1. Introduction
The predator–prey model’s applicability extends beyond depicting predator–prey dynamics to provide critical insights into ecosystem functioning and stability management [
1,
2,
3,
4]. The classical Leslie–Gower predator–prey model was proposed in [
5]
where
and
denote the population densities of the prey and predator at time
t, respectively. The parameters
r and
represent the intrinsic growth rates of the prey and predator, respectively;
K is the carrying capacity of the prey; and
denotes the nutritional value of the prey to the predator;
indicates the Leslie–Gower term; and
denotes the functional response that portrays the impact of the amount of bait on the predation rate of the predator. Generally, many authors have considered several types of functional responses, such as Holling I–IV [
6,
7,
8,
9,
10], square root [
11,
12], ratio-dependent [
13,
14], and the Allee effect [
15].
The predator’s consumption rate is described by the Holling type II functional response, and system (
1) becomes the following Holling–Tanner model proposed in [
16]:
where
a denotes the maximum predation rate and
b is the half-saturation constant. The local stability of the unique positive equilibrium of system (
2) was investigated by May [
16]. Subsequently, Hsu and Huang [
17] postulated that for a predator–prey system possessing a unique positive equilibrium, its local stability implies global stability. However, Sáez and González-Olivares [
18] demonstrated that local asymptotic stability does not, in general, guarantee global stability.
Traditional predator–prey models focus on specialist predators (single food source), but real ecosystems commonly have generalist predators (multiple food sources when prey is scarce) [
19]. Consequently, generalized predator models (with generalist predators) better capture actual ecosystem dynamics [
20,
21,
22,
23]. Specifically, a widely studied modified Holling–Tanner model—based on system (
2) and incorporating generalist predators [
24,
25]—is given below:
where
represents the degree to which the environment is protected from predators. In an ecological setting,
indicates that predators possess other food sources. The introduction of generalist predators makes the system more in line with the relationship between predators and prey in reality and more significant for research. That is, predators can resort to other resources when there is a severe shortage of food sources. Xiang et al. [
26] conducted a comprehensive analysis of the high-codimension bifurcations in system (
3), demonstrating the existence of a codimension-2 Hopf bifurcation and a codimension-3 degenerate Bogdanov–Takens bifurcation. Meanwhile, Chen et al. [
27] investigated the impact of the fear effect on the dynamics of a modified Leslie–Gower model, exploring various bifurcation types such as transcritical, Hopf, and Bogdanov–Takens bifurcations. In recent years, the modified Holling–Tanner model has been further refined by incorporating additional biological factors, including environmental influences [
28], the Allee effect [
29,
30], and prey refuge [
31], leading to a more accurate representation of ecosystem dynamics.
Predator–prey system resource harvesting (for economic gain) is widely modeled [
32,
33,
34]. Key works: Huang et al. [
35] (system (
2), constant-yield harvesting) proved Hopf bifurcation and codimension-3 Bogdanov–Takens singularity; Zhu and Lan [
36] (Leslie–Gower, Holling I, and constant-yield) found supercritical/subcritical Hopf bifurcations; Gupta et al. [
37] (Leslie–Gower, Holling I, and Michaelis–Menten) showed prey nonlinear harvesting’s dynamic influence; Yao and Liu [
38] (Leslie–Gower, hunting cooperation, and harvesting) identified extinction critical values.
Considering system (
3) with constant-yield harvesting, Wu et al. [
39] proposed the following system
Their analysis demonstrated that system (
4) possesses a cusp of codimension 4, a weak focus of order 2, and a degenerate Hopf bifurcation of codimension 2 and exhibits two limit cycles (verified via resultant elimination). In a study of a Leslie–Gower model featuring nonlinear harvesting and a generalist predator, [
40] found that while nonlinear harvesting could drive prey to extinction, the generalist nature of the predator prevents its own extinction.
In order to conduct further research based on Wu et al. [
39], we consider studying the influence of more complex harvesting on the system (
4). Therefore, we change constant-yield harvesting to nonlinear harvesting. System (
3) with nonlinear harvesting (or Michaelis–Menten-type) can be expressed as follows:
where
h denotes the catchability coefficient,
q represents the fishing effort, and
and
are positive constants. The meanings of the remaining parameters are consistent with those in system (
3). All parameters are assumed to be positive based on biological considerations. The core ecological significance of Michaelis–Menten harvesting lies in describing a kind of “resource-constrained prey capture”, which is closer to the actual scenarios in nature or human activities than simple linear harvesting.
For the simple case where
in system (
5), Gupta and Chandra have addressed the system’s permanence, stability, and bifurcation behavior. Nevertheless, their work did not extend to investigating the codimensions of either the cusp bifurcation or the Bogdanov–Takens bifurcation. Accordingly, the present study focuses on the general scenario—i.e.,
in system (
5)—and aims to demonstrate two key results: first, that system (
5) exhibits a cusp with a codimension of at least 5, and second, that it undergoes a Bogdanov–Takens bifurcation of codimension 3. Also, system (
5) has a weak focus of codimension 3.
To simplify the discussion, using the following non-dimensional
and dropping the bars, system (
5) becomes the following system
The structure of this paper is organized as follows.
Section 2 classifies the boundary equilibria.
Section 3 analyzes the existence and stability of positive equilibria in system (
6). The conditions for Bogdanov–Takens and Hopf bifurcations are derived in
Section 4.
Section 5 provides numerical simulations to validate the theoretical results. Finally,
Section 6 concludes the paper.
2. Preliminaries
In this section, we address the stability of the boundary equilibria for the system (
6). It is evident that the solutions to system (
6) are both positive and bounded. The positively invariant of system (
6) is
The Jacobian matrix of (
6) at
is
and
When
, it is easy to see that system (
6) has two boundary equilibria
and
.
Lemma 1. (1) If , is a hyperbolic saddle. If , is a hyperbolic unstable node. If , is a saddle-node which includes an unstable parabolic sector. If , is a degenerate saddle.
(2) If , is a hyperbolic stable node. If , is a hyperbolic saddle. If and , is a saddle-node which includes a stable parabolic sector. If and , is a degenerate stable node when , a saddle-node which includes a stable parabolic sector when , and a degenerate saddle when .
Proof. (1) The Jacobian matrix of system (
6) at
is
Obviously,
is a hyperbolic saddle (or unstable node) when
(or
).
and system (
6) becomes (still denoting
by
t)
Hence, when
, from Theorem 7.1 in [
41],
is a saddle-node which includes an unstable parabolic sector.
When
, supposing that
, and substituting it to the second equation of system (
7), we have
Therefore, substituting
into the first equation of system (
7), we obtain
By Theorem 7.1 in [
41],
is a degenerate saddle.
(2) The Jacobian matrix of system (
6) at
is
Obviously,
is a hyperbolic stable node when
and a hyperbolic saddle when
. When
, in order to determine the type of
, using the following transformations
system (
6) becomes
Hence, when
, from Theorem 7.1 in [
41],
is a saddle-node which includes a stable parabolic sector.
When
, according to the center manifold theorem, substituting
into the second equation of system (
8), we have
By replacing
with
in the initial equation of system (
8), we derive
is a degenerate stable node when
and a degenerate saddle when
.
When
, similar to the above analysis, we obtain
Using Theorem 7.1 in [
41],
is a saddle-node which includes a stable parabolic sector. □
When the system reaches the equilibrium point
, it indicates that both species are extinct at this time, representing the complete collapse of the ecosystem. When the system reaches the equilibrium point
, we examine the stability of the boundary equilibria for
. When
, from the first equation of system (
6), we obtain
where the discriminant of
is
Obviously, and . In the following, we discuss the number of positive roots of .
(1) If and or and , then has no positive root.
(2) If and , then has only one positive root .
(3) If and ; or and , then has only one positive root .
(4) If and , then has two positive roots and .
The types of boundary equilibrium are classified as follows.
Lemma 2. (1) When and , is a saddle-node including an unstable parabolic sector.
(2) When and ; or and , is a hyperbolic saddle.
(3) When and , is a hyperbolic unstable node, and is a hyperbolic saddle.
Proof. The Jacobian matrices of system (
6) at
and
are, respectively,
Therefore, is a hyperbolic unstable node, and is a hyperbolic saddle.
The Jacobian matrix of system (
6) at equilibrium
is
Using
system (
6) becomes (still denoting
by
t)
and the coefficients
and
are omitted for brevity. Hence, from Theorem 7.1 in [
41],
is a saddle-node which includes an unstable parabolic sector. □
When the system reaches the equilibrium point , , or , it indicates that predators have become extinct at this time, and the prey exists alone, representing the extinction of predator species in the ecosystem, and the prey enters a stable state of “no natural enemies”.
3. Positive Equilibria and Their Types
Setting
in Equation (
6) yields
From Equation (
9), we obtain
where
The derivative of
is
where the discriminant of
is
Letting
, we have
Substituting
into
and
, we obtain
Note that
,
,
,
. We obtain the following results regarding the existence of positive equilibria of system (
6).
Lemma 3. The following statements are true.
- (1)
Assume that , ; or , .
(1.1)
If , system (6) has no positive equilibrium.(1.2)
If , system (6) has a positive equilibrium .- (2)
Assume that , ; or .
(2.1)
If , system (6) has a positive equilibrium .(2.2)
If , , system (6) has no positive equilibrium.(2.3)
If , , system (6) has a double positive equilibrium .(2.4)
If , , system (6) has two positive equilibria and .- (3)
Assume that , .
(3.1)
If , system (6) has no positive equilibrium.(3.2)
If , system (6) has a positive equilibrium for or a triple positive equilibrium for .- (4)
Assume that , , .
(4.1)
If , system (6) has no unique equilibrium.(4.2)
If , system (6) has a double positive equilibrium .(4.3)
If , system (6) has two positive equilibria and .- (5)
Assume that , , .
(5.1)
If , system (6) has a positive equilibrium or .(5.2)
If , system (6) has two positive equilibria and or and .(5.3)
If , system (6) has three positive equilibria , , and .Moreover, and are elementary anti-saddle, is a hyperbolic saddle, and and are degenerate equilibria.
Proof. From condition (
10), we have
,
,
, and
. Thus
, and
are degenerate equilibria;
is a hyperbolic saddle; and
and
are elementary anti-saddles. □
Next, inspired by [
42], we will discuss the types of double and triple positive equilibria of system (
6).
3.1. A Double Positive Equilibrium
For convenience, let the double positive equilibrium
or
be denoted by
where
. By
,
h,
n, and
k can be expressed by
,
m,
s, and
q:
where
∈
for the positivity of
.
When
, we have
Hence, when , , and , is a double positive equilibrium.
Next, we will give the type of .
Theorem 1. Assume that , , and .
- (1)
If , is a cusp of codimension 2.
- (2)
If , is a cusp of codimension 3.
- (3)
If , and , is a cusp of codimension 4.
- (4)
If , and , is a cusp of codimension at least 5.
Here, and are given in the proof of this theorem.
Proof. Using
then system (
6) becomes
where
with the remaining coefficients excluded for the sake of conciseness.
Now define
then system (
12) becomes
where
with the remaining coefficients excluded for the sake of conciseness.
When
and
, we know
and
. Then according to [
42,
43],
is a cusp of codimension 2 (see
Figure 1a).
When
and
, we have
and
. According to Lemma 2.4 in [
42], the system (
15) becomes
where
where
and the expression of
is omitted for simplicity.
According to
and
, we obtain
note that
and
, which implies that
and
. Therefore, whether
and
are equal to 0 is determined by
and
, respectively.
According to Lemma 2.4 in [
42], when
,
is a cusp of codimension 3 if
(see
Figure 1b), a cusp of codimension 4 if
,
, or a cusp of codimension at least 5 if
,
. □
Because the conditions of Theorem 1 are very complex, the following remark gives two examples to show that the existence of the cusp of codimension 4 and at least 5.
Studying cusps with a codimension of at least 5 helps to more accurately predict the future development trends of ecosystems. By analyzing the system behavior near the cusp, we can identify under what circumstances the ecosystem may undergo abrupt changes, such as an increased risk of extinction for predator or prey populations. This is of great significance for early warning of the dynamic risks of ecosystems. Meanwhile, researching such cusps can help us uncover the complex dynamic behaviors of predator–prey systems with the interaction of multiple parameters, such as sudden changes in population sizes and alterations in system stability.
When the equilibrium point of the system is cusp-type, it depicts a sudden and irreversible drastic transformation of the population state in the ecosystem with minor changes in key parameters. The research results can be used to warn of the critical risk of the ecosystem and optimize ecological restoration strategies.
Remark 1. (1) When , , , , , and , is a cusp of codimension 4 (see Figure 1c). (2) When , , , , , and , is a cusp of codimension 5 (see Figure 1d). Proof. Substituting
into
and
, we obtain
and the expression of
is given in
Appendix A.
Computation with Maple yields the following resultant
where
Next, the root isolation algorithm for multivariate polynomial systems [
42,
44] is applied to find a root of
in
and a common root of
and
in
, respectively. Let
denote the sum of the positive terms in
and
denote the sum of the negative terms in
[
44].
Using “realroot
” in Maple,
has four real roots in
, where we only consider the second root as follows
where
For
of
, we obtain four positive real roots isolation intervals of
in
. For brevity, we only consider the third and fourth roots as follows
where
by direct calculation, we have
,
, and
. Hence,
is the common root of
and
.
is the root of
but not the root of
.
Therefore, when , , , , , and , that is, , is a cusp of codimension 4. When , , , , , and , that is, , is a cusp of codimension at least 5. □
3.2. A Triple Positive Equilibrium
For convenience, let the triple positive equilibrium
be denoted by
, where
. From the analysis in
Section 3.1 and by simple computation, when
and
, which implies that
and
, it is obvious that
is a triple positive equilibrium.
Next, according to the method in [
42], our goal is to determine the type of the triple positive equilibrium
.
Theorem 2. When , , and , the triple positive equilibrium is
- (1)
A nilpotent focus of codimension 3 if ;
- (2)
A nilpotent elliptic equilibrium of codimension 3 if ;
- (3)
A nilpotent elliptic equilibrium of codimension at least 4 if .
Proof. When
and
, using the transformations (
11) and (
13) in the proof of Theorem 1, system (
6) becomes
where
When
,
and
, it is easy to see that
and
. Obviously, the sign of
is determined by
. According to Lemma
in [
42], we obtain
(1) If
,
is a nilpotent focus of codimension 3 (see
Figure 2a);
(2) If
,
is a nilpotent elliptic equilibrium of codimension 3 (see
Figure 2b);
(3) If
,
is a nilpotent elliptic equilibrium of codimension at least 4 (see
Figure 2c).
□
Figure 2.
(a) When , , , , , and , is a nilpotent focus of codimension 3. (b) When , , , , , and , is a nilpotent elliptic equilibrium of codimension 3. (c) When , , , , , and , is a nilpotent elliptic equilibrium of codimension at least 4.
Figure 2.
(a) When , , , , , and , is a nilpotent focus of codimension 3. (b) When , , , , , and , is a nilpotent elliptic equilibrium of codimension 3. (c) When , , , , , and , is a nilpotent elliptic equilibrium of codimension at least 4.
6. Conclusions
This study presents a comprehensive analysis of a Holling–Tanner predator–prey model with a generalist predator and Michaelis–Menten-type prey harvesting. Our findings indicate that system (
6) can possess up to three positive equilibria and four boundary equilibria, with the latter potentially being saddle-nodes, degenerate stable nodes, or degenerate saddles.
Considering system (
6) with constant-yield harvesting, which is referred to as system (
4), the authors of [
39] demonstrated that this system possesses a cusp of codimension 4 and a weak focus of order 2. They further established that it undergoes a codimension-2 degenerate Hopf bifurcation, giving rise to two limit cycles. Gupta and Chandra [
46] studied the stability and bifurcation of the system when
in system (
5). However, they did not obtain the codimension of the cusp and Bogdanov–Takens bifurcation. Moreover, both the systems in [
39,
46] have at most two positive equilibria. Compared with [
39,
46], system (
6) has at most three positive equilibria. It is proven that the double positive equilibrium is a cusp with a codimension of at least 5 and that system (
6) has a weak focus with a multiplicity of at least 3. This indicates that, due to the influence of nonlinear harvesting, we obtain the cusp and weak focus with higher codimensions than those in [
39,
46]. From Theorem 2, the triple positive equilibrium is a nilpotent focus (or elliptic) of codimension 3 or a nilpotent elliptic equilibrium of codimension at least 4, which is not presented in [
39,
46]. Additionally, we prove that system (
6) undergoes several bifurcations, including a codimension-3 cusp-type degenerate Bogdanov–Takens bifurcation and a Hopf bifurcation. Finally, we employed numerical simulations to confirm our main theoretical results and demonstrate the existence of two limit cycles in the system. In the research on system (
6), we find the Michaelis–Menten-type harvesting leads to more complex dynamics. Based on the research on this system presented in this paper, we know that in reality, when predators prey on prey species, there exists a critical conservation threshold. When the population size falls below this threshold, predation must be suspended to prevent extinction. We can use this to predict the dynamic risks of the ecosystem, intervene in advance, and formulate flexible multi-objective management strategies.