1. Introduction
In the field of biomathematics, population dynamics and infectious diseases have received considerable attention [
1,
2,
3]. In recent years, several outbreaks of infectious diseases, such as HIV/AIDS, COVID-19, Japanese encephalitis [
4], and other widespread infectious diseases, have occurred. These diseases are harmful and pose a threat to the lives and health of individuals worldwide. Therefore, the prevention and control of infectious diseases have become top priorities. In response to the growing threat of infectious diseases, many mathematical researchers have devoted themselves to studying these diseases and have built mathematical models to analyze their transmission mechanisms [
5,
6]. While it is important to focus on diseases that affect humans, it is equally important to pay attention to infectious diseases in animals, known as eco-epidemics. The spread of a disease in a wild animal population is also known as a wildlife epidemic. Examples of such diseases include the Ebola virus, avian influenza, and tularemia. Some ecological epidemics can cross species boundaries and infect humans, resulting in zoonotic infections [
7,
8]. These cross-species infections present unique challenges in disease management and prevention. Because predation is the most common relationship between populations, mathematicians naturally combine predation systems with ecological epidemiology to analyze mathematical results [
9,
10,
11].
The transmission of infectious diseases involves numerous factors, of which the environment plays a particularly vital role. Environmental transmission refers to the spread and persistence of pathogens in the environment [
12,
13,
14]. In ecological epidemics, pathogens are often closely associated with the natural habitats of wild animals, including factors such as habitat, climate, and geographical conditions [
15,
16]. Pathogens can be transmitted in the environment through various means, including the feces, urine, saliva, and respiratory secretions of infected wild animals. Direct or indirect contact between infected animals and environmental elements such as water, soil, and vegetation can also facilitate transmission. White-nose syndrome (WNS) is a disease that primarily affects bats [
17]. It is caused by the fungus Pseudogymnoascus destructans, which forms white patches on the nose, wings, and skin of bats, compromising their immune system and causing severe health problems. WNS, which was initially discovered in North America, caused significant bat mortality within a short period [
18]. The spread of this disease is closely linked to environmental factors, including specific temperature and humidity conditions within bat habitats as well as the swarming behavior of bats [
17]. Therefore, eco-epidemiological research should focus on studying the interactions between the environment and animals to gain insights into the transmission mechanisms of diseases and to assess the associated risks. However, existing research on eco-epidemic diseases often overlooks the role of environmental infections in transmission mechanisms.
Cooperative hunting, in which predators work together to attack prey, is a strategic behavior that is observed in many animal species, such as wolves, lemurs, and sharks. This behavior not only highlights the sociality of animals, but also plays a crucial role in shaping the ecosystem stability and population dynamics of other species. Therefore, cooperative hunting in predation systems has attracted extensive attention from scholars [
19,
20,
21]. However, previous research has primarily focused on healthy populations, and few studies have explored the impact of disease on cooperative hunting. Although the authors in [
22,
23] considered both cooperative hunting and disease, they mainly considered prey disease and did not consider the relationship between predator disease and cooperative hunting. In reality, when some animals contract infectious diseases, they often self-isolate, are ostracized, or consciously leave the group [
24]. Particularly in group-living populations, these diseased individuals are typically excluded from cooperative hunting activities. One possible explanation is that healthy individuals avoid contact with sick individuals to mitigate the risk of disease transmission. To understand the relationship between disease and cooperative hunting comprehensively, it is essential to consider the influence of disease on cooperative hunting behavior. Research in this area can provide valuable insights into disease transmission and animal behavior while concurrently enhancing our understanding of ecosystem dynamics and population interactions.
When investigating intricate dynamical behaviors inherent to natural ecosystems, instantaneous system states are governed jointly by contemporary environmental conditions and preceding historical evolutions. Such temporal dependency renders conventional integer-order differential models inadequate to characterize long-range memory and nonlocal interactions across ecological systems. As a generalized extension of classical integer-order calculus, fractional calculus is endowed with a prominent merit: its inherent memory-kernel framework is capable of quantifying the hereditary properties of dynamical systems and accurately depicting cumulative historical impacts embedded within ecological evolution [
25]. In recent years, research on fractional calculus has made unprecedented progress [
26,
27,
28,
29,
30,
31]. Fractional calculus has a property between integer-order differential and integral stochastic processes, which can describe the phenomena of non-stationary, nonlinear, and long-term memory more accurately. Fractional calculus has a wider range of applications than integral calculus, such as signal processing [
27], image recognition [
28], financial engineering [
29], and medical diagnosis [
30,
31]. Particularly in ecology, many scholars have used fractional-order systems to model populations and infectious diseases, and several results have been obtained [
32,
33,
34]. However, among the numerous studies on fractional infectious diseases, most still focus on disease transmission of diseases among humans, while few have specifically studied the impact of diseases on population survival.
In many real-world problems, the system response may depend on past states or inputs, and ignoring this information can lead to false predictions of the system behavior. Therefore, an increasing number of researchers have begun to pay attention to delay differential equations [
35,
36]. This approach can reflect the historical evolution of a system and provide more accurate predictions and modeling capabilities, and is therefore favored by many mathematicians. Particularly in the field of fractional calculus, the corresponding fractional delay differential equations have been established [
37,
38]. Time delay can lead to switching of the equilibrium stability of the system and result in richer dynamic behavior. In addition, research on Hopf bifurcation has attracted much attention in recent years; in particular, the time delay is generally preferred as the bifurcation parameter [
39,
40,
41].
Inspired by the above research and to fill the gaps in the current research, we propose a new mathematical model to better understand the impact of disease on population dynamics in ecological epidemiology. The main contributions of this study are as follows:
- (1)
A fractional-order predation model that considers environmental infection is established for the first time, and the effect of disease on cooperative hunting is proposed.
- (2)
By adopting the Caputo fractional derivative, this work establishes a novel fractional eco-epidemiological model, which overcomes the drawbacks of integer-order counterparts via characterizing system memory and hereditary population dynamics.
- (3)
Considering the delay in disease transmission, the Hopf bifurcation criterion caused by the delay of disease latency is discussed.
2. Model Description and Preliminaries
Cooperative hunting constitutes a widely investigated predation strategy within eco-epidemiological modeling [
22,
23,
41]. As a representative work, Saha et al. [
22] constructed a predator–prey system featuring infected prey and cooperative predation behavior of predators:
where
S and
I represent the population densities of susceptible and infected prey, respectively.
y represents the density of predators. Liu et al. [
23] developed an eco-epidemiological model incorporating fear effect and cooperative hunting among predators:
where
and
Z represent susceptible prey, infected prey and predator, respectively. Both systems (1) and (2) incorporate disease infection within prey populations but neglect pathogenic infection in predators. To remedy this limitation, Hilker et al. [
41] constructed a model accounting for predator disease as well as intraspecific cooperative predation:
where
and
I represent the density of prey, susceptible predator populations and infected predator populations, respectively. System (3) focuses on the effects of density-mediated disease, but does not consider the effects of traits such as whether the disease affects the group hunting behavior of infected predators. Sick predators often voluntarily leave the group or are forcibly excluded from a group of uninfected predators [
24]. An animal’s internal self-protection mechanism plays a key role in this phenomenon. In addition, it is necessary to consider the transmission of diseases through the environment. Many studies have shown that factors such as animal feces and contaminated water sources can indirectly spread diseases [
15,
16,
17]. Therefore, significant attention must be paid to this key factor of environmental transmission. However, the existing research has obvious deficiencies in this aspect.
Based on the above analysis and works, we propose a PP model with cooperative hunting and environmental infection. For the purposes of this study, we make the following assumptions:
- (i)
The disease is transmitted only between predators.
- (ii)
Infected predators do not recover from the disease and are voluntarily or passively excluded from group life.
- (iii)
Infected predators do not participate in cooperative hunting and can only hunt for food on their own.
- (iv)
The strains in the environment all originate from infected predators.
Finally, the governing mathematical model is formulated as below:
where
x represents prey,
represents susceptible predators,
is infected predators, and
z is the number of pathogens in the environment. All parameter definitions for system (4) are summarized in
Table 1.
Since the initial conditions of Caputo fractional differential equations are consistent with those of integer-order differential equations, this definition intuitively aligns with the physical connotation of memory effects in biological systems and can effectively characterize the historical dependence and hereditary properties of dynamical systems [
37]. Accordingly, this paper introduces the Caputo fractional derivative into system (4) and further investigates the disease incubation period
based on the improved model. The resulting fractional-order system is expressed as follows:
The initial conditions for system (5) are as follows:
Remark 1. The parameters e and f denote the biomass conversion efficiencies of susceptible and infected predators from consumed prey, respectively. From a biological perspective, part of the prey biomass consumed is dissipated via metabolism and respiration rather than converted into predator population growth, which yields and .
Some necessary definitions and lemmas required throughout this study are presented below.
Definition 1 ([
26]).
The Caputo fractional derivative is defined bywhere n is a positive integer, and , is the Gamma function with . Definition 2 ([
42]).
The Laplace transform of Caputo fractional-order derivative iswhere . In particular, when , then Lemma 1 ([
43]).
Let be a continuous function on and satisfyingwhere and , and is the initial time. Then 5. Hopf Bifurcation
The parameter
plays a crucial role in determining the stability of system (5) and is thus chosen as the bifurcation parameter. For the convenience of subsequent analysis, we introduce the transformation:
Then system (5) turns into:
Therefore, the linearization of system (5) can be written as
where
Transforming both sides of system (20) with a Laplace transformation yields:
which can be rewritten as:
We refer to
as the characteristic matrix of system (5), where
and
Therefore, the characteristic equation of system (21) is expressed as follows
where
Assume that
is a purely imaginary root of (22). Then, it follows that
where
The specific formulas of
with
are presented as follows:
Based on (23), the following results can be obtained:
It is apparent from (24) that
We assume that there is at least one positive real root
of (25), then the specific expression of
is that
The bifurcation point is defined as
To derive the conditions for the emergence of Hopf bifurcation, we impose the following necessary hypothesis:
where the expressions of
are defined in (30), respectively. Based on the fundamental results derived above, we establish another crucial lemma as follows.
Lemma 2. If the hypothesis holds, let be the root of (22) with satisfying , then we have Proof. Differentiating both sides of (22) with regard to
, one obtains
where
is the derivative of
. Based on (28), we claim that
where
It can be deduced from Equation (29) that
where
Under hypothesis
, the proof of Lemma 2 is completed. □
From the above analysis and discussion, we draw the following conclusions.
Theorem 7. For system (5), the following results can be obtained.
- (i)
The coexistence equilibrium point of system (5) is asymptotically stable when .
- (ii)
The coexistence equilibrium of the system (5) is unstable when .
- (iii)
The system (5) undergoes a Hopf bifurcation at .
6. Numerical Simulations
We use the Adams–Bashforth–Moulton scheme [
44,
45] to compute system (5); three examples confirm its stability and the biological feasibility of Hopf bifurcation.
Example 1. The impact of cooperative hunting on the stability of the system.
Numerous scholars have incorporated cooperative hunting into predation mechanisms to construct relevant predator–prey models and demonstrated that the cooperative hunting parameter is capable of inducing system bifurcation [
19,
20,
21,
22,
23]. We further verify this conclusion via illustrative numerical examples. Setting
And by calculating that, we get
Under such circumstances, system (5) admits the disease-free equilibrium
.
Figure 1 shows that the stability of the disease-free equilibrium
changes as
takes values of 1,
and 2 under
.
In
Figure 1: (a) local asymptotic stability of the disease-free equilibrium
holds at
; (b) local asymptotic stability of the disease-free equilibrium
holds at
; (c) the disease-free equilibrium
becomes unstable when
.
Remark 2. In Figure 1, we set , implying that the fractional-order system (5) reduces to the integer-order counterpart (4). With these parameters, the population of infected predators converges to zero, and the system degenerates into a classic predator–prey model with cooperative hunting. Below, we investigate how the cooperative hunting parameter affects the stability of fractional-order system (5). We fix the parameters as
. The coexistence equilibrium of system (5) is
. With fixed
, we take three values of the cooperative hunting coefficient:
. We examine the resulting time-series evolutions of system (5), as plotted in
Figure 2. The results reveal that rising
gradually destabilizes the system. Accordingly, the cooperative hunting coefficient should be maintained within a proper range to preserve system stability.
Remark 3. As the cooperative hunting parameter rises, susceptible predators gain substantially improved prey-capturing capability. With the prey population fixed, a high predation success rate drives a continuous decline in prey abundance. Infected predators possess restricted hunting efficiency. A marked drop in available prey further limits their food intake. Sustained depletion of prey in this manner inevitably destabilizes the whole ecosystem.
In
Figure 2: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
.
Example 2. Hopf bifurcation induced by latency delay.
We next investigate the impacts of latency delay and fractional order on the stability of the coexistence equilibrium. The fixed parameters are specified as .
Under such a parameter configuration, the coexistence equilibrium reads .
First, fix
to determine the critical bifurcation value
for the onset of Hopf bifurcation. After verifying the transversality condition
holds, theoretical calculations yield the bifurcation threshold
. We then adjust the latency delay: setting
, the corresponding numerical results are plotted in
Figure 3. The resulting oscillatory time series and closed hollow orbits in the phase portrait demonstrate system instability. Next, we take
, with simulation outcomes presented in
Figure 4. The system regains local stability at this smaller delay value.
In
Figure 3: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
; (d) waveforms and phase portraits near
for
.
In
Figure 4: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
; (d) waveforms and phase portraits near
for
.
Theoretical analysis reveals that the bifurcation threshold depends on the fractional order. We next fix
and compute the critical bifurcation value
. When
, system (5) loses stability near
, as depicted in
Figure 5. By contrast, setting
renders the equilibrium
locally asymptotically stable (see
Figure 6). The stability shifts observed in
Figure 3,
Figure 4,
Figure 5 and
Figure 6 therefore validate Theorem 7.
In
Figure 5: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
; (d) waveforms and phase portraits near
for
.
In
Figure 6: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
; (d) waveforms and phase portraits near
for
.
Example 3. Effects of fractional order on the system.
We examine how the fractional order affects the system’s stability domain, adopting all parameter values specified in Example 2.
We first exclude time delay to analyze the fractional-order impacts on the stability region of the delay-free system.
Four values are chosen for comparison.
Figure 7 illustrates the trajectories of all state variables in system (5) across distinct
.
Numerical results indicate that decreasing the fractional order accelerates the system’s convergence to a stable steady state.
Next, we fix and vary .
Figure 8 presents time trajectories and phase portraits of system (5) near coexistence equilibrium
for
, revealing system instability. This outcome contrasts sharply with
Figure 6 and implies the critical bifurcation threshold is smaller than
.
In
Figure 7: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
; (d) waveforms and phase portraits near
for
.
In
Figure 8: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
; (d) waveforms and phase portraits near
for
.
With fixed
and
,
Figure 9 displays time trajectories and phase portraits of system (5) around
, where the equilibrium is asymptotically stable. Compared with
Figure 6, the time series in
Figure 9 converges faster with markedly weaker oscillation amplitudes, which suggests the corresponding bifurcation threshold exceeds
. Results from
Figure 8 and
Figure 9 demonstrate the fractional-order parameter’s impact on the critical bifurcation value: a smaller fractional order yields a larger threshold
and hence postpones the onset of Hopf bifurcation.
Figure 10 further intuitively characterizes the quantitative relation between
and
.
In
Figure 9: (a) waveforms and phase portraits near
for
; (b) waveforms and phase portraits near
for
; (c) waveforms and phase portraits near
for
; (d) waveforms and phase portraits near
for
.
Remark 4. The derived theoretical results can be interpreted ecologically from three key parameters: cooperative hunting strength, disease latency delay, and fractional order. First, excessive cooperative hunting destabilizes coexisting populations: intensified group predation depletes prey resources rapidly, creating food scarcity for diseased solitary predators and triggering cyclic population oscillations. Second, latency delay drives Hopf bifurcation: a short latent period () restricts pathogen transmission and stabilizes the ecosystem, while overly prolonged latency () lets asymptomatic infected predators continuously contaminate the environment, sparking recurrent epidemic fluctuations. Third, the fractional order describes ecosystem historical memory. A smaller fractional order strengthens memory effects, accelerating the system’s convergence to steady state and raising the critical bifurcation threshold , which improves the ecosystem’s resistance to disease-induced periodic outbreaks. Collectively, these findings provide ecological suggestions for wildlife management: controlling predator cooperative intensity and shortening pathogen latent duration effectively maintain population stability.
7. Conclusions
A novel fractal-order model of predator–prey systems is proposed that combines the characteristics of cooperative hunting and environmental infection, with a particular focus on the spread of disease between predator populations. As opposed to the traditional model, this study not only considers the direct mode of disease transmission but also introduces the mechanism of environmental transmission. This innovative perspective, which is the first of its type in eco-epidemiological research, allows us to better understand how pathogens affect predator population dynamics in natural environments. In the case of a group of social predators that have long practiced cooperative hunting strategies, the study finds that the spread of disease can seriously disrupt this cooperative relationship, thereby affecting the survival and reproduction of the population. We study the solution of the system in depth and obtain results for the boundedness, existence of the equilibrium point, and local asymptotic stability of the system. Our results provide a theoretical foundation for understanding predator population dynamics. Furthermore, we introduce the latency delay of the disease as a bifurcation parameter and obtain the sufficient conditions for Hopf bifurcation. This finding shows that when the latency delay exceeds a certain critical value , Hopf bifurcation occurs in the system, resulting in fundamental changes in the dynamic behavior of the ecosystem. The numerical simulation results further verify our theoretical analysis conclusion: when , the coexistence equilibrium points in the system show asymptotic stability, and when , the system can maintain a stable state. However, when , the stability of the system is destroyed, causing the balance between predators and prey to break down. Moreover, different fractional exponents lead to different stable convergence rates, which can be explained by the long-term memory effect embodied by the fractional derivatives. This memory feature is important in ecological models because it reflects the complex dynamic interactions between predators and prey, thereby providing insights into the evolution of ecosystems. Through numerical examples, it is found that the reduction in the fractional order number prolongs the Hopf bifurcation time.
In addition, biologically, our infection model is simplified to ease stability and bifurcation analysis, omitting multi-stage disease progression, graded infection severity, and infected predator heterogeneity, which reduces biological realism. For future work, we will subdivide infected predators into exposed, mild, and severe compartments and adopt heterogeneous infection parameters. Our core analytical methods (Jacobian stability, Mittag-Leffler boundedness, Hopf bifurcation) can be extended to these refined, more realistic models.