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B.R.Iniyalakshimi
Dept. of Soil Science and Agricultural Chemistry,
TNAU
MODELS
It is “an assembly of concepts in the form of
a mathematical equation that portrays
understanding of a natural phenomenon.”
Emprical models – statistical means
and regression- black box models
Mechanistic models- biophysical,
biochemical and physiological
mechanisms
TYPES
NUTRIENT UPTAKE MODELS
• Soil nutrient transformation models emphasize on soil
properties.
• Crop uptake models emphaize on plant characters
especially on root characters and also soil characters.
• Models are formed for (i) identifying the process which
describe nutrient uptake and (ii) evaluating quantitatively
the effect of different parameters of nutrient uptake.
• Extrapolation of a verified mechanistic model is more
reliable than that of an empirical model(Claassen and
Steingrobe, 1999).
• The typical mechanistic nutrient uptake model describes
the supply of nutrients from bulk soil to root surfaces, root
growth and morphology, and root uptake kinetics (Barber,
1995).
MECHANISTIC MODELS
Steady state models
• Flow of nutrients through a soil- steady state
• Soil – volume element conducting nutrient flow
• Neither a sink nor a source of nutrients
• based on diffusion theory
Transient models
• either a sink or source influencing / modifying its flux
(time)
• describes the dynamic process of nutrient uptake & the
concomitant changes in the ion concentration &
distribution in the rhizosphere.
SOIL NUTRIENT UPTAKE MODELING
Mechanisms
Mass flow
Diffusion
Root interception
Interception is used to describe the uptake of soil nutrients at the
root interface when soil volume is displaced by root volume
(Barber 1995).
Although conditions in the rhizosphere are sometimes different
from those in the bulk soil (Marschner 1995), the contribution of
interception to nutrient uptake is negligible for most nutrients
(Barber 1995).
Therefore, only mass flow and diffusion are considered to be
responsible for movement of nutrients to the root surface in
mechanistic modeling.
However, Tinker and Nye (2000) consider the concept of
interception to be somewhat arbitrary and argued that it can be
included in the diffusion component.
MASS FLOW
 Mass flow is the convective transport of nutrients through the
soil to the root surface by water flow as a result of transpiration
(Barber, 1995).
 The relative contribution of mass flow to nutrient uptake
depends on the nutrient, plant species, plant age, and time of
day (Marschner,1995).
 For example calcium and magnesium supplied to plants by
mass flow is significant, but its contribution to potassium
supply is negligible (Marschner, 1995).
 The influx by mass flow (FM) can be calculated by
 where v is the mean water flux in soil driven by transpiration,
and CL is the nutrient concentration in the soil solution.
DIFFUSION
 Diffusion is the movement of nutrients from areas of high
concentration to those of low concentration (Barber
1995).
 It is the main mechanism for at least phosphorus and
potassium movement in the soil to plant roots
(Marschner 1995).
 A depletion zone is produced when the concentration of
nutrient is lowered near the root surface due to root
absorption (Jungk and Claassen 1997). Diffusive flux FD
can be described by Fick’s first law,
 where D is the diffusion coefficient of the nutrient in soil,
C is the nutrient concentration in soil solution, and x is
the distance.
SIMULTANEOUS MASS FLOW AND DIFFUSION
 Mass flow and diffusion occur simultaneously to supply
nutrients to plant roots and cannot be treated as separate
processes.
 Nye and Spiers (1964) presented a partial differential
equation to describe simultaneous mass flow and
diffusion, and this equation became the foundation of the
most mechanistic nutrient uptake models.
 The Barber-Cushman model is largely based on the work
by Nye and Marriot (1969).
 Nye and Marriot (1969) revised the continuity equation
proposed by Nye and Spiers (1964) to describe the flux
of nutrient in the soil to the root surface with the nutrient
concentration in soil solution (CL)
 Nye and Marriot (1969) defined boundary conditions and
solved this equation numerically.
NYE AND MARRIOT (1969)
NYE AND TINKER MODEL
Nye and Tinker, 1977
The uptake of nutrient per unit length (U) is given by,
U= 2πrαC1
r = radius of the root
α = root absorbing power
C1= ion concentration at the root surface
 Summarizing the work by Claassen and Barber
(1976) and Cushman (1979), Barber and Cushman
(1981) suggested new boundary conditions to
include inter-root competition for nutrients.
 The new boundary conditions incorporated inter-
root competition as well as Michaelis-Menten
kinetics.
 When solved numerically, the enhanced
mechanistic model evolved into Barber-Cushman
model.
 Crop uptake is assumed to follow Michaelis-menten
relationship between concentration and flux.
 In 1983, Itoh and Barber developed a submodel to
the Barber-Cushman model to include nutrient
uptake by root hairs.
 In 1986 Claassen et al. published NST 1.0 model.
 In 1987 Oates and Barber published NUTRIENT
UPTAKE model.
 Both were based on the Barber-Cushman model.
MICHAELIS- MENTEN KINETICS
In=(Imax×Cla)/(Km+ Cla)
Where,
In = Rate of ion uptake
Imax = maximum rate of ion uptake when concentration is
not limiting
Cla = concentration of nutrient ion in soil solution at the
root surface
Km = Michaelis – menten constant which represents a
concentration of nutrient ion in soil solution when In=Imax/2.
COMPUTERIZED MODELS
 Based on Nye and Tinker model, Smethurst and Comerford
(1993b) developed a computer model, COMP8 (Competition
model version 8), which was able to calculate nutrient uptake
between two competing and contrasting root systems.
 SSAND was a revision and expansion of COMP8 by Comerford
et al. (2006).
 Its main improvements lie in the functions of predicting nutrient
uptake as influenced by mycorrhizae and simulation of
fertilization effects (Comerford et al. 2006).
 Based on COMP8 and an earlier version of
SSAND, another steady state model, PCATS was
developed to simulate nutrient uptake by a single
species by Smethurst et al. (2004).
 For transient models –NST 1.0, NST 3.0.
NYE AND TINKER, 2000
 where b is the soil buffer power,
 hence c = bc is the total amount of solute bound to the
soil particles;
 θ is the volumetric soil water content,
thus is the overall amount of solute per unit volume of soil;
 D is the solute diffusivity in water;
 f is the soil impedance factor,
 Dfθ is the effective diffusion coefficient for the solute in
the soil; and v is the water flux in the soil.
MODELLING CROP N UPTAKE
 Benbi, Prihar and Cheema (1991) – used mass flow
approach & predicted N uptake for wheat matched with
measured N uptake (wet treatments).
 In dry moisture regime other process of N uptake like
diffusion & root interception should be used.
BASED ON CROP DEMAND
 Several models - driven by demand from the plant.
 They calculate N demand for growth rates & concentration of N
required.
 Whitmore and Addiscott (1987) – computed demand using a
simple variant of the logistic function to compute the pattern of
N uptake (Y), with thermal time (x):
Y=(A-1/X + e-kx )-n
A - maximum of Y, n - shape factor, k - rate constant.
• Tillotson and Wagenet (1982) and Hutson and Wagenet
(1992) – modelled N uptake – based on Nye and Tinker
model.
• Warncke and Barber (1973) – value of α to be estabilished
for different soils, crops and species under a range of
concentrations.
• De Willigen, 1991 – more complex models give better
simulations than simpler ones.
TRANSFORMATION INCLUDING UPTAKE
 ANIMO
 Benbi’s model
 CANDY
 DAISY
 EPIC
 SWATNIT
M&M MODEL
 Satisfactorily describes P uptake flux (Fp, mol cm-1 root
h-1 ) as a function of P concentration in a well-stirred
solution (Cpb mol l-1 ).
Fp = Fp max * Cpa /(Km +Cpa )
 Fp max and Km denote the maximum Fp and Cpa at
which Fp = 0.5*Fmax .
P uptake models
Plant roots have a major influence on P dynamics in
the soil.
A= (b/a) w/2πDp
a,b = midway distance between root and root radius
Dp = diffusion co-efficient
B = Fpmax /W
W = solution velocity towards the root
Bar and Yosef (1999)
K concentration in
plant
K in soil
solution &
exchangea
ble
K flux to
roots by
mass flow &
diffusion
from soil
Root
parameters
Plant dry
biomass Fixed K
Weather parameters
Pottasium
fertilizers
Multi- Parametric model for K uptake
S UPTAKE
 Mc Caskill and Blair (1988) have developed a pseudo-
mechanistic computer simulation model for predicting
perennial pasture growth and S uptake.
 But not verified.
 Later Heng (1991) and Phimsarn(1991), developed
simple models of pasture S uptake using relationship
between actual daily ET(AET), average root density in
the soil profile, soil solution S levels, sulphate buffering
capacities.
MICRONUTRIENTS
 Mathematical models of micro-nutrient uptake by
plants have been based on models designed for
uptake of major nutrients.
 This poses a number of problems, as the behaviour
of micro-nutrients in the rhizosphere is different,
particularly with respect to interactions between
solid and solution compartments.
 There is no standard procedure for the
measurement of soil parameters that affect the
supply of micro-nutrient from the soil.
DPUM
 Dynamic Plant Uptake Model
 DGT (Diffusive Gradient in Thin-flims) tecnique is
used.
Crop Nutrient uptake models

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Crop Nutrient uptake models

  • 1. B.R.Iniyalakshimi Dept. of Soil Science and Agricultural Chemistry, TNAU
  • 2. MODELS It is “an assembly of concepts in the form of a mathematical equation that portrays understanding of a natural phenomenon.”
  • 3. Emprical models – statistical means and regression- black box models Mechanistic models- biophysical, biochemical and physiological mechanisms TYPES
  • 4. NUTRIENT UPTAKE MODELS • Soil nutrient transformation models emphasize on soil properties. • Crop uptake models emphaize on plant characters especially on root characters and also soil characters. • Models are formed for (i) identifying the process which describe nutrient uptake and (ii) evaluating quantitatively the effect of different parameters of nutrient uptake.
  • 5. • Extrapolation of a verified mechanistic model is more reliable than that of an empirical model(Claassen and Steingrobe, 1999). • The typical mechanistic nutrient uptake model describes the supply of nutrients from bulk soil to root surfaces, root growth and morphology, and root uptake kinetics (Barber, 1995).
  • 6. MECHANISTIC MODELS Steady state models • Flow of nutrients through a soil- steady state • Soil – volume element conducting nutrient flow • Neither a sink nor a source of nutrients • based on diffusion theory Transient models • either a sink or source influencing / modifying its flux (time) • describes the dynamic process of nutrient uptake & the concomitant changes in the ion concentration & distribution in the rhizosphere.
  • 7. SOIL NUTRIENT UPTAKE MODELING Mechanisms Mass flow Diffusion Root interception
  • 8. Interception is used to describe the uptake of soil nutrients at the root interface when soil volume is displaced by root volume (Barber 1995). Although conditions in the rhizosphere are sometimes different from those in the bulk soil (Marschner 1995), the contribution of interception to nutrient uptake is negligible for most nutrients (Barber 1995). Therefore, only mass flow and diffusion are considered to be responsible for movement of nutrients to the root surface in mechanistic modeling. However, Tinker and Nye (2000) consider the concept of interception to be somewhat arbitrary and argued that it can be included in the diffusion component.
  • 9. MASS FLOW  Mass flow is the convective transport of nutrients through the soil to the root surface by water flow as a result of transpiration (Barber, 1995).  The relative contribution of mass flow to nutrient uptake depends on the nutrient, plant species, plant age, and time of day (Marschner,1995).  For example calcium and magnesium supplied to plants by mass flow is significant, but its contribution to potassium supply is negligible (Marschner, 1995).  The influx by mass flow (FM) can be calculated by  where v is the mean water flux in soil driven by transpiration, and CL is the nutrient concentration in the soil solution.
  • 10. DIFFUSION  Diffusion is the movement of nutrients from areas of high concentration to those of low concentration (Barber 1995).  It is the main mechanism for at least phosphorus and potassium movement in the soil to plant roots (Marschner 1995).  A depletion zone is produced when the concentration of nutrient is lowered near the root surface due to root absorption (Jungk and Claassen 1997). Diffusive flux FD can be described by Fick’s first law,  where D is the diffusion coefficient of the nutrient in soil, C is the nutrient concentration in soil solution, and x is the distance.
  • 11. SIMULTANEOUS MASS FLOW AND DIFFUSION  Mass flow and diffusion occur simultaneously to supply nutrients to plant roots and cannot be treated as separate processes.  Nye and Spiers (1964) presented a partial differential equation to describe simultaneous mass flow and diffusion, and this equation became the foundation of the most mechanistic nutrient uptake models.
  • 12.
  • 13.  The Barber-Cushman model is largely based on the work by Nye and Marriot (1969).  Nye and Marriot (1969) revised the continuity equation proposed by Nye and Spiers (1964) to describe the flux of nutrient in the soil to the root surface with the nutrient concentration in soil solution (CL)  Nye and Marriot (1969) defined boundary conditions and solved this equation numerically.
  • 14. NYE AND MARRIOT (1969)
  • 15. NYE AND TINKER MODEL Nye and Tinker, 1977 The uptake of nutrient per unit length (U) is given by, U= 2πrαC1 r = radius of the root α = root absorbing power C1= ion concentration at the root surface
  • 16.  Summarizing the work by Claassen and Barber (1976) and Cushman (1979), Barber and Cushman (1981) suggested new boundary conditions to include inter-root competition for nutrients.  The new boundary conditions incorporated inter- root competition as well as Michaelis-Menten kinetics.  When solved numerically, the enhanced mechanistic model evolved into Barber-Cushman model.
  • 17.
  • 18.  Crop uptake is assumed to follow Michaelis-menten relationship between concentration and flux.  In 1983, Itoh and Barber developed a submodel to the Barber-Cushman model to include nutrient uptake by root hairs.  In 1986 Claassen et al. published NST 1.0 model.  In 1987 Oates and Barber published NUTRIENT UPTAKE model.  Both were based on the Barber-Cushman model.
  • 19. MICHAELIS- MENTEN KINETICS In=(Imax×Cla)/(Km+ Cla) Where, In = Rate of ion uptake Imax = maximum rate of ion uptake when concentration is not limiting Cla = concentration of nutrient ion in soil solution at the root surface Km = Michaelis – menten constant which represents a concentration of nutrient ion in soil solution when In=Imax/2.
  • 20. COMPUTERIZED MODELS  Based on Nye and Tinker model, Smethurst and Comerford (1993b) developed a computer model, COMP8 (Competition model version 8), which was able to calculate nutrient uptake between two competing and contrasting root systems.  SSAND was a revision and expansion of COMP8 by Comerford et al. (2006).  Its main improvements lie in the functions of predicting nutrient uptake as influenced by mycorrhizae and simulation of fertilization effects (Comerford et al. 2006).
  • 21.  Based on COMP8 and an earlier version of SSAND, another steady state model, PCATS was developed to simulate nutrient uptake by a single species by Smethurst et al. (2004).  For transient models –NST 1.0, NST 3.0.
  • 22. NYE AND TINKER, 2000  where b is the soil buffer power,  hence c = bc is the total amount of solute bound to the soil particles;  θ is the volumetric soil water content, thus is the overall amount of solute per unit volume of soil;  D is the solute diffusivity in water;  f is the soil impedance factor,  Dfθ is the effective diffusion coefficient for the solute in the soil; and v is the water flux in the soil.
  • 23. MODELLING CROP N UPTAKE  Benbi, Prihar and Cheema (1991) – used mass flow approach & predicted N uptake for wheat matched with measured N uptake (wet treatments).  In dry moisture regime other process of N uptake like diffusion & root interception should be used.
  • 24. BASED ON CROP DEMAND  Several models - driven by demand from the plant.  They calculate N demand for growth rates & concentration of N required.  Whitmore and Addiscott (1987) – computed demand using a simple variant of the logistic function to compute the pattern of N uptake (Y), with thermal time (x): Y=(A-1/X + e-kx )-n A - maximum of Y, n - shape factor, k - rate constant.
  • 25. • Tillotson and Wagenet (1982) and Hutson and Wagenet (1992) – modelled N uptake – based on Nye and Tinker model. • Warncke and Barber (1973) – value of α to be estabilished for different soils, crops and species under a range of concentrations. • De Willigen, 1991 – more complex models give better simulations than simpler ones.
  • 26. TRANSFORMATION INCLUDING UPTAKE  ANIMO  Benbi’s model  CANDY  DAISY  EPIC  SWATNIT
  • 27.
  • 28. M&M MODEL  Satisfactorily describes P uptake flux (Fp, mol cm-1 root h-1 ) as a function of P concentration in a well-stirred solution (Cpb mol l-1 ). Fp = Fp max * Cpa /(Km +Cpa )  Fp max and Km denote the maximum Fp and Cpa at which Fp = 0.5*Fmax . P uptake models Plant roots have a major influence on P dynamics in the soil.
  • 29. A= (b/a) w/2πDp a,b = midway distance between root and root radius Dp = diffusion co-efficient B = Fpmax /W W = solution velocity towards the root Bar and Yosef (1999)
  • 30. K concentration in plant K in soil solution & exchangea ble K flux to roots by mass flow & diffusion from soil Root parameters Plant dry biomass Fixed K Weather parameters Pottasium fertilizers Multi- Parametric model for K uptake
  • 31. S UPTAKE  Mc Caskill and Blair (1988) have developed a pseudo- mechanistic computer simulation model for predicting perennial pasture growth and S uptake.  But not verified.  Later Heng (1991) and Phimsarn(1991), developed simple models of pasture S uptake using relationship between actual daily ET(AET), average root density in the soil profile, soil solution S levels, sulphate buffering capacities.
  • 32. MICRONUTRIENTS  Mathematical models of micro-nutrient uptake by plants have been based on models designed for uptake of major nutrients.  This poses a number of problems, as the behaviour of micro-nutrients in the rhizosphere is different, particularly with respect to interactions between solid and solution compartments.  There is no standard procedure for the measurement of soil parameters that affect the supply of micro-nutrient from the soil.
  • 33. DPUM  Dynamic Plant Uptake Model  DGT (Diffusive Gradient in Thin-flims) tecnique is used.