Abstract
This paper is devoted to a mathematical model for phenol and p-cresol mixture degradation in a continuously stirred bioreactor. The biomass specific growth rate is presented as sum kinetics with interaction parameters (SKIP). A discrete time delay is introduced and incorporated into the biomass growth response. These two aspects—the mutual influence of the two substrates and the natural biological time delay in the biomass growth rate—are new in the scientific literature concerning bioreactor (chemostat) models. The equilibrium points of the model are determined and their local asymptotic stability as well as the occurrence of local Hopf bifurcations are studied in dependence on the delay parameter. The existence and uniqueness of positive solutions are established, and the global stabilizability of the model dynamics is proved for certain values of the delay. Numerical simulations illustrate the global behavior of the model solutions as well as the transient oscillations as a result of the Hopf bifurcation. The performed theoretical analysis and computer simulations can be successfully used to better understand the biodegradation dynamics of the chemical compounds in the bioreactor and to predict and control the system behavior in real life conditions.
1. Introduction
Wastewater treatment is essential for public health and environmental protection. This is a specific process for removing various contaminants from wastewater. The idea is to safely release treated water into the environment or reuse it. In this regard, practical research related to the hydraulic efficiency of green–blue flood control scenarios for vegetated rivers is currently being expanded []. The extent to which wastewater needs to be treated is determined by government water management standards and the specifics of the environment []. The treatment process takes place in wastewater treatment plants or a bioreactor. The main methods used for wastewater treatment are mechanical, biological, and chemical. Biological wastewater treatment is performed under aerobic or anaerobic conditions for biomass growth depending on the specific microorganisms used as well as on the nature and concentrations of the contained pollutants [,]. The choice of a particular method depends on the type of polluted water and the nature and concentrations of the pollutants.
The main pollutants of industrial and domestic wastewater are plant nutrients, individual or mixtures of synthetic organic chemicals, inorganic chemicals including heavy metals, pathogenic organisms, oil, sediments, radioactive substances, etc. [].
Some of the most toxic and common mixtures of synthetic organic chemicals are phenol and its derivatives including resorcinol, hydroquinone, 3-nitrophenol, 2,6-dinitrophenol, 3-chlorophenol, p-cresol (4-methylphenol), benzene, etc. Numerous scientific studies and practical applications have proven the potential of several microorganisms to biodegrade mixtures of phenol and its derivatives to environmentally friendly substances [,,]. It has been found that very good results in the biodegradation of phenolic compounds are achieved by the strains Arthrobacter, Aspergillus awamori, Burkholderia, Candida tropicalis, Pseudomonas, Rhodococcus, Trametes hirsute, Trichosporon cutaneum, just to mention a few [,,,].
Generally speaking, the kinetics describing microbial growth and biodegradation of phenolic components (substrates) are of great importance for studying the peculiarities of the wastewater treatment process []. Kinetic models are developed on the basis of expert knowledge and laboratory research with specific strains and particular water pollutants. The kinetic models provide opportunities to study various characteristics of the wastewater treatment process and support the successful and effective achievement of the prescribed environmental criteria [].
Specific microorganisms’ growth rates in a substrate mixture of two or more phenolic components are known as sum kinetic models (without interaction); multiplication kinetic models; sum kinetic models which incorporate purely competitive substrate kinetics; sum kinetics with interaction parameters (SKIP); elimination capacity-sum kinetics with interaction parameter (EC-SKIP); self-inhibition EC-SKIP (SIEC-SKIP), etc. [,,,,,].
The SKIP models are a successful extension of the sum kinetics models, because they take into account the mutual influence of the components in the substrate mixture [,]. The SKIP models demonstrate excellent prediction of the biodegradation with different microbial strains of the mixture of phenol and its derivatives: benzene, toluene, and phenol biodegradation by Pseudomonas putida F1 []; ethylbenzene and styrene by R. pyridinovorans PYJ-1 []; phenol and p-cresol mixture degradation by Aspergillus awamori strain [], etc.
In [], a mathematical model was proposed for phenol and p-cresol mixture degradation in a continuously stirred tank bioreactor. The model was presented by a system of three nonlinear ordinary differential equations as follows
where is the biomass specific growth rate, described by the SKIP (sum kinetics with interaction parameters) model in the form
In the analytic expression of , the interaction parameters and indicate the degree to which the substrates p-cresol and phenol affect the biodegradation of phenol and p-cresol, respectively. Two inhibition parameters, and , are also included in the biomass specific growth rate .
The state variables X, , , and the model parameters are described in Table 1. The numerical values in the last column were validated by laboratory experiments using the Aspergillus awamori strain and given in [].
Table 1.
Model variables and parameters.
In this paper, we modify model (1) by introducing a discrete time delay incorporated into the biomass growth response
The constant stands for the time delay in the conversion of the consumed substrate into viable biomass. The term represents the biomass of microorganisms that consumes nutrients at time and survives in the bioreactor for units of time, necessary to complete the conversion of substrate into viable biomass [,].
Bioreactor (chemostat) competition models involving time delay, recently, have been widely discussed and investigated in the literature. According to [], the conversion process of nutrients to biomass always requires a fixed length of time and thus the corresponding chemostat model should be described by a system of differential equations with discrete delays. To our knowledge, the first attempt to introduce a discrete time delay was in [], where a linear bioreactor model was discussed. Other early models in this regard can be found in [], where the effects of time delay and growth rate inhibition in the bacterial treatment of wastewater were discussed, as well as in [], where the appearance of a time delay was motivated by the existence of a lag phase in the growth response of microorganisms in the medium. A basic and well known chemostat model incorporating a time delay was proposed and studied in []. This model contained three nonlinear ordinary differential equations, describing competition of two species on a single nutrient, and established the validity of the Competitive Exclusion Principle (CEP). CEP means that the species with the lowest break-even concentration can survive in the chemostat, and it drives other species to extinction. Two-species competition was also considered in [], where CEP was proved as well. On the other hand, introducing a time delay explicitly into the model equations can help to explain the transient oscillation behavior of the bioreactor dynamics often observed in practical experiments. Detailed investigations in this direction can be found in [] on a ‘single biomass/single substrate’ model.
Recently, various mathematical delayed models involving different numbers of species growing on one or more substrates and involving different kinds of specific growth rates (monotone, such as the Monod law, or nonmonotone, such as the Haldane law, etc.) have been discussed, see [,,] and the references therein. The latter papers consider competition of n species of microorganisms on a single substrate. In [], sufficient conditions are presented which enhance the CEP and thus the global asymptotic stability of the model solutions. This was calculated for general nonmonotone response (specific growth rate) functions. The same time delayed model was modified in [] by introducing specific species death rates, different from the dilution rate in the chemostat. Under certain conditions, it was shown that the single species survival equilibrium is globally asymptotically stable. It was demonstrated numerically that the differential removal rates can lead to damped oscillation in the solutions. Similar results were established for the same model in []. There, the competitive exclusion was established by applying the method of Liapunov functionals under some technical assumptions on the biomass response functions.
In this paper, we perform mathematical analysis of the time delayed model (3)–(5). In Section 2, we find the equilibrium points of the model and investigate their local asymptotic stability and occurrence of Hopf bifurcations with respect to the delay . The basic properties of the model solutions as well as the global stabilizability of the model dynamics are presented in Section 3. Section 4 includes numerical examples, supporting the theoretical results. Concluding remarks are presented in Section 5.
2. Equilibrium Points, Local Stability, and Bifurcations
In the mathematical analysis of the model (3)–(5), we assume that the influent concentrations and are constant and consider the dilution rate D and the delay as varying parameters.
The equilibrium points of (3)–(5) are obtained as solutions of the following system of transcendental equations
Obviously, (with ) is an equilibrium point of the model for all and and is called the boundary or washout equilibrium.
In what follows, we look for solutions of (6)–(8) such that .
Similar to [], multiplying Equation (7) by , Equation (8) by , and summing them together leads to
Denoting
we obtain
The latter expression is biologically relevant if and only if . Using the numerical values in the last column of Table 1, it follows that this is satisfied: .
Now, we substitute from (11) into the expression of and obtain the specific growth rate as a function of only. Denote for simplicity
or explicitly
Figure 1 shows the graph of the function for , using the numerical values in the last column of Table 1.
Figure 1.
Graph of the function for . The vertical dot line passes through .
From Equation (6), we learn that the steady state component with respect to is the solution of the equation
If there exists a root of the latter, such that , then the equilibrium components with respect to X and are determined by the formulae
Denote . Obviously, all components of depend on the control parameter D and on the delay .
The graph of suggests the following properties of the latter, which are used in the further investigations.
Properties of
(P1) for all , and .
(P2) There exists a point such that if , and if .
(P3) The following inequalities hold true: .
For any define
Obviously, is a decreasing function of . Moreover, for any , the following inequalities are fulfilled:
Based on the above considerations we draw the following conclusions:
Therefore, the model (3)–(5) possesses up to two interior (with positive components) equilibrium points depending on the values of and D. Denote them by
where and , , are determined according to (15) after replacing the with and , respectively.
In what follows, we study the local asymptotic stability of the model equilibrium points. Here, we use the linearization technique for differential equations with a discrete time delay (see []).
The characteristic polynomial corresponding to the Jacobian matrix J of (3)–(5) is defined by , where is any complex number, and is the –identity matrix:
The following presentation holds true
Obviously, are always solutions of , i.e., eigenvalues of the Jacobian matrix evaluated at the equilibrium point , . The third eigenvalue of (17) is the root of the equation
the latter being evaluated at the components of , .
Straightforward calculations show that
where
Therefore, the characteristic Equation (18) can be rewritten in the form
where means .
In the next subsections, we study the local asymptotic stability and existence of Hopf bifurcations of the equilibrium points with respect to the delay .
2.1. The Interior Equilibrium
The interior equilibrium exists for and
Proposition 1.
For the model (3)–(5), the equilibrium point is locally asymptotically stable for all .
Proof.
The characteristic Equation (19) evaluated at is
Using the fact that , we obtain
We have in this case , so that holds true. Denote . Then the characteristic Equation (20) takes the form
Applying Theorem 1.4, Chapter 3 in [], it is enough to show that there are no purely imaginary roots , , of the latter equation. Indeed, using the presentation we obtain
Separating the real and the imaginary parts leads to
Squaring both sides in the latter equations and adding them implies
The last inequality shows that there are no pure imaginary roots of (20). This means that the interior equilibrium is locally asymptotically stable whenever it exists, i.e., m for all . The proof is completed. □
2.2. The Interior Equilibrium
Proposition 2.
For the model (3)–(5), the equilibrium point is locally asymptotically unstable for all .
Proof.
Using (21), denote
Since and , this implies that possesses at least one positive real root, and therefore is locally asymptotically unstable. □
Below, we study conditions under which the coexistence equilibrium is nonhyperbolic and undergoes local Hopf bifurcations with respect to the delay . The investigations use the same techniques as in []. We present them here in the notations of our model (3)–(5) for completeness and the reader’s convenience. The proofs of the results can be found in Appendix A.
Denote for convenience
According to Property (P2) of , it follows that for holds true. Then the characteristic Equation (21) is presented by
We are looking for solutions of (23) with respect to of the form , . For , , and using the equality , we obtain
Separating the real and the imaginary part of the latter leads to
Further, the equalities
imply
Then we have from (24)
We are looking for positive solutions with respect to of equations (26). As in [], we first investigate solutions of
where . For any fixed there will be a unique solution of (27) if the line is tangent to the curve . Denote by this unique solution in the interval , see Figure 2. Using the equality and solving for , we obtain . Clearly, if then (27) has no solutions in the interval , and if then there are exactly two solutions of (27) in the interval , one less than and one larger than (cf. Figure 2).
Figure 2.
Solutions of . The lines are , , and .
Assume that for some integer . Let be the unique solution of for and be the unique solution of for . Then is strictly decreasing, is strictly increasing, and (cf. [])
Differentiating, with respect to , the equality
and using the implicit function theorem, we obtain consecutively
Similarly, one obtains
Since is increasing for , , using the relations
we find that for . Similarly, one can show that for holds true. Therefore,
Define the function
Obviously, is defined and nonnegative for all if and only if holds true. If for some values of , then is not defined on the whole interval .
The function plays a significant role in investigating the existence of Hopf bifurcations of (cf. []). However, since , it can be used to detect other types of bifurcations of . Indeed,
- If there exists such that , then , i.e., . This means that is eventually a root of the characteristic Equation (23), so that the equilibrium becomes nonhyperbolic at leading to some kind of bifurcation.
Theorem 1.
[] Let be the largest integer such that holds true. Then the following assertions are valid:
If is a solution of (26), then the curve intersects one of the curves , , , at .
Let intersects or at for some . Then is a solution of (26), if and only if
The proof can be found in Appendix A.
Theorem 1 implies that if and , , do not intersect for , then, the equilibrium is hyperbolic, i.e., does not undergo any bifurcation with respect to .
Theorem 2.
[] Let be a root of the characteristic Equation (23) such that , . Then
The proof is given in Appendix A.
Corollary 1.
[] Let the assumptions of Theorem 1(i) be satisfied. Then the following assertions are valid:
There exists a unique integer j, , , or for some , such that the curves and intersect at .
If or , then
The proof is presented in Appendix A.
The next theorem reports the final result on the existence of local Hopf bifurcations of the interior equilibrium .
Theorem 3.
[] Let be a solution of (26). Then the following assertions hold true:
(i) There exists a unique integer such that .
(ii) If , where or for some integer i, , and or , then the equilibrium undergoes a Hopf bifurcation at . All bifurcating periodic solutions are positive and unstable and have periods in the intervals
The proof can be found in Appendix A.
2.3. The Washout Equilibrium
For (with ), we obtain from (19) the following characteristic equation
Proposition 3.
For the model (3)–(5), the equilibrium point is locally asymptotically stable for and locally asymptotically unstable for .
Proof.
Consider the characteristic Equation (40), and define the function
First, let , or equivalently, . We have
This means that there is at least one negative root of the characteristic Equation (40), thus is locally asymptotically stable.
In the case when , i.e., when , we have
so there is at least one positive root of the characteristic Equation (40), which means that is locally asymptotically unstable. This completes the proof. □
Although the washout equilibrium is not of practical interest, in Section 3 we shall prove that it is also globally asymptotically stable if . Global stability of means total washout of biomass in the reactor and breakdown of the degradation process.
In the same way as in [], one can show existence of Hopf bifurcations of when it is locally unstable, i.e., for . In this case, due to the zero X-component, the periodic solutions bifurcating from cannot be nonnegative. Any periodic solution surrounding will involve negative and positive values, i.e., the X-component of any such periodic solution will have a zero in the interval for certain and for any and will change sign there. Such kinds of periodic solutions are not biologically relevant, and we skip the corresponding investigations. The interested reader can consult [], as well as [], for more information.
3. Global Properties of the Time-Delayed Model Solutions
Consider the time-delayed model (3)–(5). Denote by the set of all nonnegative real numbers and by the Banach space of continuous functions . Define
and assume that the initial data for model (3)–(5) belong to .
According to the theory of functional differential equations (cf. [,,]), for each there exists a unique solution
of (3)–(5) defined on such that for each .
Denote , where K and are defined by (10). After multiplying Equation (5) by and adding it to Equation (4) we obtain
The latter equality means that , , so . Then, system (3)–(5) can be written in the form
Since for any , and we are interested in the asymptotic behavior of the dynamics, we consider the limiting system
where , cf. (12). The initial conditions for (41) belong to the set
Let us fix an arbitrary , and denote . If no confusion arises, we shall also use the simpler notation , as well as , instead of . As mentioned before, the solution of (41) is defined and exists for all .
Theorem 4.
If for all , then for all .
Let the following inequalities be fulfilled
Then the solution of (41) is positive for all and is uniformly bounded.
Proof .
is obvious. The plane is invariant for the model (41). Therefore, we shall consider solutions with for all .
Assume that . Then, from the second equation of (41), we have
This implies that for all .
Further, applying the variation-of-constant formula, we obtain
which implies that for each .
Denote
Then
The latter equality implies
where exponentially as . This means that all nonnegative solutions are uniformly bounded and thus exist for all . The proof is completed. □
Remark 1.
Condition (42) can be explained by the complicated expression of the SKIP model , and, in particular, by the fact that is strongly positive (see Property (P1)). Usually, in bioreactor models, the specific growth rate is assumed to satisfy . In particular, if we assume that are simultaneously fulfilled, i.e., initially the whole mixture of phenol and p-cresol is not available in the bioreactor, then condition (42) is not necessary, and it can be proved as above that all model solutions are strongly positive and uniformly bounded for all time .
The equilibrium points , , and of the reduced model (41) take the form
In what follows, we prove that the interior equilibrium point is globally asymptotically stable whenever it exists, i.e., for .
Lemma 1.
Let be a positive solution of (41). If , then there exists time such that for all .
Proof.
Let . Assume that there exists time such that for all . Then
thus, is a strictly decreasing function. Since is uniformly continuous in , applying Barbălat’s Lemma [], we obtain
Since and , the above equality implies that and as . Define the function (cf. Lemma 2.2 in [])
Then
Since, in this case, , we find that for all sufficiently large . So, there exists such that as . However, this is impossible according to the definition of , and because we have already shown that as . Hence, there exists a sufficiently large time such that . Moreover, if there exists such that then
The last inequality shows that for all . The proof is completed. □
Lemma 2.
Let be a positive solution of (41) and be its interior equilibrium point. Denote
Then and hold true.
Proof.
Assume that . Choose an arbitrary
According to Theorem 4 (see (43)), there exists time such that for all the following inequalities hold true
Lemma 1 implies that there exists time such that for all . Since , there exists such that for all . We set (cf. Lemma 3.5 in [])
Then , , for all , and
From (46) and the choice of we obtain
and further, taking into account the monotonicity of (Property (P2)), it follows
The last equality contradicts (47), which means that .
Assume now that , i.e., that the limit of exists as . We shall show that holds true. By Barbălat’s Lemma, we obtain that , i.e.,
It follows then that as , which means that as and thus
Hence, if , then holds true.
Now assume that , i.e., the limit of exists as . We shall show that is fulfilled. Applying Barbălat’s Lemma yields , i.e.,
which means that
From here, it follows that there exists the limit of as , i.e., is satisfied.
Next, we show that the equalities and are simultaneously fulfilled. Thus, we shall use some ideas from the proofs of Lemma 4.3 in [] and Theorem 3.1 in [].
Let be an arbitrary fixed number. The Fluctuation Lemma [] implies that there exists a sequence such that for each m we have
The equality leads to
Since can be arbitrarily small, it follows that
The latter inequality yields
and hence
Similarly, one can show that . This and (48) lead to
Applying the Fluctuation Lemma again, there exists a sequence such that for each k we have
Then
and therefore
Theorem 5.
Let and be an arbitrary element with such that (42) is fulfilled. Then, the corresponding positive solution converges asymptotically towards .
Proof.
Lemmas 1 and 2 imply that the solution is convergent as . Let , . Applying Barbălat’s Lemma, we obtain
and hence
From here, it follows that , because is the locally asymptotically stable equilibrium for according to Proposition 1. The proof is completed. □
The next Theorem 6 proves that the locally asymptotically stable washout equilibrium is also globally asymptotically stable. The proof uses similar ideas to Theorem 2.3 of [].
Theorem 6.
Proof.
Let . According to the definition of , this means that .
Suppose that for all sufficiently large t. Then using the function in (44) we obtain from (45)
The last inequality follows from the fact that is an increasing function for . Therefore, as for some . Since is bounded and uniformly continuous, it follows by Barbălat’s Lemma [] that as , i.e.,
Assume that there is a sequence such that . Then , which implies that , a contradiction. Therefore, for all sufficiently large t.
Assume that for all sufficiently large . Then it follows from the second equation of (41) that for all large t, which implies that for some . If , then
because is decreasing for . Therefore, as for some . Barbălat’s Lemma then implies that as , which means that leading to as . If , then obviously . Therefore, is globally asymptotically stable for the model (41). The proof is completed. □
4. Numerical Simulation
Here, we illustrate the theoretical results from the previous sections on three numerical examples for different values of the parameters D and . We use the numerical values of the model parameters in Table 1.
We notice that if is fulfilled.
The next computer simulations illustrate the occurrence of Hopf bifurcations of the interior equilibrium , investigated in Section 2.2. First we have to determine the tangent point of and the line , which coincides with the unique solution of , i.e., with the unique solution of in the interval for some (cf. []). We obtain the following values
Example 1.
For this value of D we obtain
thus, holds true. According to Theorem 1, we have , thus, there are two solutions and , and the equilibrium undergoes Hopf bifurcations at the following four values of :
Figure 3 visualizes the curve and the solutions and as well as the above intersection points.
Figure 3.
Graph of the function and of the solutions , .
We take . At this value of the delay, the two interior steady states are
According to Proposition 2, is locally asymptotically unstable for all . Theorem 5 implies that the equilibrium is globally asymptotically stable for .
Figure 4 and Figure 5 show the time evolution of the solutions of the model (3)–(5). Although the initial conditions are chosen near to , the solutions tend to the globally asymptotically stable equilibrium . Transient oscillations in the time evolution of the phase , and are observed in the right plot of Figure 4 and in Figure 5.
Figure 4.
Example 1. Left plot: solutions of (3)–(5). Right plot: transient oscillations of the phase variable .
Figure 5.
Example 1. Transient oscillations of the phase variables (left) and (right).
The next two examples demonstrate the global stability of the equilibrium points and with respect to D and .
Example 2.
For this value of D we obtain
We choose and fix . Then, there exist the two interior equilibria
Proposition 2 implies that is locally asymptotically unstable, and is the global attractor for the model (3)–(5) according to Theorem 5.
According to Theorem 4(ii) the inequality
should be fulfilled to ensure existence of positive model solutions. The right plot in Figure 6 visualizes the time evolution of towards the globally asymptotically stable equilibrium . As expected, no oscillations are observed in the time evolution of each one of the variables (right plot in Figure 6), as well as of and even for the short time , Figure 7.
Figure 6.
Example 2. Global stability of the equilibrium point (left). Time evolution of the phase variable for (right).
Figure 7.
Example 2. Time evolution of the phase variables (left) and for (right).
Example 3.
Here we have
Taking we obtain
In this case, is the global attractor of the model (Theorem 6), and is locally asymptotically unstable (Proposition 2).
According to Theorem 4, the inequality
has to be satisfied so that the model (3)–(5) possesses positive solutions. The left plot in Figure 8 illustrates the global stability of the washout equilibrium . The right plot of Figure 8 and Figure 9 show the evolution of each phase variable , , for a shorter time . Again, no transient oscillations can be seen in these plots.
Figure 8.
Example 3. Global stability of the equilibrium point (left). Time evolution of for (right).
Figure 9.
Example 3. Time evolution of (left) and for (right).
5. Conclusions and Future Work
We considered a time-delayed model, describing a phenol and 4-methylphenol (p-cresol) mixture biodegradation in a continuously stirred tank bioreactor with a SKIP specific growth rate. It was based on a previously proposed and studied dynamical model, presented in []. The discrete time delay was introduced in the microorganisms’ growth response to indicate the delay in the conversion of the consumed nutrient into viable biomass.
We presented the mathematical analysis of the proposed time-delayed model. First, in Section 2, the equilibrium points were determined, and their local asymptotic stability was investigated in dependence on the delay (and on the dilution rate D). Three equilibrium points were found, namely a boundary (washout) equilibrium with and two interior (coexistence) equilibria and with . For any fixed , values of were determined, , and it was shown that
- exists and is locally asymptotically stable for (Proposition 1);
- exists and is locally asymptotically unstable for (Proposition 2);
- exists for all and is locally asymptotically stable (unstable) if () (Proposition 3).
Then, we showed that the locally unstable equilibrium underwent local Hopf bifurcations at certain critical values of the delay parameter (Theorems 1–3). To prove this, we exploited a known approach presented in []. The occurrence of some transient oscillations as a result of the Hopf bifurcations was demonstrated by Example 1 in Section 4, see Figure 4 and Figure 5. In this example, the delay was chosen to be at one of the four existing bifurcating values, namely h, which is approximately 418 days. According to Theorem 3, the period of the bifurcating solutions lies in the interval h, which corresponds to an interval of approximately days, with a width of 318 days. Practically, this oscillating behavior is difficult to observe, not only because the periodic solutions are unstable but also due to the rather large bifurcating periods, especially in realtime laboratory experiments.
Finally, in Section 3, we established the existence and uniqueness of positive model solutions in Theorem 4. We reduced the 3-dimensional model (3)–(5) into a limiting 2-dimensional dynamical system (41). Although the reduced model was very similar to well known bioreactor models, the main difference was in the specific properties of the SKIP function and, in particular, of . We proved in Theorem 5 the global asymptotic stability of the coexistence equilibrium point with respect to whenever it exists, i.e., for . However, if , then the washout equilibrium is globally asymptotically stable (Theorem 6). These results mean practically either long-term sustainability of the biodegradation process when is the global attractor or process breakdown due to total washout of the biomass in the reactor when is the global attractor. Numerical examples in Section 4 (Examples 2 and 3) confirmed the latter theoretical results.
The time delayed model (3)–(5), investigated in this paper, shows many similarities in its dynamic properties in comparison with the previously studied [] model (1) without a time delay. These are, for example, the global attractivity of the two equilibrium points and . The main difference is the existence of Hopf bifurcations around the unstable equilibria at certain critical values of , which serve as sources of transient oscillations in practical experiments.
As mentioned before, the model parameters in Table 1 were obtained from laboratory experiments for phenol and p-cresol mixture degradation. New experimental work is planned in the future to eventually account for the time delay in the biomass growth response and the model will be validated by the new data.
The proposed model (3)–(5) could be successfully used on a bioreactor scale-up, and this is also planned in the future. It is very likely to change the values of the model parameters, which will lead to adaptation of the investigations and to new conclusions. However, the following theoretical results are independent of the particular parameter values: (i) existence of a washout steady state and of at least one interior (coexistence) equilibrium ; and (ii) the inversely proportional relationship between the dilution rate D and the time delay . Generally speaking, this means that relatively large values of D and small values of may cause biomass washout, due to the global stability of , and thus to process breakdown in the bioreactor. On the contrary, smaller values of D and larger values of lead to a stable process and biodegradation sustainability due to the global attractivity of . Since D is the controllable input in the bioreactor, these results can be very useful for the experimenter in order to obtain answers long before the physical prototype of the actual system is built and tested.
A next step in future investigations will be to treat more complex chemical compounds involving more than two substrates. The challenging element will be the design of the biomass specific growth rate as a SKIP-type model. This could be performed in dependence on experimental results showing the activity and the mutual interaction of the involved substances.
Author Contributions
Conceptualization, N.D. and P.Z.; methodology, N.D. and P.Z.; software, M.B.; theoretical investigation, N.D.; validation, M.B., N.D. and P.Z.; data curation, P.Z.; writing—original draft preparation, M.B., N.D.; writing—review and editing, M.B., N.D. and P.Z. All authors have read and agreed to the published version of the manuscript.
Funding
This research received no external funding.
Acknowledgments
This work was partially supported by the National Scientific Program “Information and Communication Technologies for a Single Digital Market in Science, Education and Security (ICTinSES)”, contract No DO1–205/23.11.2018, financed by the Ministry of Education and Science in Bulgaria. The work of the second author was partially supported by grant No BG05M2OP001-1.001-0003, financed by the Science and Education for Smart Growth Operational Program (2014–2020) in Bulgaria and co-financed by the European Union through the European Structural and Investment Funds.
Conflicts of Interest
The authors declare no conflict of interest.
Appendix A
Proof of Theorem 1.
Let be a solution of Equation (26). Then
Therefore, holds true for or for some integer . Since is defined for and , it follows that is valid (cf. Figure 3).
Let and , , intersect at . Then , which means that satisfies the second equation in (26).
If , then , i.e., , , hence , which means that . We have in this case
Thus, satisfies the first equation in (26) too, and this means that is a positive solution of (26).
If , then
In the first case and the proof is the same as above. In the second case we have and thus,
If conditions (34) do not hold, then is not a solution because the sign in the first equation of (26) is violated. This proves .
Assume that and intersect at , with or for some integer . Since then holds true. Without loss of generality let us assume that . Then exists according to (30) and (31). Using the equality it follows from the first equation of (A1) and the monotonicity of that
Therefore,
If the roots of the nominator, i.e., the solutions of (35) at are isolated, then there exists at most finite number of points at which the graphs of and are tangent. This means that and , , intersect at a finite number of points, and then follows from . The proof is completed. □
Proof of Theorem 2.
Since is a real root of Equation (23), by differentiating the latter with respect to we obtain consecutively
We have from (23) that , and therefore
Using the presentations and as well as the identity , we obtain , so that
Further,
Denoting for simplicity
Proof of Corollary 1.
The first part follows directly from Theorem 1.
If , then and by Theorem 1 it follows that . However, since otherwise which leads to , and by (27) it follows that . Therefore, and are fulfilled, thus
Proof of Theorem 3.
follows directly from Theorem 1.
The existence of Hopf bifurcations of follows from Theorem 2, Corollary 1 and the local Hopf bifurcation theorem for delay differential equations (cf. []). Since the equilibrium is locally asymptotically unstable for (see Proposition 2), any branching periodic solution of is unstable. Let , , be a pure imaginary root of (23) at . Then it follows from (25) and (33) that . If n is odd, i.e., for some integer , then it follows from the proof of Theorem 1 that , and . So we obtain
The above inequalities imply that (38) is fulfilled.
The case when n is even can be shown in a similar way. The proof is completed. □
References
- Lama, G.F.C.; Rillo Migliorini Giovannini, M.; Errico, A.; Mirzaei, S.; Padulano, R.; Chirico, G.B.; Preti, F. Hydraulic Efficiency of Green-Blue Flood Control Scenarios for Vegetated Rivers: 1D and 2D Unsteady Simulations. Water 2021, 13, 2620. [Google Scholar] [CrossRef]
- European Union, Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy. Off. J. Eur. Communities 2000, L327, 1–73.
- Pastor-Poquet, V.; Papirio, S.; Steyer, J.P.; Trably, E.; Escudie, R.; Esposito, G. High-solids anaerobic digestion model for homogenized reactors. Water Res. 2018, 142, 501–511. [Google Scholar] [CrossRef]
- Narayanan, C.M.; Narayan, V. Biological wastewater treatment andbioreactor design: A review. Sustain. Environ. Res. 2019, 29, 33. [Google Scholar] [CrossRef]
- Singh, P.; Jain, R.; Srivastava, N.; Borthakur, A.; Pal, D.B.; Singh, R.; Madhav, S.; Srivastava, P.; Tiwary, D.; Mishra, P.K. Current and emerging trends in bioremediation of petrochemical waste: A review. Crit. Rev. Environ. Sci. Technol. 2017, 47, 155–201. [Google Scholar] [CrossRef]
- Wen, Y.; Li, C.; Song, X.; Yang, Y. Biodegradation of phenol by Rhodococcus sp. strain SKC: Characterization and kinetics study. Molecules 2020, 25, 3665. [Google Scholar] [CrossRef] [PubMed]
- Arutchelvan, V.; Atun, R.C. Degradation of phenol, an innovative biological approach. Adv. Biotech. Micro 2019, 12, 555835. [Google Scholar] [CrossRef]
- Zhao, L.; Wu, Q.; Ma, A. Biodegradation of phenolic contaminants: Current status and perspectives. IOP Conf. Ser. Earth Environ. Sci. 2018, 111, 012024. [Google Scholar] [CrossRef]
- Sharma, N.K.; Philip, L.; Bhallamudi, S.M. Aerobic degradation of phenolics and aromatic hydrocarbons in presence of cyanide. Bioresour. Technol. 2012, 121, 263–273. [Google Scholar] [CrossRef]
- Tomei, M.C.; Annesini, M.C. Biodegradation of phenolic mixtures in a sequencing batch reactor: A kinetic study. Env. Sci. Pollut. Res. 2008, 15, 188–195. [Google Scholar] [CrossRef]
- Yemendzhiev, H.; Zlateva, P.; Alexieva, Z. Comparison of the biodegradation capacity of two fungal strains toward a mixture of phenol and cresol by mathematical modeling. Biotechnol. Biotechnol. Equip. 2012, 26, 3278–3281. [Google Scholar] [CrossRef][Green Version]
- Kietkwanboot, A.; Chaiprapat, S.; Müller, R.; Suttinun, O. Biodegradation of phenolic compounds present in palm oil mill effluent as single and mixed substrates by Trameteshirsuta AK04. J. Environ. Sci. Health Part A Toxic 2020, 55, 989–1002. [Google Scholar] [CrossRef] [PubMed]
- Datta, A.; Philip, L.; Bhallamudi, S.M. Modeling the biodegradation kinetics of aromatic and aliphatic volatile pollutant mixture in liquid phase. Chem. Eng. J. 2014, 241, 288–300. [Google Scholar] [CrossRef]
- Muloiwa, M.; Nyende-Byakika, S.; Dinka, M. Comparison of unstructured kinetic bacterial growth models. S. Afr. J. Chem. Eng. 2020, 33, 141–150. [Google Scholar] [CrossRef]
- Liu, J.; Jia, X.; Wen, J.; Zhou, Z. Substrate interactions and kinetics study of phenolic compounds biodegradation by Pseudomonas sp. cbp1-3. Biochem. Eng. J. 2012, 67, 156–166. [Google Scholar] [CrossRef]
- Kumar, S.; Arya, D.; Malhotra, A.; Kumar, S.; Kumar, B. Biodegradation of dual phenolic substrates in simulated wastewater by Gliomastixindicus MTCC 3869. J. Environ. Chem. Eng. 2013, 1, 865–874. [Google Scholar] [CrossRef]
- Angelucci, D.M.; Annesini, M.C.; Tomei, M.C. Modelling of biodegradation kinetics for binary mixtures of substituted phenols in sequential bioreactors. Chem. Eng. Trans. 2013, 32, 1081–1086. [Google Scholar] [CrossRef]
- Lepik, R.; Tenno, T. Biodegradability of phenol, resorcinol and 5-methylresorcinol as single and mixed substrates by active sludge. Oil Shale 2011, 28, 425–446. [Google Scholar] [CrossRef]
- Reardon, K.F.; Mosteller, D.C.; Rogers, J.D.B. Biodegradation kinetics of benzene, toluene, and phenol as single and mixed substrates for Pseudomonas putida F1. Biotechnol. Bioeng. 2000, 69, 385–400. [Google Scholar] [CrossRef]
- Reardon, K.F.; Mosteller, D.C.; Rogers, J.B.; DuTeau, N.M.; Kim, K.-H. Biodegradation Kinetics of Aromatic Hydrocarbon Mixtures by Pure and Mixed Bacterial Cultures. Environ. Health Perspect. 2002, 110, 1005–1011. [Google Scholar] [CrossRef]
- Chen, D.-Z.; Ding, Y.-F.; Zhou, Y.-Y.; Ye, J.-X.; Chen, J.-M. Biodegradation kinetics of tetrahydrofuran, benzene, toluene, and ethylbenzene as multi-substrate by Pseudomonas oleovorans DT4. Int. J. Environ. Res. Public Health 2015, 12, 371–384. [Google Scholar] [CrossRef]
- Hazrati, H.; Shayegan, J.; Seyedi, S.M. Biodegradation kinetics and interactions of styrene and ethylbenzene as single and dual substrates for a mixed bacterial culture. J. Environ. Health Sci. Eng. 2015, 13, 72. [Google Scholar] [CrossRef]
- Abuhamed, T.; Bayraktar, E.; Mehmetoǧlu, T.; Mehmetoǧlu, Ü. Kinetics model for growth of Pseudomonas putida F1 during benzene, toluene and phenol biodegradation. Process Biochem. 2004, 39, 983–988. [Google Scholar] [CrossRef]
- Yemendzhiev, H.; Gerginova, M.; Zlateva, P.; Stoilova, I.; Krastanov, A.; Alexieva, Z. Phenol and cresol mixture degradation by Aspergillus awamori strain: Biochemical and kinetic substrate interactions. In Proceedings of the 17th Internat. Central European Conf. ECOpole’08, Wilhelms Hill at Uroczysko, Piechovice, Poland, 23–25 October 2008; Volume 2, pp. 153–159. [Google Scholar]
- Dimitrova, N.; Zlateva, P. Global stability analysis of a bioreactor model for phenol and cresol mixture degradation. Processes 2021, 9, 124. [Google Scholar] [CrossRef]
- Wolkowicz, G.S.K.; Xia, H. Global asymptotic behavior of a chemostat model with discrete delays. SIAM J. Appl. Math. 1997, 57, 1019–1043. [Google Scholar] [CrossRef]
- Wang, L.; Wolkowicz, G.S.K. A delayed chemostat model with general nonmonotone response functions and differential removal rates. J. Math. Anal. Appl. 2006, 321, 452–468. [Google Scholar] [CrossRef]
- Droop, M.R. Vitamin B12 and marine ecology. IV. The kinetics of uptake, growth and inhibition in monochrysislutheri. J. Mar. Biol. Assoc. UK 1968, 48, 689–733. [Google Scholar] [CrossRef]
- Finn, R.K.; Wilson, R.E. Fermentation process control, population dynamics of a continuous propagator for microorganisms. J. Agric. Food Chem. 1954, 2, 66–69. [Google Scholar] [CrossRef]
- Bush, A.W.; Cool, A.E. The effect of time delay and growth rate inhibition in the bacterial treatment of wastewater. J. Theoret. Biol. 1976, 63, 385–395. [Google Scholar] [CrossRef]
- Caperon, J. Time lag in population growth response of isochrysis galbana to a variable nitrate environment. Ecology 1969, 50, 188–192. [Google Scholar] [CrossRef]
- Freedman, H.I.; So, J. W-H; Waltman, P. Coexistence in a model of competition in the chemostat incorporating discrete delays. SIAM J. Appl. Math. 1989, 49, 859–870. [Google Scholar] [CrossRef]
- Ellermeyer, S.F. Competition in the chemostat: Global asymptotic behavior of a model with dealayed response in growth. SIAM J. Appl. Math. 1994, 54, 279–465. [Google Scholar] [CrossRef]
- Xia, H.; Wolkowicz, G.S.K.; Wang, L. Transient oscillations induced by delayed growth response in the chemostat. J. Math. Biol. 2005, 50, 489–530. [Google Scholar] [CrossRef]
- Liu, S.; Wang, X.; Wang, L.; Song, A. Competitive exclusion in delayed chemostat models with differential removal rates. SIAM J. Appl. Math. 2014, 74, 634–648. [Google Scholar] [CrossRef]
- Hale, J.K.; Lunel, S.M.V. Introduction to Functional Differential Equations; Applied Mathematical Sciences; Springer: New York, NY, USA, 1993; Volume 99. [Google Scholar] [CrossRef]
- Kuang, Y. Delay Differential Equations: With Applications in Population Dynamics; Academic Press: Boston, MA, USA, 1993. [Google Scholar]
- Akian, M.; Bismuth, S. Instability of rapidly-oscillating periodic solutions for discontinuous differential delay equation. Differ. Integral Eq. 2002, 15, 53–90. [Google Scholar]
- Smith, H. An Introduction to Delay Differential Equations with Applications to the Life Sciences; Texts in Applied Mathematics; Springer: New York, NY, USA, 2011. [Google Scholar]
- Gopalsamy, K. Stability and Oscillations in Delay Differential Equations of Population Dynamics; Kluwer Academic Publishers: Dordrecht, The Netherlands, 1992. [Google Scholar]
- Hirsch, W.M.; Hanisch, H.; Gabriel, J.-P. Differential equation models of some parasitic infections: Methods for the study of the asymptotic behavior. Comm. Pure Appl. Math. 1985, 38, 733–753. [Google Scholar] [CrossRef]
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations. |
© 2021 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).