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Research article Special Issues

Modelling and development of sustainable energy systems

  • Due to the recent climate change, organizations all over the globe are developing plans for reducing carbon emissions by developing clean energy technologies and energy efficient devices. However, the path for transition to green energy system is still unclear and in general, the representation of green energy supply for transition pathways is limited. Therefore, this study outlines a plan for getting Swedish energy sector completely carbon neutral by 2050. The approach can also be applicable to the majority of nations worldwide. Computer based simulations are performed on Energy PLAN software for making clean, green and sustainable energy system that can balance every component of entire energy system during the study period 2022 to 2050. This study takes into account the sustainable use of renewable sources for all economic sectors as well as the interchange of energy with nearby nations under the two scenarios. Additionally, the energy system works in tandem with other industries to create a fully carbon-free environment. The results revealed that, 50% de-carbonization is possible till 2035 and 100% de-carbonization is possible till 2050. This enables a discussion of how ambitious 10-year goals might serve as a first step toward the mid-century elimination of fossil fuels from the energy sector.

    Citation: Muhammad Amir Raza, M. M. Aman, Abdul Ghani Abro, Muhammad Shahid, Darakhshan Ara, Tufail Ahmed Waseer, Mohsin Ali Tunio, Shakir Ali Soomro, Nadeem Ahmed Tunio, Raza Haider. Modelling and development of sustainable energy systems[J]. AIMS Energy, 2023, 11(2): 256-270. doi: 10.3934/energy.2023014

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  • Due to the recent climate change, organizations all over the globe are developing plans for reducing carbon emissions by developing clean energy technologies and energy efficient devices. However, the path for transition to green energy system is still unclear and in general, the representation of green energy supply for transition pathways is limited. Therefore, this study outlines a plan for getting Swedish energy sector completely carbon neutral by 2050. The approach can also be applicable to the majority of nations worldwide. Computer based simulations are performed on Energy PLAN software for making clean, green and sustainable energy system that can balance every component of entire energy system during the study period 2022 to 2050. This study takes into account the sustainable use of renewable sources for all economic sectors as well as the interchange of energy with nearby nations under the two scenarios. Additionally, the energy system works in tandem with other industries to create a fully carbon-free environment. The results revealed that, 50% de-carbonization is possible till 2035 and 100% de-carbonization is possible till 2050. This enables a discussion of how ambitious 10-year goals might serve as a first step toward the mid-century elimination of fossil fuels from the energy sector.



    Brucellosis, a zoonotic disease, is a natural epidemic disease that is not only prevalent among livestock and humans but also widely spread in wild animals [1,2]. There are human and animal brucellosis in most countries of the world, and high-risk areas of epidemics are mainly distributed in developing countries, such as Syria, Jordan, Zambia, Mongolia [3,4,5,6]. It has brought huge losses to the livestock industry worldwide and serious health problems to livestock-related practitioners, there are hundreds of thousands of new cases reported annually [6,7,8]. Infected domestic and wild animals and their excreta are the main source of infection, it is contact and pathogen infection which are the main modes of brucellosis transmission [9]. Human brucellosis is rarely transmitted to susceptible animals, and there is no infection between people reported [10,11]. Therefore, it is the eradication of animal brucellosis that is the only way to solving human health problem, and understanding the mechanisms and risk factors of the spread of brucellosis is one of the first problems that must be solved.

    Brucellosis is transmitted to susceptible individuals mainly by contact with infectious individuals or by sucking pathogens from the environment [8]. In animals, the transmission of brucellosis mainly occurs between sexually mature animals, young animals may also be infected, but generally do not have any clinical manifestations and serological tests are usually non-positive, and the infection between young animals is so little as to be almost invisible [12]. In other words, sexually mature animals are very susceptible to brucellosis, latent infections may be found in young animals, but they are generally resistant [9]. It is important that many infected animals have a longer incubation period and that these animals remain serologically non-positive during this period. That is to say, latent animals may not be infectious and it is almost impossible to be found through detection, which is an important risk factor in the elimination of brucellosis [9]. Therefore, the impact of these mechanisms on brucellosis is worthy to be studied using mathematical models.

    Statistical methods such as descriptive statistics, correlation analysis and time series analysis have been widely used for quantitative assessment of risk management measures for brucellosis, among which is very worthy of concern about the study of bison, elk and livestock brucellosis (see [13,14,15,16,17]). Theoretical studies on the impacts of the transmission mechanisms of brucellosis and applied studies on the assessments of risk management measures have also been studied using the kinetic model (see [18,19,20,21,22]). Especially in recent years, many kinetic models with indirect transmission have been established to analyze brucellosis transmission (see [23,24,25,26,27]). Although there have been many studies on brucellosis, there are still many transmission mechanisms and risk factors that are not considered in existing models. For example, infected individuals may have no infectivity in the early stage, during which time is different; and animals that are not sexually mature are hardly infected with direct and indirect modes [9]. Therefore, in the present work, a multi-stage dynamic model with distributed time delay is proposed involving the above risk factors and general nonlinear incidences. The existence and uniqueness of the endemic equilibrium is analyzed, and the local and global asymptotic stability of equilibria is proved.

    The rest of this manuscript is constructed as follows. The dynamic model with distributed time delay and some preliminary results are given in Section 2. In Section 3, the content of research is the global dynamics of the disease-free equilibrium. The global stability of the equilibrium of persistent infection are analyzed in Section 4. In Section 5, the stability results are further explained by numerical simulation. A summary and further discussion is proposed in Section 6.

    According to the transmission mechanisms of animal brucellosis, we classify animal population into three compartments: The young susceptible compartment S1(t), the adult susceptible compartment S2(t) (sexually mature), the infected compartment I(t). Similar to the definition in literature [25], B(t) can be defined as the concentration or number of pathogens in the environment. Some explanations and assumptions about the kinetic model are listed as follows. (Ⅰ) Since brucellosis can cause abortion and significantly reduce the survival rate of young animals, we suppose that infected animals have no birth rate. (Ⅱ) The supplementary rate of young susceptible animal population S1(t) is mainly derived from birth and import, it is assumed that the supplementary rate is A+bS2(t). (Ⅲ) Usually, there are two different stages for infected animals, which are no infection force in the early stage and are infectious carriers when infected animals begin to shed brucella. Therefore, we make use of a delay τ to describe the time from a susceptible individual to a infectious individual, and since the length of this time is varied, thus the delay τ is a distributed parameter in the interval [0,h], where h is the maximum value of the delay. As a result, the susceptible class S2(t) is reduced due to infection at the rate S2g(B)+S2h0ρ(τ)f(I(tτ))e(μ2+c)τdτ. (Ⅳ) Since the infected animal sheds the pathogen after the time τ, then the pathogen shedding rate of the infected animal is h0ρ(τ)h(I(tτ))e(μ2+c)τdτ. (Ⅴ) In animal breeding, only the basic ewes breed newborns, and adult animals are widely used for slaughter or trade, then the birth rate b of adult animals is assumed to be less than the elimination rate μ2 of adult animals. Therefore, the modelling for animal brucellosis is given through the following distributed time-delay system:

    {dS1dt=A+bS2μ1S1σ1S1,dS2dt=σ1S1S2g(B)S2h0ρ(τ)f(I(tτ))e(μ2+c)τdτμ2S2,dIdt=S2h0ρ(τ)f(I(tτ))e(μ2+c)τdτ+S2g(B)(μ2+c)I,dBdt=h0ρ(τ)h(I(tτ))e(μ2+c)τdτdB. (2.1)

    Here, b is the birth rate of adult animals. μ1 and μ2 are the elimination rates of young and adult animals, respectively. σ1 is the transfer rate from young susceptible individuals to sexually mature individuals. The culling rate is defined by c and d is the decay rate of the pathogen. f(I) and g(B) are contact and indirect infection rates, respectively. ρ(τ) is a distributed function, it is non-negative, continuous and h0ρ(τ)dτ=1.

    The initial conditions for system (2.1) are given as follows:

    {S1(x)=ϕ1(x),S2(x)=ϕ2(x),I(x)=ϕ3(x),B(x)=ϕ4(x),x[h,0],h>0,ϕ=(ϕ1,ϕ2,ϕ3,ϕ4)C+C. (2.2)

    Here, C denotes the Banach space C([h,0],4) of continuous functions mapping the interval [h,0] into 4 with the sup-norm ϕ=supx[h,0]|ϕi(x)|,i=1,2,3,4 for ϕC. The nonnegative cone of C is defined as C+=C([h,0],4+).

    In order to make epidemiological significance for system (2.1), f,g and h are assumed to be second-order continuous differentiable functions and satisfy the following hypotheses:

    (H1) f(0)=g(0)=h(0)=0 and f(I),g(B),h(I)>0 for I,B>0;

    (H2) f(I),g(B)>0 and f(I),g(B)0 for B,I0;

    (H3) h(I)>0 and h(I)0 for I0.

    The function f may be βIp or saturation incidences kln(1+λIk) and βIp1+kIp with constants β,p,λ,k>0 [28,29]. The pathogen infection rate g may be λB1+TB or η(1eαB) with constants λ,η,α>0 and T0 [30]. The function h may be kI with constants k>0 [31].

    It is easy to verify that the system (2.1) always has a disease-free equilibrium E0=(S01,S02,0,0), where

    S01=Aμ2μ2(μ1+σ1)bσ1,S02=Aσ1μ2(μ1+σ1)bσ1.

    The reproduction number of sytem (2.1) is given by the following expression:

    R0=nS02fI(0)μ2+c+nS02gB(0)hI(0)d(μ2+c)=R01+R02. (2.3)

    where n=h0ρ(τ)e(μ2+c)τdτ. e(μ2+c)τ denotes the probability of survival from a newly infected susceptible individual to an infectious individual. n is the total survival rate of infected individuals. fI(0) is the infection rate by an infectious individual. gB(0) is the infection rate of brucella. 1μ2+c is the average life span of infected individual. hI(0)d represents the total number of brucella shed by infectious individuals. Therefore, based on the explanation in the literature [26], R0 relies on direct and indirect infection and can be divided into two parts R01 and R02.

    In the next section, we establish that the solution of system (2.1) is non-negative and bounded and analyze the uniqueness of the equilibrium point of persistent infection. The following qualitative results indicate the nonnegativity and boundedness of the solution of system (2.1) with initial conditions (2.2).

    Theorem 2.1. (S1(t),S2(t),I(t),B(t)) is the solution of system (2.1) with the initial conditions (2.2), then S1(t),S2(t),I(t),B(t) are nonnegative and ultimately bounded.

    Proof. Since (˙S1(t)+˙S2(t))=A>0 for t[0,+) when S1(t)=S2(t)=0, it implies that S1(t)+S2(t)0 for all t[0,+). Therefore, if S1(t)=0, then S2(t)0 and ˙S1(t)=A+bS2>0, so that S1(t)0. We denote

    a1(t)=h0ρ(τ)f(I(tτ))e(μ2+c)τdτ+g(B)+μ2,a2(t)=S2(t)(h0ρ(τ)f(I(tτ))e(μ2+c)τdτ+g(B)),

    and

    a3(t)=h0ρ(τ)h(I(tτ))e(μ2+c)τdτ.

    From the last three equations in (2.1), it can conclude that

    S2(t)=S2(0)et0a1(η)dη+σ1t0etηa1(ξ)dξS1(η)dη0,I(t)=I(0)e(μ2+c)t+t0e(μ2+c)(tη)a2(η)dη0,

    and

    B(t)=B(0)edt+t0ed(tη)a3(η)dη0

    for all t0. Thus, S1(t),S2(t),I(t),B(t)0 for t0.

    We now analyze the boundedness of the solution of system (2.1). In fact,

    (˙S1(t)+˙S2(t)+˙I(t))Aμ1S1(μ2b)S2(μ2+c)I
    Aμ(S1(t)+S2(t)+I(t)),

    where μ=min{μ1,μ2b}.

    Hence, lim supt(S1(t)+S2(t)+I(t))Aμ, it implies that lim suptI(t)Aμ and lim suptB(t)ndh(Aμ). Therefore, S1(t),S2(t),I(t),B(t) are ultimately bounded.

    Since the solution of system (2.1) is nonnegative and ultimately bounded, the set

    Ω={(S1(),S2(),I(),B())C+:S1+S2+IAμ,Bndh(Aμ)},

    is positively invariant for system (2.1).

    In order to analyze the uniqueness of the positive solution of system (2.1), the following lemma is given:

    Lemma 2.1. Assume that conditions (H1)(H3) are satisfied, the functions f(I)I, h(I)I, g(B)B and g(h(I))I are monotonic decreasing for I,B>0.

    Proof. Since f(I)0, it shows that f(I) is monotonic decreasing, it follows that

    f(I)I=f(I)f(0)I0=f(ξ1)f(I),ξ1(0,I),

    and

    (f(I)I)=f(I)If(I)I20.

    That is to say, f(I)I is a monotonically decreasing function. On the basis of the above method, it can show that h(I)I and g(B)B are also monotonic decreasing. Noting that

    g(h(I))I=g(h(I))g(h(0))h(I)h(0)h(I)I=g(h(ξ2))h(ξ3)g(h(I))h(I),ξ2,ξ3(0,I),

    It can deduce that

    (g(h(I))I)=g(h(I))h(I)Ig(h(I))I20.

    Therefore, g(h(I))I is also monotonic decreasing.

    For system (2.1), the endemic equilibrium E=(S1,S2,I,B) can be derived from the following algebraic equations:

    {A+bS2=μ1S1+σ1S1,σ1S1=S2(nf(I)+g(B))+μ2S2,S2(nf(I)+g(B))=(μ2+c)I,nh(I)=dB. (2.4)

    By direct calculation, it can be written as

    {S1=A+bS2μ1+σ1,m(S2)=S2(nf(I)+g(B)),S2(nf(I)+g(B))=(μ2+c)I,B=H(I).

    where m(S2)=Aσ1(μ2(μ1+σ1)bσ1)S2μ1+σ1 and H(I)=ndh(I).

    Let us define

    F1(S2,I)m(S2)S2(nf(I)+g(H(I))),F2(S2,I)S2(nf(I)+g(H(I)))(μ2+c)I.

    Similar to the method of analysis in literature [26], using Lemma 2.1, the following result can be summarized:

    Theorem 2.2. Assume that conditions (H1)(H3) hold. Then there is a unique positive solution E=(S1,S2,I,B) of system (2.1) if and only if R0>1.

    In this section, we show that the global stability of the equilibrium point E0 of system (2.1) is independent of the initial value. The following conclusions are first obtained.

    Lemma 3.1. Assume that conditions (H1)(H3) hold. The disease-free equilibrium E0 is locally asymptotically stable if R01 and is unstable if R0>1.

    Proof. The characteristic equation at E0 is

    |λ+μ1+σ1b00σ1λ+μ2S02fI(0)Γ(λ)S02gB(0)00λ+μ2+cΓ(λ)S02fI(0)S02gB(0)00hI(0)Γ(λ)λ+d|=0, (3.1)

    where

    Γ(λ)=h0ρ(τ)e(μ2+c+λ)τdτ.

    It follows from (3.1) that

    (λ+μ1+σ1)(λ+μ2)((λ+d)(λ+μ2+cΓ(λ)S02fI(0))Γ(λ)S02gB(0)hI(0))=bσ1((λ+d)(λ+μ2+cΓ(λ)S02fI(0))Γ(λ)S02gB(0)hI(0)).

    That is,

    (λ+μ1+σ1)(λ+μ2)(λ+d)(λ+μ2+c)bσ1(λ+d)(λ+μ2+c)
    =((λ+μ1+σ1)(λ+μ2)bσ1)((λ+d)Γ(λ)S02fI(0)+Γ(λ)S02gB(0)hI(0)).

    It follows that

    H1(λ)((λ+d)(λ+μ2+c)(λ+d)Γ(λ)S02fI(0)Γ(λ)S02gB(0)hI(0))=0,

    where H1(λ)=(λ+μ1+σ1)(λ+μ2)bσ1. Since μ1+σ1+μ2>0 and μ2(μ1+σ1)bσ1>0, then H1(λ) consists of two roots which are negative real parts. Therefore, we only analyze the distribution of the roots of the following equation:

    H2(λ)=(λ+d)(λ+μ2+c)(λ+d)Γ(λ)S02fI(0)Γ(λ)S02gB(0)hI(0)=0. (3.2)

    Assume now that R0>1, then

    H2(0)=d(μ2+c)dnS02fI(0)nS02gB(0)hI(0))<0,H2(+)=+.

    Hence H2(λ) has at least one positive root in [0,+), then E0 is unstable if R0>1.

    From (3.2), we have

    (λ+d)(λ+μ2+c)=Γ(λ)(λS02fI(0)+dS02fI(0)+S02gB(0)hI(0))=(μ2+c)F(λ)n(λR01+dR0),

    or

    (λ+d)(λμ2+c+1)=R0F(λ)n(λR01R0+d). (3.3)

    Next, considering the case R01. If λ=x+yi is a solution of (3.3), one shows that x<0. Otherwise, x0 implies

    |λ+d|>|λR01R0+d|,|λμ2+c+1|>1,|R0F(λ)n|1,

    and thus

    |(λ+d)(λμ2+c+1)|>|R0F(λ)n(λR01R0+d)|,

    this is a contradiction to (3.3). Therefore, all roots of Eq (3.3) have no zero and positive real parts when R01, this shows that E0 is locally asymptotically stable.

    Theorem 3.1. Assume that conditions (H1)(H3) are established. If R01, the disease-free equilibrium E0=(S01,S02,0,0) of system (2.1) is globally asymptotically stable.

    Proof. Since the functions f(I)I, g(B)B and h(I)I are decreasing, then we have

    nS2f(I)(μ2+c)IlimI0+nS02f(I)(μ2+c)I=nS02fI(0)μ2+cb1,S2g(B)dBlimB0+S02g(B)dB=S02gB(0)db2,nh(I)(μ2+c)IlimI0+nh(I)(μ2+c)I=nhI(0)μ2+c.

    Define

    J=(10nhI(0)μ2+c1),(a1,a2)=(b1,b2)J1.

    We find a1=R0 and define a Lyapunov functional L as follows:

    L(t)=L1(t)+L2(t)+L3(t),

    where

    L1=R0(S1S01S01lnS1S01+S2S02S02lnS2S02+I)+a2B,L2=R0S02h0Ψ(τ)f(I(tτ))dτ,L3=a2h0Ψ(τ)h(I(tτ))dτ,

    and

    Ψ(τ)=hτφ(s)ds,φ(s)=ρ(s)e(μ2+c)s.

    Then the derivative of L1 along the positive solutions of system (2.1) is

    dL1dt=R0(1S01S1)dS1dt+R0(1S02S2)dS2dt+R0dIdt+a2dBdt=R0(2A+bS02+σ1S01μ1S1(μ2b)S2S01AS1bS01S2S1σ1S02S1S2)+R0(S02g(B)+S02h0φ(τ)f(I(tτ))dτ(μ2+c)I)+a2(h0φ(τ)h(I(tτ))dτdB). (3.4)

    Calculating the derivative of L2(t) along the solutions of system (2.1), one obtains

    dL2dt=R0S02h0Ψ(τ)df(I(tτ))dtdτ=R0S02h0Ψ(τ)df(I(tτ))dτdτ=R0S02(Ψ(τ)f(I(tτ)))|h0+R0S02h0dΨ(τ)dτf(I(tτ))dτ=R0S02nf(I(t))R0S02h0φ(τ)f(I(tτ))dτ. (3.5)

    Similar to the above-used method, it can obtain that

    dL3dt=a2nh(I(t))a2h0φ(τ)h(I(tτ))dτ. (3.6)

    Combining the Eqs (3.4), (3.5) and (3.6), it follows that

    dLdt=dL1dt+dL2dt+dL3dt=R0μ1S01(2S1S01S01S1)+R0bS02(2S1S02S01S2S01S2S1S02)+R0(μ2b)S02(3S2S02S1S02S01S2S01S1)+R0(nS02f(I)(μ2+c)I,S02g(B)dB)((μ2+c)I,dB)T(R0,a2)(10nh(I)(μ2+c)I1)((μ2+c)I,dB)TR0(nS02fI(0)(μ2+c),S02gB(0)d)((μ2+c)I,dB)T(R0,a2)(10nhI(0)μ2+c1)((μ2+c)I,dB)T=(R01)(b1,b2)((μ2+c)I,dB)T0.

    Similar to the analysis of Theorem 1 in the literature [32], it follows from Lemma 3.1 that the disease-free equilibrium E0 is globally asymptotically stable by LaSalle's Invariance Principle [33].

    According to Lemma 3.1, the disease-free steady state solution E0 is unstable when R0>1. Using Theorem 4.2 in [34], the uniform permanence of system (2.1) can be proven, the process is ignored here. In this following section, by constructing a Lyapunov functional, the global stability of the equilibrium of persistent infection is proved. We first analyze its local stability.

    Lemma 4.1. Assume that conditions (H1)(H3) are ture, If R0>1, the endemic equilibrium E of system (2.1) exists and is locally asymptotically stable.

    Proof. For system (2.1), the characteristic equation at E is

    |λ+μ1+σ1b00σ1H3(λ)Γ(λ)S2fI(I)S2gB(B)0nf(I)g(B)H4(λ)S2gB(B)00Γ(λ)hI(I)λ+d|=0,

    where H3(λ)=λ+nf(I)+g(B)+μ2, H4(λ)=λ+μ2+cΓ(λ)S2fI(I). By simple calculation, one obtains

    (λ+d)(λ+μ2+c)Φ1(λ)=Φ2(λ)Γ(λ)((λ+d)S2fI(I)+hI(I)S2gB(B))=Φ2(λ)Γ(λ)nΛn(λS2fI(I)Λ+d),

    or

    (λ+d)(λμ2+c+1)Φ1(λ)=Φ2(λ)Γ(λ)nΛnμ2+c(λS2fI(I)Λ+d), (4.1)

    where

    Φ1(λ)=(λ+μ1+σ1)(λ+μ2+nf(I)+g(B))bσ1,Φ2(λ)=(λ+μ1+σ1)(λ+μ2)bσ1,Λ=S2fI(I)+1dS2hI(I)gB(B)

    Noting that from Lemma 1

    Λnμ2+c=S2fI(I)n+1dS2hI(I)gB(B)nμ2+cS2(f(I)nI+ndh(I)Ig(B)B)μ2+c=S2(f(I)n+g(B))I(μ2+c)=1.

    Assume λ=x+yi is a solution of (4.1). If x0, we then have

    |λ+d|>|λS2fI(I)Λ+d|,|λμ2+c+1|>1,|F(λ)n|1,

    and

    |Φ1(λ)Φ2(λ)|=|(λ+μ1+σ1)(λ+μ2+nf(I)+g(B))bσ1(λ+μ1+σ1)(λ+μ2)bσ1|=|λ+μ2+nf(I)+g(B)bσ1λ+μ1+σ1λ+μ2bσ1λ+μ1+σ1|=|M1+nf(I)+g(B)+M2iM1+M2i|>1,

    where M1=x+μ2bσ1(x+μ1+σ1)(x+μ1+σ1)2+y2>0, M2=y+bσ1y(x+μ1+σ1)2+y2. So it concludes that

    |(λ+d)(λμ2+c+1)Φ1(λ)|>|Φ2(λ)F(λ)nΛnμ2+c(λS2fI(I)Λ+d)|,

    which is a contradiction to (4.1). Therefore, the Eq (4.1) can not have any roots with a nonnegative real part, this implies that E is locally asymptotically stable if R0>1.

    Theorem 4.1. Assume that conditions (H1)(H3) hold. If R0>1, the endemic equilibrium E=(S1,S2,I,B) of system (2.1) is globally asymptotically stable.

    Proof. Define

    L1=S1S1S1lnS1S1+S2S2S2lnS2S2+IIIlnII+S2g(B)nh(I)(BBBlnBB).

    Finding the time derivative of L1 along the positive solutions of system (2.1) gives

    dL1dt=(1S1S1)dS1dt+(1S2S2)dS2dt+(1II)dIdt+S2g(B)nh(I)(1BB)dBdt=2A+bS2+σ1S1μ1S1(μ2b)S2S1AS1bS1S2S1σ1S2S1S2+S2g(B)+S2h0φ(τ)f(I(tτ))dτ(μ2+c)IIIS2g(B)IIS2h0φ(τ)f(I(tτ))dτ+S2g(B)nh(I)(h0φ(τ)h(I(tτ))dτdB+dB)S2g(B)nh(I)BBh0φ(τ)h(I(tτ))dτ.

    By the Eq (2.4), we get

    dL1dt=μ1S1(2S1S1S1S1)+(μ2b)S2(3S2S2S1S2S1S2S1S1)+bS2(2S1S2S1S2S1S2S1S2)+nS2f(I)(3S1S1S1S2S2S1II)+S2g(B)(3+g(B)g(B)S1S1S1S2S2S1IIS2g(B)IS2g(B)I)+S2h0φ(τ)f(I(tτ))dτIIS2h0φ(τ)f(I(tτ))dτ+S2g(B)(h(I)h(I)BBBh(I)Bh(I)+1)+S2g(B)nh(I)(h0φ(τ)h(I(tτ))dτnh(I)+BBnh(I))S2g(B)nh(I)BBh0φ(τ)h(I(tτ))dτ. (4.2)

    Since the function ν(x)=1x+lnx is nonpositive for x>0 and ν(x)=0 if and only if x=1, so we define

    L2=S2f(I)h0Ψ(τ)ν(f(I(tτ))f(I))dτ.

    A direct calculation shows that

    dL2dt=S2f(I)h0Ψ(τ)ddtν(f(I(tτ))f(I))dτ=S2f(I)h0Ψ(τ)ddτν(f(I(tτ))f(I))dτ=S2f(I)(Ψ(τ)ν(f(I(tτ))f(I))h0+h0φ(τ)ν(f(I(tτ))f(I))dτ)=S2f(I)h0φ(τ)ν(f(I(t))f(I))dτ+S2f(I)h0φ(τ)ν(f(I(tτ))f(I))dτ=S2f(I)h0φ(τ)(f(I)f(I)f(I(tτ))f(I)+lnf(I(tτ))f(I))dτ=nS2f(I)f(I)f(I)+S2f(I)h0φ(τ)(f(I(tτ))f(I)+lnf(I(tτ))f(I))dτ. (4.3)

    Define

    L3=S2g(B)nh0Ψ(τ)ν(h(I(tτ))h(I))dτ.

    Calculating the time derivative of L3(t), one obtains

    dL3dt=S2g(B)nh0Ψ(τ)ddtν(h(I(tτ))h(I))dτ=S2g(B)nh0Ψ(τ)ddτν(h(I(tτ))h(I))dτ=S2g(B)nh0φ(τ)(h(I)h(I)h(I(tτ))h(I)+lnh(I(tτ))h(I))dτ=S2g(B)h(I)h(I)+S2g(B)nh0φ(τ)(h(I(tτ))h(I)+lnh(I(tτ))h(I))dτ. (4.4)

    For system (2.1), the following Lyapunov functional is considered:

    L=L1+L2+L3.

    From (4.2), (4.3) and (4.4), we can get

    dLdt=μ1S1(2S1S1S1S1)+(μ2b)S2(3S2S2S1S2S1S2S1S1)+bS2(2S1S2S1S2S1S2S1S2)+nS2f(I)(3+f(I)f(I)S1S1S1S2S2S1IIS2f(I)IS2f(I)I)+S2g(B)(3+g(B)g(B)S1S1S1S2S2S1IIS2g(B)IS2g(B)I)+S2g(B)(h(I)h(I)BBBh(I)Bh(I)+1)+S2f(I)h0φ(τ)F(τ)dτ+S2g(B)nh0φ(τ)H(τ)dτ, (4.5)

    where

    h0φ(τ)F(τ)dτ=h0φ(τ)(S2f(I)IS2f(I)IS2If(I(tτ))S2f(I)I+lnf(I(tτ))f(I))dτ=h0φ(τ)(ν(S2If(I(tτ))S2f(I)I)ν(S2f(I)IS2f(I)I))dτ=h0φ(τ)ν(S2If(I(tτ))S2f(I)I)dτnν(S2f(I)IS2f(I)I), (4.6)

    and

    h0φ(τ)H(τ)dτ=h0φ(τ)(h(I)Bh(I)BBh(I(tτ))h(I)B+lnh(I(tτ))h(I))dτ=h0φ(τ)ν(Bh(I(tτ))h(I)B)dτnν(h(I)Bh(I)B). (4.7)

    it follows from (4.5), (4.6) and (4.7) that

    dLdt=μ1S1(2S1S1S1S1)+(μ2b)S2(3S2S2S1S2S1S2S1S1)+bS2(2S1S2S1S2S1S2S1S2)+nS2f(I)(f(I)f(I)1)(1f(I)If(I)I)+nS2f(I)(ν(S1S1)+ν(S1S2S1S2)+ν(S2f(I)IS2f(I)I)+ν(f(I)If(I)I))+S2g(B)((g(B)g(B)1)(1g(B)Bg(B)B)+(h(I)h(I)1)(1h(I)Ih(I)I))+S2g(B)(ν(S1S1)+ν(S1S2S1S2)+ν(S2g(B)IS2g(B)I)+ν(g(B)Bg(B)B))+S2g(B)(ν(h(I)Bh(I)B)+ν(h(I)Ih(I)I))+S2f(I)(h0φ(τ)ν(S2If(I(tτ))S2f(I)I)dτnν(S2f(I)IS2f(I)I))+S2g(B)n(h0φ(τ)ν(Bh(I(tτ))h(I)B)dτnν(h(I)Bh(I)B))μ1S1(2S1S1S1S1)+(μ2b)S2(3S2S2S1S2S1S2S1S1)+bS2(2S1S2S1S2S1S2S1S2)+nS2f(I)(f(I)f(I)1)(1f(I)If(I)I)+S2g(B)((g(B)g(B)1)(1g(B)Bg(B)B)+(h(I)h(I)1)(1h(I)Ih(I)I))

    By Lemma 2.1, it can conclude that

    dLdt=dL1dt+dL2dt+dL3dt0.

    The equality dLdt=0 suggests that S1S1=1, S1S2S1S2=1, f(I)f(I)=1 and g(B)g(B)=1, it implies that E is the maximum invariant set of system (2.1) in the set {dLdt=0}. Using Lemma 4.1, the endemic steady state E is globally asymptotically stable.

    By choosing a specific kernel function and some infection functions, system (2.1) can be evolved into different dynamic models with time delays. In this section, some such examples are used to further illustrate theoretical results.

    Example: Consider the kernel function ρ(τ)=δ(ττ0), where δ is the Dirac delta function. Then system (2.1) can be rewritten as

    {dS1dt=A+bS2μ1S1σ1S1,dS2dt=σ1S1αS2BβS2f(I(tτ0))e(μ2+c)τ0μ2S2,dIdt=αS2B+βS2f(I(tτ0))e(μ2+c)τ0(μ2+c)I,dBdt=kI(tτ0)e(μ2+c)τ0dB. (5.1)

    Where A,b,μ1,μ2,σ1,α,β,c,k and d>0, g(B)=αB and h(I)=kI. If f(I)=βI, it is easy to verify that f(I),g(B) and h(I) satisfy the assumptions (H1)(H3). Therefore, the basic reproduction number of system (5.1) can be defined as

    R0=βS02e(μ2+c)τ0μ2+c+kαS02e(μ2+c)τ0d(μ2+c).

    In this case, if R01, the disease-free equilibrium is globally asymptotically stable and the endemic equilibrium is also globally asymptotically stable if R0>1 (see Figures 1 and 2). As is shown in Figure 2, initial values and time delays can not change dynamic properties of system (2.1) when R0 is greater than one or less than or equal to one. However, from Figure 2b, it is easy to find that time delay τ0 has a significant impact on the positive equilibrium of system (5.1).

    Figure 1.  The time series diagrams of system (5.1) illustrate the effect of the initial values. The values of the parameters are A=160,b=0.04,σ1=0.2,μ1=0.01,β=2.1×105, α=8.158×106,μ2=0.05, τ0=1,k=2,d=4. Figure 1a illustrates the time series diagrams when R0=0.6463 (c=0.3); Figure 1b shows the time series diagrams when R0=1(c=0.2).
    Figure 2.  The time series diagrams of system (5.1) illustrate the effect of the initial values and the latency delay τ0. The values of the parameters are A=160,b=0.04,σ1=0.2, μ1=0.01,β=2.1×105, α=8.158×106,μ2=0.05,c=0.1, k=2,d=4. Figure 2a illustrates the time series diagrams when R0=1.8420 (τ0=1); Figure 2b shows the time series diagrams when R0=1.8420(τ0=1),1.5854(τ0=2) and 1.3646(τ0=3).

    If f(I)=βI2 [28], then f(I) does not satisfy hypothesis (H2), that is, f(I)I is a monotonically increasing function. From Figure 3, it is easy to see that the system (5.1) appears periodic oscillation behavior under certain conditions.

    Figure 3.  The time series diagrams and phase diagrams of system (5.1) illustrate the effect of the incidence rate f(I) with the initial value (2000,5000,2000,10). The values of the parameters are A=330,b=0.04,σ1=0.2, μ1=0.01,β=1×109,α=8.158×106, μ2=0.05,c=0.02, k=2,d=4,τ0=1.

    In this article, a general S1S2IB dynamics model with distributed time delay for animal brucellosis is formulated. Under the assumptions of general biological significance, the non-negative and boundedness of the solution of system (2.1) is first proved. And then the global dynamics of the steady-state solution of system (2.1) are analyzed by constructing Lyapunov functional, it is found that the dynamic properties of equilibria depend on the basic reproduction number R0: If R01, animal brucellosis will eventually die out regardless of the initial value; and if R0>1, the spread of animal brucellosis is persistent and it eventually reaches the endemic steady state. These results imply that distributed time delay does not change the dynamic properties of system (2.1) when R0 is greater than one or less than or equal to one. Finally, similar to numerical methods in [35,36], the stability results and other dynamic behaviors are further illustrated through numerical simulation, it turns out that the system experiences periodic oscillations if the assumption (H2) is not satisfied. In other words, the system (2.1) may exhibit more complex dynamic behaviors if the function fI,gB or hI is monotonically increasing. In these cases, the impact of distributed time delay on other dynamical behaviors of system (2.1) is not completely clear, then we leave these for future work.

    This research is partially supported by the National Youth Science Foundation of China (11501528), the National Sciences Foundation of China(11571324) and the Fund for Shanxi "1331KIRT".

    The authors declare that they have no competing interests.



    [1] Khatri KL, Muhammad AR, Soomro SA, et al. (2021) Investigation of possible solid waste power potential for distributed generation development to overcome the power crises of Karachi city. Renewable Sustainable Energy Rev 143: 110882. https://doi.org/10.1016/j.rser.2021.110882 doi: 10.1016/j.rser.2021.110882
    [2] Raza MA, Khatri KL, Hussain A (2022) Transition from fossilized to defossilized energy system in Pakistan. Renewable Energy 190: 19–29. https://doi.org/10.1016/j.renene.2022.03.059 doi: 10.1016/j.renene.2022.03.059
    [3] Zheng J, Mi Z, Coffman DM, et al. (2019) Regional development and carbon emissions in China. Energy Econ 81: 25–36. https://doi.org/10.1016/j.eneco.2019.03.003 doi: 10.1016/j.eneco.2019.03.003
    [4] Müller DB, Liu G, Løvik AN, et al. (2013) Carbon emissions of infrastructure development. Environ Sci Technol 47: 11739–11746. https://doi.org/10.1021/es402618m doi: 10.1021/es402618m
    [5] Huisingh D, Zhang Z, Moore JC, et al. (2015) Recent advances in carbon emissions reduction: policies, technologies, monitoring, assessment and modeling. J Cleaner Prod 103: 1–12. https://doi.org/10.1016/j.jclepro.2015.04.098 doi: 10.1016/j.jclepro.2015.04.098
    [6] Dobravec V, Matak N, Sakulin C, et al. (2021) Multilevel governance energy planning and policy: A view on local energy initiatives. Energy Sustainability Society 11: 1–17. https://doi.org/10.1186/s13705-020-00277-y doi: 10.1186/s13705-020-00277-y
    [7] Stober D, Suškevičs M, Eiter S, et al. (2021) What is the quality of participatory renewable energy planning in Europe? A comparative analysis of innovative practices in 25 projects. Energy Res Social Sci 71: 101804. https://doi.org/10.1016/j.erss.2020.101804 doi: 10.1016/j.erss.2020.101804
    [8] Cheshmehzangi A (2021) Low carbon transition at the township level: Feasibility study of environmental pollutants and sustainable energy planning. Int J Sustainable Energy 40: 670–696. https://doi.org/10.1080/14786451.2020.1860042 doi: 10.1080/14786451.2020.1860042
    [9] Bouw K, Noorman KJ, Wiekens CJ, et al. (2021) Local energy planning in the built environment: An analysis of model characteristics. Renewable Sustainable Energy Rev 144: 111030. https://doi.org/10.1016/j.rser.2021.111030 doi: 10.1016/j.rser.2021.111030
    [10] Ezbakhe F, Pérez-Foguet A (2021) Decision analysis for sustainable development: The case of renewable energy planning under uncertainty. European J Operat Res 291: 601–613. https://doi.org/10.1016/j.ejor.2020.02.037 doi: 10.1016/j.ejor.2020.02.037
    [11] Ratanakuakangwan S, Morita H (2022) An efficient energy planning model optimizing cost, emission, and social impact with different carbon tax scenarios. Appl Energy 325: 119792. https://doi.org/10.1016/j.apenergy.2022.119792 doi: 10.1016/j.apenergy.2022.119792
    [12] Ratanakuakangwan S, Morita H (2022) Measuring the efficiency of energy planning under uncertainty. Energy Rep 8: 544–551. https://doi.org/10.1016/j.egyr.2021.11.164 doi: 10.1016/j.egyr.2021.11.164
    [13] Chang M, Thellufsen JZ, Zakeri B, et al. (2021) Trends in tools and approaches for modelling the energy transition. Appl Energy 290: 116731. https://doi.org/10.1016/j.apenergy.2021.116731 doi: 10.1016/j.apenergy.2021.116731
    [14] Jäger-Waldau A, Kougias I, Taylor N, et al. (2020) How photovoltaics can contribute to GHG emission reductions of 55% in the EU by 2030. Renewable Sustainable Energy Rev 126: 109836. https://doi.org/10.1016/j.rser.2020.109836 doi: 10.1016/j.rser.2020.109836
    [15] Raza MA, Khatri KL, Rafique K, et al. (2021) Harnessing electrical power from hybrid biomass-solid waste energy resources for microgrids in underdeveloped and developing countries. Eng Technol Appl Sci Res 11: 7257–7261. https://doi.org/10.48084/etasr.4177 doi: 10.48084/etasr.4177
    [16] Palconit EV, Villanueva JR, Enano N, et al. (2021) Resource assessment of tidal stream power in Pakiputan Strait, Davao Gulf, Philippines. Eng Technol Appl Sci Res 11: 7233–7239. https://doi.org/10.48084/etasr.3853 doi: 10.48084/etasr.3853
    [17] Perez-Sindin XS, Lee J, Nielsen T (2022) Exploring the spatial characteristics of energy injustice: A comparison of the power generation landscapes in Spain, Denmark, and South Korea. Energy Res Social Sci 91: 102682. https://doi.org/10.1016/j.erss.2022.102682 doi: 10.1016/j.erss.2022.102682
    [18] Hainoun A, Aldin MS, Almoustafa S (2010) Formulating an optimal long-term energy supply strategy for Syria using MESSAGE model. Energy Policy 38: 1701–1714. https://doi.org/10.1016/j.enpol.2009.11.032 doi: 10.1016/j.enpol.2009.11.032
    [19] Bouckaert S, Mazauric V, Maïzi N (2014) Expanding renewable energy by implementing demand response. Energy Procedia 61: 1844–1847. https://doi.org/10.1016/j.egypro.2014.12.226 doi: 10.1016/j.egypro.2014.12.226
    [20] Ma X, Chai M, Luo L, et al. (2015) An assessment on Shanghai's energy and environment impacts of using MARKAL model. J Renewable Sustainable Energy 7: 013105. https://doi.org/10.1063/1.4905468 doi: 10.1063/1.4905468
    [21] Child M, Nordling A, Breyer C (2017) Scenarios for a sustainable energy system in the Åland Islands in 2030. Energy Conversion Manage 137: 49–60. https://doi.org/10.1016/j.enconman.2017.01.039 doi: 10.1016/j.enconman.2017.01.039
    [22] Hong JH, Kim J, Son W, et al. (2019) Long-term energy strategy scenarios for South Korea: Transition to a sustainable energy system. Energy Policy 127: 425–437. https://doi.org/10.1016/j.enpol.2018.11.055 doi: 10.1016/j.enpol.2018.11.055
    [23] Mirjat NH, Uqaili MA, Harijan K, et al. (2018) Long-term electricity demand forecast and supply side scenarios for Pakistan (2015–2050): A LEAP model application for policy analysis. Energy 165: 512–526. https://doi.org/10.1016/j.energy.2018.10.012 doi: 10.1016/j.energy.2018.10.012
    [24] Felver TB (2020) How can Azerbaijan meet its Paris Agreement commitments: assessing the effectiveness of climate change-related energy policy options using LEAP modeling. Heliyon 6: e04697. https://doi.org/10.1016/j.heliyon.2020.e04697
    [25] Lei Y, Lu X, Shi M, et al. (2019) SWOT analysis for the development of photovoltaic solar power in Africa in comparison with China. Environ Impact Assessm Rev 77: 122–127. https://doi.org/10.1016/j.eiar.2019.04.005 doi: 10.1016/j.eiar.2019.04.005
    [26] Sáez de Cámara E, Fernández I, Castillo-Eguskitza N (2021) A holistic approach to integrate and evaluate sustainable development in higher education. The case study of the University of the Basque Country. Sustainability 13: 392. https://doi.org/10.3390/su13010392 doi: 10.3390/su13010392
    [27] Krey V, O'Neill BC, van Ruijven B, et al. (2012) Urban and rural energy use and carbon dioxide emissions in Asia. Energy Econ 34: S272–S283. https://doi.org/10.1016/j.eneco.2012.04.013 doi: 10.1016/j.eneco.2012.04.013
    [28] Tanoto Y, Wijaya ME (2011) Economic and environmental emissions analysis in Indonesian electricity expansion planning: Low-rank coal and geothermal energy utilization scenarios; 2011. IEEE, 177–181. https://doi.org/10.1109/CET.2011.6041459
    [29] Pronińska K, Księżopolski K (2021) Baltic offshore wind energy development—poland's public policy tools analysis and the geostrategic implications. Energies 14: 4883. https://doi.org/10.3390/en14164883 doi: 10.3390/en14164883
    [30] Dominković DF, Bačeković I, Ćosić B, et al. (2016) Zero carbon energy system of South East Europe in 2050. Appl Energy 184: 1517–1528. https://doi.org/10.1016/j.apenergy.2016.03.046 doi: 10.1016/j.apenergy.2016.03.046
    [31] Mallah S, Bansal N (2010) Allocation of energy resources for power generation in India: Business as usual and energy efficiency. Energy Policy 38: 1059–1066. https://doi.org/10.1016/j.enpol.2009.10.058 doi: 10.1016/j.enpol.2009.10.058
    [32] Koukouzas N, Tyrologou P, Karapanos D, et al. (2021) Carbon capture, utilisation and storage as a defense tool against climate change: Current developments in West Macedonia (Greece). Energies 14: 3321. https://doi.org/10.3390/en14113321 doi: 10.3390/en14113321
    [33] Østergaard PA (2015) Reviewing EnergyPLAN simulations and performance indicator applications in EnergyPLAN simulations. Appl Energy 154: 921–933. https://doi.org/10.1016/j.apenergy.2015.05.086 doi: 10.1016/j.apenergy.2015.05.086
    [34] Dahlquist E, Thorin E, Yan J (2007) Alternative pathways to a fossil-fuel free energy system in the Mälardalen region of Sweden. Int J Energy Res 31: 1226–1236. https://doi.org/10.1002/er.1330 doi: 10.1002/er.1330
    [35] Ahmed S, Nguyen T (2022) Analysis of future carbon-neutral energy system—The case of Växjö Municipality, Sweden. Smart Energy 7: 100082. https://doi.org/10.1016/j.segy.2022.100082 doi: 10.1016/j.segy.2022.100082
    [36] Shahbaz MS, Kazi AG, Othman B, et al. (2019) Identification, assessment and mitigation of environment side risks for Malaysian manufacturing. Eng Technol Appl Sci Res 9: 3851–3857. https://doi.org/10.48084/etasr.2529 doi: 10.48084/etasr.2529
    [37] Raza MA, Khatri KL, Haque MIU, et al. (2022) Holistic and scientific approach to the development of sustainable energy policy framework for energy security in Pakistan. Energy Rep 8: 4282–4302. https://doi.org/10.1016/j.egyr.2022.03.044 doi: 10.1016/j.egyr.2022.03.044
    [38] Raza MA, Khatri KL, Hussain A, et al. (2022) Sector-Wise optimal energy demand forecasting for a developing country using LEAP software. Eng Proc 20: 6. https://doi.org/10.3390/engproc2022020006 doi: 10.3390/engproc2022020006
    [39] Raza MA, Khatri KL, Israr A, et al. (2022) Energy demand and production forecasting in Pakistan. Energy Strat Rev 39: 100788. https://doi.org/10.1016/j.esr.2021.100788 doi: 10.1016/j.esr.2021.100788
    [40] Raza MA, Khatri KL, Akbar S, et al. (2021) Towards improving technical performance of a 747 MW thermal power plant. Quaid-E-Awam Uni Res J Eng Sci Technol Nawabshah 19: 104–111. https://doi.org/10.52584/QRJ.1901.15 doi: 10.52584/QRJ.1901.15
    [41] Raza MA, Khatri KL, Memon MA, et al. (2022) Exploitation of Thar coal field for power generation in Pakistan: A way forward to sustainable energy future. Energy Explorat Exploitat. 40: 1173–1196. https://doi.org/10.1177/01445987221082190 doi: 10.1177/01445987221082190
    [42] Østergaard PA, Lund H, Thellufsen JZ, et al. (2022) Review and validation of EnergyPLAN. Renewable and Sustainable Energy Rev. 168: 112724. https://doi.org/10.1016/j.rser.2022.112724 doi: 10.1016/j.rser.2022.112724
    [43] Shehu E (2021) Long-term sustainable energy plan to reduce air pollution in the Republic of Moldova. ITEGAM-JETIA 7: 72–77. https://doi.org/10.5935/jetia.v7i28.737 doi: 10.5935/jetia.v7i28.737
    [44] Yan Z, Zhang Y, Liang R, et al. (2020) An allocative method of hybrid electrical and thermal energy storage capacity for load shifting based on seasonal difference in district energy planning. Energy 207: 118139. https://doi.org/10.1016/j.energy.2020.118139 doi: 10.1016/j.energy.2020.118139
    [45] Sorknæs P, Lund H, Skov I, et al. (2020) Smart Energy Markets-Future electricity, gas and heating markets. Renewable Sustainable Energy Rev 119: 109655. https://doi.org/10.1016/j.rser.2019.109655 doi: 10.1016/j.rser.2019.109655
    [46] Raza MA, Aman MM, Abro AG, et al. (2022) Challenges and potentials of implementing a smart grid for Pakistan's electric network. Energy Strategy Rev 43: 100941. https://doi.org/10.1016/j.esr.2022.100941 doi: 10.1016/j.esr.2022.100941
    [47] Qureshi AH, Raza MA, Aman M, et al. (2022) Energy Demand Projection and Economy Nexus of Pakistan. Quaid-E-Awam Uni Res J Eng Sci Technol Nawabshah 20: 138–144. https://doi.org/10.52584/QRJ.2001.17 doi: 10.52584/QRJ.2001.17
    [48] Zhao J, Sinha A, Inuwa N, et al. (2022) Does structural transformation in economy impact inequality in renewable energy productivity? Implications for sustainable development. Renewable Energy 189: 853–864. https://doi.org/10.1016/j.renene.2022.03.050 doi: 10.1016/j.renene.2022.03.050
    [49] Abbasi KR, Adedoyin FF, Abbas J, et al. (2021) The impact of energy depletion and renewable energy on CO2 emissions in Thailand: fresh evidence from the novel dynamic ARDL simulation. Renewable Energy 180: 1439–1450. https://doi.org/10.1016/j.renene.2021.08.078 doi: 10.1016/j.renene.2021.08.078
    [50] Koondhar MA, Aziz N, Tan Z, et al. (2021) Green growth of cereal food production under the constraints of agricultural carbon emissions: A new insights from ARDL and VECM models. Sustainable Energy Technol Assess 47: 101452. https://doi.org/10.1016/j.seta.2021.101452 doi: 10.1016/j.seta.2021.101452
    [51] Raza MA, Aman MM, Rajpar AH, et al. (2022) Towards achieving 100% renewable energy supply for sustainable climate change in Pakistan. Sustainability 14: 16547. https://doi.org/10.3390/su142416547 doi: 10.3390/su142416547
    [52] Iqbal N, Abbasi KR, Shinwari R, et al. (2021) Does exports diversification and environmental innovation achieve carbon neutrality target of OECD economies? J Environ Manage 291: 112648. https://doi.org/10.1016/j.jenvman.2021.112648 doi: 10.1016/j.jenvman.2021.112648
    [53] Zhou R, Abbasi KR, Salem S, et al. (2022) Do natural resources, economic growth, human capital, and urbanization affect the ecological footprint? A modified dynamic ARDL and KRLS approach. Res Policy 78: 102782. https://doi.org/10.1016/j.resourpol.2022.102782 doi: 10.1016/j.resourpol.2022.102782
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