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1. Introduction
Morocco is one of the largest fish producers in the world, according to the 2018 report from the Food and Agriculture Organization of the United Nations (FAO). In 2018, national fishery production totaled 1371683 tons for a turnover of 11579544 thousand MAD (Moroccan Dirhams). The export volume reached more than 722921 tons for a turnover of 22,531 million MAD (DPM, 2018) [1]. A study published in December 2019 reveals that the main reason for the repression of Moroccan fish is the presence of parasites. The study was carried out by the Hassan II Agronomic and Veterinary Institute (HAVI) and the center specializing in the pathology of aquatic animals at the National Fisheries Research Institute (NFRI). The parasites are the source of major problems with natural fish stocks. Indeed, the parasites determine pathologies slowing the growth and increasing the mortality of their hosts and constitute, consequently, a limiting factor of the success of the productivity in aquaculture. Following the analysis concerning 1678 pieces of fish of different species, 537 of which come from the Atlantic (port of Essaouira and wholesale market of Casablanca) and 1141 pieces from the Mediterranean, the extent of parasitism is almost the same on the Mediterranean coast (31.1%) and the Atlantic (32%). Nematodes (anisakis + acanthocephalans) occupy most of the parasites in the Atlantic and the Mediterranean, with respective prevalence of 21.4% and 24.9%. The plerocercoid larva of the cestode was found in silver saber, with a prevalence of 8.3% at the Atlantic level, as is shown in Figure 1. It should be noted that to be contaminated, the fish must feed on plants or animals carrying parasites. In fact, several animal species can carry parasites and contaminate the fish’s environment through their excrement, which sometimes contains parasite eggs. To develop, these eggs will infect plankton, small crustaceans, snails, etc. If fish eat these organisms, they in turn can carry parasites. These reasons encouraged us to study this phenomenon and to see all the interactions that occur between populations of fish. In this context, many mathematical models have been developed to describe the dynamics of fisheries, and we can refer, for example, [2–7]. Moreover, we can cite [8], in this work, the authors have defined a bioeconomic equilibrium model for Parapeaneus longirostris and small pelagic fish populations in two different areas; the first one is protected against fishing and the second is a free access zone.
[figure omitted; refer to PDF]
They studied the influence of the predator mortality rate variation on the evolution of prey biomass and the profit of coastal trawlers. In [9], the authors have sought to highlight that the increase of the carrying capacity of marine species does not always lead to an increase on the catch levels and on the incomes. They considered a bioeconomic model of Sardina pilchardus, Engraulis encrasicolus, and Xiphias gladius marine species that are exploited by several seiners in the Moroccan Atlantic zone based on the parameters given by NFRI. In [10], the authors studied a model consisting of susceptible and infected prey populations and a predator population. More precisely, they assume that the likelihood of a predator catching a susceptible prey or an infected prey is proportional to the numbers of these two different types of prey species. They assume that the predator will eventually die as a result of eating infected prey. In previous works, in particular, in the works [11–23], the authors did not take into account parasitic helminths which have a negative impact on the evolution and behavior of populations. Therefore, the purpose of this paper is to identify parasitic Helminths in Scomber colias and Thunnus thynnus of great economic importance, which occupy a prominent place in the trophodynamic chain. We search to study a bioeconomic model in which both susceptible and infected prey populations (Scomber colias) are exposed to the predator (Thunnus thynnus), with varying degrees of exposure. However, the predator feeds preferentially on the most numerous prey types. This implies a kind of switching from the susceptible class to the infected class, and vice versa, as these two types of prey change in numerical superiority. Switching may simply come about due to individual behavior changing with varying abundance of that class of prey. The paper is organized as follows. In the next section, we present the biological model of susceptible and infected Scomber colias with the presence of the predators Thunnus thynnus; in other words, we resolve a system of three ordinary differential equations, the first equation describes the natural growth of the susceptible Scomber colias fish population a prey of the Thunnus thynnus fish population, the second equation describes the natural growth of infected Scomber colias fish population a prey of the Thunnus thynnus fish population, and the third equation describes the natural growth of the Thunnus thynnus fish population as a predator of the susceptible and infected Scomber colias. The basic reproduction number, positivity, and boundedness are studied in the first part. The existence of the steady states of this system and their stability are studied using eigenvalue analysis, and we define a bioeconomic equilibrium model for these fish populations exploited by a fishing fleet. In Section 3, we compute some numerical simulations to determine the optimal conditions under which the biological steady state can be attained. In Section 4, we give a numerical simulation of the mathematical model and discussion of the results. Finally, we give a conclusion and some potential perspectives in Section 5.
2. Biological Model
Our study is based on an epidemiological model which describes the interaction between the susceptible and infected fish population Scomber colias and their predators Thunnus thynnus. We assume that the disease is transmitted by direct contact with the prey. Due to the presence of the disease, the prey population is divided into two disjoint classes, the susceptible fish population denoted by
[figure omitted; refer to PDF]
Let
Let
The Thunnus thynnus
Following the previous assumptions, the biological model is formulated as follows
We assume that all parameters are positive,
At
3. Biological Model Analysis
3.1. Basic Reproduction Number
We assume that we have the following SI model
By dividing the second equation by
3.2. Positivity
We will denote by
Then, the system (4) becomes
Let
Therefore, all solutions starting from an interior of the first octant remain in it for all future time.
3.3. Boundedness
We define the function
We choose
Consequently,
Which gives, for
Hence, that
3.4. Equilibrium Points
For the system (4), we can see that the equilibrium points satisfy the following equations
After calculation, it is obvious that system (15) has five equilibrium points as follows
For the last equilibrium point
Since
Consider the function
If
Equation (18) admits at least one solution
To determine the uniqueness of the solution
(i) If
(ii) If
(iii) If
To depress the cubic equation, we substitute
Then, we obtain
By using Cardano’s formula, we obtain
3.5. Local Stability of Equilibrium Points
To ensure the positivity of the population’s biomass, we assure that
We consider the matrix
(1) At the equilibrium point
It has three eigenvalues:
(2) At
It has these eigenvalues:
Hence, the point
(3) In the same manner, at
It has these eigenvalues:
Then, following the conditions
(4) The variational matrix at
Since one of the eigenvalues
(5) The local stability of
(i) If
In this case, the characteristic polynomial
By considering the previous characteristic polynomial, if one of the coefficients is zero or negative while at least one other coefficient is positive, then there is one or more imaginary roots or roots with a positive real part. If all the coefficients are positive, we calculate the Routh table. The Routh Hurwitz tabular is given by
(ii) If
In this case, the characteristic polynomial is as follows:
The Routh Hurwitz tabular is given by
(iii) If
In this case, the characteristic polynomial is as follows:
The Routh Hurwitz tabular is given by
[figure omitted; refer to PDF]
Following Figure 6, in a finite time the susceptible Scomber colias, infected Scomber colias and Thunnus thynnus converge to the equilibrium point
4. Bioeconomic Model
The basic idea of this section is to define a bioeconomic model of the susceptible Scomber colias, the infected Scomber colias, and the Thunnus thynnus population exploited by three fishing fleets, and we seek to maximize the profit of each fishing fleets. The mathematical formula of catches is given by
The biomass at biological equilibrium is the solution of the following system
The profit
5. Optimal Control
The fundamental problem from the economic point of view of the exploitation of renewable resources is to determine the optimal trade-off between present and future catches. The aim of this section is the profit-making aspect of Scomber colias and Thunnus thynnus. It is a thorough study of the optimal catches policy and the profit earned by catches, focusing on quadratic costs and conservation of this fish population by constraining the latter to always stay above a critical threshold. The reason for using quadratic costs is that it allows us to derive an analytical expression for the optimal catches; the resulting solution is different from the solution obtained case of linear cost function (the bang-bang solution). It is assumed that price is a function, which decreases with increasing biomass. Thus, to maximize the total discounted profit from the fishery, we use the control
Subject to the system (4), where
Theorem 1 (Sufficient conditions).
The optimal control problem given by (58), along with the state equations of system (57), admits a control
Proof.
See the theorems in Lashari et al. [26], Lashari and Zaman [27], and Lenhart and Workman [28].
Theorem 2 (Necessary conditions).
Given optimal controls
According to Lashari et al. [26], if
Proof.
Consider the system of differential equations in (65) governing the adjoint variables
With the transversality conditions
To evaluate the optimal control of the control variable set, where
By applying the optimal control to the control variable set,
This shows that the uniqueness of the optimal control of the model has been achieved for small
6. Numerical Simulation
To study the optimal control problem numerically, we use the forward-backward Rung-Kutta sweep method. We wrote a code in MATLAB based on this method. The results are given in the following graphs. Note that all the parameters are taken as follows:
Following Figures 7–9, we can show that when the constant effort harvesting
[figure omitted; refer to PDF]
Now, for
7. Conclusion
In the literature, we found that the authors consider either epidemic models or bioeconomic models but without treating the disease of fish populations. In this work, we have developed and studied a new model concept that combines the bioeconomic model, and the epidemiological model (bioeconomic-epidemiological model) of prey-predator marine populations is developed in which both susceptible and infected prey populations (Scomber colias) are exposed to the predator (Thunnus thynnus), with varying degrees of exposure. We resolved the bioeconomic model at a steady state, and we were able to calculate the profits of each fishing fleet. The optimal harvesting policy is discussed using the Maximum Principle of Pontryagin to give a high yield and keep both population Scomber colias and Thunnus thynnus away from extension.
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Abstract
In this paper, we develop and study a mathematical model for the dynamics of Scomber colias and Thunnus thynnus prey-predator with parasitic helminths. We search to analyze a bioeconomic model in which both susceptible and infected prey populations Scomber colias are exposed to the predator Thunnus thynnus, with varying degrees of exposure. However, the predator feeds preferentially on the most numerous prey types. This implies a kind of switching from the susceptible class to the infected class, and vice versa, as these two types of prey change in numerical superiority. So, the positivity, boundedness, equilibria, stability, and bioeconomic equilibrium are studied. Some numerical simulation of stability is cited. For giving a high yield and keeping the Scomber colias and Thunnus thynnus populations away from extension, we use the Maximum Principle of Pontryagin.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer