to . Therefore, all equilibrium points (, , , and ) exist such that , , and are unstable equilibrium points; however, is a stable equilibrium point.
3.3. Reduction to 3D
The 4D dynamics solutions (1) converged in the direction of . It was sufficient to limit the study of the dynamics (1) to the set as our objective was to examine the asymptotic behavior of these solutions. This was because, according to Thieme’s findings [44], the trajectories’ asymptotic behavior would provide insight into the full dynamics (1). When restricted to , the system (1) becomes
where the solution will be restricted by the subset of given by
Therefore, the reduced model (11) admits four equilibrium points in that will be denoted as follows:
3.4. The Periodic Orbits on the Faces
Our goal in this section is to prove that there are no possible periodic orbits on the faces of the set , which will be useful later to prove that the solution will never converge to one of these faces [40,45].
- It is easy to see that the axes and are invariant. By applying the following change in the notations and for , one obtains the following model:
- It is easy to see that the axes and are invariant. By applying the following change in the notations and for , one obtains the following model:
3.5. Persistence
The objective of this section is to demonstrate the persistence of the phytoplankton (either infected or not), the zooplankton, and the free viruses by proving the uniform persistence of system (11). We prove that each of the boundary steady states of system (11) are unstable. Therefore, by consistently applying the Butler–McGehee lemma [40], we employ the same proof as the one utilized in comparable circumstances in [45]. Next, we recall a definition pertaining to the Butler–McGehee lemma [40] and uniform persistence [45].
Definition 1
([45]). Consider the dynamics with the initial condition where and . The dynamics are said to be weakly persistent once . They are said to be persistent once . They are said to be uniformly persistent once , satisfying .
Lemma 1
(Butler–McGehee lemma [40]). Consider to be a continuously differentiable function, to be a hyperbolic equilibrium point of the dynamics such that , to be the positive semi-orbit through , and to be the omega limit set of . Assume that belongs to , such that it is not the entire omega limit set. Then, should contain a non-trivial intersection of both the stable and unstable manifolds of .
Theorem 2.
Model (11) is persistent.
Proof.
The stable and unstable manifolds of the border steady states are known and depicted in Figure 3 to clarify the argument since the three faces , , and are invariant. Let be a solution having the initial condition such that , , and are provided. We will demonstrate by contradiction that there is not a point with a zero coordinate in the omega limit set.
Figure 3.
Equilibria configuration. , , and are unstable equilibrium points; however, is an asymptotically stable interior equilibrium.
- The omega limit set of , represented as , is assumed to include . It should be noted that is a saddle point with a dimension of one stable manifold, , that is limited to the -axis. In this case, is not the whole omega limit set . There is a point, , in , according to the Butler–McGehee lemma [40]. Note that the -axis is unbounded, but that is the -axis. The omega limit set of any orbit of the system (11) should be bounded since all of its orbits are bounded (within the limited set ). The existence of is contradicted by this. Consequently, should be confirmed.
- is assumed. Likewise, should not be the complete omega limit set ; hence, there is a point, , inside . Once is two-dimensional and completely contained in the face, this point should be inside the face. should contain the whole orbit via , just like in the cases of and . In Section 3.4, we demonstrated that there are no possible periodic orbits inside the face. The orbit becomes unbounded once , which runs counter to the assertion that is inside .
- is assumed. Given that is a saddle point, its stable manifold is limited to the plane and has two dimensions. Consequently, is not the whole omega limit set . Accordingly, a point, , exists inside according to the Butler–McGehee lemma [40]. Since lies entirely in the plane, and since the entire orbit through is in , this orbit is thus unbounded, which contradicts the fact that is inside .
Assume that , and let , with at least one of the components , , and being zero. Therefore, should contain the full orbit that passes over . Nevertheless, since there is no potential periodic orbit, the orbit should converge to one of the boundary equilibrium points since it should lie completely inside the , , or faces. The idea that all boundary equilibrium points are unstable is thus contradicted by the fact that this boundary equilibrium point is inside . Consequently, we have demonstrated that every component of the trajectory is bigger than zero.
and so system (11) is persistent (see [45] (Section 4.3) for another application). □
3.6. Uniform Persistence of System (7)
Keep in mind that persistence is the same as uniform persistence in a number of biological model scenarios [46]. Remember the theory in [46] regarding a dynamical system, , for which and are both invariant. This is relevant to our situation. Thus, under the following criteria, is uniformly persistent:
- The dynamics are weakly persistent;
- The dynamics are dissipative;
- The restriction of to is isolated;
- The restriction of to is acyclic.
Assume that the dynamics on defined in Proposition 1 are denoted by . is not invariant; however, when and is invariant on but repellent in the interior of on , the theorem in [46], as applied in [45,47], should be applied in our case, provided that both conditions 3 and 4 are met when restricting to . The invariant set is bounded for our system. Consequently, condition 1 is met. According to Theorem 2, condition 2 is true since the persistence implies weak persistence.
The union of the equilibrium points also covers the omega limit sets of , and as all border equilibrium points are hyperbolic, each one is the largest invariant set in its neighborhood, verifying that condition 3 is met. Since there is no cyclical link between the boundary equilibrium points, condition 4 is likewise met. As stated in the subsequent theorem, we consequently infer the uniform persistence of model (11).
Theorem 3.
Model (11) is uniformly persistent, i.e., , satisfying
3.7. Uniform Persistence of System (1)
To demonstrate that model (1) is also uniformly persistent, let us extend the persistence findings. If with the provided data , and , we obtain . Nevertheless, there is a time sequence () converging to ∞, where the corresponding solution is converging to , and . This suggests that is not globally attractive, which runs counter to the results given in Proposition 1. Additionally, suppose that contains a point on a boundary face where one of the variables , or is zero; hence, the complete orbit that passes through this point should be inside . Consequently, contains the full omega limit set .
Thus, the following theorem is the main finding that we can deduce.
Theorem 4.
Model (1) is uniformly persistent.
In the next section, the sensitivity analysis of the basic reproduction number will be discussed.
4. Sensitivity Analysis
Finding and measuring the input parameters’ contribution to the model’s outcomes is the goal of sensitivity analysis [48]. A sensitivity index is typically used to quantify the sensitivity of a variable to the parameters. This enables us to ascertain the relative change in a variable after the value of a parameter is altered. Specifically, we are able to identify the parameters that most affect the fundamental reproduction number . Partial derivatives were used to determine the sensitivity indices since is a differentiable function to certain parameters [48]. We aimed to perform a sensitivity analysis for the basic reproduction number by identifying its contribution to determining the stability of the persistence equilibrium . The sensitivity indices of with respect to a parameter, p, are given by [48]
The explicit expression of is given by .
By considering the model’s parameters, given in Table 2, we found the sensitivity indices of with respect to the model’s parameters, which are given hereafter in Table 3.
Table 2.
The parameter values used in all numerical simulations were selected arbitrarily. There is no biological meaning to these values.
Table 3.
Sensitivity of to the model’s parameters.
In relation to and , the sensitivity indices of are positive; however, the sensitivity indices of with respect to D, , , and are negative in Figure 4. Therefore, an increase in the values of parameters or leads to an increase in the value of ; however, an increase in the values of parameters D, , , and leads to a decrease in the value of . According to the values in Table 3, increasing (or decreasing) and by will increase (or decrease) the value by . However, increasing (or decreasing) D by will decrease (or increase) the value by . Similarly, increasing (or decreasing) by will decrease (or increase) the value by . Similarly, increasing (or decreasing) by will decrease (or increase) the value by . Finally, increasing (or decreasing) by will decrease (or increase) the value by . Note that is not sensitive to the other parameters of system (1).
Figure 4.
Sensitivity analysis for .
In the next section, the optimal control problem will be discussed.
5. Optimal Control Strategy
This section’s objective is to suggest an optimal strategy to adjust the concentration of the zooplankton, , to the desired value, , and minimize the virus concentration inside the reactor while maintaining an optimal dilution rate, , throughout the process. Several strategies have been applied in some mathematical studies on the anaerobic digestion process with and without the influence of leachate recirculation [49,50]. We will take into account an objective functional that reflects the adjustment of the concentration of the zooplankton, , to the desired value, , maintaining the validity of the biological process. Let be the control function representing the dilution rate (cost). The set of permissible controls is provided by
minimizing the objective function considered hereafter:
By selecting suitable positive balancing constants, , , and , the goal is to attain the desired value of the concentration of the zooplankton, , minimize the virus concentration inside the reactor, and also minimize the cost of the dilution rate, .
We demonstrate the existence of both the optimal control and the corresponding states using classic results [51]. For , system (1) can be transformed as the following:
with and .
Note that satisfies
where
Since , with , and therefore is a uniformly Lipschitz continuous function.
Consequently, a unique solution is admitted by system (17). It is possible to construct the optimal control problem for dynamics (17) subject to the minimization of the objective functional J in terms of the Hamiltonian function by using Pontryagin’s maximum principle [51,52,53].
The adjoint system provided below considers the adjoint variables , and , which correspond to the states , and with a given optimum control, D.
with , , , and .
At D, the Hamiltonian is reduced in relation to the control variable. The Hamiltonian’s derivative is provided by
Therefore, admits the solution
provided that and
In summary, the characterization of the control is
In the next section, several numerical examples will be given confirming the theoretical findings.
6. Numerical Investigations
We provide several numerical examples to support the results achieved. Using MATLAB R2024a software, the Runge–Kutta–Fehlberg method was the numerical approach used to solve the model (ode45). The parameter values used in all numerical simulations were selected arbitrarily for each case.
6.1. Direct Problem
A number of numerical examples for system (1) are presented for a fixed dilution rate. In Figure 5 and Figure 6, all components persist and then the positive steady state is stable. In Figure 7 and Figure 8, the zooplankton go extinct and the other variables persist. In Figure 9 and Figure 10, the system becomes disease-free and the phytoplankton and zooplankton persist. In Figure 11 and Figure 12, both the infectious virus and the zooplankton go extinct, and the susceptible phytoplankton persists.
Figure 5.
Dynamics of model (1); the components’ behavior (left) and the comportment (right) for , , , , , , and , with . The green dot (right) is the initial condition, and the red dot (right) is the equilibrium point in the space .
Figure 6.
The dynamics of the variables for a range of initial values for , , , , , , and , with . The various initial conditions are shown by the various colors.
Figure 7.
Dynamics of model (1); the components’ behavior (left) and the comportment (right) for , , , , , , and , with . The green dot (right) is the initial condition, and the red dot (right) is the equilibrium point in the space .
Figure 8.
The dynamics of the variables for a range of initial values for , , , , , , and , with . The various initial conditions are shown by the various colors.
Figure 9.
Dynamics of model (1); the components’ behavior (left) and the comportment (right) for , , , , , , and , with . The green dot (right) is the initial condition, and the red dot (right) is the equilibrium point in the space .
Figure 10.
The dynamics ofthe variables for a range of initial values for , , , , , , and , with . The various initial conditions are shown by the various colors.
Figure 11.
Dynamics of model (1); the components’ behavior (left) and the comportment (right) for , , , , , , and , with . The green dot (right) is the initial condition, and the red dot (right) is the steady state in the space .
Figure 12.
The dynamics of the variables for a range of initial values for , , , , , , and , with . The various initial conditions are shown by the various colors.
6.2. Optimal Control Problem
The dilution rate, D, is assumed to be a time-varying function, , in the following examples. Its initial value is , and its bounds are and . The initial state value is taken into consideration. Appendix A provides the numerical scheme utilized for the control problem. Figure 13, Figure 14 and Figure 15 demonstrate how smooth the ideal solution is. If we increase the values, the control values decrease; if we increase the and values, the control values increase. Keep in mind that altering the values of and does not affect the final zooplankton concentration value. The best approach involves lowering the virus content within the chemostat for ideal dilution rate values (costs) and adjusting the zooplankton concentration to an ideal value.
Figure 13.
Impact of the optimal dilution rate on the system for , , and .
Figure 14.
Impact of the optimal dilution rate on the system for , , and .
Figure 15.
Impact of the optimal dilution rate on the system for , , and .
7. Conclusions
We looked at a straightforward mathematical model in four dimensions that describes the growth of zooplankton on phytoplankton that it are affected by a free virus under perfect mixing conditions in a chemostat. The phytoplankton were present in two forms: susceptible and infected phytoplankton. We studied the system by calculating the basic reproduction number, the steady states, and their local and global stability. We studied the sensitivity of the basic reproduction number with respect to the model’s parameters. Furthermore, we proposed an optimal control for the dilution rate with the aim to adjust the zooplankton concentration to an optimal value and decrease the virus concentration inside the bioreactor with optimal dilution costs. Lastly, we presented a number of numerical tests that validated the results.
The marine ecosystem may be at risk due to pollutants. Although there are many diverse sources of pollution, the most well-known ones include runoff from agriculture, industry, and home sewage. Plankton communities are impacted by environmental pollutants on a number of levels, including their abundance, growth methods, dominance, and succession patterns. These poisons are transferred cascadingly to higher trophic levels in the food chain during predation. The distribution pattern and behavioral characteristics of marine species in the ecosystems largely determine the rate of contact between environmental toxins and these organisms [54]. Among a variety of phytoplankton populations, environmental pollutants implicitly inhibit the proliferation of phytoplankton cells [55,56]. This growth inhibition tendency of environmental toxins has been statistically included in a few recent studies [41,42]. It has been demonstrated that a destabilized system can result from the growth inhibition of phytoplankton populations caused by environmental toxins. Therefore, removing environmental pollutants from an aquatic system is essential to keeping it stable. By taking into account toxin-producing phytoplankton and Markov switching in an intensively polluted environment, Yu et al. [43] investigated a stochastic phytoplankton–zooplankton model and discovered that the exogenous toxicant input and environmental fluctuations significantly impact plankton survival. Therefore, future research could look into the effects of both free viruses and environmental toxins on the growth of zooplankton on phytoplankton in a chemostat as a potential extension of this study.
Author Contributions
Conceptualization, N.A.A. and M.E.H.; methodology, N.A.A. and M.E.H.; software, N.A.A. and M.E.H.; investigation, N.A.A. and M.E.H.; visualization, N.A.A. and M.E.H.; writing—original draft, N.A.A. and M.E.H.; writing—review and editing, N.A.A. and M.E.H. All authors have read and agreed to the published version of the manuscript.
Funding
This work was funded by the University of Jeddah, Jeddah, Saudi Arabia, under grant No. UJ-24-DR-2553-1.
Data Availability Statement
The original contributions presented in the study are included in the article; further inquiries can be directed to the corresponding author.
Acknowledgments
This work was funded by the University of Jeddah, Jeddah, Saudi Arabia, under grant No. UJ-24-DR-2553-1. Therefore, the authors thank the University of Jeddah for its technical and financial support. The authors are also grateful to the anonymous reviewers for their many constructive suggestions, which helped to improve the presentation of the paper.
Conflicts of Interest
The authors declare no conflicts of interest.
Appendix A. A Suitable Numerical Scheme for Resolving the Control Problem
The time interval is subdivided such that . Let , , , , , , , , and be the values of , , , , , , , , and the control at the time and , , , , , , , , and be the values of the state and adjoint variables and the controls at and , , , , , , , , and be the values of the state and adjoint variables and the control at . For the state variables, an implicit finite difference approach akin to the Gauss–Seidel method was developed. However, the adjoint states were solved using a first-order backward difference.
Hence, was calculated as follows:
provided that and .
The algorithm given hereafter was applied using MATLAB R2024a software.
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