effect of toxic metal on root and shoot biomass of a plant ......effect of toxic metal on root and...

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157 Available at http://pvamu.edu/aam Appl. Appl. Math. ISSN: 1932-9466 Vol. 9, Issue 1 (June 2014), pp. 157-185 Applications and Applied Mathematics: An International Journal (AAM) Effect of Toxic Metal on Root and Shoot Biomass of a Plant A Mathematical Model O.P. Misra and Preety Kalra School of Mathematics and Allied Sciences Jiwaji University Gwalior, M.P., 474011, India [email protected] , [email protected] Received:January 11, 2013; Accepted: April 30, 2014 Abstract In this paper, a mathematical model is proposed to study the impact of toxic metals on plant growth dynamics due to transfer of the toxic metal in plant tissues. In the model, it is assumed that the plant uptakes the metal from the soil through the roots and then it is transfered in the plant tissues and cells by transport mechanisms. It is observed experimently that when toxic (heavy) metals combines with the nutrient they form a complex compound due to which nutrient loses its inherent properties and the natural charaterstics of the nutrient are damaged. It is noticed that due to the presence of toxic (heavy) metal in the plant tissues and loss of inherent properties of nutrient due to reaction with the toxic metal, the growth rate of the plant decreases. In order to understand the impact on plant growth dynamics, we have studied two models: One model for a plant growth with no toxic effect and the other model for plant growth with toxic effect. From the analysis of the models the criteria for plant growth with and without toxic effects are derived. The numerical simulation to support the analytical results is done using MathLab. Keywords: Nutrient Concentration; Root and Shoot Biomass; Toxic Metal; Model; Equilibria and Stability AMS-MSC 2010 No.: 92B05, 92C80 1. Introduction The soil is a source of nutrients for plant growth, but it also acts as a sink for contaminants from industrial and agricultural waste materials [Basta et al. (2005); Bolan et al. (2003); Nwachukwu

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Page 1: Effect of Toxic Metal on Root and Shoot Biomass of a Plant ......Effect of Toxic Metal on Root and Shoot Biomass of a Plant A Mathematical Model O.P. Misra and Preety Kalra ... high

157

Available at http://pvamu.edu/aam

Appl. Appl. Math.

ISSN: 1932-9466

Vol. 9, Issue 1 (June 2014), pp. 157-185

Applications and Applied Mathematics:

An International Journal (AAM)

Effect of Toxic Metal on Root and Shoot Biomass of a Plant

A Mathematical Model

O.P. Misra and Preety Kalra

School of Mathematics and Allied Sciences Jiwaji University

Gwalior, M.P., 474011, India [email protected] , [email protected]

Received:January 11, 2013; Accepted: April 30, 2014 Abstract In this paper, a mathematical model is proposed to study the impact of toxic metals on plant growth dynamics due to transfer of the toxic metal in plant tissues. In the model, it is assumed that the plant uptakes the metal from the soil through the roots and then it is transfered in the plant tissues and cells by transport mechanisms. It is observed experimently that when toxic (heavy) metals combines with the nutrient they form a complex compound due to which nutrient loses its inherent properties and the natural charaterstics of the nutrient are damaged. It is noticed that due to the presence of toxic (heavy) metal in the plant tissues and loss of inherent properties of nutrient due to reaction with the toxic metal, the growth rate of the plant decreases. In order to understand the impact on plant growth dynamics, we have studied two models: One model for a plant growth with no toxic effect and the other model for plant growth with toxic effect. From the analysis of the models the criteria for plant growth with and without toxic effects are derived. The numerical simulation to support the analytical results is done using MathLab. Keywords: Nutrient Concentration; Root and Shoot Biomass; Toxic Metal; Model; Equilibria

and Stability AMS-MSC 2010 No.: 92B05, 92C80 1. Introduction

The soil is a source of nutrients for plant growth, but it also acts as a sink for contaminants from industrial and agricultural waste materials [Basta et al. (2005); Bolan et al. (2003); Nwachukwu

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158 O.P. Misra and Preety Kalra

and Agbede (2009)]. Over the last few years, the level of heavy metals in the agricultural fields are increasing as a consequence of increasing environmental pollution from industrial, agricultural and municipal wastes. Plants take heavy metals from soils through different reactions such as: absorption, ionic exchange, redox reactions, precipitation–dissolution, etc. Heavy metals, through their action, disturb plant metabolism, affecting respiration, photosynthesis, stomata opening and plant growth. Heavy metals such as lead, copper, zinc, in high concentrations, are toxic to plants, preventing their proper development. Plants uptake metals from soil through their roots and then transport within the plant and plant cells [Smical et al. (2008)]. Plants accumulate heavy metals in their tissue and their high concentrations are toxic to them. In an experiment with maize it has been shown that the presence of Aluminum concentration in plant tissue has reduced the growth rate of the plant [Lindon and Barreiro (1998)]. It is observed experimently that the heavy (toxic) metals (when they combine with nutrients) form a complex compound thereby destroying the inherrent properties of the nutrinets [Violante et al. (2010)]. Agricultural research almost completely rely upon experimental and empirical works, combined with statistical analysis so very few mathematical modelling analysis has been carried out in this direction [Leo et al. (1993); Verma et al. (2007); Gross (1990); Thornley (1976); Benjamin and Hardwick (1986); Pugliese (1988); Somma et al. (1988); Ittersum et al. (2002); Dercole et al. (2005); Ioslovich and Gautam (2005); Vance and Nevai (2007); DeAngelis and Gross (1992)]. Many of the models that have been used by agronomists and foresters to predict harvests and schedule fertilization, irrigation and pesticide application are of empirical form. A major limitation in all these approaches is the unpredictability of the environmental inputs [Gross (1990)]. Thornley initiated some work related to the mathematical modelling of individual plant growth processes in which the mathematical models were applied to a wide variety of topics in plant physiology [Thornley (1976)]. In the paper of [Verma (2007)], a study was conducted through mathematical models to understand the cadmium uptake by radish, carrot, spinach and cabbage. In this paper a dynamic macroscopic numerical model for heavy metal transport and its uptake by vegetables in the root zone is considered and analysed numerically. Some mathematical models to study the effects of toxic metal on plant growth do now exist [Verma et al. (2007); Gross (1990); Brune and Dietz (1985); Pishchik et al. (2002); Guala (2010); Thomas et al. (2005); Misra and Kalra (2012); Misra and Kalra (2013)]. Inspired by the above, therefore in this paper, a mathematical model is proposed in this paper to study the impact of toxic metals on plant growth dynamics due to the transfer of toxic metal in plant tissues.

2. Mathematical Model For the purpose of modelling, the plant is divided into root and shoot compartments in which the state variables considered are nutrient concentration and biomass. In the model, it is assumed that

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 159

the plant uptake the metal from the soil through the roots and then transfered it through the plant tissues and cells by transport mechanisms. It is further assumed in the model that the root and shoot biomass decrease due to damage of tissues and cells on account of the metal present in the components of the plant. It is also assumed in the model that the nutrient concentration in the root and shoot compartments decrease due to the formation of complex compounds with toxic metal. Model 1 (Model with no toxic effect) In the formulation of model, the plant is divided into two compartments, viz., the root and shoot compartments. The state variables associated with the each compartment are the root biomaas, shoot biomass and nutrient concentration. rW and sW denote the root biomass and shoot biomass,

respectively. 0S and 1S denote the nutrient concentration in the root and shoot compartments

respectively. Thus, to study the plant growth dynamics, the following model is proposed.

,)()()(= 011020011000 SSSDSSDWSrK

dt

dSrN

(1)

,)()()(),(= 1210200110111 SSSDSSDWSrCIuf

dt

dSsg

(2)

,)(=0

2

0

r

rrr

r

k

WWSr

dt

dW (3)

,)(=0

2

1

s

sss

s

k

WWSr

dt

dW

(4)

with the initial conditions as:

0>(0)0S , 0>(0)1S , 0>(0)rW , 0>(0)sW ,

where, NK is the nutrient uptake by the plant root and considerd independent of the amount of

root-mycorrhizal surface and its uptake characterstics. rWSr )( 0 and sWSr )( 1 represent the use of

the nutrient by the root and shoot compartments of the plant respectively (Thronley (1976) ). In the present analysis we assume the following forms for function )( 0Sr and )( 1Sr [Thronley

(1976); DeAngelis and Gross (1992)]:

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160 O.P. Misra and Preety Kalra

00 0 0

0

11

1 1 11

( ) = , ( ) > 0 > 0,

( ) = , ( ) > 0 > 0, and

(0) = 0,

r rr

S

s ss

Sr S m r S for S

K S

S er S m r S for S

K S

r

(5)

where, is the utilization coefficient. rm and sm are the proportion of total biomass allocated

to root and shoot biomass respectively, r and s are the resource-saturated rates of resource

uptake per unit of root and shoot biomass respectively, S is senescence constant, rK and sK are

half saturation constants. In the absence of nutrient concentration the plant will not grow and eventually will die out. u is the fraction of shoot in the form of leaf tissue. ),( 1CIfg is the

specific gross photosynthetic rate (Thornley, 1976) given.

,=),(1

1

11

pS

g eCI

CIlCIf

(6)

where, 1 is the maximum age of the shoot of plant. l is the specific leaf area of the whole plant.

I is the light flux density incident on the leaves in the shoot compartment, 1C is the 2CO

density and in plant. pS is the rate of senescence of the photosynthesis. β is the photochemical

efficency and γ is the conductance to CO2. In plant growth, it is considered that during the initial stage, i.e., during the lag phase, the rate of plant growth is slow. Rate of growth then increases rapidly during the exponential phase. After some time the growth rate slowly decreases due to limitation of nutrient. This phase constitutes the stationary phase. The terms

0

2

0 )(r

rr

k

WSr

and

0

2

1 )(s

ss

k

WSr

are taken as the diminishing growth phase and stationary phase in the plant growth dynamics. Where, 0rk is the maximum root biomass, 0sk is the maximum shoot biomass, r and s are

nutrient limiting coefficients, 10 1 0 20 0 1( ) and ( )D S S D S S represent the flux of nutrient from

shoot to root and root to shoot, respectively. 10D and 20D are transfer rates. 01S represents the

loss of nutreint due to leaching. 12S represent the loss of nutrient due to shedding of leaves,

where, 1 and 2 are rate constants. Model 2 (Model with toxic effect) Now, we consider the effect of toxic metal on plant growth dynamics by assuming that the growth of plant biomass is inhibitted and reduced due to the presence of the toxic metal in the soil. Let )(tC be the concentration of toxic metal in soil and )(tc be the concentration of toxic

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 161

metal in plant root. After incorporating the effect of toxic metal in Model 1, the resulting model is given as follows:

,)()()(= 01011020011000 SSSSDSSDWSrK

dt

dScrN (7)

,)()()(),(= 121210200110111 SSSSDSSDWSrCIuf

dt

dScsg (8)

,)(= 130

2

0 rr

rrr

r Wk

WWSr

dt

dW

(9)

,)(= 240

2

1 ss

sss

s Wk

WWSr

dt

dW

(10)

,= 0 KCCQdt

dC

(11)

,= CCC hfKC

dt

d

(12)

with the initial conditions as:

0>(0)0S , 0>(0)1S , 0>(0)rW , 0>(0)sW , 0>(0)C , 0>(0)C .

Here, 0Q is the constant input rate of toxic metal which is considered independent of the amount

of the root-mycorrhizal surface and its uptake characterstics. The term KC represents the uptake of toxic metal by root from soil. where, is the first order rate constant. is the soil

bulk density. K is the linear absorption coefficient. The term Cf represents the transfer of

toxic metal in the plant tissue (shoot tissue) and where f is the transfer rate of the toxic metal in

the plant tissue. The terms rW13 and sW24 represent the decrease in the growth of the plant

due to the presence of toxic metal in root and shoot, respectively; where, 1 and 2 represent the bioconcentration factors or bioavailability factors and are taken as follows [Nwachukwu and Agbede (2009); Smical et al. (2008)]:

KC

f

CCC

21 , .

(13)

The terms cS 01 and cS 12 represent the decrease in the nutrient concentration in the root and

shoot respectively due to the formation of complex compounds with toxic metal. 1 and 2 are

reaction rates of 0S and 1S with C respectively. h is the natural decay rate of C due to soil

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162 O.P. Misra and Preety Kalra

depletion on account of the natural process of leaching. is the natural decay rate of C on account of leaching and other natural process. Here, all the parameters NK , 10D , 20D , 1 , 2 ,

r , s , , rK , sK , S , 1 , u , l , I , 1C , , pS , 0rk , 0sk , r , s , 1 , 2 , 0Q , , , k , ,

f , 1 , 2 , 3 , 4 and h are taken as positive constants.

3. Boundedness and Dynamical Behavior

3.1. Analysis of Model 1

Now, we show that the solutions of the model given by (1) to (4) are bounded in a positive orthant in

4R . The boundedness of the solutions is given by the following lemma. Lemma 3.1. All the solutions of model will lie in the region

,,0,0),(

0:),,,(= 00

1

110

4101

s

ss

r

rr

gNsr

kW

kW

CIufKSSRWWSSB

as ,t for all positive initial values 4

0 1( (0), (0), (0), (0)) ,r sS S W W R where 1 1 2= min ( , ) .

Proof: By adding equations (1) and (2), we get

,)(),()(

101110 SSCIufK

dt

SSdgN

where, 1 1 2= min ( , ) and then by the usual comparison theorem we get, as ,t

.),(

1

110

CIufKSS gN

From equation (3), we get,

,1)(0

0

r

rrr

r

k

WWSr

dt

dW

.1

0

r

rrrrr k

WWm

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 163

Then, by the usual comparison theorem we get, as ,t :

r

rr

kW

0 .

Similarly from equation (4), we get

s

ss

kW

0 .

This completes the proof of lemma. Now we show the existence of the interior equilibrium *E of Model 1. The system of equations

(1) - (4) has one feasible equilibria ),,,( ***1

*0

*sr WWSSE . The equilibrium *E of the system is

obtained by solving the following equations:

0,=)()()( *01

*1

*020

*0

*110

**0 SSSDSSDWSrK rN (14)

0,=)()()(),( *

12*1

*020

*0

*110

**11 SSSDSSDWSrCIuf sg (15)

0,=0

*rrr kW (16)

0.=0

*sss kW (17)

Thus, from the above set of equations we get the positive equilibrium ),,,(= ***1

*0

*sr WWSSE ,

where

,= 0*

r

rr

kW

(18)

,= 0*

s

ss

kW

(19)

and the positive value of *

0S and *1S can be obtained by solving the following pair of equations:

0,=)()()(=),( 01102001100

0101 SSSDSSDk

SrKSSFr

rN

(20)

0.=)()(),(=),( 12010

10

01102 SSk

Srk

SrCIufKSSFs

s

r

rgN

(21)

From equations (20) and (21), we have:

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164 O.P. Misra and Preety Kalra

1. 0=,0)( 01 SF implies 0,=))((=)( 0110

2011011 NrNrrrrrr KKSKKlkmSlSf

2. 0=)(0, 11 SF implies 0,=)(=)( 12010112 SDDKSf N

3. 0=,0)( 02 SF implies 0,=))((=)( 010

201021 mKSmKkmSSf rrrrrrrr

4. 0=)(0, 12 SF implies 0,=))((=)( 120

212122 mKSmKkmSSf ssssssss

where

1201011 = DDl and ),(= 1CIufKm gN .

The two equations (20) and (21) intersect each other in the positive phase plane satisfying

0>/ 01 dSdS , for equation (20) and 0</ 01 dSdS , for equation (21), showing the existence of the

unique interior equilibrium *E . From equation (15) as 1 :

22010

*02010*

1

)(=

DD

SDDS . (22)

Now, we discuss the dynamical behaviour of the interior equilibrium point *E of the model given by (1)-(4) and for this local and global stability analysis have been carried out subsequently. The characteristic equation associated with the variational matrix about equilibrium *E is given by

0,=)( 2

231312

54 PPPPPPP (23)

where

*

1 10 20 1 2 10 2020

* * *10

3 10 20 2 421 0

* *21

5 1 3 20

= , = ,( )

( )= , = ,

( )

( )= , > 0.

r r r r

r

S

s s s s r

s r

s

s

m K WP D D P D D

K S

m K W e r S WP D D P

K S k

r S WP PP P

k

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 165

From the nature of the roots of the characteristic equation (23) we derive that the equilibrium point *E is always locally asymptotically stable.

Now, we discuss the global stability of the interior equilibrium point *E of the system (1)-(4). The non-linear stability of the interior positive equilibrium is determined by the following theorem. Therorem 3.2. In addition to assumptions (5), let )( 0Sr and )( 1Sr , satisfy in 1B

,)(0,)(0

,)(0,)(0

11

00

sssss

rrrrr

KmSrmSr

KmSrmSr

(24)

for some positive constants rK and sK less than 1. Then, if the following inequalities hold

120102

*2

2010 )(1<)(

DDmK

WmDD

rrr

rrr ,)(1 220102

*

DDmK

Wm

sss

sss (25)

2

20 )(1

11

rrrr

rrrrr mKk

Kmm

,)(

)(12

0

*0

120102

*

r

r

rrr

rrr

k

SrDD

mK

Wm

(26)

2

20 )(1

11

ssss

sssss mKk

Kmm

,)(

)(12

0

*1

220102

*

s

s

sss

sss

k

SrDD

mK

Wm

(27)

*E is globally asymptotically stable with respect to solutions initiating in the interior of the

positive orthant. Proof: Since 1B is an attracting region, and does not contain any invariant sets on the part of its

boundary which intersect in the interior of 4R , we restrict our attention to the interior of 1B . We

consider a positive definite function about *E

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166 O.P. Misra and Preety Kalra

*

**2*11

2*00101 )(

2

1)(

2

1=),,,(

r

rrrrsr

W

WlnWWWSSSSWWSSV

*

**

s

ssss

W

WlnWWW .

Then, the derivatives along solutions, 1V is given by

01102001100*

001 )()()()(= SSSDSSDWSrKSSV rN

12102001101*

11 )()()(),()( SSSDSSDWSrCIufSS sg

01

*

00

*

1)(11)(1s

sss

s

s

r

rrr

r

r

k

WSrW

W

W

k

WSrW

W

W .

After some algebraic manipulations, this can be written as

012010*

0*

001 )()()(= SDDWSrKSSV rN

122010*

1*

11 )()(),()( SDDWSrCIufSS sg

0

*1

*

0

*0

* 1)()()

1)()(s

ssss

r

rrrr k

WSrWW

k

WSrWW

1)()())(())2()((

0010

**002010

*11

*00

r

rrrr k

WSSrWWSSDDSSSS

,1)()())((0

121**

11

s

ssss k

WSSrWWSS

where

* * *0 0 0 0 0 0,

1 0 *0 0 0,

( ( ) ( )) ( ),( ) =

( ), =

r S r S S S S SS

r S S S

and

* * *1 1 1 1 1 1

2 1 *1 1 1

( ( ) ( )) ( ),( ) =

( ), = .

r S r S S S S SS

r S S S

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 167

Note from (24) and the mean value theorem that

rrrrrr

rr KmSmK

m

|)(|

)(1 012 and sss

sss

ss KmSmK

m

|)(|

)(1 122.

We know that

),()(=)()( *0012010

*01012010

*0 SSDDWSSDDWSrK rrN

),()(=)()(),( *1122010

*121220101 SSDDWSSDDWSrCIuf ssg

,)()(

=1)( *

0

*0

0

*0 rr

r

r

r

rsr WWk

Sr

k

WSr

).()(

=1)( *

0

*1

0

*1 ss

s

s

s

ss WWk

Sr

k

WSr

Hence, 1V can be written as the sum of three quadratic forms,

332*

222*

11112*

001 )()(){(= aWWaSSaSSV rr 44

2*)( aWW ss

,}))(())(())(( 24**

1112*

11*

0013**

00 aWWSSaSSSSaWWSS ssrr where

* *11 1 0 10 20 1 22 2 1 10 20 2

* *0 1

33 440 0

12 10 20 13 0 1 00

24 1 2 10

= ( ) , = ( ) ,

( ) ( )= , = ,

= 2( ), = ( ) ( ) 1 ,

= ( ) ( ) 1 .

r s

r s

r s

r r

r

s s

s

a S W D D a S W D D

r S r Sa a

k k

Wa D D a r S S

k

Wa r S S

k

By Sylvester’s criteria, we find that 1V is negative definite if

,< 2211

212 aaa (28)

,2< 3311

213 aaa (29)

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168 O.P. Misra and Preety Kalra

and

224 22 44< 2a a a (30)

hold. However, (25) implies (28), (26) implies (29) and (27) implies (30). Hence, 1V is negative

definite and so 1V is a Liapunov function with respect to *E , whose domain contains 1B , proving the theorem. The above theorem shows, the system settles down to a steady state solution provided inequalities (25) to (27) hold. 3.2. Analysis of Model 2

Now, in the following we show that the solutions of model given by (7) to (12) are bounded in a positive orthant in

6R . The boundedness of solutions is given by the following lemma. Lemma 3.3. All the solutions of model will lie in the region

16 0 02 0 1 0 1

1

( , )= ( , , , , , ) : 0 , 0 ,0 ,N g r s

r s C r sr s

K uf I C k kB S S W W C R S S W W

,,00 00

h

QQC C

as t , for all positive initial values 6

0 1( (0), (0), (0), (0), (0), (0)) ,r s CS S W W C R where

1 1 2= min ( , ) . Proof: By adding equations (7) and (8), we get

,)(),()(

101110 SSCIufK

dt

SSdgN

where 1 1 2= min ( , ) and then by the usual comparison theorem we get, as :t

1

110

),(

CIufK

SS gN .

From equation (9), we get

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 169

00 1)(

r

rrr

r

k

WWSr

dt

dW

0

1r

rrrrr k

WWm

.

Then, by the usual comparison theorem we get, as :t

r

rr

kW

0 .

Similarly from equation (10), we get

s

ss

kW

0 .

From equation (11), we get

CQdt

dC 0 .

Then, by the usual comparison theorem we get, as :t

0Q

C .

From equation (12), we get,

CC h

KQ

dt

d

0 .

Then, by the usual comparison theorem we get, as :t

h

KQC

0 .

This complete the proof of the Lemma. Now, we find the interior equilibrium E

~ of Model 2. The system of equations (7) - (12) has one

feasible equilibria )~

,~

,~

,~

,~

,~

(~

10 Csr CWWSSE . The equilibrium E~

of the system is obtained by

solving the following equations,

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170 O.P. Misra and Preety Kalra

0,=~~~

)~~

()~~

(~

)~

( 0101102001100 SSSSDSSDWSrK CrN (31)

0,=~~~

)~~

()~~

(~

)~

(),( 12121020011011 SSSSDSSDWSrCIuf Csg (32)

0,~

1)~

( 130

0

r

rr

k

WSr (33)

0,~

1)~

( 240

1

s

ss

k

WSr (34)

0,=~~

0 CKCQ (35)

.0=~~~

CC hfCK (36)

Thus, from the above set of equations we get the positive equilibrium )~

,~

,~

,~

,~

,~

(=~

10 Csr CWWSSE ,

where

,)

~(

1=~

0

310

Sr

kW

r

rr

(37)

,)

~(

1=~

1

420

Sr

kW

s

ss

(38)

,=~ 0

K

QC

(39)

.~

~

hf

CKC

(40)

The positive value of 0

~S and 1

~S can be obtained by solving the following pair of equations:

0 1 3 01 0 1 0 10 1 0 20 0 1

1 0 1 0

( , ) = ( ) ( ) ( )

= 0,

r rN

r r

C

k kG S S K r S D S S D S S

S S

(41)

0 1 3 0 2 4 0 02 0 1 1 0 1 1 0

2 1 1 0 2 1

( , ) = ( , ) ( ) ( )

= 0.

r s r sN g C

r s r s

C

k k k kG S S K uf I C r S r S S

S S S

(42)

From equations (41) and (42), we have

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 171

1. 0=,0)( 01 SG implies 0,=)(=)( 20210201011 lKSlKlkmSlSg rrrrr

2. 0=)(0, 11 SG implies 0,=)(=)( 12010310112 SDDkKSg rNr

3. 0=,0)( 02 SG implies 0,=)(=)( 40430

203021 lKSlKlkmSlSg rrrrrr

4. 0=)(0, 12 SG implies 0,=)((=)( 41450

215122 lKSlKlkmSlSg ssssss

where

),~

(= 1120101 Cr DDl ,= 3102 rNr kKl ,)~

( 113 srCl

42031014 )),((= srsrgN kkCIufKl and srCl )~

( 225 .

The two equations (41) and (42) intersect each other in the positive phase plane satisfying

0>/ 01 dSdS , for equation (41) and 0</ 01 dSdS , for equation (42), showing the existence of the

unique interior equilibrium E~

. From equation (32), as 1 :

222010

020101 ~

~)(

=~

CDD

SDDS .

(43)

Now, we discuss the dynamical behaviour of the interior equilibrium point E

~ of the model given

by (7)-(12) and for this local and global stability analysis have been carried out subsequently. The characteristic equation associated with the variational matrix about equilibrium E

~ is given

by

0,=432

23

14

87 aaaaJJ (44)

where

,= 64211 JJJJa

,)~

()~

())(()(= 51306421642

2010212 JSrJSrJJJJJJDDJJa

2

3 1 2 10 20 1 2 4 6 1 2 4 6 0 3 2 6

1 5 1 4

= ( ( ) ) ( )( ) ( ) ( )

( ) ( ),

a J J D D J J J J J J J J r S J J J

r S J J J

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172 O.P. Misra and Preety Kalra

513041516230642

2010214 )~

()~

()~

()~

())((= JSrJSrJJJSrJJJSrJJDDJJa and

.=,=

,~

)~

(=,

)~

(

~=

,~

)~

(=,

)~

(

~=

,~

)~

(

~=,

~

)~

(

~=

87

0

16

1

425

0

04

0

313

22201021

1

211201020

1

hfJKJk

WSrJ

Sr

WJ

k

WSrJ

Sr

WJ

DDSK

eWKmJDD

SK

WKmJ

s

sss

r

rrr

C

s

S

ssssC

r

rrrr

From the Routh-Hurwitz's criteria it is found that E~

is locally asymptotically stable if0,0,0,0 4321 aaaa and 02

3421321 aaaaaa .

Now, we discuss the global stability of the interior equilibrium point E

~ of the system (7)-(12).

The non-linear stability of the interior positive equilibrium state is determined by the following theorem. Therorem 3.4. In addition to assumptions (5) , let )( 0Sr and )( 1Sr satisfy in 2B ,

,)(0 0 rrmSr ,)(0 0 rrr KmSr

,)(0 1 ssmSr sss KmSr )(0 1 , (46)

for some positive constants rK and sK less than 1. Then, if the following inequalities hold

112010221

2201021

~

)(1

~

9

4<))((

Crrr

rrr DDmK

WmAADDAA

10 20 2 22

,(1 )

s s sC

s s s

m WD D

K m

(47)

2

20

31 )(1

1

rrrr

rrrrr mKk

KmAAm

,)

~(~

)(1

~

9

4

0

0112010231

r

rC

rrr

rrr

k

SrDD

mK

WmAA

(48)

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 173

2

20

42 )(1

1

ssss

sssss mKk

KmAAm

,)

~(~

)(1

~

9

4

0

1222010242

s

sC

sss

sss

k

SrDD

mK

WmAA

(49)

<)(~ 2

133 CA C ,~

)(1

~

9

4112010235 KDD

mK

WmAA C

rrr

rrr

(50)

.~

)(1

~

9

4)(

~

222010245

2

144 KDDmK

WmAAC

K

fA C

sss

sssC

(51)

E~

is globally asymptotically stable with respect to solutions intiating in the interior of the positive orthant.

Proof: Since 2B is an atttracting region, and does not contain any invariant sets on the part of its

boundary which intersect in the interior of 6R , we restrict our attention to the interior of 2B .

We consider a positive definite function about E

~

r

rrrrCsr

W

WlnWWWASSASSACWWSSV ~

~~)

~(

2

1)

~(

2

1=),,,,,( 3

2112

2001102

2254 )

~(

2

1)

~(

2

1~

~~CC

s

ssss CCA

W

WlnWWWA

,

where, 1,=(iAi 2 , 3, 4 , 5) are arbitrary positive constants.

Then, the derivatives along the solutions, 2V is given by

01011020011000012 )()()()~

(= SSSSDSSDWSrKSSAV CrN

1212102001101112 )()()(),()~

( SSSSDSSDWSrCIufSSA Csg

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174 O.P. Misra and Preety Kalra

3 0 30

1 ( ) 1r r r Cr

r r

W WA W r S

W k C

4 1 40

1 ( ) 1s s s Cs

s s

W W fA W r S

W k KC

CCCC hfkCkCCQCCA )~

()~

( 05 .

After some algebraic manipulations, this can be written as

011201000012 )~

(~

)()~

(= SDDWSrKSSAV CrN

12220101112 )~

(~

)(),()~

( SDDWSrCIufSSA Csg

3 0 30

4 1 40

)( ) ( ) 1

( ) ( ) 1

r r Cr r

r

s s Cs s

s

WA W W r S

k C

W fA W W r S

k KC

CCCC hfKCCQCCA )~

()~

( 05

010012010211100 )~

)(~

())()(~

)(~

( SSSADDAASSSS CC

2 1 1 2 1 0 0

1 0 3 1 00

( )( ) ( )( )

( ) ( ) 1

C C r r

r r

r

A S S S S S W W

WA r S A S

k

1 1 2 1 4 2 1

0

( )( ) ( ) ( ) 1

( )( )

s ss s

s

C C

WS S W W A r S A S

k

C C K

33 3 3 1

44

4 4 1

( )( ) ( )( ) ( )

( )( )

( )( ) ( ),

C C r r r r C

C C s s

Cs s

W W A W W C C A CC

W W AC

fW W C C A C

K

where,

0 0 0 0 0 01 0

0 0 0

( ( ) ( )) ( ), ,( ) =

( ), = ,

r S r S S S S SS

r S S S

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 175

* * *1 1 1 1 1 1

2 1 *1 1 1

( ( ) ( )) ( ), ,( ) =

( ), = ,

r S r S S S S SS

r S S S

and

1

2

1 1( ), ,

( ) =1

, .

C C C CC C

C

C CC

Note from (46) and the mean value theorem that

rrrrrr

rr KmSmK

m

|)(|

)(1 012, sss

sss

ss KmSmK

m

|)(|

)(1 122 and

.|)(| 012

0

Q

CK

Q

We know that

),~

(~~

)(=)~

(~

)( 001120100101120100 SSDDWSSDDWSrK CrCrN

1 10 20 2 2 1

2 1 10 20 2 2 1 1

( , ) ( ) ( )

= ( ) ( ),

g s C

s C

uf I C r S W D D S

S W D D S S

),~

()

~(

=)

1)~

(0

0

00 rr

r

r

r

rr WWk

Sr

k

WSr

),~

()

~(

=1)~

(0

1

01 ss

s

s

s

ss WWk

Sr

k

WSr

),~

(=0 CCKKCCQ

.)()~

(= fhhf CCCC

Hence, 2V can be written as the sum of three quadratic forms,

442

332

222

11112

002 )~

()~

()~

()~

{(= aWWaWWaSSaSSV ssrr

1600121100662

552 )

~)(

~()

~)(

~()

~()

~( aSSaSSSSaaCC CCCC

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176 O.P. Misra and Preety Kalra

1 1 26 0 0 13

1 1 24 56

( )( ) ( )( )

( )( ) ( )( )

C C r r

s s C C

S S a S S W W a

S S W W a C C a

36 46 35

45

( )( ) ( )( ) ( )( )

( )( ) },

C C r r C C s s r r

s s

W W a W W a C C W W a

C C W W a

where

.=,)(~

,)(~

,=

,=

,=

,1)()(=,=

,1)()(=),)((=

,=,=

,)

~(

=,)

~(

=

,~~

)(=,~~

)(=

5614445

13335

3336

4446

12226

0124122401116

0013011320102112

66555

0

1444

0

0333

2220101222211201001111

KaCK

fAa

CAa

CAa

CAa

SAa

k

WSASrAaSAa

k

WSASrAaDDAAa

fhaKAak

SrAa

k

SrAa

DDWSAaDDWSAa

C

C

s

ss

r

rr

s

s

r

r

CsCr

By Sylvester’s criteria we find that 2V is negative definite if

,15

4<,

15

4<

,9

4<

,15

4<

,9

4<

,9

4<

,15

4<,

15

4<,

9

4<,

9

4<

66552566644

246

5544245

6633236

5533235

4422224

66222266611

2163311

2132211

212

aaaaaa

aaa

aaa

aaa

aaa

aaaaaaaaaaaa

(52)

hold. We note that inequalities in Equation (51), i.e., 6611216 15

4< aaa , 6622

226 15

4< aaa ,

,15

4< 6633

236 aaa 6644

246 15

4< aaa and 6655

256 15

4< aaa are satisfied due to arbitrary choice of 1A , 2A ,

3A , 4A and 5A , respectively, and above conditions reduces to the following conditions:

,9

4< 2211

212 aaa (53)

,9

4< 3311

213 aaa (54)

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 177

,9

4< 4422

224 aaa (55)

,9

4< 5533

235 aaa (56)

.9

4< 5544

245 aaa (57)

However, (47) implies (53), (48) implies (54), (49) implies (55), (50) implies (56) and (51) implies (57). Hence, 2V is negative definite and so 2V is a Liapunov function with respect to E

~,

whose domain contains 2B , proving the theorem. The above theorem shows, the system settles down to a steady state solution provided inequalities (47) to (51) hold.

4. Numerical Example

For the model 1, consider the following values of parameters-

10 20

1 0 0

1

1 2

= 10, = 1, = 1, = 1.5, = 1.2,

= 4, = 0.1, = 0.1, = 3, = 5,

= 0.01, = 90, = 20, = 20, = 0.5,

= 30, = 0.1, = 1, = 0.374, = 5,

= 0.014, = 1.2, = 1.4, = 0.1, = 0.2.

N s r s r

r s

s r

p r s

K K K

m m D D

S k k u

l C I

S

For the above set of parametric values, we obtain the following values of interior equilibrium *E

4.92=*0S , 56.4=*

1S , 16.67=*rW , ,14.29=*

sW

which is asymptotically stable (see Figure 1). Further, to illustrate the global stability of interior equilibrium *E of model 1 graphically, numerical simulation is performed for different initial conditions (see Table 1 and 2) and results are shown in Figures 2 and 3 for rWS 0 phase plane and sWS 1 phase plane respectively. All

the trajectories are starting from different initial conditions and reach to interior equilibrium *E .

Table 1. Different initial conditions for 0S and rW of Model 1

(0)0S 0.1 12 25 8

(0)rW 2 0.1 25 30

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178 O.P. Misra and Preety Kalra

Table 2. Different initial conditions for 1S and sW of Model 1

(0)1S 0.1 4 25 10

(0)sW 5 0.1 25 30

For the Model 2, with above set of parametric values and with the additional values of parameters given by

1 2

0 3

4

= 1.8, = 2, = 1, = 2.5, = 2.5,

= 0.75, 0.8, = 12, = 1, 0.1,

0.1,

h

K f Q

we obtain the following values of interior equilibrium E~

as

0.95=~

0S , 0.58=~

1S , 12.61=~

rW , 10.43=~

sW , 4.17=~C , 2.37. =

~C

For these set of parametric values, the stability conditions given in Equations (47)-(51) are satisfied. Hence, E

~ is asymptotically stable (see Figure 4).

Further, to illustrate the global stability of interior equilibrium E

~ of model 2 graphically,

numerical simulation is performed for different initial conditions (see Table 3 and 4) and results are shown in Figures 5 and 6 for rWS 0 phase plane and sWS 1 phase plane respectively. All

the trajectories are starting from different initial conditions and reach to interior equilibrium E~

.

Table 3. Different initial conditions for 0S and rW of Model 2

(0)0S 0.1 2 2 0.6

(0)rW 6 0.1 16 20

Table 4. Different initial conditions for 1S and sW of model 2

(0)1S 0.1 1 1.3 0.2

(0)sW 6 0.1 14 16

Tolerance indices (T.I.) are determined through the use of following formula [Kabir et al. (2008)]:

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 179

Mean root massin presenceof toxicant

. .( ) = 100Mean root massin absenceof toxicant

T I root

Meanshoot massin presenceof toxicant

. .( ) = 100Meanshoot massin absenceof toxicant

T I shoot

Table 5. Tolerance indices of root mass and shoot mass at different toxic input rate 0Q

when f = 0.8

S.No. Q0 Wr Ws T.I (Wr)% T.I(Ws)%

1 0 16.6667 14.2857 100 100

2 1 14.1207 12.3998 84.76 86.79

3 5 13.4270 11.6459 80.56 81.52

4 10 12.8228 10.7818 76.93 75.47

5 15 12.3166 9.9020 73.89 69.31

6 20 11.8603 8.9253 71.15 62.48

7 25 11.4345 7.8006 68.60 54.60

8 30 11.0295 6.4758 66.17 45.30

9 35 10.6385 5.0461 63.82 35.32

10 40 10.2569 3.7212 61.49 26.05

11 45 9.8819 2.6627 59.27 18.64

12 50 9.5123 1.8989 57.07 13.29

13 60 8.7856 1.0211 52.71 7.15

14 70 8.0691 0.6121 48.41 4.28

15 100 5.8564 0.2245 35.13 1.57

Table 6. Bioavailability factors or bioconcentration factors 1 and 2 at different value of f

when Q0 = 15

F Wr Ws C θc

β1 β2

0.1 10.72 13.44 5.22 3.76 0.72 0.04 0.2 11.00 12.72 5.22 3.62 0.69 0.07 0.3 11.27 12.09 5.22 3.49 0.67 0.11 0.4 11.51 11.53 5.22 3.37 0.65 0.14 0.5 11.74 11.05 5.22 3.26 0.63 0.17 0.6 11.94 10.62 5.22 3.15 0.60 0.19 0.7 12.14 10.23 5.22 3.05 0.59 0.22 0.8 12.31 09.89 5.22 2.96 0.57 0.24 0.9 12.48 09.58 5.22 2.87 0.55 0.26

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180 O.P. Misra and Preety Kalra

5. Conclusion

From Figures 7(a) and 7(b), is observed that the equilibrium levels of nutrient concentrations in each compartmentwith no toxic effect are more than that of the equilibrium levels of nutrient concentrations in respective compartments when toxiceffect is considered. Further, from Figures8(a) and 8(b), it is observed that the equilibrium levels of root biomass and shoot biomasswith no toxic effect are more than those of the root biomass and shoot biomass when toxic effect isbeing considered. From the non-trivial positive equilibrium E

~ (Table 5), it is

concluded that theroot biomass and shoot biomass decrease as the input rateof toxic metal 0Q

increases and this phenomena will continue till 0Q reaches 60thQ because upto this value of

0Q , the stability criteria continue to hold. From table 6, it is observed that as the transfer rate of

toxic metal from root to shoot increases, toxicant concentration factor in root tissues decreases and consequentely root biomass increases. On the contrary, toxicant concentration factor in shoot tissues increases as the transfer rate increases causing a decline of the shoot biomass. Figures 9(a) and 9(b) represent the dynamical behaviour of the nutrient concentration of root and shoot with respect to C . From these figures, it is observed that nutrient concentration in root and shoot

decrease as the level of the toxic metal concentration in root increases.

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182 O.P. Misra and Preety Kalra

Violante, A., Cozzolino, V., Perelomov, L., Caporale, A.G. and Pigna, M. (2010). Mobility and Bioavaility od Heavy Metals and Metalloids in Soil Environments, J.Soi. Sci. Plant Nutr. 10(3): 268-292.

Figure 1. Trajectories of the Model 1 with respect to time (with no toxic effect) showing

the stability behaviour

Figure27. Phase plane graph for nutrient concentration in root S0 and root biomass Wr at

different initial conditions given in Table 1 for Model 1 (with no toxic effect) showing the global stability behaviour.

0 50 100 150 200 250 3000

5

10

15

20

25

t

S

0(t)

S1(t)

Wr(t)

Ws(t)

0 5 10 15 20 25 300

5

10

15

20

25

Wr

S0

0 5 10 15 20 25 300

5

10

15

20

25

Ws

S1

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 183

Figure 3. Phase plane graph for nutrient concentration in shoot S1 and shoot biomass Ws at different initial conditions given in Table 1 for Model 1 (with no toxic effect) showing the global stability behaviour.

Figure 4. Trajectories of the model 2 with respect to time (with toxic effect) showing the

stability behaviour.

Figure 5. Phase plane graph for nutrient concentration in root S0 and root biomass Wr at

different initial conditions given in Table 3 for Model 2 (with toxic effect) showing the global stability behavior.

0 20 40 60 80 100 120 140 160 180 2000

2

4

6

8

10

12

14

t

S0(t)

S1(t)

Wr(t)

Ws(t)

C(t)

C(t)

2 4 6 8 10 12 14 16 18 200

0.2

0.4

0.6

0.8

1

1.2

1.4

1.6

1.8

2

Wr

S0

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184 O.P. Misra and Preety Kalra

Figure 6. Phase plane graph for nutrient concentration in shoot S1 and shoot biomass Ws

at different initial conditions given in Table 4 for Model 2 (with toxic effect) showing the global stability behaviour.

Figure 7(a). Graph between nutrient concentration of root S0 and time t for Model 1

(with no toxic effect) and for Model 2 (with toxic effect)

Figure 7(b). Graph between nutrient concentration in shoot S1 and time t for Model 1 (with no toxic effect) and for Model 2 (with toxic effect)

4 6 8 10 12 14 160

0.2

0.4

0.6

0.8

1

1.2

1.4

Ws

S1

W

0 50 100 150 200 250 3000

5

10

15

20

25

t

S0(t

)

With no toxic effect (model 1)

With toxic effect (model 2)

Q0 = 12

0 50 100 150 200 250 3000

5

10

15

20

25

t

S1(t

)

With no toxic effect (model 1)

With toxic effect (model 2)

Q0 = 12

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AAM: Intern. J., Vol. 9, Issue 1 (June 2014) 185

Figure 8(a). Graph between root biomass Wr and time t for Model 1 (with no toxic effect) and for Model 2 (with toxic effect)

Figure 8(b). Graph between shoot biomass Ws and time t for Model 1(with no toxic

effect) and for Model 2 (with toxic effect).

Figure 9(a). Phase Plane Graph of nutrient concentration in root S0 and θC for Model 2

when Q0 = 12.

0 50 100 150 200 250 3000

2

4

6

8

10

12

14

16

18

t

Wr(t

)

With no toxic effect (model 1)

With toxic effect (model 2)Q0 = 12

0 50 100 150 200 250 3000

2

4

6

8

10

12

14

t

Ws(t

)

With no toxic effect (model 1)

With toxic effect (model 2)

Q0 = 12

0.4 0.6 0.8 1 1.2 1.4 1.6 1.8 2

1.4

1.6

1.8

2

2.2

2.4

2.6

2.8

S0(t)

C(t

)

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186 O.P. Misra and Preety Kalra

Figure 9(b). Phase Plane Graph of nutrient concentration in shoot S1 and θC for Model

2 when Q0 = 12.

0.5 0.6 0.7 0.8 0.9 1 1.1 1.2 1.3

1.4

1.6

1.8

2

2.2

2.4

2.6

2.8

S1(t)

C(t

)