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# Persistence and extinction for stochastic delay differential model of prey predator system with hunting cooperation in predators

*Advances in Difference Equations*
**volume 2020**, Article number: 124 (2020)

## Abstract

Stochastic differential models provide an additional degree of realism compared to their corresponding deterministic counterparts because of the randomness and stochasticity of real life. In this work, we study the dynamics of a stochastic delay differential model for prey–predator system with hunting cooperation in predators. Existence and uniqueness of global positive solution and stochastically ultimate boundedness are investigated. Some sufficient conditions for persistence and extinction, using Lyapunov functional, are obtained. Illustrative examples and numerical simulations, using Milstein’s scheme, are carried out to validate our analytical findings. It is observed that a small scale of white noise can promote the survival of both species; while large noises can lead to extinction of the predator population.

## Introduction

Prey–predator (PP) interaction is one of the most extensively studied issues in ecological and mathematical literature; see [1–3]. The classic prey–predator models are mostly variations of the Lotka–Volterra model, which was proposed by Lotka [4] and Volterra [5]. Many studies have explored the effect of predator hunting cooperation on PP systems [6–8]. Most of these studies utilize deterministic models, which of course supported us with useful results for protecting species. However, the natural growth of populations is always affected by environmental stochastic perturbations which should be taken into account in the process of mathematical modeling. Ecological systems are often subject to environmental noise (e.g., temperature, precipitation), which is an important factor in ecosystems, to suppress a potential population explosion [9]. In reality, natural phenomena counter an environmental noise and usually do not follow deterministic laws strictly but oscillate randomly about some average values, so that the population density never attains a fixed value with the advancement of time [10, 11]. Therefore, it is useful to see how changes in environment affect the relationship between predator and prey populations. Many authors have investigated this phenomenon (see, e.g., [12–15]).

A key question in population biology is understanding the conditions under which populations coexist or go extinct. Extinction is one of the most important terms in population dynamics. A species is said to be extinct when the last existing member dies. Therefore, extinction becomes a certainty when there are no surviving individuals that can reproduce and create a new generation. In ecology, extinction is often used informally to refer to local extinction, in which a species ceases to exist in the chosen area of study, but may still exist elsewhere. There are a variety of causes that can contribute directly or indirectly to the extinction of species or group of species, such as lack of food and space or toxic pollution of the entire population habitat, competition for food to better adapted competitors, predation, etc. [16]. Due to the importance of this topic in population dynamics, our main goal in this paper is to investigate persistence and extinction in the considered model.

We should also mention here that time-delays (time-lags) have been extensively introduced into equations used in mathematical ecology to represent the time required for maturation period, reaction time, feeding time, etc. [17–19]. The presence of time-delay in a system greatly affects its stability. It can destabilize the equilibrium points and give rise to a stable limit cycle, oscillations grow, and enrich the dynamics of the model. Incorporating time-delays has been considered by many authors in prey–predator models and biological systems [20–23].

Hutchinson [23] first introduced the delay in a logistic differential equation. He proposed a delay differential model for a single species of the form

Here, *r* (>0) is the intrinsic growth rate and *K* (>0) is the carrying capacity of the population, and time-delay *τ* was considered as hatching time. \(\phi(\theta)\) is continuous on \(\theta\in[-\tau,0]\). (This equation is referred to as Hutchinson’s equation or delayed logistic equation.)

A simple general two-dimensional delayed model of interaction between prey \(x(t)\) and a generalist predator \(y(t)\) is represented by

The function \(\mathcal{G}_{1}(x(t-\tau_{1}),K)\) is logistic per capita growth rate of prey, where *K* is the environmental carrying capacity, and \(\mathcal{G}_{2}(y)\) is the per capita growth rate of predator. \(\mathcal{F}(x(t))\) and \(\mu\mathcal{F}(x(t))\) are 0 extra responses of predator for a particular prey, and *μ* is the conversion efficiency (\(0<\mu<1\)). Time-delay \(\tau_{1}\) represents the gestation period of the prey or reflects the impact of density-dependent feedback mechanism [24]. Time-delay \(\tau_{2}\) is incorporated in the functional response of predator equation to represent the reaction time with the prey. In reality, the reproduction of predators is not immediate to the consumption of prey, as there is some discrete time lag necessary for prey gestation [17].

There exist various and extensive studies of the dynamics of the delayed PP model; see, e.g., [25–28]. In [27], the authors investigated the complex dynamics of a delayed PP system with cooperation among the prey species, they have considered time delays in the growth components for each of the species. Berec [28] assumed a Holling type II functional response of the form \(\mathcal{F}(x,y)= \frac{\sigma(y) x}{1+c(y) \sigma(y) x}\), where *σ* is the consumption rate of prey by their predator and *c* is the handling time of the predator, both *σ* and *c* are not constant quantities. Alves *et al.* [6] considered consumption rate depending on the predator density to implement predator cooperation for searching and capturing the prey. Assuming that \(\alpha>0\) is the cooperative ‘hunting’ parameter, with functional response of the form \(\mathcal{F}(x,y)= \frac{(1+\alpha y)x}{1+c(1+\alpha y)x}\), the suggested model takes the form

where \(\delta>0\) is the death rate of predator and \(a>0\) is an intra-specific competition rate for predators. The description of the model parameters is presented in Table 1.

It is known that deterministic models, such as (2), are stable with a cyclic behavior in the common period for the sizes of species populations. However, in practice, stochastic variations will occur in the values of *x* and *y*, which may produce a qualitatively different behavior. These variations may lead to an extinction of the predator as a result of a possible extinction of the prey. Deterministic models may be inadequate for capturing the exact variability in nature. Then, stochastic models are required for an accurate approximation of the dynamics of such interactions. The random fluctuations result in changing some degree of parameters in the deterministic environment. Many authors have studied stochastic population models and revealed the effects of environmental noises on the dynamics of population models (see [14, 29–31]). Hattaf *et al.* [14] studied the impact of random noise in the dynamics of delayed SIR epidemic model. They deduced a threshold parameter to determine the extinction and persistence of the disease. However, in [32], the authors studied the effect of environmental fluctuations of a delayed Harrison-type PP model, they analyzed the impact of the combination of delay and noise in the dynamical behavior of the model. In [33], the authors studied the effect of environmental fluctuations on a competitive model for two phytoplankton species where one species liberate toxic substances by considering a discrete time delay parameter in the growth equations of both species.

In this paper, we consider and investigate a stochastic version of PP system (2), so that

\(B_{1}(t)\), \(B_{2}(t)\) are standard independent Wiener processes defined on a complete probability space \((\varOmega,\mathcal{A}, \{ \mathcal{A}\}_{t \geq0},\mathbf{P})\) with a filtration \(\{ \mathcal{A}\}_{t \geq0}\) satisfying the usual conditions; and \(\sigma_{1}\), \(\sigma_{2}\) are the positive intensities of white noises.

The rest of this paper is organized as follows. In Sect. 2, we briefly investigate the qualitative behavior for deterministic model (2). In Sect. 3, we study *stochastic delay differential equations* (SDDEs) (3). Sufficient criteria for global existence, stochastically ultimate boundedness, persistence in mean, and extinction of the system are obtained. Some numerical simulations to validate our mathematical findings are given in Sect. 4, and finally the essential results and their ecological explanations are summarized in Sect. 5.

## Deterministic analysis

Herein, we study the qualitative behavior of the deterministic model. Under some restrictions on the parameters of system (2), there exist three equilibrium points \(\mathcal{E}_{0}\), \(\mathcal{E}_{1}\), and \(\mathcal{E}^{*}\) (see Appendix). We linearize the system around \(\mathcal{E}^{*}=(x^{*},y^{*})\), so that \(x(t)=x^{*}+\tilde{x}(t)\), \(y(t)=y^{*}+\tilde{y}(t)\), then we have

where the coefficients are given by

The characteristic equation of linearization model (4) is given by

Let us define a threshold parameter \({\mathcal{R}_{0}^{d}}= \frac{\mu K}{\delta(1+cK)} \).

### Remark 1

The extinction equilibrium \(\mathcal{E}_{0}\) is always a saddle point, and the boundary equilibrium point \(\mathcal{E}_{1}\) is locally asymptotically stable if \({\mathcal{R}_{0}^{d}}\equiv \frac{\mu K}{\delta (1+cK)} <1\).

To gain insight regarding interior equilibrium \(\mathcal{E}^{*}\), we consider different values of time-lags \(\tau_{1}\) and \(\tau_{2}\): (i) \(\tau_{1}=\tau_{2}=0\), (ii) \(\tau_{1}>0\), \(\tau_{2}=0\), (iii) \(\tau_{1}=0\), \(\tau_{2}>0\), (iv) \(\tau_{1}>0\), \(\tau_{2}>0\).

• Case (i): When \(\tau_{1}=\tau_{2}=0\), equation (5) becomes

Thus all the roots of (6) have negative real parts if

• Case (ii): When \(\tau_{2} = 0\), \(\tau_{1} > 0\), equation (5) becomes

Let \(\lambda=i\omega\) be the root of (7), then it follows that

which leads to

where \(c_{1}=(a_{1}+a_{4})^{2}-2(a_{1}a_{4}-a_{2}a_{5})-a_{3}^{2}\) and \(c_{2}=(a_{1}a_{4}-a_{2}a_{5})^{2}-(a_{3}a_{4})^{2}\). Thus, equation (9) has at least one positive root \(\omega_{1}\) if \(c_{2}<0\), therefore we have

where \(j=0,1,2,\dots\). Thus, \(\mathcal{E}^{*}\) remains stable for \(\tau_{1} <\tau_{1}^{\prime}\) and unstable for \(\tau_{1} >\tau_{1}^{\prime}\) such that \(\tau_{1}^{\prime}=\min\{\tau_{1,j}\}\).

• Case (iii): For \(\tau_{1} = 0\), \(\tau_{2} > 0\), in the same manner, we have

where \(j=0,1,2,\dots\). Therefore, \(\mathcal{E}^{*}\) remains stable for \(\tau_{2} <\tau_{2}^{\prime}\) and unstable for \(\tau_{2} >\tau_{2}^{\prime}\) such that \(\tau_{2}^{\prime}=\min\{\tau_{2,j}\}\) provided that \((a_{1}a_{4}+a_{3}a_{4})^{2}<(a_{2}a_{5})^{2}\).

• Case (iv): When \(\tau_{1},\tau_{2}>0\), we assume first that \(\tau_{1}\) is varying and \(\tau_{2}\) is fixed in its stable interval \(\tau_{2}\in[0,\tau'_{2})\). Assume that there exists a real number \(\omega>0\) such that \(\lambda =i\omega\) is a root of characteristic equation (5), then separating real and imaginary parts, we get

Squaring and adding both sides yields

where

Equation (13) is a peculiar equation in a complicated form, it is not easy to presume about the nature of the roots. Thus, by applying Descartes rule of signs, we can say that (13) has at least one positive root \(\omega_{0}\) if

In this case, we have

where \(j=0,1,2,\dots\). Thus, \(\mathcal{E}^{*}\) remains stable for \(\tau _{1}<\tau_{1}^{*}\) such that \(\tau_{1}^{*}=\min\{\tau_{1,j}\}\) as in (14).

To check the transversality condition of Hopf bifurcation, we fix \(\tau _{2}\) in its stable interval and differentiate equations (12) with respect to \(\tau_{1}\). Then, substituting \(\tau_{1}=\tau_{1,0}\) and \(w=w_{0}\), we have

where

From (15), we get

Assume that

then a Hopf bifurcation occurs for \(\tau_{1}=\tau_{1,0}\).

Therefore, for Case (iv), we arrive at the following theorem.

### Theorem 1

*Suppose that*\(\mathcal{E}^{*}\)*exists for system* (2) *and*\((H_{1})\)*–*\((H_{3})\)*hold*, *such that*\(\tau_{2}\in[0,\tau_{2}^{\prime})\), *then there exists a positive threshold parameter*\(\tau_{1}^{*}\)*such that the interior equilibrium*\(\mathcal{E}^{*}\)*is locally asymptotically stable for*\(\tau_{1}<\tau_{1}^{*}\)*and unstable for*\(\tau_{1}>\tau_{1}^{*}\). *Furthermore*, *system* (2) *undergoes a Hopf bifurcation at*\(\mathcal{E^{*}}\)*where*\(\tau_{1}=\tau_{1}^{*}\).

If \(\tau_{1}\) is fixed in its stable interval and \(\tau_{2}\) varies, we arrive at the following remark.

### Remark 2

If \(\tau_{1}\in[0,\tau_{1}^{\prime})\), there exists a threshold parameter \(\tau _{2}^{*}\) such that the interior equilibrium \(\mathcal{E}^{*}\) is locally asymptotically stable for \(\tau_{2}<\tau_{2}^{*}\) and unstable for \(\tau _{2}>\tau_{2}^{*}\), where \(\tau_{2}^{*}=\min\{\tau_{2,j}\}\) is given by

## Stochastic analysis

In this section, we extend the analysis to the stochastic model, where we incorporate white noise into the growth equations of both prey and predator. Recall model (3)

We assume that \(\kappa\in[-\tau,0]\), \(\tau=\max\{\tau_{1},\tau_{2}\}\), i.e., \((x_{0},y_{0})=(\phi_{1},\phi_{2})^{T} \in C([-\tau,0],{\mathbb {R}}_{+}^{2})\) with \({\mathbb {R}}_{+}^{2}=\{(x,y)\in{\mathbb {R}}^{2}: x>0,y>0\}\), if \((x,y) \in{\mathbb {R}}^{2}\), its norm is denoted by \(|(x,y)|=\sqrt{x^{2}+y^{2}}\). The initial value of system (17) becomes

Now, we investigate the existence and uniqueness of positive solutions.

### Existence and uniqueness of positive solution

In order to prove that the model of SDDEs (17) has a unique global solution (i.e., no explosion in a finite-time) for any given initial condition, the coefficients of system (17) are generally required to satisfy the linear growth condition and local Lipschitz condition [34, 35].

To show that model (17) has a global positive solution, let us firstly prove that the model has a positive local solution by making the change of variables. Then we prove that this solution will also not explode to infinity at any finite time by using a suitable stochastic Lyapunov functional.

### Theorem 2

*Let the coefficients of system* (17) *be locally Lipschitz continuous*, *then for any given initial data* (18) *there is a unique positive solution*\((x(t),y(t))\)*of system* (17) *on*\(t\geq -\tau\), *and the solution will remain in*\({\mathbb {R}}_{+}^{2}\)*with probability one*.

### Proof

Let \(n(t)=\ln x(t)\), \(p(t)=\ln y(t)\), we have the system

for any initial values \(n(\kappa)=\ln x(\kappa)\), \(p(\kappa)=\ln y(\kappa)\), \(\kappa\in[-\tau,0]\). It is easy to show that all the coefficients of (19) satisfy the local Lipschitz condition; therefore, there is a unique local solution \((n(t),p(t))\) on \([-\tau ,\tau_{e})\), where \(\tau_{e}\) is explosion time [36]. By Ito’s formula, we can see that \(x(t)=e^{n(t)}\), \(y(t)=e^{p(t)}\); therefore, there is a unique local positive solution of (17) for any given initial value \((x_{0},y_{0})\in{\mathbb{R}}_{+}^{2}\).

To show that this solution is global, we need to show \(\tau_{e}=\infty\) a.s. (almost surely). Let \(l_{0}>0\) be sufficiently large so that \((x(t),y(t))=\{(\phi _{1}(t),\phi_{2}(t)):-\tau\leq t \leq0\} \in C([-\tau,0];{\mathbb {R}}_{+}^{2})\) all lie within the interval \([\frac{1}{l_{0}},l_{0}]\). Now, for each integer \(l\geq l_{0}\), define the stopping time \(\tau_{l}=\inf\{t\in[-\tau,\tau_{e}):x(t)\notin(\frac {1}{l},l),y(t)\notin(\frac{1}{l},l)\}\), let \(\inf\phi=\infty\). \(\tau_{l}\) is increasing with *l* and let \(\tau _{\infty}=\lim_{l\rightarrow\infty}\tau_{l}\), then \(\tau_{\infty}\leq\tau _{e}\). By showing \(\tau_{\infty}=\infty\) a.s., we want to conclude that \(\tau_{e}=\infty\) a.s. If this assertion is erroneous, then there exists a pair of constants \(T>0\) and \(\epsilon\in(0,1)\) such that \(P\{\tau _{\infty}\leq T\}>\epsilon\). Therefore, there is an integer \(l_{1}\geq l_{0}\) such that

Define a \(\mathcal{C}^{2}\)-function \(V(x,y):{\mathbb {R}}_{+}\times{\mathbb {R}}_{+}\rightarrow{\mathbb {R}}_{+}\) by

Clearly, this function is nonnegative for all \(x,y \geq0\). Let \(l \geq l_{0}\) and \(T>0\) be arbitrary. For \(0 \leq t \leq\tau_{l} \land T\), by Itô’s formula for *V*, we get

where *γ* is a positive number. Therefore

Taking expectation of both sides implies

Set \(\varOmega_{l}=\{\tau_{l}\leq T\}\) for \(l\geq l_{1}\) and by the virtue of (20), we obtain \(\mathcal{P}(\varOmega_{l}) \geq\epsilon\). For every \(\eta\in\varOmega_{l}\), \(x(\tau_{l},\eta)\) and \(y(\tau_{l},\eta)\) equal either *l* or \(\frac{1}{l}\), Consequently, \(V(x(\tau_{l},\eta),y(\tau_{l},\eta))\) is no less than either \(l-\log l -1\) or \(\frac{1}{l}+\log l -1\). Therefore, we can get

It follows from (22) that

where \(1_{\varOmega_{l}}\) is the indicator function of \(\varOmega_{l}\). Letting \(l\rightarrow\infty\) leads to a contradiction that \(\infty> V(x(0),y(0))+\gamma T=\infty\). Therefore, we get \(\tau_{\infty}=\infty\) a.s. □

### Stochastically ultimate boundedness

After discussion on the existence and uniqueness of positive solution of SDDEs (17), we show that the positive solution does not explode to infinity in a finite time.

### Definition 1

([37])

The solution \((x(t), y(t))\) of SDDEs (17) is said to be stochastically ultimately bounded a.s. if, for any \(\epsilon\in (0,1)\), there is a positive constant \(\varphi=\varphi(\epsilon)\) such that \(\lim_{t\rightarrow\infty}\sup\mathbf{P}\{|(x(t),y(t))| > \varphi\} < \epsilon\).

### Theorem 3

*If any*\(\theta\in(0,1)\)*and*\(\mu\theta(\mu K e^{\tau_{2}}-\delta )>a\), *and there exists a positive constant*\(N=N(\theta)\), *which is independent of the initial value* (18), *such that*

*then the positive solution*\((x(t),y(t))\)*of system* (17) *is stochastically ultimately bounded*.

### Proof

To prove (23), define

Applying Itô’s formula gives

Denote

where

for \((x,y)\in{\mathbb {R}}_{+}^{2}\). Note that \(H(x,y)\) is bounded in \(\mathbb{R}_{+}^{2}\). Hence, we have

Thus, we obtain

Again, using Itô’s formula, we have

If \(\mu\theta(\mu K e^{\tau_{2}}-\delta)>a\), then

which implies that

We get

Since \(\lim_{t\rightarrow\infty}\sup \mathbf{E}|x(t),y(t)|^{\theta}\leq N\), then, for any \(\epsilon>0\), let \(\varphi=N^{2}/\epsilon^{2}\). By Chebyshev’s inequality

we obtain

Thus, model (17) is stochastically ultimately bounded. □

### Persistence

Under certain restrictions on the parameter values with small intensities of white noise, we investigate the conditions under which the persistence of system SDDEs (17) occurs.

Let us first define persistence in the mean of a dynamical system.

### Definition 2

The species \(y(t)\) is said to be persistent (see [16]) in the mean if

In order to show the persistence, we go through some necessary lemmas.

### Lemma 1

([38])

*Let*\(M=\{M_{t}\}_{t\geq0}\)*be a real*-*valued continuous local martingale vanishing at*\(t=0\). *Then*

*and also*

*where*\(\langle M,M \rangle_{t}\)*denotes the quadratic variation of**M*.

### Lemma 2

([39])

*Let*\(y(t) \in\mathbb{C}[[0,\infty) \times \varOmega, (0,\infty) ]\). *If there exist positive constants*\(\lambda _{0}\), *λ**such that*

*for all*\(t \geq0\), *where*\(F\in\mathbb{C}[[0,\infty)\times\varOmega, \mathbb{R}]\)*and*\(\lim_{t\rightarrow\infty}\frac{F(t)}{t}=0\)*a*.*s*., *then*

Let us define a threshold parameter \(\mathcal{R}_{0}^{s}\) as follows:

### Theorem 4

*Let*\((x(t),y(t))\)*be the solution of SDDEs* (17) *with initial conditions* (18). *Assume that*\(2r>\sigma_{1}^{2}\), *then system* (17) *will be persistent if*\(\mathcal{R}_{0}^{s}>1\), *so that*\(\lim\inf_{t\rightarrow\infty}\frac{1}{t} \int_{0}^{t}y(s)\,ds>0\), *a*.*s*.

### Proof

Using Itô’s formula to the first equation of system (17) yields

Integrating inequality (27) from 0 to *t* results in

Thus,

where

it follows from Lemma 1 that

Note

Therefore, \(\lim_{t\rightarrow\infty} \int_{t}^{t+\tau_{1}}\frac{x(s-\tau _{1})\,ds}{t}=0\). Moreover, \(\lim_{t\rightarrow\infty} \int_{0}^{\tau_{1}} \frac{x(s-\tau _{1})\,ds}{t}=\lim_{t\rightarrow\infty}\frac{\int_{-\tau_{1}}^{0}\phi_{1} (t)\, dt}{t}=0\). Thus, we obtain

By Itô’s formula, we get

so we have

Therefore,

Let

utilizing Itô’s formula, we obtain

According to (32), we have

• Case (1): When \(x(t)\leq1\), then

Substituting (30) into (35), we obtain

Therefore,

where

Since \(2r>\sigma_{1}^{2}\) and \(\mathcal{R}_{0}^{s}>1\), this implies that \(\lambda>0\). Using this together with (29) and Lemma 2, one obtains

• Case (2): When \(x(t)>1\), from (33) we can get

Since \(\mathcal{R}_{0}^{s}>1\), and following a similar proof to Case (1), we can obtain

This completes the proof. □

### Extinction

Extinction is one of the most important terms in population dynamics. A species is said to be extinct if there is no existing member in the habitat. Although, under some conditions, the solution to the original deterministic DDEs (2) may be persistent, the solution to the associated SDDEs will become extinct with probability one. This reveals the important fact that the environmental noise may make the population extinct. Now, we establish the conditions under which extinction of predator population occurs.

### Definition 3

The species \(y(t) \) is said to go to extinction with probability one if \(\lim_{t\to\infty} y(t)=0 \) a.s.

### Theorem 5

*Let*\(a>\mu\alpha\). *If*\(\mathcal{R}_{0}^{s}<1\), *then the solution*\((x(t),y(t))\)*of model* (17), *for any given initial value* (18), *satisfies*

*which means*\(\lim_{t\to\infty} y(t)=0 \)*exponentially almost surely*. *In other words*, *the predators die out with probability one*. *In addition*,

### Proof

According to (32), we have

since \((a>\mu\alpha)\), then

Thus, we have two cases.

• When \(x(t)\leq1\), according to (42), we can get

therefore, we have

So,

where

In view of the strong law of large numbers of Brownian motion, we can easily obtain that

Thus, it follows from (45) and since \(\mathcal{R}_{0}^{s}<1\)

• When \(x(t)>1\), by (42), we have

then

Therefore,

where

In view of the strong law of large numbers of Brownian motion, we can easily obtain that

Therefore,

which implies that \(y(t)\) tends to zero exponentially with probability one,

By taking the limit on both sides of (28) and (30) at the same time, we can get

This completes the proof. □

## Numerical simulations

In this section, we attempt to validate the mathematical results obtained in the previous sections. We utilize Milstein’s scheme with a strong order of convergence one discussed in [40]. The corresponding discretization system to SDDEs (17) is

Here, \(\xi_{1,n}\) and \(\xi_{2,n}\) are mutually independent \(N(0,1)\) random variables, \(m_{1}\), \(m_{2}\) are integers such that the time delays can be expressed in terms of the step-size as \(\tau_{1} = m_{1}h\) & \(\tau _{2}=m_{2}h\). We provide some numerical simulations of the stochastic model (17) and its corresponding deterministic model (2).

Taking the parameter values \(\alpha=0.12\), \(a=0.08\), \(c=0.3\), \(r=1\), \(\mu=0.9\), \(\delta=0.39\), \(K=1\), \(\sigma_{1}=\sigma_{2}=0.001\), and \(\tau _{1}=\tau_{2}=0.1\), Fig. 1 shows the persistence of system (17) with initial values \((0.4,0.8)\) such that \(\mathcal {R}_{0}^{s}=\frac{\mu K}{\tilde{\delta}(1+c)}=1.78>1\). If we increase the hunting cooperative parameter *α* as \(\alpha =1.2\) keeping all other parameters the same, we can observe that the predator dominates the prey population; see Fig. 1 (right). The population densities vary around the deterministic steady state values.

Figure 2 shows the impact of small white noise on dynamics of the system. The figure displays a periodic solution of the deterministic system when \(\tau_{1}=\tau_{1}^{*}=0.8\) & \(\tau_{2}= 0.1<\tau _{2}^{*}\), \(a=0.08\), \(\delta=0.19\), \(\alpha=1.6\), \(c=0.6\), \(K=1\), \(\mu =0.9\), \(r=1\). However, with small noises \(\sigma_{1}=0.004\) & \(\sigma _{2}=0.0001\), where \(\mathcal{R}_{0}^{s}=2.96>1\), we can observe that the periodic solution is damped in both population densities. If the intensity of white noises increases, then the predator goes to extinction, as \(\mathcal{R}_{0}^{s}<1\).

Figure 3 shows that the population of prey varies around the deterministic steady state value (left), and the predator population goes to extinction at \(t=70\) with the deterministic model; while with white noise at \(t=20\) (right). In this simulation, we choose initial values \((x(0),y(0))=(0.8,0.4)\) and parameter values \(a=0.19\), \(\mu=0.8\), \(\alpha=0.1\), \(c=0.8\), \(K=1\), \(\delta=0.59\), \(r=1\), \(\sigma_{1}=0.001\), \(\sigma_{2}=0.023\), \(\tau_{1}=\tau _{2}=0.1\). Then \(\mathcal{R}_{0}^{s}=0.75<1\). According to Theorem 5, the solution of (17) obeys \(\lim\sup_{t\rightarrow\infty }\frac{\ln y(t)}{t}<0\) a.s., that is, y(t) tends to zero exponentially with probability one. On the other hand, for deterministic model (2), the condition of \(\mathcal{R}_{0}^{d}= \frac{\mu K}{\delta (1+cK)}=0.7 <1\) is satisfied, so the boundary equilibrium point \((\mathcal{E}_{1},0)=(1,0)\) is a stable point.

Figure 4 shows that the environmental noise plays an important role in extinction of the predator population. When we increase the intensity of Brownian motion \(B_{2}(t)\) to \(\sigma_{2}=0.1\), \(c=0.3\), \(\mu=0.6\), and \(\delta=0.4\) with other parameters as in Fig. 3, the extinction occurs in the predator population when \(\mathcal{R}_{0}^{s}=0.92<1\). This means \(y(t)\) of system (17) will go to extinction with probability one. However, with the same parameters, deterministic model (2) has an interior stable equilibrium \(\mathcal{E}^{*}=(0.82,0.22)\). Therefore, the population \(y(t)\) becomes extinct exponentially with probability one when white noise increases.

### Remark 3

Extinction of the predator population possibly occurs when the intensity of white noise is large, such that \(\mathcal{R}_{0}^{s}<1\). This would not happen in deterministic system (2) without noises (see Fig. 4). If the predator death rate is large, extinction of the predators can also occur in deterministic model (2); while with a small noise in the stochastic model, extinction of the predator population occurs faster than in the deterministic model (see Fig. 3).

## Discussion and conclusion

In this paper, we studied the dynamics of SDDEs for a prey–predator system with hunting cooperation in predators. We investigated the effect of environmental fluctuations on the model. We first studied the qualitative behaviors of the deterministic model through local stability analysis of the interior equilibrium points and obtained critical values of delays, where the Hopf bifurcation occurs for the deterministic model. We then considered how environmental fluctuations affect extinction of predator and prey populations. We established the existence and uniqueness of global positive solution and the stochastically ultimate boundedness of the system. We have shown the effect of environmental noises on the persistence and possible extinction of prey and predator populations. We verified the obtained analytical results with supportive numerical simulations using Milstein’s scheme. Conditions under which persistence of the system occurs have been established when \(\mathcal{R}_{0}^{s}>1\); while with \(\mathcal{R}_{0}^{s}<1\), extinction of the predator occurs. It can also be observed that the extinction of the predator population occurs more rapidly for stochastic system (17) when the intensity of white noise increases, see Figs. 3–4. It has also been shown numerically that the predator population dominates the prey population as cooperative hunting parameter increases (see Fig. 1).

Our main findings, theoretically and numerically, are all represented in terms of the system parameters and the intensity of randomly fluctuating driving forces. This indicates that time-delay and white noise have a considerable impact on the dynamics and presence of prey and predator populations. For future investigation, one may extend our results with other kinds of environmental noise such as color noise [41] or telephone noise [42].

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### Acknowledgements

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Data sharing not applicable to this paper as no datasets were generated or analyzed during the current study.

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This work is generously funded by PhD Program, United Arab Emirates University (UAE).

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Correspondence to Fathalla A. Rihan.

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## Appendix: Preliminaries and analysis for deterministic model

### Appendix: Preliminaries and analysis for deterministic model

There are three types of equilibrium points for deterministic system (2): (i) Trivial equilibrium point \(\mathcal{E}_{0} \equiv (0,0)\); (ii) Axial equilibrium point \(\mathcal{E}_{1} \equiv(K,0)\); and (iii) Interior equilibrium point \(\mathcal{E}^{*} \equiv(x^{*},y^{*})\). Here,

\(y^{*}\) is a positive real root of the equation

where

Equation (56) must have at least one positive real root if \(c\delta<\mu\). Therefore, the existence of the coexisting equilibrium \(\mathcal{E}^{*}\) assumes restrictions on the parameters so that

### Lemma 3

*The positive solution of deterministic model* (2), \((x(t),y(t))\), *satisfies*

*for*\(\tau_{1},\tau_{2}>0\)*with*\(\mu Ke^{r \tau_{2}}>\delta\).

### Proof

With the positive initial condition \((x(0),y(0))\), we can verify that the solution \((x(t),y(t))\) of system (2) is positive. From the first equation of system (2) we can consider

Integrating both sides of (59) from \(t-\tau_{1}\) to *t*, we have

Using (60) and from the first equation of (2), we get

i.e., for \(\epsilon>0\), there exists \(T_{1}>0\) such that \(x(t)\leq K e^{r\tau_{1}}+\epsilon\) for all \(t>T_{1}\).

Similarly, from the second equation of (2), we get

Thus, \(y(t)\leq\xi+\epsilon\) for all \(t>T_{2}\), conclusion of this theorem can be achieved by letting \(\epsilon\rightarrow0\). □

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Rihan, F.A., Alsakaji, H.J. Persistence and extinction for stochastic delay differential model of prey predator system with hunting cooperation in predators.
*Adv Differ Equ* **2020, **124 (2020). https://doi.org/10.1186/s13662-020-02579-z

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### Keywords

- Extinction
- Hunting cooperation
- Milstein’s numerical scheme
- Persistence
- Stochastic prey–predator model
- Time-delay