1. Introduction
Single-species dynamics is one of the core research areas in theoretical ecology. Research about single-species dynamics enables the researcher to find out the conditions of extinction and persistence of the species. The researchers’ strong motivation to develop mathematical models is to understand the underlying causes of cyclical patterns, such as those observed in population dynamics of stochastic single-species models [
1].
Population modeling is very important for species management, for example, in developing recovery plans for species threatened by extinction, managing fisheries for the highest possible sustainable yield, and trying to contain or prevent the spread of invasive species [
2,
3,
4].
The biological phenomenon of the Allee effect occurs when the per capita growth rate of a population decreases and the population size becomes significantly low. This is a thorough biological explanation of the Allee effect that can be due to various factors, such as difficulties in finding resources, decreased mating opportunities, or even increased predation risk. Incorporating the Allee effect into the model is crucial in capturing these dynamics, especially when modeling endangered species or those at risk of extinction. In the literature, one can find several models of the dynamical single-species growth system; the Gompertz growth model [
5], Verhulst growth model with or without Allee effect [
6], power law growth model [
7], interconnections between deterministic and stochastic systems [
8], and Gilpin–Ayala model [
9] are only a few that can be mentioned.
Outside of a few clear trends, the dynamics of biological phenomena, particularly of populations for living beings, are frequently influenced by unpredictable components due to the complexity and variability of environmental conditions [
10]. Researchers have been extensively studying biological dynamical systems for a long time now, particularly in the context of modeling and analyzing random fluctuations [
11,
12]. The study of population events such as persistence in stationary distribution and extinction in stochastic single-species models has become an interesting and important research field. Developing the sufficient conditions for the persistence of biological species is one of the hot issues in population dynamics, as mentioned in [
13,
14,
15] and references therein.
The population may be affected by sudden environmental noise [
16,
17]. For example, earthquakes [
18], changes in temperature [
19], and hurricanes [
20] can be appropriately modeled as random fluctuations or stochastic events, as their occurrence and impact are less predictable and more influenced by stochasticity. These sudden environmental perturbations may bring substantial social and economic losses. Stochastic single-species models perturbed by Brownian motion have been extensively researched by many scholars [
21,
22,
23,
24,
25,
26]. However, stochastic extension of population process driven by Gaussian noise cannot explain the aforementioned random and intermittent environmental perturbations. Introducing a Lévy process into the underlying population dynamics would explain the impact of these random jumps. There have been a few studies investigating dynamical systems where the noise source is a Lévy process [
27]. Implying the Lévy noise in the biological system to simulate the effect caused by the external environment is more effective and nearer to reality than using Gaussian noise. The investigation of the single-species model is still in its infancy, even though noisy fluctuations naturally portray random intermittent jumps. Lévy noise is widely applied in studying natural and man-made phenomena in science, among which we can mention biology [
28], physics [
29], and economics [
30].
Under this research heading, we consider the population dynamics of a single-species growth model with Allee effect perturbed by stable Lévy fluctuations. We analyze the influence of Lévy noisy fluctuation on System (
1). Investigating the impact of noisy fluctuations plays a pivotal part in demonstrating the intricate interactions between single-species models and their complex surroundings. We study how Allee effects and stochasticity affect the population persistence together.
The most probable phase portrait was first proposed by Duan [
31] (Section 5.3.3). Cheng et al. [
32] obtained the analytical results of the MPPP and showed that the MPPP can provide useful information about the propagation of stochastic dynamics in a one-dimensional model. Wang et al. [
33] studied stochastic bifurcation by applying the qualitative changes of the MPPP to a stochastic system driven by multiplicative stable Lévy noise. In [
34], the authors investigated the most probable trajectories of the tumor growth system with immune surveillance under correlated Gaussian noises and derived the analytical solution of the most probable steady state by utilizing the extremum theory with the local Fokker–Planck equation for the system. A function which summarizes the behavior of the dynamics of a continuous stochastic process was defined as the Onsager–Machlup function [
35]. The Onsager–Machlup function for stochastic models driven by both non-Gaussian and Gaussian noises was established in [
36]. The authors also examined the corresponding MPPP of the stochastic dynamical systems. Cheng et al. [
37] focused on the impact of Gaussian noise and jump-stable Lévy noise in a genetic regulatory system; they minimized the Onsager–Machlup action functional for the stochastic dynamics driven by Gaussian noise and obtained the most probable transition pathway. This inspired us to study the MPPP of the single-species model.
Therefore, our goal involves investigating how the most probable trajectories escape from the single-species state to the extinction state more quickly. This investigation can contribute to answering critical questions in the field of biology. Among these, it is important to answer the question of whether there exists a transition between permanence and extinction. We probe the transition pathways from the extinction state to the stable state, which are crucial in a single-species model. This allows us to investigate the biological behavior of species.
To the best of our knowledge, the work in [
38] is closely related to our work; Y. Jin employed a Lévy jump process to describe sudden environmental perturbations and developed a stochastic model for a single species incorporating both the Allee effect and jump-diffusion. She demonstrated that this model possesses a unique, global, and positive solution; furthermore, she examined the stochastic permanence, extinction, and growth rate of the solution, discovering that these properties are intricately linked to the jump-diffusion component of the model.
However, our results in the present paper are different from those in [
38]. We delve into the most probable phase portrait of a stochastic single-species model that incorporates the Allee effect and is influenced by both non-Gaussian and Gaussian noise. The deterministic counterpart of this model exhibits three fixed points, with one being an unstable state sandwiched between two stable equilibria. We derive the Onsager–Machlup function for the stochastic model and proceed to determine the most probable paths that it follows. Additionally, we conduct numerical simulations to corroborate our theoretical findings.
Gao et al. [
39] proposed a fast and accurate numerical algorithm to simulate the nonlocal Fokker–Planck equations with non-Gaussian
-stable symmetric Lévy motions, whether on a bounded or infinite domain. Compared with this paper, the connection is that we utilize a finite difference method, which they have also explored, to find numerical solutions for the Fokker–Planck equation determined by a nonlocal differential equation. The difference lies in that we obtain the maximum possible path of the population system in the single-species model under jump-diffusion noise and determine the corresponding maximum possible stable equilibrium state.
In this study, we compute a single-species model, concentrating on the Verhulst growth model with the Allee effect developed by Y. Jin [
38]. Explicitly, we consider the following stochastic single-species growth model with Allee effect:
for
and
, where
is the left limit of the population size
. A detailed description of parameters reflecting biological mechanisms is outlined in
Table 1.
Model (
1) should be computationally efficient, allowing for fast simulations and analysis. It is important for Model (
1) to capture essential biological details; however, over-complicating the model can make it more difficult to interpret and validate. Finding the right balance between simplicity and complexity is crucial. Model (
1) is applicable to the specific biological system, organism, tissue, or cellular process of interest.
The stochastic force is a compensated Poisson random measure with associated Poisson random measure and intensity measure , in which is a Lévy measure on a measurable subset of with .
It is important to acknowledge the need to balance biological realism with mathematical tractability. The following restriction on System (
1) is natural for biological meaning:
when
, the perturbation stands for the increasing species, e.g., planting, while
represents that the species is decreasing, e.g., harvesting and epidemics.
The main aim of this study is to investigate the stochastic dynamics of single-species biological populations in random environments. We model the evolution of these populations with first-order ordinary autonomous differential equations by introducing the coefficients and inputs, which are stochastic processes. The two stochastic processes germane to this study are Brownian motion and Lévy process. Brownian motion describes random fluctuations that are continuous in time but nowhere differentiable (see
Section 2.1); a Lévy process, of which Brownian motion is a special case, is used to model random fluctuations that may have discontinuities or jumps (see
Section 2.2).
Here, we develop a stochastic single-species model with the Allee effect influenced by Gaussian and non-Gaussian noises. Model (
1) accurately captures the essential biological processes. In other words, the model is relevant and suitable for investigating the specific aspects of biology under consideration. First, we review the deterministic version of the model, calculate its equilibrium solutions, and describe the behavior of the fixed points. Second, we obtain the highest possible paths and the corresponding maximum possible stable states attracting the nearby maximum possible paths of the stochastic System (
1). We accomplish this by finding the stationary density function, which is the solution of the nonlocal Fokker–Planck equation. To solve the nonlocal partial differential equation, we use the finite difference method proposed in [
39]. This method helps us explore to some dynamical behaviors of the single-species system under the impact of non-Gaussian Lévy noise.
The rest of this study is organized as follows. In
Section 2, we recall the definitions of the one-dimensional Brownian motion
and symmetric
-stable Lévy motion
. In
Section 3, we discuss the formulation and analysis of the deterministic single-species Model (
2) the with Allee effect. In
Section 4, we explain the analysis of the stochastic single-species Model (
1) with Allee effect. We then review the definition of the Onsager–Machlup function and most probable phase portraits in
Section 4.1 and
Section 4.2, respectively. The numerical results and the biological implication of our experimental findings are presented in
Section 5. We conclude our research with a brief summary in the last section.
5. Numerical Results and Biological Implications
To allow readers to better understand our results, we performed numerical simulations to illustrate our theoretical results. Based on the finite difference method [
39], numerical simulations are very useful in the study of real population examples. In the present section, we define the bifurcation time as the time between the changes in number of maximally likely equilibrium states. This is a time scale for the birth of a new most probable stable equilibrium state. In addition, we show the intervals in which there exist one or two maximally likely stable equilibrium states, the value of the equilibrium states, and the point where the number of metastable states of the stochastic single-species Model (
1) varies. Because the numerical solutions of a model depend on the values of all its deterministic parameters and noise intensities, we discuss the effect of the parameters in
Table 1 on the investigated System (
1). For simplicity, we simulated the four most probable transition pathways together with the initial conditions selected in different intervals.
When plotting the figures, we fixed the deterministic parameters , , the noise intensity and the stability index .
The potential function denoted by
in
Figure 1a has two stable steady states
and
and an unstable steady state
for
This function has a maximum value at the unstable equilibrium solution
. The potential function attains its minima at the stable fixed points
and
. For the value of
the nonlinear System (
2) has only one equilibrium point, which is the trivial point
.
In
Figure 1b, we sketch the equilibrium states versus attack rate
. For
, there exist two stable equilibrium states
and
and one unstable equilibrium state
While
,
is the unique equilibrium state that is stable;thus, the parameter
is the bifurcation parameter value.
The distance between the unstable equilibrium
and the stable fixed point
becomes very small when
approaches 1. This indicates that the expected time to extinction may be too short, as clarified in
Figure 1b.
Figure 2 displays the numerical simulation of the stochastic single-species Model (
1) with Allee effect when it is persistent or extinct at different value of initial condition
. This figure proves that the solutions of the stochastic nonlinear System (
1) are positive and that species extinction occurs when the initial condition is less than the value of
, as demonstrated in
Figure 2b. While the initial condition is greater than the value of
, there is stochastic persistence.
In
Figure 3a, we depict the most probable transition pathways
of System (
6) for seven distinct values of
ranging from 0 to 1. The method of finding the most probable transition paths of System (
5) is equivalent to solving the one-dimensional boundary value problem in (
9). A numerical technique for computing solutions of the second-order Euler–Lagrange differential in Equation (
8) is the shooting method.
Figure 3b demonstrates the curves for the most probable steady state
of the stochastic single-species Model (
1) with
driven by Gaussian noise at different values of the noise intensity
The steady-state curves exhibit a bi-stability in the interval
. For
, the stable steady state stays at the extinction state, while for
it is located at the stable equilibrium state. Because of the presence of Gaussian noise with
term, the numerical result in
Figure 3b is completely different from the numerical result in
Figure 1b. By perturbing the parameters and observing the resulting changes in model output, it is evident that Model (
1) is sensitive to changes in its parameters.
Concerning the question of why the most probable transition pathways shown in
Figure 3a are not related to the numerical simulations shown in
Figure 2, it is because we simulated six true trajectories of the stochastic single-species Model (
1) under different noise intensities in
Figure 2. However, the most probable transition pathways depicted in
Figure 3a are reference trajectories, which are not necessarily the true trajectories of the stochastic single-species Model (
1), although their tubes are likely to contain the largest number of true trajectories of the system.
The most probable trajectories of the stochastic single-species Model (
1) with Allee effect are plotted graphically in
Figure 4 and
Figure 5a. Here, the values of the noise intensities are set as
and
respectively. We choose the stability index
and the interval
. These figures evolve as the initial value
changes, telling us that the maximal likely equilibrium state (maximizer)
lies between 9 and 10 at the bifurcation time 1.13; in other words, the maximizer in high concentration is between 9 and 10. This is different from the deterministic equilibrium stable solution
due to the effects of external noise.
Figure 5a draws the MPPP for different values of the initial point
. As seen in
Figure 5a, the most probable growth state is attracted to the maximally likely equilibrium state of extinction, then leads to the maximally likely equilibrium state in the high concentration as time moves forward. For the initial point
with two values of 0.0001 and 1 around
, the two trajectories of
starting from them are relatively close. Given two specific values 8 and 10 of the initial point
that are around
, the ascending trajectory of
starting from
and the descending trajectory starting from
coincide at a specific time point, which is 0.5.
From
Figure 5b, it can be observed that the maximum value of the stationary density function
is situated at the maximum likely stable state
with the initial condition
. As the initial condition
increases, it raises the peak point of the stationary density function
. This shows that the extinction of the species may not happen, and the high peak occurs at the maximum likely stable state
.
When there is no jump in the stochastic single-species Model (
1), i.e.,
,
Figure 3a illustrates the most probable transition paths in the
-plane with initial condition
and terminal condition
under the same transition time interval
for different values of
.
Figure 3b displays the most probable steady state
determined by (
17) (computed by numerical simulations under
) for different values of
. When there exist jumps in the stochastic single-species Model (
1) with
and
, we calculated the four most probable transition pathways using simulations based on the system dynamics and the given parameters, as exhibited in
Figure 4 and
Figure 5a. Regardless of the starting point, these most probable transition pathways eventually converge to a specific horizontal line with
between 9 and 10. The fact that the high peak of the stationary density function is located at 9.0846 effectively corroborates this point, as demonstrated in
Figure 5b. The most probable transition pathways ultimately provide a more comprehensive understanding of the system’s behavior and validate the predicted dynamics of the system through numerical simulations.
Figure 6a tells us that as time increases, the most probable paths converge quickly to the stable state
and remain at a nearly constant level, then approach the high stable equilibrium state. Although the values of the initial point
are different, these most probable transition pathways invariably converge towards a specific horizontal line positioned within the range of
between 9 and 10. This convergence is firmly supported by the observation that the stationary density function peaks precisely at 9.0846, as clearly illustrated in
Figure 6b. Ultimately, these transition pathways offer a deeper understanding of the system’s behavior, effectively validating the predicted dynamics.
The rising rate of the two trajectories of
initiating from 0.0001 and 1 in
Figure 5a differs significantly from that of the two trajectories of
commencing from 0.001 and 4 in
Figure 6a. While the peak heights of the probability density function in
Figure 5b are different from those in
Figure 6b, the locations of the peaks are surprisingly consistent, all precisely at 9.0846. We compare the peak heights of the probability density function while noting the surprising consistency in the location of the peaks.