Citation: Yun Kang, Sourav Kumar Sasmal, Komi Messan. A two-patch prey-predator model with predator dispersal driven by the predation strength[J]. Mathematical Biosciences and Engineering, 2017, 14(4): 843-880. doi: 10.3934/mbe.2017046
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Spatial heterogeneity, dispersal patterns, and biotic interactions influence the distribution of species within a landscape [4, 47, 60, 68, 70]. Spatial self-organization results from local interactions between organisms and the environment, and emerges at patch-scales [61, 75]. For example, limited dispersal ability and its related dispersal patterns [57] is considered to be one of the key factors that promote the development of self-organized spatial patterns [1, 42, 71, 72].
In nature, especially for ecological communities of insects, dispersal of a predator is usually driven by its non-random foraging behavior which can often response to prey-contact stimuli [23], including spatial variation in prey density [40] and different types of signals arising directly from prey [76]. For instances, bloodsucking insects respond to the carbon dioxide output and the visual signals of a moving animal, which in tsetse flies (Glossina spp.) lead to the formation of a "following swarm" associated with herds of grazing ungulates [14, 34]. Most mosquitoes were attracted over a larger distance by the odor of the host [17, 18, 19]. The wood-wasp, Sirex noctilio, is attracted by the concentration of the scent [19, 53]. Social ants excite "pheromone trails" to encourage other individuals to visit the same food source [6]. Plant-feeding insects commonly detect food items by gustatory signals [65, 66, 66]. These non-random foraging behaviors driven by prey-mediated patch attractants, prey attractants themselves, and arrestant stimuli following the encounter of a prey, can lead to predation rates that are greater in regions where prey are more abundant (i.e., density-dependent predation), thus regulate population dynamics of both prey and predator.
Recent experimental work on population dynamics of immobile Aphids and Coccinellids by [44] show that the foraging movements of predator Coccinellids are combinations of passive diffusion, conspecific attraction, and retention on plants with high aphid numbers which is highly dependent on the strength of prey-predator interaction. Their study also demonstrates that predation by coccinellids was responsible for self-organization of aphid colonies. Many ecological systems exhibit similar foraging movements of predator. For example, Japanese beetles are attracted to feeding induced plant volatiles and congregate where feeding is taking place [52]. Motivated by these field studies, we propose a two-patch prey-predator model incorporating foraging movements of predator driven by the strength of prey-predator interaction, to explore how this non-random dispersal behavior of predator affect population dynamics of prey and predator.
Dispersal of predator plays an important role in regulating, stabilizing, or destabilizing population dynamics of both prey and predator. There are fair amount literature on mathematical models of prey-predator interactions in patchy environments. For example, see work of [47, 25, 3, 24, 26, 27, 64, 74, 20, 21, 62, 38, 39] and also see [41] for literature review. Many studies examine how the interactions between patches affect the synchronicity of the oscillations in each patch, e.g. see the work of [28, 35], and how interactions may stabilize or destabilize the dynamics. For instances, [37, 35] studied a model with two patches, each with the wellknown prey-predator Rosenzweig-McArthur dynamics, linked by the density independent dispersal (i.e., dispersal is driven by the difference of species' population densities in two patches). His study showed that this type of spatial predator-prey interactions might exhibit self-organization capable of producing stabilizing heterogeneities in prey distribution, and spatial populations can be regulated through the interplay of local dynamics and migration.
However, due to the intricacies that arise in density-dependent dispersal models, there are relatively limited work on models with non-random foraging behavior of predator or non-linear dispersal behavior [40] but see the two patch model with predator attraction to prey, e.g. [32], or predator attraction to conspecific, e.g. [58], or only predators migrate who are attracted to regions with concentrated food resources, see the work of [22, 8]. [40] proposed a non random foraging PDE model through a mechanistic approach to demonstrate that area-restricted search does yield predator aggregation, and explore the the consequences of area-restricted search for predator-prey dynamics. In addition, they provided many supporting ecological examples (e.g. Coccinellids, blackbirds, etc.) that abide by their theory. [32] studied a two-patch predator-prey Rosenzweig-MacArthur model with nonlinear density-dependent migration in the predator. The migration term of the predator is derived by extending the Holling time budget argument to migration. Their study showed that the extension of the Holling time budget argument to movement has essential effects on the dynamics. By extending the model of [32], [16] formulated a similar two patch prey-predator model with density-independent migration in prey and density-dependent migration in the predator. Their study shows that several foraging parameters such as handling time, dispersal rate can have important consequences in stability of prey-predator system. [10] investigated the population-dispersal dynamics for predator-prey interactions in a two patch environment with assumptions that both predators and their prey are mobile and their dispersal between patches is directed to the higher fitness patch. They proved that such dispersal, irrespectively of its speed, cannot destabilize a locally stable predator-prey population equilibrium that corresponds to no movement at all.
In this paper, we formulates a new version of Rosenzweig-MacArthur two patch prey predator model with mobility only in predator. Our model is distinct from others as we assume that the non-random foraging movements of predator is driven by the strength of prey-predator interactions, i.e., predators move towards patches with more concentrated prey and predator. Our model can apply to many insects systems such as Aphids and Coccinellids, Japanese beetles and their host plants, etc. For instance, the experimental work of [5] demonstrated that attraction to uninfested potato plants by Colorado potato beetle does not occur when the plants are small. However, when small plants are infested by conspecific larvae they become highly attractive to adult beetles. Thus predators beetles are are more attracted toward patches with high prey-predator interaction strength. The prey-predation attraction can also be observed in the field work of [44]. The main focus of our study of such prey-predator interactions in heterogeneous environments is to explore the following ecological questions:
1.How does our proposed nonlinear density-dependent dispersal of predator stabilize or destabilize the system?
2.How does dispersal of predator affect the extinction and persistence of prey and predator in both patches?
3.How may dispersal promote the coexistence of prey and predator when predator goes extinct in the single patch?
4.What are potential spatial patterns of prey and predator?
5.How are the effects of our proposed nonlinear density-dependent dispersal of predator on population dynamics different from the effects of the traditional density-independent dispersal?
The rest of the paper is organized as follows: In Section (2), we provide the detailed derivation of our two patch prey-predator model. In Section (3), we perform completed local and global dynamics of our model, and derive sufficient conditions that lead to the persistence and extinction of predator as well as permanence of the model. In Section (4), we perform bifurcation simulations to explore the dynamical patterns and compare the dynamics of our model to the traditional model [26, 27, 37, 35, 36]. In Section (5), we conclude our study and discuss the potential future study. The detailed proofs of our analytical results are provided in the last section.
Let
duidt=riui(1−uiki)−biuivi1+bihiuidvidt=cibiuivi1+bihiui−δivi | (1) |
where
We assume that the dispersal of predator from one patch to the other is driven by the strength of the prey-predator interaction in two patches which is termed as the attraction strength. More specifically, in the presence of dispersal, the dispersal rate of predators from Patch
bjujvj1+bjhjujρijvi−biuivi1+bihiuiρjivj | (2) |
where
du1dt=r1u1(1−u1k1)−b1u1v11+b1h1u1dv1dt=c1b1u1v11+b1h1u1−δ1v1+(b1u1v11+b1h1u1ρ21v2−b2u2v21+b2h2u2ρ12v1)du2dt=r2u2(1−u2k2)−b2u2v21+b2h2u2dv2dt=c2b2u2v21+b2h2u2−δ2v2+(b2u2v21+b2h2u2ρ12v1−b1u1v11+b1h1u1ρ21v2). | (3) |
We use the similar rescaling approach in [51] by letting
xi=bihiui,yi=bihicivi,Ki=bihiki,ai=cihi,di=ciδibihi, |
then we have
v1(b1u11+b1h1u1ρ21v2−b2u2v21+b2h2u2ρ12)=v1(b1x1b1h11+x1ρ21c2b2h2y2−b2x2b2h2c2b2h2y21+x2ρ12)=v1(ρ21a1a2c1b2x1y21+x1−ρ12a22c2b2x2y21+x2) |
and
v2(b2u21+b2h2u2ρ12v1−b1u1v11+b1h1u1ρ21)=v2(b2x2b2h21+x2ρ12c1b1h1y1−b1x1b1h1c1b1h1y11+x1ρ21)=v2(ρ12a1a2c2b1x2y11+x2−ρ21a21c1b1x1y11+x1) |
For mathematical convenience, we assume that
v1(ρ21a1a2c1b2x1y21+x1−ρ12a22c2b2x2y21+x2)=v1y2ρa2b2(a1x11+x1−a2x21+x2) |
and
v2(ρ12a1a2c2b1x2y11+x2−ρ21a21c1b1x1y11+x1)=y1v2ρa1b1(a2x21+x2−a1x1y11+x1). |
Denote that
dx1dt=r1x1(1−x1K1)−a1x1y11+x1dy1dt=a1x1y11+x1−d1y1+ρ1(a1x1y11+x1⏟attraction strength to Patch 1y2−a2x2y21+x2⏟attraction strength to Patch 2ρ12y1)dx2dt=r2x2(1−x2K2)−a2x2y21+x2dy2dt=a2x2y21+x2−d2y2+ρ2(a2x2y21+x2⏟attraction strength to Patch 2y1−a1x1y11+x1⏟attraction strength to Patch 1y2) | (4) |
where
1.In the absence of dispersal, Model (4) is reduced to the following uncoupled Rosenzweig-MacArthur prey-predator single patch models
dxidt=rixi(1−xiKi)−aixiyi1+xidyidt=aixiyi1+xi−diyi | (5) |
where
(a)In the absence of predation, population of prey
(b)Predator is specialist (i.e., predator
2.There is no dispersal in prey species. This assumption fits in many prey-predator (or plant-insects) interactions in ecosystems such as Aphid and Ladybugs, Japanese beetles and its feeding plants, etc.
3.The dispersal of predator from Patch
The state space of Model (4) is
Theorem 3.1. Assume all parameters are nonnegative and
1.If there is no dispersal in predator, i.e.,
(a) Model (5) always has the extinction equilibrium
(b) If
(c) If
(d) If
2.The sets
dxidt=rixi(1−xiKi)−aixiyi1+xidyidt=aixiyi1+xi−diyi | (6) |
dxjdt=rjxj(1−xjKj) | (7) |
where
Notes and biological implications. Theorem 3.1 provides a foundation on our further study of local stability and global dynamics of Model (4). More specifically, Item 2 of Theorem 3.1 implies that Model (4) has the same the invariant sets
Now we start with the boundary equilibria of Model (4). Recall that
μi=diai−di,ν1=(K1−μ1)(1+μ1)a1K1,ν2=r(K2−μ2)(1+μ2)a2K2. |
We define the following notations for all possible boundary equilibria of Model (4):
E0000=(0,0,0,0),EK1000=(K1,0,0,0),Eμ1ν100=(μ1,ν1,0,0),EK10μ2ν2=(K1,0,μ2,ν2),EK10K20=(K1,0,K2,0),E00K20=(0,0,K2,0),E00μ2ν2=(0,0,μ2,ν2),Eμ1ν1K20=(μ1,ν1,K2,0). |
The following theorem provides sufficient conditions on the existence and stability of these boundary equilibria:
Theorem 3.2. [Boundary equilibria of Model (4)] Model (4) always has the following four boundary equilibria
E0000,EK1000,E00K20,EK10K20 |
where the first three ones are saddles while
Eb11=Eμ1ν100,Eb12=Eμ1ν1K20,Eb21=E00μ2ν2andEb22=EK10μ2ν2. |
Then if
sa:
sb:
sc:
sd:
And
ua:
ub:
uc:
In addition, if
Notes and biological implications. Theorem 3.2 implies the following points regarding the effects of dispersal in predators:
1.Dispersal has no effects on the local stability of the boundary equilibrium
2.Large dispersal of predator in its own patch may have stabilizing effects from the results of Item sd: In the absence of dispersal, the dynamics of Patch
3.Large dispersal of predator in its own patch may have destabilizing effects from the results of Item ub: In the absence of dispersal, the dynamics of Patch
4.Under conditions of
In this subsection, we focus on the extinction and persistence dynamics of prey and predator of Model (4). First we show the following theorem regarding the boundary equilibrium
Theorem 3.3. Model (4) has global stability at
Notes and biological implications. Theorem 3.3 implies that the dispersal of predators does not effect the global stability of the boundary equilibrium
To proceed the statement and proof of our results on persistence, we provide the definition of persistence and permanence as follows:
Definition 3.4 (Persistence of single species)We say species
b≤lim infτ→∞z(τ)≤lim supτ→∞z(τ)≤B. |
where
Definition 3.5 (Permanence of a system)We say Model (4) is permanent in
b≤lim infτ→∞min{x1(τ),y1(τ),x2(τ),y2(τ)} |
≤lim supτ→∞max{x1(τ),y1(τ),x2(τ),y2(τ)}≤B. |
The permanence of Model (4) indicates that all species in the system are persistence.
Theorem 3.6. [Persistence of prey and predator] Prey
1.
2.
3.
Notes and biological implications. Theorem 3.6 indicates that the dispersal of predators does not affect the persistence of preys, while small dispersal of predator
Theorem 3.7 [Permanence of the two patch dispersal model] Model (4) is permanent if one of the following inequalities hold
1.
2.
3.
Notes and biological implications. According to Theorem 3.6, we can conclude that Model (4) is permanent whenever both predators are persistent. Theorem 3.7 provides such sufficient conditions that can guarantee the coexistence of bother predator for the two patch model (4), thus provides sufficient conditions of its permanence. Item 1 of this theorem implies that if predator
Let
dxidt=rixi(1−xiKi)−aixiyi(1+xi)=aixi1+xi[ri(Ki−xi)(1+xi)aiKi−yi]=pi(xi)[qi(xi)−yi]dyidt=yi[aixi1+xi−di+ρiyj(aixi1+xi−ajxj1+xj)]=yi[pi(xi)−di+ρiyj(pi(xi)−pj(xj))] |
If
qi(xi)−yi=0⇔qi(xi)=yi,pi(xi)−di+ρiyj(pi(xi)−pj(xj))=0⇔pi(xi)=aixi1+xi=ρiyjpj(xj)+di1+ρiyj=ρiqj(xj)pj(xj)+di1+ρiqj(xj) | (8) |
which gives:
xi=ρiqj(xj)pj(xj)+diai(1+ρiqj(xj))−(ρiqj(xj)pj(xj)+di) | (9) |
=ρiqj(xj)pj(xj)+diρiqj(xj)[ai−pj(xj)]+ai−di | (10) |
Since
x1=a2[r2ρ1x2(K2−x2)+K2d1]r2ρ1x2(K2a1−K2a2−a1)−r2ρ1x22(a1−a2)+K2(a1r2ρ1+a1a2−a2d1)=ft(x2)fb(x2)=F(x2)x2=a1[r1ρ2x1(K1−x1)+K1d2]r1ρ2x1(K1a2−K1a1−a2)−r1ρ2x21(a2−a1)+K1(a2r1ρ2+a1a2−a1d2)=gt(x1)gb(x1)=G(x1) | (11) |
with
1.
2.
3.
4.
Theorem 3.8. [Interior equilibrium] If
1.Assume that
xci=Ki(riρj+ai−dj−√(ai−dj)(riρj+ai−dj))riρj. |
Model (4) has no interior equilibrium if
And it has at least one interior equilibrium
ai>max{aj,d1,d2},aj>max{d1,d2},ρj<4Kiai(aj−ai)(dj−aj)ri(Kiaj−Kiai+aj)2, |
F(xc2)<K1,andG(xc1)<K2 |
where sufficient conditions for the inequalities
ρi≤4(Kiai−Kidi−di)Kjrjandρj<4Kjaj(Kiai−Kidi−di)ajrjK2j+rjKi(Kjaj−Kjai−ai)2. |
In addition, we have
2.Assume that
a1=a2=a>max{d1,d2},F(xc2)<K1,andG(xc1)<K2 |
where sufficient conditions for the inequalities
ρi<4(Kia−Kidi−di)Kjrj |
for both
Notes and biological implications. Theorem 3.8 provides sufficient conditions on the existence of no interior equilibrium when
1.If
2.If
The question is how we can solve the explicit form of an interior equilibrium of Model (4). The following theorem provides us an example of such interior equilibrium of Model (4).
Theorem 3.9. [Interior equilibrium and the stability] Suppose that
μ1=da1−d,ν1=(K1−μ1)(1+μ1)a1K1,μ2=da2−d,ν2=r(K2−μ2)(1+μ2)a2K2. |
If
1.
μ1(K1a1−a1−K1d−d)a1K1+rμ2(K2a2−a2−K2d−d)a2K2>0. |
2.Assume that
μ1(K1a1−a1−K1d−d)a1K1+rμ2(K2a2−a2−K2d−d)a2K2<0. |
If
ρi>max{−νj−rjμiμj(Kiai−Kid−ai−d)(Kjaj−Kjd−aj−d)(KiKjajνjdνi(ai−d)2), |
−μiνjKj(νiρj+1)(aj−d)2(Kiai−Kid−ai−d)rjμjνiKi(ai−d)2(Kjaj−Kjd−aj−d)−1νj}. |
If, in addition,
Notes and biological implications. Theorem 3.9 implies Model (4) has an interior equilibrium
From mathematical analysis in the previous sections, we can have the following summary regarding the effects of dispersal of predators for Model (4):
1.Large dispersal of predator at Patch
2.Small dispersal of predator at Patch
3.Dispersal has no effects on the persistence of prey and the number of boundary equilibrium. It has also no effects on the local stability of the boundary equilibrium
4.If
5.If
To continue our study, we will perform bifurcations diagrams and simulations to explore the effects on the dynamical patterns and compare dynamics of our model (4) to the classical two patch model (12).
In this subsection, we perform bifurcation diagrams and simulations to obtain additional insights on the effects of dispersal on the dynamics of our proposed two patch model (4). We fix
1.Choose
2.Choose
3.Choose
In summary, Figure 1, 2, 3, and 4 suggest that dispersal of predator may stabilize or destabilize interior dynamics; it may drive the extinction of predator in one or both patches; and it may generate the following patterns of multiple attractors via two or three interior equilibria:
1.Multiple interior attractors through three interior equilibria: In the presence of dispersal, Model (4) can have the following types of interior equilibria and the corresponding dynamics:
• Two interior sinks and one interior saddle: Depending on the initial conditions with
• One interior sink and two interior saddles: Depending on the initial conditions with
We should also expect the case of one sink v.s. one saddle v.s. one source and the case of two source v.s. one saddle when the interior sink(s) become unstable and go through Hopf-bifurcation. In addition, Model (4) seems to be permanent whenever it processes three interior equilibria.
2.Boundary attractors and interior attractors through three interior equilibria:
• one interior sink and one interior saddle: Depending on the initial conditions with
• two interior saddles: Model (4) converges either to the fluctuated interior attractors or to the boundary attractors with one predator going extinct for almost all initial conditions depending on the initial conditions with
• one interior source and one interior saddle: Depending on the initial conditions with
Model (4) has bistability between interior attractors and the boundary attractors whenever it processes two interior equilibria. This implies that depending on the initial conditions, predator at one patch can go extinct when the system has two interior equilibria.
In general, simulations suggest that Model (4) is permanent when it processes one or three interior equilibria while it has bistability between interior attractors and the boundary attractors whenever it processes two interior equilibria.
The dispersal of predator in our model is driven by the strength of prey-predator interactions. This is different from the classical dispersal model such as Model (12) which has been introduced in [36]:
dxidt=rixi(1−xiKi)−aixiyi1+xidyidt=aixiyi1+xi−diyi+ρi(yj−yi)dxjdt=rjxj(1−xjKj)−ajxjyj1+xjdyjdt=ajxjyj1+xj−djyj−ρj(yj−yi) | (12) |
where
Recently, [51] studied Model (12) with both dispersal in prey and predator. Liu provide global stability of the interior equilibrium for the symmetric case and performed simulations for the asymmetric cases. Here we provide rigorous results on the persistence and permanence conditions that can be used for the comparisons to our Model (4) in the following theorem:
Theorem 4.1. [Summary of the dynamics of Model (12)] Define
^μi=^diai−^di,^νi=qi(^μi)=ri(Ki−^μi)(1+^μi)aiKiandˆνij=ρj^νidj+ρj |
where
1.Model (12) is positively invariant and bounded in its state space
2.Boundary equilibria: Model (12) always has the following four boundary equilibria
E0000,EK1000,E00K20,EK10K20 |
where the first three ones are saddles while
d1+d2+ρ1+ρ2>a1K11+K1+a2K21+K2 |
and
ˆd1−a1K11+K1+K2a2(a1K11+K1−d1−ρ1)(d2+ρ2)(1+K2)>0⇔[d1−a1K11+K1][1−K2a2(d2+ρ2)(1+K2)]+ρ1d2+ρ2[d2−K2a2(1+K2)]>0. |
and it is a saddle if one of the above inequalities does not hold. If
3.Subsystem
dxidt=rixi(1−xiKi)−aixiyi1+xidyidt=aixiyi1+xi−diyi+ρi(yj−yi)dyjdt=−djyj−ρj(yj−yi) | (13) |
whose global dynamics can be described as follows:
3a Prey
3b Model (13) has global stability at
3c Model (13) has global stability at
4.Persistence of prey: Prey
4(a)
4(b)
4(c)
5.Extinction of prey
6.Persistence and extinction of predators: Predator
7.Permanence of Model (12): Model (12) is permanent if
8.The symmetric case: Let
Notes. Theorem 4.1 indicates follows:
1.If
2.Proper dispersal of predators can drive the extinction of prey in one patch.
3.Dispersal has no effects on the persistence of predator. This is different from our proposed model (12).
To see how different types of strategies in dispersal of predators affect population dynamics of prey and predator, we start with the comparison of the boundary equilibria of our model (4) and the classic model (12). Both Model (4) and (12) always have four boundary equilibria
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
LAS and GAS if |
GAS if |
|
LAS if |
Does not exists | |
Does not exists | LAS if |
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
Persistence of prey | Always persist, dispersal of predator has no effects | One or both prey persist if conditions 4. in Theorem (4.1) holds. Small dispersal of predator in Patch |
Extinction of prey | Never extinct |
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
Persistence of predator | Predator at Patch |
Predators in both patches have the same persistence conditions. They persist if |
Extinction of predator | Simulations suggestions (see the yellow regions of Figure (1a) and Figure (3a)) that the large dispersal of predator in Patch |
Predators in both patches have the same extinction conditions. They go extinct if |
1.The boundary equilibria:
2. Persistence and extinction of prey. According to the comparison of sufficient conditions leading either persistence or extinction of prey in a patch listed in Table 2, we can conclude that the strength of dispersal ability of predator has huge impact on the prey for the classical model (12) but not for our model (4).
3. Persistence and extinction of predator. Simulations and the comparison of sufficient conditions leading either persistence or extinction of predators in a patch listed in Table 3, suggest that the strength of dispersal ability of predator has profound impacts on the persistence of predator for our model (4) while it has no effects on the persistence of predator for the classical model (12).
4.Permanence of a system depends on the persistence of each species involved in the system. Our comparisons of sufficient conditions leading to the persistence of prey and predator listed in Table 2-3, indicate that dispersal of predator has important impacts in the persistence of predator in our model (4) while it has significant effects on the persistence of prey of the classical model (12). We can include that (ⅰ) the large dispersal of predator in a patch has potential lead to the extinction of prey (the classical model (12)) or predator (our model (12)) in that patch, thus destroy the permanence of the system; (ⅱ) the small dispersal of predator in Patch
5.Interior equilibria: Both our model (4) and the classical model (12) have the maximum number of three interior equilibria. However, for the symmetric case, our model (4) can have the unique interior equilibrium (see Theorem 3.9) while the classical model can potentially process three interior equilibria [36].
6.Multiple attractors: Both our model (4) and the classical model (12) have two types bi-stability: (a) The boundary attractors where one of prey or predator can not sustain and the interior attractors where all four species can co-exist; and (b) Two distinct interior attractors. One big difference we observed is that for the symmetric case when each single patch model has global stability at its unique interior equilibrium, our model (4) can have only one interior attractor while the classical model can potentially have two distinct interior attractors. This is due to the fact that Model (4) has unique interior equilibrium while Model (12) can potentially process three interior equilibria as we mentioned earlier.
The idea of "metapopulation" originated from [48] where R. Levins used the concept to study the dynamics of pests in agricultural field in which insect pests move from site to site through migrations. Since Levin's work, many mathematical models have been applied to study prey-predator interactions between two or multiples patches that are connected through random dispersion, see examples in [37, 36, 7, 43, 35, 46, 47, 59, 9, 26, 2, 55, 29]. The study of these metapopulation models help us get a better understanding of the dynamics of species interacting in a heterogeneous environment, and allow us to obtain a useful insight of random dispersal effects on the persistence and permanence of these species in the ecosystem. Recently, there has been increasing empirical and theoretical work on the non-random foraging movements of predators which often responses to prey-contact stimuli such as spatial variation in prey density [11, 40], or different type of signals arising directly from prey [76]. See more related examples of mathematical models in [49, 45, 12, 8, 13, 22, 10, 44, 16, 32, 28, 56]. Kareiva [41] provided a good review on varied mathematical models that deal with dispersal and spatially distributed populations and pointed out the needs of including non-random foraging movements in meta-population models. Motivated by this and the recent experimental work of immobile Aphids and Coccinellids by [44], we formulate a two patch prey-predator model (4) with the following assumptions: (a) In the absence of dispersal the model reduced to the two uncoupled Rosenzweig-MacArthur prey-predator single patch models (5); (b) Prey is immobile; and (c) Predator foraging movements are driven by the strength of prey-predator interaction. We provide basic dynamical properties such positivity and boundedness of our model in Theorem 3.1.
Based on our analytic results and bifurcation diagrams, we list our main findings regarding the following questions stated in the introduction how our proposed nonlinear density-dependent dispersal of predator stabilizes or destabilizes the system; how it affects the extinction and persistence of prey and predator in both patches; how it may promote the coexistence; and how it can generate spatial population patterns of prey and predator:
1.Theorem (3.2) provides us the existence and local stability features of the eight boundary equilibria of our model (4). This result indicates that large dispersal of predator in its own patch may have both stabilizing and destabilizing effects on the boundary equilibrium depending on certain conditions. Theorem (3.3) gives sufficient conditions on the extinction of predator in both patches, which suggest that predator can not survive in the coupled system if predator is not able to survive at its single patch. In this case, dispersal of predator has no effect on promoting the persistence of predator but dispersal may drive predator extinct even if predator is able to persist at the single patch state (see white regions of Figure (1a), (2a), and (3a)).
2.Theorem (3.6) provides sufficient conditions of the persistence of prey and predator while Theorem (3.7) provides sufficient conditions of the permanence of our two patch model. These results imply that under certain conditions, large dispersal of predator can promote its persistence, thus, promote the permanence of the coupled system while predator in that patch goes extinct in the absence of dispersal. Our numerical studies also suggests that large dispersal can also drive the extinction of predators in both patches (see white regions of Figure (1a), (2a), and (3a)).
3.Theorem (3.8) and Theorem (3.9) provide sufficient conditions on the existence and the local stability of the interior equilibria under certain conditions. Our analytic study shows that large dispersal of predator may be able to stabilize the interior equilibrium when one of the single patch has global stable interior equilibrium while the other one has limit cycle dynamics. At the mean time, our bifurcation diagrams (see Figure (1b), (2b), and (2b)) suggest that the stabilizing or destabilizing effects of predator's dispersal are not definite, i.e., dispersal can either stabilize or destabilize the system depending on other life history parameters. Moreover, our simulations also suggest that the dispersal of predator can either generate multiple interior equilibria or destroy the interior equilibrium which leads to the extinction of predator in one patch or predators in both patches.
Comparisons to the classic model (12). We provide detailed comparison between the dynamics of our model (4) to the classic model (12). These comparisons suggest that the mode of forging movement of predator has profound impacts on the dynamics of the coupled two patch model.Here we highlight two significant differences: (1) the strength of dispersal ability of predator has profound impacts on the persistence of predator for our model (4) while it has no effects on the persistence of predator for the classical model (12). However, the dispersal of predator has huge impacts on the persistence of prey for the classical model (12) while it has little or no effects on the persistence of prey for our model (4). And (2) for the symmetric case, our model (4) has a unique interior equilibrium while the classical model (12) can have up to three interior equilibria thus it is able to generate different spatial patterns.
Proof of Theorem 3.1
Proof.Notice that both
dxidt=rixi(1−xiKi)−aixiyi1+xi≤rixi(1−xiKi) |
which implies that
lim supt→∞xi(t)≤Ki. |
Define
dVdt=rho2d(x1+y1)dt+ρ1d(x2+y2)dt=ρ2x1(1−x1K1)+ρ1rx2(1−x2K2)−ρ2d1y1−ρ1d2y2=ρ2x1(1−x1K1)+ρ1rx2(1−x2K2)+ρ2d1x1+ρ1d2x2−ρ2d1(x1+y1)−ρ1d2(x2+y2)≤M−d[ρ2(x1+y1)+ρ1(x2+y2)]=M−dV |
where
M=max0≤x1≤K1{ρ2x1(1−x1K1+d1)}+max0≤x2≤K2{ρ1x2(1−x2K2+d2)}. |
Therefore, we have
lim supt→∞V(t)=lim supt→∞ρ2(x1(t)+y1(t))+ρ1(x2(t)+y2(t))≤Md |
which implies that Model (5) is bounded in
If there is no dispersal in predator, i.e.,
Recall that both
dyjdt=−djyj−ρjaixiyi1+xiyj≤0⇒lim supt→∞yj(t)=0. |
Applying the results in [69], we can conclude that Model (4) is reduced to the single patch model (5) when
In the case that
Summarizing the discussions above, we can conclude that the statement of Theorem 3.1 holds.
Proof of Theorem 3.2.
Proof.According Theorem 3.1, sufficient condition for the single patch model (5) having the unique interior equilibrium
The local stability of an equilibrium
J(x∗1,y∗1,x∗2,y∗2)=|(1−2x∗1K1)−a1y∗1(1+x∗1)2−a1x∗11+x∗100a1y∗1(1+ρ1y∗2)(1+x∗1)2a1x∗1(1+ρ1y∗2)1+x∗1−ρ1a2x∗2y∗21+x∗2−d1−ρ1a2y∗1y∗2(1+x∗2)2ρ1y∗1(a1x∗11+x∗1−a2x∗21+x∗2)00r(1−2x∗2K2)−a2y∗2(1+x∗2)2−a2x∗21+x∗2−ρ2a1y∗1y∗2(1+x∗1)2ρ2y∗2(a2x∗21+x∗2−a1x∗11+x∗1)a2y∗2(1+ρ2y∗1)(1+x∗2)2a2x∗2(1+ρ2y∗1)1+x∗2−ρ2a1x∗1y∗11+x∗1−d2| | (14) |
After substituting the boundary equilibria
The eigenvalues of (14) evaluated at
λ1=−1 (<0), λ2=a1K11+K1−d1<0⇔μ1>K1, |
λ3=−r (<0), λ4=a2K21+K2−d2<0⇔μ2>K2. |
Therefore,
Now we focus on the local stability of
λ1=−r,λ2=K2(a2−d2)−d21+K2+ρ2ν1[K2(a2−d1)−d1](1+K2) |
and
λ3+λ4=K1(a1−d1)−(a1+d1)a1K1(a1−d1),λ3λ4=d1(K1(a1−d1)−d1)a1K1. |
Notice that the eigenvalues of
1.If
K2(a2−d1)−d1<0⇔eithera2≤d1 or K2<d1a2−d1. |
Therefore, we can conclude that
0<d1a2−d1<K2<μ2andρ2<d2−K2(a2−d2)ν1[K2(a2−d1)−d1]. |
2.If
ρ2>K2(a2−d2)−d2ν1[d1−K2(a2−d1)]. |
Therefore,
Summarizing the discussions above, we can conclude that the boundary equilibrium
1.
2.
3.
4.
And
1.
2.
3.
Similarly, we can obtain sufficient conditions for the local stability of the boundary equilibrium
If
μ1<K1<d2a1−d2⇒d1a1−d1<d2a1−d2⇒d1<d2 |
and
μ2<K2<d1a2−d1⇒d2a2−d2<d1a2−d1⇒d2<d1 |
which are contradiction. Therefore,
Now if
K(a−d)(Ka−Kd−d)+ρj(Ka−Kd−d)2K(K+1)(a−d)2>0 |
which indicates that
Proof of Theorem 3.3.
Proof.Let
rixi(1−xiKi)−aixiyi(1+xi)=aixi1+xi[ri(Ki−xi)(1+xi)aiKi−yi] |
=pi(xi)[qi(xi)−yi]. |
We construct the following Lyapunov functions
V1(x1,y1)=ρ2∫x1K1p1(ξ)−p1(K1)p1(ξ)dξ+ρ2y1 | (15) |
and
V2(x2,y2)=ρ1∫x2K2p2(ξ)−p2(K2)p2(ξ)dξ+ρ1y2 | (16) |
Now taking derivatives of the functions (15) and (16) with respect to time
ddtV1(x1(t),y1(t))=ρ2p1(x1)−p1(K1)pi(x1)dx1dt+ρ2dy1dt=ρ2[p1(x1)−p1(K1)][q1(x1)−y1]+ρ2y1[p1(x1)−d1]+ρ1ρ2y1y2[p1(x1)−p2(x2)]=ρ2[p1(x1)−p1(K1)]q1(x1)+ρ2y1[p1(K1)−d1]+ρ1ρ2y1y2[p1(x1)−p2(x2)] | (17) |
and
ddtV2(x2(t),y2(t))=ρ1p2(x2)−p2(K2)p2(x2)dx2dt+ρ1dy2dt=ρ1[p2(x2)−p2(K2)][q2(x2)−y2]+ρ1y2[p2(x2)−d2]+ρ1ρ2y1y2[p2(x2)−p1(x1)].=−ρ1[p2(x2)−p2(K2)]q2(x2)+ρ1y2[p2(K2)−d2]+ρ1ρ2y1y2[p2(x2)−p1(x1)] | (18) |
Let
ddtV=ddtV1(x1(t),y1(t))+ddtV2(x2(t),y2(t))=ρ2[p1(x1)−p1(K1)]q1(x1)+ρ2y1[p1(K1)−d1]+ρ1[p2(x2)−p2(K2)]q2(x2)+ρ1y2[p2(K2)−d2]. |
Since
Proof of Theorem 3.6.
Proof.
According to Theorem 3.1, we know that Model (4) is attracted to a compact set
First we focus on the persistence conditions for prey
dx1x1dt|x1=0,y1=0=(1−x1K1)−a1y11+x1|x1=0,y1=0=1>0. |
According to Theorem 2.5 of [33], we can conclude that prey
Since both
1.If
dy1y1dt|EK1000=[a1x11+x1−d1+ρ1(a1x1y21+x1−a2x2y21+x2)]|EK1000=a1K11+K1−d1dy1y1dt|EK10K20=[a1x11+x1−d1+ρ1(a1x1y21+x1−a2x2y21+x2)]|EK10K20=a1K11+K1−d1. |
Since
2.If
dy1y1dt|EK10μ2ν2=[a1x11+x1−d1+ρ1(a1x1y21+x1−a2x2y21+x2)]|EK10μ2ν2=a1K11+K1−d1+ρ1(a1K1ν21+K1−a2μ2ν21+ν2)=a1K11+K1−d1+ρ1ν2(a1K11+K1−a2μ21+μ2)=a1K11+K1−d1+ρ1ν2(a1K11+K1−d2)>0. |
According to the proof of Theorem 3.2, we can see that sufficient condition that
(a)
(b)
(c)
where
Based on the discussion above, we can conclude that the statement of Theorem 3.6 holds.
Proof of Theorem 3.7.
Proof. If
dy1y1dt|EK10μ2ν2=[a1x11+x1−d1+ρ1(a1x1y21+x1−a2x2y21+x2)]|EK10μ2ν2=a1K11+K1−d1+ρ1(a1K1ν21+K1−a2μ2ν21+ν2)=a1K11+K1−d1+ρ1ν2(a1K11+K1−a2μ21+μ2)=a1K11+K1−d1+ρ1ν2(a1K11+K1−d2)>0. |
Since
a1K11+K1−d2>0⇔K1>d2a1−d2andρ1>d1−K1(a1−d1)v2[K1(a1−d2)−d2]. |
Similarly, we can show that predator
Kj−12<μj<Kj,μi>Ki,0<djai−dj<Ki<μi |
andρi>di−Ki(ai−di)νj[Ki(ai−dj)−dj]. |
According to Theorem 3.6, we can conclude that prey
Ki−12<μi<Ki,μj>Kj−12andKj>max{μj,diaj−di}. |
Therefore, Model (4) is permanent if the above inequalities hold for both
Ki−12<μi<Ki,Kj−12<μj<Kj<diaj−diandρj<Kj(aj−dj)−djνi[di−Kj(aj−di)]. |
Therefore, both predator
Ki−12<μi<Ki,Ki>max{μi,djai−dj}, |
Kj−12<μj<Kj<diaj−diandρj<Kj(aj−dj)−djνi[di−Kj(aj−di)]. |
Based on the discussion above, we can conclude that the statement of Theorem 3.7 holds.
Proof of Theorem 3.8.
Proof.If
The interior equilibrium
ft(x2)=a2[r2ρ1x2(K2−x2)+K2d1],fb(x2)=r2ρ1x2(K2a1−K2a2−a1)−r2ρ1x22(a1−a2)+K2(a1r2ρ1+a1a2−a2d1) |
and
gt(x1)=a1[r1ρ2x1(K1−x1)+K1d2],gb(x1)=r1ρ2x1(K1a2−K1a1−a2)−r1ρ2x21(a2−a1)+K1(a2r1ρ2+a1a2−a1d2). |
Notice that the nullclines
1.
2.
fb(x2)|a1=a2=a=a[r2ρ1(K2−x2)+K2(a−d1)]. |
3.
4.
gb(x1)|a1=a2=a=a[r1ρ2(K1−x1)+K1(a−d2)]. |
According to Theorem 3.1, we know that population of prey
lim supt→∞xi(t)≤Ki. |
Thus, we can restrict the function
Now we assume that
r22ρ21(K2a1−K2a2−a1)2<4K2r2ρ1(a2−a1)(a1r2ρ1+a1a2−a2d1) |
⇔ρ1<4K2a2(a1−a2)(d1−a1)r2(K2a1−K2a2+a1)2 |
while
fb(0)=K2(a1r2ρ1+a2(a1−d1))>0andfb(K2)=a2K2(a1−d1)>0. |
And
r21ρ22(K1a2−K1a1−a2)2<4K1r1ρ2(a1−a2)(a2r1ρ2+a1a2−a1d2) |
⇔ρ2<4K1a1(a1−a2)(a2−d2)r1(K1a2−K1a1+a2)2. |
Similar cases can be made for
a1>a2,ρ1<4K2a2(a1−a2)(d1−a1)r2(K2a1−K2a2+a1)2 |
or
a2>a1,ρ2<4K1a1(a2−a1)(d2−a2)r1(K1a2−K1a1+a2)2 |
hold.
Now we focus on sufficient conditions lead to both
fb(x2)=r2ρ1x2(K2a1−K2a2−a1)−r2ρ1x22(a1−a2)+K2(a1r2ρ1+a1a2−a2d1). |
Therefore, we have
ρ2<4K1a1(a2−a1)(d2−a2)r1(K1a2−K1a1+a2)2. |
The discussion so far also indicates that we have both
ai>max{aj,di},ρj<4Kiai(aj−ai)(dj−aj)ri(Kiaj−Kiai+aj)2. |
Now assume that these conditions hold, then we have
xc1=K1(r1ρ2+a1−d2−√(a1−d2)(r1ρ2+a1−d2))r1ρ2∈(0,K1) |
and
xc2=K2(r2ρ1+a2−d1−√(a2−d1)(r2ρ1+a2−d1))r2ρ1∈(0,K2). |
If
max0≤x2≤K2{F(x2)}=F(xc2)≤max0≤x2≤K2{ft(x2)}min0≤x2≤K2{fb(x2)}=fb(K2/2)fb(K2)=K2r2ρ1+4d14(a1−d1) |
and
max0≤x1≤K1{G(x1)}=G(xc1)≤max0≤x1≤K1{gt(x1)}min0≤x1≤K1{gb(x1)}=gt(K1/2)gb(K2a1−K2a2−a12(a1−a2)) |
=a1K1(r1K1ρ2/4+d2)K1a1(a2−d2)−r1ρ2(K1a1−K1a2−a2)24(a1−a2), |
therefore, we have
K2r2ρ1+4d14(a1−d1)≤K1⇔ρ1≤4(K1a1−K1d1−d1)K2r2. |
and
K2≥a1K1(r1K1ρ2/4+d2)K1a1(a2−d2)−r1ρ2(K1a1−K1a2−a2)24(a1−a2)⇔ρ2≤4K1a1(K2a2−K2d2−d2)a1r1K21+r2K2(K1a1−K1a2−a2)2. |
Therefore, we can conclude that Model (4) has at least one interior equilibrium
ai>max{aj,d1,d2},aj>max{d1,d2},ρi≤4(Kiai−Kidi−di)Kjrj |
and
ρj<min{4Kiai(aj−ai)(dj−aj)ri(Kiaj−Kiai+aj)2,4Kiai(Kjaj−Kjdj−dj)airiK2i+rjKj(Kiai−Kiaj−aj)2}. |
In addition, since both
x1=F(x2)≥F(0)=a2d1a1r2ρ1+a1a2−a2d1 |
andx2=G(x1)≥G(0)=a1d2a2r1ρ2+a1a2−a1d2. |
Therefore, we have
Now assume that
fb(x2)|a1=a2=a=a[r2ρ1(K2−x2)+K2(a−d1)]andgb(x1)|a1=a2=a |
=a[r1ρ2(K1−x1)+K1(a−d2)] |
which indicates that
a>max{d1,d2},F(xc2)<K1,andG(xc1)<K2. |
Applying the similar arguments for the case
max0≤x2≤K2{F(x2)}=F(xc2)≤max0≤x2≤K2{ft(x2)}min0≤x2≤K2{fb(x2)}=fb(K2/2)fb(K2)=K2r2ρ1+4d14(a1−d1) |
and
max0≤x1≤K1{G(x1)}=G(xc1)≤max0≤x1≤K1{gt(x1)}min0≤x1≤K1{gb(x1)}=gt(K1/2)gb(K1)=K1r1ρ2+4d24(a2−d2). |
Therefore, we can conclude that Model (4) has at least one interior equilibrium
a1=a2=a>max{d1,d2},ρi<4(Kia−Kidi−di)Kjrj |
for both
Proof of Theorem 3.9.
Proof.Suppose that
xi(xj)=ρiqj(xj)pj(xj)+diai(1+ρiqj(xj))−(ρiqj(xj)pj(xj)+di)=ρiqj(xj)pj(xj)+diρiqj(xj)[ai−pj(xj)]+ai−di |
which indicates that
xi(μj)=ρiqj(μj)pj(μj)+dρiqj(μj)[ai−pj(μj)]+ai−d=dai−d=μi. |
This implies that
H(λ)=λ4+(α1+α2)λ3+[α1α2+d(β1+β2)]λ2+d(α1β2+α2β1)λ+d2(β1β2−γ1γ2=0 |
where
αi=−riμi(Kiai−Kid−ai−d)Kiai⇒[αi>0⇔Kia1−Kid−ai−d<0⇔Ki−12<μi<Ki]βi=νi(νjρi+1)(ai−d)2ai>0γi=ρiνiνj(aj−d)2aj>0β1β2−γ1γ2=ν1ν2(a1−d)(a2−d)2(ν1ρ2+ν2ρ1+1)a1a2>0. |
Then the real parts of the solutions of
μ1(K1a1−K1d−a1d)K1a1+rμ2(K2a2−K2d−a2−d)K2a2>0. |
Assume that
ρi>max{−νj−rjμiμj(Kiai−Kid−ai−d)(Kjaj−Kjd−aj−d)(KiKjajνjdνi(ai−d)2), |
−μiνjKj(νiρj+1)(aj−d)2(Kiai−Kid−ai−d)rjμjνiKi(ai−d)2(Kjaj−Kjd−aj−d)−1νj}. |
Now if
Now we should show that Model (4) has the unique
1.
μ<xc2=K(ρ1+a−d−√(a−d)(ρ1+a−d))ρ1∈(0,K). |
2.
μ<xc1=K(ρ2+a−d−√(a−d)(ρ2+a−d))ρ2∈(0,K). |
The discussions above indicate that both
Proof of Theorem 4.1.
Proof.Proof of Item 1 can be obtained by adopting the proof provided in Theorem 3.1. We omit details.
The stability of
Item 3(a): If
dxixidt|xi=0=ri>0. |
Item 3(b): Recall
Vij(xi,yi,yj)=(ρj+dj)∫xiKipi(ξ)−pi(Ki)pi(ξ)dξ+(ρj+dj)yi+ρiyj. |
If
dVij(xi,yi,yj)dt=(ρj+dj)[(pi(xi)−pi(Ki)]qi(xi)+yi(pi(Ki)−ˆdi)<0 |
since
Item 3(c): We construct the following Lyapunov function
Vij(xi,yi,yj)=(ρj+dj)∫xiˆμipi(ξ)−pi(ˆμi)pi(ξ)dξ+(ρj+dj)∫yiˆνiηi−ˆνiηidηi+ρi∫yjˆνijηj−ˆνijηjdηj. |
If
dVij(xi,yi,yj)dt |
=(ρj+dj)[(pi(xi)−pi(ˆμi)][qi(xi)−ˆνi]−ρiˆνi((ρj+dj)yj−ρjyi)2(ρj+dj)yiyj<0. |
Therefore, Model (13) has global stability at
Item 4: If
dxjxjdt|xj=0,yj=0=rj>0 when ^μi>Ki |
and
dxjxjdt|xj=0,yj=ˆνij=rj−ajˆνij>0 when Ki−12<^μi<Ki. |
The persistence of both prey can be easily obtained from the persistence of one prey.
If
Item 5: We construct the following Lyapunov function
V(xi,yi,xj,yj)=(ρi+di)∫xjˆμjpj(ξj)−pj(ˆμj)pj(ξj)dξj+(ρi+di)∫yjˆνjηj−ˆνjηjdηj+ρixi+∫yiˆνjiηi−ˆνjiηidηi. |
Then we have
dV(xi,yi,xj,yj)dt=(ρj+dj)[(pi(xi)−pi(ˆμi)][qi(xi)−ˆνi]−ρiˆνi((ρj+dj)yj−ρjyi)2(ρj+dj)yiyj+ρjpi(xi)[qi(xi)−ˆνji]<(ρj+dj)[(pi(xi)−pi(ˆμi)][qi(xi)−ˆνi]−ρiˆνi((ρj+dj)yj−ρjyi)2(ρj+dj)yiyj+ρjpi(xi)[qi(Ki−12)−ˆνji]=(ρj+dj)[(pi(xi)−pi(ˆμi)][qi(xi)−ˆνi]−ρiˆνi((ρj+dj)yj−ρjyi)2(ρj+dj)yiyj+ρjpi(xi)[ri(Ki+1)24aiKi−ˆνji]. |
Therefore, if
Item 6: Define
dVdt=ρ2(p1(x1)−d1)y1+ρ1(p2(x2)−d2)y2. |
Notice that
dVdt=ρ2(p1(x1)−d1)y1+ρ1(p2(x2)−d2)y2<−δ(ρ2y1+ρ1y2). |
Therefore, both predators go extinct if
x′i=rixi(1−xiKi) |
which converges to
On the other hand, if
dVdt=ρ2(p1(x1)−d1)y1+ρ1(p2(x2)−d2)y2>δ(ρ2y1+ρ1y2). |
Therefore, both predators persist if
Item 7 can be obtained from Item 4 and Item 6.
Item 8 can be obtained from eigenvalues of the Jacobian matrix of Model (12) evaluated at the symmetric interior equilibrium
V(x1,y1,x2,y2)=ρ2∫x1μp1(ξ1)−p1(μ)p1(ξ1)dξ1+ρ2∫y1νη1−νη1dη1+ρ1∫x2μp2(ξ2)−p2(μ)p2(ξ2)dξ2+ρ1∫y2νη2−νη2dη2 |
which gives
dV(x1,y1,x2,y2)dt=ρ2(p1(ξ1)−p1(μ))(q1(x1)−K)+ρ1(p2(ξ2)−p2(μ))(q2(x2)−K) |
+ρ1ρ2ν(y1−y2)(1y1−1y2)y1y2. |
This research is partially supported by NSF-DMS(1313312); NSF-IOS/DMS (1558127) and The James S. McDonnell Foundation 21st Century Science Initiative in Studying Complex Systems Scholar Award (UHC Scholar Award 220020472). We also would like to acknowledge the partial support from Natural Science Foundation of Jiangsu Province (BK20140927), Tianyuan Fund for Mathematics of NSFC (11426132, 11601226), and from Nanjing Tech University. The research of K.M is also partially supported by the Department of Education GAANN (P200A120192). S.K.S. is partially supported by the NBHM post-doctoral fellowship. All authors would like to thank Dr. Andrea Bruder for the discussions on the modeling dispersal strategies in the early stage of this manuscript.
[1] | [ L. Aarssen,R. Turkington, Biotic specialization between neighbouring genotypes in lolium perenne and trifolium repens from a permanent pasture, The Journal of Ecology, 73 (1985): 605-614. |
[2] | [ R. F. Alder, Migration alone can produce persistence of host-parasitoid models, The American Naturalist, 141 (1993): 642-650. |
[3] | [ J. Bascompte,R. V. Solé, Spatially induced bifurcations in single-species population dynamics, Journal of Animal Ecology, 63 (1994): 256-264. |
[4] | [ B. M. Bolker,S. W. Pacala, Spatial moment equations for plant competition: Understanding spatial strategies and the advantages of short dispersal, The American Naturalist, 153 (1999): 575-602. |
[5] | [ C. J. Bolter,M. Dicke,J. J. Van Loon,J. Visser,M. A. Posthumus, Attraction of colorado potato beetle to herbivore-damaged plants during herbivory and after its termination, Journal of Chemical Ecology, 23 (1997): 1003-1023. |
[6] | [ C. Carroll,D. H. Janzen, Ecology of foraging by ants, Annual Review of Ecology and Systematics, 4 (1973): 231-257. |
[7] | [ A. Casal,J. Eilbeck,J. López-Gómez, Existence and uniqueness of coexistence states for a predator-prey model with diffusion, Differential and Integral Equations, 7 (1994): 411-439. |
[8] | [ P. L. Chesson,W. W. Murdoch, Aggregation of risk: Relationships among host-parasitoid models, American Naturalist, 127 (1986): 696-715. |
[9] | [ W. C. Chewning, Migratory effects in predator-prey models, Mathematical Biosciences, 23 (1975): 253-262. |
[10] | [ R. Cressman,K. Vlastimil, Two-patch population models with adaptive dispersal: The effects of varying dispersal speeds, Journal of Mathematical Biology, 67 (2013): 329-358. |
[11] | [ E. Curio, The Ethology of Predation ,Springer-Verlag Berlin Heidelberg, 7 1976. |
[12] | [ M. Doebli, Dispersal and dynamics, Theoretical Population Biology, 47 (1995): 82-106. |
[13] | [ W. Feng,B. Rock,J. Hinson, On a new model of two-patch predator-prey system with migration of both species, Journal of Applied Analysis and Computation, 1 (2011): 193-203. |
[14] | [ J. Ford, The Role of the Trypanosomiases in African Ecology. A Study of the Tsetse Fly Problem, in Oxford University Press, Oxford, 1971. |
[15] | [ A. G. Gatehouse, Permanence and the dynamics of biological systems, Host Finding Behaviour Of Tsetse Flies, null (1972): 83-95. |
[16] | [ S. Ghosh,S. Bhattacharyya, A two-patch prey-predator model with food-gathering activity, Journal of Applied Mathematics and Computing, 37 (2011): 497-521. |
[17] | [ M. Gillies,T. Wilkes, The range of attraction of single baits for some West African mosquitoes, Bulletin of Entomological Research, 60 (1970): 225-235. |
[18] | [ M. Gillies,T. Wilkes, The range of attraction of animal baits and carbon dioxide for mosquitoes, Bulletin of Entomological Research, 61 (1972): 389-404. |
[19] | [ M. Gillies,T. Wilkes, The range of attraction of birds as baits for some west african mosquitoes (diptera, culicidae), Bulletin of Entomological Research, 63 (1974): 573-582. |
[20] | [ I. Hanski, null, Metapopulation Ecology, Oxford University Press, Oxford, 1999. |
[21] | [ I. A. Hanski,M. E. Gilpin, null, Metapopulation Biology: Ecology, Genetics, and Evolution, Academic Press, San Diego, 1997. |
[22] | [ M. Hassell,R. May, Aggregation of predators and insect parasites and its effect on stability, The Journal of Animal Ecology, 43 (1974): 567-594. |
[23] | [ M. Hassell,T. Southwood, Foraging strategies of insects, Annual Review of Ecology and Systematics, 9 (1978): 75-98. |
[24] | [ M. Hassell,O. Miramontes,P. Rohani,R. May, Appropriate formulations for dispersal in spatially structured models: comments on bascompte & Solé, Journal of Animal Ecology, 64 (1995): 662-664. |
[25] | [ M. P. Hassell,H. N. Comins,R. M. May, Spatial structure and chaos in insect population dynamics, Nature, 353 (1991): 255-258. |
[26] | [ A. Hastings, Can spatial variation along lead to selection for dispersal?, Theoretical Population Biology, 24 (1983): 244-251. |
[27] | [ A. Hastings, Complex interactions between dispersal and dynamics: Lessons from coupled logistic equations, Ecology, 74 (1993): 1362-1372. |
[28] | [ C. Hauzy,M. Gauduchon,F. D. Hulot,M. Loreau, Density-dependent dispersal and relative dispersal affect the stability of predator-prey metacommunities, Journal of Theoretical Biology, 266 (2010): 458-469. |
[29] | [ R. D. Holt, Population dynamics in two-patch environments: Some anomalous consequences of an optimal habitat distribution, Theoretical Population Biology, 28 (1985): 181-208. |
[30] | [ S. Hsu,S. Hubbell,P. Waltman, A mathematical theory for single-nutrient competition in continuous cultures of micro-organisms, SIAM Journal on Applied Mathematics, 32 (1977): 366-383. |
[31] | [ S. Hsu, On global stability of a predator-prey system, Mathematical Biosciences, 39 (1978): 1-10. |
[32] | [ Y. Huang,O. Diekmann, Predator migration in response to prey density: What are the consequences?, Journal of Mathematical Biology, 43 (2001): 561-581. |
[33] | [ V. Hutson, A theorem on average liapunov functions, Monatshefte für Mathematik, 98 (1984): 267-275. |
[34] | [ V. Hutson,K. Schmit, Permanence and the dynamics of biological systems, Mathematical Biosciences, 111 (1992): 1-71. |
[35] | [ V. A. Jansen, Regulation of predator-prey systems through spatial interactions: A possible solution to the paradox of enrichment, Oikos, 74 (1995): 384-390. |
[36] | [ V. A. Jansen, The dynamics of two diffusively coupled predator-prey populations, Theoretical Population Biology, 59 (2001): 119-131. |
[37] | [ V. A. A. Jansen, Theoretical Aspects of Metapopulation Dynamics, PhD thesis, Ph. D. thesis, Leiden University, The Netherlands, 1994. |
[38] | [ Y. Kang,D. Armbruster, Dispersal effects on a discrete two-patch model for plant-insect interactions, Journal of Theoretical Biology, 268 (2011): 84-97. |
[39] | [ Y. Kang,C. Castillo-Chavez, Multiscale analysis of compartment models with dispersal, Journal of Biological Dynamics, 6 (2012): 50-79. |
[40] | [ P. Kareiva,G. Odell, Swarms of predators exhibit "prey-taxis" if individual predators use area-restricted search, American Naturalist,, 130 (1987): 233-270. |
[41] | [ P. Kareiva,A. Mullen,R. Southwood, Population dynamics in spatially complex environments: Theory and data [and discussion], Philosophical Transactions of the Royal Society of London B: Biological Sciences, 330 (1990): 175-190. |
[42] | [ S. Kéfi,M. Rietkerk,M. van Baalen,M. Loreau, Local facilitation, bistability and transitions in arid ecosystems, Theoretical Population Biology, 71 (2007): 367-379. |
[43] | [ P. Klepac,M. G. Neubert,P. van den Driessche, Dispersal delays, predator-prey stability, and the paradox of enrichment, Theoretical Population Biology, 71 (2007): 436-444. |
[44] | [ M. Kummel,D. Brown,A. Bruder, How the aphids got their spots: Predation drives self-organization of aphid colonies in a patchy habitat, Oikos, 122 (2013): 896-906. |
[45] | [ K. Kuto,Y. Yamada, Multiple coexistence states for a prey-predator system with cross-diffusion, Journal of Differential Equations, 197 (2004): 315-348. |
[46] | [ I. Lengyel,I. R. Epstein, Diffusion-induced instability in chemically reacting systems: Steady-state multiplicity, oscillation, and chaos, Chaos: An Interdisciplinary Journal of Nonlinear Science, 1 (1991): 69-76. |
[47] | [ S. A. Levin, Dispersion and population interactions, American Naturalist, 108 (1974): 207-228. |
[48] | [ R. Levins, Some demographic and genetic consequences of environmental heterogeneity for biological control, Bulletin of the Entomological Society of America, 15 (1969): 237-240. |
[49] | [ Z.-z. Li,M. Gao,C. Hui,X.-z. Han,H. Shi, Impact of predator pursuit and prey evasion on synchrony and spatial patterns in metapopulation, Ecological Modelling, 185 (2005): 245-254. |
[50] | [ X. Liu,L. Chen, Complex dynamics of Holling type Ⅱ Lotka--Volterra predator--prey system with impulsive perturbations on the predator, Chaos, Solitons & Fractals, 16 (2003): 311-320. |
[51] | [ Y. Liu, The Dynamical Behavior of a Two Patch Predator-Prey Model ,Honor Thesis, from The College of William and Mary, 2010. |
[52] | [ J. H. Loughrin,D. A. Potter,T. R. Hamilton-Kemp,M. E. Byers, Role of feeding-induced plant volatiles in aggregative behavior of the japanese beetle (coleoptera: Scarabaeidae), Environmental Entomology, 25 (1996): 1188-1191. |
[53] | [ J. Madden, Physiological reactions of Pinus radiata to attack by woodwasp, Sirex noctilio F.(Hymenoptera: Siricidae), Bulletin of Entomological Research, 67 (1977): 405-426. |
[54] | [ L. Markus, Ⅱ. Asymptotically autonomous differential systems, in Contributions to the Theory of Nonlinear Oscillations (AM-36), Vol. Ⅲ, Princeton University Press, 1956, 17–30. |
[55] | [ R. M. May, Host-parasitoid systems in patchy environments: A phenomenological model, The Journal of Animal Ecology, 47 (1978): 833-844. |
[56] | [ R. McMurtrie, Persistence and stability of single-species and prey-predator systems in spatially heterogeneous environments, Mathematical Biosciences, 39 (1978): 11-51. |
[57] | [ T. F. Miller,D. J. Mladenoff,M. K. Clayton, Old-growth northern hardwood forests: Spatial autocorrelation and patterns of understory vegetation, Ecological Monographs, 72 (2002): 487-503. |
[58] | [ W. W. Murdoch,C. J. Briggs,R. M. Nisbet,W. S. Gurney,A. Stewart-Oaten, Aggregation and stability in metapopulation models, American Naturalist, 140 (1992): 41-58. |
[59] | [ M. Pascual, Diffusion-induced chaos in a spatial predator-prey system, Proceedings of the Royal Society of London B: Biological Sciences, 251 (1993): 1-7. |
[60] | [ M. Rees,P. J. Grubb,D. Kelly, Quantifying the impact of competition and spatial heterogeneity on the structure and dynamics of a four-species guild of winter annuals, American Naturalist, 147 (1996): 1-32. |
[61] | [ M. Rietkerk,J. Van de Koppel, Regular pattern formation in real ecosystems, Trends in Ecology & Evolution, 23 (2008): 169-175. |
[62] | [ P. Rohani,G. D. Ruxton, Dispersal and stability in metapopulations, Mathematical Medicine and Biology, 16 (1999): 297-306. |
[63] | [ M. L. Rosenzweig,R. H. MacArthur, Graphical representation and stability conditions of predator-prey interactions, American Naturalist, 97 (1963): 209-223. |
[64] | [ G. D. Ruxton, Density-dependent migration and stability in a system of linked populations, Bulletin of Mathematical Biology, 58 (1996): 643-660. |
[65] | [ L. M. Schoonhoven, Plant recognition by lepidopterous larvae, (1972), 87–99. |
[66] | [ L. M. Schoonhoven, On the variability of chemosensory information, The Host-Plant in Relation to Insect Behaviour and Reproduction, Symp. Biol. Hung., 16 (1976), 261–266. |
[67] | [ L. M. Schoonhoven, Chemosensory systems and feeding behavior in phytophagous insects, (1977), 391–398. |
[68] | [ E. W. Seabloom,O. N. Bjørnstad,B. M. Bolker,O. Reichman, Spatial signature of environmental heterogeneity, dispersal, and competition in successional grasslands, Ecological Monographs, 75 (2005): 199-214. |
[69] | [ G. Seifert and L. Markus, Contributions to the Theory of Nonlinear Oscillations ,Princeton University Press, 1956. |
[70] | [ Y. Shahak,E. Gal,Y. Offir,D. Ben-Yakir, Photoselective shade netting integrated with greenhouse technologies for improved performance of vegetable and ornamental crops, International Workshop on Greenhouse Environmental Control and Crop Production in Semi-Arid Regions, 797 (2008): 75-80. |
[71] | [ R. V. Solé and J. Bascompte, Self-Organization in Complex Ecosystems ,Princeton University Press, Princeton, 2006. |
[72] | [ A. Soro,S. Sundberg,H. Rydin, Species diversity, niche metrics and species associations in harvested and undisturbed bogs, Journal of Vegetation Science, 10 (1999): 549-560. |
[73] | [ H. R. Thieme, Mathematics in Population Biology ,Princeton University Press, 2003. |
[74] | [ D. Tilman and P. M. Kareiva, Spatial Ecology: The Role of Space in Population Dynamics and Interspecific Interactions ,volume 30, Princeton University Press, 1997. |
[75] | [ J. van de Koppel,J. C. Gascoigne,G. Theraulaz,M. Rietkerk,W. M. Mooij,P. M. Herman, Experimental evidence for spatial self-organization and its emergent effects in mussel bed ecosystems, Science, 322 (2008): 739-742. |
[76] | [ J. K. Waage, Behavioral Aspects of Foraging in the Parasitoid, Nemeritis Canescens (Grav. ) ,PhD Thesis, from University of London, 1977. |
[77] | [ J. Wang,J. Shi,J. Wei, Predator-prey system with strong Allee effect in prey, Journal of Mathematical Biology, 62 (2011): 291-331. |
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Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
LAS and GAS if |
GAS if |
|
LAS if |
Does not exists | |
Does not exists | LAS if |
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
Persistence of prey | Always persist, dispersal of predator has no effects | One or both prey persist if conditions 4. in Theorem (4.1) holds. Small dispersal of predator in Patch |
Extinction of prey | Never extinct |
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
Persistence of predator | Predator at Patch |
Predators in both patches have the same persistence conditions. They persist if |
Extinction of predator | Simulations suggestions (see the yellow regions of Figure (1a) and Figure (3a)) that the large dispersal of predator in Patch |
Predators in both patches have the same extinction conditions. They go extinct if |
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
LAS and GAS if |
GAS if |
|
LAS if |
Does not exists | |
Does not exists | LAS if |
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
Persistence of prey | Always persist, dispersal of predator has no effects | One or both prey persist if conditions 4. in Theorem (4.1) holds. Small dispersal of predator in Patch |
Extinction of prey | Never extinct |
Scenarios | Model (4) whose dispersal is driven by the strength of prey-predator interactions | Classical Model (12) whose dispersal is driven by the density of predators |
Persistence of predator | Predator at Patch |
Predators in both patches have the same persistence conditions. They persist if |
Extinction of predator | Simulations suggestions (see the yellow regions of Figure (1a) and Figure (3a)) that the large dispersal of predator in Patch |
Predators in both patches have the same extinction conditions. They go extinct if |