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Research article

Water resource policy support system of the Caspian Basin

  • Received: 08 February 2019 Accepted: 06 June 2019 Published: 19 June 2019
  • Water resource policy support system (WRPSS) is a process that addresses environmental policy and water resource management analyses in conjunction with data interpretation. We examine the use of a WRPSS in Iran’s northern semi-arid region of the Caspian Basin and present how eight human and non-human pressure factors, if automated, would assist in water resource security. The main features of the WRPSS include: (1) water policy modifications suitable to local environmental conditions for water evaluation and (2) development of spatial tools to derive criteria weights. A dynamic, calculative process formulates weight and critical intervals for each pressure parameter provided. The developed knowledge-base ensures the WRPSS record represents a realistic, practicable, and functional system for sound water policy. Such know-how is useful in determining water resource pressure factors in relation to a policy support system (PSS) analysis. WRPSS ensures results are interpreted within the relevant context of maximizing efficiency of water policy goals and PSS interpellation. Results indicate the Caspian Basin’s agricultural water consumption and dam infrastructure are considered most and least important sub-criteria, respectively. Moreover, the sub-basin of Haraz-Ghareh Su is worst off study-wide.

    Citation: Amir Hedayati Aghmashhadi, Giuseppe T. Cirella, Samaneh Zahedi, Azadeh Kazemi. Water resource policy support system of the Caspian Basin[J]. AIMS Environmental Science, 2019, 6(4): 242-261. doi: 10.3934/environsci.2019.4.242

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  • Water resource policy support system (WRPSS) is a process that addresses environmental policy and water resource management analyses in conjunction with data interpretation. We examine the use of a WRPSS in Iran’s northern semi-arid region of the Caspian Basin and present how eight human and non-human pressure factors, if automated, would assist in water resource security. The main features of the WRPSS include: (1) water policy modifications suitable to local environmental conditions for water evaluation and (2) development of spatial tools to derive criteria weights. A dynamic, calculative process formulates weight and critical intervals for each pressure parameter provided. The developed knowledge-base ensures the WRPSS record represents a realistic, practicable, and functional system for sound water policy. Such know-how is useful in determining water resource pressure factors in relation to a policy support system (PSS) analysis. WRPSS ensures results are interpreted within the relevant context of maximizing efficiency of water policy goals and PSS interpellation. Results indicate the Caspian Basin’s agricultural water consumption and dam infrastructure are considered most and least important sub-criteria, respectively. Moreover, the sub-basin of Haraz-Ghareh Su is worst off study-wide.


    In the field of biomathematics, the predator-prey model has been studied by many scholars. They explored the dynamical behavior among biological populations by establishing differential equations [1,2,3,4]. In 1925, the Lotka-Volterra model described the variation in population size between predator and prey in [5,6]. This model describes that population size changes are interacting. After that, in order to study the situation that predator populations have other food sources besides prey population, Leslie and Gower [7,8] proposed a Leslie-Gower type predator-prey model. This model mainly explores the fact that when the preferred food decreases, the number of predators also decreases. Then Aziz-Alaoui and Okiye added a constant to the denominator of the Leslie-Gower type functional response function in [9], calling it the modified Leslie-Gower type. This type limits the growth of predators due to severe shortages of preferred foods, despite the predators having other food sources. Besides, the impact of infectious diseases on populations in nature is also important. In order to study the dynamical behavior of populations in more complex situations, some factors influencing population size changes have been added to the Leslie-Gower type model. The authors of [10] describe the mechanism of disease transmission by using the Holling type Ⅱ. Some scholars have included disease factors in their studies of fractional differential equations as well, e.g., [11,12,13,14].

    However, in nature, biological populations are inevitably impacted by environment noise more or less. During the past decades, many investigators have focused on the study of stochastic biological models [15,16]. Among them, a predator-prey-parasite model with stochastic perturbations has been studied by Majumder et al. [17]. Parasitic infections divide prey populations into susceptible and infected populations, and infected populations lose fertility and do not heal again. Both susceptible and infected prey populations are preyed upon by predators, and the predators will not be infected by the disease. They constructed the following model:

    {dx(t)=[ax(t)bx2(t)λx(t)y(t)cx(t)z(t)m1+x(t)+y(t)]dt+σ1x(t)dB1(t),dy(t)=[λx(t)y(t)my2(t)ey(t)z(t)m1+x(t)+y(t)γy(t)]dt+σ2y(t)dB2(t),dz(t)=[rz(t)fz2(t)m2+x(t)+y(t)]dt+σ3z(t)dB3(t),

    where x(0)0, y(0)0, z(0)0.

    In addition, the fear of predators can also influence the birth rates and offspring survival of prey populations. Zanette et al. [18] verified this idea through experiments. It is noted in [19] that the mental state of juvenile prey can be mediated by predator-induced fear and this fear may have an impact on their survival rates as adults. Thus, many scholars have realized that the fear costs of predators can directly or indirectly affect the prey population. So it should be included in the predator-prey system. Based on this view, scholars have studied the fear effect of biological populations [20,21]. Qi and Meng [22] used (θ+K(1θ)K+z(t)) to represent the fear function to measure the cost of fear. θ[0,1] represents the cost of minimum fear and K represents the level of prey fear of predator populations. Let κ(θ,K,z)=θ+K(1θ)K+z; we have κ(θ,K,z)z<0. From this, it is clear that the larger the predator population, the stronger the inhibitory effect on the growth of the prey population. Therefore, introducing a fear factor into the prey-predator system can help us to explore the variation of populations in different situations better.

    In addition, natural species may be subjected to unexpected environmental disruptions such as epidemics, hurricanes, earthquakes and so on. Random perturbations described by Brownian can only characterize the continuous influence, but it does not describe sudden and drastic environmental changes very well. To explain this occurrence, Bao et al. included Lévy jumps into population models in [23,24]. Wu and Wang [25] considered the population dynamical behaviors of stochastic system with jumps. So we also want to introduce Lévy jumps into a stochastic predator-prey model.

    Inspired by the articles above, we consider adding a fear factor to susceptible prey populations and considered more complex diseases, using the Holling type Ⅱ function to represent the spread of disease. Finally, we use Lévy noise to describe the situation when the population is subjected to drastic changes from the outside. We consider the following stochastic disease including predator-prey model with Lévy noise and fear effects:

    {dx(t)=x(t)[r(θ+K(1θ)K+z(t))bx(t)az(t)1+b1(x(t)+y(t))+b2z(t)ηy(t)b3+x(t)]dt+σ1x(t)dB1(t)+Γx(t)γ1(u)˜N(du,dt),dy(t)=y(t)[ηx(t)b3+x(t)cy(t)dz(t)1+b1(x(t)+y(t))+b2z(t)γ]dt+σ2y(t)dB2(t)+Γy(t)γ2(u)˜N(du,dt),dz(t)=z(t)[βgz(t)m+x(t)+y(t)]dt+σ3z(t)dB3(t)+Γz(t)γ3(u)˜N(du,dt), (1.1)

    with initial values x(0)=x0, y(0)=y0 and z(0)=z0. In this model, x(t), y(t) and z(t) denote the population densities of the susceptible prey, infected prey and predator population at time t respectively. And the per capita maximum fertility rates of the prey and predator populations are written as r and β respectively; the intensity of interspecific competition in prey populations is denoted by b and c; η represents the disease transmission rate and ηx(t)y(t)b3+x(t) describes the spread of the disease; a and d are the consumption rates and γ is the death rate of the infected prey population. g represents the interspecific competition of predators and m is the half-saturation constant of predators. b1 and b2 represent the prey saturation constants and predator disturbance respectively. There are no negative constants among any of the parameter values.

    Bi(t) (i=1,2,3) represents Brownian motion, and each value is independent of each other. In addition, there is a complete probability space (Ω,F,{Ft}t0,P) with a filtration {Ft}t0 that meets the normal requirements, and Bi(t) (i=1,2,3) is defined on this probability space. σ2i  (i=1,2,3) represents the noise's level of intensity. The left limits of x(t), y(t) and z(t) are represented by x(t), y(t) and z(t) respectively. N(dt,du) is a Poisson counting measure which is defined on λ(du). The characteristic measure λ on the measure subset Γ of [0,+] such that λ(Γ)<. N(dt,du) is defined on R+×(R{0}), R+:=(0,). Besides, ˜N(dt,du)=N(dt,du)λ(du)dt is the corresponding martingale measure. γi(u) (i=1,2,3) measures the effect of a Lévy jump on prey and predator populations, γi(u)>1 (i=1,2,3) for uΓ. In addition, it is important to note that Lévy jumps have a facilitating effect on the ecosystem when γi>0 (i=1,2,3), such as an ocean red tide. When γi<0 (i=1,2,3), Lévy jumps have a negative effect on the ecosystem, such as tsunamis and earthquakes. See [26,27] for specific examples.

    In this article, we need to assume that the coefficients satisfy the following assumption:

    Assumption 1. There exists a positive constant K which gives:

    Γ[ln(1+γi(u))]2λ(du)<K,        Γγ2i(u)λ(du)<K,   i=1,2,3.

    It means that the intensity of Lévy noise is not very large. Here are some inequalities we will frequently use:

    lnpp1,  p>0;           pr1+r(p1),  p0, 1r0.

    Lemma 1. ([28]) Denote by Σ(t) a local martingle vanishing at t=0. Define

    ¯Σ(t)=t0dΣ(s)(1+s)2dt,  t0,

    where Σ(t)=Σ,Σ(t) stands for the Meyer's angle bracket process. If lim supt+¯Σ(t)<+, then limt+t1Σ(t)=0, a.s.

    The rest of the research for this paper is as follows. In Section 2, we present the existence and uniqueness of the positive solution of System (1.1). In Section 3, we first studied the conditions for population extinction. Then we considered the existence and extinction of susceptible prey populations and predator populations under conditions where the disease is effectively prevented and infected prey populations are extinct. In Section 4, it proves the stochastic ultimate boundedness of System (1.1) and the existence of ergodic stationary distribution of the System (1.1) when Lévy noise does not exist. In Section 5, we select suitable parameters and use numerical simulations to prove our conclusions. Lastly, we briefly summarize the work of article.

    In order to study the dynamical behavior of the system, we first verify that there is a globally unique positive solution for System (1.1). First, we give Lemma 2 to show that the positive solution of the system exists locally and uniquely, and then prove that the solution exists globally with Theorem 1.

    Lemma 2. For any given initial value (x0,y0,z0)R3+, there exists a unique local positive solution (x(t),y(t),z(t)) to System (1.1), as defined on the interval t[0,τe), where τe is the explosion time.

    Proof. Consider the equation

    {dN1(t)=dlnx(t)=[r(θ+K(1θ)K+eN3(t))beN1(t)aeN3(t)1+b1(eN1(t)+eN2(t))+b2eN3ηeN2(t)b3+eN1(t)σ212+Γ[ln(1+γ1(u))γ1(u)]λ(du)]dt+σ1dB1(t)+Γln(1+γ1(u))˜N(dt,du),dN2(t)=dlny(t)=[ηeN1(t)b3+eN1(t)ceN2(t)deN3(t)1+b1(eN1(t)+eN2(t))+b2eN3(t)γσ222+Γ[ln(1+γ2(u))γ2(u)]λ(du)]dt+σ2dB2(t)+Γln(1+γ2(u))˜N(dt,du),dN3(t)=dlnz(t)=[βgeN3(t)m+eN1(t)+eN2(t)σ232+Γ[ln(1+γ3(u))γ3(u)]λ(du)]dt+σ3dB3(t)+Γln(1+γ3(u))˜N(dt,du),

    with initial values N1(0)=lnx0, N2(0)=lny0 and N3(0)=lnz0 on t0. It is easy to see that the above equation satisfies the local Lipschitz condition. Therefore, System (1.1) has a unique local solution (N1(t),N2(t),N3(t)) for t[0,τe), and τe is the explosion time. Because x(t)=eN1(t), y(t)=eN2(t) and z(t)=eN3(t), by Itô's formula, we get that (x(t),y(t),z(t)) is the unique local positive solution to System (1.1) with the initial value (x0,y0,z0).

    Theorem 1. For any given initial value (x0,y0,z0)R3+, a unique global positive solution (x(t),y(t),z(t)) exists in System (1.1) for t[0,+).

    Proof. In order to prove that the solution is global, we need to prove τe= a.s. Let m0>0 be sufficiently large to make x0,y0,z0[1m0,m0] for each integer mm0; then, define the stopping time

    τm=inf{t[0,τe):min{x(t),y(t),z(t)}1m   or  max{x(t),y(t),z(t)}m}.

    Let inf= ( refers to the empty set). Obviously, as m tends to infinity, τm is increasing. Let τ=limmτm and ττe, a.s. If we can prove τ=  a.s. then we have τe=  a.s., for all t0.

    We can proof by contradiction. If not, there exists a pair constants T0 and ε(0,1) such that P(τT)>ε. Thus  m1m0, we have

    P(τmT)ε for all mm1.

    Define a C2-function V: R3+R+

    V(x,y,z)=(x1lnx)+(y1lny)+(z1lnz).

    Because s1lns>0, for all s>0, we have V(x,y,z)>0. Applying Itô's formula, the following equation yields

    dV(x,y,z)=LV(x,y,z)dt+σ1(x1)dB1(t)+σ2(y1)dB2(t)+σ3(z1)dB3(t)+Γ[x(t)γ1(u)ln(1+γ1(u))]˜N(dt,du)+Γ[y(t)γ2(u)ln(1+γ2(u))]˜N(dt,du)+Γ[z(t)γ3(u)ln(1+γ3(u))]˜N(dt,du); (2.1)

    LV:R3+R+ is given as follows and using Assumption 1, we obtain

    LV(x,y,z)=rx(θ+K(1θ)K+z)bx2axz1+b1(x+y)+b2zηxyb3+xr(θ+K(1θ)K+z)+bx+az1+b1(x+y)+b2z+ηyb3+x+σ21+σ22+σ232+ηxyb3+xcy2dyz1+b1(x+y)+b2zγyηxb3+x+cy+dz1+b1(x+y)+b2z+γ+βzgz2m+x+yβ+gzm+x+y+Γ[γ1(u)ln(1+γ1(u))]λ(du)+Γ[γ2(u)ln(1+γ2(u))]λ(du)+Γ[γ3(u)ln(1+γ3(u))]λ(du)rxbx2+bx+ab2+ηycy2+cy+db2+γ+βz+gzM+(β+g)z,

    where

    M=sup{bx2+(r+b)x+ab2cy2+(η+c)y+db2+γ+σ21+σ22+σ312+Γ[γ1(u)ln(1+γ1(u))]λ(du)+Γ[γ2(u)ln(1+γ2(u))]λ(du)+Γ[γ3(u)ln(1+γ3(u))]λ(du)} (2.2)

    is a positive constant.

    We have that z2(z1lnz)+ln42V(x,y,z)+ln4. We can write:

    LV(x,y,z)M+(β+g)ln4+2(β+g)V(x,y,z)M1(1+V(x,y,z)), (2.3)

    where M1=max{M+(β+g)ln4,2(β+g)}.

    Combining (2.1) and (2.3), we can obtain that

    dV(x,y,z)M1(1+V(x,y))dt+σ1(x1)dB1(t)+σ2(y1)dB2(t)+σ3(z1)dB3(t)+Γ[x(t)γ1(u)ln(1+γ1(u))]˜N(dt,du)+Γ[y(t)γ2(u)ln(1+γ2(u))]˜N(dt,du)+Γ[z(t)γ3(u)ln(1+γ3(u))]˜N(dt,du). (2.4)

    The integration is taken at both ends of the inequality (2.4) from 0 to τmT, followed by the expectation, yielding

    EV(x(τmT),y(τmT)),z(τmT))V(x0,y0,z0)+M1EτmT0(1+V(x,y,z))dtV(x0,y0,z0)+M1ET0V(x(t),y(t),z(t))dt+M1TV(x0,y0,z0)+G1T0EV(x(t),y(t),z(t))dt+M1T.

    By Gronwall's inequality, we can get

    EV(x(τmT),y(τmT),z(τmT))(V(x0,y0,z0)+M1T)eM1T.

    Let Ωm=τmT; we have P(Ωm)ε. So for ωΩm, at least one value of x(τm,ω), y(τm,ω) or z(τm,ω) equals either m or 1m. Note that V(x(τm),y(τm),z(τm)) is no less than (m1lnm)(1m1ln1m). Consequently,

    (V(x0,y0,z0)+M1T)eM1TE(1Ωm(ω),V(x(τm),y(τm),z(τm)))ε(m1lnm)(1m1ln1m),

    where 1Ωm(ω) is the indicator function of ωm. Then, let m; we deduce that

    ε(m1lnm)(1m1ln1m)+;

    this is contradictory. Hence, we can get τ=.

    The result is confirmed.

    In this section, we consider the long time behavior of System (1.1). The conditions when the susceptible prey population, the infected prey population and the predator population are all extinct are first considered. Then we explore the existence and extinction of susceptible prey populations and predator populations in the context of the effective prevention of infectious disease.

    Theorem 2. For any given initial value (x0,y0,z0)R3+, the solution (x(t),y(t),z(t)) of system (1.1) has the following properties if Assumption 1 holds:

    r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)<0,ησ222Γ[γ2(u)ln(1+γ2(u))]λ(du)<0,βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du)<0;

    then the predator and prey populations will be extinctive almost surely, that is

    limtx(t)=0, limty(t)=0, limtz(t)=0. (3.1)

    Proof. First of all, we consider the prey population. We have d{etlnx(t)}=etdlnx(t)+etlnx(t) and the fundamental inequality lnxx1 for all x>0. Calculating by Itô's formula, we get

    dlnx(t)=[r(θ+K(1θ)K+z)bxaz1+b1(x+y)+b2zηyb3+xσ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]dt+σ1dB1(t)+Γln(1+γ1(u))˜N(du,dt)[r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]dt+σ1dB1(t)+Γln(1+γ1(u))˜N(du,dt).

    Integrating both sides of the above inequality simultaneously, we have

    lnx(t)lnx0+t0[r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]ds+t0σ1dB(s)+t0Γln(1+γ1(u))˜N(du,ds).

    Then, we have

    lnx(t)t[r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]+t0σ1dB1(s)t+Σ1(t)t+lnz0t. (3.2)

    Denote Σ1(t)=t0Γln(1+γ1(u))˜N(ds,du); in light of Assumption 1,

    Σ1,Σ1(t)=tΓ[ln(1+α(x))]2λ(du)<Ft,

    where F is a positive number. So we have t0F(1+s)2ds=tt+1<; then, it follows from Lemma 2 that

    limtt1Σ1(t)=0,  a.s. (3.3)

    Taking the limit on both sides of the inequality (3.2) and bringing in (3.3), we get

    lim suptlnx(t)tlimt[r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)+t0σ1dB1(s)t+Σ1(t)t+lnz0t]=r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du).

    When r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)<0, the susceptible prey population will be extinct.

    Similarly, for the infected prey and predator populations, we have

    lim suptlny(t)tησ222Γ[γ2(u)ln(1+γ2(u))]λ(du),
    lim suptlnz(t)tβσ232Γ[γ3(u)ln(1+γ3(u))]λ(du).

    When ησ222Γ[γ2(u)ln(1+γ2(u))]λ(du)<0 and βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du)<0, the infected prey and predator population will be extinct.

    The result is confirmed.

    In this section, we expect that infectious diseases transmitted among prey populations will be effectively prevented, susceptible prey populations will no longer be infected and infected prey populations will gradually die out. Considering the extinction of the infected population under the condition that ησ222Γ[γ2(u)ln(1+γ2(u))]λ(du)<0, i.e., after the infectious disease is cured, we have limty(t)=0. For ε>0, there exist t1 and a set Ωε such that P(Ωε)1ε and ηx(t)y(t)b3+x(t)<ε; for t1t and ωΩε. Therefore, we next focused on the changes in susceptible and predator populations when infected prey populations perished.

    Definition 1. ([29]) The susceptible prey populations and predator populations are said to be persistent in mean if

    lim inft1tt0x(s)ds>0 a.s., lim inft1tt0y(s)ds>0 a.s.

    Lemma 3. ([30]) Let b(t)C(Ω×[0,+),R+)

    1) If there exist two positive constants T and v0 such that lnb(t)vtv0t0b(s)ds+σB(t) for tT, where σ>0, then

    {lim supt1tt0b(s)dsvv0, if v0,limtb(t)=0,                        if v<0.

    2) If there exist two positive constants T and v0 such that lnb(t)vtv0t0b(s)ds+σB(t) for tT, where σ>0, then

    lim inft1tt0b(s)dsvv0.

    Theorem 3. Suppose that (x(t),y(t),z(t)) denotes the positive solution to System (1.1) with the initial positive value (x0,y0,z0)>0; when infected prey populations tend to become extinct, that is, limty(t)=0, we have the following

    (A1). If r<σ212Γ[γ1(u)ln(1+γ1(u))]λ(du), β>σ232Γ[γ3(u)ln(1+γ3(u))]λ(du), then the predator is persistent in mean and the susceptible prey is extinct, that is

    limtx(t)=0  andlimtt1t0z(s)ds=mg(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du)).

    (A2). If 1b(rθ2ab2σ212Γ[γ1(u)ln(1+γ1(u))]λ(du))>0 and β<σ232Γ[γ3(u)ln(1+γ3(u))]λ(du), then the susceptible prey is persistent in mean and the predator is extinct, that is

    limtz(t)=0  andlim inftt1t0x(s)ds1b(rθ2ab2σ212Γ[γ1(u)ln(1+γ1(u))]λ(du))>0.

    (A3). If 1b(rθ2ab2σ212Γ[γ1(u)ln(1+γ1(u))]λ(du))>0 and β>σ232Γ[γ3(u)ln(1+γ3(u))]λ(du), then both the susceptible prey and predator are persistent in mean, that is

    lim inftt1t0x(s)ds1b(rθ2ab2σ212Γ[γ1(u)ln(1+γ1(u))]λ(du))>0  andlim inftt1t0z(s)dsmg(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du))>0.

    Proof. According to Theorem 2, when ησ222Γ[γ2(u)ln(1+γ2(u))]λ(du)<0, limt+y(t)=0. So we know that ε2>0 for T2>0 when t>T2 such that 0<y(t)ε2.

    (A1) Similarly, when limt+x(t)=0, we know that ε1>0 for T1>0 when t>T1 such that 0<x(t)ε1. We obtain

    dlnz(t)(βσ232gz(t)m+ε1+ε2Γ[γ3(u)ln(1+γ3(u))]λ(du))dt+σ3B3(t)+Γln(1+γ3(u))˜N(du,dt).

    Integrating both sides of the above formula, we have

    lnz(t)lnz(0)(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du))tgm+ε1+ε2t0z(s)ds+t0σ3B3(t)+t0Γln(1+γ3(u))˜N(du,ds). (3.4)

    Similarly, we have

    lnz(t)lnz(0)(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du))tgmt0z(s)ds+t0σ3B3(s)+t0Γln(1+γ3(u))˜N(du,ds). (3.5)

    Applying Lemma 3 and Assumption 1 to (3.4) and (3.5) respectively, we have

    0<mg(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du))lim inftt1t0z(s)dslim suptt1t0z(s)ds(m+ε1+ε2)g(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du)). (3.6)

    For ε1,ε2, we can obtain

    limtt1t0z(s)ds=mg(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du)). (3.7)

    (A2) When βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du)<0, z(t) comes to extinct, limtz(t)=0. By Itô's formula, we have

    dlnx(t)[r(θ+K(1θ))bxσ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]dt+σ1dB1(t)+Γln(1+γ1(u))˜N(du,dt) (3.8)

    and

    dlnx(t)[rθbxab2ηε2σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]dt+σ1dB1(t)+Γln(1+γ1(u))˜N(du,dt). (3.9)

    Integrating both sides of (3.8) and (3.9) from 0 to t and letting ηε2=rθ2, we obtain

    lnx(t)lnx(0)[r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]tbt0x(s)ds+t0σ1dB1(s)+t0Γln(1+γ1(u))˜N(du,ds)

    and

    lnx(t)lnx(0)[rθab2rθ2σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)]tbt0x(s)ds+t0σ1dB1(s)+t0Γln(1+γ1(u))˜N(du,ds).

    Similar to (A1), by Lemma 3 and Assumption 1, we can get

    1b(rθ2ab2σ212Γ[γ1(u)ln(1+γ1(u))]λ(du))lim inftt1t0x(s)dslim suptt1t0x(s)ds1b(r(θ+K(1θ))σ212Γ[γ1(u)ln(1+γ1(u))]λ(du)).

    (A3) From (3.5), we can deduce that

    lim inftt1t0z(s)dsmg(βσ232Γ[γ3(u)ln(1+γ3(u))]λ(du))>0.

    The conclusion is confirmed.

    Moreover, when γi(u)=0 (i=1,2,3), this means that the population will not suffer drastic environmental changes. So, System (1.1) produces the following system:

    {dx(t)=[rx(t)(θ+K(1θ)K+z(t))bx2(t)ax(t)z(t)1+b1(x(t)+y(t))+b2z(t)ηx(t)y(t)b3+x(t)]dt+σ1x(t)dB1(t),dy(t)=[ηx(t)y(t)b3+x(t)cy2(t)dy(t)z(t)1+b1(x(t)+y(t))+b2z(t)γy(t)]dt+σ2y(t)dB2(t),dz(t)=[βz(t)gz2(t)m+x(t)+y(t)]dt+σ3z(t)dB3(t). (4.1)

    In this part, we solve the stochastically ultimately bounded problem for the system solution. Before the proof we need preparation.

    Definition 2. ([31]) The solution of System (1.1) is called stochastically ultimately bounded, for any ε(0,1) if there exists a constant H=H(ε) such that for any initial value W0=(x0,y0,z0) in R3+, the solution W(t)=(x(t),y(t),z(t)) of System (1.1) has the property that

    lim suptP{|W(t)|>H}<ε.

    Theorem 4. The solution of System (1.1) is stochastically ultimately bounded for any initial value W0=(x0,y0,z0) in R3+.

    Proof. First, define a function V:R3+R+

    V21(x,y,z)=x2+y2+z2+(m+x+y)z2V1(x,y,z)+V2(x,y,z).

    By Itô's formula, we can get

    dV21(x(t),y(t),z(t))=LV21(x(t),y(t),z(t))dt+[σ1x(t)dB1(t)+σ2y(t)dB2(t)]z2+(m+x+y)[2z2σ3dB3(t)]+2σ1x2dB1(t)+2σ2y2dB2(t)+2σ3z2dB3(t).

    So we have

    LV1(x,y,z)2x(rxbx2)+σ21x2+2y(ηycy2)+σ23y2+2βz2+σ22z2 (4.2)

    and

    LV2(x,y,z)=[m+rx(θ+K(1θ)K+z)bx2ax(t)z(t)1+b1(x(t)+y(t))+b2z(t)ηx(t)y(t)b3+x(t)+ηx(t)y(t)b3+x(t)cy2(t)dy(t)z(t)1+b1(x(t)+y(t))+b2z(t)γy(t)]z2+2(m+x+y)z2(βgzm+x+y)+σ23(m+x+y)z2. (4.3)

    Rectifying (4.2) and (4.3) yields

    LV21(x,y,z)[m+rxbx2cy2γy]z2+2(m+x+y)βz22gz3+σ23(m+x+y)z2+(2r+σ21)x22bx3+(2η+σ22)y22cy3+(2β+σ23)z2=[m+rxbx2cy2γy+(2β+σ23)(m+x+y)]z22gz3+(2r+σ21)x22bx3+(2η+σ22)y22cy3+(2β+σ23)z2. (4.4)

    Define the function

    R(t)=etV21(x,y,z);

    we can obtain

    LR=et(V21+LV21)et{(m+x+y)z2+[m+rxbx2cy2γy+(2β+σ23)(m+x+y)]z22gz3+(2r+σ21)x22bx3+(2η+σ22)y22cy3+(2β+σ23)z2}. (4.5)

    From the above equation we can obtain that there exists a positive number G such that LWGet. Therefore integrating both sides of (4.5) from 0 to t gives

    R(t)R(0)+G(et1)+t0et{(m+x+y)[2z2σ3dB(t)]+2σ1x2dB(t)+2σ2y2dB(t)+2σ3z2dB(t)}ds. (4.6)

    Then, the expectations are taken at both ends of (4.6), so the following results can be obtained

    E(et{(m+x+y)z2+x2+y2+z2})R(0)+G(et1).

    Therefore, we have

    E|W(t)|2=E(x2+y2+z2)etR(0)+G(1et)G1.

    Using Chebyshev inequality, we obtain

    P{|W(t)|>H}E|W(t)|2H2. (4.7)

    Next, taking the upper limit of (4.7) gives

    lim suptP{|W(t)|>H}G1H2=ε2<ε,  a.s.

    where ε(0,1) and H=22G1ε.

    The conclusion is confirmed.

    Let X(t) be a homogeneous Markov process in Eh (Eh denotes Euclidean h-space) described by the stochastic equation

    dX(t)=g(X)dt+lψ=1σψdBu(t).

    The diffusion matrix is given as follows:

    Φ(x)=(aij(x)),  aij(x)=lψ=1σiψσjψ.

    If there exists a bounded domain UEh with a regular boundary, then the following lemma holds:

    Lemma 4. ([32]) The Markov process X(t) has a unique stationary distribution ς() if it satisfies the following conditions:

    (A.1):Suppose a positive number M makes di,j=1aij(x)ζiζjM|ζ|2, xU, ξRd.

    (A.2):There exists a C2function such that LV is negative for R3+U. Then we have

    P{limT1TT0f(X(t))dt=Ehf(x)μ(dx)}=1

    for xEh, where f() is a function integrable with respect to the measure ς.

    To verify the condition (A.2), it is necessary to prove that there exist a neighborhood U and a nonnegative function V(x,y,z) such that LV is negative for any EhU.

    Lemma 5. ([33]) For s>0, the following inequality holds:

    s(1s)+2s2s. (4.8)

    Theorem 5. According to Lemma 4, for any initial value (x0,y0,z0), there exists an ergodic stationary distribution for System (4.1) if the following conditions hold.

    b2η(rσ212ab2)2r(b3b+1)(b+1)2(γ+db2+σ222)>0,  2db2+2γ+σ22η<0,  σ232β<0,c2γη2γ(c+2bηr(b+1)Aηr2b)>0,  and  3bη2γ(c+2bηr(b+1)Aηr2b)>0.

    Proof. Now we prove the condition (A.2). According to the inequality b(xrb)2>0, we derive

    L(x)rxbx2r(b3+x)+rb3+r2b.

    Define V11(x,y)=lny+Ax, where A is a positive constant which will be determined later; we have

    LV11(x,y)=ηxb3+x+cy+dz1+b1(x+y)+b2z+γ+σ222Ar(b3+x)+A(rb3+r2b)2ηArx+γ+σ222+A(rb3+r2b)+db2+cy. (4.9)

    Then define V12=b2r2x+br(b+1)(lnx) and use Lemma 5; we can obtain

    LV12(x,y)b2r2[rx(θ+K(1θ)1+z)bx2]+brxbr(b+1)(rσ212ab2)+bηyr(b+1)brxbr(b+1)(rσ212ab2)+bηyr(b+1). (4.10)

    Next, we define V13(x,y)=V11(x,y)+2Aηr2bV12(x,y)+1γ(c+2bnr(b+1)Aηr2b)y. Combining (4.9) and (4.10), we have the following inequality

    LV13(x,y)2ηArx+γ+σ222+A(rb3+rb)+db2+cy+2Aηr2b[brxbr(b+1)(rσ212ab2)+bηyr(b+1)]+(ηxyb3+xcy2γy)1γ(c+2bηr(b+1)Aηr2b)2br(b+1)(rσ212ab2)Aηr2b+γ+σ222+db2+A(rb3+rb)+ηγ(c+2bηr(b+1)Aηr2b)xyc2γy2. (4.11)

    Choose

    A=b3η(rσ212ab2)2r2(b3b+1)2(b+1)2.

    So we have

    LV13(x,y)b2η(rσ212ab2)2r(b3b+1)(b+1)2+db2+γ+σ222+ηγ(c+2bηr(b+1)Aηr2b)xyc2γy2B+ηγ(c+2bηr(b+1)Aηr2b)xyc2γy2B+η2γ(c+2bηr(b+1)Aηr2b)x2[c2γη2γ(c+2bηr(b+1)Aηr2b)]y2, (4.12)

    where B=b2η(rσ212ab2)2r(b3b+1)(b+1)2(γ+db2+σ222)>0.

    In the next step, we make

    V14(x,y,z)=(yi+zi)

    and i(0,1) is a positive number. By Itô's formula, we have

    LV14=iyi[ηxb3+xcydz1+b1(x+y)+b2zγ(1+i)σ222]izi[βgzm+x+y(1+i)σ232]iyix(db2+γ+(1+i)σ222η)+b3(db2+γ+(1+i)σ222)b3+x+izi[(1+i)σ232β]+icy1i+igmz1ii(2db2+2γ+(1+i)σ22η)yi+izi[(1+i)σ232β]+icy1i+igmz1i. (4.13)

    Let us choose i sufficiently small such that

    2db2+2γ+(1+i)σ22η<0,  (1+i)σ232β<0.

    Finally, we define the function V15=RV13+V14+3Rx+(m+x+y)z2, where R is a positive constant satisfying RB+fu1+fu2+fu3=2, in which fu1,fu2 and fu3 are bounded functions on [0,) and fui=supt0fi(t) (i=1,2,3); it will be determined later.

    According to (4.3), we can obtain

    LV15RB+i(2db2+2γ+(1+i)σ22η)yiR[c2γη2γ(c+2bηr(b+1)Aηr2b)]y2R[3bη2γ(c+2bηr(b+1)Aηr2b)]x2+izi[(1+i)σ232β]+icy1i+igmz1i2gz3+3Rrx+[m+rxbx2+ηycy2+(m+x+y)(σ23+2β)]z2=f1+f2+f3RB, (4.14)

    where

    f1=R[c2γη2γ(c+2bηr(b+1)Aηr2b)]y2+i(2db2+2γ+(1+i)σ22η)yi+icy1i,f2=2gz3+[m+rxbx2+ηycy2+(m+x+y)(σ23+2β)]z2+izi[(1+i)σ232β]+igmz1i,f3=3RrxR[3bη2γ(c+2bηr(b+1)Aηr2b)]x2.

    With the condition that c2γη2γ(c+2bηr(b+1)Aηr2b)>0, 2bη2γ(c+2bηr(b+1)Aηr2b)>0. Denote

    Σ(x,y,z)=f1+f2+f3RB.

    Then we have

    Σ(x,y,z){Σ(+,y,z), as x+,Σ(x,+,z), as y+,Σ(x,y,+), as z+,RB+fu1+fu2++fu32, as x0+, y0+ or z0+. (4.15)

    Therefore, we can deduce that

    LV15(x,y,z)1 (4.16)

    for (x,y,z)R3+U, which implies that the condition (A.2) in Lemma 4 is satisfied.

    The next step will be to prove the condition (A.1) and the following is the diffusion matrix of the System (4.1):

    ˜A(x;y;z)=(σ21x2000σ22y2000σ23z2).

    Choose ˜M=minx,y,zUR+3{σ21x2,σ22y2,σ23z2} such that

    σ21x2ζ21+σ22y2ζ22+σ23z2ζ23˜M|ζ2|,  for  all  (x,y,z)U, ζR3.

    Therefore we can conclude that the condition (A.1) in Lemma 4 holds. Further, from Lemma 4, we can infer that System (4.1) is ergodic and has a unique stationary distribution.

    In this section, to verify the conditions obtained by theorems, we take the determined initial values x0=2.9, y0=1.4 and z0=0.5 for the numerical simulation of System (1.1). In addition, let σ1=σ2=σ3=0.6 and γ1=γ2=γ3=0.06. The figures for the numerical simulations are as follows, where the left figure shows the numerical simulation of the stochastic model with white noise and Lévy noise, and the right figure shows the numerical simulation of the deterministic model.

    Example 1.

    As shown on the left in Figure 1, in order to verify the case of extinction of both the predator and prey populations in Theorem 2, we chose the appropriate parameters r=0.1,θ=0.09,K=0.35,b=0.8,a=0.27,b1=0.16,b2=0.5, η=0.015,b3=0.08,c=0.08,d=0.004,γ=0.06,β=0.013,g=0.01,m=0.01, σ1=σ2=σ3=0.6 and Γ1=Γ2=Γ3=0.06; then, we have 0.1×(0.09+0.35×0.01)0.622Γ[0.06ln(1+0.06)]λ(du)0.172<0, 0.0150.622Γ[0.06ln(1+0.06)]λ(du)0.003<0 and 0.130.622Γ[0.06ln(1+0.06)]λ(du)0.168<0. In this case, the populations of x(t),y(t) and z(t) all tend to become extinct, in accordance with the conclusion obtained in Theorem 2. Compared to the graph on the right, the curve of the stochastic model converges to zero with sharp fluctuations, while the curve of the deterministic model is smooth and takes longer to converge to zero. This shows that random factors accelerate the rate of population extinction when the conditions of Theorem 2 hold.

    Figure 1.  Select the following parameter values: r=0.1,θ=0.09,K=0.35,b=0.8,a=0.27,b1=0.16,b2=0.5,η=0.015, b3=0.08,c=0.08,d=0.004,γ=0.06,β=0.013,g=0.01,m=0.01. Then susceptible prey populations, infected prey populations, and predator populations tend to become extinct.

    Example 2.

    When 0.0150.622Γ[0.06ln(1+0.06)]λ(du)0.003<0, the infected prey population tends to become extinct. This is illustrated in Figures 24.

    Figure 2.  Susceptible prey populations and infected prey populations become extinct and predator populations persist. Select the following parameter values: r=0.1,θ=0.09,K=0.35,b=0.8,a=0.27,b1=0.16,b2=0.5,η=0.015, b3=0.08,c=0.08,d=0.004,γ=0.06,β=0.38,g=0.01,m=0.01.
    Figure 3.  Select the following parameter values: r=21.45,θ=0.09,K=0.35, b=0.8,a=0.27,b1=0.16,b2=0.5,η=0.015, b3=0.08,c=0.08,d=0.004,γ=0.06,β=0.01,g=0.01,m=0.01. Then the susceptible prey populations persist and populations of infected prey and predator populations become extinct.
    Figure 4.  Select the following parameter values: r=21.45,θ=0.09, K=0.35,b=0.8,a=0.27,b1=0.16,b2=0.5,η=0.015,b3=0.08, c=0.08,d=0.004,γ=0.06,β=0.19,g=0.01,m=0.01. Then the infected prey populations become extinct, and susceptible prey populations and predator populations persist.

    In order to verify the conditions of (A1) in Theorem 3, the numerical simulation we made by selecting suitable parameters is shown in Figure 2. Figure 2 shows that when r=0.1,θ=0.09,K=0.35,b=0.8,a=0.27,b1=0.16,b2=0.5,η=0.015,b3=0.08, c=0.08,d=0.004,γ=0.06,β=0.38,g=0.01,m=0.01, σ1=σ2=σ3=0.6 and Γ1=Γ2=Γ3=0.06; then, we have 0.10.622Γ[0.06ln(1+0.06)]λ(du)0.08<0, 0.0150.622Γ[0.06ln(1+0.06)]λ(du)0.003<0 and 0.380.622Γ[0.06ln(1+0.06)]λ(du)0.199>0. At this time, susceptible and infected prey populations x(t) and y(t) tend to become extinct and predator populations y(t) tend to persist. Compared to the deterministic model, the left curve with the effect of white noise and Levy noise changes more dramatically.

    In order to verify the conditions of (A2) in Theorem 3, the numerical simulation we made by selecting suitable parameters is shown in Figure 3. We chose r=21.45 and β=0.01 and the other parameters take the same value. Then we have 21.450.622Γ[0.06ln(1+0.06)]λ(du)>0 and 0.010.622Γ[0.06ln(1+0.06)]λ(du)<0. At this point, as seen in Figure 3, susceptible prey populations tend to persist and predator populations tend to become extinct. Whereas in the right picture, x(t) is gradually leveling off and z(t) is not extinct, but slowly rising.

    In order to verify the conditions of (A3) in Theorem 3, the numerical simulation we made by selecting suitable parameters is shown in Figure 4. We set r=21.45 and β=0.19 and the other parameters take the same value. Then we have 21.450.622Γ[0.06ln(1+0.06)]λ(du)>0 and 0.190.622Γ[0.06ln(1+0.06)]λ(du)>0. From Figure 3, we can see that both the susceptible prey populations and predator populations tend to be persistent. This satisfies the condition given by (A3) in Theorem 3. z(t) grows more rapidly in the deterministic model than in the model with white noise versus Lévy noise.

    Example 3.

    To verify the condition of Theorem 5 that System (1.1) has an ergodic stationary distribution, we chose the following parameter values: r=18,θ=0.09,K=0.35,b=0.8,a=0.27,b1=0.16,b2=4.6,η=0.78, b3=0.18,c=0.7,d=0.004,γ=0.19,β=0.65,g=0.012 and m=0.012. From the conditions obtained in Theorem 5, it follows that η2γ(c+2bηr(b+1)Aηr2b)1.863<c2γ2.579, η2γ(c+2bηr(b+1)Aηr2b)1.863<3b=2.4, b2η(rσ212ab2)2r(b3b+1)(b+1)22.360>γ+db2+σ222=0.37, 2db2+2γ+σ220.741<η=0.78 and σ232=0.18<0.65. As shown in Figure 5, the sample paths are concentrated within regions of circularity or ellipticity, which indicates that the system is stochastically stable.

    Figure 5.  Select the following parameter values: r=18,θ=0.09,K=0.35, b=0.8,a=0.27,b1=0.16,b2=4.6,η=0.78,b3=0.18, c=0.7,d=0.004,γ=0.19, β=0.65,g=0.012,m=0.012. The distribution of the sample path in the phase space.

    This paper discusses the dynamical properties of predator-prey models with fear effects and disease transmission in prey population. Meanwhile, susceptible prey populations, infected prey populations and predator populations are affected by white noise and Lévy noise. By constructing the appropriate Lyapunov equation, we proved the uniqueness of the global positive solution of System (1.1). From Theorem 2, it is clear that under certain conditions, Lévy noise can lead to population extinction. Furthermore, the fear effect can also lead to population size change. When the fear effect is too large, it is more likely to result in population extinction. We also explored the existence and extinction of susceptible prey populations and predator populations under conditions when infectious diseases prevalent among prey populations are effectively prevented and infected prey populations die out in Theorem 3. Then, we studied the stochastic ultimate boundedness of System (4.1) and the ergodic stationary distribution under certain conditions without the influence of Lévy noise. Finally, the numerical simulations were performed at the end to further illustrate the validity of the theoretical results. Adding the influence of environmental factors to the model made it more consistent with the predator-prey relationship in the ecosystem. This shows that stochastic factors have an effect on the behavior of population dynamics and in some cases can accelerate the extinction of populations. The fear effect also affects the population size change; when the fear effect is stronger, the population is more likely to become extinct.

    This research was supported by the Natural Science Foundation of Heilongjiang Province (No. LH2022A002, No. LH2021A018), National Natural Science Foundation of China (No. 12071115) and Fundamental Research Funds for the Central Universities (No. 2572020BC09).

    The authors declare that there is no conflict of interest.



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