Skip to main content
Springer logoLink to Springer
. 2025 Aug 29;87(10):137. doi: 10.1007/s11538-025-01515-0

Stability of Difference Equations with Interspecific Density Dependence, Competition, and Maturation Delays

Geoffrey R Hosack 1,, Maud El-Hachem 1, Nicholas J Beeton 1
PMCID: PMC12397156  PMID: 40879690

Abstract

A general system of difference equations is presented for multispecies communities with density dependent population growth and delayed maturity. Interspecific competition, mutualism, predation, commensalism, and amensalism are accommodated. A sufficient condition for the local asymptotic stability of a coexistence equilibrium in this system is then proven. Using this system, the generalisation of the Beverton-Holt and Leslie-Gower models of competition to multispecies systems with possible maturation delays is presented and shown to yield interesting stability properties. The stability of coexistence depends on the relative abundances of the species at the unique interior equilibrium. A sufficient condition for local stability is derived that only requires intraspecific competition to outweigh interspecific competition. The condition does not depend on maturation delays. The derived stability properties are used to develop a novel estimation approach for the coefficients of interspecific competition. This approach finds an optimal configuration given two conjectures. First, coexisting species strive to outcompete competitors. Second, persisting species are more likely in stable systems with strong dampening of perturbations and high ecological resilience. The optimal solution is compared to estimates of niche overlap using an empirical example of malaria mosquito vectors with delayed maturity in the Anopheles gambiae sensu lato species complex.

Introduction

Delayed maturity, where juveniles have zero fecundity before maturing into reproductive adults, and interspecific density dependence caused by the fundamental ecological interactions of competition, mutualism, predation, commensalism or amensalism are two important factors that determine the stability of ecosystems and ecological communities (May 1974). Sufficient conditions for local asymptotic stability of equilibria are therefore derived for an m-dimensional vector of species abundances x(t)=[x1(t),,xm(t)] in the system of delay difference equations (Fisher 1984),

xi(t+1)=σδiixi(t)+Fi(x(t-δi))xi(t-δi),iM={1,,m},tZ. 1

In Eq. (1), each species iM attains adulthood and reproductive maturity at age δiN0={0,1,2,}. The adults of species i with age greater or equal to δi survive to the next time step with age-class specific probability σδii(0,1) and complementary probability of adult mortality, zi=1-σδii. Adults reproduce with per capita population growth function Fi that accounts for immature survival, the delayed maturity of species i, and both intraspecific and interspecific density dependence.

The single species case (m=1) of Eq. (1) corresponds to the well-known model proposed by Clark (1976). A short summary of findings for this important equation are as follows. Clark (1976) presents a sufficient condition for local stability at an equilibrium x1 that does not depend on the maturation delay,

ddx1(t)x1(t)F1x1(t)x1(t)=x1<z1=1-σδ11. 2

However, necessary and sufficient conditions do depend on the delay and also require numerical calculation outside special cases (Clark 1976). The necessary and sufficient local stability conditions are shown by Kuruklis (1994) and Papanicolaou (1996) to generalise even for real-valued σδ11R. Local stability for the single species model in certain cases also implies global stability, but not generally (López and Parreño 2016). Fisher and Goh (1984) propose sufficient conditions for global stability by construction of a Lyapunov function using results from La Salle (1976). These sufficient conditions also do not depend on the delay. Elaborations based on Clark (1976) are not considered further here, for example, Goh (1980) and Streipert and Wolkowicz (2023) generalise to density dependent survival functions. See Liz (2020) for a recent review and further analysis of single species delayed difference population models based on Eq. (1) with m=1.

The multispecies delayed system with m>1 in Eq. (1) has received far less attention compared to the single species case. Exceptionally, Fisher (1984) shows that the local and global stability properties are deduced from the corresponding non-delayed system defined by

xi(t+1)=zi-1Fi(x(t))xi(t),zi=1-σδii(0,1),iM. 3

In the important case of interspecific competition in non-delayed systems, Sacker (2011) states that consideration of multispecies discrete-time systems “inevitably” leads to consideration of the multispecies extension of the Leslie-Gower model (Leslie and Gower 1958) equivalent to the non-delayed system with

xi(t+1)=Fi(x(t))xi(t)=λixi(t)1+kMAikxk(t),iM, 4

for m-dimensional positive fecundity rate vector λ>0 and m×m nonnegative matrix A0 composed of nonnegative entries Aij0 for all i,j{1,,m}. The interspecific competitive effect of species j on the population growth rate of species ij is defined by Aij, and intraspecific competition is defined by Aii. Sacker (2011) provides sufficient conditions for global asymptotic stability of the unique positive equilibrium in the non-delayed model that depends on “sufficiently small” interspecific competition defined by A, the entry-wise inequality λ>1, and the condition

λi-1jM\iλjAijAjj,iM. 5

Using the results of Fisher (1984), global stability of the corresponding delayed system in the form of Eq. (1) can be evaluated by considering the global stability of the identical equilibrium provided by the modified non-delayed system of Eq. (3). The condition of global stability for the delayed system thus depends not only on the density-independent fecundity rates via Eq. (5) but also the adult survival probabilities via Eq. (3).

In Sect. 2, sufficient conditions are given for local stability in the general multispecies delayed model of Eq. (1). The sufficient conditions for stability derived by linearisation of an equivalent age-specific version provide the multispecies analogue of the sufficient condition of Eq. (2) for the single species case. Constraints on the eigenvalues of its linearised approximation near an equilibrium are obtained using a geometric argument by Gers̆gorin’s Theorem (Gers̆gorin 1931) as extended by Brualdi (1982) using directed graphs. The result is applied to a competitive delay multispecies (CDM) model. The CDM model extends the multispecies Leslie-Gower model of competition of Eq. (4) to allow for potential delayed maturity and age-specific survival probabilities (Sect. 3). Sufficiency conditions are established such that a positive coexistence equilibrium, if it exists, is both unique and locally asymptotically stable if interspecific competition does not outweigh intraspecific competition. Importantly, these conditions hold even if the exact values of the delays, density independent fecundity rates and age-specific survival probabilities in the CDM model are unknown or uncertain.

It is also shown that the local asymptotic stability of the interior equilibrium for the CDM model depends on the relative abundances, that is, the species composition or fractional contributions of each species to the total equilibrium abundance. This result is used in Sect. 4 to develop a method to find an optimal configuration of the parameters A given the assumptions that i) species are more likely to persist in a system with greater resilience and faster return times to a stable equilibrium after disturbances, and ii) species seek to increase competitive advantage over other species. The estimate requires knowledge of fecundity, density independent survival probability and an observed equilibrium in which species coexist. The approach does not require specific information about the carrying capacities of the species, but instead depends only on estimates of relative abundance that are often more readily available from field data than absolute or true abundance (Sinka et al. 2016). The development extends ideas that relate relative abundance to measures of niche overlap and parameterisation of the competition coefficients in the Lotka-Volterra competitive system of ordinary differential equations (Levins 1968; May 1975). The previous and novel procedures are compared using empirical estimates provided by Pombi et al. (2017) for a system of three competing species of Anopheles gambiae sensu lato mosquitoes with delayed maturity that vector human malaria.

Interspecific Density Dependence with Delayed Maturity

An equivalence exists between a delayed difference equation system and an expanded non-delayed system with explicit age structure, which has been applied to both single species (Fisher and Goh 1984; Streipert and Wolkowicz 2023) and multiple species (Fisher 1984) examples. It can be shown that Eq. (1) is indeed a collapsed version of an expanded age-specific model with age-specific immature survival probabilities. To see this, let a{0,,δi-1} denote the age-classes of species i with immature age-specific survival probabilities σai(0,1]. Define the vector-valued per capita growth function G adjusted for the explicit inclusion of immature survival probabilities such that

Gi(x)a=0δi-1σai=Fi(x),iM. 6

If δi=0 then the empty product a=0δi-1σai is defined as the multiplicative identity with value one. Define the vectors of age-specific abundances with size (δi+1) for each species at time t by

yi(t)=[y0i(t),,yδii(t)],

where yai(t) is the abundance of age class a{0,,δi} for species i at time t. Define also the vector y(t)=[y1(t),,ym(t)] of size (m+iMδi) of all age classes for all species at time t. Let h denote the vectorised function such that y(t+1)=h(y(t)), where yai(t+1)=hai(y(t)) for a=1,,δi and iM. Let the m-dimensional vector

yδM(t)=[yδ11(t),,yδmm(t)]=x(t)

denote the adult abundances of the m species at time t, where δ=[δ1,,δm]. The system of recurrence equations for y(t) composed of ages a{0,,δi} for each species iM at times tZ is then defined by

yai(t+1)=haiy(t)=GiyδM(t)yδii(t)ifa=0andδi>0σa-1iya-1i(t)ifa{1,,δi-1}andδi>0σδi-1iyδi-1i(t)+σδiiyδii(t)ifa=δiandδi>0σ0iy0i(t)+GiyδM(t)y0i(t)ifa=δi=0. 7

Given the definition yδM(t)=x(t), Eq. (7) is for a=0 and δi>0 equivalent to

y0i(t+1)=Gix(t)xi(t).

For the case of no maturation delay with δi=0 such that y0i(t)=yδii(t)=xi(t), Eq. (7) is equivalent to

y0i(t+1)=σ0ixi(t)+Gix(t)xi(t).

Eq. (7) then collapses to the equivalent delayed system,

xi(t+1)=σδiixi(t)+xi(t-δi)Gi(x(t-δi))a=0δi-1σai,iM, 8

Eq. (1) is by Eq. (6) equivalent to Eq. (8). Let y denote a positive equilibrium such that y=h(y)>0. Note that the adult age class equilibrium abundances of Eq. (7) are equivalent to those of Eq. (8), such that yδM=x, because yδM(t)=x(t) by definition.

The construction of Eq. (7) generalises the approach of Fisher and Goh (1984) to the multispecies case, where adult reproduction through Gi contributes to the recruits y0i(t+1) of species i. If the age classes are not of explicit interest then the assignment σai=1 for a{0,,δi-1} and iM in Eq. (7) is an obvious choice as used in the multispecies context by Fisher (1984). The choice of how to specify the immature age classes is a matter of interpretation that may for example depend on whether immature individuals should be explicit and observable or implicit and latent. Eq. (8) has been analysed for single species (m=1) to establish local stability conditions by Clark (1976). For the single species case, Fisher and Goh (1984) also construct a Lyapunov function on the scalar equation of Eq. (8) with m=1 to provide sufficient conditions of global stability for certain models. Sufficient global stability conditions for the positive equilibrium (Sacker 2011) and boundary equilibria (Jiang and Niu 2017; Hou 2021) of specific multispecies non-delayed versions of Eq. (8) with competitive density dependent growth functions have previously been presented.

Here, sufficient local stability conditions are provided for the general multispecies system with delays. The Jacobian matrix of Eq. (7) evaluated at equilibria derived from Eq. (8) for the adult compartments is investigated in Sect. 2.1. A sufficient condition for local asymptotic stability is then derived for the case of non-zero adult equilibrium abundances (Sect. 2.2). The case of boundary equilibria is investigated in Sect. 2.3. A detailed examination is then provided for a multispecies competitive system of particular interest (Sect. 3).

Local Asymptotic Stability

Applying Eq. (2) shows that for the single species case (m=1), a sufficient condition for the local stability of Eq. (8) at an equilibrium x1 is

G1(x1)+x1dG1(x1(t))dx1(t)x1(t)=x1×a=0δ1-1σai<z1. 9

The above sufficient condition does not depend on the delay except through the product of the survival probabilities of the immature stages. Necessary and sufficient conditions for local stability, however, depend on the delay with closed-form expressions only available for certain choices of functional forms and parameter values (Clark 1976; Fisher and Goh 1984). It will be shown that a closed form expression similar to Eq. (9) provides a sufficient condition for local stability in the multispecies delayed system of Eqs. (7) and (8).

Let J denote the matrix of partial derivatives of Eq. (7) with dimensions (m+iMδi)×(m+iMδi), such that the (kl) entry of J is Jkl=hky(t)/yl(t). An equilibrium y of the multispecies age classes of the delayed system of Eq. (7) is locally asymptotically stable if the moduli of all eigenvalues of the Jacobian matrix evaluated at the equilibrium, denoted by the matrix J, are less than one. The spectral radius of a square matrix is defined as the maximum magnitude of all its eigenvalues. The equilibrium y of Eq. (7) is therefore locally asymptotically stable if and only if the spectral radius of J is less than one, denoted ρ(J)<1.

For species i with maturation delay δi>0, the partial derivatives of Eq. (7) evaluated at equilibrium are then

haiy(t)ybj(t)y(t)=y=σbiifi=j,a=1,,δi,b=a-1,σδiiifi=j,a=b=δi,Gi(x)+xiGi(x(t))xi(t)x(t)=xifi=j,a=0,b=δj,xiGi(x(t))xj(t)x(t)=xifij,a=0,b=δj,0otherwise. 10

For species i without delayed maturity (δi=0), the partial derivatives are

h0iy(t)ybj(t)y(t)=y=σ0i+Gi(x)+xiGi(x(t))xi(t)x(t)=xifi=j,b=δj,xiGi(x(t))xj(t)x(t)=xifij,b=δj,0otherwise. 11

Evidently, only the zero age classes (a=0) in Eq. (10) depend on the equilibrium values. The Jacobian matrix evaluated at the equilibrium y is

J=J11J12J1mJ21J22J2mJm1Jm2Jmm 12

that consists of block matrices defined by

Jij=0000σ0i+Gi(x)+xiGi(x(t))xi(t)x(t)=xσ0i000000σδi-2i00000σδi-1iσδiiifi=j,0xiGi(x(t))xj(t)x(t)=x00ifij,

where the block matrix in the second case has all zero entries except for the last entry in its first row if δi>0 and, by Eqs. (10) and (11),

Jij=σ0i+Gi(x)+xiGi(x(t))xi(t)x(t)=xifi=j,xiGi(x(t))xj(t)x(t)=xifij,

if δi=0 otherwise.

Sufficient Condition for Local Stability of Coexistence Equilibrium

The graph of Eq. (12) is used to construct a sufficient condition for the local asymptotic stability of the equilibrium. This result builds on a well-known result that bounds the location of the eigenvalues. Let s(B) denote the spectrum of matrix B, which is the set of eigenvalues of B, that is the point set of values of v that satisfy det(B-vI)=0. The Gers̆gorin theorem (see, e.g., Horn and Johnson 1985) provides a geometric argument for bounding the spectrum of eigenvalues in the complex plane.

Theorem 1

(Gers̆gorin) For n×n matrix B, let

Ri(B)=jiBij,i,

denote the deleted absolute row sums. The eigenvalues of B are located in the region formed by the union of n discs such that

s(B)iv:v-BiiRi(B).

Gers̆gorin’s theorem establishes that the eigenvalues of B are located within the Gers̆gorin region. The discs that form a Gers̆gorin region are called Gers̆gorin discs and the corresponding boundaries of the discs are Gers̆gorin circles.

Direct application of the Gers̆gorin theorem to J does not necessarily bound the Gers̆gorin discs within unit distance of the origin of the complex plane. The deleted absolute row sums that correspond to rows with the adult survival probabilities, σδii for iM in Eq. (12), are not necessarily less than σδii. If any of these sums exceed one then at least one Gers̆gorin circle extends beyond unit distance of the origin, and the Gers̆gorin theorem then fails to bound the spectral radius to less than one. For example, this occurs in the case of a simple lag in adult emergence, where σai=1 for a=0,,δi-1. Application of the theorem to the transposition of the Jacobian matrix would give rise to consideration of the deleted absolute column sums. However, deleted absolute column sums of J that include the partial derivatives of the per capita growth function must similarly account for the adult stage daily survival probabilities.

More can be said, however, if the graph of J is also taken into account. The following terminology is needed (Horn and Johnson 1985, Ch.6); see also Patten (1985) for an ecological application. The directed graph of n×n matrix J has a directed arc (edge) between a pair Pi and Pj of the n nodes P1,,Pn if and only if Jij0. A directed path is a sequence of arcs Pi1Pi2, Pi2Pi3, Pi3Pi4, , with length defined as the number of arcs in the sequence. A cycle is a directed path that starts and ends at the same node such that no other node appears more than once; this is sometimes named a simple (directed) cycle. A nontrivial cycle γ excludes cycles of length one. If there exists a directed path of finite length that begins at Pi and ends at Pj for every pair {Pi,Pj} of distinct nodes in the directed graph of J, then the directed graph is then said to be strongly connected.

The definitions of (weakly or strongly) connected graphs and (weakly) irreducible matrices are also required. Let |B| denote the matrix with entries equal to the absolute value of the entries of B. A matrix B with all positive (nonnegative) entries is denoted by B>0 (B0). (Horn and Johnson 1985, Ch.6) show the equivalence between the following statements for an n×n matrix B:

  1. B is irreducible,

  2. (I+|B|)n-1>0, and

  3. the directed graph of B is strongly connected.

Let α1,,αr form a partition of {1,,n}=i=1rαi such that αiαj= for ij. Let the submatrices B(αi,αj) indexed by rows αi and columns αj of B with 1i,jr form a partition of the matrix B. The matrix B is reducible if either n=1 and B=0, or a permutation P exists to triangular block form,

PBP-1=B(α1,α1)000B(α2,α1)B(α2,α2)00B(αr,α1)B(αr,α2)B(αr,αr), 13

where the diagonal blocks B(αw,αw) for w{1,,r} are square, and either irreducible or a zero entry. These diagonal blocks correspond to the classes of B, where a class is a set of nodes that communicate (Berman and Plemmons 1994). Two nodes Pi and Pj, ij, communicate if there is a directed path from Pi to Pj, and also from Pj to Pi. An irreducible matrix B is a triangular block matrix with a single block, and an irreducible matrix is not reducible.

Additionally, a matrix B is said to be weakly irreducible if C=(I+|B|)n-1 has at least one nonzero off-diagonal entry Cij, ij, in each row i=1,,n such that Cji is also nonzero. The matrix B is weakly irreducible if and only if its directed graph is weakly connected such that a nontrivial cycle exists between each node and another node. Note that an irreducible n×n matrix B with n>1 is weakly irreducible.

The following theorem (Brualdi 1982) uses the weakly connected property. Let C(B) denote the set of all nontrivial cycles γ in the directed graph of B.

Theorem 2

(Brualdi) If the n×n matrix B is weakly irreducible, then

s(B)γC(B)v:Piγ|v-Bii|PiγRi(B).

If a cycle γ of length k>1 includes nodes Pi1Pi2, , PikPik+1 with Pi1=Pik+1 then the index i=i1,i2,,ik in the products of the above theorem.

Theorem 3

Assume that the system of Eq. (7) with adult stages x(t)=yδM(t) has an interior equilibrium, x=yδM>0. Let the Jacobian matrix of Eq. (12) with dimensions (m+iMδi)×(m+iMδi) be expressed in the triangular block form of Eq. (13) with partition α1,,αr. Let DwM denote the set of species with nodes in αw. If, for all iDw and w{1,,r},

Gi(x)+xiGi(x(t))xi(t)x(t)=x+jDw\ixiGi(x(t))xj(t)x(t)=xa=0δi-1σai<zi,

then the equilibrium is locally asymptotically stable.

The proof of the above theorem is given in Appendix A.1.

Theorem 3 is the multispecies generalisation of Eq. (9). The theorem does not explicitly depend on the lags δ except through the product of survival probabilities of the immature stages. Theorem 3 uses Theorem 2 that depends on the weakly irreducible condition. The weakly irreducible condition for J holds by Eq. (12) if δi1 for all iM. An irreducible J is also weakly irreducible. For completeness, a sufficient condition for irreducibility and the strongly connected property follows.

Lemma 1

If the partial derivatives of the zero age classes with the mature age classes in Eqs. (10) and (11) evaluated at equilibrium are all non-zero, then J is irreducible.

The proof is in Appendix A.2.

Sufficient Conditions for Local Stability of Boundary Equilibria

Let x^=[x,x] denote a boundary equilibrium, where x=0 is an r-dimensional vector with r{1,2,,m}. The boundary equilibria are those where the positive equilibrium abundances in x>0 form a p-dimensional vector, p=m-r. If x is m-dimensional then x^=0 is the trivial equilibrium. A sufficient condition for the local asymptotic stability is provided by application of Theorem 3 to the Jacobian matrix evaluated at x^. However, if the per capita population growth functions satisfy a certain condition then more can be said.

Let J^ denote the Jacobian matrix of Eq. (12) evaluated at an equilibrium where at least one of the species has zero abundance. Let J and J denote the block submatrices on the main diagonal of J^ conformally partitioned with x^ such that the first r rows correspond to the r species with zero equilibrium abundances.

Theorem 4

Assume that Eq. (7) for iM has the property that

x^i=xi=0x^iGi(x^)=0,

and assume ρ(J)<1. The equilibrium x^ is locally asymptotically stable if

Gi(x^)a=0δi-1σai<zi,i{k:x^k=xk=0}.

The proof of the above theorem is found in Appendix A.3.

The condition on the per capita growth function Gi of an introduced or invading species with zero equilibrium abundance xi says that its population cannot grow in the absence of any reproducing individuals for species i at the boundary equilibrium. The assumption on the spectral radius ρ(J) corresponds to a locally stable interior equilibrium x for the p species with non-zero equilibrium abundances in the absence of the r species with zero equilibrium abundances, x.

Multispecies Competition with Delayed Maturation

For an important specific example of Eqs. (7) and (8) with yδM(t)=x(t), consider the per capita density dependent growth function defined by

Gix(t-δi)=λi1+qi-1kMAikxk(t-δi),iM, 14

where A0 is an m×m matrix with positive main diagonal entries and nonnegative off-diagonal entries. The matrix A defines the intraspecific and interspecific competitive interactions that intensify with greater numbers of reproducing adults both within and among species. By construction, a positive entry Aij>0 indicates a negative effect of species j on species i. Each entry of the nonnegative matrix A defines the strength of competitive density dependence exerted by species j after duration δi in the immature life history stage of species i. The off-diagonal entry Aij defines the strength of density dependence of species j on species i relative to the intraspecific density dependence, Aii, on the species i. The m-dimensional vector λ=[λ1,,λm] of density independent fecundity rates specifies the per capita number of new recruits generated by the adults of each species in the absence of density dependence that would occur if A=0. The ith row of A assesses the relative magnitudes of each species on the population growth of species i. The parameter qi>0 determines the overall impact of both intraspecific and interspecific density dependence on the population growth rate of species i.

Remark 1

Without loss of generality, the specification Aii=1 for iM in the CDM model defines qi-1 as the strength of intraspecific density dependence in the denominator of Eq. (14).

The general delayed model with structure defined by Eqs. (7), (8) and (14) and m1 is for convenience referred to here as the Competitive Delayed Multispecies (CDM) model. The nondelayed version of Eq. (8) with σ=0 and per capita growth function defined by Eq. (14) is a generalisation of models that have a long history in mathematical biology. For m=1, it is the influential Beverton-Holt model (Beverton and Holt 1957). For m=2, it is the Leslie-Gower model (Leslie and Gower 1958). For m>1, the non-delayed model is known as the competitive multispecies Leslie-Gower model (Sacker 2011; Jiang and Niu 2017). A single species delayed version appears in Fisher and Goh (1984) and a multispecies competitive system with common delay δi=δ for all iM appears in Hosack et al. (2023).

Before proceeding with multispecies analysis, the stability properties for the case m=1 are now provided. If λ1>1 in the single species model (m=1) without delay (δ1=0), then the model is of Beverton-Holt form with a positive equilibrium, x1=q1(λ1-1)/A11, that is globally asymptotically stable (Elaydi 2005); if 0<λ1<1 then the zero solution is asymptotically stable. The delayed version of this model with δ1>0 from Eqs. (6) and Eq. (14) multiplies the fecundity rate by the product of juvenile stage survival probabilities. Application of the results of Fisher (1984) for the case of maturation delay (δ1>0) also multiplies the fecundity rate by a factor z1-1 in the corresponding non-delayed system of Eq. (3) given the per capita growth function of Eq. (14). Therefore, if λ1a=1δ1-1σa1>z1 in the delayed Beverton-Holt system, then its equilibrium x1=q1(z1-1λ1a=1δ1-1σa1-1)/A11 is both positive and globally asymptotically stable. The stability conditions for the single species model with or without delayed maturation do not depend on the parameters q1 and A11 that scale its positive equilibrium. However, unlike the non-delayed Beverton-Holt model, the stability condition for δ1>0 depends on both juvenile and adult stage survival probabilities.

Coexistence Equilibrium

The positive equilibrium with species-specific delays is derived. Let the m-dimensional vector x(t) denote the reproducing adult abundances for the set of species M at time t, such that xi(t)=yi(t,δi) for iM. Let x>0 denote the interior equilibrium abundances of the reproducing adult age classes, and define the density independent rate of adult recruitment of species i by λ~i=λia=0δi-1σai. If δi=0 then λ~i=λi (Sect. 2). If the positive equilibrium exists, then Eqs. (8) and (14) obtain

xi=σδiixi+λ~ixi1+qi-1kMAikxk,iM. 15

Using the daily probability of mortality zi=1-σδii and rearranging terms gives jMAijxj=λ~izi-1qi for all iM, or equivalently Ax=diag[λ~-z]diag[z]-1q, where diag[v] is the d×d diagonal matrix with main diagonal entries corresponding to the entries of a d-dimensional vector v and zeroes in the off-diagonal entries. For nonsingular A, the equilibrium abundances are

x=A-1diagλ~-zdiag[z]-1q. 16

A feasible interior equilibrium of Eq. (15) for an arbitrary number of species m1 corresponds to a positive equilibrium x>0 that is unique by Eq. (16).

Often the density independent parameters λ~ and z that relate to life history parameters within a species have comparatively more information available than the more uncertain density dependent parameters A and q that govern relationships among species. What can be generally said about the feasibility of the coexistence equilibrium if the exact values of q are unknown or uncertain? The following proposition sets sufficient conditions on A such that the interior equilibrium is feasible if q>0 are free parameters.

Lemma 2

If the feasible interior equilibrium exists, x>0, given λ~>z>0 and nonsingular A with all positive entries on the main diagonal, then q>0 exists.

The proof is found in Appendix A.4.

The condition λ~>z corresponds to positive population growth rates in the absence of competition, and the condition z>0 corresponds to non-negligible density independent mortality of mature adults. The condition of all positive main diagonal entries of A corresponds to the presence of intraspecific competition for all species. Lemma 2 then guarantees that a positive q exists for any feasible interior equilibrium x>0.

Jacobian Matrix at Coexistence Equilibrium

Sufficient conditions for the global stability of the positive equilibrium of the non-delayed version of the CDM model have been presented (Sacker 2011; Jiang and Niu 2017; Hou 2021). For the single species case m=1 with delay δ1>0, sufficient conditions for the global stability of the positive equilibrium x1=q1(λ1-z1)/z1 have been provided (Fisher and Goh 1984). The positive equilibrium x>0 of the general CDM model, if it exists, is locally asymptotically stable if the moduli of all eigenvalues of the Jacobian matrix of Eq. (12) evaluated at the feasible interior equilibrium are less than one. For species i with maturation delay δi>0, the partial derivatives are

haiy(t)ybj(t)=σbiifi=j,a=1,,δi,b=a-1,σδiiifi=j,a=b=δi,λi1-qi-1Aiiyδii(t)1+qi-1kMAikyδkk(t)1+qi-1kMAikyδkk(t)ifi=j,a=0,b=δj,-λiqi-1Aijyδii(t)1+qi-1kMAikyδkk(t)2ifij,a=0,b=δj,0otherwise. 17

For species i without delayed maturity (δi=0), the partial derivatives are

h0iy(t)yaj(t)=σ0i+λi1-qi-1Aiiy0i(t)1+qi-1kMAikyδkk(t)1+qi-1kMAikyδkk(t)ifi=j,a=δj,-λiqi-1Aijy0i(t)1+qi-1kMAikyδkk(t)2ifij,a=δj,0otherwise. 18

Let J denote the Jacobian matrix of partial derivatives defined by Eqs. (17) and (18). Note that Eq. (16) is equivalent to

1+qi-1jMAijxj=λ~izi,iM. 19

Assume that A is nonsingular and that intraspecific density dependence occurs for all species. Then a positive q>0 exists for a corresponding feasible interior equilibrium x by Lemma 2. The parameters in q appear only in the zero age classes of Eqs. (17) and (18). If x>0 in Eq. (16) then Eq. (19) is applied so that the parameters q are implicit in the entries expressed as quotients of the equilibrium values. For the zero (a=0) age class of each species iM, Eqs. (17), (18) and (19) yield partial derivatives evaluated at the interior equilibrium x of

h0iy(t)yδjj(t)y(t)=y=ziλiλ~i-λi(λ~i-zi)λ~i2AiixikMAikxkifi=jandδi>0,σ0i+zi1-(λi-zi)λiAiixikMAikxkifi=jandδi=0,-ziλi(λ~i-zi)λ~i2AijxikMAikxkifij,0otherwise. 20

The Jacobian matrix J evaluated at the feasible interior equilibrium is then given by Eq. (12).

Numerical Evaluation of Stability for All Coexistence Equilibria

The derived J enables two useful applications without knowledge of q that are usefully applied in the empirical application of Sect. 4: i) the stability of an interior equilibrium can be calculated given x, and ii) the stability of all possible feasible interior equilibria in fact only require consideration of the equilibrium relative abundances of the m species on the m-1 simplex. These results are useful because otherwise the typically unknown or uncertain q scales the magnitudes of the species abundances at a feasible interior equilibrium such that xR+m. For i), the Jacobian matrix evaluated at the feasible interior equilibrium by Eq. (20) shows that the typically unknown vector q is accounted for in the stability analysis given a positive equilibrium x. For ii), the feasible equilibrium abundances appear as ratios in Eq. (20). To explore the entire feasible space of the Jacobian evaluated at any interior equilibrium x>0, define the total abundance of an interior equilibrium by xT=kxk. Thus the relative abundance of the species k is pk=xk/xT>0, that is, xk=pkxT with kpk=1, such that Aijxj/kMAikxk=Aijpj/kMAikpk for all i,jM in Eq. (20). Numerical evaluation of the eigenvalues of J for all possible interior equilibria is then implemented through exploration of the simplex {pi:iM,pi>0,kMpk=1} as the feasible region given only parameters A, λ and σ.

Note that there are infinitely many equilibria represented within the simplex. Each point in the simplex corresponds to the equilibrium relative abundances of the species, or fractional contribution of each species to the total abundance aggregated over all species at the equilibrium. The total abundance of an interior equilibrium xT is a strictly positive real number. Hence the possible equilibria that correspond to a single point in the simplex form an infinite set, and this is true of every point in the simplex that together form an infinite set. However, the set of eigenvalues or spectrum s(J) for a given interior equilibrium x depends only on the species equilibrium relative abundances and not the total abundance. Therefore, the condition that the moduli of all eigenvalues of J are less than one can be numerically checked to assess local asymptotic stability of any x>0 by consideration of its corresponding unique point in the simplex.

Sufficient Condition for Stability of Coexistence Equilibrium

Proposition 1

Assume that λ~>z>0. If

Aii>jM\iAij,iM,

then any interior equilibrium x>0 of the CDM model is feasible with an associated q>0, and the interior equilibrium is locally asymptotically stable.

The proof of the proposition is in Appendix A.5.

The constraint of Proposition 1 shows that if interspecific competition is not greater than intraspecific competition, then the coexistence equilibrium exists and is locally stable. The condition does not depend on the species-specific delays.

Sufficient Condition for Stability of Alternative Equilibria

By the uniqueness of the interior equilibrium of Eq. (16), if it exists, the only other possible equilibria for the CDM model are the boundary equilibria and the trivial equilibrium.

Corollary 1

Assume that the condition of Proposition 1 applies to guarantee stability of the interior portion x>0, of the equilibrium, if present, such that ρ(J)<1. Then a boundary equilibrium x^=[x,x], where x=0, or trivial equilibrium, where x^=x=0, is locally asymptotically stable if

λ~i-zizi<qi-1kMAikx^k=qi-1k{l:x^l=xl}Aikxk,i{j:x^j=xj=0},

where the empty sum in the case of the trivial equilibrium is zero.

The proof is in Appendix A.6.

The sufficient condition for the local stability of the interior equilibrium only depends on the equilibrium through the relative abundances of the species (Sect. 3.3); however, the corresponding sufficient condition for the stability of the boundary equilibrium in the above corollary depends on the actual non-zero equilibrium abundances x of the established species. The boundary or trivial equilibrium is locally asymptotically stable if the fecundity rate at the conclusion of the immature life history phase is less than the probability of adult mortality.

Applications

The above properties of the CDM model are now used to provide estimates for unknown density dependent parameters q and A. In Sect. 4.1, a popular descriptive approach to estimate niche overlap is summarised. If coerced to define the entries of A, this descriptive approach endows a special structure such that Lemma 2 applies, and so q>0 is then also available. However, the niche overlap method is not strongly linked to a dynamic model framework. Therefore, Sect. 4.2 explores an alternative approach that estimates A and q based on the dynamic properties of the CDM model. The optimisation uses the spectral radius to determine the resilience of the ecosystem in terms of the relative dampening or amplification of perturbations away from the interior equilibrium. The level of resilience, which is maximised by minimising the spectral radius, is balanced against a maximisation of the average interspecific competition strength among species, which is destabilising by Proposition 1. The idea is that i) observed species abundances are more likely to persist in ecosystems with greater resilience, and ii) species seek to increase competitive advantage over shared resources. The approach requires only the relative abundances of the species rather than actual abundances that can be more difficult to obtain (Sinka et al. 2016). For example, models of habitat overlap and segregation among species sometimes require genetic methods to identify species from subsamples of field populations (Tene Fossog et al. 2015). Such analyses often use relative abundance because the actual abundances of the species are unobserved. The descriptive and objective approaches are compared for an example in Sect. 4.3.

Relationship between CDM Model and Niche Overlap Indices

It has long been recognised that interspecific density dependence can be difficult to estimate. (Beverton and Holt 1957, p.169) for example suggest that “a true measure of competition requires considerable knowledge of the dynamics of the system”. The Leslie-Gower model was an early attempt to provide a mechanistic model with estimable density dependence for a two-species extension of the Beverton-Holt model of density dependent population growth (Leslie and Gower 1958). Later, various measures of niche overlap indices were introduced into the ecological literature that were loosely based on the continuous Lotka-Volterra model (May 1975). Pianka (1974), for example, proposes αij=rRpirpjrrRpir2rRpjr2-1/2 as a measure of niche overlap between species i and j, where pkr is the proportion of the resource r from the set of resources R used by species k. The resulting αij are proposed as the “canonical” estimator of interspecific competitive coefficients (May 1975), where in a competitive community of m species, it is assumed that Aij=αij is a density dependent coefficient. The resulting m×m interspecific competition matrix A constructed by this method is symmetric and positive semidefinite (May 1975).

The CDM model benefits in two ways from assuming α=A. First, the main diagonal entries of A equal one. The unknown qi-1 in the density dependent growth functions Gi(x(t-δi)) of Eq. (14) are therefore interpreted as setting intraspecific density dependence on the per capita scale for species i as in Remark 1. Second, the rank of a symmetric matrix corresponds to the number of its non-zero eigenvalues. Therefore, if the competitive relationships or niches among the species differ such that the rows (columns) of A are linearly independent, then the matrix A has full rank m and all positive eigenvalues. It would be reasonable for different species to interact with their environments differentially, and linear independence of rows (columns) of A would typically be expected. The matrix A is then nonsingular with intraspecific density dependence present for all species. The unique interior equilibrium then exists by Lemma 2 if also λ~>z. So the choice of parameterisation of A by the Pianka index guarantees a feasible interior equilibrium for the CDM model.

Yet Pianka (1974) explicitly cautions that α only measures “niche overlap”, not competition, because species can adopt strategies to decrease competitive interactions even as their niche overlap increases. Another criticism of assuming α=A is that the coefficients α are typically based on observations of relative abundances among species, whereas the unobserved competitive coefficients A are the real measure of interspecific and intraspecific density dependence on population growth rates. Thus, a field survey that shows strong positive correlation of relative abundances among species across sites may suggest strong competition because α has large off-diagonal entries, whereas in fact the species may exploit distinct non-overlapping microhabitats within each site. In this example, the competition matrix A is a diagonal matrix that reflects the absence of interspecific competition so that clearly αA.

Optimised Competition

The results available for the CDM model suggest an alternative approach to estimating the strength of competition. Estimates for density independent adult mortality rates z and per capita reproduction rates λ~, as defined in the delayed maturity model, are generally available in the literature, but estimates of the density dependent parameters q and A are comparatively lacking. Estimates of the former parameters often depend on a mix of field observations or laboratory studies, and so are more attainable than the latter parameters that determine the magnitude of density dependence. Assume that an estimate of the adult abundances x¯>0 is available for the interior equilibrium, so that x¯x. The estimate x¯ may for example be derived from estimated mean adult abundances of the species. Here, an estimate of the competition matrix A is derived based on the stability properties of the dynamic system. This ecologically and dynamically motivated estimate is available for the CDM model in the absence of estimates for q. The optimisation approach can also be viewed as a hypothesis for how competing species might set competitive interaction strengths at a stable, and potentially observable, configuration.

Whereas the condition for local asymptotic stability depends on the comparison of the spectral radius with the threshold of one, the following interpretation also considers the magnitude. This conceptual approach uses the spectral radius to assess the amplification potential for perturbations away from equilibrium, and is conceptually based on the analogous construction for the reproduction number of nonnegative populations (Diekmann and Heesterbeek 2000). The magnitude of the spectral radius is also used in ecology as a measure of the “resilience” of a stable equilibrium in a system of difference equations (Beddington et al. 1976). Resilience is a measure of species persistence in ecosystems subject to change and disturbance (Holling 1973) and is defined as the rate of return to a stable equilibrium or the inverse of the return time after a perturbation (Nakajima and DeAngelis 1989). Beddington et al. (1976) defines the asymptotic return time to a stable equilibrium as

TR=1-ρJ-1.

A system of species with greater resilience and shorter return time TR is more likely to persist in the face of perturbations with corresponding decreased risk of species extinctions (Beddington et al. 1976).

Let ϕ denote the vector of deviations for all age classes of all species from the interior equilibrium caused by a local perturbation. The magnitude of this deviation can be summarised by the vector norm ||ϕ||1=i|ϕi|. The corresponding matrix norm for a n×n square matrix W is ||W||1=i,j=1n|Wij|=maxϕ0||Wϕ||1/||ϕ||1 that assesses the maximum amplification of the deviation from the interior equilibrium. The spectral radius of W for a matrix norm ||·|| is defined by ρ(W)=limt||Wt||1/t. Also, limtWt=0 if and only if ρ(W)<1 (Horn and Johnson 1985, Theorem 5.6.12). The spectral radius is therefore interpreted as a long term average of the maximum amplification away from the interior equilibrium per unit time t following a perturbation. For use in the objective function of an optimisation, note that the spectral radius is a continuous function of a matrix W. Not only is the spectral radius related to the matrix norm through the long term average amplification, but any matrix norm also provides an upper bound on the spectral radius, ρ(W)||W||. The matrix norm and spectral radius are thus closely linked. The spectral radius for a stable system will also be bounded between zero and one.

Here, both the competition matrix A and the long term average per unit time t multiplication number (amplification) of the CDM model is optimised for the observed x¯. The interior equilibrium of the CDM model, if it exists, is unique by Eq. (16). The joint optimisation maximises competition, or niche overlap if these terms are considered synonymous, while minimising the spectral radius ρ(J) that defines the long term average amplification of perturbations away from the interior equilibrium, x. If ρ(J)<1 then the deviations will decrease over time such that the adult abundances eventually return to x. Otherwise, the deviations may continue to increase and the species abundances will not return to the interior equilibrium.

The entries of the Jacobian matrix for the CDM model depend only on the species equilibrium relative abundances and the given parameters z and λ~ (Sect. 3.3). Assume that the density independent fecundity and survival rates are given such that population growth will occur in the absence of competition, that is, λ~>z. Let the Jacobian of the CDM model as a function of species abundances x and competition matrix A be denoted by J(x,A). For example, J=J(x,A) in Eq. (12) for the CDM model evaluated at the interior feasible equilibrium. By Eq. (20), J(x,A)=J(p,A) where p=x/iMxi. The following minimisation problem is constructed:

A^=argminASm[ρ(J(x¯,A))-1]i,j=1mAij,

where Sm is the set of m×m candidate matrices for A and x¯ is the vector of estimated equilibrium abundances.

The conjecture encapsulated by this objective function is that i) it will be favourable to species i if it can outcompete its competitors for limited resources and so increase Aij, ij, and ii) species are more likely to persist and be observed near the interior equilibrium in a system with greater resilience and shorter return time. That is, a system with a larger spectral radius and hence larger average amplification of perturbations away from equilibrium will be less likely to persist and be observed near the equilibrium than one with a small spectral radius, where perturbations are relatively attenuated. The objective function also allows multiplication by a constant without effect on the optimisation. For example, multiplication by m-2 allows interpretation of the summation in the objective function as a measure of the average competition strength defined by the mean of the entries of A.

Note that the choice of objective function optimises both increased competition and increased resilience of the equilibrium estimate x¯. The objective function does not simply seek to minimise the spectral radius at that point: The latter approach would be expected to favour diagonal A^ because decreasing interspecific competition is stabilising as seen in Proposition 1. For large systems and non-symmetric or unconstrained Sm the number of unknowns would increase at the rate m2 and so outpace the information provided by the m-dimensional vector x¯. It is conceivable then that the objective function may not have a single global optimum. In other words, A^ may not be identifiable. In such cases, it may be useful to include constraints on the candidate set of matrices Sm as informed by prior knowledge or theoretical justification.

A low dimensional numerical example is provided below. In this example, the candidate set for optimisation includes only the nonnegative matrices with main diagonal entries equal to one with reference to Remark 1. Lemma 2 then applies so that a positive q is guaranteed for any feasible interior equilibrium given any choice of matrix B in this candidate set. Furthermore, the canonical structure of α described in Sect. 4.1 is then adopted so that Sm is the set of symmetric nonnegative matrices with main diagonal entries equal to one.

Example Application

Pombi et al. (2017) apply Pianka’s method (Sect. 4.1) that uses field estimates of relative abundances among species to estimate the niche overlap of three species of important malaria mosquito vectors within the Anopheles gambiae sensu lato (s.l.) species complex: An. arabiensis (Aa), An. coluzzii (Ac) and An. gambiae sensu stricto (Ag). For this analysis, the CDM model is applied so that x(t) corresponds to adult females of the above three species. Additionally, Pombi et al. (2017) provide the total observed abundances across three sites in Burkina Faso. These estimates are halved to account for an approximate 1:1 sex ratio, and are summarised here with the estimated niche overlaps from Pombi et al. (2017): graphic file with name 11538_2025_1515_Figa_HTML.jpg For this example, it will be assumed that the population abundance estimate x¯ approximates the interior equilibrium x of the CDM model (Sect. 4.2). The fecundity rates λ~, adult survival probabilities σ and delays δ are assumed similar for all three species in the An. gambiae s.l. complex using estimates provided by North and Godfray (2018). For iM, the duration of the immature period is set to δi=10, maximum fecundity rate is λ~i=9/2 per female per day (the oviposition rate estimate is halved since this CDM model only applies to females with assumed 1:1 sex ratio) and adult probability of mortality is zi=0.125 per day. Rates of hybridisation among the three species are assumed negligible. In this example CDM model, the survival probabilities are absorbed into the fecundity parameter λ~ so that σaii=1 for ai=1,,δi-1 with σδii=1-zi for iM. This specification corresponds to a latent lagged population of immatures. See Hosack et al. (2023) for an elaboration that uses the above estimate for A=α with interspecific hybridisation in a risk analysis of a genetic biocontrol application.

Let A=α denote the assumption that the competition coefficients are identifiable with niche overlap indices estimated by the Pianka method, as suggested by May (1975) and discussed in Sect. 4.1. The matrix A=α is nonnegative and nonsingular, and so the interior equilibrium is feasible by Lemma 2 with the knowledge that λ~>z>0 from the above estimates, and q>0 is then available from Eq. (16). The sufficient condition for local asymptotic stability of the interior equilibrium provided by Proposition 1 is not satisfied by A=α. However, the numerical approach of Sect. 3.3 applies, and Figure 1a shows that all numerically evaluated interior equilibria in the simplex, which correspond to different parameterisations of qR+m, are locally asymptotically stable for A=α. The abundance estimate has corresponding relative abundance vector p=x¯/xtot=[0.34,0.42,0.24], where xtot=ix¯i. This point does not correspond with the configuration of relative abundances that minimises the spectral radius. The spectral radius approaches one as the interior equilibrium approaches a boundary. Figure 1b shows the return trajectory to equilibrium after a random perturbation.

Fig. 1.

Fig. 1

Spectral radius for all possible interior equilibrium species abundances given Pianka niche overlap estimate A=α (top, a) and optimised estimate A=A^ (bottom, c). In (a) and (c), points show the location of equilibrium with lowest spectral radius () and the location of the abundance estimate x¯ (×). Note change in colour legend of (a) versus (c) to aid visualisation. The return to equilibrium after a perturbation that decreases the species abundances by 33%, 28% and 13% for the three species Aa, Ac and Ag is shown for A=α (top, b) and A=A^ (bottom, d). In (b) and (d), points at 365 days denote the equilibrium values of each species, x¯

For comparison, the estimate A^ is presented with the same abundance estimate x¯x (and relative abundances p) and proportional perturbations away from equilibrium. The set of possible competition matrices S3 is constrained to symmetric matrices with ones along the main diagonal for comparison with the niche overlap method. The resulting optimised estimate for competition is graphic file with name 11538_2025_1515_Figb_HTML.jpg The above estimates are roughly half the magnitude of the estimates provided by the niche overlap method, α, presented in Pombi et al. (2017). The competitive system has an interior feasible equilibrium by Lemma 2 that is locally asymptotically stable by Proposition 1.

The basin of attraction for the optimised estimate A=A^ is deeper in Figure 1c compared to the niche overlap estimate, and the minimum spectral radius is estimated to be near the abundance estimate. The optimisation decreases the spectral radius at x¯ while increasing the average strength of competition (Sect. 4.2). The optimisation thereby shifts the bottom of the “bowl” formed by the basin of attraction for the interior equilibrium x towards the estimate x¯. This latter result, of course, may not always exactly correspond to x¯ given the constraints imposed on the set of possible candidate matrices S3 for fixed λ~ and z. For m=3 the number of unknowns given symmetric A with fixed main diagonal is the same as the number of species. The smaller spectral radius given optimised estimate A^ corresponds to a faster return time to equilibrium following perturbation (Figure 1d) compared to the niche overlap estimate (Figure 1b). The difference on the logarithmic scale is most apparent for An. arabiensis and An. gambiae s.s. that approach their equilibrium values noticeably more quickly in the optimised case. This optimal configuration reflects faster rates of return of species abundances towards x¯ with reduced spectral radius in its linearised approximation compared to the niche overlap system, and so the perturbation is more dampened in the optimised system with greater resilience.

Conclusion

Sufficient conditions are presented for the local asymptotic stability of feasible interior equilibria within general multispecies systems of difference equations with delayed maturity. Interspecific competition, mutualism, predation, and commensalism or amensalism are accommodated by the general model framework. The competitive delay multispecies (CDM) model is presented as an important specific example. A sufficient condition is provided for stability of coexistence in the CDM model that only requires stronger intraspecific competition relative to interspecific competition, regardless of delay. Moreover, evaluation of the simplex of relative abundances can exhaustively assess the stability properties of a system described by the CDM model given only competition A, fecundity λ and survival probabilities σ. In cases where competition A is unknown, a technique is provided to predict an optimal set of density dependence coefficients. A numerical illustration is provided for a low dimensional system, but future research would be needed to evaluate its suitability for very large systems.

Acknowledgements

The authors thank Lawrence Forbes and the anonymous reviewers for helpful comments. This work was supported, in whole or in part, by a grant to the Foundation for the National Institutes of Health from the Bill & Melinda Gates Foundation [INV-008525].

Appendix

Proof of Theorem 3

Proof

Each set D1,,Dr is formed by a unique set of |Dw|1 species such that w|Dw|=|M|. Clearly, the spectrum s(J) with J in the triangular form of Eq. (13) is the union of the eigenvalues of each matrix J(αw,αw) with dimensions (|Dw|+iDwδi)×(|Dw|+iDwδi) that is irreducible or a zero entry for w{1,,r}. The condition for local asymptotic stability is then ρ(J(αw,αw))<1 for w{1,,r}.

If |Dw|=1 then Dw consists of a single node of species i that does not form a cycle with any other node, and so δi=0. By Eq. (11), if

Gi(x)+xiGi(x(t))xi(t)x(t)=x<1-σδii=zi,iDw,|Dw|=1,

then ρ(J(αw,αw))<1.

If |Dw|>1 then each species iDw has either age structure, δi>0, or a nontrivial cycle with at least one other species jDw\i, or both. Let γi denote a cycle of minimum length that incorporates all age classes within species iDw. For iDw with |Dw|>1, let Γi denote the product of deleted absolute row sums that corresponds to γi,

Γi=PkγiRkJ(αw,αw)=Gi(x)+xiGi(x(t))xi(t)x(t)=x+jDw\ixiGi(x(t))xj(t)x(t)=xa=0δi-1σai,iDw.

Among the rows of J(αw,αw) that contribute to the above Rk(J(αw,αw)) of Γi, the only non-zero diagonal entry contributed by species i is σδii. The matrix J(αw,αw) is irreducible and hence weakly irreducible. Thus, a necessary condition for the bound on the spectral radius to be less than one is the condition

Γi<1-σδii=zi,iDw,

so that the maximum distance from the origin to the boundary of the eigenvalue region associated with γi by Theorem 2 is less than σδii+zi=1. The nodes included in cycle γi must also be included in any larger cycle that additionally incorporates any set Dw\i of alternative species that communicate with species i. Moreover, each species dDw\i contributes the product Γd associated with the minimal non-trivial cycle γd of that species, so that the overall product of absolute deleted row sums for any subset of species EDw is ΓE=iEΓi. If the sufficient conditions 0<Γi<zi1 are met for all iDw, then ΓE<1 for any EDw and ρ(J(αw,αw))<1.

Proof of Lemma 1

Proof

Let D denote the directed graph of J. For δi>0 a directed path in D exists that includes all nodes of species i by the delayed age structure of Eq. (7) because σaii>0 for ai=0,,δi-1. If the partial derivatives of Eq. (10) and (11) are non-zero for all cross partials of the zero age classes with the mature age classes, then Eq. (12) shows that a cycle in D also exists that includes each node within a species to any other node, either within the species or in another species. D is then strongly connected and J is irreducible.

Proof of Theorem 4

Proof

The matrix J^ may be permuted to have block structure

J^=J0J

that is conformally partitioned with respect to x^=[x,x] and with zero entries in the upper right quadrant from Eq. (12), although not necessarily the lower left quadrant. The spectrum of eigenvalues s(J^) is therefore the union of the spectra s(J)s(J). It is given that the maximum modulus of the eigenvalues in s(J) is less than one. Again by Eq. (12), J is a block diagonal matrix with each of the r blocks corresponding to a species i with zero equilibrium abundance for the adult class, xi=0, i=1,,r. The spectrum of eigenvalues for J is then the union of the spectra for each block. The largest cycle in each block is also the minimal cycle that includes all age classes. The condition of the proposition is sufficient for the moduli of eigenvalues to be less than one across the r blocks by application of Theorem 3 to each block.

Proof of Lemma 2

Proof

The interior equilibrium is unique by Eq. (16), and so it suffices to show that the solution for q=diag[z]diagλ~-z-1Ax is positive given A, λ~, z and positive x>0. The m×m matrix diag[z]diagλ~-z-1 is diagonal with positive entries along the main diagonal, and so q>0 if Ax>0. If Aii>0 for all iM then k=1mAikxkAiixi>0 for all iM since x>0 and A0.

Proof of Proposition 1

Proof

The constraint given the nonnegativity of A ensures that the main diagonal entries of A are positive, and so if the constraint holds then it is also true that A is diagonally dominant such that |Aii|>jM\i|Aij| for all iM. The latter constraint is a known result that ensures A is invertible (see Horn and Johnson 1985, Corollary 5.6.17. Lemma 2 then applies, and so also Eqs. (16) and (20) hold for q>0 corresponding to x>0. Application of Theorem 3 to the CDM model by Eqs. (17) and (20) shows that the interior equilibrium x>0 is locally asymptotically stable if

ziλiλ~i1-λ~i-ziλ~iAiixikMAikxk+jM\iλ~i-ziλ~iAijxikMAikxka=0δi-1σai<zi,iM. 21

Given constraints A0, 0<zi<1 and λ~i-zi>0, the difference within the absolute value in the above equation is always positive because 0<λ~i-zi<λ~i and 0<AiixikMAikxk. By the definition λ~i=λa=0δi-1σai, Eq. (21) is therefore equivalent to

λ~i-ziλ~i×xikMAikxk-Aii+jM\iAij<0,iM,

where the terms outside of the brackets on the left hand side are positive.

Proof of Corollary 1

Proof

The result follows from Theorem 4 applied to the CDM model with Lemma 2 in force because Eq. (14) has the property that x^i=xi=0x^iGi(x^)=0 for iM. The condition for local asymptotic stability from Theorem 4 is that |Gi(x^)|a=0δi-1σai<1 for all i{j:x^j=xj}, where λ~i=λia=0δi-1σai and Gi is defined by Eq. (14).

Funding

Open access funding provided by CSIRO Library Services.

Data Availability

The reproducible code and simulated data is publicly available at: https://github.com/csiro-risk-assessment/MultiSppMaturityDelayStability.

Footnotes

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

References

  1. Beddington JR, Free CA, Lawton JH (1976) Concepts of stability and resilience in predator-prey models. J Anim Ecol 45:791–816 [Google Scholar]
  2. Berman A, Plemmons RJ (1994) Nonnegative Matrices in the Mathematical Sciences, Volume 9 of Classics in Applied Mathematics. Philadelphia: Society for Industrial and Applied Mathematics. Republication of first edition by Academic Press, 1979
  3. Beverton RJH, Holt SJ (1957) On the Dynamics of Exploited Fish Populations. Number 11 in Fish and Fisheries Series. Republished by Springer Science+Business Media Dordrecht, 1993
  4. Brualdi RA (1982) Matrices eigenvalues, and directed graphs. Linear and Multilinear Algebra 11:143–165 [Google Scholar]
  5. Clark CW (1976) A delayed-recruitment model of population dynamics, with an application to baleen whale populations. J Math Biol 3:381–391 [DOI] [PubMed] [Google Scholar]
  6. Diekmann O, Heesterbeek JAP (2000) Mathematical Epidemiology of Infectious Diseases. John Wiley & Son Ltd, Chichester, West Sussex, England [Google Scholar]
  7. Elaydi S (2005) An Introduction to Difference Equations (3rd ed.). Springer
  8. Fisher ME (1984) Stability of a class of delay-difference equations. Nonlinear Anal 8:645–654 [Google Scholar]
  9. Fisher ME, Goh BS (1984) Stability results for delayed-recruitment models in population dynamics. J Math Biol 19:147–156 [Google Scholar]
  10. Gers̆gorin S, (1931) Uber die abgrenzung der eigenwerte einer matrix. Izvestiya Akademii Nauk SSSR Seriya Matematicheskaya 1:749–754 [Google Scholar]
  11. Goh B-S (1980) Management and Analysis of Biological Populations. Elsevier [Google Scholar]
  12. Holling CS (1973) Resilience and stability of ecological systems. Annu Rev Ecol Syst 4:1–23 [Google Scholar]
  13. Horn RA, Johnson CR (1985) Matrix Analysis. Cambridge University Press, New York [Google Scholar]
  14. Hosack GR, Beeton NJ, Ickowicz A, Peel D, Wilkins A, Dambacher JM, Wickramarachchi A, McDonald M, Tay WT, Wilson L, Bauer D, Hayes KR (2023) Risk Assessment for Controlling Mosquito Vectors with Engineered Nucleases: Paternal Male Bias Construct. Report No. EP2022-4945. Hobart, Australia: CSIRO. 10.25919/2t8h-5k81
  15. Hou Z (2021) On existence and uniqueness of a modified carrying simplex for discrete Kolmogorov systems. J Differ Equations Appl 27:284–315 [Google Scholar]
  16. Jiang J, Niu L (2017) On the equivalent classification of three-dimensional competitive Leslie/Gower models via the boundary dynamics on the carrying simplex. J Math Biol 74:1223–1261 [DOI] [PubMed] [Google Scholar]
  17. Kuruklis SA (1994) The asymptotic stability of . J Math Anal Appl 188:719–731 [Google Scholar]
  18. La Salle JP (1976) The Stability of Dynamical Systems. Society for Industrial and Applied Mathematics, Philadelphia, Pennsylvania [Google Scholar]
  19. Leslie PH, Gower JC (1958) The properties of a stochastic model for two competing species. Biometrika 45:316–330 [Google Scholar]
  20. Levins R (1968) Evolution in Changing Environments. Princeton University Press, Princeton, New Jersey [Google Scholar]
  21. Liz E (2020) Clark’s equation: A useful difference equation for population models, predictive control, and numerical approximations. Qualitative Theory of Dynamical Systems 19:71 [Google Scholar]
  22. López VJ, Parreño E (2016) L.A.S. and negative Schwarzian derivative do not imply G.A.S. in Clark’s equation. J Dyn Diff Equat 28:339–374 [Google Scholar]
  23. May RM (1974) Stability and Complexity in Model Ecosystems, 2nd edn. Princeton University Press, Princeton, New Jersey [Google Scholar]
  24. May RM (1975) Some notes on estimating the competition matrix, . Ecology 56:737–741 [Google Scholar]
  25. Nakajima H, DeAngelis DL (1989) Resilience and local stability in a nutrient-limited resource-consumer system. Bull Math Biol 51:501–510 [Google Scholar]
  26. North AR, Godfray HCJ (2018) Modelling the persistence of mosquito vectors of malaria in Burkina Faso. Malar J 17:140 [DOI] [PMC free article] [PubMed] [Google Scholar]
  27. Papanicolaou VG (1996) On the asymptotic stability of a class of linear difference equations. Math Mag 69:34–43 [Google Scholar]
  28. Patten BC (1985) Energy cycling in the ecosystem. Ecol Model 28:1–71 [Google Scholar]
  29. Pianka ER (1974) Niche overlap and diffuse competition. Proceedings of the National Academy of Sciences USA 71:2141–2145
  30. Pombi M, Kengne P, Gimonneau G, Tene-Fossog B, Ayala D, Kamdem C, Santolamazza F, Guelbeogo WM, Sagnon N, Petrarca V, Fontenille D, Besansky NJ, Antonio-Nkondjio C, Dabiré RK, della Torre A, Simard F, Costantini C, (2017) Dissecting functional components of reproductive isolation among closely related sympatric species of the Anopheles gambiae complex. Evol Appl 10:1102–1120
  31. Sacker RJ (2011) Global stability in a multi-species periodic Leslie-Gower model. J Biol Dyn 5:549–562 [Google Scholar]
  32. Sinka ME, Golding N, Massey NC, Wiebe A, Huang Z, Hay SI, Moyes CL (2016) Modelling the relative abundance of the primary African vectors of malaria before and after the implementation of indoor, insecticide-based vector control. Malar J 15:142 [DOI] [PMC free article] [PubMed] [Google Scholar]
  33. Streipert SH, Wolkowicz GSK (2023) Technique to derive discrete population modelswith delayed growth. J Biol Dyn 17:2244987 [DOI] [PubMed] [Google Scholar]
  34. Tene Fossog B, Ayala D, Acevedo P, Kengne P, Ngomo Abeso Mebuy I, Makanga B, Magnus J, Awono-Ambene P, Njiokou F, Pombi M, Antonio-Nkondjio C, Paupy C, Besansky NJ, Costantini C (2015) Habitat segregation and ecological character displacement in cryptic African malaria mosquitoes. Evol Appl 8:326–345 [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

The reproducible code and simulated data is publicly available at: https://github.com/csiro-risk-assessment/MultiSppMaturityDelayStability.


Articles from Bulletin of Mathematical Biology are provided here courtesy of Springer

RESOURCES