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Single-species population models with stage structure and partial tolerance in polluted environments


  • We propose stage-structured single-species population models with psychological effects and partial tolerance in polluted environments in this paper. First, the conditions of extinction and the time for extinction are investigated respectively. Especially, the time for extinction takes longer as the value of the psychological effects increases. Then the weak persistence in the mean around the pollution-free equilibrium and the stochastic permanence have been derived under some moderate conditions. Further, the existence of a periodic solution for the periodic single-species population has been determined. The corresponding numerical simulations verify the efficiency of the main theoretical results.

    Citation: Xingmin Wu, Fengying Wei. Single-species population models with stage structure and partial tolerance in polluted environments[J]. Mathematical Biosciences and Engineering, 2022, 19(9): 9590-9611. doi: 10.3934/mbe.2022446

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  • We propose stage-structured single-species population models with psychological effects and partial tolerance in polluted environments in this paper. First, the conditions of extinction and the time for extinction are investigated respectively. Especially, the time for extinction takes longer as the value of the psychological effects increases. Then the weak persistence in the mean around the pollution-free equilibrium and the stochastic permanence have been derived under some moderate conditions. Further, the existence of a periodic solution for the periodic single-species population has been determined. The corresponding numerical simulations verify the efficiency of the main theoretical results.



    Pollution in ecological environments has always been a widespread concern of the public. With the rapid development of the modern industrial society, the environmental pollution caused by human activities has become an issue and it has series impacts on the survival of single-species populations in the environment. Under the assumption that the growth rate of a local population was linearly dependent on the absorbed toxicant concentration, Hallam et al. [1] studied the ecological impact of toxicant concentration on single-species populations for the first time. Later, single-species population models gradually attracted the attentions of researchers around the world. For example, Ma et al. [2] considered the survival threshold of small populations when the capacity of the environment was limited, and they observed the changes in the environment by uptake and egestion of organisms. Wang et al. [3] later generalized the results in [2] into periodic toxicant inputs and discussed the permanence of single-species populations. After two decades, motivated by Hallam's model in [1], Liu et al. [4] investigated a single-species model in a polluted closed environment with pulsed toxicant inputs; they found that impulsive toxicant inputs led to periodic behaviors and oscillations for their solution. Then He and Wang [5] followed Hallam's model and assumed that newborns carried some amount of toxicant within each living organism that is diffused into the environment after death, they further analyzed the sufficient conditions for uniform persistence, weak persistence in the mean and the extinction of a single-species population. By simplifying Hallam's model, Liu and Wang [6] investigated the thresholds for local extinction and weak persistence in the mean for single species by using a deterministic model and stochastic model respectively. In [7], they continued to study the survival threshold for a stochastic generalized logistic model, stochastic Leslie model and stochastic Gallopin model; they obtained that the intensity of white noise made sense. Further, survival thresholds were extensively discussed in [8,9,10] for a single-species model with Markov switching and pulsed toxicant inputs in a polluted environment with two types of noises, for an n-species stochastic Lotka-Volterra cooperative model and for a stochastic cooperative species model in a polluted environment, respectively. Moreover, single-species population models with partial pollution tolerance and psychological effects in a polluted environment were respectively paid more attention in [11,12,13,14,15]. Especially, Wei and Chen [12] proposed a single-species population model with psychological effects in a polluted environment:

    dx(t)=[x(bd)cx2αxCoλxCe1+βC2e]dtσxCe1+βC2edB(t),dCo(t)=[kCe(g+m+b)Co]dt,dCe(t)=[uehCe]dt, (1.1)

    where x(t) is the density of a single-species population in a polluted environment at time t; Co(t) and Ce(t) are the concentration of toxicants in the organism, and the concentration of toxicants in the environment at time t respectively. They derived the sufficient conditions for local extinction, weak persistence in the mean and stochastic permanence; they also found that psychological effects had an impact on the density of populations.

    In this paper we consider stage-structured single-species population models because there exist differences between juveniles and adults at the distinct stages in their lifetimes. Usually, in a population, adults produce juveniles, hunt for juveniles and protect juveniles against attacks from their predators; juveniles cannot produce newborns and have less experience for hunting untill they turn into adults. Motivated by the previous contributions in [16,17,18] and the assumptions proposed in [12,16], we establish a stage-structured population model with pollution and psychological effects as follows:

    dJ(t)=[aAeJJrJCoJαJcJJ2]dt,dA(t)=[αJeAArACoAcAA2λg(A,Ce)]dtσg(A,Ce)dB(t),dCo(t)=[kCegComCobCo]dt,dCe(t)=[uehCe]dt, (1.2)

    where J(t) and A(t) respectively indicate the densities of juveniles and adults in a population at time t; g(A,Ce) describes the assumptions that adults are directly affected by a heavily polluted environment in a nonlinear form, and by a lightly polluted environment in a linear form as follows:

    g(A,Ce)={ACe1+βC2e,Ce>c(heavypollution),ACe,Ce<c(lightpollution). (1.3)

    In other words, the nonlinear form in Eq (1.3) means that adults produce the psychological effects with a rate β to avoid being harmed by pollution because adults with good vertebrate organs and highly differentiated nervous systems can transmit the information on their surroundings to their nervous systems well; the single-species population is in a heavily polluted environment when Ce>c is valid, and the population is in a lightly polluted environment when Ce<c holds; here, c is a threshold value for a polluted environment. We further assume that juveniles are indirectly affected by the environmental pollution, and that juveniles are produced by adults at a constant rate a; eJ and eA are the natural mortality rates of juveniles and adults respectively; rJ and rA refer to the loss rates for the juveniles and adults respectively; α indicates the conversion rate from juveniles to adults; cJ and cA are the intra-specific competition rates for juveniles and adults; λ denotes the contact rate between adults and toxicants in the environment. Because the contact rate is always affected by weather conditions, temperature and other types of noise, the constant contact rate λ is replaced by a random variable ˜λ=λ+σξ(t) with white noise ξ(t) satisfying ξ(t)dt=dB(t), where B(t) is a scalar standard Brownian motion process. β represents the inhibition rate or psychological effects of adults when they are surrounded by the polluted environment; it also describes the sensitivity of adults to the polluted environment; k is the uptake rate from the polluted environment; g,m and b express the loss rates due to egestion, metabolic process and reproduction, respectively; ue(t) is regarded as the external toxicant input into the environment; h represents the natural purification rate of the environment itself.

    Theorem 2.1. Model (1.2) with heavy pollution has a unique solution (J(t),A(t),Co(t),Ce(t)) for any (J(0),A(0),Co(0),Ce(0)) and t0; the solution will remain in R4+ with a probability of 1.

    Proof. Since the coefficients of System (1.2) satisfy the local Lipschitz condition [19], there is a unique local solution (J(t),A(t),Co(t),Ce(t))R4+,t[0,τe) (where τe is the explosion time) for any initial value (J(0),A(0),Co(0),Ce(0))R4+. In order to prove that this solution is global, we only need to prove that τe=. We assume that l0 is a sufficiently large integer such that (J(0),A(0),Co(0),Ce(0)) is in the interval [1l0,l0]; for each integer ll0, we define a stopping time [19]:

    τl=inf{t[0,τe):min{J(t),A(t),Co(t),Ce(t)}1lormax{J(t),A(t),Co(t),Ce(t)}l}. (2.1)

    Throughout this paper, we set inf=. It is apparent that τl increases with respect to l. We set τ=limlτl; therefore, ττe holds almost surely. We claim that τ= is valid almost surely. The proof goes by contradiction from now on. If the statement is false, then there exists a pair of constants T>0 and ε(0,1) such that P{τT}>ε. Hence there exists an integer l1l0 such that

    P{τlT}ε,forallll1. (2.2)

    We define a Lyapunov-function V1:R4+R as follows:

    V1=J1lnJ+A1lnA+Co1lnCo+Ce1lnCe. (2.3)

    The generalized Itô's formula gives

    dV1=LV1dt(A1)σCe1+βC2edB(t); (2.4)

    together with 0<Co<1 and 0<Ce<1, we have

    LV1<(eJ+cJ)JcJJ2(eA+cAa)AcAA2+(rJ+rA)Co+(λ+k)Ce+eJ+eA+α+g+m+b+ue+h+σ2C2e2(1+βC2e)2C1+rJ+rA+eJ+eA+α+ue+h+λ+g+m+b+k+σ22:=M, (2.5)

    where C1 is the maximum for the quadratic forms of A and J with negative signs for their highest-order terms; we therefore have

    dV1Mdt(A1)σCe1+βC2edB(t). (2.6)

    Integrating both sides of Inequality (2.6) from 0 to τlT implies that

    τlT0dV1τlT0MdtτlT0(A(t)1)σCe(t)1+βC2e(t)dB(t), (2.7)

    and then taking expectations yields

    EV1(τlT)V1(0)+MT. (2.8)

    We set Ωl={τlT} for ll1; then, Expression (2.2) turns into P{Ωl}ε. Note that for every ωΩl, each component J(τlT),A(τlT),Co(τlT)orCe(τlT) equals either l or 1l; hence, Inequality (2.8) could be rewritten as

    V1(0)+MTEV1(τlT)εmin{l1lnl,1l1+lnl}. (2.9)

    This, as l, leads to a contradiction

    >V1(0)+MT. (2.10)

    Therefore the assertion τ= is valid almost surely. The proof is complete.

    Corollary 2.2. Model (1.2) with light pollution has a unique solution (J(t),A(t),Co(t),Ce(t)) for any (J(0),A(0),Co(0),Ce(0)) and t0; the solution will remain in R4+ with a probability of 1.

    Lemma 3.1. [12] The upper boundaries of toxicant concentrations in organisms and in a polluted environment are given as

    Ceueh,Cokueh(g+m+b). (3.1)

    Lemma 3.2. For any given constant T, the lower boundaries of toxicant concentrations in organisms and in a polluted environment are obtained as

    (Ce)(ue)h+ehT(1(ue)h),(Co)((ue)h+ehT)g+m+b+e(g+m+b)T(1(Ce)g+m+b). (3.2)

    Proof. From the fourth equation of Model (1.2), we have

    ˙Ce(t)(ue)hCe.

    By a method of constant variation, we get

    Ce(t)(ue)h+ehT(1(ue)h),

    therefore the first assertion is valid. Similarly, by the third equation of Model (1.2), we obtain

    ˙Co(t)k(Ce)(g+m+b)Co.

    The method of constant variation gives that

    Co(t)(Ce)g+m+b+e(g+m+b)T(1(Ce)g+m+b),

    which further implies the second assertion.

    Theorem 3.1. If the coefficients of Model (1.2) with heavy pollution satisfy

    a<eA+cA+rA(Co)+λ(Ce)1+β(Ce)2, (3.3)

    then the densities of juveniles and adults in a local population will go to extinction.

    Proof. Let us define V2=ln(J+A) according to Itô's formula

    dV2=LV2dtσACe(J+A)(1+βC2e)dB(t). (3.4)

    We claim that

    LV2=1J+A(aAeJJrJCoJcJJ2eAArACoAcAA2λACe1+βC2e)A22(J+A)2σ2C2e(1+βC2e)2 (3.5)

    given J>1 and A>1; it is thus estimated by

    LV2<1J+A[(eJcJrJ(Co))J+(aeAcArA(Co)λ(Ce)1+β(Ce)2)A]q1, (3.6)

    and together with Lemma 3.1

    q1=max{eJcJrJ(Co),aeAcArA(Co)λ(Ce)1+β(Ce)2}.

    Integrating both sides of Eq (3.4) and dividing by t gives

    1tln(J(t)+A(t))<1tln(J(0)+A(0))+q11tt0A(s)σCe(s)(J(s)+A(s))(1+βC2e(s))dB(s). (3.7)

    According to the strong law of large numbers of the local martingale [19]

    limt1tt0σA(s)Ce(s)(J(s)+A(s))(1+βC2e(s))dB(s)=0almost surely (3.8)

    Taking the upper limit on both sides of Inequality (3.7), we get

    lim supt1tln(J(t)+A(t))<q1<0. (3.9)

    Hence

    limtJ(t)=0andlimtA(t)=0. (3.10)

    Corollary 3.1. If the coefficients of Model (1.2) with light pollution satisfy

    a<eA+cA+rA(Co)+λ(Ce), (3.11)

    then the densities of juveniles and adults in a local population will go to extinction.

    Considering the following n-dimensional stochastic differential equation:

    dx(t)=f(x(t))dt+g(x(t))dB(t),x(t)Rn+, (3.12)

    we introduce the following useful definitions and lemmas.

    Definition 3.1. [20] The solution x(t) of Eq (3.12) is called stochastically ultimately bounded if, for any ε(0,1), there is a positive constant χ(=χ(ε)) such that for any initial value x(0)Rn+, the solution has the property that

    lim suptP{|x(t)|>χ}<ε. (3.13)

    Definition 3.2. [21] The solution x(t) of Eq (3.12) is said to be stochastically permanent if, for any ε>0, there are constants δ1>0 and δ2>0 such that

    lim inftP{|x(t)|δ1}1ε,lim suptP{|x(t)|δ2}1ε. (3.14)

    Lemma 3.3. The densities of juveniles and adults in Model (1.2) with heavy pollution are stochastically ultimately bounded.

    Proof. We define V3=et(J+A); applying Itô's formula gives

    LV3=et(J+A+LJ+LA)=etF(J,A)<C2et, (3.15)

    where F(J,A) yields a positive boundary C2 as follows:

    F(J,A)=(1eJrJCo)JcJJ2+(1+aeArACo)AcAA2λACe1+βC2e<C2.

    We further derive

    J(t)+A(t)<et[J(0)+A(0)]+C2(1et)ett0σA(s)Ce(s)1+βC2e(s)dB(s). (3.16)

    Let |X|=J2+A2; given that

    Eett0σA(s)Ce(s)1+βC2e(s)dB(s)=0,J2+A2J+A,

    and taking expectations on both sides of Inequlity (3.16), we obtain that

    lim suptE|X(t)|C2. (3.17)

    The Chebyshev's inequality and Definition 3.1 gives

    lim suptP{|X(t)|>χ}<ε. (3.18)

    Lemma 3.4. Model (1.2) with heavy pollution has the following property:

    lim suptE1|X(t)|2+θH, (3.19)

    provided that θ is a positive number and satisfies the following condition:

    (aα)(eJ+rJ)(eA+rA+λ)0.5(3+θ)σ2>0. (3.20)

    Proof. Motivated by the approaches in Theorem 4.5 of [6] and Lemma 3.5 of [20], we define V4=(J+A)1; the generalized Itô's formula gives that

    dV4=LV4dt+V24σACe1+βC2edB(t), (3.21)

    where

    LV4=V24[aA(eJ+rJCo)J+αJαJ(eA+rACo+λCe1+βC2e)AcJJ2cAA2]+V34σ2C2eA2(1+βC2e)2V24[(aα)(eJ+rJ)(eA+rA+λ)](J+A)+V24(αJ+cJJ2+cAA2)+V34σ2A2[(aα)(eJ+rJ)(eA+rA+λ)σ2]V4+(α+cJ)cA. (3.22)

    We define V5=V2+θ4; the generalized Itô's formula again yields that

    dV5=LV5dt+(2+θ)V3+θ4σACe1+βC2edB(t), (3.23)

    where

    LV5=(2+θ)V1+θ4LV4+0.5(2+θ)(1+θ)V4+θ4σ2A2C2e(1+βC2e)2(2+θ)V1+θ4{[(aα)(eJ+rJ)(eA+rA+λ)σ2]V4+(α+cJ)cA}+0.5(2+θ)(1+θ)σ2V2+θ4C3V1+θ4C4V2+θ4, (3.24)

    with

    C3=(2+θ)[(α+cJ)cA],C4=(2+θ)[(aα)(eJ+rJ)(eA+rA+λ)0.5(3+θ)σ2]. (3.25)

    We differentiate Eq (3.23) with factor eKt, so

    d(eKtV5)=L(eKtV5)dt(KeKtV5+eKtV5LV5)σACe1+βC2edB(t). (3.26)

    We choose a moderate constant K such that C4K>0 and obtain

    L(eKtV5)=eKt[KV5+LV5]C5eKt. (3.27)

    Therefore, Eq (3.26) gives

    E[eKtV2+θ4(t)]V2+θ4(0)+C5KeKt,

    which leads to

    lim suptEV2+θ4(t)C5K:=H.

    The Cauchy inequality implies

    (J+A)2+θ22+θ|X|2+θ;

    thus

    lim suptE1|X(t)|2+θlim suptE[22+θV2+θ4(X(t))]22+θC5K:=H. (3.28)

    Theorem 3.2. If Condition (3.20) is valid, then the densities of juveniles and adults in Model (1.2) with heavy pollution are stochastically permanent.

    Proof. Given Inequality (3.28) in Lemma 3.4, we have

    lim inftE1|X(t)|2+θH. (3.29)

    For any given ε>0, we set

    δ2+θ1=εH. (3.30)

    The Chebyshev's inequality and Expression (3.30) gives that

    P{|X(t)|<δ1}=P{1|X(t)|>1δ1}δ2+θ1E1|X(t)|2+θε; (3.31)

    therefore,

    P{|X(t)|δ1}1ε. (3.32)

    According to Definition 3.2, the left side of the definition is valid. For the above ε>0, we define

    δ2=C2ε.

    The Chebyshev's inequality and Inequality (3.17) yields that

    P{|X(t)|>δ2}E|X(t)|δ2ε; (3.33)

    therefore,

    P{|X(t)|δ2}1ε. (3.34)

    That is to say, by Definition 3.2, the densities of juveniles and adults in a local population are stochastically permanent.

    Corollary 3.2. If Condition (3.20) is valid, then the densities of juveniles and adults in Model (1.2) with light pollution are stochastically permanent.

    Theorem 3.3. If the coefficients of Model (1.2) with heavy pollution satisfy

    a<cJ+2cJˆJ+0.5α+eJ,2σ2<2cA+4cAˆA+2eAa2α,k<min{2(g+m+b),2h1}, (3.35)

    then the densities of juveniles and adults are weakly persistent in the mean under the expectation around the pollution-free equilibrium (ˆJ,ˆA,0,0) in the long run; that is,

    lim supt1tEt0(ζ1(J(s)ˆJ)2+ζ2(A(s)ˆA)2+ζ3C2o(s)+ζ4C2e(s))dsζ5, (3.36)

    where ˆJ and ˆA simultaneously satisfy αˆJ=eAˆA+cAˆA2 and aˆA=eJˆJ+αˆJ+cJˆJ2, as well as

    ζ1=2cJ+4cJˆJ+α+2eJ2a,ζ2=2cA+4cAˆA+2eAa2α2σ2,ζ3=2(g+m+b)k,ζ4=2hk1,ζ5=u2e+(a+2σ2)ˆA2+aˆJ2. (3.37)

    Proof. New variables are governed as follows:

    w1=JˆJ,w2=AˆA,w3=Co,w4=Ce. (3.38)

    Hence, Model (1.2) is rewritten as given by the following equations:

    dw1=[a(w2+ˆA)(eJ+rJw3+α)(w1+ˆJ)cJ(w1+ˆJ)2]dt,dw2=[α(w1+ˆJ)(rAw3+eA+λw41+βw24)(w2+ˆA)cA(w2+ˆA)2]dtσw41+βw24(w2+ˆA)dB(t),dw3=[kw4(g+m+b)w3]dt,dw4=[uehw4]dt. (3.39)

    We define a C2-function

    V6=w21+w22+w23+w24.

    Applying Itô's formula implies that

    dV6=LV6dt2σw2w41+βw24(w2+ˆA)dB(t), (3.40)

    where

    LV6=2w1[a(w2+ˆA)(eJ+rJw3+α)(w1+ˆJ)cJ(w1+ˆJ)2]+2w2[α(w1+ˆJ)(rAw3+eA+λw41+βw24)(w2+ˆA)cA(w2+ˆA)2]+2w3[kw4(g+m+b)w3]+2w4[uehw4]+σ2w24(1+βw24)2(w2+ˆA)2=2aw1w2+2aˆAw12(eJ+α)w212rJw3w212ˆJw1(eJ+rJw3+α)2cJw1(w21+2ˆJw1+(ˆJ)2)+2αw1w2+2αˆJw22eAw222w22(rAw3+λw41+βw24)2w2ˆA(rAw3+eA+λw41+βw24)2cAw2(w22+2ˆAw2+(ˆA)2)+2kw3w42(g+m+b)w23+2uew42hw24+σ2w22w24(1+βw24)2+2σ2ˆAw2w24(1+βw24)2+σ2(ˆA)2w24(1+βw24)2,

    Given w1>1 and w2>1, it is thus estimated by

    LV6<aw21+aw22+aw21+a(ˆA)22(eJ+α)w212cJw214cJˆJw21+αw21+αw22+αw22+α(ˆJ)22eAw222cAw224cAˆAw22+kw23+kw242(g+m+b)w23+u2e+w242hw24+2σ2w22+2σ2(ˆA)2=(2a2eJα2cJ4cJˆJ)w21+(a+2α2eA2cA4cAˆA+2σ2)w22+(k2(g+m+b))w23+(k+12h)w24+u2e+(a+2σ2)ˆA2+aˆJ2.

    Therefore, by Expression (3.37), one gets that

    LV6<ζ1w21ζ2w22ζ3w23ζ4w24+ζ5. (3.41)

    Integrating from 0 to t on both sides of Eq (3.40) and taking the expectation, we derive the required Expression (3.36) as time t tends to infinity. The proof is complete.

    Corollary 3.3. If coefficients of Model (1.2) with light pollution satisfy Condition (3.35), then the densities of juveniles and adults are weakly persistent in the mean under the expectation around the pollution-free equilibrium (ˆJ,ˆA,0,0) in the long run.

    We assume that a(t),rJ(t),cJ(t),rA(t),cA(t),α(t),λ(t) and σ(t) are both positive and continuous functions with a period T. We further investigate the periodic model given by Model (4.1) due to the existence of periodic phenomena in the real world.

    dJ(t)=[a(t)AeJ(t)JrJ(t)CoJα(t)JcJ(t)J2]dt,dA(t)=[α(t)JeA(t)ArA(t)CoAcA(t)A2λ(t)g(A,Ce)]dtσ(t)g(A,Ce)dB(t),dCo(t)=[k(t)Ceg(t)Com(t)Cob(t)Co]dt,dCe(t)=[ue(t)h(t)Ce]dt. (4.1)

    Lemma 4.1. [22,23] Consider the following periodic stochastic differential equation:

    dx(t)=f(t,x(t))dt+g(t,x(t))dB(t),xRn, (4.2)

    where both f(t,x(t)) and g(t,x(t)) are T-periodic functions with respect to t. If System (4.2) has a global positive solution, suppose that there exists a T-periodic Lyapunov function V(t,x) with respect to t; the following conditions are satisfied outside of a certain compact set:

    (i)inf|x|>rV(t,x),r, (4.3)
    (ii)LV(t,x)1. (4.4)

    Then, System (4.2) has a T-periodic solution.

    Theorem 4.1. If the coefficients of Model (4.1) satisfy

    m1QM1>2, (4.5)

    then Model (4.1) has a positive periodic solution, where

    m1=1TT0(2a(t)α(t)+(eJ(t)eA(t))Λ112σ2(t))dt,
    M1=max{cJ4,(a+cA)24(cA)2},Q(t)=eJ(t)+eA(t)+(rJ(t)+rA(t))Co+α(t)+λ(t)Ce1+βC2e,

    and Λ1 represents the minimum of the densities of juveniles and adults in a local population.

    Proof. The existence and uniqueness of the global positive solution of Model (4.1) is derived by a similar way as shown in Theorem 2.1, so we will omit the details. Next, we define the C2-function V7(t,J,A) as follows:

    V7=J1lnJ+A1lnA+ω(t), (4.6)

    where ω(t) is a function defined in [0,) with ω(0)=0 that satisfies the following equation:

    ˙ω(t)=2a(t)α(t)+(eJ(t)eA(t))Λ112σ2(t)m1. (4.7)

    Integrating ˙ω(t) from t to t+T yields that

    ω(t+T)ω(t)=t+Tt˙ω(s)ds=0, (4.8)

    so ω(t) is a periodic function defined in [0,) with a period T. It is easy to check that

    lim inf(J,A)R2+DV7(t,J,A) (4.9)

    in the set

    D={(J,A)|(J,A)[ε,1ε]×[ε,1ε]},

    where ε is a sufficiently small positive number that satisfies

    2cJε<(a+cA)24cAQ+m1, (4.10)
    2(a+cA)ε<c4Q+m1, (4.11)
    (cJ)2ε2+G3<1, (4.12)
    (cA)2ε2+G4<1. (4.13)

    The generalized Itô's formula yields that

    LV7=a(t)AeJ(t)JrJ(t)CoJα(t)JcJ(t)J2a(t)AJ+Q(t)+cJ(t)J+α(t)JeA(t)ArA(t)CoAcA(t)A2λ(t)ACe1+β(t)C2eα(t)JA+cA(t)A+σ2(t)C2e2(1+β(t)C2e)2+˙ω(t)<cJ(t)J2+cJ(t)JcA(t)A2+(a(t)+cA(t))A2a(t)α(t)(eJ(t)eA(t))Λ1+12σ2(t)+˙ω(t)+Q=cJ(t)J2+cJ(t)JcA(t)A2+(a(t)+cA(t))Am1+Q<C7m1+Q, (4.14)

    with

    Q(t)=eJ(t)+eA(t)+(rJ(t)+rA(t))Co+α(t)+λ(t)Ce1+βC2e,

    where (cJ)J2+cJJ(cA)A2+(a+cA)A yields a maximum C7. To show LV7(t,J,A)<1 in R2+D, we separate R2+D into four parts:

    D1={(J,A)R2+|0<J<ε},D2={(J,A)R2+|0<A<ε},D3={(J,A)R2+|J>1ε},D4={(J,A)R2+|A>1ε}.

    Case 1. When (J,A)D1, we get

    LV7<cJ(t)JcJ(t)J2cA(t)A2+(a(t)+cA(t))Am1+Q<cJJ(cJ)J2(cA)(Aa+cA2(cA))2+(a+cA)2(4cA)m1+Q<cJε+(a+cA)24(cA)m1+Q. (4.15)

    Inequality (4.10) gives

    LV7<12((a+cA)24(cA)m1+Q):=G1<1.

    Case 2. When (J,A)D2, we obtain

    LV7<(a(t)+cA(t))AcJ(t)(J12)2+cJ(t)4m1+Q<(a+cA)ε+cJ4m1+Q. (4.16)

    Inequality (4.11) yields

    LV7<12(cJ4m1+Q):=G2<1.

    Case 3. When (J,A)D3, we have

    LV7<12cJ(t)J212cJ(t)J2+cJ(t)JcA(t)A2+(a(t)+cA(t))Am1+Q<12(cJ)J2(cJ)2(J1)2+12cJ(cA)A2+(a+cA)Am1+Q. (4.17)

    Inequality (4.12) shows that

    LV7<(cJ)2ε2+G3<1,

    with

    G3=C7+12cJm1+Q.

    Case 4. When (J,A)D4, we derive

    LV7<12cA(t)A212cA(t)A2+(a(t)+cA(t))AcJ(t)J2+cJ(t)Jm1+Q<12(cA)A2((cA)2Aa+cA2(cA))2+(a+cA)22(cA)(cJ)J2+cJJm1+Q. (4.18)

    Inequality (4.13) implies that

    LV7<(cA)2ε2+G4<1,

    where

    G4=C7+(a+cA)22(cA)m1+Q.

    So, LV7(t,J,A)<1 is checked when (J,A)R2+D.

    In this section, we present the numerical simulations to verify the aforementioned main results. Due to the linear dependence of the diffusion coefficients in [24,25], we govern the data from [12] and the Milstein's method in [26]; we let the threshold value for the polluted environment in Expression (1.3) be c=0.30 and take k=0.20,g=0.08,m=0.04,h=0.40,b=0.20,θ=0.10 and the initial values (J(0),A(0),Co(0),Ce(0))=(0.40,0.20,0.05,0.10). Then, the the discretization equations corresponding to Model (1.2) are written as

    Jn=Jn1+[aAn1Jn1(eJ+rJCo,n1+α+cJJn1)]Δt,An=An1+αJn1[An1(eA+rACo,n1+cAAn1)+λgn1]Δtσgn1ξΔt0.5σ2g2n1(ξ2ΔtΔt),Co,n=Co,n1+[kCe,n1(g+m+b)Co,n1]Δt,Ce,n=Ce,n1+[uehCe,n1]Δt, (5.1)

    where

    gn1(An1,Ce,n1)={An1Ce,n11+βC2e,n1,Ce,n1>c,An1Ce,n1,Ce,n1<c, (5.2)

    and ξ is a Gaussian random variable with a standard normal distribution N(0,1).

    Example 5.1. The parameters of extinction in Model (1.2) are presented in Table 1. We choose (I)–(III) as the parameters of Model (1.2) in a heavily polluted environment; and choose (IV) as the parameters of Model (1.2) in a lightly polluted environment. It is easy to verify that Condition (3.3) of Theorem 3.1 and Condition (3.11) of Corollary 3.1 are satisfied.

    aeAcArA(Co)λ(Ce)1+β(Ce)2=0.0359<0, (5.3)
    \begin{equation} a-e_{A}-c_A-r_{A}(C_{o})_{*}-\lambda (C_{e})_{*} = -0.0406 < 0, \end{equation} (5.4)
    Table 1.  Parameters for extinction for Model (1.2).
    No. a e_J e_A r_J r_A \alpha c_{J} c_{A} \lambda u_{e} \sigma \beta
    {\rm{(I)}} 0.35 0.10 0.15 0.10 0.15 0.25 0.05 0.20 0.30 0.30 0.30 0.10
    {\rm{(II)}} 0.35 0.10 0.15 0.10 0.15 0.25 0.05 0.20 0.30 0.30 0.30 1.00
    {\rm{(III)}} 0.35 0.10 0.15 0.10 0.15 0.25 0.05 0.20 0.05 0.30 0.30 10.0
    {\rm{(IV)}} 0.32 0.10 0.15 0.10 0.15 0.25 0.05 0.20 0.05 0.10 0.30 null

     | Show Table
    DownLoad: CSV

    where (C_{o})_{*} = 0.05, C^{*}_{e} = 0.10, (C_{e})_{*} = 0.75.

    The results of numerical simulations indicate that the densities of juveniles and adults tend to extinction as shown in Figures 1 and 2. We conclude that the densities of juveniles and adults are slightly different between Figures 1 and 2, and that the time for extinction was extended as a result of increasing the psychological effects \beta from 0.10 to 10.0. By the same arguments, the simulations for extinction of juveniles and adults with external toxicant periodic inputs to Model (1.2) are demonstrated in Figure 2, and the time for extinction behaves in the similar way as shown in Figure 1.

    Figure 1.  Extinction derived from Model (1.2), with constant input for heavy pollution, u_e(t) = 0.30 , and for light pollution, u_e(t) = 0.10 , in Table 1.
    Figure 2.  Extinction derived from Model (1.2), with periodic input for heavy pollution, u_e(t) = 0.30+0.10\sin(0.35t) , and for light pollution, u_e(t) = 0.10+0.10\sin(0.35t) .

    Example 5.2. Main parameters for the stochastic permanence of Model (1.2) are given in Table 2. We next investigate the impacts of the psychological effects \beta and external toxicant input u_e for juveniles and adults in a local population. We take (V)–(VII) as the parameters of Model (1.2) in a heavily polluted environment, and take (VIII) as the parameters of Model (1.2) in a lightly polluted environment. It is easy to verify that Condition (3.20) of Theorem 3.2 is satisfied, and that

    (a\wedge \alpha)-(e_{J}+r_{J})\vee(e_{A}+r_{A}+\lambda)-0.5(3+\theta){\sigma}^2 = 0.0345 > 0.
    Table 2.  Parameters for stochastic permanence in Model (1.2).
    No. a e_J e_A r_J r_A \alpha c_{J} c_{A} \lambda u_{e} \sigma \beta
    {\rm{(V)}} 0.35 0.05 0.10 0.10 0.05 0.32 0.05 0.10 0.10 0.30 0.10 0.10
    {\rm{(VI)}} 0.35 0.05 0.10 0.10 0.05 0.32 0.05 0.10 0.10 0.30 0.10 1.00
    {\rm{(VII)}} 0.35 0.05 0.10 0.10 0.05 0.32 0.05 0.10 0.10 0.30 0.10 10.0
    {\rm{(VIII)}} 0.35 0.05 0.10 0.10 0.05 0.32 0.05 0.10 0.10 0.10 0.10 null

     | Show Table
    DownLoad: CSV

    Thus, juveniles and adults in a lightly polluted environment and in a heavily polluted environment are stochastically permanent as shown in Figures 3 and 4.

    Figure 3.  Stochastic permanence of Model (1.2), with constant input for heavy pollution, u_e(t) = 0.30 , and for light pollution, u_e(t) = 0.10 , in Table 2.
    Figure 4.  Stochastic permanence of Model (1.2), with periodic input for heavy pollution, u_e(t) = 0.30+0.10\sin(0.35t) , and for light pollution u_e(t) = 0.10+0.10\sin(0.35t) .

    The simulations shown in (a)–(c) of Figures 3 and 4 reveal that the densities for juveniles and adults in a heavily polluted environment grow as the value of the psychological effects \beta increases from 0.10 to 10.0. Further, the densities for juveniles and adults in a lightly polluted environment, as shown in (d), present higher levels than that in the heavily polluted environment shown in (c) of Figure 3. We take the parameters in Table 2 and external toxicant periodic inputs u_e(t) = 0.30+0.10\sin(0.35t) for heavy pollution and u_e(t) = 0.10+0.10\sin(0.35t) for light pollution; then, the stochastic permanence of the juveniles and adults in Model (1.2) in Figure 4 are similar to those in Figure 3.

    Example 5.3. We take the parameters in Table 3, and verify that Conditions (3.35) of Theorem 3.3 are satisfied. That is

    \begin{equation} \begin{aligned} &c_{J}+2c_{J}\hat{J}+0.5\alpha+e_{J}-a = 0.05 > 0, \quad 2c_{A}+4c_{A}\hat{A}+2e_{A}-a-2\alpha-2\sigma^2 = 0.05 > 0, \\ &2(g+m+b)-k = 0.49 > 0, \quad 2h-1-k = 0.05 > 0. \end{aligned} \end{equation} (5.5)
    Table 3.  Parameters for weak persistence in the means according to Model (1.2).
    No. a e_{J} e_{A} r_{J} r_{A} \alpha c_{J} c_{A} \lambda k u_{e} h \sigma \beta
    {\rm{(IX)}} 0.35 0.05 0.10 0.10 0.05 0.20 0.10 0.20 0.30 0.15 0.30 0.60 0.20 0.10
    {\rm{(X)}} 0.35 0.05 0.10 0.10 0.05 0.20 0.10 0.20 0.30 0.15 0.30 0.60 0.20 1.00
    {\rm{(XI)}} 0.35 0.05 0.10 0.10 0.05 0.20 0.10 0.20 0.30 0.15 0.30 0.60 0.20 10.0
    {\rm{(XII)}} 0.35 0.05 0.10 0.10 0.05 0.20 0.10 0.20 0.35 0.15 0.10 0.60 0.20 null

     | Show Table
    DownLoad: CSV

    The pollution-free equilibrium of Model (1.2) is (\hat{J}, \hat{A}, 0, 0) = (0.50, 0.50, 0, 0) ; then, the weak persistence in the mean of Model (1.2) is demonstrated in Figures 5 and 6. Taking (IX)–(XI) as the parameters of Model (1.2) for a heavily polluted environment, we find that the densities for weak persistence in the means for juveniles and adults in a heavily polluted environment arise when the value of the psychological effects \beta is increasing from 0.10 to 10.0 as shown in (a)–(c) of Figure 5. Again, taking (XII) as the parameters of Model (1.2) for a lightly polluted environment, the corresponding numerical simulations reveal that the survival levels of juveniles and adults, as shown in (d), are higher those shown in (c) of Figure 5.

    Figure 5.  Weak persistence in the means of Model (1.2), with constant input for heavy pollution, u_e(t) = 0.30 , and for light pollution u_e(t) = 0.10 , in Table 3.
    Figure 6.  Weak persistence in the means of Model (1.2) , with periodic input for heavy pollution, u_e(t) = 0.30+0.10\sin(0.35t) , and for light pollution, u_e(t) = 0.10+0.10\sin(0.35t) .

    The external toxicant periodic inputs u_e(t) = 0.30+0.10\sin(0.35t) and u_e(t) = 0.10+0.10\sin(0.35t) were taken into account for heavy pollution and light pollution respectively; then, the stochastic permanence of juveniles and adults, asaccording to Model (1.2) in Figure 6, the same as those in Figure 5.

    Example 5.4. Let all parameters be periodic functions of t as follows:

    \begin{equation} \begin{array}{llll} a(t) = 0.35+0.01\sin(0.1t), & e_J(t) = 0.05+0.01\sin(0.1t), & e_A(t) = 0.10+0.01\sin(0.1t), \\ r_J(t) = 0.10+0.01\sin(0.1t), & r_A(t) = 0.05+0.01\sin(0.1t), & \alpha(t) = 0.32+0.01\sin(0.1t), \\ c_J(t) = 0.05+0.01\sin(0.1t), & c_A(t) = 0.10+0.01\sin(0.1t), & \lambda(t) = 0.10+0.01\sin(0.1t), \\ k(t) = 0.20+0.01\sin(0.1t), & g(t) = 0.08+0.01\sin(0.1t), & m(t) = 0.04+0.01\sin(0.1t), \\ h(t) = 0.40+0.01\sin(0.1t), & b(t) = 0.20+0.01\sin(0.1t), & \sigma(t) = 0.15+0.01\sin(0.1t). \end{array} \end{equation} (5.6)

    It is obvious that Condition (4.5) of Theorem 4.1 is satisfied. When the psychological effect were varied from 0.10 to 10.0, as shown in (a)–(c) of Figure 7, the corresponding simulations showed that the periodicity of Model (1.2) becomes apparent in a heavily polluted environment, and also that the survival levels for juveniles and adults in a lightly polluted environment, as shown in (d), are higher than those in a heavily polluted environment, as shown in (c) of Figure 7.

    Figure 7.  Periodic solution of Model (1.2) with heavy pollution, u_e(t) = 0.30+0.01\sin(0.1t) , and light pollution, u_e(t) = 0.10+0.01\sin(0.1t) .

    We investigate the survival levels and periodicities of single-species population models with stage structure and psychological effects within a polluted environment in this study. We always assumed that within a local population, adults produced juveniles at a constant rate, juveniles matured and turned into adults at a constant rate and that juveniles were not involved in the hunting. Adults frequently hunt in polluted environments for survival and reproduction, inevitably taking losses because of the polluted environment. Both juveniles and adults experienced losses due to toxicants within organisms.

    The main results demonstrate that the extinction of juveniles and adults in heavily polluted environments depends on the psychological effects, and the time to extinction of the juveniles and adults becomes shorter in Model (1.2) as the value of the psychological effects varies from 0.10 to 10.0; also, the time to extinction in a lightly polluted environment is around 1000 days longer than that in a heavily polluted environment as presented in Figures 1 and 2.

    Further, the research results also show that under the conditions of constant toxicant inputs and a periodic toxicant input, the survival levels including the stochastic permanence in Theorem 3.2 and weak persistence in the mean in Theorem 3.3 in a heavily polluted environment, decrease when the value of the psychological effects increases as presented in (a)–(c) of Figures 36. Meanwhile, the densities for juveniles and adults, as according to Model (1.2) are higher in a lightly polluted environment than that in a heavily polluted environment; the corresponding numerical simulations are shown in (d) of Figures 36. Finally, the existence of the periodic solution to Model (1.2) has been derived in Theorem 4.1 for both heavily and lightly polluted environments. The corresponding numerical simulations were carried out by employing Milstein's method as presented in Figure 7.

    This research was supported by the National Natural Science Foundation of China (61911530398), Special Projects of the Central Government Guiding Local Science and Technology Development (2021L3018) and the Natural Science Foundation of Fujian Province of China (2021J01621).

    All authors declare that they have no conflict of interests regarding this study.



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