Abstract
This paper proposes a stochastic predator–prey model with hunting cooperation and nonlinear stochastic disturbance, and focuses on the effects of nonlinear white noise and hunting cooperation on the populations. First, we present the thresholds and for extinction and persistence in mean of the predator. When is less than 0, the predator population is extinct; when is greater than 0, the predator population is persistent in mean. Moreover, by establishing suitable Lyapunov functions, we investigate the threshold for the existence of a unique ergodic stationary distribution. At last, we carry out the numerical simulations. The results show that white noise is harmful to the populations and hunting cooperation is beneficial to the predator population.
Keywords:
hunting cooperation; stochastic prey–predator model; nonlinear perturbation; stationary distribution; persistence in mean MSC:
37H10; 60H10; 92B05
1. Introduction
Since the famous differential system of marine fisheries was proposed by two mathematicians, Lotka [1] and Volterra [2], a large number of population systems, such as the predator–prey system, have been proposed. For the description of predation rate, scholars have widely proposed a series of functional responses, such as Holling I–III [3,4,5], Crowley–Martin [6], Beddington–Deangelis [7], etc. Moreover, Cosner [8] proposed a functional response to describe the hunting cooperation behavior of predators in 1999. There are many kinds of single population growth models, such as logistic growth [9,10], the Gomportz model [11], or the linear growth rate [12].
When a prey encounters a predator, it will produce anti-predator responses, such as camouflage [13,14,15], seeking refuge [16,17,18], etc. Faced with these anti-predation responses, predators also look for ways to restrain them, such as hunting cooperation. Hunting cooperation is a widespread phenomenon in nature. For example, lions hunt faster animals in a cooperative way [19,20]; wolves cooperate to take down creatures larger than themselves [21]. Many scholars have studied how hunting cooperation affects the dynamic behavior of the predator–prey model. The authors of [22] studied a diffusion prey–predator model with hunting cooperation; the results showed that the predators of the hunting cooperation model cause different bifurcations and the bistable phenomenon. Moreover, [23] also indicated that the hunting cooperation model causes bifurcations. A three-species food chain model with hunting cooperation was proposed in [24]. Ref. [25] investigated a stochastic predator–prey model with hunting cooperation and the conditions for the existence of a unique ergodic stationary distribution were given. These results suggest that hunting cooperation plays a vital role in describing the relationship between prey and predator.
Combined with the above observations, this paper considers a predator–prey model, associating the prey with a linear mass-action type functional response and the predator with hunting cooperation
where and denote the densities of prey and predator, respectively. In addition, other parameters are revealed in Table 1. All the parameter values are regarded as non-negative.
Table 1.
Biological significance of each parameter.
Ecosystems are unavoidably affected by some indeterminate environmental disturbances, such as changeable weather, unexpected natural disaster, etc. These can be viewed as white noise. Therefore, many scholars introduce random disturbance into their deterministic model [26,27,28,29,30]. When the perturbation form adopted by these scholars are and , then the dynamic behavior of the model is studied under the condition. Moreover, Qi et al. [25] and Liu et al. [31] proposed a stochastic predator–prey model with nonlinear perturbation of the form and . This kind of disturbance can be dependent on the squaring of the state variables x and y. If , some research results can be changed, such as the existence of a unique ergodic stationary distribution condition. Therefore, a predator–prey model with cooperative hunting behavior and nonlinear perturbation is considered in this paper
with the initial value
All parameter meanings of model are the same as those of model . and are independent standard Brownian motions. represent the intensities of the white noise on the prey and predator, respectively.
The feature of model is to be introduced into hunting cooperation and nonlinear stochastic interference, where the prey population aligns with the linear growth rate. Then the purpose of this paper is to study the effects of hunting cooperation and nonlinear stochastic disturbance on the dynamics of the model. In contrast to the model of hunting cooperation in the deterministic environment, we consider the effect of environmental perturbations on the predator–prey model. In comparison with [25], in addition to the stationary distribution, sufficient conditions for extinction and persistence in mean are also considered in the stochastic environment. Thus this improves the results of some related research work.
The frame of this paper is shown below. In Section 2, we introduce some basic lemmas and the well-posedness of model . In Section 3, we prove the main results of the paper, including extinction and persistence in mean. Furthermore, Section 4 concentrates on the unique ergodic stationary distribution of model . Several numerical simulations are given in Section 5.
2. Preliminaries
Lemma 1
([32]). For any initial value , the solution of model fulfills
Furthermore,
Lemma 2
([33]). Set
where y, ρ, , . Then we have such that , and it has the following property
Lemma 3.
For , , , we have
Theorem 1.
For any given , a unique positive solution of model exists on , and the solution will remain in with probability one.
Proof of Theorem 1.
Obviously, the coefficients of model satisfy the local Lipschitz condition. Therefore, for any given , model has a unique solution in , where represents the time of the explosion. To indicate the global property of this solution, we need to prove . Let be sufficient for any initial value lying within . For each , define the stopping time:
where . Obviously, is increasing as . Let , so a.s. Next, we only need to prove a.s. If , then there are two constants and such that
Then, there exists an integer such that Constructing a function V:
where . In view of Itô’s formula, we obtain
where
where
hence,
where is a positive number.
Thus, we obtain
Taking integral on the from 0 to and taking expectation, then
Let for , according to , we obtain . For each , it follows that or equals either l or , and we obtain
Therefore,
where is the indicator function of , let ; we obtain the contradiction. For the construction and calculation of V functions, see [34]. The proof is completed. □
Lemma 4.
For any given , there admits a constant , such that the solution (x(t),y(t)) of model satisfies
Proof of Lemma 4.
Define
Applying Itô’s formula yields
where We derive
Here
where
and are continuous adapted increasing processes on with . is a real-valued continuous local martingale with . Then
This suggests that there is a positive constant such that
for all . □
Theorem 2.
For any given , the solution (x(t),y(t)) of model is stochastically ultimate boundedness.
Proof of Theorem 2.
Define
Applying Itô’s formula yields
where
where is a positive constant, denoted as
Thus,
Utilizing Itô’s formula to results in,
Then, we obtain
which indicates that
According to Lemma 3, one has
Therefore, for any , set , according to Chebyshev inequality, we have
thus,
The proof is finished. □
3. Extinction and Persistence in Mean
Theorem 3.
If , then the predator goes to extinct, that is
Proof of Theorem 3.
In view of Itô’s formula, we derive
Integrating the both sides of results in
Taking the upper limit of equation , by calculating when , we yield
This completes the proof. □
Remark 1.
From the expression for , setting reasonable parameter values for k, δ and d, it is easy to understand that when is large, . Biologically speaking, this means that the predator population is extinct.
Lemma 5.
Providing the following auxiliary stochastic model,
we can easily obtain , and we can gain if holds. The prey can be persistent and model exists as a unique ergodic stationary distribution,
where κ is a constant such that .
Theorem 4.
If holds, then the predator can be persistent in the mean and satisfies
Proof of Theorem 4.
Utilizing Itô’s formula yields
where . Integrating from 0 to t and then dividing both sides of by t, one has
According to the ergodic theorem, we obtain
Taking the limit inferior of yields
It completes the proof. □
Remark 2.
Based on the expression for , we find that is greater than 0 when is small. It also shows that the predator has a lower bound, which is greater than 0. Biologically speaking, the predator population is persistent in the mean when the noise is low. Theorems 3 and 4 show that noise has an adverse effect on the predator population.
4. Stationary Distribution
Theorem 5.
Assume that , then model has a unique ergodic stationary distribution.
Proof of Theorem 5.
where
The diffusion matrix of is
Let
such that
which fulfills condition (B.1) of assumption (B) in [35]. In the following part, we construct a - function V:
where and such that
where
Then, define a -function V:
where , is the unique minimum point of .
According to Itô’s formula, this yields
where , such that .
Similarly,
Then,
Let
We can choose
such that
where .
Then we have
Using Itô’s formula leads to
where B is defined in . Therefore,
Construct a bounded closed set
In the set , we can choose
We first divide into four domains:
Next, we demonstrate that on .
Case 1. For any , due to
thus
In view of and , we can conclude that for all .
Case 2. For any , due to
one can obtain
where E is defined in .
According to , we can obtain that for all .
Case 3. For any , since
we can obtain
where D is defined in .
Following , we can conclude that for all
Case 4. For any , due to
one has
Together with , we can deduce that for all
Remark 3.
According to the expression of , it can be seen that when and are small, holds, the model has a unique ergodic stationary distribution, which also means that the populations are persistent.
5. Numerical Simulations
In this part, Milstein’s method [36] is used to simulate the conclusions. Considering the following discrete equation
where and obey the Gaussian distribution. The next three examples verify the results of this paper.
Case 1: The effect of white noise
In this case, we analyze the impacts of environmental disturbances on the prey and predator populations. Taking the parameter values in Table 2. Choosing We can obtain , and which satisfy the conditions of Theorems 4 and 5, respectively. This indicates the prey and predator populations are persistent (see Figure 1a,b). That is to say, when the white noise is small, it has less effect on the populations at this time. Furthermore, we see that model exists as a unique stationary distribution (see Figure 1c,d). Keeping the other parameters fixed, let . Notice that holds, which fulfills the condition of Theorem. We find the prey population is persistent (see Figure 2a) and the predator population is extinct (see Figure 2b). This shows the impact of white noise on is significant. That is, only the prey population is persistent.
Table 2.
The parameter values of model .
Figure 1.
(a,b) The persistence of model . (c,d) The probability density functions of and of model .
Figure 2.
(a,b) The paths of prey and predator .
Case 2: The effect of hunting cooperation coefficient .
In this case, we investigate the effects of hunting cooperation on populations. Let , other parameters remain unchanged as Case 1. We obtain , and . Through numerical simulation, we deduce that the prey and predator populations are persistent in mean (see Figure 3a,b) and the model exists as a unique stationary distribution (see Figure 3c,d). Furthermore, we see that as the hunting cooperation coefficient increases, the number of predator population also increases (see Figure 4a,b). That is to say, hunting cooperation is beneficial to the growth of predator populations.
Figure 3.
(a,b) The persistence of model with . (c,d) The probability density functions of and of model with .
Figure 4.
(a,b) The trajectories of and for model with different hunting cooperation coefficients.
6. Conclusions
Compared to other interrelated papers for deterministic or stochastic predator–prey models with hunting cooperation, this paper considers the dynamic behavior of the model from several aspects. At first, we prove the well-posedness of model . Secondly, we prove the extinction and persistence in mean. Moreover, we study the unique stationary ergodic distribution. The influence of nonlinear disturbance on the model is also illustrated. The main results are summarized as follows
- (1)
- If holds, the predator can be extinct.
- (2)
- When holds, the prey can be persistent and have a unique ergodic stationary distribution.
- (3)
- When , the predator can be persistent in the mean.
- (4)
- When , then model has a unique ergodic stationary distribution.
Besides, through several numerical simulations, we find that environmental disturbance can specifically impact the survival of the prey and predator populations. Even the predator population will become extinct when the noise is high. On the other hand, we discover that hunting cooperation positively affects the predator population. Practical and effective hunting cooperation is beneficial to the survival of the predator population.
In a word, we find that the predation rate is a saturated functional response when . However, this paper mainly studies the case that . Figure 4 shows the obvious influence of the predation cooperation coefficient on the model. In addition, according to Lemma 5, Theorem 4 and the construction of V function in proving Theorem 5, we can see the important influence of nonlinear disturbance on the model. Moreover, we overcome the difficulties in the construction of V function and the process of inequality expansion and contraction. The above description improves on previous studies.
Author Contributions
Writing—original draft preparation, Y.Z.; writing—review and editing, Y.Z. and X.M.; visualization, Y.Z. and X.M.; supervision, X.M.; project administration, X.M.; funding acquisition, X.M. All authors have read and agreed to the published version of the manuscript.
Funding
This work was supported by the Shandong Provincial Natural Science Foundation of China (ZR2019MA003), the Research Fund for the Taishan Scholar Project of Shandong Province of China, and the SDUST Research Fund (2014TDJH102).
Informed Consent Statement
Not applicable.
Data Availability Statement
Not applicable.
Conflicts of Interest
The authors declare no conflict of interest.
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