ArticlePDF Available

A Structured Prey-Predator System with Alternative Diffusive Predator Resource

Authors:

Abstract and Figures

The present paper deals with a stage-structured prey-predator model having alternative diffusive resource for predator.The mathematical analysis with regard positivity, boundedness, equilibria and their stability with and without diffusion, and bifurcation are carried out. Using differential inequality, we obtain sufficient conditions that ensure the persistence of the system.Finally, analytical results are verified with the help of numerical simulations. http://ceser.in/ceserp/index.php/ijees/article/view/4969
Content may be subject to copyright.
A Structured Prey-Predator System with Alternative
Diffusive Predator Resource
Rachana Pathak1, Anuj Kumar2and Manju Agarwal 3
Department of Mathematics and Astronomy,
Lucknow University, Lucknow-226007, India
1rachanapathak2@gmail.com
2guptaanujkm89@gmail.com
3manjuak@yahoo.com
ABSTRACT
The present paper deals with a stage-structured prey-predator model having alternative
diffusive resource for predator.The mathematical analysis with regard positivity, bounded-
ness, equilibria and their stability with and without diffusion, and bifurcation are carried out.
Using differential inequality, we obtain sufficient conditions that ensure the persistence of
the system.Finally, analytical results are verified with the help of numerical simulations.
Keywords: Alternative Resource;Prey-Predator;Diffusion; Stability; Persistence.
2000 Mathematics Subject Classification: 49K05, 49K15, 49S05.
1 Introduction
The dynamics of prey-predator systems is one of the dominant subjects in mathematical ecol-
ogy due to its universal existence and importance.These interactions show a slight difference in
stability when a resource (such as predator’s resource) is present in the system, as it works as
an alternative source of intake besides the prey population. Such system has been considered
broadly, by several mathematicians, ecologists and biologists(Dubey and Das,2000,Dubey and
Upadhyay,2004;Freedman and Shukla,1989;Freedman and Krisztin,1992;He,1996;Sarkar and
Roy,1993;Shi,2009;Wang and Chen,1997) .There are many species in the nature, whose in-
dividual members have a life history that takes them through two stages : immature and
mature.Agarwal and Devi(2010) studied the effects of toxicants on the dynamics of a single
species growth model with stage structure consisting of immature and mature stages and also
showed that equilibrium level of immature population is more prone for the effects of toxicants
in comparison to the mature population.Agarwal and Devi (2010) proposed and analysed a
ratio-dependent predator-prey model where the prey population is stage structured and preda-
tor population is influenced by the resource biomass.They noted that the influence of resource
biomass on the predator population may lead to the extinction of prey population at a lesser
value of maturity time in comparison to the absence of the resource biomass.
International Journal of Ecological Economics and Statistics;
Volume. 38, Issue No. 3; Year 2017; Int. J. Ecol. Econ. Stat.;
ISSN 0973-1385 (Print), ISSN 0973-7537 (Online)
Copyright © 2017, [International Journal of Ecological Economics & Statistics]
ISSN 0973-1385 (Print), ISSN 0973-7537 (Online)
www.ceser.in/ceserp
www.ceserp.com/cp-jour
Keeping above all in mind we have developed a resource based prey-predator model. The dif-
fusion of the predator’s resource has also been taken into account. In the model, the stability
of the system has been analysed by using the theory of nonlinear ordinary differential equa-
tions. The prey population is taken to be structured according to two stages immature and
mature. The model has initially been analysed locally and globally without diffusion. We have
also studied the diffusivity coefficient with initial boundary conditions. Finally, it is concluded
that the large value of the diffusion coefficient makes the uniform steady state stable in both
the cases when the interior equilibrium is stable or when it is unstable without diffusion.
2 Mathematical Model
Let us consider a prey-predator system with alternative diffusive predator resource. In the
model, the prey is structured according to two different stages, immature xi(t, u, v)and mature
xm(t, u, v)population respectively.y(t, u, v)is the density of the predator. R(t, u, v )denotes the
resource present at time t0and coordinates (u, v)S, where Sis a simply connected
domain in uvplane.Let the specific rate of resource uptake per unit predator in unit time
is hR and supply rate of the external resource input to the system be constant and equal to
R0. Resource involved in predator growth, may be used due to consumption at a rate hRy
and its density also reduces due to certain degradation factors present in the environment
at a rate aR. Predator lose certain part of its density, at a rate gdue to death. The uptake
concentration of mature prey by predator is taken as of linear form at the rate l. Assuming that
at any time t>0birth into the immature prey population is proportional to the existing mature
prey population with proportionality constant αand the death rate of immature prey population
is proportional to that existing immature population, with proportionality constant γ. For mature
prey population, the death rate is taken to be logistic in nature, with proportionality constant
β. Finally, observing that those immature preys born at time tτthat survive to time texit
from the immature category and enter the mature prey population.Keeping in view of these
considerations, the non-linear model is proposed as follows
∂xi
∂t =αxmγxiαeγτxm(tτ),
∂xm
∂t =αeγτ xm(tτ)βx2
mlxmy
1+R+xm,
∂y
∂t =lxmy
1+R+xm+hRy gy2,
∂R
∂t =(R0aR)RhRy +dR2R,
,(2.1)
Imposing the following boundary and initial conditions on the system 2.1 as,
xi(0,u,v)=ψi(u, v )0,
xm(0,u,v)=ψm(u, v )0,
y(0,u,v)=θ(u, v )0,
R(0,u,v)=ψ(u, v )0,
(2.2)
∂xi
∂n =∂xm
∂n =∂y
∂n =∂R
∂n =0,(2.3)
xi(0) 0,x
m(t)=φm(t)0,τt<0,y(0) 0,R(0) 0.(2.4)
International Journal of Ecological Economics & Statistics
88
where nis the unit outward normal to the region ∂S .ψi
mand ψare smooth initial functions.
Sis simply connected domain in the uvplane with piecewise smooth boundary ∂S .2
2
∂u2+2
∂v2is the Laplacian diffusion operator.dRis the co efficient of R.
Here we first analyse model 2.1.For continuity of initial conditions,we require
xi(0) = 0
τ
αeγsφm(s)ds, (2.5)
the total survivors of these prey members who were born between τand 0.With the help of
2.5,the solution of the first equation of system 2.1 can be written in terms of solutions of xmas
follows
xi(t)=t
tτ
αeγ(ts)xm(s)ds, (2.6)
Now from equations 2.5 and 2.6, we can noted that mathematically no information of xi(t)is
needed for the system 2.1.Using the equations 2.5 and 2.6,we can find the properties of the xi
if we know the properties of xm.Now we consider the following model for analysis
∂xm
∂t =αeγτ xm(tτ)βx2
mlxmy
1+R+xm,
∂y
∂t =lxmy
1+R+xm+hRy gy2,
∂R
∂t =(R0aR)RhRy +dR2R,
,(2.7)
boundary and initial conditions on the system 2.7 as,
xm(0,u,v)=ψm(u, v )0,y(0,u,v)=θ(u, v)0,R(0,u,v)=ψ(u, v)0,(2.8)
∂xm
∂n =∂y
∂n =∂R
∂n =0,x
m(t)=φm(t)0,τt<0,y(0) 0,R(0) 0.(2.9)
3 Analysis of the model system without Diffusion
Model 2.1 without diffusion takes the following form
dxm
dt =αeγτ xm(tτ)βx2
mlxmy
1+R+xm
,
dy
dt =lxmy
1+R+xm
+hRy gy2,
dR
dt =(R0aR)RhRy,
(3.1)
3.1 Positivity of Solutions
Theorem 3.1. All solutions of the system 3.1 are positive for all t0.
P roof Clearly y(t)and R(t)for y(0) >0,R(0) >0,t > 0.Now xm(0) >0, hence if there
exists t0such that xm(t0)=0, then t0>0. Assume that t0is the first time such that xm(t)=0,
that is t0=inf {t>0:xm(t)=0}. Then
˙xm(t0)=αeγτ φm(t0τ)>0,(0 t0τ)
αeγτ φm(t0τ)>0,(t0),(3.2)
International Journal of Ecological Economics & Statistics
89
so that ˙xm(t0)>0.Hence for sufficiently small ε>0,˙xm(t0ε)>0.But by the definition of
t0,˙xm(t0ε)0,a contradiction. Hence xm(t)>0for all t0.
3.2 Boundedness of Solutions
In the following lemma, we state the bounds of the various variables which would be needed
in our study.
Lemma 3.2. The set Ω={(xm,y,R):0xmA, 0yA2and0RA1},is the re-
gion of attraction for all solutions initiating in the interior of the positive octant, where A=
αeγτ
β,A
2=lA +hA1
gand A1=R0
a.
P roof Let (xm,y,R)be solution with positive initial values (xm0,y
0,R
0). From system 3.1, we
get
dxm
dt αeγτ xm(tτ)βx2
m.(3.3)
According to comparison principle, it follows that
lim
t→∞ sup xmαeγτ
β=A. (3.4)
Now from the system 3.1, we get
dR
dt R0RaR2.(3.5)
According to comparison principle again, we get
lim
t→∞ sup RR0
a=A1.(3.6)
From the second equation of the system 3.1, we get
dy
dt =(lA +hA1)ygy2.(3.7)
Again using comparison principal, we have
lim
t→∞ sup ylA +hA1
g=A2.(3.8)
This completes the proof of lemma.
3.3 Equilibrium Analysis
The analysis of the system 3.1, we can get the following equilibria:
1. E0(0,0,0), this equilibrium point is obvious.
2. E1(xm1,0,0), where xm1=αeγτ
β.
3. E2(0,0,R
2), where R2=R0
a.
International Journal of Ecological Economics & Statistics
90
4. E3(xm3,0,R
3), where xm3=αeγτ
βand R3=R0
a, obtained by the equation 2.7.
5. E4(0,y
4,R
4), where y4=R0h
ag +h2and R4=R0g
ag +h2, obtained by the equation 2.7.
6. E5xm,¯y, 0), existence of equilibrium point E5is given as.
Here ¯xmand ¯yare the positive solutions of the system of algebraic equations given below
αeγτ β¯xml¯y
1+ ¯xm=0,
l¯xm
1+ ¯xmg¯y=0.(3.9)
From second equation of the system 3.9 we get
¯y=l¯xm
g(1 + ¯xm)(3.10)
Putting the value of ¯yfrom equation 3.10 in the first equation of the system 3.9 we have
following expression
Fxm)=¯
x3
m+2βg gαeγτ¯
x2
m+2gαeγτ +l2¯xmeγτ .(3.11)
From equation (3.11), we have
F(0) = gαeγτ <0.(3.12)
And
Fαeγτ
β=l2αeγτ
β>0.(3.13)
Thus there exists a ¯xm,0<¯xm<αeγτ
βsuch that Fxm).Now, the sufficient condition
for the uniqueness of E5is Fxm)>0.From 3.11 we can find and Fxm)as follows,
Fxm)=3¯
x2
m+22βg eγτ¯xm+2gαeγτ +l2>0.(3.14)
By using 3.11 in 3.14 we can check that Fxm)is positive. Hence the existence of E5.
7. E6(x
m,y
,R
)existence of this equilibrium point given as.
Here x
m,y
and Rare the positive solutions of the system of algebraic equations
αeγτ βx
mly
1+R+x
m=0,
lx
m
1+R+x
m+hRgy=0,
R0aRhy=0.
(3.15)
From last equation of the system 3.15,we have
y=R0aR
h.(3.16)
with condition
R0>aR
.(3.17)
International Journal of Ecological Economics & Statistics
91
From first equation of the system 3.15, we get following expression
R=p1x2
m+p2x
m+p3
p4+p5x
m
.(3.18)
where p1=βh,p2=h(βαeγτ ),p
3=R0lhαeγτ ,
p4=al +hαeγτ ,p
5=βh.
Using the value of yand Rin the second equation of the system 3.15, we have
G(x
m)=b1x4
m+b2x3
m+b3x2
m+b4xm+b5.(3.19)
where
b1=p1h2+ag(p1+p5),
b2=p2
5(hl gR0)+h2+ag(q1+p1p4+p2p5)+h2gR0+agp1p5,
b3=gR0p2
5+q4+hlq4+h2+ag(q2+p2p4+p3p5)+h2gR0+ag(p1p4+p2p5),
b4=gR0p2
4+q4+hlp2
4+h2+ag(q3+p3p4)+h2gR0+ag(p2p4+p3p5),
b5=(p3+p4)h2+agp3gR0p4,
q1=2p1p2,q
2=p2
2+2p1p3,q
3=2p2p3,q
4=2p4p5.
From equation 3.19, we have
G(0) = (p3+p4)h2+agp3gR0p4<0.(3.20)
if h2+agp3<gR
0p4.
And
Gαeγτ
β=b1βαeγτ
β4
+b2αeγτ
β3
+b3αeγτ
β2
+b4αeγτ
β+b5>0.
(3.21)
Thus there exists a x
m,0<x
m<αeγτ
βsuch that G(x
m).Now, the sufficient condition
for the uniqueness of E6is G(x
m)>0.From 3.20 we can find and G(x
m)as follows,
G(x
m)=4b1x3
m+3b2x2
m+2b3xm+b4>0.(3.22)
By using 3.20 in 3.22 we can check that G(x
m)is positive.
Hence the existence of E6.
3.4 Local Stability Analysis
To discuss the local stability of the system 3.1,we compute the variational matrices correspond-
ing to each equilibrium point.The entries of general variational matrix are given by differentiat-
ing the right side of system 3.1 with respect to xm,y and R.From these matrices we note the
following results:
1. The equilibrium point E0is unstable manifold in xmRplane.
International Journal of Ecological Economics & Statistics
92
2. The equilibrium points E1and E2are unstable points in yRand xmyplane respec-
tively.
3. The equilibrium point E3and E4is unstable in yand xmdirection respectively.
4. The equilibrium point E5is unstable in xmdirection if αe(γ+λ)τ(a+R0)g+h2>
hlR0in presence of τand in absence of τ,α(a+R0)g+h2>hlR
0.
5. The characteristic polynomial corresponding to interior equilibrium point is given as:
λ3+l1λ2+l2λ+l3+eλτ l4λ2+l5λ+l6=0.(3.23)
where
l1=a22 a33 +g11;l2=a12 a21 a23a32 +a22 a33 a22g11 a33 g11,
l3=a13a21a32 +a12a21 a33 a23a32 g11 +a22a33 g11;l4=αeγτ ;l5=αeγτ (a22 +a33 ),
l6=αeγτ (a23a32 a22a33),
a12 =lxm
1+R+xm,a
13 =lxmy
(1+R+xm)2,a
21 =(1+R)ly
(1+R+xm)2,a
22 =lxm
1+R+xm+hR 2gy,
a23 =hy lxmy
(1+R+xm)2,a
32 =hR,
a33 =R02aR hy, g11 =2βxm(1+R)ly
(1+R+xm)2.
CaseA :τ=0The associated characteristic equation of the system 3.1 is
λ3+(l1+l4)λ2+(l2+l5)λ+l3+l6=0.(3.24)
By using Routh-Hurwitz criteria all roots of equation 3.24 have negative real parts if and only if
.
(H1):l1+l4>0,l
2+l5>0and Δ=(l1+l4)(l2+l5)(l3+l6)>0.So the equilibrium point
E6is locally asymptotically stable when H1holds.
CaseB :τ== 0 Let λ=be one such that.Substituting this in equation 3.23 and equating
real and imaginary parts, we get
l5ωcosωτ l6l4ω2sinωτ =ω3l2ω. (3.25)
l6l4ω2cosωτ +l5ωsinωτ =l1ω2l3.(3.26)
Squaring and adding the equations 3.25 and 3.26, we get
ω6+l2
1l2
42l2ω4+l2
2l2
52l1l3+2l4l6ω2+l2
3l2
6=0.(3.27)
We define
H(ω)=ω6+l2
1l2
42l2ω4+l2
2l2
52l1l3+2l4l6ω2+l2
3l2
6and assume that
International Journal of Ecological Economics & Statistics
93
H2:H(0) = l3<l
6holds.
It is easy to check that H(0) <0if H2holds and H()>0.Therefore, the equation 3.27
always has at least one positive root.
Again solving equations 3.25 and 3.26, we get a critical value of delay given as follows
τ=1
ωcos1l6l4ω2l1ω2l3l5ω2l2ω2
l2
5ω2+(l6l4ω2)2+2
δ,k =0,1,2.... (3.28)
3.5 Hopf Bifurcation
Differentiating equation 3.23 with respect to τ,we obtained
1
=3λ2+2l1λ+l2+eλτ (2l4+l5)
λ(λ3+l1λ2+l2λ+l3)τ
λ.(3.29)
We can obtain here d(Reλ)
τ=τ0
=0.(3.30)
Verifying numerically it has been obtained that the transversality condition holds and hence
Hopf bifurcation occurs at τ=τ0.
3.6 Global Stability Analysis
Theorem 3.3. Let the following inequality holds in the region Ω
max βx
m(1 + R+x
m)
3(1+x
my+R),g, a(1 + R+x
m)
x
m(1 + y)>l
2,(3.31)
and
τ>1
γlog α
M1,
where
M1=βx
m3l(1 + x
my+R)
2(1+R+x
m),
then the equilibrium point E6is globally asymptotically stable.
proof For proving this theorem, we will show that
lim
t→∞
xm(t)=x
m,lim
t→∞
y(t)=y,lim
t→∞
R(t)=R.
Let us consider following positive definite function
V=1
2(xmx
m)2+yyyln y
y+RRRln R
R.(3.32)
The derivative of Vwith respect to time tis given as
dV
dt =αeγτ (xmx
m)(xmx
m)(tτ)β(xm+x
m)lx
my
(1 + R+xm)(1+ R+x
m)(xmx
m)2
g(yy)2a(RR)2+lx
m
(1 + R+xm)(1+ R+x
m)(yy)(RR)+ l(1 + R)
(1 + R+xm)(1+ R+x
m)
International Journal of Ecological Economics & Statistics
94
(xmx
m)(yy)+ lx
my
(1 + R+xm)(1+R+x
m)(xmx
m)(yy).(3.33)
Applying Cauchy-Schwartz inequality,we get following expression
dV
dt 1
2αeγτ (xmx
m)2+1
2αeγτ (xmx
m)2(tτ)g(yy)2a(RR)2
β(xm+x
m)lx
my
(1 + R+xm)(1+R+x
m)(xmx
m)2+1
2
lx
m
(1 + R+xm)(1+R+x
m)(RR)2
+1
2
lx
m
(1 + R+xm)(1+R+x
m)(yy)2+1
2
l(1 + R)
(1 + R+xm)(1+R+x
m)(xmx
m)2
+1
2
l(1 + R)
(1 + R+xm)(1+R+x
m)(yy)2+1
2
lx
my
(1 + R+xm)(1+R+x
m)(xmx
m)2
+1
2
lx
my
(1 + R+xm)(1+R+x
m)(RR)2.(3.34)
Arranging similar terms,maximizing right hand side and assuming following inequality
max βx
m(1 + R+x
m)
3(1+x
my+R),g, a(1 + R+x
m)
x
m(1 + y)>l
2.We get
dV
dt ≤−M1(xmx
m)2M2(yy)2M3(RR)2+1
2αeγτ (xmx
m)2+1
2αeγτ (xmx
m)2(tτ).
(3.35)
where
M1=βx
m3l(1 + x
my+R)
2(1+R+x
m),M
2=gl
2,M
3=alx
m(1 + y)
2(1+R+x
m).Now we assume
following Lyapunov function
V1=V+αeγτ
2t
tτ
(xmx
m)2(θ)dθ, (3.36)
and,hence
dV1
dt =dV
dt +αeγτ
2(xmx
m)2(t)αeγτ
2(xmx
m)2(tτ).(3.37)
Substituting the value of dV
dt in equation 3.37,we have
dV1
dt ≤−M1(xmx
m)2M2(yy)2M3(RR)2+αeγτ (xmx
m)2.(3.38)
Therefore
dV1
dt ≤−M1αeγτ (xmx
m)2M2(yy)2M3(RR)2.(3.39)
The last expression is negative definite provided that
τ>1
γlog α
M1.
Using the application of the Lyapunov-LaSalle type theorem (Ma etal.,2009) we get required
result
lim
t→∞
xm(t)=x
m,lim
t→∞
y(t)=y,lim
t→∞
R(t)=R.
This completes the proof of the theorem(3.3).
International Journal of Ecological Economics & Statistics
95
3.7 Permanence of Solutions
Theorem 3.4. Assume that αeγτ >lA
2and R0>hA
2. Then system 3.1 is permanent.
P roof
From first equation of the system 3.1,we get
dxm
dt αeγτ xm(tτ)lA2xmβx2
m,, (3.40)
According to comparison principle,it follows that
xmmin =αeγτ lA2
β=A3.(3.41)
with condition αeγτ >lA
2.Similarly way, we get from the second equation of the system 3.1.
dy
dt lA3
1+A1+A+hA1ygy2.. (3.42)
By using comparison principle,we get
ymin =1
glA3
1+A1+A+hA1=A4.(3.43)
From the last equation the system 3.1 we get
dR
dt (R0hA2)RaR2.(3.44)
Again using comparison principle,we have
Rmin =R0hA2
a.(3.45)
with condition R0>hA
2.Hence the Theorem follows.
4 Model with Diffusion
In this section considering the model 2.7 and noting that as a sequence xm=x
m,y =y,R =
Rare the uniform steady points for this system.Here, it is required to show that if E6is asymp-
totically stable for system 3.1, then the corresponding uniform steady state is asymptotically
stable for system 2.7.Further, the cases where E6is unstable for the system 3.1,but the corre-
sponding uniform steady state is uniform for 2.7 is discussed.This is supported by choosing a
positive definite function.
W(t)=S
V(xm,y,R)dA. (4.1)
Where Vis same as defined in 3.32.Differentiating Wwith respect to time along the solutions
of model 2.7,we obtain
dW
dt =I1+I2.(4.2)
Where
I1=S
dV
dt dA. (4.3)
International Journal of Ecological Economics & Statistics
96
I2=Sd1
∂V
∂xm
2xm+d2
∂V
∂y 2y+dR
∂V
∂R2RdA. (4.4)
Since dV
dt is negative definite,I1is also the same sign as dV
dt .
The Vconsists of the following properties:
∂V
∂xm
|∂S =∂V
∂y |∂S =∂V
∂R|∂S =0 (4.5)
for all points of S.
2V
∂R∂xm
=2V
∂y∂xm
=0.(4.6)
2V
∂R2>0,2V
∂x2
m
>0,2V
∂y2>0.(4.7)
as d1=d2=0.So,the term which is left in I2is
I2=S
dR
∂V
∂R 2R. (4.8)
Using Green’s First Identity in the plane
S
F12G1dA =S
F1
∂G1
∂n dS1S
(F.G)dA. (4.9)
Now equation 4.8 can be written as
I2=S
dR
2V
∂R2∂R
∂u 2
+∂R
∂v 2dA. (4.10)
We concluded from the above analysis as follows:
1. if dV
dt is negative definite then dW
dt is also negative definite which gives that if the equi-
librium point E6is asymptotically global stable in absence of diffusion, then the corre-
sponding uniform steady state E6of boundary value problem 2.7 must also be globally
stable.
2. If dV
dt is positive definite then also dW
dt can be made negative definite with the increasing
value of dRwhich implies that if E6is unstable in the absence of diffusion then the cor-
responding uniform steady stable of 2.7 can be made stable by the increment made in
diffusion coefficient (i.e.dR).
Now,dealing with the case that the region under consideration Sis rectangle given by S=
{(u, v):0uδ1,0vδ2}
From 4.10, I2can be rewritten as,
I2=dRS
2V
∂R2(RR)
∂u 2
+(RR)
∂v 2dA (4.11)
where dA =dudv
δ2
0δ1
0(RR)
∂u 2
dudv =1
δ1δ2
01
0(RR)
∂v 2
du1dv. (4.12)
International Journal of Ecological Economics & Statistics
97
where u=u1δ1.Utilizing the following inequality (Denn,1975)in 4.11 we get
1
0∂x
∂u2
du π21
0
x2du. (4.13)
δ2
0δ1
0(RR)
∂u 2
dudv π2
δ1δ2
0δ1
0
(RR)2dudv =π2
δ2
1S
(RR)2dA. (4.14)
Similarly
δ2
0δ1
0(RR)
∂u 2
dudv π2
δ2
2S
(RR)2dA. (4.15)
Hence dW
dt =I1+I2can be written as
dW
dt S
VdAδ2
1+δ2
2π2
δ2
1δ2
2dRa2R
R2
0S
(RR)2dA.(4.16)
From 4.16, note that if dV
dt is positive definite then also dW
dt could be made negative definite by
increasing the diffusion coefficient dRto a sufficiently large value that is dR>δ2
1δ2
2R2
0
Ra2π2δ2
1+δ2
2SVdA,
then the uniform steady state is asymptotically stable.
5 Numerical simulation
This section is mainly based on numerical simulation due to the complexity of the analytical
solutions.Using numerical simulation instead of real world data,which of course would be of
great interest,has the advantage to isolate the effects of the species interaction easily.
We use the parameter values as α=8=0.1=0.9=0.5,l =2,h =1,g =0.4,R
0=
10,a=0.4.
Here, we also note that all conditions of local stability, global stability and persistence are
satisfied for the above set of parameter values.
International Journal of Ecological Economics & Statistics
98
Figure 1. Variation of population with time at τ=0.1.
Figure 2.Phase Portrait at τ=0.1.
Figure 3. Variation of population with time at τ=10.
International Journal of Ecological Economics & Statistics
99
Figure 4.Phase Portrait at τ=10.
Figure(1)and Figure(2) show that system is stable when value of τ=0.1and trajectories of
all population trend to their equilibrium points. When we increase the value of τthe density
of population decrease and trend to zero when value of τbecome 10 (see Figure(3)).Also
dynamic behaviour of the system become unstable when τ=10.The presentation of this
behaviour is shown by Figure (4).
6 Discussion
In this paper, a resource based prey-predator system has been proposed and analysed into
consideration where the prey is being structured, according to the two stages immature and
mature. In modelling process, we assume that the predator has alternative diffusive resource
besides the prey. The diffusion of resource has taken into account, which play an important
role in the dynamics of the system. The analysis of the system shows that diffusion coefficient
can effectively change the stability of the system.
Acknowledgements
Dr.Rachana Pathak thankfully acknowledges the NBHM PDF, Ref. No.(2/40(29)/2014/R&D-
11).
Prof.Manju Agarwal thankfully acknowledges the DST PROJECT, Ref.No.(SR/MS-23: 793/12).
Anuj Kumar thankfully acknowledges the Science and Engineering Research Board (SERB),
New Delhi, India for the financial assistance in the form of Junior Research Fellowship (SR/S4/MS:793/12).
International Journal of Ecological Economics & Statistics
100
References
Agarwal M., Devi S.,2010,Persistence in a ratio-dependent predatorprey-resource model
with stage structure for prey, Int. J. Biomath. 3,313-336.
Agarwal M., Devi S.2010, A time-delay model for the effect of toxicant in a single species
growth with stage structure, Nonlin. Anal. Real World Appl. 11,23762389. Denn M.K.,
1975, Stability of Reaction and Transport Process, Prentice Hall, Englewood Cliffs, New
Jersey.
Dubey B.,Das B.,2000, Modelling the interaction of two predators competing for a prey in a
diffusive system. Indian J. Pure appl. Math 31(7) : 823-827.
Dubey,B.,Upadhyay,R.K.,2004,Persistence and extinction of one-prey and two-predators
system,Nonlinear Anal.,Modelling and Control,9(4),307–329.
Freedman H.I. and Shukla J.B.,1989,The effect of a predator resource on a diffusive
preypredator system. Nat. Res. Model. 3,359-383.
Freedman, H.I., Krisztin T.,1992, Global stability in models of population analysis. Proc.
Royal Soc. of Edinburg,122 A, 69-84.
He,X., 1996,Stability and delays in a predator-prey system.J.Math.Anal.Appl.,198,355–
370.
Ma Z., Li W., Zhao Y.,Wang W., Zhang H., Li Z.,2009,Effects of prey refuges on a
predatorprey model with a class of functional responses: the role of refuges, Math. Biosci.
218,73-79.
Sarkar A. K.,Roy A.B.,1993, Oscillatory behaviour in a resource based plant behavior
model with random behaviour attack, Ecological Modelling 68,213-226.
Shi R.,Chen L.,2009,The study of ratio-dependent predator prey model with stage-structure
in the prey, Nonlinear Dyn. 58,443-451.
Wang,W.,Chen,L.,1997,A predator-prey system with stage-structure for preda-
tor,Comput.Math.Appl.,33,83–91.
International Journal of Ecological Economics & Statistics
101
ResearchGate has not been able to resolve any citations for this publication.
Article
Full-text available
In this paper, a mathematical model is proposed and analysed to study the dynamics of one-prey two-predators system with ratio-dependent pre- dators growth rate. Criteria for local stability, instabil ity and global stability of the nonnegative equilibria are obtained. The permanent co-existence of the three species is also discussed. Finally, computer simulat ions are performed to investigate the dynamics of the system.
Article
Full-text available
In this paper, a ratio-dependent predator–prey model with stage structure in the prey is constructed and investigated. In the first part of this paper, some sufficient conditions for the existence and stability of three equilibriums are obtained. In the second part, we consider the effect of impulsive release of predator on the original system. A sufficient condition for the global asymptotical stability of the prey-eradication periodic solution is obtained. We also get the condition, under which the prey would never be eradicated, i.e., the impulsive system is permanent. At last, we give a brief discussion.
Article
As a continuation of author's recent work (J. Math. Anal. Appl., 198 (1996), 355-370), a classical autonomous Lotka-Volterra predator-prey model with variable bounded delays is concerned. By means of Lyapunov functionals, we establish sufficient conditions on the global attractivity of the positive equilibrium of the model. As a corollary, we show that small delays do not change the global stability of the positive equilibrium of the model. An explicit estimate of the delays is also derived. We give also an affirmative answer to the open problem proposed in the previous paper. AMS (MOS) subject classification: 34D05, 34K20, 92D25.
Article
A mathematical model with diffusion is proposed and analyzed. We consider a resource based ecological model where two predators are competing with interference for a limited prey. Criteria for local stability, instability and global stability are obtained in the absence of diffusion. It is shown that, in the absence of intraspecific interaction of the predator species, the interior equilibrium becomes unstable. It is also shown that an unstable equilibrium state may be stabilized by incresing diffusion coefficients appropriately.
Article
A model of a predator-prey system with diffusion and predator resource is studied. Both constant and variable resources are considered. In the absence of diffusion, criteria for local stability, instability, and global stability of equilibria, as well as persistence and extinction, are obtained. It is shown that an otherwise unstable uniform equilibrium state may be stabilized by diffusion.
Article
This paper deals with a ratio-dependent predator-prey model where the prey population is stage-structured consisting of immature and mature stages and the predator population is influenced by the resource biomass. By means of a transformation of variables, we transform the model into a dynamical system in such a way that there is one-to-one correspondence between the positive values of the original model and the positive values of the transformed model, so that the results which are true for the transformed model are also true for the original model. Dynamical behaviors such as positivity, boundedness, stability, bifurcation and persistence of the model are studied analytically using theory of differential equations. Computer simulations are carried out to substantiate the analytical findings. It is noted that the influence of the resource biomass on the predator population may lead to the extinction of prey population at a lesser value of maturity time in comparison to the absence of the resource biomass.
Article
This paper studies the asymptotoc behavior of a predator-prey model with stage structure. It is found that an orbitally asymptotically stable periodic orbit exists in that model. When time delay due to gestation of predator and time delay from crowding effect of prey are incorporated, we establish the condition for the permanence of populations and sufficient conditions under which positive equilibrium of the model is globally stable.
Article
In this paper, we investigate a single-species growth model with stage-structure consisting of immature and mature stages for the effects of toxicants with constant maturation time-delay. We study the dynamics of our model in three cases: an instantaneous emission of toxicant, a constant emission of toxicant, and a periodic emission of toxicant into the environment. We present results on positivity and boundedness of all solutions under appropriate conditions. The model equations are analyzed mathematically with regard to the nature of equilibria and their stabilities using the theory of nonlinear differential equations and computer simulations. It is shown that under suitable conditions, there exists a globally asymptotically stable positive equilibrium. It is concluded from the analysis that as the concentration of toxicant in the environment increases, equilibrium densities of both immature and mature populations decrease. It is also noted that the effects of toxicants are more on the equilibrium level of immature population in comparison to the mature population.
Article
This paper considers the mathematical model of a resource-based plant-herbivore system with nutrient recycling and incorporation of the average number of herbivores attacking the plants. It has been shown that the supply rate of external resources and the ratio of parameters which take into account the loss of plant biomass due to grazing, litterfall and the herbivore mortality rate play an important role in shaping the dynamics of the plant-herbivore system. The criteria for existence of small- and large-amplitude non-constant periodic oscillations of plant biomass and herbivore numbers are derived.