Citation: Hai The Pham. Biosensors based on lithotrophic microbial fuel cells in relation to heterotrophic counterparts: research progress, challenges, and opportunities[J]. AIMS Microbiology, 2018, 4(3): 567-583. doi: 10.3934/microbiol.2018.3.567
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Since 1976, about 25 outbreaks of EVD have been declared including the latest one in Western Africa (2014-2015) which was the most devastating one among human populations [18,56]. There are five known Ebola virus strains: ZEBOV, SEBOV, ICEBOV, BDBV, REBOV [18]. Of these, the first four have highly threatened both human and nonhuman primates, causing viral hemorrhagic fever with case fatality rates of up to 90% [18,50]. For instance, the most recent and deadliest Ebola outbreak in Western Africa was caused by the ZEBOV virus strain.
No approved treatments and homologated vaccines are currently available. However, dedicated research efforts have led to the first therapeutic trial with ZMapp [28]. Furthermore, the VSV-ZEBOV vaccine has been found and is still in its third experimental phase [28]. These two remarkable efforts have helped to curtain the recent Western Africa outbreak, even though the latter effort was less decisive (due to its late trial at the end of the West African outbreak) than the former.
Other control efforts (including rehydration, isolation, education of populations at risk, avoidance of consumption of bush meat, practicing of safe burials) have been implemented to stop past Ebola outbreaks. In addition to the threat EVD poses to human health, the negative impact of EVD infection on already threatened animal populations in Africa has come to light and led to a resurgence of efforts to understand the complex life ecology of Ebola virus in nature [26,51]. However, despite considerable efforts, it remains unclear how the EVD is maintained and transmitted in nature, and how the index case (first patient) is infected. Since EVD is a zoonotic-borne disease (transmitted accidentally by direct contact with infected living or dead animals), human epidemics were concomitant with epizootic in great apes [37,38]. Moreover, due to the fact that recent works have provided new evidence that fruit bats might play an important role as a reservoir species of EVD, some intricate and pending questions which are biologically relevant have been raised:
1. Where and how does the index case (first patient) acquire the infection?
2. Do direct transmissions from bats to humans and/or nonhuman primates occur?
3. Which human behaviors expose humans to the risk of contracting EVD from non-human sources?
4. Are fruit bats the only reservoir hosts for Ebola viruses?
5. What are the environmental factors contributing to Ebola virus transmission to human beings and non-human primates from the reservoir species?
6. Can mathematical modeling help to understand and predict the of EVD outbreaks in the future?
This paper focuses on the last question. We address it, with the ultimate aim to answer the other five questions. Before moving to the modeling section, there is a need to support and motivate these questions. Since the 1976 Sudan outbreak where there was evidence that the index case was a worker in a cotton factory with evidence of bats at site, many other index cases (from 1994-2001) showed evident contacts with bats and/or consumption of butchered great apes and/or other wildlife meat. The synoptic Table 1 summarizes the sources for contamination of the first patient during EVD outbreaks and highlights his/her contact with bats, dead or butchered wildlife bush meat. The table also talks to the transmission from bat to human, from non-human primate to human, and it illustrates how human behaviors can drive the contamination of EVD. The issue of fruit bats being reservoir for Ebola viruses is supported by the work [37] which has demonstrated that fruit bats bear Ebola viruses and are not affected by the disease. Furthermore, the first four questions are biologically investigated in [26,37,51] where the known, the probable/suspected and the hypothetical direct transmission mechanisms (routes) of EVD are addressed. Regarding the fifth question, the works in [9,10,46,53,60] highlight the indirect environmental contamination route of EVD.
Year | Country | Species | Starting date | Source of infection |
1976 | DRC | Zaire | September | Unknown. Index case was a mission school teacher. |
1976 | Sudan | Sudan | June | Worker in a cotton factory. |
Evidence of bats at site. | ||||
1977 | DRC | Zaire | June | Unknown (retrospective). |
1979 | Sudan | Sudan | July | Worker in cotton factory. |
Evidence of bats at site. | ||||
1994 | Gabon | Zaire | December | Gold-mining camps. |
Evidence of bats at site. | ||||
1994 | Ivory Coast | Ivory Coast | November | Scientist performing autopsy on a dead wild chimpanzee. |
1995 | Liberia | Ivory Coast | December | Unknown. Refugee from civil war. |
1995 | DRC | Zaire | January | Index case worked in a forest adjoining the city. |
1996 | Gabon | Zaire | January | People involved in the butchering of a dead chimpanzee. |
1996-1997 | Gabon | Zaire | July | Index case was a hunter living in a forest camp. |
2000-2001 | Uganda | Sudan | September | Unknown. |
2001-2002 | Gabon | Zaire | October | Contact with dead or butchered apes or other wildlife. |
2001-2002 | DRC | Zaire | October | Contact with dead or butchered apes or other wildlife. |
2002-2003 | DRC | Zaire | December | Contact with dead or butchered apes or other wildlife. |
2003 | DRC | Zaire | November | Contact with dead or butchered apes or other wildlife. |
2004 | Sudan | Sudan | May | Unknown. |
2005 | DRC | Zaire | April | unknown. |
2007 | DRC | Zaire | December | Contact with dead or butchered apes or other wildlife. |
2007 | Uganda | Bundibugyo | December | Unknown. |
2008 | DRC | Zaire | December | Index case was a village chief and a hunter. |
2012 | Uganda | Bundibugyo | June | Index case was a secondary school teacher in Ibanda district. |
2012 | DRC | Zaire | June | Index case was a hunter living in a forest camp. |
2013-2015 | Guinea | Zaire | December | Contact with bats or fruits contaminated by bat droppings. |
2014-2015 | Liberia | Zaire | April | Index case was transported from Guinea. |
2014-2015 | Sierra Leone | Zaire | April | A traditional healer, treating Ebola patients from Guinea. |
2014 | DRC | Zaire | August | Pregnant women who butchered a bush animal. |
The complexity of the questions raised above is captured in [26,51] for the EVD mechanisms of transmission in a complex Ebola virus life ecology as depicted in Fig. 1 of the disease transmission diagram. This will be reflected in the construction of our model by: (a) Taking into account the well known, the probable/suspected, the hypothetical and the environmental transmission pathways; (b) Involving the interplay between the epizootic phase (during which the disease circulates periodically amongst non-human primate populations and decimates them), the enzootic phase (during which the disease always remains in fruit bat populations) and the epidemic phase (during which the EVD threatens and decimates human populations) of the disease under consideration.
The complexity of the Ebola virus life ecology is clear from the biological studies carried out in [26,51] (see also Ebola virus ecology and transmission therein). From the mathematical point of view, the complexity and challenges we are confronted with and have addressed range from the modeling of the forces of infection, the computation of the reproduction number (see Eq. (8) and Remark1), the computation of the endemic equilibrium, to the use of less standard tools (e.g. decomposition techniques [54]) to investigate the dynamics of EVD.
Note that the recent and former EVD outbreaks have highlighted the importance of human behavior in the transmission process [11,21,41]. For instance, there were evidence of behavioral reaction and self-protection measures: people were scared, they panicked and left care centers, etc... As this important feature calls for a different modeling approach based on "Behavioral Epidemiology" developed in [41], we are busy investigating it in another work, where self-protection measures driven by human behavior is incorporated.
The rest of the paper is organized as follows. In Section 2 we derive the model. The mathematical analysis starts in Section 3 with the basic properties of the model, followed by the computation of the reproduction number
To avoid confusion, bat will not be called "animal". The term animal is reserved for any non-human primate and/or any other wild animal that may be responsible for the transmission of EVD. Note that our model formulation is focused essentially on non-human primates (great apes) as animal species.
Motivated by the biological papers [25,26,37,51] regarding the transmission mechanisms and the recent mathematical works [9,53], our model is based on the zoonotic-borne disease setting and takes into account both direct and indirect transmission routes. We distinguish three host populations: humans and animals as end hosts and fruit bats as intermediate reservoir hosts [5,32,37,45,47]. Since the model incorporates the indirect environmental transmission, we add the dynamics of the concentration of free living Ebola viruses in the environment [53,56,60]. The latter compartment should not be considered as an epidemiological class; it is regarded as a pool of Ebola viruses. This pool is supplied by infected humans, infected animals and infected fruit bats with:
(ⅰ) The presence of carcasses of infected and dead animals in the forest on which some animals can feed [56].
(ⅱ) The manipulation of infected fruit bats and animals hunted by humans for food.
(ⅲ) The contaminated fruits harvested for food by humans and primates in the forest [25,26,37].
(ⅳ) The contaminated syringes re-used in health care centers [50,55,58].
(ⅴ) The bed linen contaminated by infected human's stool, urine, vomits or sweat in health care centers or in family homes of infected individuals [50,55].
(ⅵ) The bush fruits contaminated by bats droppings [38].
As mentioned earlier, the variables include the human, the animal, the bat (reservoir of Ebola viruses) populations and the concentration of free living Ebola viruses in the environment. More precisely, at time
The model derivation is based on the following main assumptions:
The works in [26,51] amongst others on the complex Ebola virus life ecology lead to the dynamics flowchart in Fig. 1 which in turn gives the following system of nonlinear ordinary differential equations:
$ \dfrac{dS_h}{dt} = \Lambda_h - (\lambda_h+ \mu_h)S_h, $ | (1a) |
$ \dfrac{dE_h}{dt} = \lambda_hS_h - \left(\mu_h + \omega\right)E_h, $ | (1b) |
$ \dfrac{dI_h}{dt} = \omega E_h - \left( \mu_h+\gamma \right)I_h, $ | (1c) |
$ \dfrac{dR_h}{dt} = \gamma(1-f)I_h - \mu_hR_h, $ | (1d) |
$ \dfrac{dV}{dt} = \alpha_h I_h + \alpha_a I_a + \alpha_b I_b - \mu_v V, $ | (1e) |
$ \dfrac{dS_a}{dt} = \Lambda_a - (\lambda_a+ \mu_a) S_a, $ | (1f) |
$ \dfrac{dI_a}{dt} = \lambda_aS_a - (\mu_a +\delta_a ) I_a, $ | (1g) |
$ \dfrac{dS_b}{dt} = \Lambda_b - (\lambda_b + \mu_b)S_b, $ | (1h) |
$ \dfrac{dI_b}{dt} = \lambda_bS_b -\mu_b I_b. $ | (1i) |
The force of infection acting on humans is,
$ \lambda_h=\dfrac{\beta_{hh}\left(I_h+\xi_h\nu_h\gamma f I_h + \theta_h\gamma(1-f) I_h\right)}{N_h} + \dfrac{\beta_{ha}\left(1+\xi_a\nu_a\delta_a\right)I_a}{N_h}+ \dfrac{\beta_{hb}I_b}{N_h} + \dfrac{\beta_{hv}V}{K+V}. $ | (2) |
It is the sum of the contributions below:
● The human-to-human force of infection
$ \lambda_{hh} = \dfrac{\beta_{hh}}{N_h}\left(1+\xi_h\nu_h\gamma f + \theta_h\gamma(1-f)\right)I_h, $ |
which gathers the three contamination processes by:
-infected, i.e.
-Ebola-deceased, i.e.
-clinically recovered individuals i.e.
● The animal-to-human force of infection
$ \lambda_{ha} = \dfrac{\beta_{ha}(1 + \xi_a\nu_a\delta_a)I_a}{N_h}, \;\;\;\;\text{where} \;\;\;\; \xi_a = \dfrac{1}{\tau_a}. $ |
● The bat-to-human force of infection
$ \lambda_{hb}= \dfrac{\beta_{hb}I_b}{N_b}. $ |
● The environment-to-human force of infection
$ \lambda_{hv}= \dfrac{\beta_{hv}V}{K+V}. $ |
Similarly, the force of infection within the animal population
$ \lambda_a= \dfrac{\beta_{aa} (1 + \xi_a\nu_a\delta_a)I_a}{N_a} + \dfrac{\beta_{ab}I_b}{N_a} + \dfrac{\beta_{av}V}{K+V}, $ | (3) |
involves the following three contributions:
● The animal-to-animal force of infection
$ \lambda_{aa}= \dfrac{\beta_{aa} (1+\xi_a\nu_a\delta_a)I_a}{N_a}; $ |
● The bat-to-animal force of infection
$ \lambda_{ab}= \dfrac{\beta_{ab}I_b}{N_a}. $ |
● The environment-to-animal force of infection
$ \lambda_{av}= \dfrac{\beta_{av}V}{K+V}. $ |
Finally, the force of infection in bat's population is modeled by
$ \lambda_b = \beta_{bb}I_b + \dfrac{\beta_{bv}V}{K+V} $ | (4) |
and consists of two contributions from:
-Within bat adequate contacts
$ \lambda_{bb} = \beta_{bb}I_b. $ |
-The contact with the environment
$ \lambda_{bv} = \dfrac{\beta_{bv}V}{K+V}. $ |
Note that we have considered the infection through contact with environmental free Ebola viruses. As it is the case for most models involving free-living pathogens in the environment [3,4,8,12,17,49,53,59], the environmental-related forces of infection,
Finally, the last equation of system (1) describes the dynamics of Ebola viruses with shedding from humans, animals and bats. The parameters used for system (1) and their biological interpretations are giving in Table 2. For notational simplifications let,
Symbols | Biological interpretations |
|
Recruitment rate of susceptible humans, animals and bats, respectively. |
|
Natural mortality rate of humans, animals and bats, respectively. |
|
Virulence of Ebola virus in the corpse of the dead humans. |
|
Mean duration of time that elapse after death before a human cadaver is completely buried. |
|
Modification parameter of infectiousness due to dead human individuals. |
|
Mean duration of time that elapse after death before an animal's cadaver is completely cleared out. |
|
Modification parameter of infectiousness due to dead animals individuals. |
|
Virulence of Ebola virus in the corpse of dead animals. |
|
Incubation rate of human individuals. |
|
Removal rate from infectious compartment due to either to disease induced death, or by recovery. |
|
Death rate of infected animals. |
|
Shedding rates of Ebola virus in the environment by humans, animals and bats, respectively. |
|
Mean duration of time that elapse before the complete clearance of Ebola virus in humans. |
|
Modification parameter of contact rate of recovered humans (sexual activity of recovered). |
in the semen/breast milk of a recovered man/woman. | |
|
Proortion of removed human individuals who die due EVD (i.e. case fatality rate). |
|
Virus 50 % infectious dose, sufficient to cause EVD. |
|
Contact rate between susceptible humans and infected humans. |
|
Contact rate between susceptible humans and bats. |
|
Contact rate between susceptible humans and Ebola viruses. |
|
Contact rate between susceptible humans and infected animals. |
|
Contact rate between susceptible bats and infectious bats. |
|
Contact rate between susceptible animals and infectious bats. |
|
Contact rate between susceptible bats and and Ebola viruses. |
|
Contact rate between susceptible and infected animals. |
|
Contact rate between susceptible animals and Ebola viruses. |
$ \Phi_h = 1+\xi_h\nu_h\gamma f + \theta_h\gamma(1-f) \;\;\;\; \text{and} \;\;\;\; \Phi_a = 1+\xi_a\nu_a\delta_a. $ |
With this notation it is easy to check that system (1) interconnects the following sub-models:
● The human population sub-model
$ \left\{dShdt=Λh−βhhΦhShIhNh−βhaΦaShIaNh−βhbShIbNh−βhvShVK+V−μhSh,dEhdt=βhhΦhShIhNh+βhaΦaShIaNh+βhbShIbNh+βhvShVK+V−(μh+ω)Eh,dIhdt=ωEh−(μh+γ)Ih,dRhdt=γ(1−f)Ih−μhRh.\right. $ | (5) |
● The animal population sub-model
$ \left\{dSadt=Λa−βaaΦaSaIaNa−βabSaIbNa−βavSaVK+V−μaSa,dIadt=βaaΦaSaIaNa+βabSaIbNa+βavSaVK+V−(μa+δa)Ia.\right. $ | (6) |
● The bat population sub-model
$ \left\{dSbdt=Λb−βbbSbIb−βbvSbVK+V−μbSb,dIbdt=βbbSbIb+βbvSbVK+V−μbIb.\right. $ | (7) |
It should be emphasized that not much is known about the bat-to-bat EVD transmission. However, knowing that fruit bats settle or congregate for rest or sleep (they live in colony), it is acceptable to assume that direct bat-to-bat contact is the main route of transmission and can be modeled by mass action incidence.
● The evolution of free-living Ebola viruses in the environment which is modeled by Eq. (1e).
The model presented her is a new in many respects. It extends the existing works [1,9,16,24,35,36,44,53] in the sense that it considers the three phases of disease: the epizootic cycle in animals, the enzootic phase in fruit bats and the epidemic phase in humans. In particular, the novelty of our model is clear from the most recent work [9], where direct human-to-human transmission was considered and all other sources (e.g. consumption of bush meat, manipulation of fruit bats, indirect environmental contamination) were encompassed in a constant recruitment of Ebola viruses in the environment. The model developed here enriches the latter by modeling this recruitment through consideration of the complex Ebola virus life ecology, where animals and bats are explicitly involved in the EVD transmission cycle. It is therefore understandable why throughout this paper, we refer to system (1) as the full model.
For the EVD transmission model (1) to be epidemiological meaningful, it is important to prove that all state variables are non-negative at all time. That is, solutions of the system (1) with non-negative initial data will remain non-negative for all time
Theorem 3.1. Let the initial data
Furthermore, if we set
$N_h(0)\leq \dfrac{\Lambda_h}{\mu_h},\;\; N_a(0)\leq \dfrac{\Lambda_a}{\mu_a}, \;\;N_b(0)\leq \dfrac{\Lambda_b}{\mu_b} , \;\;V(0)\leq \dfrac{\Lambda_v}{\mu_v}, $ |
we have
$ N_h(t)\leq \dfrac{\Lambda_h}{\mu_h}, \;\; N_a(t)\leq \dfrac{\Lambda_a}{\mu_a},\;\; N_b(t)\leq \dfrac{\Lambda_b}{\mu_b} ,\;\; V(t)\leq \dfrac{\Lambda_v}{\mu_v}, \; \forall t\geq 0. $ |
Proof. Suppose
$\dfrac{d}{dt}\left\{S_h(t)\rho(t)\right\} = \Lambda_h\rho(t), $ |
where
$ S_h(t)\rho(t) - S_h(0) = \int^{t}_0 \Lambda_h \rho(t)dt, $ |
so that the division of both side by
$ S_h(t) = \left[S_h(0) + \int^{t}_0 \Lambda_h \rho(t)dt \right]\times \rho(t)^{-1} >0. $ |
The same arguments can be used to prove that
Furthermore,
Finally, using the fact that
Combining Theorem 3.1 with the trivial existence and uniqueness of a local solution for the model (1), we have established the following theorem which ensures the mathematical and biological well-posedness of system (1) (see [9], Theorem 3.3).
Theorem 3.2. The dynamics of model (1) is a dynamical system in the biological feasible compact set
$ \Gamma = \left\{(S_h, E_h, I_h, R_h, S_a, I_a, S_b, I_b, V) \in \mathbb R^9_+: N_h\leq \frac{\Lambda_h}{\mu_h}, N_a\leq \frac{\Lambda_a}{\mu_a}, N_b\leq \frac{\Lambda_b}{\mu_b}, V\leq \frac{\Lambda_v}{\mu_v} \right\} $ |
The disease free equilibrium (DFE) of the model is obviously
$P_0 = \left( S^0_h, 0, 0, 0, S^0_a, 0, S^0_b, 0, 0\right),\;\; \text{where} \;\; S^0_h = \dfrac{\Lambda_h}{\mu_h},\;\; S^0_a = \dfrac{\Lambda_a}{\mu_a},\;\; S^0_b = \dfrac{\Lambda_b}{\mu_b}.$ |
To compute the basic reproduction number of the model, we use the standard method of the next generation matrix developed in [2,8,19,20]. We separate the infected states
$ \mathcal F= \left(λhSh00λaSaλbSb0\right) \;\; \text{and}\;\; \mathcal W = \left((μh+ω)Eh−ωEh+(μh+γ)Ih−γ(1−f)Ih+μhRh(μa+δa)IaμbIb−αhIh−αaIa−αbIb+μvV\right). $ |
The Jacobian matrices
$ F= \left(0βhhΦh0βhaΦaβhbβhvΛhμhK000000000000000βaaΦaβabβavΛaμaK0000βbbΛbμbβbvΛbμbK000000\right) $ |
and
$ W= \left((μh+ω)00000−ω(μh+γ)00000−γ(1−f)μh000000μa+δa000000μb00−αh0−αa−αbμv\right), \text{respectively}.$ |
$ FW^{-1} = (Rhhv0Rhhv200Rahv0Rbhv0βhvΛhKμhμv000000000000Rhav0βavαhΛaKμaμv(μh+γ)0Raav0Rbav0βavΛaKμaμvRhbv0βbvαhωKμbμv(μh+γ)0Rabv0Rbbv0βbvΛbKμbμv000000)$ |
and
$ Rhhv0=βhhΦhω(μh+ω)(μh+γ)+αhβhvΛhωKμhμv(μh+ω)(μh+γ),Rbav0=βavΛaαbKμaμbμv+βabμb,Rahv0=βhaΦaμa+δa+βhvαaΛhKμhμv(μa+δa),Rbhv0=βhbμb+βhvαbΛhKμhμbμv,Raav0=βaaΦaμa+δa+βavΛaαaKμaμv(μa+δa),Rabv0=βbvΛbαaKμbμv(μa+δa),Rhav0=βavαhΛaωKμaμv(μh+ω)(μh+γ),Rhbv0=βbvαhΛbωKμbμv(μh+ω)(μh+γ),Rbbv0=βbbΛbμ2b+βbvΛbαbKμ2bμv,Rhhv20=βhhΦhμh+γ+βhvαhΛhKμh(μh+γ). $ |
Since zero is an eigenvalue for
$ \mathcal G = \left(Rhhv0Rahv0Rbhv0Rhav0Raav0Rbav0Rhbv0Rabv0Rbbv0\right), $ | (8) |
Therefore,
$\mathcal R_0= \rho{(\mathcal G)}, $ |
where for a square matrix
Based on some of the realistic assumptions stated in subsection 2.2, the remark below gives the explicit formula of the basic reproduction number
Remark 1. In some cases, the explicit formula for
1. In the sub-model with only human population dynamics and environmental transmission [53], the basic reproduction number denoted by
$ \mathcal R_{0, hv} = \mathcal R^{hhv}_0 = \dfrac{\beta_{hh}\Phi_h\omega}{(\mu_h+\omega)(\mu_h+\gamma)} + \dfrac{\alpha_h\beta_{hv}\Lambda_h\omega}{K\mu_h\mu_v(\mu_h+\omega)(\mu_h+\gamma)}. $ | (9) |
If in addition, the indirect transmission is neglected (i.e.
$ \mathcal R_{0, h} = \dfrac{\beta_{hh}\Phi_h\omega}{(\mu_h+\omega)(\mu_h+\gamma)}. $ | (10) |
We emphasize that the basic reproduction number giving by (10) is suitable for comparison with the basic reproduction numbers for some existing EDV models. For instance, looking at the expression
(ⅰ) The contribution from infected human individuals, i.e.
(ⅱ) The contribution from the clinically recovered individuals, i.e.
(ⅲ) The contribution from Ebola-deceased individuals, i.e.
With the above decomposition of
2. In the sub-model without animal's population dynamics, the basic reproduction number denoted by
$ \mathcal R_{0, hbv}= \dfrac{\mathcal R^{hhv}_0+\mathcal R^{bbv}_0+ \sqrt{\left(\mathcal R^{hhv}_0-\mathcal R^{bbv}_0\right)^2+4\mathcal R^{hbv}_0\mathcal R^{bhv}_0}}{2}. $ | (11) |
3. In the sub-model without bat's population dynamics, the basic reproduction number denoted by
$ \mathcal R_{0, hav}=\dfrac{\mathcal R^{hhv}_0+\mathcal R^{aav}_0+ \sqrt{\left(\mathcal R^{hhv}_0-\mathcal R^{aav}_0\right)^2+4\mathcal R^{hav}_0\mathcal R^{ahv}_0}}{2}. $ | (12) |
4. Suppose
$ \mathcal R_0 = \max\left\{\mathcal R_{0, b} \; ;\; \dfrac{\mathcal R^{hhv}_0+\mathcal R^{aav}_0 + \sqrt{\left(\mathcal R^{hhv}_0-\mathcal R^{aav}_0\right)^2+4\mathcal R^{hav}_0\mathcal R^{bhv}_0}}{2}\right\}. $ | (13) |
5. If
$ \mathcal R_0 = \max\left\{ \mathcal R_{0, hv}\; ; \; \mathcal R_{0, a} \; ;\; \mathcal R_{0, b} \right\} $ | (14) |
where
$ \mathcal R_{0, a} = \dfrac{\beta_{aa}\Phi_a}{\delta_a +\mu_a} \;, \; \mathcal R_{0, b} = \dfrac{\beta_{bb}\Lambda_b}{\mu^2_b} $ | (15) |
are the intra-specific basic reproduction numbers of the animal's population and bat's population without the environmental transmission, respectively and
Using Theorem 2 in [20], the following result is established:
Lemma 3.3. The DFE of system (1) is LAS whenever
The epidemiological implication of Lemma 3.3 is that EVD can be eliminated from the community when
Theorem 3.4. The DFE
Proof. Let
$ \left\{dxdt=(F−W)x−f(x,y),dydt=g(x,y), \right. $ | (16) |
where
$f(x,y)=((Nh−Sh)[βhhΦhIh+βhaΦaIaNh+βhbIb]+βhvV(ΛhμhK−ShK+V)00(Na−Sa)[βaaΦaIa+βabIbNa]+βavV(ΛaμaK−SaK+V)βbbIb(Λbμb−Sb)+βbvV(ΛbμbK−SbK+V)0),$ |
and
$ g(x, y) = (Λh−λhSh−μhShΛa−λaSa−μaSaΛb−λbSb−μbSb). $ |
It is straightforward that
$ \dfrac{d\widehat{x}}{dt} = \left(F-W\right)\widehat{x}. $ | (17) |
From Theorem 2 in [20], we have
$ \left\{d¯Shdt=Λh−μh¯Sh,d¯Sadt=Λa−μa¯Sa,d¯Sbdt=Λb−μb¯Sb. \right. $ | (18) |
It is straightforward that the linear system (18) has a unique equilibrium given by
Remark 2. To extend this global result in the case when
In this section, we investigate the existence of equilibrium points other than the disease free equilibrium, namely possible boundary equilibrium points and interior equilibria. First of all, let us give some useful remarks.
Assume that an equilibrium is such that
Similarly, if an equilibrium of (1) is such that
Obviously, if an equilibrium of (1) is such that
Conversely, assume the human population is disease free, then the free virus concentration
As a consequence, we have proven the following result:
Lemma 3.5. System (1) has no other boundary equilibrium than the disease-free equilibrium.
This lemma is very important as it excludes the possibility for the full model (1) to exhibit non trivial boundary equilibrium points. This suggests that the full model could have exactly one interior (endemic) equilibrium with the disease being present in all the populations under consideration. This, together with the existence and uniqueness of interior equilibrium for some system (1)-related sub-models [9], motivates the following conjecture that we make.
Conjecture 1. Assume that
The stability of the endemic equilibrium will be shown numerically at a later stage.
Remark 3. Actually, Conjecture 1 could be addressed in a separate work, by reducing the finding of equilibria to a fixed-point problem and apply a suitable fixed-point theorem for a multi-variable and sub-linear function for monotone dynamical systems or for systems of ordinary differential equations which generate an order preserving flow [29,30,48].
In order to investigate the effects of the environmental contamination on the transmission of EVD, it is reasonable to consider the sub-model of system (1) without the environment compartment. Note that, even though the full model (which couples many subsystems) could have two equilibria (namely, the disease free and the interior equilibria), it is not obvious that all its sub-models will exhibit the same property since the coupling can reduce or increase for example the number of equilibrium points. Below is the sub-model involving only human, animal and bat populations, but excluding the environment influence.
Here the environmental transmission is neglected. This assumption reflects the disease transmission cycles in [26,51], where the indirect contamination is not explicitly mentioned. This amounts to getting rid of the last terms in Eqs. (2)-(4) of the forces of infection. The model in this setting reads therefore:
$ \dfrac{dS_h}{dt} = \Lambda_h - \dfrac{\beta_{hh}\Phi_hS_hI_h}{N_h} - \dfrac{\beta_{ha}\Phi_aS_hI_a}{N_h} - \dfrac{\beta_{hb}S_h I_b}{N_h} - \mu_hS_h $ | (19a) |
$ \dfrac{dE_h}{dt} = \dfrac{\beta_{hh}\Phi_hS_hI_h}{N_h} + \dfrac{\beta_{ha}\Phi_aS_hI_a}{N_h} +\dfrac{\beta_{hb}S_h I_b}{N_h} - \left(\mu_h + \omega\right)E_h $ | (19b) |
$ \dfrac{dI_h}{dt} = \omega E_h - \left( \mu_h+\gamma \right)I_h $ | (19c) |
$ \dfrac{dR_h}{dt} = \gamma(1-f)\, I_h - \mu_hR_h $ | (19d) |
$ \dfrac{dS_a}{dt} = \Lambda_a - \dfrac{\beta_{aa}\Phi_a S_a I_a}{N_a} - \dfrac{\beta_{ab} S_a I_b}{N_a} - \mu_a S_a $ | (19e) |
$ \dfrac{dI_a}{dt} = \dfrac{\beta_{aa}\Phi_a S_a I_a}{N_a} + \dfrac{\beta_{ab} S_a I_b}{N_a} - (\mu_a +\delta_a ) I_a $ | (19f) |
$ \dfrac{dS_b}{dt} = \Lambda_b - \beta_{bb} S_b I_b - \mu_bS_b $ | (19g) |
$ \dfrac{dI_b}{dt} = \beta_{bb} S_b I_b - \mu_b I_b $ | (19h) |
The corresponding basic reproduction for this model is easily computed as
$ \mathcal R_{0, hab} = \max\left\{\mathcal R_{0, h}\;, \; \mathcal R_{0, a} \;, \; \mathcal R_{0, b} \right\} $ | (20) |
where,
$ \mathcal R_{0, h} = \dfrac{\beta_{hh}\Phi_h\omega}{(\mu_h+\omega)(\mu_h+\gamma)},\;\; \mathcal R_{0, a}= \dfrac{\beta_{aa}\Phi_a}{\mu_a +\delta_a} \: \: \text{and} \: \: \mathcal R_{0, b} = \dfrac{\beta_{bb}\Lambda_b}{\mu^2_b}. $ | (21) |
Actually,
Remark 4. Note that the non-negative matrix
$ \mathcal R_{0} = \rho{(\mathcal G)} \geq \mathcal R_{0, hab}.$ |
Consequently, the indirect environmental contamination enhances the transmissibility of EVD, and thus it increases the epidemic/endemic level of the disease.
The dynamics of sub-system (19) are confined in the biological feasible compact set subset of
$ \Gamma_{hab} = \left\{(S_h, E_h, I_h, R_h, S_a, I_a, S_b, I_b) \in \mathbb R^5_+ : N_h\leq \dfrac{\Lambda_h}{\mu_h }, \;\; N_a\leq \dfrac{\Lambda_a}{\mu_a }, \: \, N_b\leq \dfrac{\Lambda_b}{\mu_b } \right\}. $ | (22) |
Sub-model (19) is triangular. Indeed the variables (
Theorem 4.1. ([54], Theorem 3.1) Consider the system
$ \left\{dxdt=f(x),x∈Rn,dydt=g(x,y),x∈Rn,y∈Rm,withright−handsideofclassC1,and(x∗,y∗)anequilibriumpoint,i.e.,f(x∗)=0=g(x∗,y∗). \right. $ | (23) |
1.If
2. Moreover, if all the trajectories of system (23) are forward bounded, then
In order to apply Theorem 4.1, we need to study some sub-systems of Eq. (19).
We give here the long run behavior of the sub-model
$ \left\{dSbdt=Λb−βbbSbIb−μbSb,dIbdt=βbbSbIb−μbIb,\right. $ | (24) |
by establishing the global stability of its equilibrium points. Obviously this system (24) has two equilibria; namely, the disease-free equilibrium
$ S^0_b= \dfrac{\Lambda_b}{\mu_b},\;\; I^0_b=0 $ |
and the endemic equilibrium
$ \overline{P}_b = \left(\overline{S}_b, \, \overline{I}_b \right), $ |
which exists whenever
$ \overline{S}_b = \dfrac{\mu_b}{\beta_{bb}},\;\; \overline{I}_b = \dfrac{ \mu_b\left(\mathcal R_{0, b}-1\right)}{\beta_{bb}}. $ | (25) |
Obviously the dynamics of sub-model (24) are confined in the biological feasible compact set
$\Omega_b = \left\{ (S_b, I_b)\in \mathbb R^2_+ : S_b+I_b \leq \dfrac{\Lambda_b}{\mu_b}\right\}.$ |
Looking at model (24) in which the mass action law is applied, it is standard to deduce from the Lyapunov-LaSalle techniques its asymptotic behavior summarized in the result below.
Proposition 1. The following statements hold:
● If
● If
Here, we consider the subsystem (19e)-(19f)
$ \left\{dSadt=Λa−βaaΦaSaIaNa−βabSaIbNa−μaSa,dIadt=βaaΦaSaIaNa+βabSaIbNa−(μa+δa)Ia.\right. $ | (26) |
The dynamics of sub-model (26) are confined in the biological feasible compact set
$\Omega_a = \left\{ (S_a, I_a)\in \mathbb R^2_+ : S_a+I_a \leq \dfrac{\Lambda_a}{\mu_a}\right\}.$ |
Using the global asymptotic stability of equilibria for subsystem (24), the following two subsystems will be considered.
The variables
$ \left\{dSadt=Λa−βaaΦaSaIaNa−μaSa,dIadt=βaaΦaSaIaNa−(μa+δa)Ia.\right. $ | (27) |
Direct calculations show that model (27) has two possible non-negative equilibrium states: the disease-free equilibrium
$ \left\{¯Sa=Λaμa+(μa+δa)(R0,a−1),¯Ia=Λa(R0,a−1)μa+(μa+δa)(R0,a−1).\right. $ |
We have the following proposition:
Proposition 2. The following statements are satisfied.
● If
● When
Proof. The GAS of the disease-free equilibrium
$V_0(S_a, I_a) = \dfrac{1}{2}I^2_a. $ |
The directional derivative of
$˙V0(Sa,Ia)=[βaΦaSa−(μa+δa)Na]I2aNa,=−(μa+δa)[Ia+(R0,a−1)Sa]I2aNa.$ |
Thus,
For the GAS of the endemic equilibrium
$Q(Sa,Ia)=(Sa+Ia)−(¯Sa+¯Ia)−(¯Sa+¯Ia)ln(Sa+Ia¯Sa+¯Ia)+k(Ia−¯Ia−¯IalnIa¯Ia),=Na−¯Na−¯NalnNa¯Na+k(Ia−¯Ia−¯IalnIa¯Ia), $ |
defined in the set
$ \Lambda_a = \mu_a\overline{N}_a -\delta_a\overline{I}_a, (\mu_a+\delta_a) = \dfrac{\beta_{aa}\Phi_a\overline{S}_a}{\overline{N}_a}.$ |
With this in mind and the fact that
$\dfrac{S_a}{S_a+I_a} - \dfrac{\overline{S}_a}{\overline{S}_a+\overline{I}_a} = \dfrac{\overline{I}_a(S_a - \overline{S}_a) - \overline{S}_a(I_a-\overline{I}_a)}{(S_a+I_a)(\overline{S}_a+\overline{I}_a)}, $ |
the directional derivative
$˙Q=−μa(Sa−¯Sa)2Sa+Ia−(μa+δa+kβaaΦa¯Sa¯Sa+¯Ia)(Ia−¯Ia)2Sa+Ia,−(2μa+δa−kβaaΦa¯Ia¯Sa+¯Ia)(Ia−¯Ia)(Sa−¯Sa)Sa+Ia. $ |
Choose the constant
$2\mu_a +\delta_a - \dfrac{k\beta_{aa}\Phi_a\overline{I}_a}{\overline{S}_a+\overline{I}_a} = 0, $ |
or equivalently
$ k= \dfrac{(2\mu_a +\delta_a)\overline{S}_a+\overline{I}_a}{\beta_{aa}\Phi_a\overline{I}_a}. $ |
Thus, the directional derivative of
$\dot Q = - \dfrac{\mu_a(S_a-\overline{S}_a)^2}{S_a+I_a} - \left(\mu_a +\delta_a + \dfrac{k\beta_{aa}\Phi_a\overline{S}_a}{\overline{S}_a+\overline{I}_a}\right) \dfrac{(I_a-\overline{I}_a)^2}{S_a +I_a}, $ |
from which we can see clearly that
Sub-model (26) is considered when the bat population is at endemic state
$ \left\{dSadt=Λa−βaaΦaSaIaNa−βabSa¯IbNa−μaSa,dIadt=βaaΦaSaIaNa+βabSa¯IbNa−(μa+δa)Ia.\right. $ | (28) |
Since
Let
$ \overline{D}_b= \beta_{ab}\overline{I}_b. $ | (29) |
$ \left\{Λa−(βaaΦaˆIa+¯Db)ˆSaˆNa−μaˆSa=0,(βaaΦaˆIa+¯Db)ˆSaˆNa−(μa+δa)ˆIa=0.\right. $ | (30) |
Set
$ \widehat{\lambda}_a =\dfrac{\beta_{aa}\Phi_a \widehat{I}_a + \overline{D}_b}{\widehat{N}_a}. $ | (31) |
Then, from (30) and (31), we have
$ \widehat{S}_a = \dfrac{\Lambda_a}{\mu_a + \widehat{\lambda}_a}, \;\; \widehat{I}_a = \dfrac{\Lambda_a\widehat{\lambda}_a}{\left(\mu_a + \delta_a\right)\left(\mu_a + \widehat{\lambda}_a\right)}, \;\; \widehat{N}_a = \dfrac{\Lambda_a\left(\mu_a + \delta_a + \widehat{\lambda}_a\right)}{\left(\mu_a + \delta_a\right)\left(\mu_a + \widehat{\lambda}_a\right)}. $ | (32) |
Substituting (32) into (31) yields
$ \widehat{\lambda}_a =\dfrac{\beta_{aa}\Phi_a \Lambda_a\widehat{\lambda}_a + \overline{D}_b\left(\mu_a + \delta_a\right)\left(\mu_a + \widehat{\lambda}_a\right)}{\Lambda_a\left(\mu_a + \delta_a + \widehat{\lambda}_a\right)}. $ |
From this latter expression, we derive the quadratic equation
$ \Lambda_a \left(\widehat{\lambda}_a\right)^2 + \left[\Lambda_a\left(\mu_a + \delta_a \right)-\overline{D}_b(\mu_a+\delta_a)-\beta_{aa}\Phi_a \Lambda_a \right] \widehat{\lambda}_a - \mu_a\left(\mu_a + \delta_a \right)\overline{D}_b = 0. $ | (33) |
Denote the discriminant of Eq. (33) by
$ \Delta_a = \left[\Lambda_a\left(\mu_a + \delta_a \right)-\overline{D}_b(\mu_a+\delta_a)-\beta_{aa}\Phi_a \Lambda_a \right]^2 + 4\mu_a\Lambda_a\left(\mu_a+\delta_a\right)\overline{D}_b >0. $ | (34) |
Then, the unique positive root of Eq. (33) is
$ \widehat{\lambda}_a = \dfrac{ \left(\beta_{aa}\Phi_a - \mu_a - \delta_a\right) \Lambda_a + \overline{D}_b(\mu_a+\delta_a)+ \sqrt{\Delta_a}}{2\Lambda_a}. $ | (35) |
Thus, the components of the unique equilibrium point
$ \left\{ˆSa=2Λ2a2μaΛa+(βaaΦa−μa−δa)Λa+¯Db(μa+δa)+√Δa,ˆIa=Λa[(βaaΦa−μa−δa)Λa+¯Db(μa+δa)+√Δa](μa+δa)[2μaΛa+(βaaΦa−μa−δa)Λa+¯Db(μa+δa)+√Δa].\right. $ | (36) |
Proposition 3. The endemic equilibrium
Proof. We first establish the LAS of
$ J(\widehat {E}_a) = (−βaaΦa(ˆIa)2(ˆNa)2−¯DbˆIa(ˆNa)2−μa− βaaΦa(ˆSa)2(ˆNa)2+¯DbˆSa(ˆNa)2βaaΦa(ˆIa)2(ˆNa)2+¯DbˆIa(ˆNa)2βaaΦa(ˆSa)2(ˆNa)2−¯DbˆSa(ˆNa)2−(μa+δa)). $ |
Since
$ trace(J(ˆEa))=βaaΦa(ˆSa−ˆIa)−(δa+2μa)ˆNa−¯DbˆNa,=−[(μa+δa)(1−R0,a)+μa]ˆSa−[βaaΦa+2μa+δa]ˆIa−¯DbˆNa,<0. $ | (37) |
Furthermore, the determinant
$ det(J(ˆEa))=βaaΦa(μa+δa)(ˆIa)2+¯Db(μa+δa)ˆIa−μaβaaΦa(ˆSa)2(ˆNa)2+μa¯DbˆSa+μa(μa+δa)(ˆNa)2(ˆNa)2,=(μa+δa)[βaaΦa(ˆIa)2+μa(ˆIa)2+¯DbˆIa+2μaˆSaˆIa](ˆNa)2+(μa+δa)μaˆSa(1−R0,a)+¯Dbμaδa(ˆNa)2, $ | (38) |
which is positive whenever
Secondly, we prove the global attractiveness of
$ g(S_a, I_a) = \dfrac{1}{I_a}, $ |
defined on the connected region
$\dfrac{\partial(gX_1)}{\partial S_a} + \dfrac{\partial(gX_2)}{\partial I_a} = - \dfrac{\beta_{aa}\Phi_a}{N_a} - \dfrac{\overline{D}_b}{I^2_a} - \dfrac{\mu_a}{I_a} < 0.$ |
Hence, by Dulac's criterion, there is no periodic solution in the interior of
We conclude the series of sub-models by studying the dynamics of the human subpopulation when the other subpopulations (bats and animals) are at their different equilibrium states. The subsystem under investigation is constituted of Eqs. (19a)-(19d) given below.
$ \left\{dShdt=Λh−βhhΦhShIhNh−βhaΦaShIaNh−βhbShIbNh−μhSh,dEhdt=βhhΦhShIhNh+βhaΦaShIaNh+βhbShIbNh−(μh+ω)Eh,dIhdt=ωEh−(μh+γ)Ih,dRhdt=γ(1−f)Ih−μhRh. \right. $ | (39) |
Consider the subsystem (19a)-(19d) dealing with human subpopulation, where the animals and bats subpopulations are at disease-free equilibrium
$ \left\{dShdt=Λh−βhhΦhShIhNh−μhSh,dEhdt=βhhΦhShIhNh−(μh+ω)Eh,dIhdt=ωEh−(μh+γ)Ih,dRhdt=γ(1−f)Ih−μhRh. \right. $ | (40) |
Model (40) is well posed mathematically and biologically in the compact set
$ \Omega_h = \left\{ (S_h, E_h, I_h, R_h)\in \mathbb R^4_+ : N_h= S_h+E_h+I_h+R_h \leq \dfrac{\Lambda_h}{\mu_h}\right\}. $ | (41) |
System (40) has two equilibrium points, namely the disease-free
$P^0_h= \left(\dfrac{\Lambda_h}{\mu_h}, 0, 0, 0\right), $ |
which always exists and the endemic equilibrium point
$\mathcal{R}^0_{0h} = \frac{\beta_{hh}\Phi_h\omega}{\left(\mu_h+\omega\right)\left(\mu_h+\gamma\right)} >1. $ |
Set
$B_h = \left(\mu_h+\omega\right)\left(\mu_h+\gamma\right).$ |
Then the components of
$ ¯Sh=Λh[μh(μh+ω+γ)+γω(1−f)]μh[Bh(R00h−1)+μh(μh+ω+γ)+γω(1−f)],¯Eh=Λh(μh+γ)(R00h−1)Bh(R00h−1)+μh(μh+ω+γ)+γω(1−f),¯Ih=ωΛh(μh+γ)(R00h−1)(μh+γ)[Bh(R00h−1)+μh(μh+ω+γ)+γω(1−f)],¯Rh=γ(1−f)ωΛh(μh+γ)(R00h−1)μh(μh+γ)[Bh(R00h−1)+μh(μh+ω+γ)+γω(1−f)]. $ |
The asymptotic behavior of model (40) is completely described by
Theorem 4.2. The following statements hold true:
(1) The disease-free equilibrium point
(2) The endemic equilibrium point
Proof. The first item is established using the Lyapunov function
$L_h= L_h\left(S_h, E_h, I_h, R_h\right) = \dfrac{\omega}{B_h}E_h + \dfrac{1}{\mu_h+\gamma} I_h.$ |
The Lie derivative of
$\dot{L}_h = \left[\dfrac{\beta_{hh}\Phi_h\omega S_h}{B_hN_h}-1 \right]I_h = - \left[\left(1-\mathcal R_{0, h}\right)S_h + E_h+I_h+R_h \right]\dfrac{I_h}{N_h}.$ |
Clearly
As for the second item of Theorem 4.2, the proof of the global asymptotic stability is quiet long and challenging. We refer the interested reader to [39,61] where the proof is provided using a geometrical approach [40].
Thanks to Theorem 4.1 and combining Proposition 1, Proposition 2 and Proposition 4.2 we are now able state the first main result regarding the asymptotic behavior of the environmental-free model (19).
Theorem 4.3. For system (19), the following statements hold true:
1. If
2. If
The model under consideration in this section is
$ \left\{dShdt=Λh−βhhΦhShIhNh−¯DaShNh−μhSh,dEhdt=βhhΦhShIhNh+¯DaShNh−(μh+ω)Eh,dIhdt=ωEh−(μh+γ)Ih,dRhdt=γ(1−f)Ih−μhRh, \right. $ | (42) |
where the constant
$ \overline{D}_a = \beta_{ha}\Phi_a\overline{I}_a. $ | (43) |
This model is obviously a dynamical system on the biological feasible domain given in (41).
Due to the fact
$ \lambda^{**}_h = \dfrac{\beta_{hh}\Phi_h I^{**}_h + \overline{D}_a}{N^{**}_h}. $ | (44) |
Then
$ \left\{Λh−(λ∗∗h+μh)S∗∗h=0,λ∗∗hS∗∗h−(μh+ω)E∗∗h=0,ωE∗∗h−(μh+γ)I∗∗h=0,γ(1−f)I∗∗h−μhR∗∗h=0. \right. $ | (45) |
From (45), we have
$ \left\{S∗∗h=Λhμh+λ∗∗h,E∗∗h=Λhλ∗∗h(μh+ω)(μh+λ∗∗h),I∗∗h=ωΛhλ∗∗hBh(μh+λ∗∗h),R∗∗h=γ(1−f)ωΛhλ∗∗hμhBh(μh+λ∗∗h),N∗∗h=[μhBh(μh+λ∗∗h)+μh(μh+γ)λ∗∗h+μhωλ∗∗h+γ(1−f)ωλ∗∗h]μhBh(μh+λ∗∗h). \right. $ | (46) |
Putting the above expressions (46) in (44), yields the following quadratic equation with respect to
$ a_h \left(\lambda^{**}_h\right)^2 + b_h\lambda^{**}_h + c_h = 0, $ | (47) |
where the constant coefficients
$ \left\{ah=Λh[μhBh+μh(μh+γ)+μhω+γ(1−f)ω],bh=μ2hBhΛh−μhβhhΦhωΛa+μhω−μh(μh+γ)(μh+ω)¯Da,ch=−μ2hBh¯Da. \right. $ | (48) |
Since,
Similar arguments to those in [39,61] can be used to prove the global asymptotic stability of the unique endemic equilibrium point
Theorem 4.4. If
Replacing
$ \left\{dShdt=Λh−βhhΦhShIhNh−(ˆDa+¯Db)ShNh−μhSh,dEhdt=βhhΦhShIhNh+(ˆDa+¯Db)ShNh−(μh+ω)Eh,dIhdt=ωEh−(μh+γ)Ih,dRhdt=γ(1−f)Ih−μhRh, \right. $ | (49) |
where
$ \widehat{D}_{a} = \beta_{ha}\Phi_a\widehat{I}_{a}. $ | (50) |
The theoretical analysis of subsystem (49) is similar to that of subsystem (42). Denoting by
Theorem 4.5. If
We summarize the existence of the four equilibria of system (19) and their stability properties in the following table.
Equilibria | Conditions of existence | Stability | |
| |
GAS | |
| |
GAS | |
| |
GAS | |
| |
GAS |
We carried out a sensitivity analysis. This allows to identify the parameters that are most influential in determining population dynamics [42,43]. A Latin Hypercube Sampling (LHS) scheme [15,43] samples
Parameters | | | | | |
| | 0.2343 | 0.1922 | 0.0124 | 0.0172 |
| -0.1822 | 0.2005 | 0.1610 | | 0.0180 |
| -0.3116 | | 0.3008 | | 0.0132 |
| | | | -0.0341 | 0.0329 |
| 0.1060 | -0.1786 | -0.1134 | | -0.0148 |
| | | | | |
| -0.0143 | -0.0493 | -0.0453 | -0.0530 | 0.0202 |
| 0.0030 | -0.0099 | 0.284 | -0.0491 | -0.0250 |
| -0.0107 | 0.0630 | 0.0010 | -0.1381 | 0.0356 |
| -0.0218 | 0.0572 | 0.0200 | -0.0509 | -0.0518 |
| -0.1213 | 0.1149 | 0.0410 | -0.1530 | 0.0256 |
| -0.1299 | -0.2465 | | 0.0513 | -0.0613 |
| 0.0463 | -0.0623 | 0.1735 | 0.0108 | 0.0092 |
| 0.0239 | -0.0450 | -0.0185 | -0.325 | -0.0044 |
| 0.0143 | 0.0490 | -0.0125 | 0.0067 | 0.0154 |
| 0.043 | 0.0177 | 0.1003 | -0.0653 | -0.0434 |
| 0.0078 | -0.0041 | -0.0254 | -0.0113 | -0.0506 |
| 0.0133 | 0.0073 | 0.0845 | -0.0410 | -0.0025 |
| 0.0142 | -0.0065 | | -0.0320 | -0.0106 |
| 0.0375 | -0.0581 | 0.0141 | 0.0003 | 0.0263 |
| -0.2682 | 0.3205 | 0.1217 | 0.0220 | 0.0038 |
| -0.3700 | | 0.3747 | -0.0114 | 0.0125 |
| 0.0785 | 0.0106 | 0.0022 | -0.0824 | -0.0129 |
| -0.1816 | 0.2399 | 0.1559 | -0.0395 | -0.0448 |
| 0.0196 | 0.0757 | 0.1389 | -0.0976 | |
| -0.0242 | 0.0984 | 0.0080 | | -0.0030 |
| -0.0214 | -0.0310 | -0.0280 | -0.0071 | 0.0391 |
| -0.0145 | 0.1266 | -0.0036 | | -0.0596 |
| -0.0214 | 0.0150 | 0.0718 | 0.0737 | 0.0339 |
Parameters | | | | |
| | 0.3341 | 0.0602 | 0.0406 |
| -0.1412 | 0.2206 | 0.8767 | -0.0122 |
| -0.3108 | | | -0.0214 |
| | | 0.0180 | 0.0341 |
| 0.0936 | -0.2108 | | -0.0046 |
| | | | |
| 0.0055 | 0.0391 | -0.0337 | -0.0270 |
| -0.0913 | 0.1327 | -0.0923 | -0.0041 |
| -0.0183 | 0.0184 | 0.0608 | -0.0183 |
| -0.0483 | 0.0745 | -0.0953 | -0.0253 |
| -0.1496 | -0.2233 | 0.0116 | 0.0046 |
| 0.0124 | -0.0410 | 0.0286 | -0.0295 |
| 0.0690 | -0.0647 | -0.3869 | 0.0175 |
| -0.0221 | 0.0308 | 0.0099 | 0.0539 |
| 0.0035 | -0.0057 | 0.0042 | 0.0170 |
| -0.2865 | 0.3144 | -0.0275 | -0.0105 |
| -0.3649 | | -0.0063 | -0.0131 |
| -0.2057 | 0.3168 | 0.0372 | 0.0050 |
| -0.0686 | 0.0757 | -0.2270 | |
| -0.0719 | 0.0684 | | -0.0245 |
| 0.0063 | 0.0049 | -0.2936 | 0.0053 |
Parameters | | | | |
| | 0.2046 | 0.1034 | 0.0202 |
| -0.3295 | | 0.3423 | -0.0096 |
| | | | 0.0203 |
| | | | |
| 0.01 | 0.0066 | 0.0254 | -0.0085 |
| -0.0047 | 0.0470 | 0.0421 | -0.0097 |
| -0.0110 | 0.0116 | -0.0052 | 0.0244 |
| -0.1750 | -0.1661 | | -0.0014 |
| 0.0404 | 0.0196 | 0.1127 | -0.0412 |
| -0.0375 | -0.0105 | 0.0071 | 0.0263 |
| 0.0091 | -0.0128 | -0.0147 | 0.0408 |
| -0.0182 | 0.0316 | 0.0038 | -0.0090 |
| 0.0037 | 0.0187 | | -0.0041 |
| -0.0096 | -0.0177 | 0.0319 | -0.0294 |
| -0.2646 | 0.3093 | 0.2130 | 0.0209 |
| -0.3794 | | | 0.0162 |
| 0.0055 | 0.0171 | -0.0102 | -0.0538 |
| -0.0803 | 0.0556 | 0.0875 | |
| -0.0094 | 0.0178 | -0.0178 | 0.0804 |
Parameters | Range | Values | Units | Source |
| Variable | 100 | | N/A |
| Variable | 5 | | N/A |
| Variable | 10 | | N/A |
| 0-1 | 0.33/365 | | [57] |
| 0-1 | 0.4/365 | | Assumed |
| 0-1 | 0.5/365 | | Assumed |
| 0-1 | 0.85/30 | | Assumed [10,46] |
| 0-1 | 1/2.5 | | [50,57] |
| 1-7 | 2.5 | | [50,57] |
| 0-1 | 1/7 | | Assumed |
| 1-14 | 7 | | Assumed |
| 1-5 | 1.2 | | Assumed |
| 1-5 | 1.3 | | Assumed |
| 1/2-1/21 | 1/21 | | [22,50] |
| 1/7-1/14 | 1/14 | | [57] |
| 0-1 | 0.5/365 | | Assumed |
| 10-100 | 50 | | [8] |
| 20-200 | 100 | | Assumed |
| 50-400 | 200 | | Assumed |
| 1/81-1 | 1/61 | | [50] |
| 1-81 | 61 | | [50] |
| 0.4-0.9 | 0.70 | dimensionless | [50,52,57] |
| | | [8] | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable |
In this section, we give numerical simulations that support the theory presented in the previous sections. The simulations are produced by MatLab. While the parameters values for human-to-human transmission are mostly taken from [50,57], we have proposed almost all the parameter values regarding animal-to-human, bat-to-human, environment-to-human, environment-to-animal, environment-to-bat, animal-to-animal, animal-to-bat and bat-to-bat transmission mechanisms.
We numerically illustrate the asymptotic behavior of the full model and the sub-model without the environmental contamination. The GAS of the disease-free equilibrium
We numerically assess the impact of the contaminated environment on the severity/endemicity of EVD, as well as the effects of bats and animals on the long run and severity/endemicity of EVD.
Figure 8 and Figure 9 show the increasing behavior of the full model-related infected component with respect to the indirect effective contact rates
To illustrate the effects of bats and animals on the dynamics of EVD, Figure 9 is the simulation of the model (1) with and without bats on the one hand and with and without animals on the other hand. It can be seen that the incorporation of bats increases significantly the endemic level of EVD in the human population, while the involvement of animals does not.
The main purpose of this paper was to build and analyze a mathematical model for the transmission dynamics of EVD in a complex Ebola virus life ecology. We have then developed and analyzed both theoretically and numerically a new model by taking into account the known, the probable/suspected and the hypothetical mechanisms of transmission of EVD [26,37,51]. The proposed model captures as much as possible the essential patterns of the disease evolution as a three cycle transmission process in the following two ways:
1. It involves the interplay between the epizootic phase (during which the disease circulates periodically amongst non-human primates populations and decimates them), the enzootic phase (during which the disease always remains in fruit bats population) and the epidemic phase (during which the EVD threatens and decimates the human beings).
2. It includes the direct transmission mechanism between and within the three different types of populations which are humans, animals and fruit bats, as well as the indirect route of infection through a contaminated environment.
More precisely, we have extended and enriched the few existing SEIR-type human models for EVD with five additional compartments which model the direct transmissions within/between animal and fruit bat populations as well as the environmental indirect contamination. In this double setting of direct and indirect transmissions, our major findings from the theoretical, numerical and computational point of view read as follows:
From the theoretical perspective, our results are two-fold:
● For the full model with the environmental contamination, we have computed the basic reproduction number
● The sub-model without the environmental contamination exhibits one globally asymptotically stable disease-free equilibrium whenever the host-specific basic reproduction numbers,
From the numerical and computational point of view, the following three facts were addressed:
● In order to assess the role of a contaminated environment on the spreading of EVD, the infected human component resulting from sub-model without the environmental contamination was compared with that of the full model. Similarly, we have considered the sub model without animals on the one hand, and the sub model without bats on the other hand, and found that bats influence more the dynamics of EVD than animals. This is probably because almost all EVD outbreaks were due to consumption and manipulation of fruits bats.
● Global sensitivity analyses were performed to identify the most influential model parameters on the model variables. It shows that the effective contact rate between humans and fruit bats and the bat mortality rate were the most influential parameters on the latent and infected human individuals. This is probably because almost all EVD outbreaks were due to consumption and manipulation of fruits bats.
● Numerical simulations, apart from supporting the theoretical results and the existence of a unique global stable endemic equilibrium for the full model (when
Despite the high level of generalization and complexity of our work, it still offers many opportunities for extensions. Theses include:
(ⅰ) The incorporation of the Ebola-deceased compartments to better capture the transmission mechanisms of EVD during funerals [9].
(ⅱ) The incorporation of the transmission in health care centers in which medical staff can be infected as well [58].
(ⅲ) The incorporation of patches to account for the internationalization of EVD as it is the case in Western Africa [13,23,31].
(ⅳ) The modeling of multi-species transmission mechanism in the case where the same region is threaten by more than one Ebola virus strain.
(ⅴ) The incorporation of the human behavior. For instance, there were evidence of behavioral reaction and self-protection measures: people were scared, they panicked and left care centers, etc...Thus the need to fill the gap of lack of modeling human behavior [11,21]. This important feature calls for a modeling approach based on "Behavioral Epidemiology" developed in [41], which we are already addressing in another work which takes into account self-protection measures driven by human behavior.
(ⅵ) The modeling of some optimal control strategies such as vaccination, isolation, quarantine, treatment, early detection, environmental decontamination.
This work was initiated and mostly developed during the postdoctoral fellowship of the first author (T.B.) at the University of Pretoria in South Africa. (T.B.) and the third author (J.L.) would like to acknowledge the support of the South African Research Chairs Initiative in Mathematical Models and Methods in Bioengineering and Biosciences at the University of Pretoria. The authors are grateful to two anonymous referees whose comments helped to substantially improve this work.
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Year | Country | Species | Starting date | Source of infection |
1976 | DRC | Zaire | September | Unknown. Index case was a mission school teacher. |
1976 | Sudan | Sudan | June | Worker in a cotton factory. |
Evidence of bats at site. | ||||
1977 | DRC | Zaire | June | Unknown (retrospective). |
1979 | Sudan | Sudan | July | Worker in cotton factory. |
Evidence of bats at site. | ||||
1994 | Gabon | Zaire | December | Gold-mining camps. |
Evidence of bats at site. | ||||
1994 | Ivory Coast | Ivory Coast | November | Scientist performing autopsy on a dead wild chimpanzee. |
1995 | Liberia | Ivory Coast | December | Unknown. Refugee from civil war. |
1995 | DRC | Zaire | January | Index case worked in a forest adjoining the city. |
1996 | Gabon | Zaire | January | People involved in the butchering of a dead chimpanzee. |
1996-1997 | Gabon | Zaire | July | Index case was a hunter living in a forest camp. |
2000-2001 | Uganda | Sudan | September | Unknown. |
2001-2002 | Gabon | Zaire | October | Contact with dead or butchered apes or other wildlife. |
2001-2002 | DRC | Zaire | October | Contact with dead or butchered apes or other wildlife. |
2002-2003 | DRC | Zaire | December | Contact with dead or butchered apes or other wildlife. |
2003 | DRC | Zaire | November | Contact with dead or butchered apes or other wildlife. |
2004 | Sudan | Sudan | May | Unknown. |
2005 | DRC | Zaire | April | unknown. |
2007 | DRC | Zaire | December | Contact with dead or butchered apes or other wildlife. |
2007 | Uganda | Bundibugyo | December | Unknown. |
2008 | DRC | Zaire | December | Index case was a village chief and a hunter. |
2012 | Uganda | Bundibugyo | June | Index case was a secondary school teacher in Ibanda district. |
2012 | DRC | Zaire | June | Index case was a hunter living in a forest camp. |
2013-2015 | Guinea | Zaire | December | Contact with bats or fruits contaminated by bat droppings. |
2014-2015 | Liberia | Zaire | April | Index case was transported from Guinea. |
2014-2015 | Sierra Leone | Zaire | April | A traditional healer, treating Ebola patients from Guinea. |
2014 | DRC | Zaire | August | Pregnant women who butchered a bush animal. |
Symbols | Biological interpretations |
|
Recruitment rate of susceptible humans, animals and bats, respectively. |
|
Natural mortality rate of humans, animals and bats, respectively. |
|
Virulence of Ebola virus in the corpse of the dead humans. |
|
Mean duration of time that elapse after death before a human cadaver is completely buried. |
|
Modification parameter of infectiousness due to dead human individuals. |
|
Mean duration of time that elapse after death before an animal's cadaver is completely cleared out. |
|
Modification parameter of infectiousness due to dead animals individuals. |
|
Virulence of Ebola virus in the corpse of dead animals. |
|
Incubation rate of human individuals. |
|
Removal rate from infectious compartment due to either to disease induced death, or by recovery. |
|
Death rate of infected animals. |
|
Shedding rates of Ebola virus in the environment by humans, animals and bats, respectively. |
|
Mean duration of time that elapse before the complete clearance of Ebola virus in humans. |
|
Modification parameter of contact rate of recovered humans (sexual activity of recovered). |
in the semen/breast milk of a recovered man/woman. | |
|
Proortion of removed human individuals who die due EVD (i.e. case fatality rate). |
|
Virus 50 % infectious dose, sufficient to cause EVD. |
|
Contact rate between susceptible humans and infected humans. |
|
Contact rate between susceptible humans and bats. |
|
Contact rate between susceptible humans and Ebola viruses. |
|
Contact rate between susceptible humans and infected animals. |
|
Contact rate between susceptible bats and infectious bats. |
|
Contact rate between susceptible animals and infectious bats. |
|
Contact rate between susceptible bats and and Ebola viruses. |
|
Contact rate between susceptible and infected animals. |
|
Contact rate between susceptible animals and Ebola viruses. |
Equilibria | Conditions of existence | Stability | |
| |
GAS | |
| |
GAS | |
| |
GAS | |
| |
GAS |
Parameters | | | | | |
| | 0.2343 | 0.1922 | 0.0124 | 0.0172 |
| -0.1822 | 0.2005 | 0.1610 | | 0.0180 |
| -0.3116 | | 0.3008 | | 0.0132 |
| | | | -0.0341 | 0.0329 |
| 0.1060 | -0.1786 | -0.1134 | | -0.0148 |
| | | | | |
| -0.0143 | -0.0493 | -0.0453 | -0.0530 | 0.0202 |
| 0.0030 | -0.0099 | 0.284 | -0.0491 | -0.0250 |
| -0.0107 | 0.0630 | 0.0010 | -0.1381 | 0.0356 |
| -0.0218 | 0.0572 | 0.0200 | -0.0509 | -0.0518 |
| -0.1213 | 0.1149 | 0.0410 | -0.1530 | 0.0256 |
| -0.1299 | -0.2465 | | 0.0513 | -0.0613 |
| 0.0463 | -0.0623 | 0.1735 | 0.0108 | 0.0092 |
| 0.0239 | -0.0450 | -0.0185 | -0.325 | -0.0044 |
| 0.0143 | 0.0490 | -0.0125 | 0.0067 | 0.0154 |
| 0.043 | 0.0177 | 0.1003 | -0.0653 | -0.0434 |
| 0.0078 | -0.0041 | -0.0254 | -0.0113 | -0.0506 |
| 0.0133 | 0.0073 | 0.0845 | -0.0410 | -0.0025 |
| 0.0142 | -0.0065 | | -0.0320 | -0.0106 |
| 0.0375 | -0.0581 | 0.0141 | 0.0003 | 0.0263 |
| -0.2682 | 0.3205 | 0.1217 | 0.0220 | 0.0038 |
| -0.3700 | | 0.3747 | -0.0114 | 0.0125 |
| 0.0785 | 0.0106 | 0.0022 | -0.0824 | -0.0129 |
| -0.1816 | 0.2399 | 0.1559 | -0.0395 | -0.0448 |
| 0.0196 | 0.0757 | 0.1389 | -0.0976 | |
| -0.0242 | 0.0984 | 0.0080 | | -0.0030 |
| -0.0214 | -0.0310 | -0.0280 | -0.0071 | 0.0391 |
| -0.0145 | 0.1266 | -0.0036 | | -0.0596 |
| -0.0214 | 0.0150 | 0.0718 | 0.0737 | 0.0339 |
Parameters | | | | |
| | 0.3341 | 0.0602 | 0.0406 |
| -0.1412 | 0.2206 | 0.8767 | -0.0122 |
| -0.3108 | | | -0.0214 |
| | | 0.0180 | 0.0341 |
| 0.0936 | -0.2108 | | -0.0046 |
| | | | |
| 0.0055 | 0.0391 | -0.0337 | -0.0270 |
| -0.0913 | 0.1327 | -0.0923 | -0.0041 |
| -0.0183 | 0.0184 | 0.0608 | -0.0183 |
| -0.0483 | 0.0745 | -0.0953 | -0.0253 |
| -0.1496 | -0.2233 | 0.0116 | 0.0046 |
| 0.0124 | -0.0410 | 0.0286 | -0.0295 |
| 0.0690 | -0.0647 | -0.3869 | 0.0175 |
| -0.0221 | 0.0308 | 0.0099 | 0.0539 |
| 0.0035 | -0.0057 | 0.0042 | 0.0170 |
| -0.2865 | 0.3144 | -0.0275 | -0.0105 |
| -0.3649 | | -0.0063 | -0.0131 |
| -0.2057 | 0.3168 | 0.0372 | 0.0050 |
| -0.0686 | 0.0757 | -0.2270 | |
| -0.0719 | 0.0684 | | -0.0245 |
| 0.0063 | 0.0049 | -0.2936 | 0.0053 |
Parameters | | | | |
| | 0.2046 | 0.1034 | 0.0202 |
| -0.3295 | | 0.3423 | -0.0096 |
| | | | 0.0203 |
| | | | |
| 0.01 | 0.0066 | 0.0254 | -0.0085 |
| -0.0047 | 0.0470 | 0.0421 | -0.0097 |
| -0.0110 | 0.0116 | -0.0052 | 0.0244 |
| -0.1750 | -0.1661 | | -0.0014 |
| 0.0404 | 0.0196 | 0.1127 | -0.0412 |
| -0.0375 | -0.0105 | 0.0071 | 0.0263 |
| 0.0091 | -0.0128 | -0.0147 | 0.0408 |
| -0.0182 | 0.0316 | 0.0038 | -0.0090 |
| 0.0037 | 0.0187 | | -0.0041 |
| -0.0096 | -0.0177 | 0.0319 | -0.0294 |
| -0.2646 | 0.3093 | 0.2130 | 0.0209 |
| -0.3794 | | | 0.0162 |
| 0.0055 | 0.0171 | -0.0102 | -0.0538 |
| -0.0803 | 0.0556 | 0.0875 | |
| -0.0094 | 0.0178 | -0.0178 | 0.0804 |
Parameters | Range | Values | Units | Source |
| Variable | 100 | | N/A |
| Variable | 5 | | N/A |
| Variable | 10 | | N/A |
| 0-1 | 0.33/365 | | [57] |
| 0-1 | 0.4/365 | | Assumed |
| 0-1 | 0.5/365 | | Assumed |
| 0-1 | 0.85/30 | | Assumed [10,46] |
| 0-1 | 1/2.5 | | [50,57] |
| 1-7 | 2.5 | | [50,57] |
| 0-1 | 1/7 | | Assumed |
| 1-14 | 7 | | Assumed |
| 1-5 | 1.2 | | Assumed |
| 1-5 | 1.3 | | Assumed |
| 1/2-1/21 | 1/21 | | [22,50] |
| 1/7-1/14 | 1/14 | | [57] |
| 0-1 | 0.5/365 | | Assumed |
| 10-100 | 50 | | [8] |
| 20-200 | 100 | | Assumed |
| 50-400 | 200 | | Assumed |
| 1/81-1 | 1/61 | | [50] |
| 1-81 | 61 | | [50] |
| 0.4-0.9 | 0.70 | dimensionless | [50,52,57] |
| | | [8] | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable |
Year | Country | Species | Starting date | Source of infection |
1976 | DRC | Zaire | September | Unknown. Index case was a mission school teacher. |
1976 | Sudan | Sudan | June | Worker in a cotton factory. |
Evidence of bats at site. | ||||
1977 | DRC | Zaire | June | Unknown (retrospective). |
1979 | Sudan | Sudan | July | Worker in cotton factory. |
Evidence of bats at site. | ||||
1994 | Gabon | Zaire | December | Gold-mining camps. |
Evidence of bats at site. | ||||
1994 | Ivory Coast | Ivory Coast | November | Scientist performing autopsy on a dead wild chimpanzee. |
1995 | Liberia | Ivory Coast | December | Unknown. Refugee from civil war. |
1995 | DRC | Zaire | January | Index case worked in a forest adjoining the city. |
1996 | Gabon | Zaire | January | People involved in the butchering of a dead chimpanzee. |
1996-1997 | Gabon | Zaire | July | Index case was a hunter living in a forest camp. |
2000-2001 | Uganda | Sudan | September | Unknown. |
2001-2002 | Gabon | Zaire | October | Contact with dead or butchered apes or other wildlife. |
2001-2002 | DRC | Zaire | October | Contact with dead or butchered apes or other wildlife. |
2002-2003 | DRC | Zaire | December | Contact with dead or butchered apes or other wildlife. |
2003 | DRC | Zaire | November | Contact with dead or butchered apes or other wildlife. |
2004 | Sudan | Sudan | May | Unknown. |
2005 | DRC | Zaire | April | unknown. |
2007 | DRC | Zaire | December | Contact with dead or butchered apes or other wildlife. |
2007 | Uganda | Bundibugyo | December | Unknown. |
2008 | DRC | Zaire | December | Index case was a village chief and a hunter. |
2012 | Uganda | Bundibugyo | June | Index case was a secondary school teacher in Ibanda district. |
2012 | DRC | Zaire | June | Index case was a hunter living in a forest camp. |
2013-2015 | Guinea | Zaire | December | Contact with bats or fruits contaminated by bat droppings. |
2014-2015 | Liberia | Zaire | April | Index case was transported from Guinea. |
2014-2015 | Sierra Leone | Zaire | April | A traditional healer, treating Ebola patients from Guinea. |
2014 | DRC | Zaire | August | Pregnant women who butchered a bush animal. |
Symbols | Biological interpretations |
|
Recruitment rate of susceptible humans, animals and bats, respectively. |
|
Natural mortality rate of humans, animals and bats, respectively. |
|
Virulence of Ebola virus in the corpse of the dead humans. |
|
Mean duration of time that elapse after death before a human cadaver is completely buried. |
|
Modification parameter of infectiousness due to dead human individuals. |
|
Mean duration of time that elapse after death before an animal's cadaver is completely cleared out. |
|
Modification parameter of infectiousness due to dead animals individuals. |
|
Virulence of Ebola virus in the corpse of dead animals. |
|
Incubation rate of human individuals. |
|
Removal rate from infectious compartment due to either to disease induced death, or by recovery. |
|
Death rate of infected animals. |
|
Shedding rates of Ebola virus in the environment by humans, animals and bats, respectively. |
|
Mean duration of time that elapse before the complete clearance of Ebola virus in humans. |
|
Modification parameter of contact rate of recovered humans (sexual activity of recovered). |
in the semen/breast milk of a recovered man/woman. | |
|
Proortion of removed human individuals who die due EVD (i.e. case fatality rate). |
|
Virus 50 % infectious dose, sufficient to cause EVD. |
|
Contact rate between susceptible humans and infected humans. |
|
Contact rate between susceptible humans and bats. |
|
Contact rate between susceptible humans and Ebola viruses. |
|
Contact rate between susceptible humans and infected animals. |
|
Contact rate between susceptible bats and infectious bats. |
|
Contact rate between susceptible animals and infectious bats. |
|
Contact rate between susceptible bats and and Ebola viruses. |
|
Contact rate between susceptible and infected animals. |
|
Contact rate between susceptible animals and Ebola viruses. |
Equilibria | Conditions of existence | Stability | |
| |
GAS | |
| |
GAS | |
| |
GAS | |
| |
GAS |
Parameters | | | | | |
| | 0.2343 | 0.1922 | 0.0124 | 0.0172 |
| -0.1822 | 0.2005 | 0.1610 | | 0.0180 |
| -0.3116 | | 0.3008 | | 0.0132 |
| | | | -0.0341 | 0.0329 |
| 0.1060 | -0.1786 | -0.1134 | | -0.0148 |
| | | | | |
| -0.0143 | -0.0493 | -0.0453 | -0.0530 | 0.0202 |
| 0.0030 | -0.0099 | 0.284 | -0.0491 | -0.0250 |
| -0.0107 | 0.0630 | 0.0010 | -0.1381 | 0.0356 |
| -0.0218 | 0.0572 | 0.0200 | -0.0509 | -0.0518 |
| -0.1213 | 0.1149 | 0.0410 | -0.1530 | 0.0256 |
| -0.1299 | -0.2465 | | 0.0513 | -0.0613 |
| 0.0463 | -0.0623 | 0.1735 | 0.0108 | 0.0092 |
| 0.0239 | -0.0450 | -0.0185 | -0.325 | -0.0044 |
| 0.0143 | 0.0490 | -0.0125 | 0.0067 | 0.0154 |
| 0.043 | 0.0177 | 0.1003 | -0.0653 | -0.0434 |
| 0.0078 | -0.0041 | -0.0254 | -0.0113 | -0.0506 |
| 0.0133 | 0.0073 | 0.0845 | -0.0410 | -0.0025 |
| 0.0142 | -0.0065 | | -0.0320 | -0.0106 |
| 0.0375 | -0.0581 | 0.0141 | 0.0003 | 0.0263 |
| -0.2682 | 0.3205 | 0.1217 | 0.0220 | 0.0038 |
| -0.3700 | | 0.3747 | -0.0114 | 0.0125 |
| 0.0785 | 0.0106 | 0.0022 | -0.0824 | -0.0129 |
| -0.1816 | 0.2399 | 0.1559 | -0.0395 | -0.0448 |
| 0.0196 | 0.0757 | 0.1389 | -0.0976 | |
| -0.0242 | 0.0984 | 0.0080 | | -0.0030 |
| -0.0214 | -0.0310 | -0.0280 | -0.0071 | 0.0391 |
| -0.0145 | 0.1266 | -0.0036 | | -0.0596 |
| -0.0214 | 0.0150 | 0.0718 | 0.0737 | 0.0339 |
Parameters | | | | |
| | 0.3341 | 0.0602 | 0.0406 |
| -0.1412 | 0.2206 | 0.8767 | -0.0122 |
| -0.3108 | | | -0.0214 |
| | | 0.0180 | 0.0341 |
| 0.0936 | -0.2108 | | -0.0046 |
| | | | |
| 0.0055 | 0.0391 | -0.0337 | -0.0270 |
| -0.0913 | 0.1327 | -0.0923 | -0.0041 |
| -0.0183 | 0.0184 | 0.0608 | -0.0183 |
| -0.0483 | 0.0745 | -0.0953 | -0.0253 |
| -0.1496 | -0.2233 | 0.0116 | 0.0046 |
| 0.0124 | -0.0410 | 0.0286 | -0.0295 |
| 0.0690 | -0.0647 | -0.3869 | 0.0175 |
| -0.0221 | 0.0308 | 0.0099 | 0.0539 |
| 0.0035 | -0.0057 | 0.0042 | 0.0170 |
| -0.2865 | 0.3144 | -0.0275 | -0.0105 |
| -0.3649 | | -0.0063 | -0.0131 |
| -0.2057 | 0.3168 | 0.0372 | 0.0050 |
| -0.0686 | 0.0757 | -0.2270 | |
| -0.0719 | 0.0684 | | -0.0245 |
| 0.0063 | 0.0049 | -0.2936 | 0.0053 |
Parameters | | | | |
| | 0.2046 | 0.1034 | 0.0202 |
| -0.3295 | | 0.3423 | -0.0096 |
| | | | 0.0203 |
| | | | |
| 0.01 | 0.0066 | 0.0254 | -0.0085 |
| -0.0047 | 0.0470 | 0.0421 | -0.0097 |
| -0.0110 | 0.0116 | -0.0052 | 0.0244 |
| -0.1750 | -0.1661 | | -0.0014 |
| 0.0404 | 0.0196 | 0.1127 | -0.0412 |
| -0.0375 | -0.0105 | 0.0071 | 0.0263 |
| 0.0091 | -0.0128 | -0.0147 | 0.0408 |
| -0.0182 | 0.0316 | 0.0038 | -0.0090 |
| 0.0037 | 0.0187 | | -0.0041 |
| -0.0096 | -0.0177 | 0.0319 | -0.0294 |
| -0.2646 | 0.3093 | 0.2130 | 0.0209 |
| -0.3794 | | | 0.0162 |
| 0.0055 | 0.0171 | -0.0102 | -0.0538 |
| -0.0803 | 0.0556 | 0.0875 | |
| -0.0094 | 0.0178 | -0.0178 | 0.0804 |
Parameters | Range | Values | Units | Source |
| Variable | 100 | | N/A |
| Variable | 5 | | N/A |
| Variable | 10 | | N/A |
| 0-1 | 0.33/365 | | [57] |
| 0-1 | 0.4/365 | | Assumed |
| 0-1 | 0.5/365 | | Assumed |
| 0-1 | 0.85/30 | | Assumed [10,46] |
| 0-1 | 1/2.5 | | [50,57] |
| 1-7 | 2.5 | | [50,57] |
| 0-1 | 1/7 | | Assumed |
| 1-14 | 7 | | Assumed |
| 1-5 | 1.2 | | Assumed |
| 1-5 | 1.3 | | Assumed |
| 1/2-1/21 | 1/21 | | [22,50] |
| 1/7-1/14 | 1/14 | | [57] |
| 0-1 | 0.5/365 | | Assumed |
| 10-100 | 50 | | [8] |
| 20-200 | 100 | | Assumed |
| 50-400 | 200 | | Assumed |
| 1/81-1 | 1/61 | | [50] |
| 1-81 | 61 | | [50] |
| 0.4-0.9 | 0.70 | dimensionless | [50,52,57] |
| | | [8] | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable | |
| 0-1 | | Variable |