A dynamical trichotomy for structured populations experiencing positive density-dependence in stochastic environments
Sebastian J. Schreiber

TL;DR
This paper develops a mathematical framework for structured populations with positive density-dependence and environmental randomness, revealing a trichotomy of extinction, unbounded growth, or probabilistic outcomes.
Contribution
It introduces a dynamical trichotomy for structured populations under stochastic positive density-dependence, extending understanding of long-term behaviors in such models.
Findings
Populations either go extinct, grow unbounded, or have probabilistic outcomes.
The models apply to spatially structured populations with Allee effects.
Results are demonstrated with age-structured populations facing mate limitation.
Abstract
Positive density-dependence occurs when individuals experience increased survivorship, growth, or reproduction with increased population densities. Mechanisms leading to these positive relationships include mate limitation, saturating predation risk, and cooperative breeding and foraging. Individuals within these populations may differ in age, size, or geographic location and thereby structure these populations. Here, I study structured population models accounting for positive density-dependence and environmental stochasticity i.e. random fluctuations in the demographic rates of the population. Under an accessibility assumption (roughly, stochastic fluctuations can lead to populations getting small and large), these models are shown to exhibit a dynamical trichotomy: (i) for all initial conditions, the population goes asymptotically extinct with probability one, (ii) for all positive…
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A dynamical trichotomy for structured populations experiencing positive density-dependence in stochastic environments
Sebastian J. Schreiber
Department of Evolution and Ecology, One Shields Avenue, University of California, Davis, CA 95616 USA
Abstract.
Positive density-dependence occurs when individuals experience increased survivorship, growth, or reproduction with increased population densities. Mechanisms leading to these positive relationships include mate limitation, saturating predation risk, and cooperative breeding and foraging. Individuals within these populations may differ in age, size, or geographic location and thereby structure these populations. Here, I study structured population models accounting for positive density-dependence and environmental stochasticity i.e. random fluctuations in the demographic rates of the population. Under an accessibility assumption (roughly, stochastic fluctuations can lead to populations getting small and large), these models are shown to exhibit a dynamical trichotomy: (i) for all initial conditions, the population goes asymptotically extinct with probability one, (ii) for all positive initial conditions, the population persists and asymptotically exhibits unbounded growth, and (iii) for all positive initial conditions, there is a positive probability of asymptotic extinction and a complementary positive probability of unbounded growth. The main results are illustrated with applications to spatially structured populations with an Allee effect and age-structured populations experiencing mate limitation.
1. Introduction
Higher population densities can increase the chance of mating success, reduce the risk of predation, and increase the frequency of cooperative behavior [Courchamp et al., 2008]. Hence, survivorship, growth, and reproductive rates of individuals can exhibit a positive relationship with density i.e. positive density-dependence. In single species models, positive density-dependence can lead to an Allee effect: the existence of a critical density below which the population tends toward extinction and above which the population persists [Dennis, 1989, McCarthy, 1997, Scheuring, 1999, Gascoigne and Lipcius, 2004, Schreiber, 2003]. Consequently, the importance of Allee effects have been widely recognized for conservation of at risk populations and the management of invasive species [Courchamp et al., 2008]. Population experiencing environmental stochasticity and a strong Allee effect are widely believed to be especially vulnerable to extinction as the fluctuations may drive their densities below the critical threshold [Courchamp et al., 1999]. When population densities lie above the critical threshold for the unperturbed system, analyses and simulations of stochastic models support this conclusion [Dennis, 1989, 2002, Liebhold and Bascompte, 2003, Roth and Schreiber, 2014a, Dennis et al., 2015, Assas et al., 2016]. However, these studies also show that when population densities lie below the critical threshold, stochastic fluctuations can rescue the population from the deterministic vortex of extinction.
Individuals within population often differ in diversity of attributes including age, size, gender, and geographic location [Caswell, 2001]. Positive density-dependence may differentially impact individuals in populations structured by these attributes [Gascoigne and Lipcius, 2005, Courchamp et al., 2008]. This positive density-dependence can lead to an Allee threshold surface (usually a co-dimension one stable manifold of an unstable equilibrium) that separates population states that lead to extinction from those that lead to persistence [Schreiber, 2004].
While several studies have examined how environmental stochasticity and population structure interact to influence persistence of populations experiencing negative-density dependence [Hardin et al., 1988, Benaïm and Schreiber, 2009, Roth and Schreiber, 2014b, Hening et al., 2016], I know of no studies that examine this issue for populations experiencing positive density-dependence. To address this gap, this paper examines stochastic, single species models of the form
[TABLE]
where is a column-vector of population densities, is a non-negative matrix that determines the population densities in the next year as a function of the current densities and the environmental state over the time interval . To focus on the effects of positive density-dependence, I assume that the entries of are non-decreasing functions of the population densities. Under additional suitable assumptions described in Sections 2 and 3, this paper shows that there is a dynamical trichotomy for (1): (i) asymptotic extinction occurs with probability one for all initial conditions, (ii) long-term persistence occurs with probability one for all positive initial conditions, or (iii) long-term persistence and asymptotic extinction occur with complementary positive probabilities for all positive initial conditions. The model assumptions and definitions are presented in Section 2. Exemplar models of spatially-structured populations and age-structured populations are also presented in this section. The main results and applications to the exemplar models appear in Sections 3 and 4. Proofs of the main results are relegated to Section 5.
2. Models, assumptions, and definitions
Throughout this paper, I consider stochastic difference equations of the form given by equation (1). The state space for these equations is the non-negative cone . Define the standard ordering on this cone by for if for all . Furthermore, if but and if for all . Throughout, I will use to denote the sup norm and to denote the associated operator norm. Define the co-norm of a matrix by . The co-norm is the minimal amount that the matrix stretches a vector. Define to be the non-negative component of
For (1), there are five standing assumptions
**A1.Uncorrelated environmental fluctuations: **
is a sequence of independent and identically distributed (i.i.d) random variables taking values in a separable metric space (such as ).
**A2.Feedbacks depend continuously on population and environmental state: **
the entries of the matrix function are continuous functions of population state and the environmental state .
**A3.The population only experiences positive feedbacks: **
For all and , whenever
**A4.Primitivity: **
There exists such that for all and .
**A5.Finite logarithmic moments: **
For all , . There exists such that for all .
The first assumption implies that is a Markov chain on and the second assumption ensures this stochastic process is Feller. The third assumption is consistent with the intent of understanding how non-negative feedbacks, in and of themselves, influence structured population dynamics. An important implication of this assumption is that the system is monotone i.e. if , then for all where are solutions to (1) with initial conditions and , respectively. The fourth assumption ensures that all states in the population contribute to all other population states after time steps. The final assumption is meet for most models and ensures that Kingman [1973]’s subadditive ergodic theorem and the random Perron-Frobenius theorem of Arnold et al. [1994] are applicable.
To see that these assumption include models of biological interest, here are a few examples.
Example 1 (Scalar models)
Considered an unstructured population with in which case . To model mate limitation, McCarthy [1997] considered a model where corresponds to the density of females and, with the assumption of a 1:1 sex ratio, also equals the density of males. The probability of a female successfully mating is given by where is the male density and determines how effectively individuals find mates. If a mated individual produces on average daughters, then the population density in the next year is . If we allow to be stochastic, then (1) is determined by . Allowing the to be a log-normal would satisfy assumptions A1–A5.
To model predator saturation [Schreiber, 2003], let be the probability that individual escapes predation from a predator population with an “effective” attack rate of and handling time . If is the number of offspring produced by an individual which escaped predation, then the population density in the next year is . Letting be stochastic yields . Allowing the to be a log-normal would satisfy assumptions A1–A5.
Finally, Liebhold and Bascompte [2003] used a more phenomenological model of the form where is the critical threshold in the absence of stochasticity and are normally distributed with mean zero. This model also satisfies all of the assumptions.
We can use these scalar models, which were studied by [Roth and Schreiber, 2014a], to build structured models as the next two examples illustate.
Example 2 (Spatial models)
Consider a population that live in distinct patches. is the population density in patch . Let be the critical threshold in patch and be the environmental state in patch . Let be the fraction of individuals dispersing from patch to patch , and be the corresponding dispesal matrix. Then the spatial model is
[TABLE]
where diag denotes a diagonal matrix with the indicated diagonal elements. If is a primitive matrix and the are a multivariate normals with zero means, then this model satisfies the assumptions.
Example 3 (Age-structured models)
Consider a population with age classes and is the density of age individuals. Assume that final age classes reproduce i.e. ages reproduce. If mate limitation causes positive density dependence (see Example 1) and reproductively mature individuals mate randomly, then the fecundity of individuals in age class equals where is the maximal fecundity of individuals of age . Let be the probability an individual survives from age to age . This yields the followng nonlinear Leslie matix model
[TABLE]
If and are multivariate log-normals, then this model satisfies the assumptions A1–A5.
3. Main results
To state the main results, consider the linearization of (1) at the origin and near infinity. At the origin, the linearized dynamics are given by . Hence, the rate at which the population grows at low density is approximately given by the rate at which the random product of matrices, , grows. Kingman [1973]’s subadditive ergodic theorem implies there exists (possibly ) such that
[TABLE]
To characterize population growth near infinity, for all the subadditive ergodic theorem implies there exists an such that
[TABLE]
where is the vector of ones. Due to our assumption that the entries of are non-decreasing with respect the entries of , is non-decreasing with respect to . Hence, the following limit exists (possibly )
[TABLE]
With these definitions and assumptions, the following theorem is proven in Section 5.
Theorem 3.1**.**
**Unconditional persistence: **
If , then
[TABLE]
**Unconditional extinction: **
If , then
[TABLE]
**Conditional persistence and extinction: **
If , then for all there exist such that
[TABLE]
and
[TABLE]
To get statements about all initial conditions with probability one in the final case, an assumption that ensures that the environmental stochasticity can drive the population to low or high densities is needed. Define to be accessible if for all there exists such that
[TABLE]
for all All of the examples in Section 2 satisfy this accessibility condition.
Theorem 3.2**.**
If and is accessible, then
[TABLE]
Proofs of both theorems are presented in Section 5. The scalar version of these theorems were proven in Theorem 3.2 of [Roth and Schreiber, 2014a].
4. Applications
To illustrate the applicability of the two theorems, we consider the spatial structured and age structured models introduced in section 3.
Example 2 (spatially structured populations) revisited
Consider the spatial structured model described in Example 2 and characterized by (2). For this model,
[TABLE]
For simplicity, let us assume that the fraction of individuals dispersing is and dispersing individuals land with equal likelihood on any patch (including the possibility of returning to its original patch). Then is given by for and . Assume that
I claim that . Indeed, let Then where Id denotes the identity matrix and
[TABLE]
Dividing by and taking the limit as , this inequality implies that . Hence, as claimed. Theorem 3.2 implies that for all , with positive probability whenever
Understanding is more challenging. However, Proposition 3 of Benaïm and Schreiber [2009] implies that varies continuously as a function of . In the limit of , and . Hence, for populations where but , there are two types of dynamics. If for all patches (i.e. populations are unable to persist in each patch at low density), then there is a positive probability of going either asymptotically extinct or a complementary positive probability of persistence. Alternatively, if for at least one patch, then the population persists with probability one whenever .
Now consider the case that all individuals disperse i.e. . Then i.e. is the geometric mean of the spatial average of the . By Jensen’s inequality, when is greater than when . Hence, one can get the scenario where increasing the dispersal fraction shifts a population from experiencing asymptotic extinction with positive probability to a population that persists with probability one. This corresponds to a positive density-dependence analog of a ph,enomena observed in models with negative density-dependent feedbacks [Benaïm and Schreiber, 2009, Hening et al., 2016] and density-independent feedbacks [Metz et al., 1983, Jansen and Yoshimura, 1998, Schreiber, 2010, Evans et al., 2013]. However, in these models, the long-term outcome never exhibits a mixture of extinction and persistence.
Example 3 (age-structured populations) revisited
Consider the age-structured model with mate-limitation in Example 3 where there are reproductive stages. If are multivariate log-normals, then is accessible. Define
[TABLE]
As for all , the dominant eigenvalue of is strictly less than one. Thus,
[TABLE]
As , it follows that for all positive initial conditions there is a positive probability of asymptotic extinction (in contrast the spatial model which always has a positive probability of persistence and unbounded growth.)
To say something about persistence, assume that have the same log mean and non-degenerate log-covariance matrix Then is an increasing function of with and . Hence, there is a critical , call it , such that the population goes asymptotically extinct with probability one whenever and the population persists with positive probability whenever .
5. Proofs
First, I prove Theorem 3.1. Assume and . As the entries of are non-decreasing functions of ,
[TABLE]
In particular, with probability one as claimed.
Next, assume that . Given any , choose such that and
[TABLE]
Then
[TABLE]
In particular, with probability one as claimed.
Finally, assume that and As the entries of are non-increasing in , there exists such that for . Hence,
[TABLE]
Define the random variable
[TABLE]
Equation 4 implies that with probability one. For all , define the event For and , I claim that for all on the event I prove this claim by induction. by assumption. Suppose that for . Then
[TABLE]
This completes the proof of the claim that for all on the event It follows that on the event and that
[TABLE]
In particular, almost sure on the event . As the events are increasing with , Therefore, given , there exists such that . For this , and ,
[TABLE]
To show convergence to with positive probability when , choose sufficiently large so that
[TABLE]
By the Random Perron-Frobenius theorem [Arnold et al., 1994, Theorem 3.1 and Remark (ii) on pg. 878],
[TABLE]
for all elements of the standard basis of and where T denotes the transpose of a vector. Equation 5 implies that all of the entries of grow exponentially in time at rate greater than with probability one.
Define
[TABLE]
By (5) and the primitivity assumption A4, with probability one. Define the events
[TABLE]
Now, suppose that . I claim that for all on the event . by the choice of . Assume that for . Then
[TABLE]
Equation (5) implies that on the event
[TABLE]
Hence, almost surely on the event As are an increasing set of events, . For any there is such that Hence, for this and ,
[TABLE]
This completes the proof of Theorem 3.1.
The proof of Theorem 3.2 follows from Theorem 3.1 and the following proposition.
Proposition 5.1**.**
Assume is accessible. Let and be such that
[TABLE]
and
[TABLE]
Then
[TABLE]
Proof.
Define the event
[TABLE]
For any , define for any event in the -algebra generated by . Define the stopping time
[TABLE]
Since is accessible, there exists such that for all . Let equal if and [math] otherwise. The strong Markov property implies that for all
[TABLE]
Let be the -algebra generated by . The Lévy zero-one law implies that for all , almost surely. On the other hand, the Markov property implies that for all . Hence for all .
∎
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