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1. Introduction
Beverton–Holt equation is an useful discrete equation for modelling the evolution of species which reproduce by eggs such as birds, fishes and insects [1]. It can be considered the counterpart of the logistic equation in the Verhulst´s continuous-time model. The basic Beverton–Holt model is parameterized by two positive sequences, namely, the carrying capacity of the environment which depends on resources availability, temperature, humidity, etc., and the intrinsic growth rate which is associated with the species reproduction capability, the survivorship chance etc. The intrinsic growth rate has typically to exceed unity to avoid extinction. In the most general case, those parameters can be changed to sequences to describe potential different behaviors of the population evolution in different periods, for instance, seasonality. There are other two typical parameters to be eventually considered which generalize the model such as the independent consumption which describes recruitment variations due to unforeseen disturbances and eventual repopulation or interchange of population with neighbour environments and the harvesting process associated with fishing or hunting and which depends on regulation based on the available spawning stock and foreseen recruitment. The basic time-invariant Beverton–Holt equation has two equilibrium points which are the extinction point, which is locally unstable, and the carrying capacity level which is globally asymptotically stable. The so-called Cushing–Henson conjecture established that, if the equation is modelled by periodic parameterizing sequences of carrying capacities and intrinsic growth rates, then the averaged periodic sequence of population lies below the average of the corresponding average of the carrying capacities. The conjecture has been rigorously proved to be true by Stevic [2]. Some extensions of the basic model concerning the Cushing–Henson conjectures for the Beverton–Holt q-difference equation have been discussed in [3]. A control theory point of view on the Beverton–Holt equation has been adopted and discussed in [4–6] while giving a design procedure of the environment carrying capacity for monitoring the suitable sequence of values to follow of the population evolution. The applicability of the proposed method is claimed for semiopen environments such like certain fisheries. It is discussed in [7] how, in practice, the intrinsic growth rate can be dependent on the environment carrying capacity. Also, it is discussed in [8] an impulsive extended competition Beverton–Holt model between species from the stability point of view. The usefulness of the Beverton–Holt and other mathematical models in maritime biology is described in [9]. In [10–13], the harvesting action is investigated in an extended Beverton–Holt model. Normally, harvesting refers to fishing or hunting which is subjected to authorities regulation but it can also be total or partially illegal while associated to furtive uncontrolled actions. See also some references therein and [6, 8]. Other related studies consider alternative generalizations concerned with periodic behaviors, associated, for instance, to seasonality [14, 15], global dynamics analysis of some extended equation versions [16], presence of bifurcations [17, 18] or resonances [19], and perturbations of the basic model. See, for instance [18]. On the other hand, an extended Beverton model on isolated time scales is analyzed in detail in [20]. Also, an extension of the Beverton–Holt model including discrete delays in the evolution dynamics has been investigated in [21]. A Beverton–Holt model extension including discrete delays in the evolution dynamics has been investigated in [21]. On the other hand, it can be pointed out that Beverton–Holt-based models are used also by biologists when monitoring fishing stock availability and fishing migrations to evaluate the recommended maximum number of captures (or recommended harvesting action) to avoid the environment degradation and species extinction. See, for instance [22, 23], and some of the references therein.
In this paper, we focus on a generalized Beverton–Holt equation which assumes a quadratic-type penalty for the population excess describing the potential internal competence between the individuals for food, refuge, etc. The harvesting action is considered jointly with eventually present independent consumption if necessary. It is seen that the presence of such a term can translate into the presence of two other equilibrium points. The paper also designs species evolution control laws by monitoring the harvesting action and the influence in the results of considering a modelling function of Allee’s effect which makes difficult growing or even can cause extinction for small numbers of reproductive individuals.
The paper is organized as follows. Section 2 deals with the equilibrium points in the presence and absence of harvesting action, considered together with eventual independent consumption, in the case when the intrinsic growth rate elements exceed unity. The harvesting sequence can have positive, negative or null elements. The local asymptotic stability of each feasible (that is being real and non-negative) equilibrium points is characterized in the case when the parameterizing sequences converge to limits. Section 3 develops two methods to derive control laws for the harvesting actions again if the intrinsic growth rate exceeds unity for all time. The first proposed method is based on the convergence of the solution sequence of the population to a prescribed targeted equilibrium point of the population value by choosing the harvesting sequence. Classical criteria for convergence of sequences, such as D’Alembert, Cauchy, and Raabe criteria, are involved in the respective monitoring rules of the harvesting action. The second method relies on a sample-to-sample monitoring of the solution sequence to target a prescribed evolution pattern by designing the harvesting sequence. Next, Section 4 relies on introducing Allee’s effect to modify the basic Beverton–Holt equation to describe the situation arising under small numbers of individuals which make difficult the reproductive action and can lead to extinction even the intrinsic growth rate exceeds unity for all time. The equilibrium points, their stability conditions as well as extinction conditions are investigated if the intrinsic growth rate exceeds unity for all time. The second part of this section proposes a penalty term in the Beverton–Holt equation for high levels of population in the absence of harvesting. The resulting equilibrium points and their stability issues are also investigated if the intrinsic growth rate exceeds unity for all time. On the other hand, Section 5 relies on extinction conditions and the local asymptotic stability of the extinction equilibrium point if the intrinsic growth sequence has elements being less than unity in the absence of harvesting by considering the modified model with quadratic penalty time for high levels of population. The local asymptotic stability of the positive equilibrium points is also investigated. Section 6 is devoted to discuss some numerical examples and, finally, some conclusions end the paper. In the following, the subsequent notation is used:
and denote, respectively, the sets of non-negative and nonpositive integer numbers
and denote, respectively, the sets of positive and negative integer numbers
and denote, respectively, the sets of non-negative and nonpositive real numbers
and denote, respectively, the sets of positive and negative real numbers
2. Equilibrium Points and Their Local Asymptotic Stability under Positive, Null, or Negative Harvesting
“Harvesting” is referred to fishing and hunting subject to administrative regulation which depends on the species population. On the other hand, “independent consumption” refers to positive of negative supplies of extra populations due to migrations from outside of the environment under consideration [10, 13, 14]. In the sequel, we consider both effects together integrated in the same additive perturbation sequence to that of the standard population evolution sequence. Consider the following, in general, time-varying Beverton–Holt equation subject to harvesting action eventually combined with independent consumption:with initial condition , where is the intrinsic growth rate of the species and is the environment carrying capacity sequence, both being positive real sequences. If a constraint ; is prefixed for some sequence so that the harvesting sequence has to fulfil:
The harvesting sequence defines the population amount which is not related to the dynamics evolution within the environment because of natural reproduction and dead concerns. It is related to an increase or decrease of individuals due to population flux either from or to the habitat plus eventual decrease of population due to hunting or fishing. In this way, the sequence can take negative values at a particular sampling instant because of the sign in (1), this situation will correspond to an increase of the amounts of individuals), positive values (that is, decrease of population), or zero (that is, the population is just modified by the natural reproduction and dead within the considered habitat). According to that philosophy, the harvesting is considered in this paper as the eventual combination of an eventual traditional harvesting (that is, hunting/fishing) and eventual migrations in both senses from or to the habitat under study. Also, the hunting or fishing includes, in general, legal or illegal actions (poaching).
It turns out that any equilibrium point needs to be real non-negative in order to be feasible (that is, real and positive) as it is addressed in the subsequent result.
Theorem 1.
Assume that , , and with ; . Then, the solution of (1) has:
(i) A real positive equilibrium point and a null equilibrium point (extinction) at if .
(ii) If then there is no nonextinction feasible equilibrium point and the nonextinction equilibrium points are feasible if .
(iii) If then the potential nonextinction equilibrium points and are given by
which are real if and only if . The equilibrium point is feasible if and only if which restricts the above-given inequality for realness. Also, the equilibrium point is feasible if and only if . If then . In terms of the intrinsic growth rate, the nonextinction equilibrium points and are both feasible if and , equivalently, if ( if ). Also, is not feasible for and is feasible for irrespective of and .
Proof.
Note directly that the extinction level is an equilibrium point. Also, by replacing in (1) the limits of the various sequences, one gets a single root if and, if , then
Thus, since , if then there is no real non-negative solution to (1) since (4) fails for and .
If , or if , then the roots of (2) are
Properties [(i)-(ii)] have been proved. On the other hand, the nonextinction equilibrium points and are both feasible for if , equivalently, if ( if ). Also, is not feasible for from (5) and is feasible, also from (5), for irrespective of and .
Note that, in order for the roots of (4) to be real, since , it is needed that , where
Note that, are real if and only if the zeros of , that is, , are non-negative real since . Since is a convex parabola, , and both equilibrium points and are real (and they can be positive) if and only if . Contrarily, if then the zeros are not real and the nonextinction equilibrium points never exist. Since, their feasibility implies that then the equilibrium point is feasible if and only if . Since for . Also, the equilibrium point is feasible if and only if . It is obvious that then . Property (iii) is proved.
The use of the inverse sequence of that of a the population evolution sequence is of interest to derive easily some interesting results concerning the stability and the asymptotic boundedness of the solution as it is addressed in the subsequent result:
Theorem 2.
Define the inverse sequence of the solution of (1) as ; . The following properties hold:
(i) The inverse sequence of the solution is given by the discrete equation:
where ; , subject to ; , and is zero if for any , with
for . The solution is equivalently expressed from given initial conditions as follows:
(ii) is bounded, equivalently, does not vanish neither at any sample nor asymptotically (and then the population does not extinguish either in finite time or asymptotically) if . In particular, if and then
is bounded for any given finite for all if . For any finite , so that , the sequence satisfies:
(iii) Define by assuming that subject to . Assume that for any integer , some and some . Then, . The constraint is satisfied under any of the subsequent stipulations for each :
(1) requiring that the harvesting sequence and the carrying capacity
(2) and requiring that and
(3) and requiring that
(iv) The extinction equilibrium point is unstable. The two positive equilibrium points in (5) arising when the parametrical sequences , , fulfil the following theories:
(a) is jointly feasible and locally asymptotically stable if
(b) If is feasible then it is not locally asymptotically stable
(c) If then the unique nonextinction equilibrium point is jointly feasible and locally asymptotically stable
Proof.
One obtains (7) directly from the following equivalent expression to (1):subject to ; for keeping the sample-to-sample non-negativity of , where ; , andwith ; . One gets from (13) thatwhich leads toso thatwhich leads directly to (8). Equation (9) follows directly from recursive calculations with (7). Property (i) has been proved. Property (ii) is a direct consequence of Property (i) since ; and since .
To prove Property (iii), we rewrite an upper-bounding expression of (7) assince implies that ; subject to . Since it is also assumed that ; , this constraint is achieved if ; , and some , where for any integer , some and some then it follows from [Lemma 1.2 (i), [24]] that . The stipulation 1 is got from the constraints (implying that ) and then , .
The stipulation 2 follows for (implying that ) and so that the subsequent constraint holds ; .
The stipulation 3 follows for and so that the following constraint holds ; .
Property (iii) has been proved. Property (iv) follows from a local perturbation analysis. It is assumed that the invariant equation (1) perturbed from any equilibrium point as ; . The linearized perturbation transmitted to the next sample is ; which leads to ; and, for sufficiently small , , , so that is locally asymptotically stable, if and only if . Equivalently, if and only if . Contrarily, the equilibrium point is not locally asymptotically stable (that is, either critically stable or unstable) if and only if , that is, if and only if . In particular, it is unstable if , that is, if . The local asymptotic stability constraint fails and the instability constraint holds if (extinction equilibrium point) since .
Then, the extinction equilibrium point is unstable.
For addressing the local asymptotic stability of the other two equilibrium points and , provided they are feasible and distinct (that is, the radicand of (5) is real positive), note that equilibrium points are locally asymptotically stable if and only if
Considering under the above constraint, that one becomes equivalent to
The above-given constraint (19) holds if , wherewhereandwhere
Thus, , as necessary condition , equivalently, in order for the radicand in the definition of to be non-negative (equilibrium feasibility condition), with if and . For , is locally asymptotically stable from since holds trivially. Now (20)–(23), one gets that is locally asymptotically stable, that is, , if and only if:which coincides with the feasibility condition. Thus, is both feasible and locally asymptotically stable if and only if .
For the local asymptotic stability of , equation (19) becomes modified as follows:so that, one gets the two associated constraints:
(1)
(2)
The above-given first condition is equivalent to since . This constraint is the feasibility constraint for harvesting also already needed for . The above-given second condition is equivalent to just to reverse the equality in the constraint (24), that is,so that is both feasible and locally asymptotically stable if and only ifwhich is a contradiction. Thus, is unstable if feasible and distinct of .
If is feasible, that is, the radicand of (5) is null so that , then the equilibrium point is given by which satisfies trivially the above given local asymptotic stability condition so that the confluent nonextinction equilibrium point resulting with is locally asymptotically stable. Property (iv) has been proved.
Concerning Theorem 2(i), note that the denominator in the right-hand-side of (8) cannot be zero at any sample since the the value of the sequence is bounded by hypothesis.
Remark 1.
Note that, the admissible harvesting sequence of Theorem 2(iii) can be generated from (8) by generating as follows by fulfilling one of the stipulations 1–3 for each :
(a) Through the stipulation 1 in the proof of Theorem 2: ; , where is chosen such that ; and the sequence is generated subject to ; . Note that, and ; .
(b) Through the stipulation 2 in the proof of Theorem 2: , where ; and is chosen such that . Note that, and .
(c) Through the stipulation 3 in the proof of Theorem 2: , where ; and . Note that, and .
Remark 2.
The local asymptotic stability of the equilibrium points addressed in Theorem 2 (iv) relies to the cases of absence of harvesting in the steady state dynamics () or in the cases of stationary fishing/hunting or stationary repopulation actions . Those cases correspond to constant values of the harvesting sequence in finite time or asymptotically. In the paper, the dynamics is globally stable if the population solution sequence is bounded for any given finite initial condition. This circumstance might be compatible with the event that some of the equilibrium points be locally unstable, stable, or critically stable if there are more than one equilibrium points. An equilibrium point is said to be globally asymptotically stable if it globally stable and all solution converges asymptotically to such a point for any given finite initial conditions.
In the third case, the largest positive equilibrium point is larger under negative stationary harvesting (having a meaning of stationary repopulation and/or immigration to the habitat from outside), than the equilibrium point arising in the absence of harvesting. In the second case, the global stability condition leads to the conclusion that the larger equilibrium point is locally asymptotically stable and the smaller one is not locally asymptotically stable unless they are coincident for a stationary harvesting effort .
The following result proves that, if the harvesting action sequence has a limit , then a limit point of the solution cannot exceed the amount .
Proposition 1.
If , , and then
Proof.
On gets from (1) that
If , one gets by taking limits in (29) as thatand, equivalently,
Then, the given properties follow directly from (31) and .
The following result establishes the boundedness of the solution sequence under bounded non-negative harvesting.
Proposition 2.
Assume that , , If ; then is bounded.
Proof.
Assume on the contrary that .Then, from L´Hopital rule for quotients with numerator and denominator tending to infinity, since the harvesting sequence is non-negative,so that
A contradiction for the sequence to diverge, which completes the proof.
3. Control Laws for Monitoring the Harvesting Action
The first part of this section is addressed to derive harvesting control laws based on Theorem 2(iv) guaranteeing the convergence to a prescribed equilibrium point under the assumption on the intrinsic growth sequence . Known criteria for absolute convergence of series or for convergence of series of non-negative elements to a prescribed limit can be used to calculate the harvesting control sequence based on the previous calculation of , which reflects the harvesting effect in the inverse of the solution sequence, so as to satisfy Theorem 2(iv). The last part of the section proposes harvesting control laws which make the solution sequence of the population evolution to sample-to-sample, rather than asymptotically, behave according to a prescribed suitable pattern.
Now, rewrite the population solution sequence as an equilibrium perturbation in the form , where is the suited equilibrium point and ; . Thus, one can rewrite from (6) the one-step ahead evolution of the incremental sequence in the form of Lemma 1.2 (iii) of [24] as follows:where for each ,for any chosen such that ; which guarantees that and ; . Note that, ; . Sufficient conditions for convergence are , and
The condition (40) is equivalent to and the condition (41) is guaranteed ifsince, from (38) and the condition ; , one gets:which induces also the further necessary condition , since as , guaranteed in turn if
(equivalently, if ) and , equivalently, if , or if
3.1. Harvesting Control Law Based on d´ Alembert Convergence Criterion
a) with ; is guaranteed under d´ Alembert convergence criterion in order to , equivalently, , ifif and ; . Then, since ; , equation (44) leads towith . One gets from (12), by using ; , thatso that, equivalently,which equalized to (7) in Theorem 2 (i) leads to:
Then, combining (45) and (48)
Equivalently,for some with ; . If the necessary limit condition for is forced for all values of the sequence, one has in the above equation thatso that for each :
Step 1: for a given scalar and a prefixed equilibrium point such that , so that, equivalently, and given at the -th sampled time , , , , , and , one calculates for some gain according to (51).
Step 2: one calculates and then
Note that, the condition with (and then implying hunting/fishing action) if so that . Conversely, with (and then implying repopulation) if so that .
3.2. Harvesting Control Law Based on Cauchy Root Test
Note that for a given the sequence generated byguarantees that since ; . Furthermore, is equivalent to . It can be taken with . The control law is derived by Step 1 and Step 2 of Section 3.1 under the replacement of (51) by the subsequent equation which implements (51) by respecting the constraint on the sequence:
3.3. Harvesting Control Law Based on Raabe Convergence Criterion
The condition with ; is achieved from Raabe criterion if
; with . Furthermore, the condition is achieved with ; with . Then, the joint conditions and ; with and are achieved for a given harvesting control at the - sample if
Then, Step 1 and Step 2 of Section 3.1 are executed to get the harvesting control at the next -sample.
3.4. Control Law Based on a Reference Model
It is assumed that is a suitable reference implicit model for the population. Note that, from (1) that ; if ; , where the “a priori” population (that is, the harvesting free one) at the -the sample is given by
While the “a posteriori” one is which equalizes the targeted value by the reference model. If then the harvesting action implies a fishing or a hunting action while if then the harvesting consists in repopulation and if then no harvesting is performed. The following result is obvious from the above equations:
Proposition 3.
Assume that . Then, the following properties hold:
(i) Then, and .
(ii) Define by so that and define , with , such that . Then, and .
(iii) If , equivalently, if (since ) then , and .
The above-given result establishes that the population sequence convergence to a limit neither requires the convergence of its parameterizing sequences defining the intrinsic growth rates and the carrying capacities nor implies the convergence to zero of the harvesting control sequence (Proposition 1 (ii)).
4. Model Extensions by considering Allee and Overpopulation Effects
Note that, in (1) for some implies that , that is, extinction in finite time in the absence of positive harvesting implies that the extinction remains afterwards for all time. However, the asymptotic extinction is not possible according to this model if in the presence of negative or null harvesting as it is obvious from the instability of the zero equilibrium point. Note also that cannot be strictly decreasing as addressed as follows:
Proposition 4.
Assume that is nonzero. If then the asymptotic extinction is not possible. If , then the asymptotic extinction is not possible under positive initial conditions.
Proof.
Note that, if for any , then
Thus, if then the asymptotic extinction is not possible. Next, assume that ; . Then, for some implies that . Take a positive real constant . Assume asymptotic extinction so that and assume also that for some .Then, which is a contradiction to . As a result, if then so that is not possible.
4.1. Consider Allee Effect for Small Number of Individuals
The well-known Allee effect establishes that under small population numbers, extinction is possible because of the difficulties for the individuals to meet members of the cohort. Now, we modify (1) with a density-dependent function which penalizes the presence of small numbers of individuals as follows. It is assumed in the sequel that in (1) which is coherent with forbidding harvesting under very small amounts of individuals in the environment: It is still assumed that the intrinsic growth rate exceeds unity for all time.
Theorem 3.
The following properties hold:
(i) If for all such that which is guaranteed under the stronger sufficient condition then is strictly decreasing so that it converges to zero.
(ii) Assume that where , , . If for ; , ; , and
then is strictly decreasing so that it converges to zero. If (59) is replaced with then is not necessarily strictly decreasing while still .
Proof.
Note from (58) that if and only if , and equivalentlywhich is guaranteed for all if such that ; , if . Property (i) has been proved. On the other hand, the condition ; implies thatwhich is guaranteed ifthe second above-given constraint being already guaranteed by the constraint ; , implying also that for the given constraint on in (62) and then is strictly decreasing so that it converges to zero. Note also that if then . Property (ii) has been proved.
Remark 3.
Note that, if with being zero or close to zero, then Theorem 3(iii) follows if and ; . Note also that a coherent under the above-given theorem to describe the Allee effect is with reflecting the difficulties for small numbers to find partners. Exponents might lead to large numbers of individuals, in mathematical terms, to the unbounded growing of the population. A parallel description for in might be appropriate to describe competence within the cohort, for instance for food or refuge seeking, since it penalizes the presence of huge numbers of individuals in the cohort along the evolution process.
The penalty for high levels of populations mentioned in the last remark can also be described by introducing quadratic or higher terms in the denominator of the evolution equation as it is now addressed.
4.2. Incorporation of a Penalty Term for High Number of Individuals
In the following, we introduce a penalty term to deal with the presence of a high number of individuals. It is still assumed that the intrinsic growth rate sequence exceeds unity.
Proposition 5.
Consider the modified Beverton–Holt equation:with . The following properties hold:
(i) Neither asymptotic extinction nor asymptotic population unboundedness are possible for any given finite initial condition .
(ii) Assume that , and . Then, there is a unique positive equilibrium point for , that is, it is smaller than the equilibrium point for and it is a globally asymptotically stable attractor. The extinction equilibrium point is unstable for .
Proof.
Rewrite the Beverton–Holt equation as
Thus, the population inverse is described by the following equation:
Since and ; . Then, if as , as and, from (65), and , and ; , a contradiction to the unboundedness of . Thus, is bounded for any given finite .On the other hand, if , for any arbitrarily small there is some arbitrarily large such that , equivalently, . But then so that cannot be arbitrarily small. Therefore, asymptotic extinction is not possible and for any finite initial condition , one has 0 < . Property (i) has been proved.
To prove Property (ii), note that the limiting equation at an eventual equilibrium point is given bywhich is satisfied by the extinction equilibrium point and by which satisfies the constraint from (66). If then , since , and if then . Now, we prove that is globally asymptotically stable. First, we prove that it is locally asymptotically stable and in a second step that it is globally asymptotically stable. Consider the linearized evolution of the inverse of , where under a perturbation around the equilibrium point leading to . One gets:since ; . From the above-given identity, the one-step ahead evolution of the linearized perturbation of the inverse of the solution is given by the following equation:
Now, we prove that so that . It has been proved before that the equilibrium point satisfies the constraints:
since so that . Furthermore, since which holds since . Since then and ; since and any eventual perturbation of the equilibrium point at any sample becomes reduced in size at the next sample. Therefore, the equilibrium point is locally asymptotically stable.
We now prove that the extinction equilibrium point is unstable. Take a small perturbation , at any sample , being less than , of which needs to be positive since a negative perturbed equilibrium point is unfeasible since it implies a negative population. Then, for and the zero equilibrium point is unstable provided thatwhich holds if . If then, if . Thus, the zero equilibrium point associated with extinction is unstable. Since the nonzero equilibrium point has already proved to be locally asymptotically stable then it is also globally asymptotically stable. The proof is complete.
5. Extinction Issues and Associated Stability Results in the Absence of Haversting
It is now investigated the extinction of the solution sequence ; of the modified Beverton–Holt equation (63) if , and . Basically, it is found that:
(i) If then the only locally stable equilibrium point is (extinction). There is another equilibrium point which is unstable. As a result, the solution sequence is globally stable (that is, bounded for all time and any given finite initial condition) but the population extinguishes asymptotically. On the other hand, remember from the former sections that if , the extinction equilibrium point is unstable while is stable. As a result, the solution sequence is also globally stable and the population never extinguishes asymptotically if Allee´s effect is not considered.
(ii) If , there are, at least two, equilibrium points and . If there are no more equilibrium points than the extinction point and . If then there is another equilibrium point , The extinction equilibrium point is locally asymptotically stable, is unstable and is locally stable or instable depending on the combined values of the parameterization triple . The solution sequence is still globally stable as before.
The equilibrium points satisfy ; so that they satisfy either or . Note that if is an equilibrium point then with and . The subsequent result addresses the existence and local asymptotic stability of the extinction and nonextinction equilibrium points and the global stability of the evolution sequence for small intrinsic growth rates such that .
Theorem 4.
Assume that . Then, the following properties hold:
(i) is an equilibrium points. If and then and are the equilibrium points.
(ii) If then the nonzero feasibly equilibrium points are the positive real zeros of
that is,
so that, if , then is an equilibrium point and there is no nonzero equilibrium point. If then and also there are two distinct positive equilibrium points, namely,
which become identical if .
(iii) The inverse sequence of the evolution sequence of the limiting Beverton-Holt equation is given by the following equation:
The sequence is ultimately bounded for any finite initial condition and it can converge to some limit (already proved in (ii) since ).
(iv) The null equilibrium point is locally asymptotically stable. In particular,
(1) and it is strictly decreasing if and
(2) If then is bounded and strictly decreasing for any finite and and it is strictly decreasing if and , since
(v) If then the evolution sequence is globally stable for any given finite initial condition. If then the evolution sequence is globally asymptotically stable for any given finite initial condition and the evolution sequence converges asymptotically towards the species extinction.
If , then the extinction point is locally stable and the equilibrium point is unstable. The equilibrium point is unstable if and it is locally asymptotically stable if .
Define the parameters and for . Then, the above-given local asymptotic stability condition of is that for given and , satisfies the subsequent constraint:
Proof.
Properties (i)-(ii) are direct by calculating the real positive zeros , equation (74), which satisfy the subsequent equation of the stationary modified Beverton–Holt equation (63), with and , such that with is satisfied:requiring that and implying also, if , that so that if ( if and only if ). If then the zeros are complex conjugate with nonzero imaginary parts so that (extinction) is the unique equilibrium point. Properties (i) and (ii) have been proved.
The evolution of the inverse sequence of the population evolution sequence of the stationary modified Beverton–Holt equation is given by the following equation:so that one gets the solution sequence (75) which is got via direct recursive calculation from initial conditions. The subsequent expression is equivalent to (75):
Assume that . Then, since , one gets in the above equation for any given finite initial condition :so that
Consider the subsequent claims:
(a) then . This claim is impossible since then is a contradiction. Then, the sequence is ultimately bounded, that is, , for any given finite .
(b) then . This claim is possible with , so that , (including the case , ) since then is not a contradiction. It is not possible with , so that since then is a contradiction, and it is not possible either with , so that , since then is also a contradiction. Property (iii) has been proved.
To prove Property (iv), first take with . Then,which implies that with the extra constraint that in order that . Both constraints together reduce to the first one since . Thus, if then and it is strictly decreasing. Thus, the extinction equilibrium point is locally asymptotically stable, as claimed, if and . Now, assume that . Then,with a positive denominator to ensure that is bounded and strictly decreasing. Both constraints jointly hold if , equivalently,which holds unconditionally for any finite if , since in that case and are unfeasible since they are complex conjugate with nonzero imaginary parts so that the unique equilibrium point is ; and for if . Property (iv) has been proved.
To prove Property (v), first note that that if . Thus, for any large initial condition , it follows that is arbitrarily close to the extinction equilibrium point , which is locally asymptotically stable so that for sufficiently large initial condition and is bounded for any given finite initial condition. Therefore, any evolution sequence is globally stable and it converges asymptotically to zero if since then the unique locally asymptotically stable equilibrium point is the extinction so that it is also a global attractor. Now, the local stability/instability properties of and of Property (v) are proved. Note from Property (iv) that:
(a) If then is bounded and strictly decreasing for any finite initial condition . Also, both and are unfeasible;
(b) If then if so that is locally asymptotically stable and is unstable since any solution from any initial condition , being arbitrarily close to converges asymptotically to .
It remains to prove that is conditionally stable. Note that, for a first-order perturbation of the equilibrium point at any -th sample, one has that , , with so that
Then, is unstable if ; , equivalently if,which is satisfied under the two subsequent conditions:
(a) , which is equivalent to , which together with the former constraints and , yields ;
(b) which is equivalent to .
As a result, is instable if .
In the same way, in order for to be locally asymptotically stable, which is fulfilled under two conditions, namely,
(c) which holds if and only if ;
(d) which holds if and only if
which are equivalently combined into the local stability condition . Taking into account that , the condition becomes equivalent tosubject to and define parameters (note that does not need to be considered since then is stable) and . Then, the constraint takes the form and the above local stability constraint (87) of takes the form (76).Remark 4.
Note from Theorem 4 (ii) that any nonzero equilibrium point is less than the carrying capacity if contrarily to the case when where is an equilibrium point.
Remark 5.
Note that, contrarily to Theorem 4(iv), if and , then, in the absence of harvesting, cannot be strictly decreasing converging to zero since, for the limit solution sequence to be strictly decreasing, it is necessary that
what implies that so that is impossible for any given positive finite initial condition if ; . Thus, the extinction equilibrium point is unstable if ; .
6. Numerical Simulations
6.1. Example 1
This example illustrates the results of Theorem 1. The sequences , and are respectively generated by means of the following difference equationsc:with the following values for the parameters:and the following initial conditions:
In this way the conditions of Theorem 1 about the sequences and are fulfilled since and .
In a first simulation, the harvesting sequence with is considered so that and then the conditions of Theorem 1(i) are satisfied. Figure 1 shows the evolution of the species population and that of the environment carrying capacity if the population is initially . One can see that as Theorem 1(i) points out.
[figure(s) omitted; refer to PDF]
On the other hand, Figure 2 displays the evolution of the species population and that of the environment carrying capacity if the population is initially . Again, one can see that although the initial population is close to the equilibrium point . The results displayed in Figures 1 and 2 illustrate the fact that the equilibrium point is globally asymptotically unstable while the equilibrium point is globally asymptotically stable.
[figure(s) omitted; refer to PDF]
In a second simulation the same values of (89) and (90) are maintained but the sequence converges to a nonzero value . Concretely, the time evolution of is displayed in Figure 3 while that of and if the population is initially is shown in Figure 4.
[figure(s) omitted; refer to PDF]
In this example the fact that is observed so that the conditions of Theorem 1(ii) and Theorem 1(iii) are satisfied. In fact, the Beverton–Holt equation (1) possesses two equilibrium points given by (1). Concretely, such equilibrium points are and . One can see that although the initial condition is close to the equilibrium point . Such a fact illustrates that is unstable while is globally asymptotically stable in the sense that all solutions generated by finite initial conditions converge to such an equilibrium.
6.2. Example 2
This example illustrates the results of Theorem 3 related with the Allee effect for small number of individuals in the species. The intrinsic growth rate and carrying capacity sequences, and , are given by (88) with the same values for the parameters , , , and than those pointed out in (89). Moreover, the harvesting sequence is zero for all and the function appearing in the modified Beverton-Holt equation (58) is given by the following equation:with and . In this way, for all and the conditions of Theorem 3(i) are fulfilled. Figure 5 shows the evolution of the species population if the population is initially . Figure 6 displays the evolution of the function and the inverse of the sequence . In Figure 5, one can see that the species population converges to the extinction as Theorem 3(i) establishes since for all as it is shown in Figure 6.
[figure(s) omitted; refer to PDF]
Now, the function appearing in the modified Beverton–Holt equation (58) is given by the following equation:with and for all . In this way, the conditions of Theorem 3(ii) are fulfilled. Figure 7 shows the evolution of the species population if the population is initially . One can see that the species population converges to the extinction as Theorem 3(ii) establishes.
[figure(s) omitted; refer to PDF]
6.3. Example 3
The following two examples illustrate the results of Proposition 5 about the modified Beverton–Holt equation (63).
(i) The sequences , and are respectively defined as
to illustrated the result (i) of such a proposition with , , , , and . Figure 8 shows the evolution of the species population if the population is initially . One can see that the species population neither extinguishes nor increases in an unboundedness way as Proposition 5 (i) establishes.
(ii) The sequences , , and are, respectively, generated by means of the following difference equations:
with the following values for the parameters:
and the following initial conditions:
In this way the conditions of Proposition 5(ii) about the sequences , and are fulfilled since , and . Figure 9 shows the evolution of the species population and that of the environment carrying capacity if the population is initially . One can see that as Proposition 1(ii) points out.
[figure(s) omitted; refer to PDF]
On the other hand, Figure 10 displays the evolution of the species population and that of the environment carrying capacity if the population is initially . Again, one can see that although the initial population is close to the equilibrium point . The results displayed in Figures 9 and 10 illustrate the fact that the equilibrium point is globally asymptotically unstable while the equilibrium point is globally asymptotically stable for .
[figure(s) omitted; refer to PDF]
6.4. Example 4
The following examples illustrate the results of Section 5 about the modified Beverton–Holt equation (63). The sequences and are, respectively, generated by means of the following difference equations:with the following values for the parameters:and the following initial conditions:
In this way the conditions of Section 5 about the sequences and are fulfilled since and . Several choices for the sequence are considered to illustrate the results of Section 5:
(i) In the first case is given by the difference equation:
with the values for the parameters and and the initial condition . In this way, and then, the conditions that , and are fulfilled so that the modified Beverton–Holt equation has two equilibrium points, namely, the stable point (extinction) and the unstable one .
Figure 11 shows the evolution of the species population and that of the environment carrying capacity if the population is initially . The results displayed in Figure 11 illustrates the fact that the equilibrium point is globally asymptotically stable while the equilibrium point is unstable for as Section 5 points out.
(ii) In the second case is given by (102) with the values for the parameters and and the initial condition . In this way, and then, the conditions that , and are fulfilled so that the modified Beverton–Holt equation has two equilibrium points, namely, the stable point (extinction) and the unstable one . Figure 12 shows the evolution of the species population and that of the environment carrying capacity if the population is initially . The results displayed in Figure 12 illustrate the fact that the equilibrium point is globally asymptotically stable while the equilibrium point is unstable as Theorem 4 (i) establishes.
(iii) In the third case is given by (102) with the values for the parameters and and the initial condition . In this way, and then, the conditions that , and are fulfilled so that the modified Beverton–Holt equation has only one equilibrium point, namely, the stable point (extinction). Figure 13 shows the evolution of the species population and that of the environment carrying capacity if the population is initially . The results displayed in Figure 13 illustrate the fact that the unique equilibrium point is globally asymptotically stable, that is asymptotically stable for any finite initial condition, as Theorem 4 (ii) establishes.
(iv) In the fourth case is given by (102) with the values for the parameters and and the initial condition . In this way, and then, the conditions that , and are fulfilled so that the modified Beverton–Holt equation has three equilibrium points, namely, the stable point (extinction) and the unstable ones and . Figure 14 shows the evolution of the species population and that of the environment carrying capacity if the population is initially . The results displayed in Figure 14 illustrate the fact that the equilibrium point is globally asymptotically stable while the other ones are unstable as Theorem 4 (ii) establishes.
[figure(s) omitted; refer to PDF]
7. Conclusions
This paper has discussed a generalized time-varying Beverton–Holt equation which considers the presence of positive or negative harvesting and, eventually, a quadratic-type penalty for the population excess. Such a term takes account for the potential internal competence between the cohort individuals for food, refuge, etc. The harvesting action (describing hunting/fishing actions) is considered jointly with eventually present independent consumption (describing migrations from outside of the habitat to inside or vice-versa). It is seen that the presence of the penalty term can translate into the presence of two other positive equilibrium points. Some particular stability results have been also derived for the stationary equation, which arises when its parameterizing sequences converge, for the case of small levels of population by introducing a term taking account for the Allee effect. The paper has also designed some species evolution control laws by monitoring the harvesting action and has discussed the influence in the stability results of considering a modelling function of Allee effect which makes difficult growing or even can cause extinction for small numbers of reproductive individuals.
The equilibrium points of the stationary solution in the presence and absence of harvesting action have been characterized and their local asymptotic stability properties have been investigated in the case of intrinsic growth rate exceeding unity and eventual execution of harvesting actions and in the case of the intrinsic growth rate being less than unity. Some numerical examples have been also discussed.
Acknowledgments
The authors are grateful to the Basque Government for its support through Grant no. IT1555-22 and to MCIN/AEI 269.10.13039/501100011033 for Grant no. PID2021-1235430B-C21/C22. The authors are also grateful to the referees by their useful comments.
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