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ABSTRACT
This paper introduces a time-since-recovery structured, multi-strain, multi-population model of avian influenza. Influenza A viruses infect many species of wild and domestic birds and are classified into two groups based on their ability to cause disease: low pathogenic avian influenza (LPAI) and high pathogenic avian influenza (HPAI). Prior infection with LPAI provides partial immunity towards HPAI. The model introduced in this paper structures LPAI-recovered birds (wild and domestic) with time-since-recovery and includes cross-immunity towards HPAI that can fade with time. The model has a unique disease-free equilibrium (DFE), unique LPAI-only and HPAI-only equilibria and at least one coexistence equilibrium. We compute the reproduction numbers of LPAI () and HPAI (
) and show that the DFE is locally asymptotically stable when
and
. A unique LPAI-only (HPAI-only) equilibrium exists when
(
) and it is locally asymptotically stable if HPAI (LPAI) cannot invade the equilibrium, that is, if the invasion number
(
). We show using numerical simulations that the ODE version of the model, which is obtained by discarding the time-since-recovery structures (making cross-immunity constant), can exhibit oscillations, and also that the pathogens LPAI and HPAI can coexist with sustained oscillations in both populations. Through simulations, we show that even if both populations (wild and domestic) are sinks when alone, LPAI and HPAI can persist in both populations combined. Thus, reducing the reproduction numbers of LPAI and HPAI in each population to below unity is not enough to eradicate the disease. The pathogens can continue to coexist in both populations unless transmission between the populations is reduced.
1. Introduction
Infectious disease dynamics often occur within the context of complex ecological communities [Citation9]. Moreover, many important host–pathogen systems consist of multiple pathogen strains, circulating among multiple species of hosts [7]. Understanding how multi-species transmission affects the persistence of a given pathogen strain can help inform prediction and management of infectious disease outbreaks, and understanding how such transmission among hosts modulates the coexistence of pathogen strains and thus the maintenance of genetic variation within pathogens is essential for gauging how pathogens are likely to evolve. This community dimension of epidemiology is widely recognized as being a significant frontier in quantitative epidemiology and the public health sciences [Citation10].
These issues arise with particular urgency in the case of the avian influenza viruses (AIVs), which present a global economic problem in the poultry industry costing annually hundreds of millions of dollars [Citation16] and pose a serious public health risk due to the threat of emergence of a novel pathogen strain circulating among human hosts, with potentially devastating consequences [Citation24]. Influenza A viruses can infect many species of warm-blooded vertebrates [Citation26], but the great majority of viral strains appear to be found in wild waterbirds, such as shorebirds and gulls (Charadriiformes) and ducks and geese (Anseriformes) [Citation12]. These species can come into contact with domestic poultry, which can pose a direct threat to the poultry industry, and also provide a conduit for potential transmission to humans.
Mathematical models can provide essential tools for understanding many aspects of infectious disease dynamics [Citation10], and become particularly important when grappling with the complexities of multi-pathogen, multi-host systems, for instance when hosts themselves may mount strain-specific immune responses to infection. A realistic model of avian influenza (AI) would be highly complex, since it would have to account for transmission within and among multiple potential species of wild hosts, many of which are migratory [Citation21] and occupy seasonally forced environments [Citation24]. As a way station towards such a realistic model, here we consider a system in which there are two host populations, which we call domestic and wild bird populations, each of which has relatively simple intrinsic dynamics. These two host populations are in turn infected by two strains of AI A, one of which is a strain of low pathogenic avian influenza (LPAI), and the other a strain of high pathogenic avian influenza (HPAI). HPAI viruses are defined by the fact that they cause at least 75% mortality in 4–8 week chickens, infected intravenously [Citation20]. HPAI strains are of influenza A subtypes H5 and H7 (e.g. H5N1, H7N9).
The basic dynamics of each host consists of a steady flow of fresh susceptibles into each host population, and a constant rate of intrinsic mortality. In the absence of the virus, the hosts have very stable dynamics. (This assumption would need to be relaxed when considering the detailed dynamics of natural populations, which fluctuate seasonally and among years.) Transmission of the virus occurs in a density-dependent fashion, both within and between these two populations. Hosts can recover from infection with LPAI, and when they do recover, are immune for life from further infection by this viral strain. However, LPAI-recovered birds can be infected by HPAI. Consistent with empirical evidence, there is a degree of cross-protection in the immune response, so infection by LPAI can protect against HPAI. However, this cross-immunity fades with time, and incorporating the dynamics of such time-dependent fade-out in immune protection is one of the mathematical complexities of our model. By contrast, infection with HPAI is assumed to always lead to death (possibly by culling) in domestic birds; in wild birds, HPAI leads to death or recovery with permanent immunity to both strains.
Our focus will be on the implications of partial cross-immunity, but to put our results into context, it is useful to consider what might be expected when cross-immunity is complete. If cross-immunity is complete, then LPAI and HPAI simply compete for susceptible hosts. If there is only one population, within which each strain could persist alone, whichever strain can persist at the lowest level of susceptibles will eliminate the other strain. With two populations, there are two resources (the susceptibles in the two populations), so there are other possibilities. One is that the two strains coexist, for example if LPAI is better at exploiting wild susceptibles and HPAI is better at exploiting domestic susceptibles. Another possibility is that each strain can exclude the other, in which case the first strain to arrive persists and the second strain cannot invade (alternative equilibria). If cross-immunity is not complete, HPAI can infect at least some LPAI-recovered birds, and so it has an additional resource. Therefore, coexistence is possible in a single population if LPAI is better at exploiting susceptibles; with complete cross-immunity, LPAI would eliminate HPAI, but with partial cross-immunity, it is sometimes possible for HPAI to invade and persist by infecting LPAI-recovered birds. With two populations, of course, there is additional scope for coexistence. The analyses and simulations presented below help illuminate the conditions that permit such coexistence.
We first present the basic model (for a flow chart of the model, see Figure ). Then, we characterize the conditions for each viral strain to be able to increase when rare and alone. We derive expressions for the basic reproduction number for each strain, which are functions of the joint densities of the domestic and wild bird populations. Next, we consider the conditions for the increase of each strain when rare, when the other strain is present, and aim at characterizing conditions for the coexistence of the two strains. Such coexistence is not guaranteed. The two viral strains can be viewed as interacting in two distinct ways. Firstly, they compete exploitatively for healthy hosts. Given that there are two host populations, as noted above, there is the potential for a degree of niche partitioning that could facilitate viral strain coexistence [Citation9]. Secondly, the loss of partial immunity means there is a partial, time-lagged facilitation of the dynamics of HPAI, emerging from hosts who get infected with LPAI, but recover. This means that even if all hosts have been infected by LPAI (so no fully susceptible hosts are available at all), some hosts can become available for infection by HPAI.
Figure 1. Flow chart of model (Equation1(1)
(1) ).
![Figure 1. Flow chart of model (Equation1(1) dSwdt=Λw−λLwSw−λHwSw−μwSw,dILwdt=λLwSw−(μw+αLw)ILw,∂rLw∂t+∂rLw∂τ=−qw(τ)λHwrLw−μwrLw,rLw(0,t)=αLwILw,dIHwdt=λHwSw+λHw∫0∞qw(τ)rLw(τ,t)dτ−(μw+αHw+νHw)IHw,dRHwdt=αHwIHw−μwRHw,dSddt=Λd−λLdSd−λHdSd−μdSd,dILddt=λLdSd−(μd+αd)ILd,∂rd∂t+∂rd∂τ=−qd(τ)λHdrd−μdrd,rd(0,t)=αdILd,dIHddt=λHdSd+λHd∫0∞qd(τ)rd(τ,t)dτ−(μd+νHd)IHd.(1) ).](/cms/asset/36124092-d6d0-4d19-b8e0-0428761dc526/tjbd_a_1111449_f0001_c.jpg)
This replenishment of hosts for HPAI involves a lag, relative to LPAI infection. We will use numerical simulations to demonstrate that this permits the entire system to persist, but at times with sustained, large-scale oscillations in infection by each viral strain. Such oscillations can emerge even if each viral strain on its own tends towards a stable equilibrium when it alone is infecting the two host populations.
2. The model
We consider a time-since-recovery structured model to study the dynamics of LPAI and HPAI (indicated by L and H subscripts or superscripts, respectively) in wild and domestic bird populations (indicated by w or 1 subscripts for wild birds and d or 2 subscripts for domestic birds). The wild bird population is divided into nonintersecting classes of susceptible ( ), infected with HPAI (
), infected with LPAI (
), recovered from LPAI (
), and recovered from HPAI (
). Similarly, the domestic bird population is divided into susceptible (
), infected with HPAI (
), infected with LPAI (
) and recovered from LPAI (
) classes. Since the detection of even one HPAI-infected domestic bird results in culling the entire farm and the death of the infected bird, we do not include an HPAI-recovered class for the domestic bird population. The LPAI-recovered classes
,
denote the density of (per unit τ) recovered birds at time t with time-since-recovery equal to τ.
The susceptible bird populations are generated by the recruitment/birth rates ( and
) and reduced by the natural death rates (
and
) and by infection with HPAI or LPAI. The new infections with LPAI and HPAI, respectively, per unit time per susceptible host are modelled by
and
in wild birds. The forces of infection for LPAI and HPAI, respectively, in the wild bird population are given by
Similarly, the forces of infection for LPAI and HPAI, respectively, in the domestic bird population are given by
The aggregate β parameters can be interpreted as the product of rate of contacts between a susceptible (wild or domestic) bird and an infected (LPAI or HPAI) bird and the probability that the contact resulted in transmission. For instance, is the HPAI transmission rate to wild birds from domestic birds; similarly,
is the LPAI transmission rate to domestic birds from wild birds (per susceptible bird per infected bird). Thus, the rate of change of the population of susceptible wild and domestic bird populations is given by
The infected wild birds recover from LPAI infection at a rate
and the domestic birds recover at a rate
. LPAI causes mild infection in domestic and wild birds (http://www.cdc.gov/flu/avianflu/avian-in-birds.htm), hence we neglect the LPAI-induced death rate. The LPAI-infected wild and domestic bird populations increase by the new incidences
and
, respectively. Thus, the wild and domestic bird populations infected with LPAI satisfy the following equations:
The HPAI-infected wild and domestic bird populations increase by the new incidences
and
, respectively. Wild birds infected with HPAI can recover at a rate
; domestic birds do not recover from HPAI. Studies show that an earlier infection with LPAI provides temporary immunity towards HPAI and this immunity fades with time-since-recovery from LPAI [Citation8, Citation18]. As τ is the time elapsed since the recovery from the last LPAI infection, the additional new HPAI infections per unit time from wild birds that have recovered from LPAI are given by the following term:
where
is the susceptibility to HPAI of a wild bird that recovered from LPAI τ time units ago relative to that of a naive wild bird. Similarly, the new HPAI infections per unit time of the domestic birds recovered from LPAI infections are given by the following term:
where
is the relative susceptibility to HPAI of an LPAI-recovered domestic bird. Thus, the wild and domestic bird populations infected with HPAI satisfy the following equations:
where
and
are disease death rates induced by HPAI in wild and domestic birds, respectively. We combine these differential equations with those for LPAI-recovered classes,
and
, which have relative susceptibilities to HPAI of
and
, respectively, where
for every
. Thus, the differential equations modelling the recovered classes are
We note that in the above equations, we have assumed mass-action incidence. Since the contacts in influenza (avian or human) scale with the total population size, most influenza models are built with mass-action incidence [Citation1]. With the above notation, we have the following time-since-recovery structured, multi-strain, multi-population model:
(1)
(1)
A schematic flow diagram of model (Equation1(1)
(1) ) is given in Figure , and the associated model variables and parameters are defined in Tables and , respectively.
Table 1. Definition of the variables of model (Equation1
(1)
(1) ).
Table 2. Definition of the parameters of model (Equation1
(1)
(1) ).
3. LPAI–HPAI dynamics in wild and domestic bird populations
We first examine the existence and stability of equilibria of system (Equation1(1)
(1) ). Model (Equation1
(1)
(1) ) has four equilibria: the disease-free equilibrium (DFE); two boundary equilibria, LPAI-only and HPAI-only; and the coexistence equilibrium.
3.1. Disease-free equilibrium
System (Equation1(1)
(1) ) has a DFE
given by
where
and
The LPAI and HPAI basic reproduction numbers for the wild bird population are denoted by and
, respectively, and are given by
The epidemiological meaning of basic reproduction number (
) is the number of secondary cases produced by one LPAI (HPAI)-infected wild bird during its infectious period in an entirely susceptible population of wild birds. Similarly, the basic reproduction numbers for LPAI and HPAI in the domestic bird population are denoted by
and
respectively, and are given by
We also define the reproduction numbers between populations. In particular, the LPAI and HPAI reproduction numbers of domestic birds in the wild bird population are denoted by
and
respectively, and are given by
The reproduction number
(
) gives the number of secondary cases one LPAI (HPAI)-infected domestic bird will produce during its lifetime as infectious in an entirely susceptible wild bird population. Similarly, we denote the LPAI and HPAI reproduction number of wild birds in the domestic bird population as
and
respectively, which are given by
The reproduction number
(
) gives the number of secondary cases one LPAI (HPAI)-infected wild bird will produce during its lifetime as infectious in an entirely susceptible domestic bird population.
We call the reproduction numbers population-specific reproduction numbers and the reproduction numbers
cross-population reproduction numbers.
We denote the basic reproduction number of LPAI for the full system (Equation1(1)
(1) ) as
which is given by
Similarly, the basic reproduction number of HPAI for the full system (Equation1
(1)
(1) ) is given by
These basic reproduction numbers
,
are threshold values which determine whether LPAI or HPAI can invade the DFE. The basic reproduction number
of the full system (Equation1
(1)
(1) ) is the maximum of the LPAI and HPAI reproduction numbers: that is,
Theorem 3.1.
If and
, then the DFE,
is locally asymptotically stable.
Proof.
Let denote the perturbations around the DFE; then, we obtain the following linearized system:
(2)
(2)
Suppose that the perturbations and
have exponential forms such as
and
After dropping the bars, we obtain the following first-order ODEs:
Solving these differential equations, we obtain
The infected compartments
of the linearized system (Equation2
(2)
(2) ) are decoupled from the remaining equations. Using the next generation matrix approach, the linearized system for the infected compartment
can be rewritten as
where
The next generation matrix is a matrix of reproduction numbers:
The LPAI basic reproduction number
is the principal eigenvalue of the matrix
:
Similarly, the HPAI reproduction number
is the principal eigenvalue of the matrix
:
The reproduction number is given by the principal eigenvalue of the next generation matrix K. Thus, the basic reproduction number of the full system (Equation1
(1)
(1) ) is
Note that if
, then all eigenvalues of the subsystem involving infected compartments
have negative real parts [Citation6] (Theorem 2, p. 33). For values of λ different from the eigenvalues of the subsystem, we have
which leads to
. The remaining eigenvalues of the full system are
,
and
Hence, all the eigenvalues are negative or have negative real parts. Thus, the DFE is locally asymptotically stable when
. If
then the
subsystem has an eigenvalue with a positive real part, thus the DFE is unstable.
Furthermore, we can show the global stability of the DFE.
Theorem 3.2.
Assume . Then, the DFE is globally stable.
Proof.
Integrating the PDEs and adding all equations for wild birds in system (Equation1(1)
(1) ), we have the following inequality for the total population size
of wild birds:
Hence,
. Similarly, we have for the total domestic bird population
the inequality
. That means that the set
is invariant. For initial conditions in the set Γ, we have
(3)
(3) where we recall that
and
. We note also that since
and
, the integral is no larger than the total population size of recovered individuals, and the sum of the susceptible and recovered individuals is no larger than
and
, respectively. The right-hand side of the above system is linear. Furthermore, if
, that implies [Citation6] that the matrix of the right-hand side above has only eigenvalues with negative real parts. Therefore,
(4)
(4) Thus, the DFE is globally stable. This completes the proof.
The global stability of the DFE means that the model does not exhibit backward bifurcation.
3.2. LPAI-only and HPAI-only equilibria
System (Equation1(1)
(1) ) has two boundary equilibria: the LPAI-only equilibrium denoted by
and the HPAI-only equilibrium denoted by
.
The invasion number of HPAI when the system is at the LPAI-only equilibrium is and it is given by
(5)
(5) where
(6)
(6)
Similarly, the invasion number of LPAI when the system is at the HPAI-only equilibrium is and
(7)
(7) where
(8)
(8) As with the reproduction numbers, the invasion reproduction numbers are also obtained through the next generation approach [Citation6], where the next generation operator of HPAI invading the equilibrium of LPAI is given by
Correspondingly, the next generation operator of LPAI invading the equilibrium of HPAI is given by
We call the main diagonal entries of the next generation matrices the population-specific invasion numbers, and denote them by
, where
We call the off diagonal entries the cross-population invasion numbers, and denote them by
where
We denote the forces of infection of LPAI when wild and domestic bird populations are at the
equilibrium by
and
, respectively:
(9)
(9)
Substituting LPAI-only equilibrium into system (Equation1
(1)
(1) ) and setting the time derivatives to zero, we can show that
Furthermore, we have
We show the existence and uniqueness of an LPAI-only equilibrium by showing the existence and uniqueness of
and
Solving Equations (Equation9
(9)
(9) ) for
and
, we see that if
and
are unique, so are
and
if and only if
We then substitute the expressions for
and
into Equation (Equation9
(9)
(9) ) and obtain
(10)
(10) where
and
Based on Equations (Equation10
(10)
(10) ), setting
and
, we define a nonlinear operator P in the following way. Let
; then
For any two
and
, we say that
provided that
and
Then,
is a positive cone in
. If we set
, then the operator P maps C into itself.
Theorem 3.3.
There exists a unique LPAI-only equilibrium, if
.
Proof.
Let and
s.t.
, then by the mean value theorem we obtain the following for the first component of the nonlinear operator P,
where
and
.
Hence, P is monotone in K. If and
are less than
, then the operator
satisfies
, where
Notice that when
, the principal eigenvalue of the matrix
is
. Determine
such that the principal eigenvalue of
is
Let v be the eigenvector corresponding to the principal eigenvalue
of
. Therefore,
such that
. Rescale v so that its components are less than ε, that is
, where
and
. Then, it is clear that
. To show the existence of LPAI-only equilibrium, we define an increasing sequence;
and
. Note that
, where
. Since
is a increasing bounded sequence, it converges. Namely
. Since
,
is a fixed point for P.
Suppose there are two fixed points and
which are ordered, that is
, then
where
is the derivative of P with respect to u (Appendix 1) and
. Notice that if
and
, then
. Thus, we have
Repeating n times, we obtain
since
Since
and
(Appendix 1), therefore
and
. Thus, we have
Now, suppose that there are two fixed points
and
ordered as
, which means
and
Then,
where
with
and
and
. Notice that for any
, we have
since
and
That is we have,
Applying the same steps as before, we arrive at
So in either order, there exists a unique fixed point, and therefore a unique equilibrium.
Theorem 3.4.
Assume . Then, the LPAI-only equilibrium is locally asymptotically stable iff
.
Proof.
We obtain the following linear system for perturbations.
(11)
(11) where
and
are as defined in Equation (Equation6
(6)
(6) ). Considering the exponential solutions such as
,
,
and
, we obtain two non-homogeneous linear first-order differential equations. Solving them, we obtain
For the remaining equations, which do not depend on and
, we suppose that the perturbations are exponential functions of the form
. We get the following eigenvalue problem after dropping the bars,
(12)
(12) where
,
,
The equations involving HPAI, that is
and
in the above eigenvalue problem, decouple. Thus, two eigenvalues of the system will be determined by the subsystem involving equations of
and
(matrix C; the other eigenvalues are the eigenvalues of A). The eigenvalues of the Jacobian matrix C have negative real parts if and only if the spectral radius of the next generation matrix is less than 1 [Citation6] (Theorem 2, p. 33). Following the next generation matrix approach, we obtain the next generation matrix
where
The principal eigenvalue of the next generation matrix
gives the invasion number of HPAI which is denoted by
; if this is greater than or equal to 1, then at least one eigenvalue of C has a positive real part, so the LPAI-only equilibrium is unstable.
Thus, the eigenvalues of C have negative real parts if . By contradiction, we show that if
, then the eigenvalues of the matrix A do not have non-negative real parts. The characteristic equation of A is as follows:
(13)
(13) We rewrite Equation (Equation13
(13)
(13) ) as follows:
(14)
(14) If
, then
(15)
(15) Similar analysis yields
(16)
(16) So the characteristic equation (Equation14
(14)
(14) ) leads the following inequality:
(17)
(17) From the equations for the LPAI-only equilibrium, we obtain
and
. Thus, the inequality (Equation17
(17)
(17) ) becomes
(18)
(18) This contradiction completes the proof. Hence, the characteristic equation (Equation13
(13)
(13) ) cannot have roots with non-negative real parts.
Theorem 3.5.
Assume Then, there exists a unique HPAI-only equilibrium. The HPAI-only equilibrium is locally asymptotically stable if
and unstable if
Proof.
Proof of Theorem 3.5 is very similar to the proof of Theorems 3.3 and 3.4, and will be omitted.
3.3. Coexistence equilibrium
In this section, we investigate the existence of the coexistence equilibrium (i.e. interior equilibrium), that is, the equilibrium in which both LPAI and HPAI are present in wild and domestic bird populations. We suppose that all the β parameters, are positive. Special cases can be obtained by setting some or all the cross-coefficients to zero. For instance, the LPAI and HPAI might coexist only in the wild bird population, and only HPAI persist in the domestic bird population. In this paper, we will only consider the case when both pathogens coexist in both populations. Thus, the coexistence equilibrium is given by
. We study the existence of the interior equilibrium by showing the existence of the forces of infections
, and
We solve equations of the equilibrium for
,
and
and obtain
Setting,
and
we obtain
Using above expressions and the definitions of forces of infections, we arrive at the following equations:
(19)
(19)
(20)
(20)
(21)
(21)
(22)
(22) Note that
and
depend on
Using Equations (Equation19
(19)
(19) )– (Equation22
(22)
(22) ), we define a nonlinear operator T in the following way. Let
, then
(23)
(23)
For vectors, and
, we define a partial order and say that
if and only if
With this partial order ,
is a positive cone in
. We define the set
to be
where
The nonlinear operator T maps
into itself, and it is monotone in the cone
(Proposition A.2 in Appendix 2).
Let denote the LPAI-only equilibrium,
denote the HPAI-only equilibrium and
denote the coexistence equilibrium. In the previous section, we showed that if both invasion numbers are greater than unity, then both LPAI-only and HPAI-only equilibria are unstable. Next, we show that in such a situation, there exists a coexistence equilibrium,
We first linearize the nonlinear operator T around the LPAI-only and the HPAI-only equilibria, and denote the linearization by for
. For any
, we have
(24)
(24) Let
be the spectral radius of
for
, then by the Perron–Frobenius theorem
is an eigenvalue of the linear operator
. By Proposition A.2,
is a positive matrix in the order created by the cone
. Thus, the spectral radius is a simple eigenvalue to which there corresponds a ‘positive’ eigenvector in the cone
. In particular,
where
and
.
Theorem 3.6.
Assume and
then there exists at least one coexistence equilibrium
Proof.
Since and
, Proposition A.3 (Appendix 2) implies that
and
. Note that we also have
For given
and
, there exist small positive numbers
and
s.t.
We apply the operator T to the above inequality to obtain
Note that
and
for η small enough. Thus,
Similarly,
For small enough ξ, we have
Thus, we have
T is a monotone operator, so we apply the operator T to the above inequality repeatedly and obtain
Hence,
is a decreasing sequence. In addition, we have
Similarly, applying the nonlinear operator T n times, we have
Hence,
is a decreasing sequence bounded below by something strictly larger than
. Thus, the sequence converges to something with strictly positive components.
Thus,
is such that
,
,
, and
Hence, there exists a coexistence equilibrium. Our numerical simulations have not revealed alternative equilibria.
4. Simulations
Understanding how LPAI and HPAI compete and coexist in wild and domestic bird populations can further be approached through simulations. To do so, it is necessary to assess some reasonable values for parameters in the models. The parameter values we choose are for illustrative purposes, grounded in empirical studies, but to ascertain more accurate values requires more detailed empirical studies in the future.
4.1. Estimating parameter values
Determining realistic or at least plausible parameter values is obstructed by the enormous diversity of wild and domestic bird species that can be affected by AI and the lack of time-series data. AI A LPAI viruses have been isolated from more than 100 different species of wild birds. AI A viruses are predominantly found in gulls, terns, and shorebirds or waterfowl such as ducks, geese and swans (http://www.cdc.gov/flu/avianflu/avian-in-birds.htm). These wild birds are considered as reservoirs (hosts) for LPAI viruses. HPAI viruses also infect these species predominantly, killing some species within days and infecting others without symptoms. Average lifespan varies dramatically from species to species. Mallards have a lifespan of 3 years (http://en.wikipedia.org/wiki/Mallard) while albatrosses can live up to 38 years. A table of various birds' maximum lifespan is given in http://web.stanford.edu/group/stanfordbirds/text/essays/How_Long.html. We assume that LPAI is not virulent to wild birds [Citation11]. We further take wild birds to be infected with LPAI for a range of 2–21 days. We assume the same duration for HPAI infection. Hence, ,
, and
range from 365/2 to 365 /21. The recruitment rate of wild birds is unknown. We take
in the range 1000–3000 birds per year. This implies a carrying capacity of wild birds from 500 to 15,000. We use a similar parameter range for domestic fowl. This might literally pertain to say the wild waterfowl populations found in a single small lake in China, interacting with a local population of domestic waterfowl. Alternatively, this could refer to population ‘units’, and thus larger spatial areas.
Table 3. Parameter ranges.
Poultry is infected with LPAI viruses mainly through contact with infected wild birds or contaminated surfaces and/or water. LPAI is a mild illness in poultry typically leading to recovery. We assume an infection period for LPAI of 2–21 days in poultry. HPAI is extremely virulent in poultry and causes severe illness and death, typically within 48 h. We assume no recovery from HPAI in poultry since affected individuals either die or are destroyed for security reasons. Poultry is usually kept for 2 years [Citation14]; we take a range 0.5–5 years, so that to 2 year
. There are
billion poultry units in the world [Citation14]. We take
in the range 1000–3000 with an average value of 1500. This is consistent with the number of poultry units estimated from literature values if they are measured in units of
. Parameter ranges are given in .
4.2. Main questions
AI's rich ecology and evolution is a source of novel mathematical models capable of addressing new questions in biology. Theoretically, each population may be a source for a pathogen, where the intra-population transmission of the pathogen allows the pathogen to sustain itself within the focal population, or a sink, where the intra-population transmission is not sufficient to sustain the pathogen but transmission in the sink population is maintained by spillover infection from a source population [Citation5]. Naturally, the pathogen persists if at least one of the host populations is a source. However, a single pathogen might also persist if both host populations are sinks (basically because cross-transmission in effect increases the number of available hosts). In the case when two host populations and two pathogens are present, the situation is more complex. We will call population A a sink for pathogen p if pathogen p cannot persist in population A if population A is isolated from population B. Could a pathogen persist in sink–sink host populations when under competition from another pathogen? If ‘yes’, under what conditions? Could two pathogens persist if both host populations are sink populations for each one of them? The status of wild birds and domestic birds as source–sinks for LPAI and HPAI viruses in some cases is known. Wild birds are a source host population for LPAI viruses, as some species of wild birds are a natural reservoir for them. There is little discussion in the literature about whether LPAI viruses are endemic in domestic bird populations. Based on the data, however, our results in [Citation13] concluded that domestic birds are a sink host population for the LPAI viruses. Although we estimated the LPAI virus reproduction number to be above one, LPAI cannot persist on its own in poultry because it is out-competed by HPAI. On the other hand, HPAI viruses are now endemic in domestic bird populations in some countries in Asia and Africa [Citation17], and our model captures that scenario [Citation13]. The source–sink status of wild and domestic birds for HPAI and LPAI are summarized in Table .
Table 4. Source-sink status of birds to AI viruses.
The source–sink status of wild birds for HPAI viruses is an open question of significant interest [Citation19, Citation20]. Is the HPAI virus capable of sustained transmission in the wild bird population? What is the role of cross-immunity? We address these questions as well as the question of oscillatory coexistence of LPAI and HPAI through the ODE version of model (Equation1(1)
(1) ) (in which
and
are constants rather than functions of time-since-infection) in the next section.
4.3. Simulations with the full ODE system
We explored conditions for coexistence by conducting simulations of the ordinary differential equation (ODE) system corresponding to model (Equation1(1)
(1) ). In the ODE system, the relative susceptibilities of LPAI-recovered birds, which in Equation (Equation1
(1)
(1) ) were
and
, are set to constants
and
, meaning that cross-immunity does not fade with time. Therefore, all LPAI-recovered birds in each population are the same, and so can be combined into variables
and
, with the rate of change for the wild population given by
(and an analogous equation for the domestic population). In the HPAI-infected equations, the integrals are replaced by or
, giving a system of nine ODEs.
We investigate scenarios of coexistence of LPAI and HPAI in wild and domestic birds in the form of an equilibrium or in the form of sustained oscillations. We will call the order of prevalences ‘realistic’ if in the wild birds LPAI prevalence is higher than HPAI prevalence, and in domestic birds HPAI prevalence is higher than LPAI prevalence. We expect our prevalences in the simulations to be in this realistic order.
Figure shows a coexistence equilibrium with realistic parameter values and realistic prevalence order, that is HPAI prevalence in domestic birds is higher than that of LPAI and LPAI prevalence for wild birds is higher than that of HPAI. The solution stabilizes to an equilibrium. We note that in Figure at equilibrium domestic birds are HPAI infected out of a total of 826 domestic birds at equilibrium (both times
), giving as infection rate of 1 in 50. Just for a comparison, in a recent outbreak of HPAI in the US poultry industry approximately 50 million birds were affected out of 2 billion birds [Citation25] which is 1 in 40. Thus, our figure is a reasonable approximation of reality.
Figure 2. Coexistence with realistic parameter values. The parameter values used in the figure are as follows: ,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
. The reproduction numbers are
and
. The invasion coefficients are as follows:
and
. The red line shows HPAI in wild birds, the orange dashed line shows HPAI in domestic birds, the blue line shows LPAI in wild birds, the green dashed line shows LPAI in domestic birds.
![Figure 2. Coexistence with realistic parameter values. The parameter values used in the figure are as follows: Λw=2000, μw=0.25, νHw=36.5, αHw=36.5, αLw=73, qw=0.5, β11L=.018776, β11H=0.005, Λd=1020, μd=0.5, νHd=36.5, αd=52.14, qd=0.5, β22L=.02539, β22H=0.04897, β12L=0.006, β21L=0.03, β12H=0.002, β21H=0.031. The reproduction numbers are RL=2.54 and RH=2.71. The invasion coefficients are as follows: RˆLH=1.75 and RˆHL=1.98. The red line shows HPAI in wild birds, the orange dashed line shows HPAI in domestic birds, the blue line shows LPAI in wild birds, the green dashed line shows LPAI in domestic birds.](/cms/asset/a153bab5-d277-481c-aee9-32fe96bb9e40/tjbd_a_1111449_f0002_c.jpg)
For Figure , the LPAI reproduction numbers are ,
,
, and
. In addition, the HPAI reproduction numbers are
,
,
, and
. The invasion numbers are
and
. We see that, as we expect, the population-specific reproduction numbers of LPAI in wild birds and HPAI in domestic birds are higher than one; all other numbers are lower than one. With these parameters, wild birds are a sink for HPAI with realistic parameter values and a realistic order of prevalences. We note that we can obtain with realistic parameters and realistic prevalence order a case where HPAI in wild birds is a source. However, the
would be larger and a larger
should be more detectable in practice. Thus with the available information, we cannot deduce for sure whether HPAI will persist on its own in wild birds; however, the model suggests that the situation is closest to reality if HPAI is a sink for wild birds.
Figure shows that the full system can exhibit sustained, complex oscillations. We note that the prevalences are generally in realistic order and the parameters used in the examples are biologically reasonable. For wild birds, LPAI is generally higher than HPAI. The reversed order is observed for domestic birds. The oscillations of LPAI and HPAI are shifted half a period both in wild and domestic birds. That is, when LPAI is at high values, HPAI is at low values and vice versa. This is a manifestation of the competition of LPAI and HPAI for susceptible hosts in both wild and domestic birds. We note that in the full system oscillations can be obtained for relatively intermediate or low values for and
, which shows that even intermediate levels of cross-immunity to HPAI can destabilize the system. The parameters
and
change the shape of the oscillations. In general, oscillations, whenever found, are observed in a moderate neighbourhood of the parameters for which they occur.
Figure 3. Oscillations with realistic parameter values. The parameter values used in the figure are as follows: ,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
. The reproduction numbers are
and
. The invasion coefficients are as follows:
and
. The red line shows HPAI in wild birds, the orange dashed line shows HPAI in domestic birds, the blue line shows LPAI in wild birds, the green dashed line shows LPAI in domestic birds.
![Figure 3. Oscillations with realistic parameter values. The parameter values used in the figure are as follows: Λw=2000, μw=0.25, νHw=36.5, αHw=36.5, αLw=73, qw=0.45, β11L=.018776, β11H=0.015, Λd=1020, μd=0.5, νHd=36.5, αd=52.14, qd=0.5, β22L=.025, β22H=0.04897, β12L=0.006, β21L=0.03, β12H=0.0, β21H=0.031. The reproduction numbers are RL=2.54 and RH=2.7. The invasion coefficients are as follows: RˆL=1.37 and RˆH=1.86. The red line shows HPAI in wild birds, the orange dashed line shows HPAI in domestic birds, the blue line shows LPAI in wild birds, the green dashed line shows LPAI in domestic birds.](/cms/asset/504f9bd5-0c8a-4974-8fd0-e3a480546e9e/tjbd_a_1111449_f0003_c.jpg)
Furthermore, we note that oscillation and persistence of HPAI occurs in the case when , that is when transmission from domestic to wild birds of HPAI does not occur. In this case, persistence of HPAI is only possible if
. We note that HPAI in wild birds emerges (or is likely detectable) only from time to time.
Figure is an illustration of a sink–sink scenario for both pathogens. A sink–sink scenario is a scenario where both pathogens are sinks for each of the populations but they can persist together in a coexistence equilibrium. We say that a sink–sink scenario occurs if the following is satisfied in each of the populations if they are isolated (no cross-transmission):
The reproduction numbers and the invasion numbers of both pathogens are smaller than one.
Figure 4. Coexistence with realistic parameter values. The parameter values used in the figure are as follows: ,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
,
. The reproduction numbers are
and
. The invasion coefficients are as follows:
and
. The red line shows HPAI in wild birds, the orange dashed line shows HPAI in domestic birds, the blue line shows LPAI in wild birds, the green dashed line shows LPAI in domestic birds.
![Figure 4. Coexistence with realistic parameter values. The parameter values used in the figure are as follows: Λw=2000, μw=0.25, νHw=36.5, αHw=36.5, αLw=73, qw=0.426, β11L=.0086, β11H=0.005, Λd=1020, μd=0.5, νHd=36.5, αd=52.14, qd=1, β22L=.02539, β22H=0.0166, β12L=0.0043, β21L=0.0131, β12H=0.0014, β21H=0.0332. The reproduction numbers are RL=1.45 and RH=1.29. The invasion coefficients are as follows: RLˆ=1.17 and RHˆ=1.22. The red line shows HPAI in wild birds, the orange dashed line shows HPAI in domestic birds, the blue line shows LPAI in wild birds, the green dashed line shows LPAI in domestic birds.](/cms/asset/7121c357-5bc5-49ed-9fb0-7fdfd3c84bf0/tjbd_a_1111449_f0004_c.jpg)
We were able to produce an example of this scenario, where all intra- and cross-population components of the reproduction numbers and invasion reproduction numbers are smaller than one. The coexistence of LPAI and HPAI under a sink–sink scenario is shown in Figure . All components of the reproduction numbers and the invasion reproduction numbers are smaller than one:
Table
In this case, if all cross-coefficients , where
, then both LPAI and HPAI will die out. Persistence of both pathogens occurs only through the cross-population transmission. This scenario is easy to find with no constraints on parameters, but in our example, the parameters are plausible and we have a realistic prevalence order in wild and domestic birds.
4.4. LPAI and HPAI dynamics in the wild bird system only
We saw that the full ODE system corresponding to system (Equation1(1)
(1) ) can exhibit oscillations where LPAI and HPAI coexist. An interesting question occurs whether the coexistence equilibrium can lose stability if restricted to just the wild bird system. This question is of particular importance in the ODE case as it is well known that alternative ODE models with cross-immunity do not always lead to oscillations. For instance, Castillo-Chavez et al. found that age structure or quarantine needs to be introduced for a cross-immunity model to show oscillations [Citation3, Citation4]. However, it turns out that this is not the case with system (Equation1
(1)
(1) ) with wild birds only. The characteristic equation of the coexistence equilibrium looks ‘almost’ stable but for some parameter values the coexistence equilibrium can be destabilized (the analytical expression giving parameter combinations for which the system is unstable is too complicated to interpret, so we illustrate instability with numerical examples). Figure shows sustained oscillations for both LPAI and HPAI. The oscillations in LPAI have much larger amplitude. HPAI peaks follow LPAI peaks by about 1/4 period which is typical for classical predator–prey dynamics. The parameters chosen including the reproduction numbers and invasion reproduction numbers have plausible values. To obtain oscillations with these parameter choices, our simulations suggested that we need to choose
. That suggests that oscillations, which often mimic outbreaks, occur if the LPAI cross-immunity to HPAI is nearly or completely non-existent. Figure also shows sustained oscillations. Looking more closely at the figure, we can see two oscillation patterns superimposed, differing in period. With the short period oscillations, the peak of LPAI is followed by a peak of HPAI, somewhat resembling predator–prey oscillations. The unstable equilibrium values are given by
. In the simulation in Figure , the reproduction number of LPAI is somewhat high to be realistic. Decreasing
to
from the parameter listed in Figure allows the oscillations of LPAI and HPAI to be shifted so they are half the period out of phase, so that the maximum of HPAI occurs at the same moment as the minimum of LPAI. In this case, we say the the system exhibits fully competitive oscillation.
Figure 5. Sustained oscillations in the wild birds only system. Parameter values are ,
,
,
,
,
,
,
,
,
,
,
,
. The reproduction numbers are
and
. The invasion coefficients are
and
. The red line shows HPAI and the blue line shows LPAI.
![Figure 5. Sustained oscillations in the wild birds only system. Parameter values are Λw=2000, μw=0.14, νHw=49.5, αHw=51.6, αLw=73, qw=0.98, β11L=.018776, β11H=0.015, Sw(0)=3449.72, ILw(0)=14.684, RLw(0)=3366.78, IHw(0)=7, RHw(0)=769.5. The reproduction numbers are RL=3.66 and RH=2.116. The invasion coefficients are RˆL=1.73 and RˆH=2.08. The red line shows HPAI and the blue line shows LPAI.](/cms/asset/dc137c98-e8ee-49ba-b669-59e552d9e86e/tjbd_a_1111449_f0005_c.jpg)
It is useful to develop some intuitive understanding for why oscillations arise in this system. Biologically, the system is not really analogous to a predator–prey system. Recall that LPAI and HPAI both attack susceptible hosts. If , there is complete cross-immunity, and the relation between LPAI and HPAI is simply that of being competitors for susceptible hosts. One does not find coexistence in this case in a single population. In this model, infection by HPAI always gives complete immunity to LPAI. However, if
, there is only partial (or no) immunity to HPAI conferred by prior infection by LPAI, so LPAI-recovered hosts can be infected by HPAI. A direct predation analogue in this system would be if HPAI could infect LPAI-infected hosts and eliminate the LPAI infection, thereby directly reducing the number of LPAI-infected hosts. In our model, HPAI does not have this direct effect because it just attacks LPAI-recovered hosts. However, attacking LPAI-recovered hosts increases the prevalence of HPAI, and allows it to infect more susceptible hosts, for which it is competing with LPAI. It would, therefore, be analogous to a system in which one competitor can consume the carcasses of the other. For the parameters of Figure , the number of LPAI-infected hosts increases whenever
and decreases otherwise. As
increases, it decreases
until it is below this value (HPAI also helps decrease
, but it is less common, especially when
is near its peak). For HPAI to increase requires
Even though this threshold is higher (due to the high death rate), it applies to the sum of susceptible and LPAI-recovered hosts (the latter discounted by
). Because most LPAI-infected birds recover, as the peak in
draws down
, it also increases
, so that the condition for HPAI to increase can sometimes continue to be met after LPAI has started to decrease, as in the figure. For the parameters of the figure, HPAI relies mostly on LPAI-recovered birds, the peak of which is after the peak in
. HPAI, therefore, is increasing most rapidly after the LPAI peak. Eventually, HPAI depletes the hosts it attacks, and starts to decrease. By this time, the susceptible hosts have started to increase (because of the low level of
), but they then increase faster until they are high enough for
to start to increase. So oscillations in this system arise because of a combination of competition, and a phenomenon analogous to ‘scavenging’ among carnivores.
Figure 6. Sustained oscillations in the wild birds only system. Parameter values are ,
,
,
,
,
,
,
,
,
,
,
,
. The reproduction numbers are
and
. The invasion coefficients are
and
. The red line shows HPAI and the blue line shows LPAI.
![Figure 6. Sustained oscillations in the wild birds only system. Parameter values are Λw=3810, μw=0.054, νHw=87.5, αHw=87.4, αLw=69.4, qw=0.99, β11L=.0131, β11H=0.01, Sw(0)=5000, ILw(0)=40, RLw(0)=12000, IHw(0)=15, RHw(0)=25,000. The reproduction numbers are RL=13.3 and RH=4.0. The invasion coefficients are RˆL=3.3 and RˆH=4. The red line shows HPAI and the blue line shows LPAI.](/cms/asset/04b7ed38-6ed1-49a7-82fa-e7e07df23709/tjbd_a_1111449_f0006_c.jpg)
We next address the question of whether we can reduce and still obtain oscillations. The most influential parameter for that to occur is
, which needs to be fairly low (
in Figure and
in Figure , both reasonable for wild birds) to produce oscillations with smaller
. Raising
allows oscillations without
becoming excessively small and therefore unrealistic for wild bird populations. Raising the sum
also allows for lowering
. Still with nearly realistic other parameters,
needs to stay above
for oscillations to occur.
LPAI persists at higher levels than HPAI in Figures –, which is the realistic scenario for wild bird populations. However, raising as in Figures and leads to oscillations but also increases the prevalence of HPAI at times to levels higher than LPAI which in wild birds is unrealistic. Lack of cross-immunity from LPAI in domestic birds may explain why HPAI persists in domestic birds at higher prevalence levels.
For realistic parameter values, it appears that in most cases oscillations of LPAI have larger amplitude and go to higher values compared to oscillations in HPAI. In the future, we expect that long-term empirical time-series of AI will become available. There is considerable temporal variability in avian flu prevalence, and the processes we have explored could help explain some of the drivers of these dynamics. Our model predictions about phase shifts and differences in amplitude for flu strains differing in pathogenicity and cross-infectivity should be useful in future studies in interpreting patterns in such data.
5. Discussion
AI continues to be a threat to human health. Recently, strains of HPAI H7N9 have started infecting humans and hold potential to turn pandemic with deadly consequences. Studying AI in birds and humans is of paramount importance if we are to be prepared for the next deadly pandemic.
In this paper, we introduce an AI model for multiple bird populations. The model incorporates two strains, one LPAI and one HPAI. We are interested in studying the dynamics of LPAI and HPAI in wild and domestic birds. Our model builds on previous work. Several models published before have studied the interplay between LPAI and HPAI. Lucchetti et al. [Citation13] were the first to introduce LPAI and HPAI but the wild bird population in that article is taken as a periodic source, not as a dynamical variable. Bourouiba et al. [Citation2] studied the transmission of LPAI and HPAI in wild bird populations only. They assumed no cross-immunity and that LPAI-recovered birds can get infected by HPAI with the same transmission coefficients as do susceptible birds. However, reinfected wild birds can show higher survivability. The results of this article are mostly obtained through simulations and are specific to the parameters chosen. A model close to the one considered here is introduced by Augusto and Gumel [Citation1]. This model studies LPAI and HPAI in both wild and domestic birds and assumes reinfection by HPAI of exposed and infectious birds with LPAI. It assumes that the partial immunity to HPAI conferred by LPAI infection is fixed, whereas we allow it to wane with time (so their model is a pure ODE model, whereas ours includes PDEs). Also, their model includes exposed (infectious but asymptomatic) classes, and includes two mechanisms by which LPAI can change into HPAI. One is mutation, which takes place in LPAI-exposed birds but produces HPAI-exposed and HPAI-infected birds. In the other process, when LPAI-exposed birds become symptomatic (enter an infected class), a fraction of them become LPAI-infected and the rest become HPAI-infected birds. (In addition, birds with LPAI can become infected by HPAI, as in our model.) This article finds backward bifurcation and multiple coexistence equilibria which are caused by the reinfection with HPAI of LPAI-exposed birds and LPAI-infected birds. The article makes two conjectures which are both true and are explained in the case of wild birds only in [Citation23]. One of our main contributions here relative to article [Citation1] is that we provide rigorous analytical results for when each strain persists and when it dies out, and when the two strains coexist for the case when both reproduction numbers are greater than one. These are quantified in terms of the invasion reproduction numbers and are satisfied for all parameter values. One difference from the model in [Citation1] is that our model does not exhibit backward bifurcation. Also, of course, we allow cross-immunity to fade with time.
We compute the reproduction numbers and
and the invasion reproduction numbers
and
. The model has a unique DFE which is locally and globally stable if both reproduction numbers are smaller than one. The global stability of the DFE rules out backward bifurcation. There are also a unique LPAI-only and a unique HPAI-only equilibria which exist if the LPAI (HPAI) reproduction number is larger than one. The LPAI-only equilibrium is locally asymptotically stable whenever it exists if
. The HPAI-only equilibrium is locally asymptotically stable whenever it exists if
. We show that if
and
, then a coexistence equilibrium exists. The question about the uniqueness of the coexistence equilibrium remains open.
Simulations suggest that the coexistence equilibrium is not stable for all parameter regimes. In fact, the coexistence equilibrium can be destabilized even in the corresponding ODE system in which and
are assumed constant. Since the semi-trivial equilibria are locally stable, this clearly suggests that the interaction between the strains, that is
and/or
, is necessary for the destabilization of the coexistence equilibrium. Next, we asked whether the presence of both populations and transmission between the populations were necessary for instability. Investigating the wild bird system only [Citation22], we find numerically that the ODE model of wild birds with LPAI and HPAI also can exhibit oscillations in which both LPAI and HPAI persist. In the wild bird system, oscillations are found with high values of
, which means that destabilization of the system occurs if cross-immunity is very low. In the full system, oscillations can be found for larger ranges of
and
. Thus, transmission between the two populations allows for destabilization of the system for a variety of cross-immunity levels. For sustained oscillations in a single population considered alone, LPAI-recovered birds must be almost as susceptible to HPAI infection as are naive birds.
Simulations suggest that for plausible parameter values, we can also produce realistic prevalences. In particular, in wild birds, the LPAI prevalence is higher than the HPAI prevalence, while in domestic birds, it is vice versa. Of particular interest is the case when a population is a sink for a pathogen but persistence in a multi-population multi-pathogen system is still possible. We call population A a sink for pathogen p, where LPAI or HPAI, if pathogen p cannot persist alone in population A, if isolated. It is well known that, in a system with two sink habitats, a population can sometimes persist by using both habitats. We have investigated this question in the case of competition of pathogens. In the case of competition, we say that a population A is a sink for pathogen p if its within-population reproduction number is less than one, or if its reproduction number is greater than one, its within-population invasion reproduction number is smaller than one and the other pathogen is present. We show through simulations that coexistence of both pathogens is possible, if all their within-population and cross-population reproduction numbers are smaller than one. This observation is very important since estimates of the reproduction number of HPAI H5N1 in poultry vary around one [Citation14, Citation15, Citation24] but our results imply that even if the reproduction number is below one, HPAI may persist in the wild-domestic bird system, even under competition with LPAI. We note that in the sink–sink scenario, even though the species-specific, strain-specific reproduction and invasion numbers are below one, the overall strain-specific reproduction and invasion numbers are above one, which gives persistence.
Future empirical studies will be required to refine parameter estimation and ascertain the likelihood of observing the complex dynamics revealed by this model. Also, in the future it would be useful to explore alternative models of recruitment instead of the constant rate of input assumed in model (Equation1(1)
(1) ). Finally, it is likely that spatial dynamics are significant in this system. Many wild waterfowl are migratory and can move over large areas. Some birds may return to the same area each winter, but others may move among regions. Domestic fowl are concentrated in more discrete locations, with less mobility, one expects. Dealing with spatial patchiness, migration and heterogeneity will likely be important in more realistic future characterizations of cross-population transmission in AI.
Acknowledgments
RDH and MB thank the University of Florida Foundation for support.
Disclosure statement
No potential conflict of interest was reported by the authors.
ORCID
Necibe Tuncer http://orcid.org/0000-0002-6388-2499
Additional information
Funding
References
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Appendix 1. LPAI-only equilibrium
Proposition A.1.
Let denote the derivative of the operator P; then, the spectral radius of
is less than 1.
Proof.
The derivative of the operator P is . Note that
is a positive matrix, since all its entries are positive. Let A be a
square matrix given as
Clearly,
. Since
, dividing by
we obtain
where
Let
, then
. Thus, 1 is an eigenvalue of A corresponding to a positive eigenvector. By Perron–Frobenius theorem, the spectral radius of A is
. Furthermore,
since
.
Appendix 2. Coexistence equilibrium
Proposition A.2.
Derivatives of the nonlinear operator T satisfy the following inequalities:
T is monotone in
, that is
T maps the set
into itself.
.
Proof.
We only prove the inequalities
and
, since the inequalities of other derivatives when
can be derived by applying the same steps. Note that
Thus,
Next, we prove the inequalities
and
Inequalities for the other derivatives when
can be shown in a similar way. Note that
as in Equation (Equation21
(21)
(21) ). The derivative of
with respect to
is
Combining the terms, we obtain
Clearly,
is negative, provided that
(A1)
(A1) Since
the left side of Equation (EquationA1
(A1)
(A1) ) is less than the following integral
The derivative of
with respect to
is
Reorganizing the terms, we obtain
(A2)
(A2) The derivative
is positive if the term inside the square brackets in Equation (EquationA2
(A2)
(A2) ) is positive. Thus,
if
(A3)
(A3) and
(A4)
(A4) Applying integration by parts, Equation (EquationA3
(A3)
(A3) ) becomes
Since
, the expression in Equation (EquationA4
(A4)
(A4) ) is greater than the following:
(A5)
(A5) By integration by parts, Equation (EquationA5
(A5)
(A5) ) becomes
which is positive, since
We prove the monotonicity of the operator T, by showing that
whenever
Because of the symmetry, the steps for proving the rest of the inequalities
,
and
are similar.
Using the mean value theorem, we obtain
We just proved that
,
,
,
. Since
we have
Thus,
Next, we show that T maps the set CT into itself by showing it for
. Since
and
, it is clear that
Proposition A.3.
The spectral radius if and only if
and the spectral radius
if and only if
Proof.
We only show that iff
, since the other case is similar. We have
where v is the positive eigenvector,
. The linearization matrix
at the LPAI-only equilibrium is given as follows:
which is equivalent to the following block triangular matrix,
The
block diagonal matrices are as follows:
and the components of the
matrix
are as follows:
The principal eigenvalue of
is
The eigenvalues of
are smaller than one, as we showed in Proposition A.1. Therefore, the principal eigenvalue of
is greater than 1 if and only if
.