Loading [MathJax]/jax/output/SVG/jax.js
Research article Special Issues

Evaluation of the bioenergy potential of agricultural and agroindustrial waste generated in southeastern Mexico

  • Received: 22 May 2024 Revised: 31 July 2024 Accepted: 12 August 2024 Published: 29 August 2024
  • The generation of large volumes of agricultural and agroindustrial waste in the state of Tabasco represents a significant waste management challenge. We aimed to determine the bioenergy potential of five types of biomasses: Banana rachis, coconut shell, cocoa pod husk, sugarcane bagasse, and palm kernel shell, generated in agricultural and agroindustrial processes. This research involved characterizing and evaluating the energy quality of these biomasses by determining their calorific values and assessing their viability as fuel alternative sources. Additionally, we explored these biomasses' calorific value potential to reduce the inadequate disposal of wastes, reduce environmental impact, and provide alternative uses for these materials, which are typically discarded or have limited added value in the southeast region. The yield of waste generation per amount of production was estimated, with cocoa pod husk biomass and sugarcane bagasse, banana rachis, coconut shell, and palm kernel shell generating 0.685, 0.283, 0.16, 0.135, and 0.0595 kg of biomass per kg of crop, respectively. The bioenergy potential was evaluated through direct measurements using a calorimeter bomb, and indirect measurements using stoichiometric calculations. Four stoichiometric methods based on predictive equations were employed to determine the energy content of the biomasses from their elemental composition (Dulong, Friedl, Channiwala, Boie). The biomasses with the highest calorific values were coconut shell and cocoa pod husk, with values of 16.47 ± 0.24 and 16.02 ± 1.54 MJ/kg, respectively. Moreover, banana rachis had the lowest calorific value at 13.68 ± 3.22 MJ/kg. The calorific values of the sugarcane bagasse and palm kernel shell were 13.91 ± 0.98 and 15.29 ± 1.02, respectively. The factorial experimental design and statistical analysis revealed trends and magnitudes in the evaluation of energy determination methods and types of waste. The predictive equation of Dulong showed the highest similarity to the experimental values, especially for coconut shell (16.02 ± 0.08 MJ/kg). The metal content in biomasses such as palm kernel shell and coconut shell were below the limits established in ISO 17225:2014. Finally, our results indicated that coconut shell has superior characteristics for potential use as an alternative fuel, whereas banana rachis requires exploring alternative utilization options.

    Citation: Nathaly A. Díaz Molina, José A. Sosa Olivier, José R. Laines Canepa, Rudy Solis Silvan, Donato A. Figueiras Jaramillo. Evaluation of the bioenergy potential of agricultural and agroindustrial waste generated in southeastern Mexico[J]. AIMS Energy, 2024, 12(5): 984-1009. doi: 10.3934/energy.2024046

    Related Papers:

    [1] Yoichi Enatsu, Yukihiko Nakata . Stability and bifurcation analysis of epidemic models with saturated incidence rates: An application to a nonmonotone incidence rate. Mathematical Biosciences and Engineering, 2014, 11(4): 785-805. doi: 10.3934/mbe.2014.11.785
    [2] Fang Zhang, Wenzhe Cui, Yanfei Dai, Yulin Zhao . Bifurcations of an SIRS epidemic model with a general saturated incidence rate. Mathematical Biosciences and Engineering, 2022, 19(11): 10710-10730. doi: 10.3934/mbe.2022501
    [3] Thomas Torku, Abdul Khaliq, Fathalla Rihan . SEINN: A deep learning algorithm for the stochastic epidemic model. Mathematical Biosciences and Engineering, 2023, 20(9): 16330-16361. doi: 10.3934/mbe.2023729
    [4] Guo Lin, Shuxia Pan, Xiang-Ping Yan . Spreading speeds of epidemic models with nonlocal delays. Mathematical Biosciences and Engineering, 2019, 16(6): 7562-7588. doi: 10.3934/mbe.2019380
    [5] Yang Chen, Wencai Zhao . Dynamical analysis of a stochastic SIRS epidemic model with saturating contact rate. Mathematical Biosciences and Engineering, 2020, 17(5): 5925-5943. doi: 10.3934/mbe.2020316
    [6] Andrei Korobeinikov, Philip K. Maini . A Lyapunov function and global properties for SIR and SEIR epidemiological models with nonlinear incidence. Mathematical Biosciences and Engineering, 2004, 1(1): 57-60. doi: 10.3934/mbe.2004.1.57
    [7] Jack Farrell, Owen Spolyar, Scott Greenhalgh . The effect of screening on the health burden of chlamydia: An evaluation of compartmental models based on person-days of infection. Mathematical Biosciences and Engineering, 2023, 20(9): 16131-16147. doi: 10.3934/mbe.2023720
    [8] Tahir Khan, Fathalla A. Rihan, Muhammad Ibrahim, Shuo Li, Atif M. Alamri, Salman A. AlQahtani . Modeling different infectious phases of hepatitis B with generalized saturated incidence: An analysis and control. Mathematical Biosciences and Engineering, 2024, 21(4): 5207-5226. doi: 10.3934/mbe.2024230
    [9] Shuixian Yan, Sanling Yuan . Critical value in a SIR network model with heterogeneous infectiousness and susceptibility. Mathematical Biosciences and Engineering, 2020, 17(5): 5802-5811. doi: 10.3934/mbe.2020310
    [10] Roberto A. Saenz, Herbert W. Hethcote . Competing species models with an infectious disease. Mathematical Biosciences and Engineering, 2006, 3(1): 219-235. doi: 10.3934/mbe.2006.3.219
  • The generation of large volumes of agricultural and agroindustrial waste in the state of Tabasco represents a significant waste management challenge. We aimed to determine the bioenergy potential of five types of biomasses: Banana rachis, coconut shell, cocoa pod husk, sugarcane bagasse, and palm kernel shell, generated in agricultural and agroindustrial processes. This research involved characterizing and evaluating the energy quality of these biomasses by determining their calorific values and assessing their viability as fuel alternative sources. Additionally, we explored these biomasses' calorific value potential to reduce the inadequate disposal of wastes, reduce environmental impact, and provide alternative uses for these materials, which are typically discarded or have limited added value in the southeast region. The yield of waste generation per amount of production was estimated, with cocoa pod husk biomass and sugarcane bagasse, banana rachis, coconut shell, and palm kernel shell generating 0.685, 0.283, 0.16, 0.135, and 0.0595 kg of biomass per kg of crop, respectively. The bioenergy potential was evaluated through direct measurements using a calorimeter bomb, and indirect measurements using stoichiometric calculations. Four stoichiometric methods based on predictive equations were employed to determine the energy content of the biomasses from their elemental composition (Dulong, Friedl, Channiwala, Boie). The biomasses with the highest calorific values were coconut shell and cocoa pod husk, with values of 16.47 ± 0.24 and 16.02 ± 1.54 MJ/kg, respectively. Moreover, banana rachis had the lowest calorific value at 13.68 ± 3.22 MJ/kg. The calorific values of the sugarcane bagasse and palm kernel shell were 13.91 ± 0.98 and 15.29 ± 1.02, respectively. The factorial experimental design and statistical analysis revealed trends and magnitudes in the evaluation of energy determination methods and types of waste. The predictive equation of Dulong showed the highest similarity to the experimental values, especially for coconut shell (16.02 ± 0.08 MJ/kg). The metal content in biomasses such as palm kernel shell and coconut shell were below the limits established in ISO 17225:2014. Finally, our results indicated that coconut shell has superior characteristics for potential use as an alternative fuel, whereas banana rachis requires exploring alternative utilization options.



    In the modeling of infectious diseases, incidence rate and recovery rate are two important factors that affect the dynamical behavior of the models. The bilinear incidence rate βSI are frequently used to describe the epidemic transmission process, where β is the transmission rate, S and I represent the numbers of susceptible and infective respectively. But, it is unrealistic when the number of infective individuals is large. To study the cholera epidemic spread in Bari in 1973, Capasso and Serio [1] proposed a saturated incidence rate:

    βSI1+αI, (1.1)

    where βI describes the infection force of the disease, 11+αI measures the inhibition effect from the behavioral change of the susceptible individuals as the number of infected gradually increases.

    In classical epidemic models, the recovery rate is usually assumed to be proportional to the number of infected, which means that medical resources are plentiful for the infectious diseases [2]. In fact, when diseases break out, medical resources tend to be scarce [3,4,5]. In order to study the influence of hospital beds on infectious diseases, the following nonlinear recovery rate function [5] is proposed by Shan and Zhu:

    γ(b,I)=γ0+b(γ1γ0)b+I, (1.2)

    where γ0 and γ1 are the minimum and maximum per-capita recovery rates respectively, b denotes the number of hospital beds. An SIR model with (1.2) is studied, and it is found that backward bifurcation, saddle-node bifurcation, Hopf bifurcation and cusp type of Bogdanov-Takens bifurcation of codimension 3 will happen with different values of b [5].

    Cui et al. studied an SIR epidemic model (system (1.3)) with saturate incidence rate and nonlinear recovery rate [6]. It is proved that when the number of hospital beds is small enough, system (1.3) can take place backward bifurcation, saddle-node bifurcation and Hopf bifurcation.

    S(t)=ΛβSI1+αIμS,I(t)=βSI1+αIμIϵIγ(b,I)I,R(t)=γ(b,I)IμR, (1.3)

    where S(t),I(t),R(t) are the numbers of susceptible, infected, recovered at time t respectively, γ(b,I) is defined in (1.2). Besides, Λ is the birth rate; the interpretations of β and α are the same as in [1]; μ denotes the natural death rate; ϵ represents the disease-induced death rate.

    To describe the heterogeneity of contact, complex networks are therefore incorporated into the epidemic models. Li and Yousef studied a network-based SIR epidemic model with saturated treatment function [7]. Huang and Li studied the complex dynamical properties of a network-based SIS epidemic model with saturated treatment function [8]. A condition which can determine the direction of bifurcation at R0=1 is derived in [7,8]. Wang and Yang [9] employed an edge-compartmental approach which can reduce the dimension of a mean-field vector-borne model to research the global dynamics of the system. Wang and Yang [10] proposed a degree-edge-mixed SIS model and used a novel geometric method to completely investigate the stability of feasible equilibrium. Based on the SIR model [7], Yang et al. adopted the edge-compartmental approach to prove the existence of backward bifurcation and deeply analyzed the local stability of each endemic equilibrium [11].

    To our knowledge, few people combined saturated incidence rate and nonlinear recovery rate to discuss the dynamics of network-based epidemic models. So the research of this paper is still valuable, the highlights are summarized as follows:

    A new network-based SIR epidemic model is established and then reduced to a degree-edge-mixed model by an edge-compartmental approach;

    A necessary and sufficient condition which determines the existence of backward bifurcation at R0=1 is derived;

    The stability of the feasible endemic equilibrium is proved by a geometric approach.

    We know that time delay exists in the epidemic spreading, Jiang and Zhou [12] studied the influence of time delay on epidemic spreading under limited resources. They found that time delay can induce first-order, continuous and hybrid phases and a small resources amount can effectively control the spread of infectious diseases if the delay exceeds a threshold. The stability of nonlinear systems with time delay has been studied in the literature [13,14,15,16,17]. Yang et al. obtained the existence of a positive periodic solution for neutral-type integral differential equation arising in epidemic model with time-varying delay [18]. Of course, we do not consider the delay factor in our paper, which will be a worthy of attention and research work.

    The structure of this paper is as follows. In Section 2, a new SIR epidemic model is proposed on complex networks. Besides, the dimension of the system is reduced by the edge-compartmental method. In Section 3, the existence and stability of the disease-free equilibrium and endemic equilibrium are studied. The results of numerical simulations are given in Section 4. Lastly, conclusions and discussions are presented in Section 5.

    In this section, we extend model (1.3) to the network. Furthermore, disease-induced death rate is not considered and the susceptible individuals will not be infected once vaccinated. The other parameters are exactly the same as in system (1.3) and we show the interpretation of the parameters in Table 1 for better visualization. All the nodes are classified into n groups and the nodes in the same group have the same degree. Suppose that Sk(t),Ik(t),Rk(t) be the densities of susceptible, infected, recovered with degree k at time t respectively. So, the specific mean-field equations of network-based SIR model are as follows:

    Sk(t)=ΛβkSk(t)θ(t)1+αθ(t)μSk(t)ηSk(t),Ik(t)=βkSk(t)θ(t)1+αθ(t)μIk(t)(γ0+b(γ1γ0)b+θ(t))Ik(t),Rk(t)=(γ0+b(γ1γ0)b+θ(t))Ik(t)μRk(t)+ηSk(t), (2.1)

    with θ(t) is the probability that any given edge is connected to an infected node, assume the network is uncorrelated, then

    θ(t)=1knk=1kp(k)Ik(t),

    where p(k) is the probability that a node is connected to k other nodes and k=nk=1kp(k) denotes the mean degree of the network. It is supposed that newborns are balanced by deaths, that is Λ=μ.

    Table 1.  Definition of parameters.
    Parameter Definition
    μ The birth rate / The death rate
    β Transmission rate of infected individuals
    α The saturated coefficient
    b The number of hospital beds
    γ0 The minimum per-capita recovery rate
    γ1 The maximum per-capita recovery rate
    η Proportion that has been vaccinated

     | Show Table
    DownLoad: CSV

    Inspired by the edge-compartmental method [9,10,11], we can rewrite system (2.1) as the following degree-edge-mixed model:

    Sk(t)=μβkSk(t)θ(t)1+αθ(t)μSk(t)ηSk(t),θ(t)=βkθ(t)1+αθ(t)nk=1k2p(k)Sk(t)μθ(t)(γ0+b(γ1γ0)b+θ(t))θ(t). (2.2)

    Remark 1. The dimension of degree-edge-mixed model (2.2) is much lower than system (2.1). So the process of analysis presented in this paper will be relatively concise.

    Lemma 1. If θ(0)>0,Sk(0)>0, then for all kN and tR+, we have Sk(t)>0,θ(t)>0.

    Proof. Firstly, we prove that θ(t)>0 for all t>0. From the (n+1)th equation of system (2.2), we have θ(t)=θ(0)et0z(τ)dτ,z(t)=βk(1+αθ(t))nk=1k2p(k)Sk(t)μγ0b(γ1γ0)b+θ(t). Since θ(0)>0, we can deduce θ(t)>0 for all t>0.

    Note that Sk(0)>0, in view of the continuity of Sk(t), we can find a small δ>0, such that Sk(t)>0 for t(0,δ). Now we demonstrate that Sk(t)>0 for all t>0. If not, we may assume that there exists t0δ>0, s.t. Sk(t0)=0 and Sk(t)>0 for t(0,t0). Thus, from the first n equation of system (2.2), we can obtain Sk(t0)=μ>0. This leads to Sk(t)<0 for some t(0,t0), which is apparently a contradiction. Therefore, Sk(t)>0 for all t>0.

    Remark 2. From the result of Lemma 1 and the fact Sk(t)+Ik(t)+Rk(t)=1, we can assert that Ω:={(S1,S2,,Sn,θ)0<Sk(t)1,0θ(t)<1} is a positive invariant set of system (2.2).

    System (2.2) has a unique disease-free equilibrium given by E0=(μμ+η,μμ+η,,μμ+η,0)Rn+1. Linearizing the (n+1)th equation of system (2.2) at E0 yields

    θ(t)=(βμk2(μ+η)kμγ1)θ(t). (3.1)

    Solving Eq (3.1) by a constant variation method, we can build the following equation:

    θ(t)=θ(0)e(μ+γ1)t+βμk2(μ+η)kt0e(μ+γ1)(st)θ(s)ds.

    Using the approach introduced in [19], we can calculate the basic reproduction number R0 by taking Laplace transform:

    R0=βμk2(μ+η)k+0e(μ+γ1)tdt=βμk2(μ+η)(μ+γ1)k,

    where k2=nk=1k2p(k).

    The local and global stability of the disease-free equilibrium E0 will be proved in this subsection.

    Theorem 1. If R0<1, the disease-free equilibrium E0 of system (2.2) is locally asymptotically stable, whereas if R0>1,E0 is unstable.

    Proof. Linearizing system (2.2) at E0 yields to

    Sk(t)=(μη)Sk(t)βkμμ+ηθ(t),θ(t)=(βμk2(μ+η)kμγ1)θ(t). (3.2)

    Furthermore, the Jacobian matrix of Eq (3.2) is

    J(E0)=(μη00βμμ+η0μη02βμμ+η00μηnβμμ+η000βμk2(μ+η)kμγ1)(n+1)×(n+1).

    Obviously, λ=(μ+η) is n-multiple negative eigenvalue. So, the stability of E0 is determined by the following eigenvalue:

    λ=βμk2(μ+η)kμγ1=(μ+γ1)(R01).

    Therefore, all eigenvalues of the Jacobian matrix J(E0) are negative when R0<1, and hence, E0 is locally asymptotically stable. By contrast, if R0>1,E0 is unstable.

    Next, we will prove the global stability of the disease-free equilibrium E0.

    Theorem 2. Denote ^R0 =β(b+1)k2(μ+bμ+γ0+bγ1)k, if ^R01, then E0 is globally asymptotically stable.

    Proof. Let a Lyapunov function V(t)=θ(t), then

    V(t)=βθ(t)k(1+αθ(t))nk=1k2p(k)Sk(t)μθ(t)(γ0+b(γ1γ0)b+θ(t))θ(t)βk2kθ(t)μθ(t)(γ0+b(γ1γ0)b+θ(t))θ(t)=[βk2kμγ0b(γ1γ0)b+1b(γ1γ0)(1θ(t))(b+1)(b+θ(t))]θ(t)[βk2kμγ0b(γ1γ0)b+1]θ(t)=[μ+γ0+b(γ1γ0)b+1](^R01)θ(t),

    if ^R0 <1, V(t)0; if ^R0 =1, then V(t)b(γ1γ0)(1θ(t))(b+1)(b+θ(t))θ(t)0. The equality holds if and only if θ(t)=0. Hence, we can conclude that the disease-free equilibrium E0 is globally asymptotically stable if ^R01.

    Remark 3. Because γ0<γ1, so R0=μ(μ+bμ+γ0+bγ1)(μ+η)(μ+bμ+γ1+bγ1)^R0<^R0.

    Remark 4. If ^R0<1, that is R0<μ(μ+bμ+γ0+bγ1)(μ+η)(μ+bμ+γ1+bγ1)<1, then E0 is globally asymptotically stable.

    Remark 5. It seems that the condition R0<1 is not sufficient to ensure the global asymptotic stability of E0. So system (2.2) may exist backward bifurcation at R0=1 which will be proved later.

    The existence of feasible positive equilibrium will be proved in this subsection.

    Theorem 3. If R0>1, system (2.2) admits at least an endemic equilibrium.

    Proof. Assume that E=(Sk,θ),k=1,2,,n, is an endemic equilibrium of system (2.2), then E should satisfy

    0=μβkSkθ1+αθμSkηSk,0=βθk(1+αθ)nk=1k2p(k)Skμθ(γ0+b(γ1γ0)b+θ)θ. (3.3)

    Then we can obtain Sk=μ(1+αθ)βkθ+(μ+η)(1+αθ),k=1,2,,n. Substituting Sk into the (n+1)th equation of (3.3), then we can get a self-consistency equation:

    F(θ):=μ+γ0+b(γ1γ0)b+θβknk=1k2p(k)μβkθ+(μ+η)(1+αθ)=0. (3.4)

    Since R0>1,F(0)<0,F(1)>0, using the Immediate Value Theorem, we can conclude that Eq (3.4) has at least one positive root in (0,1). This implies that system (2.2) admits at least an endemic equilibrium.

    Remark 6. If R01, then F(0)0,F(1)>0, we can not conclude whether system (2.2) exists endemic equilibrium by the method of the Immediate Value Theorem. However, we already know that E0 is not globally asymptotically stable, so system (2.2) may also exist endemic equilibrium when R01. In other words, the system may take place backward bifurcation at R0=1 which will be proved in Theorem 4.

    Next, we will derive a necessary and sufficient condition which determines the existence of backward bifurcation at R0=1.

    Theorem 4. System (2.2) exists backward bifurcation at R0=1 if and only if b<ˆb; the system undergoes forward bifurcation if and only if b>ˆb, where

    ˆb=μ(γ1γ0)k22(μ+γ1)[μαk22+(μ+γ1)kk3],k3=nk=1k3p(k).

    Proof. The endemic equilibrium should satisfy Eq (3.4). Replacing β by (μ+η)(μ+γ1)kR0μk2 and we can obtain the following equation:

    μ+γ0+b(γ1γ0)b+θ(μ+η)(μ+γ1)R0nk=1k2p(k)μQ0=0, (3.5)

    where Q0=(μ+η)(μ+γ1)kkθR0+(μ+η)(1+αθ)μk2.

    If we keep in mind that θ is a function of R0, then the direction of bifurcation is depended on the sign of θR0|(R0,θ)=(1,0). More exactly, if θR0|(R0,θ)=(1,0)<0, then backward bifurcation occurs at R0=1. Conversely, the forward bifurcation happens.

    Next, taking the derivative of Eq (3.5) associated with R0 by the implicit function theorem, then yields to the following equation:

    b(γ1γ0)θR0(b+θ)2+(μ+η)(μ+γ1)[nk=1k2p(k)(R0Q1μQ0)Q20]=0, (3.6)

    where Q1=μ(μ+η)[(μ+γ1)kkθ+(μ+γ1)kkθR0R0+μαk2θR0].

    Substituting (R0,θ)=(1,0) into Eq (3.6), we can obtain the following equation by simple calculation and arrangement:

    θR0|(R0,θ)=(1,0)=bμ(μ+γ1)k22b(μ+γ1)2kk3+bμα(μ+γ1)k22μ(γ1γ0)k22.

    Thus if

    θR0|(R0,θ)=(1,0)<0b<μ(γ1γ0)k22(μ+γ1)[μαk22+(μ+γ1)kk3].

    The same holds true also for the other proposition.

    Remark 7. It is a fact that the number of hospital beds does play a key role in determining whether there is a backward bifurcation at R0=1. More precisely, if b is small enough to satisfy the result of Theorem 4, backward bifurcation will occur. In this case, there will also exist endemic equilibrium even if R0<1 (see Figure 2(b)). That is to say, R0<1 is not sufficient to eradicate the diseases from the population, which is unfavorable to the control of infectious diseases.

    Figure 1.  The time evolutions of θ(t) with different initial conditions θ(0)=0.001×i,i=1,2,,20. (a) ^R0=0.8933<1. (b) R0=1.5008>1..
    Figure 2.  (a) The time evolutions of θ(t) with different initial conditions θ(0)=0.001×i,i=1,2,,20. (b) The backward bifurcation diagrams in the R0θ-plane with different values of b..

    Otherwise, when b is big enough, forward bifurcation will take place at R0=1. In this case, E0 will be globally asymptotically stable when R0<1. This also shows the existence of the threshold for the number of hospital beds. When the relevant departments provide enough hospital beds such that b>ˆb, infectious diseases can be completely eliminated if R0<1.

    From the above discussions, we can summarize the following results.

    Corollary 1. For system (2.2),

    (1) if R0<1 and

    (a) b<ˆb, there exists two endemic equilibria;

    (b) b>ˆb, there is no endemic equilibrium.

    (2) when R0=1, if b<ˆb, then there exists a unique endemic equilibrium; otherwise, there is no endemic equilibrium.

    (3) if R0>1, the endemic equilibrium always exist (see Theorem 3) and the number of endemic equilibrium is associated with the value of b (see Figure 3).

    Figure 3.  Bifurcation diagrams in the R0θ-plane with different values of b. Forward bifurcation takes place at R0=1 for each subgraph.

    In this subsection, we will use a geometric approach to prove the local stability of the endemic equilibrium. Linearizing system (2.2) at E yields

    Sk(t)=(μηβkθ1+αθ)Sk(t)βkSk(1+αθ)2θ(t),θ(t)=βθk(1+αθ)nk=1k2p(k)Sk(t)+(βk(1+αθ)2nk=1k2p(k)Skμγ0b2(γ1γ0)(b+θ)2)θ(t). (3.7)

    And hence the characteristic equation can be expressed as follows:

    (λ+μ+η+βkθ1+αθ)xk+βkSk(1+αθ)2y=0,βθk(1+αθ)nk=1k2p(k)xk+(λ+μ+γ0+b2(γ1γ0)(b+θ)2βk(1+αθ)2nk=1k2p(k)Sk)y=0, (3.8)

    where (xk,y) is the eigenvector that correspond to eigenvalue λ. From the first equation of (3.8), we can obtain

    xk=βkSkyβkθ(1+αθ)+(λ+μ+η)(1+αθ)2,k=1,2,,n.

    Substituting xk into the second equation of (3.8) leads to

    H(λ)y=0,

    where H(λ)=βknk=1k3p(k)βSkθβkθ(1+αθ)2+(λ+μ+η)(1+αθ)3+λ+μ+γ0+b2(γ1γ0)(b+θ)2βknk=1k2p(k)Sk(1+αθ)2.

    If y=0, then λ=μηβkθ1+αθ<0. Otherwise, when y0, then H(λ)=0. Since

    βkSkθ1+αθ=μμSkηSk,Sk=μ(1+αθ)βkθ+(μ+η)(1+αθ),βknk=1k2p(k)Sk1+αθ=μ+γ0+b(γ1γ0)b+θ, (3.9)

    and hence

    H(λ)=βknk=1k2p(k)(μμSkηSk)βkθ(1+αθ)+(λ+μ+η)(1+αθ)2+λ+βknk=1k2p(k)Sk1+αθb(γ1γ0)θ(b+θ)2βknk=1k2p(k)μβkθ(1+αθ)+(μ+η)(1+αθ)2=βknk=1k2p(k)(μμSkηSk)βkθ(1+αθ)+(λ+μ+η)(1+αθ)2+λb(γ1γ0)θ(b+θ)2+βknk=1k2p(k)μβkθ+(μ+η)(1+αθ)βknk=1k2p(k)μβkθ(1+αθ)+(μ+η)(1+αθ)2=βknk=1k2p(k)(μμSkηSk)βkθ(1+αθ)+(λ+μ+η)(1+αθ)2+λb(γ1γ0)θ(b+θ)2+βknk=1k2p(k)μαθβkθ(1+αθ)+(μ+η)(1+αθ)2. (3.10)

    Besides, taking the derivative of F associated with θ, we can have:

    F(θ)=b(γ1γ0)(b+θ)2+βknk=1k2p(k)μ(βk+(μ+η)α)(βkθ+(μ+η)(1+αθ))2=βknk=1k2p(k)μ(βkSkθ1+αθ+(μ+η)αSkθ1+αθ)(βkθ+(μ+η)(1+αθ))2Skθ1+αθb(γ1γ0)(b+θ)2=βknk=1k2p(k)μμSkηSk+(μ+η)αSkθ1+αθθ(βkθ+(μ+η)(1+αθ))b(γ1γ0)(b+θ)2=βknk=1k2p(k)(μμSkηSk)(1+αθ)+(μ+η)αSkθθ(βkθ(1+αθ)+(μ+η)(1+αθ)2)b(γ1γ0)(b+θ)2=βknk=1k2p(k)μμSkηSk+μαθθ(βkθ(1+αθ)+(μ+η)(1+αθ)2)b(γ1γ0)(b+θ)2. (3.11)

    Therefore, we can obtain that

    H(0)=βknk=1k2p(k)μμSkηSk+μαθβkθ(1+αθ)+(μ+η)(1+αθ)2b(γ1γ0)θ(b+θ)2=θF(θ). (3.12)

    Theorem 5. When F(θ)<0, then E is unstable; when F(θ)>0, then E is locally asymptotically stable.

    Proof. When F(θ)<0, since H(0)=θF(θ)<0,limλ+H(λ)=+, by the Intermediate Value Theorem, we can conclude that the equation H(λ)=0 has at least one positive real solution, so E is unstable.

    When F(θ)>0, we rewrite the equation H(λ)=0 as the following equation:

    ˆH(λ)=βknk=1k2p(k)(μμSkηSk)nikL(λ,i,θ)+βknk=1k2p(k)μαθβkθ(1+αθ)+(μ+η)(1+αθ)2nk=1L(λ,k,θ)+(λb(γ1γ0)θ(b+θ)2)nk=1L(λ,k,θ)=0, (3.13)

    where L(λ,k,θ)=βkθ(1+αθ)+(λ+μ+η)(1+αθ)2. Suppose Eq (3.13) has a solution λ with Reλ0, then since

    |ˆH(λ)|ˆH(Reλ)ˆH(0)=nk=1L(0,k,θ)H(0)=nk=1L(0,k,θ)θF(θ),

    if F(θ)>0, we can conclude that |ˆH(λ)|>0, this contradicts with the fact ˆH(λ)=0. So Eq (3.13) has no solution with nonnegative real parts. Therefore, when F(θ)>0,E is locally asymptotically stable.

    Corollary 2. If R0<1 and b<ˆb, system (2.2) exists two endemic equilibria, the one with smaller value is unstable; the other one with larger value is locally asymptotically stable.

    Proof. If R0<1 and b<ˆb, there exists two endemic equilibria (see Corollary 1). For the endemic equilibrium with smaller value, since F(θ)<0 (see Figure 2(b)), then E is unstable; and for the endemic equilibrium with larger value, since F(θ)>0, so E is locally asymptotically stable.

    Next, numerical simulations will be presented to validate the previous theoretical results. Our simulations are based on the scale-free network with p(k)=ξk2.5,k=1,2,,100, and the constant ξ is chosen so that the equation 100k=1p(k)=1 holds. For better visualization, we present the values of the parameters in Table 2.

    Table 2.  Parameter values of numerical simulations.
    Parameter Figure 1(a) Figure 1(b) Figure 2(a) Figure 2(b) Figure 3 Figure 4(a) Figure 4(b)
    μ 0.02 0.02 0.01 0.01 0.01 0.02 0.02
    β 0.006 0.03 0.009 0.03 0.03
    α 10 10 10 10 10 0/3/6/9/12 10
    b 0.03 0.03 0.003 0.003/0.005/0.007/0.009/0.011 0.0165/0.017/0.0175/0.018 0.03 0/0.003/0.006/0.009/0.012
    γ0 0.03 0.03 0.005 0.005 0.005 0.03 0.03
    γ1 0.09 0.09 0.08 0.08 0.08 0.09 0.09
    η 0.008 0.008 0.008 0.008 0.008 0.008 0.008

     | Show Table
    DownLoad: CSV

    Firstly, we verify the stability of the disease-free equilibrium E0. According to the selected parameter values, we can calculate R0=0.3002,^R0=0.8933. It is known that E0 is globally asymptotically stable from the result of Theorem 2. As seen in Figure 1(a), limt+θ(t)=0. Therefore, this does support the global stability of E0.

    In Figure 1(b), we can obtain R0=1.5008>1 and hence model (2.2) exists endemic equilibrium. Observing the simulation results, we can see that all trajectories move towards to a positive constant and the unique endemic equilibrium could be stable. However, when R0>1, model (2.2) can exhibit more complex dynamics (see Figure 3).

    Secondly, we will verify that system (2.2) may exist endemic equilibrium when R0<1. The parameter values as shown in Table 2, since R0=0.4280<1,^R0=4.5545>1, therefore E0 is not globally asymptotically stable from the result of Theorem 2. From Figure 2(a), it can be observed that the trajectories partially converge to zero or partially move towards to a positive level which corresponds to different initial conditions. Therefore, the initial infectious density must be controlled to a lower level for the control of the diseases. The result of the co-existence of two locally asymptotically stable equilibria is named as the bistable phenomenon.

    Different values of b are taken to show the bifurcation diagrams. In Figure 2(b), backward bifurcation occurs at R0=1 when b<ˆb=0.016. Besides, the larger the value of b, the smaller the depth of backward bifurcation. In Figure 3, the parameters are the same as those given in Figure 2, except for the value of b. It can be seen that forward bifurcation occurs at R0=1 for each subgraph. The reason is that although the values of b are different, they are all bigger than ˆb. Hence, the numerical simulation results are consistent with the theoretical results of Theorem 4.

    At the same time, we can observe that the shapes of the bifurcation curves are different from Figure 3. For example, the endemic equilibrium curve has an "S shape" when b=0.017. That is to say, backward bifurcation takes place at a certain value of R0. And the situation results in the existence of three endemic equilibria. So, the number of endemic equilibrium is uncertain when R0>1.

    Lastly, we will investigate the effect of α and b on diseases transmission through numerical simulations. The parameters in Figure 4 are the same as those in Figure 1(b) and R0=1.5008>1. From Figure 4, we can observe that the larger α or b, the value of θ(t) at steady state will be smaller, which means that the final density of infected individuals will also be smaller. This indicates that the behavioral change of individuals can indeed suppress the spread of the diseases. Besides, enriching the adequate hospital beds is also important for the control of the diseases.

    Figure 4.  The time evolutions of θ(t) with initial condition θ(0)=0.01. (a) α=3×(i1), (b) b=0.003×(i1),i=1,2,,5.

    Many scholars proved that the number of hospital beds plays an important role in the occurrence of bifurcation [5,6,20,21,22], but most of them studied the homogeneously mixed models. In [6], Cui et al. obtained a quadratic equation with respect to I and discussed the existence and classification of equilibrium from the algebraic perspective. The condition for the existence of backward bifurcation is proved by reducing system (1.3) into the center manifold. In this paper, a network-based SIR epidemic model which is the extension of model (1.3) is proposed. Using the edge-compartmental approach, we reduced the dimension of the system. It is proved that when θR0|(R0,θ)=(1,0)<0b<ˆb, backward bifurcation will occur at R0=1. The method is different from the approach in [6]. Moreover, the condition which determines the direction of bifurcation at R0=1 is related to the network structure.

    It is also possible that system (2.2) exists multiple endemic equilibria when R0>1 (see Figure 3). In conclusion, the condition R0<1 is not enough to guarantee the global asymptotic stability of E0, and R0>1 does not confirm the uniqueness of endemic equilibrium. In addition, we established a relationship between the local stability of endemic equilibrium and the tangent slope of the epidemic curve. It is observed that the larger α or b can reduce the endemic level (see Figure 4). Therefore, the effect from the individual behavioral change should not be ignored and the hospital beds should be adequately provided in the process of controlling the infectious diseases.

    However, whether system (2.2) can exhibit more complex dynamical behavior such as Hopf, saddle-node, transcritical and Bogdanov-Takens bifurcation are not discussed. At present, the bifurcation theory on networks is still less. It will be interesting and important to solve the problem and we leave this for future work.

    The authors declare they have not used Artificial Intelligence (AI) tools in the creation of this article.

    Research Project Supported by National Nature Science Foundation of China (Grant Nos. 12071445, 12271519), the Fundamental Research Program of Shanxi Province (Grant Nos. 20210302123031, 202203021211091), the Science and Technology Innovation Program of higher education in Shanxi Province (Grant No. 2023L436).

    The authors declare there is no conflict of interest in this paper.



    [1] FAO (2022) FAOSTAT, Land use, 2022. Available from: https://www.fao.org/faostat/en/#data/RL.
    [2] FAO (2022) FAOSTAT, Crops and livestock products, 2022. Available from: https://www.fao.org/faostat/en/#data/QCL.
    [3] FAO (2022) FAOSTAT, Value of agricultural production, 2022. Available from: https://www.fao.org/faostat/en/#data/QV.
    [4] FAO (2022) FAOSTAT, Macro indicators, 2022. Available from: https://www.fao.org/faostat/en/#data/MK.
    [5] SIAP (2022) Statistical yearbook of agricultural production, 2022. Available from: https://nube.siap.gob.mx/cierreagricola/.
    [6] SIAP (2023) Performance of the agri-food GDP in the third quarter of 2023 (2022: Ⅲ–2023 Ⅲ).
    [7] SEDEC (2023) State profile, 2023. Available from: https://tabasco.gob.mx/sites/default/files/users/sdettabasco/Perfil%20del%20Estado.pdf.
    [8] INEGI Quarterly indicator of State economic activity (ITAEE), Tabasco.
    [9] Chauhan A, Upadhyay S, Saini G, et al. (2022) Agricultural crop residue-based biomass in India: Potential assessment, methodology and key issues. Sustainable Energy Technol Assess 53: 102552.https://doi.org/10.1016/j.seta.2022.102552 doi: 10.1016/j.seta.2022.102552
    [10] Tauro R, García C, Skutsch M, et al. (2018) The potential for sustainable biomass pellets in Mexico: An analysis of energy potential, logistic costs and market demand. Renewable Sustainable Energy Rev 82: 380–389.https://doi.org/10.1016/j.rser.2017.09.036 doi: 10.1016/j.rser.2017.09.036
    [11] Peñaloza DF, Laiton LJ, Caballero DF, et al. (2012) Sciencimetric study of trends in the utilization of cocoa by-products (Theobroma cacao L.). Rev Espacio I+D, Innov Desarro 10: 83–94.https://doi.org/10.31644/IMASD.27.2021.a05 doi: 10.31644/IMASD.27.2021.a05
    [12] Balladares CA (2016) Physicochemical characterization of cocoa and coffee leachates from the Ecuadorian coast, as potential sources of bioethanol production. Available from: http://hdl.handle.net/10553/22931.
    [13] Lu F, Rodriguez J, Van Damme I, et al. (2018) Valorisation strategies for cocoa pod husk and its fractions. Curr Opin Green Sustainable Chem 14: 80–88.https://doi.org/10.1016/j.cogsc.2018.07.007 doi: 10.1016/j.cogsc.2018.07.007
    [14] Vásquez ZS, de Carvalho Neto DP, Pereira GVM, et al. (2019) Biotechnological approaches for cocoa waste management: A review. Waste Manage 90: 72–83.https://doi.org/10.1016/j.wasman.2019.04.030 doi: 10.1016/j.wasman.2019.04.030
    [15] Campos R, Nieto KH, Oomah BD (2018) Cocoa (Theobroma cacao L.) pod husk: Renewable source of bioactive compounds. Trends Food Sci Technol 81: 172–184.https://doi.org/10.1016/j.tifs.2018.09.022 doi: 10.1016/j.tifs.2018.09.022
    [16] Fernandes ERK, Marangoni C, Souza O, et al. (2013) Thermochemical characterization of banana leaves as a potential energy source. Energy Convers Manage 75: 603–608.https://doi.org/10.1016/j.enconman.2013.08.008 doi: 10.1016/j.enconman.2013.08.008
    [17] Espina R, Barroca R, Abundo MLS (2022) The optimal high heating value of the torrefied coconut shells. Eng Technol Appl Sci Res 12: 8605–8610.https://doi.org/10.48084/etasr.4931 doi: 10.48084/etasr.4931
    [18] Trujillo AF, Arias LS (2013) Coconut, a renewable resource for the design of green materials. Entre Cienc Ing 7: 93–100. Available from:https://revistas.ucp.edu.co/index.php/entrecienciaeingenieria/article/view/637.
    [19] Irawan A, US Latifah, DIP Meity (2017) Effect of torrefaction process on the coconut shell energy content for solid fuel, AIP Conf Proc 1826: 020010.https://doi.org/10.1063/1.4979226 doi: 10.1063/1.4979226
    [20] Triana O, León TS, Céspedes MI, et al. (2014) Characterization of sugarcane harvest residues stored in bulk. ICIDCA Sobre Deriv Caña Azúc 48: 65–70. Available from:https://www.redalyc.org/articulo.oa?id = 223131337010.
    [21] Kalifa MA, Habtu NG, Jembere AL, et al. (2024) Characterization and evaluation of torrefied sugarcane bagasse to improve the fuel properties. Curr Res Green Sustain Chem 8: 100395.https://doi.org/10.1016/j.crgsc.2023.100395 doi: 10.1016/j.crgsc.2023.100395
    [22] Schmitt CC, Moreira R, Neves RC, et al. (2020) From agriculture residue to upgraded product: The thermochemical conversion of sugarcane bagasse for fuel and chemical products. Fuel Proc Technol 197: 106199.https://doi.org/10.1016/j.fuproc.2019.106199 doi: 10.1016/j.fuproc.2019.106199
    [23] Liew RK, Nam WL, Chong MY, et al. (2018) Oil palm waste: An abundant and promising feedstock for microwave pyrolysis conversion into good quality biochar with potential multi-applications. Proc Saf Environ Prot 115: 57–69.https://doi.org/10.1016/j.psep.2017.10.005 doi: 10.1016/j.psep.2017.10.005
    [24] Ohimain EI, Izah SC (2014) Energy self-sufficiency of smallholder oil palm processing in Nigeria. Renewable Energy 63: 426–431.https://doi.org/10.1016/j.renene.2013.10.007 doi: 10.1016/j.renene.2013.10.007
    [25] Syamsiro M, Saptoadi H, Tambunan BH, et al. (2012) A preliminary study on use of cocoa pod husk as a renewable source of energy in Indonesia. Energy Sustainable Dev 16: 74–77.https://doi.org/10.1016/j.esd.2011.10.005 doi: 10.1016/j.esd.2011.10.005
    [26] Vásquez ZS, de Carvalho Neto DP, Pereira GVM, et al. (2019) Biotechnological approaches for cocoa waste management: A review. Waste Manage 90: 72–83.https://doi.org/10.1016/j.wasman.2019.04.030 doi: 10.1016/j.wasman.2019.04.030
    [27] Redondo C, Rodríguez M, Vallejo S, et al. (2020) Biorefinery of biomass of agro-industrial banana waste to obtain high-value biopolymers. Molecules 25: 3829.https://doi.org/10.3390/molecules25173829 doi: 10.3390/molecules25173829
    [28] da Silva JCG, Alves JLF, de Araujo WV, et al. (2019) Pyrolysis kinetics and physicochemical characteristics of skin, husk, and shell from green coconut wastes. Energy Ecol Environ 4: 125–132.https://doi.org/10.1007/s40974-019-00120-x doi: 10.1007/s40974-019-00120-x
    [29] Sarkar JK, Wang Q (2020) Different pyrolysis process conditions of South Asian waste coconut shell and characterization of gas, bio-char, and bio-oil. Energies 13: 1970.https://doi.org/10.3390/en13081970 doi: 10.3390/en13081970
    [30] Nadzri SNIHA, Sultan MTH, Shah AUM, et al. (2022) A comprehensive review of coconut shell powder composites: Preparation, processing, and characterization. J Thermoplast Compos Mater 35: 2641–2664.https://doi.org/10.1177/089270572093080 doi: 10.1177/089270572093080
    [31] Dewajani H, Zamrudy W, Irfin Z, et al. (2023) Utilization of Indonesian sugarcane bagasse into bio asphalt through pyrolysis process using zeolite-based catalyst. Mater Today Proc 87: 383–389.https://doi.org/10.1016/j.matpr.2023.04.171 doi: 10.1016/j.matpr.2023.04.171
    [32] Sales A, Lima SA (2010) Use of Brazilian sugarcane bagasse ash in concrete as sand replacement. Waste Manage 30: 1114–1122.https://doi.org/10.1016/j.wasman.2010.01.026 doi: 10.1016/j.wasman.2010.01.026
    [33] Abnisa F, Daud WMAW, Husin WNW, et al. (2011) Utilization possibilities of palm shell as a source of biomass energy in Malaysia by producing bio-oil in pyrolysis process. Biomass Bioenergy 35: 1863–1872.https://doi.org/10.1016/j.biombioe.2011.01.033 doi: 10.1016/j.biombioe.2011.01.033
    [34] Sosa JA, Laines JR, García DS, et al. (2022) Activated carbon: A review of residual precursors, synthesis processes, characterization techniques, and applications in the improvement of biogas. Environ Eng Res 28: 220100.https://doi.org/10.4491/eer.2022.100 doi: 10.4491/eer.2022.100
    [35] Pérez M de L, Hernández JC, Bideshi DK, et al. (2020) Agave: a natural renewable resource with multiple applications. J Sci Food Agric 100: 5324–5333.https://doi.org/10.1002/jsfa.10586 doi: 10.1002/jsfa.10586
    [36] Borrega M, Hinkka V, Hörhammer H, et al. (2022) Utilizing and valorizing oat and barley straw as an alternative source of lignocellulosic fibers. Materials 15: 7826.https://doi.org/10.3390/ma15217826 doi: 10.3390/ma15217826
    [37] Ali AH, Wanderlind EH, Almerindo GI (2024) Activated carbon obtained from malt bagasse as a support in heterogeneous catalysis for biodiesel production. Renewable Energy 220: 119656.https://doi.org/10.1016/j.renene.2023.119656 doi: 10.1016/j.renene.2023.119656
    [38] Chung WJ, Shim J, Ravindran B (2022) Application of wheat bran-based biomaterials and nano-catalyst in textile wastewater. J King Saud Univ Sci 34: 101775.https://doi.org/10.1016/j.jksus.2021.101775 doi: 10.1016/j.jksus.2021.101775
    [39] Armynah B, Tahir D, Tandilayuk M, et al. (2019) Potentials of biochars derived from bamboo leaf biomass as energy sources: Effect of temperature and time of heating. Int J Biomater 2019: 1–9.https://doi.org/10.1155/2019/3526145 doi: 10.1155/2019/3526145
    [40] Sagastume A, Cabello JJ, Hens L, et al. (2020) The energy potential of agriculture, agroindustrial, livestock, and slaughterhouse biomass wastes through direct combustion and anaerobic digestion. The case of Colombia. J Clean Prod 269: 122317.https://doi.org/10.1016/j.jclepro.2020.122317 doi: 10.1016/j.jclepro.2020.122317
    [41] Mdhluli FT, Harding KG (2021) Comparative life-cycle assessment of maize cobs, maize stover and wheat stalks for the production of electricity through gasification vs traditional coal power electricity in South Africa. Clean Environ Syst 3: 100046.https://doi.org/10.1016/j.cesys.2021.100046 doi: 10.1016/j.cesys.2021.100046
    [42] Appiah NB, Li J, Rooney W, et al. (2019) A review of sweet sorghum as a viable renewable bioenergy crop and its techno-economic analysis. Renewable Energy 143: 1121–1132.https://doi.org/10.1016/j.renene.2019.05.066 doi: 10.1016/j.renene.2019.05.066
    [43] Mazurkiewicz J, Marczuk A, Pochwatka P, et al. (2019) Maize straw as a valuable energetic material for giogas plant feeding. Materials 12: 3848.https://doi.org/10.3390/ma12233848 doi: 10.3390/ma12233848
    [44] Niju S, Swathika M, Balajii M (2020) Pretreatment of lignocellulosic sugarcane leaves and tops for bioethanol production. Lignocellulosic Biomass Liquid Biofuels, 301–324.https://doi.org/10.1016/B978-0-12-815936-1.00010-1 doi: 10.1016/B978-0-12-815936-1.00010-1
    [45] Chala B, Oechsner H, Latif S, et al. (2018) Biogas potential of coffee processing waste in Ethiopia. Sustainability 10: 2678.https://doi.org/10.3390/su10082678 doi: 10.3390/su10082678
    [46] Mekuria D, Diro A, Melak F, et al. (2022) Adsorptive removal of methylene blue dye using biowaste materials: Barley bran and enset midrib leaf. J Chem 2022: 1–13.https://doi.org/10.1155/2022/4849758 doi: 10.1155/2022/4849758
    [47] Kosheleva RI, Mitropoulos AC, Kyzas GZ (2019) Synthesis of activated carbon from food waste. Environ Chem Lett 17: 429–438.https://doi.org/10.1007/s10311-018-0817-5 doi: 10.1007/s10311-018-0817-5
    [48] Prieto García F, Canales-Flores RA, Prieo-Méndez J, et al. (2022) Evaluation of three lignocellulose biomass materials (barley husk, corn cobs, agave leaves) as precursors of activated carbon. Rev Fac Cienc 11: 17–39.https://doi.org/10.15446/rev.fac.cienc.v11n1.97719 doi: 10.15446/rev.fac.cienc.v11n1.97719
    [49] Araújo L, Machado AR, Pintado M, et al. (2023) Toward a circular bioeconomy: Extracting cellulose from grape stalks. Eng Proc 86.https://doi.org/10.3390/ECP2023-14746 doi: 10.3390/ECP2023-14746
    [50] Martinelli FRB, Ribeiro FRC, Marvila MT, et al. (2023) A Review of the use of coconut fiber in cement composites. Polymers 15: 1309.https://doi.org/10.3390/polym15051309 doi: 10.3390/polym15051309
    [51] Elnagdy NA, Ragab TIM, Fadel MA, et al. (2024) Bioethanol production from characterized pre-treated sugarcane trash and Jatropha agrowastes. J Biotechnol 386: 28–41.https://doi.org/10.1016/j.jbiotec.2024.02.015 doi: 10.1016/j.jbiotec.2024.02.015
    [52] Darmayanti R, Wika Amini H, Fitri Rizkiana M, et al. (2019) Lignocellulosic material from main indonesian plantation commodity as the feedstock for fermentable sugar in biofuel production. ARPN J Eng Appl Sci 14: 3524–3534.
    [53] Perea MA, Manzano F, Hernandez Q, et al. (2018) Peanut shell for energy: Properties and its potential to respect the environment. Sustainability 10: 3254.https://doi.org/10.3390/su10093254 doi: 10.3390/su10093254
    [54] Daud WMAW, Ali WSW (2004) Comparison on pore development of activated carbon produced from palm shell and coconut shell. Bioresour Technol 93: 63–69.https://doi.org/10.1016/j.biortech.2003.09.015 doi: 10.1016/j.biortech.2003.09.015
    [55] Abnisa F, Arami A, Daud WMAW, et al. (2013) Characterization of bio-oil and bio-char from pyrolysis of palm oil wastes. Bioenergy Res 6: 830–840.https://doi.org/10.1007/s12155-013-9313-8 doi: 10.1007/s12155-013-9313-8
    [56] Sable H, Kumar V, Mishra R, et al. (2024) Bamboo stem derived biochar for biosorption of Cadmium (Ⅱ) ions from contaminated wastewater. Environ Nanotechnol Monit Manag 21: 100936.https://doi.org/10.1016/j.enmm.2024.100936 doi: 10.1016/j.enmm.2024.100936
    [57] Manríquez A, Sierra J, Muñoz P, et al. (2020) Analysis of urban agriculture solid waste in the frame of circular economy: Case study of tomato crop in integrated rooftop greenhouse. Sci Total Environ 734.https://doi.org/10.1016/j.scitotenv.2020.139375 doi: 10.1016/j.scitotenv.2020.139375
    [58] Soares IS, Perrechil F, Grandis A, et al. (2024) Cassava waste (stem and leaf) analysis for reuse. Food Chem Adv 4: 100675.https://doi.org/10.1016/j.focha.2024.100675 doi: 10.1016/j.focha.2024.100675
    [59] Gómez E, Roriz CL, Heleno SA, et al. (2021) Valorisation of black mulberry and grape seeds: Chemical characterization and bioactive potential. Food Chem 337: 127998.https://doi.org/10.1016/j.foodchem.2020.127998 doi: 10.1016/j.foodchem.2020.127998
    [60] Al Afif R, Pfeifer C, Pröll T (2020) Bioenergy recovery from cotton stalk. Advances Cotton Res. https://doi.org/10.5772/intechopen.88005 doi: 10.5772/intechopen.88005
    [61] Stavropoulos GG, Zabaniotou AA (2005) Production and characterization of activated carbons from olive-seed waste residue. Microporous Mesoporous Mater 82: 79–85.https://doi.org/10.1016/j.micromeso.2005.03.009 doi: 10.1016/j.micromeso.2005.03.009
    [62] Dominguez EL, Uttran A, Loh SK, et al. (2020) Characterisation of industrially produced oil palm kernel shell biochar and its potential as slow release nitrogen-phosphate fertilizer and carbon sink. Mater Today Proc 31: 221–227.https://doi.org/10.1016/j.matpr.2020.05.143 doi: 10.1016/j.matpr.2020.05.143
    [63] Toro JL, Carrillo ES, Bustos D, et al. (2019) Thermogravimetric characterization and pyrolysis of soybean hulls. Bioresour Technol Rep 6: 183–189.https://doi.org/10.1016/j.biteb.2019.02.009 doi: 10.1016/j.biteb.2019.02.009
    [64] Marafon AC, Salomon KR, Amorim ELC, et al. (2020) Use of sugarcane vinasse to biogas, bioenergy, and biofertilizer production. Sugarcane Biorefinery, Technol Perspectives, 179–194.https://doi.org/10.1016/B978-0-12-814236-3.00010-X doi: 10.1016/B978-0-12-814236-3.00010-X
    [65] Sindhu R, Binod P, Pandey A, et al. (2019) Biofuel production from biomass. Current Dev Biotechnol Bioeng, 79–92.https://doi.org/10.1016/B978-0-444-64083-3.00005-1 doi: 10.1016/B978-0-444-64083-3.00005-1
    [66] Solís JA, Morales M, Ayala RC, et al. (2012) Obtaining activated carbon from agro-industrial waste and its evaluation in the removal of color from sugarcane juice. Tecnol, Cienc, Educ 27: 36–48. Available from:https://www.redalyc.org/articulo.oa?id = 48224413006.
    [67] Medhat A, El-Maghrabi HH, Abdelghany A, et al. (2021) Efficiently activated carbons from corn cob for methylene blue adsorption. Appl Surface Sci Advances 3: 100037.https://doi.org/10.1016/j.apsadv.2020.100037 doi: 10.1016/j.apsadv.2020.100037
    [68] Abbey CYB, Duwiejuah AB, Quianoo AK (2023) Removal of toxic metals from aqueous phase using cacao pod husk biochar in the era of green chemistry. Appl Water Sci 13: 57.https://doi.org/10.1007/s13201-022-01863-5 doi: 10.1007/s13201-022-01863-5
    [69] Marín FJ, García RM, Barrezueta SA (2020) Results of the application of biochar obtained from banana and cocoa residues in corn cultivation. Rev Cient Agroecosist 8: 83–88. Available from:https://aes.ucf.edu.cu/index.php/aes/article/view/404.
    [70] Pinzon DA, Adarme CA, Vargas LY, et al. (2022) Biochar as a waste management strategy for cadmium contaminated cocoa pod husk residues. Int JRecycl Org Waste Agric 11: 101–115.https://doi.org/10.30486/ijrowa.2021.1920124.1192 doi: 10.30486/ijrowa.2021.1920124.1192
    [71] Nosratpour MJ, Karimi K, Sadeghi M (2018) Improvement of ethanol and biogas production from sugarcane bagasse using sodium alkaline pretreatments. J Environ Manage 226: 329–339.https://doi.org/10.1016/j.jenvman.2018.08.058 doi: 10.1016/j.jenvman.2018.08.058
    [72] Santos CV, Lourenzani AEBS, Mollo M, et al. (2021) Study of the biogas potential generated from residue: peanut shells. Rev Bras Ciênc Ambient (Online) 56: 318–326.https://doi.org/10.5327/Z21769478765
    [73] Tsai WT, Lee MK, Chang YM (2006) Fast pyrolysis of rice straw, sugarcane bagasse and coconut shell in an induction-heating reactor. J Anal Appl Pyrolysis 76: 230–237.https://doi.org/10.1016/j.jaap.2005.11.007 doi: 10.1016/j.jaap.2005.11.007
    [74] Zheng J, Yi W, Wang N (2008) Bio-oil production from cotton stalk. Energy Convers Manage 49: 1724–1730.https://doi.org/10.1016/j.enconman.2007.11.005 doi: 10.1016/j.enconman.2007.11.005
    [75] Kim SW, Koo BS, Lee DH (2014) Catalytic pyrolysis of palm kernel shell waste in a fluidized bed. Bioresour Technol 167: 425–432.https://doi.org/10.1016/j.biortech.2014.06.050 doi: 10.1016/j.biortech.2014.06.050
    [76] Robak K, Balcerek M (2018) Review of second-generation bioethanol production from residual biomass. Food Technol Biotechnol 56: 174–187.https://doi.org/10.17113/ftb.56.02.18.5428 doi: 10.17113/ftb.56.02.18.5428
    [77] Guerrero AB, Ballesteros I, Ballesteros M (2018) The potential of agricultural banana waste for bioethanol production. Fuel 213: 176–185.https://doi.org/10.1016/j.fuel.2017.10.105 doi: 10.1016/j.fuel.2017.10.105
    [78] Kaur M, Kaur M (2012) A review on utilization of coconut shell as coarse aggregates in mass concrete. Int J Appl Eng Res 7: 2063–2065.
    [79] Tomar R, Kishore K, Singh Parihar H, et al. (2021) A comprehensive study of waste coconut shell aggregate as raw material in concrete. Mater Today Proc 44: 437–443.https://doi.org/10.1016/j.matpr.2020.09.754 doi: 10.1016/j.matpr.2020.09.754
    [80] Chávez V, Valencia A, Córdova C, et al. (2017) Banana stem leachates: Obtaining and potential uses. Cuad Biodivers 53: 1–8.https://doi.org/10.14198/cdbio.2017.53.01 doi: 10.14198/cdbio.2017.53.01
    [81] Abdul Wahid FRA, Saleh S, Abdul Samad NAF (2017) Estimation of higher heating value of torrefied palm oil wastes from proximate analysis. Energy Proc 138: 307–312.https://doi.org/10.1016/j.egypro.2017.10.102 doi: 10.1016/j.egypro.2017.10.102
    [82] Florian TDM, Villani N, Aguedo M, et al. (2019) Chemical composition analysis and structural features of banana rachis lignin extracted by two organosolv methods. Ind Crops Prod 132: 269–274.https://doi.org/10.1016/j.indcrop.2019.02.022 doi: 10.1016/j.indcrop.2019.02.022
    [83] Granados DA, Velásquez HI, Chejne F (2014) Energetic and exergetic evaluation of residual biomass in a torrefaction process. Energy 74: 181–189.https://doi.org/10.1016/j.energy.2014.05.046 doi: 10.1016/j.energy.2014.05.046
    [84] Jirón EG, Rodríguez K, Bernal C (2020) Cellulose nanofiber production from banana rachis. IJESC 10: 24683–24689.
    [85] Balogun AO, Lasode OA, McDonald AG (2018) Thermochemical and pyrolytic analyses of Musa spp. residues from the rainforest belt of Nigeria. Environ Prog Sustainable Energy 37: 1932–1941.https://doi.org/10.1002/ep.12869 doi: 10.1002/ep.12869
    [86] Meramo SI, Ojeda KA, Sanchez E (2019) Environmental and safety assessments of industrial production of levulinic acid via acid-catalyzed dehydration. ACS Omega 4: 22302–22312.https://doi.org/10.1021/acsomega.9b02231 doi: 10.1021/acsomega.9b02231
    [87] Guerrero AB, Aguado PL, Sánchez J, et al. (2016) GIS-Based assessment of banana residual biomass potential for ethanol production and power generation: A case study. Waste Biomass Valor 7: 405–415.https://doi.org/10.1007/s12649-015-9455-3 doi: 10.1007/s12649-015-9455-3
    [88] Ozyuguran A, Akturk A, Yaman S (2018) Optimal use of condensed parameters of ultimate analysis to predict the calorific value of biomass. Fuel 214: 640–646.https://doi.org/10.1016/j.fuel.2017.10.082 doi: 10.1016/j.fuel.2017.10.082
    [89] Titiloye JO, Abu Bakar MS, Odetoye TE (2013) Thermochemical characterisation of agricultural wastes from West Africa. Ind Crops Prod 47: 199–203.https://doi.org/10.1016/j.indcrop.2013.03.011 doi: 10.1016/j.indcrop.2013.03.011
    [90] Ghysels S, Acosta N, Estrada A, et al. (2020) Integrating anaerobic digestion and slow pyrolysis improves the product portfolio of a cocoa waste biorefinery. Sustainable Energy Fuels 4: 3712–3725.https://doi.org/10.1039/D0SE00689K doi: 10.1039/D0SE00689K
    [91] Akinola AO, Eiche JF, Owolabi PO, et al. (2018) Pyrolytic analysis of cocoa pod for biofuel production. Niger J Technol 37: 1026.https://doi.org/10.4314/njt.374.1866 doi: 10.4314/njt.374.1866
    [92] Londoño-Larrea P, Villamarin-Barriga E, García AN, et al. (2022) Study of cocoa pod husks thermal decomposition. Appl Sci 12: 9318.https://doi.org/10.3390/app12189318 doi: 10.3390/app12189318
    [93] Tsai C, Tsai W, Liu S, et al. (2018) Thermochemical characterization of biochar from cocoa pod husk prepared at low pyrolysis temperature. Biomass Convers Biorefin 8: 237–243.https://doi.org/10.1007/s13399-017-0259-5 doi: 10.1007/s13399-017-0259-5
    [94] Adjin M, Asiedu N, Dodoo D, et al. (2018) Thermochemical conversion and characterization of cocoa pod husks a potential agricultural waste from Ghana. Ind Crops Prod 119: 304–312.https://doi.org/10.1016/j.indcrop.2018.02.060 doi: 10.1016/j.indcrop.2018.02.060
    [95] Channiwala SA, Parikh PP (2002) A unified correlation for estimating HHV of solid, liquid and gaseous fuels. Fuel 81: 1051–1063.https://doi.org/10.1016/S0016-2361(01)00131-4 doi: 10.1016/S0016-2361(01)00131-4
    [96] Kabir R, Anwar S, Yusup S, et al. (2022) Exploring the potential of coconut shell biomass for charcoal production. Ain Shams Eng J 13: 101499.https://doi.org/10.1016/j.asej.2021.05.013 doi: 10.1016/j.asej.2021.05.013
    [97] Borel LDMS, de Lira TS, Ataíde CH, et al. (2021) Thermochemical conversion of coconut waste: Material characterization and identification of pyrolysis products. J Therm Anal Calorim 143: 637–646.https://doi.org/10.1007/s10973-020-09281-y doi: 10.1007/s10973-020-09281-y
    [98] Said M, John G, Mhilu C, et al. (2015) The study of kinetic properties and analytical pyrolysis of coconut shells. J Renewable Energy 2015: 1–8.https://doi.org/10.1155/2015/307329 doi: 10.1155/2015/307329
    [99] Rout T, Pradhan D, Singh RK, et al. (2016) Exhaustive study of products obtained from coconut shell pyrolysis. J Environ Chem Eng 4: 3696–3705.https://doi.org/10.1016/j.jece.2016.02.024 doi: 10.1016/j.jece.2016.02.024
    [100] Gani A, Erdiwansyah, Desvita H, et al. (2024) Comparative analysis of HHV and LHV values of biocoke fuel from palm oil mill solid waste. Case Stud Chem EnvironEng 9: 100581.https://doi.org/10.1016/j.cscee.2023.100581 doi: 10.1016/j.cscee.2023.100581
    [101] Nizamuddin S, Jayakumar NS, Sahu JN, et al. (2015) Hydrothermal carbonization of oil palm shell. Korean J Chem Eng 32: 1789–1797.https://doi.org/10.1007/s11814-014-0376-9 doi: 10.1007/s11814-014-0376-9
    [102] Kim SJ, Jung SH, Kim JS (2010) Fast pyrolysis of palm kernel shells: Influence of operation parameters on the bio-oil yield and the yield of phenol and phenolic compounds. Bioresour Technol 101: 9294–9300.https://doi.org/10.1016/j.biortech.2010.06.110 doi: 10.1016/j.biortech.2010.06.110
    [103] Uemura Y, Omar WN, Tsutsui T, et al. (2011) Torrefaction of oil palm wastes. Fuel 90: 2585–2591.https://doi.org/10.1016/j.fuel.2011.03.021 doi: 10.1016/j.fuel.2011.03.021
    [104] Chang G, Huang Y, Xie J, et al. (2016) The lignin pyrolysis composition and pyrolysis products of palm kernel shell, wheat straw, and pine sawdust. Energy Convers Manage 124: 587–597.https://doi.org/10.1016/j.enconman.2016.07.038 doi: 10.1016/j.enconman.2016.07.038
    [105] Marrugo G, Valdés CF, Chejne F (2016) Characterization of colombian agroindustrial biomass residues as energy resources. Energy Fuels 30: 8386–8398.https://doi.org/10.1021/acs.energyfuels.6b01596 doi: 10.1021/acs.energyfuels.6b01596
    [106] Ma Z, Chen D, Gu J, et al. (2015) Determination of pyrolysis characteristics and kinetics of palm kernel shell using TGA–FTIR and model-free integral methods. Energy Convers Manage 89: 251–259.https://doi.org/10.1016/j.enconman.2014.09.074 doi: 10.1016/j.enconman.2014.09.074
    [107] Liew RK, Chong MY, Osazuwa OU, et al. (2018) Production of activated carbon as catalyst support by microwave pyrolysis of palm kernel shell: a comparative study of chemical versus physical activation. Res Chem Intermed 44: 3849–3865.https://doi.org/10.1007/s11164-018-3388-y doi: 10.1007/s11164-018-3388-y
    [108] Athira G, Bahurudeen A, Appari S (2021) Thermochemical conversion of sugarcane Bagasse: composition, reaction kinetics, and characterisation of by-products. Sugar Tech 23: 433–452.https://doi.org/10.1007/s12355-020-00865-4 doi: 10.1007/s12355-020-00865-4
    [109] Kanwal S, Chaudhry N, Munir S, et al. (2019) Effect of torrefaction conditions on the physicochemical characterization of agricultural waste (sugarcane bagasse). Waste Manage 88: 280–290.https://doi.org/10.1016/j.wasman.2019.03.053 doi: 10.1016/j.wasman.2019.03.053
    [110] Chen WH, Ye SC, Sheen HK (2012) Hydrothermal carbonization of sugarcane bagasse via wet torrefaction in association with microwave heating. Bioresour Technol 118: 195–203.https://doi.org/10.1016/j.biortech.2012.04.101 doi: 10.1016/j.biortech.2012.04.101
    [111] Iryani DA, Kumagai S, Nonaka M, et al. (2017) Characterization and production of solid biofuel from sugarcane bagasse by hydrothermal carbonization. Waste Biomass Valor 8: 1941–1951.https://doi.org/10.1007/s12649-017-9898-9 doi: 10.1007/s12649-017-9898-9
    [112] Beta San Miguel Beta San Miguel, Responsabilidad BSM. Available from: https://www.bsm.com.mx/resp_ambiental.html.
    [113] Oleopalma (2022) 2022 Sustainable ability report.
    [114] American Society of Testing Methods (2002) ASTM D-2974, standard test methods for moisture, ash, and organic matter of peat and other organic soils, 2002. Available from: https://www.astm.org/d2974-14.html.
    [115] Sheng C, Azevedo JLT (2005) Estimating the higher heating value of biomass fuels from basic analysis data. Biomass Bioenergy 28: 499–507.https://doi.org/10.1016/j.biombioe.2004.11.008 doi: 10.1016/j.biombioe.2004.11.008
    [116] Friedl A, Padouvas E, Rotter H, et al. (2005) Prediction of heating values of biomass fuel from elemental composition. Anal Chim Acta 544: 191–198.https://doi.org/10.1016/j.aca.2005.01.041 doi: 10.1016/j.aca.2005.01.041
    [117] Wang C, Deng X, Xiang W, et al. (2020) Calorific value variations in each component and biomass-based energy accumulation of red-heart Chinese fir plantations at different ages. Biomass Bioenergy 134: 105467.https://doi.org/10.1016/j.biombioe.2020.105467 doi: 10.1016/j.biombioe.2020.105467
    [118] Yin CY (2011) Prediction of higher heating values of biomass from proximate and ultimate analyses. Fuel 90: 1128–1132.https://doi.org/10.1016/j.fuel.2010.11.031 doi: 10.1016/j.fuel.2010.11.031
    [119] Environmental Protection Agency USA (1996) EPA, METHOD 6010B, Inductively coupled plasma-atomic emission spectrometry, 1996.
    [120] Husain Z, Zainac Z, Abdullah Z (2002) Briquetting of palm fibre and shell from the processing of palm nuts to palm oil. Biomass Bioenergy 22: 505–509.https://doi.org/10.1016/S0961-9534(02)00022-3 doi: 10.1016/S0961-9534(02)00022-3
    [121] Sosa JA, Laines JR, Guerrero D, et al. (2022) Bioenergetic valorization of Sargassum fluitans in the Mexican Caribbean: The determination of the calorific value and washing mechanism. AIMS Energy 10: 45–63.https://doi.org/10.3934/energy.2022003 doi: 10.3934/energy.2022003
    [122] Demirbas A (2002) Relationships between heating value and lignin, moisture, ash and extractive contents of biomass fuels. Energy Explor Exploit 20: 105–111.https://doi.org/10.1260/014459802760170420 doi: 10.1260/014459802760170420
    [123] López MI, Sosa JA, Laines JR, et al. (2023) Aerobic biotransformation of Sargassum fluitans in combination with sheep manure: optimization of control variables. Chem Ecol 39: 823–842.https://doi.org/10.1080/02757540.2023.2263427 doi: 10.1080/02757540.2023.2263427
    [124] Vergara GR (2022) Physical and energetic characterization of the fibrous residue from the processing of African palm by varying the percentage of humidity for bioenergy use in the Quevepalma company. Available from: http://repositorio.espe.edu.ec/handle/21000/28641.
    [125] Huaraca JN (2022) Determination of the calorific value of agroindustrial waste from wheat husk and barley straw enriched with cellulose nanoparticles as an energy alternative. Available from: http://dspace.espoch.edu.ec/handle/123456789/20236.
  • Reader Comments
  • © 2024 the Author(s), licensee AIMS Press. This is an open access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0)
通讯作者: 陈斌, bchen63@163.com
  • 1. 

    沈阳化工大学材料科学与工程学院 沈阳 110142

  1. 本站搜索
  2. 百度学术搜索
  3. 万方数据库搜索
  4. CNKI搜索

Metrics

Article views(1358) PDF downloads(217) Cited by(0)

/

DownLoad:  Full-Size Img  PowerPoint
Return
Return

Catalog