<!DOCTYPE article PUBLIC "-//NLM//DTD JATS (Z39.96) Journal Archiving and Interchange DTD v1.0 20120330//EN" "JATS-archivearticle1.dtd">
<article xmlns:xlink="http://www.w3.org/1999/xlink">
  <front>
    <journal-meta>
      <journal-title-group>
        <journal-title>M. Machulyak);
yakymenko@gmail.com (Y. Yakymenko)</journal-title>
      </journal-title-group>
    </journal-meta>
    <article-meta>
      <title-group>
        <article-title>Modeling Vegetation Index Dynamics in GIS Based on Remote Observations*</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Roman Pasichnyk</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Ludmila Babala</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Mykhaylo Machulyak</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Yurii Yakymenko</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>West Ukrainian National University</institution>
          ,
          <addr-line>11 Lvivska Str., Ternopil, 46009</addr-line>
          ,
          <country country="UA">Ukraine</country>
        </aff>
      </contrib-group>
      <pub-date>
        <year>2025</year>
      </pub-date>
      <volume>000</volume>
      <fpage>0</fpage>
      <lpage>0003</lpage>
      <abstract>
        <p>The primary objective of this study is to develop and implement methods for modeling vegetation index dynamics based on remote sensing data, focusing on their application in agricultural monitoring systems. This paper explores the use of the Monod system o f differential equations for modeling the dynamics of vegetation indices, particularly NDVI, which allows for more accurate prediction of plant development under both normal and stress conditions. An analysis of the structural and parametric identification of the Monod model is conducted, addressing the complexity of nonlinear parameter estimation in differential equation systems. From the methodological perspective, a specialized approach for parameter identification is proposed, which accounts for the nonlinearity of the model and utilizes a combination of non-uniform and uniform grids for effective parameter space exploration. The application of the Levenberg-Marquardt gradient method for refining initial parameter estimates allows achieving high accuracy in modeling vegetation index dynamics. The findings of this study can be valuable for agricultural practitioners, researchers, and decision-makers interested in early stress detection and yield prediction in crop production systems.</p>
      </abstract>
      <kwd-group>
        <kwd>eol&gt;classification</kwd>
        <kwd>vegetation indices</kwd>
        <kwd>NDVI</kwd>
        <kwd>remote sensing</kwd>
        <kwd>Monod system of differential equations</kwd>
        <kwd>parametric identification</kwd>
        <kwd>Levenberg-Marquardt method</kwd>
        <kwd>plant growth modeling</kwd>
        <kwd>geographic information systems</kwd>
        <kwd>temperature stress</kwd>
        <kwd>yield prediction</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>1. Introduction</title>
      <p>Remote sensing is a useful technique for direct non-destructive monitoring of crop conditions [1,2].
Systematization of remote sensing results of vegetation indices in geographic information systems (GIS) is
a key step for effective analysis and use of this data. For efficient utilization of remote sensing results of
vegetation indices such as NDVI, NDRE, they need to be systematized in geographic information systems
(GIS). This process allows converting raw data into valuable information for monitoring vegetation
conditions, predicting yields, and making informed decisions in agriculture.</p>
      <p>The aim of this study is to develop and implement methods for modeling vegetation index dynamics
based on remote sensing data, particularly adapting the Monod system of differential equations for
predicting NDVI and MTCI indicators. The research focuses on developing a methodology for structural and
parametric identification of the Monod model, taking into account the nonlinearity of its parameters, and
experimental verification of this methodology's effectiveness on real data. Such creation of tools for early
detection of stresses in plant development and prediction of future yields will allow farmers to make more
informed decisions regarding agronomic measures.</p>
      <sec id="sec-1-1">
        <title>The first step is geospatial referencing of data. Vegetation indices are stored as raster layers, where each</title>
        <p>pixel has an index value, or as vector layers for analyzing individual areas. These layers are superimposed
on other geospatial data, such as cadastral maps or meteorological data, providing a comprehensive picture.
Spatial databases are used to store and manage large volumes of data, enabling spatial queries and analysis.
Attribute data associated with geospatial objects are stored in tabular databases used for statistical analysis
and report generation.
_______________________</p>
      </sec>
      <sec id="sec-1-2">
        <title>An important aspect is the creation of time series that reflect the dynamics of vegetation indices for each</title>
        <p>geospatial object. This allows tracking changes in vegetation condition over time and identifying anomalies.
Image classification and segmentation enable the identification of zones with different vegetation conditions
and individual objects, such as damaged areas. Integration with meteorological, agrochemical, and cadastral
data allows analysis of various factors' impact on vegetation condition. Using free software such as QGIS
automates and simplifies the process of systematizing and analyzing remote sensing data.</p>
        <p>Typically, vegetation indices that are widely used in crop models are calculated using spectral reflectance
coefficients. These vegetation indices, evaluated from
data collected by portable optical devices on
unmanned aerial vehicles, have been used for grain yield prediction [3, 4, 5]. An interesting study [6] aimed
to evaluate the most suitable vegetation index for determining crop response to elevated air temperature,
heat stress, and herbicide damage. Spectral reflectance coefficients, yield components, and growth
parameters such as plant height, leaf area index (LAI), and above-ground dry matter of rice cultivated in a
temperature gradient field chamber to simulate global warming conditions were observed from 2016 to 2018.</p>
      </sec>
      <sec id="sec-1-3">
        <title>The relationships between vegetation indices and yield parameters were evaluated considering stress</title>
        <p>conditions. NDVI, MTCI, and cumulative growing degree-days formed sigmoidal curves with high R-squared
values under normal growth conditions, but their amplitudes significantly decreased with herbicide damage.
Vegetation indices, particularly NDVI and MTCI, revealed slow growth and crop development caused by
stress using relationships with cumulative GDD. Maximum values of these indices are often used for crop
yield prediction.</p>
      </sec>
      <sec id="sec-1-4">
        <title>These observations highlight the importance of predicting the dynamics of NDVI and MTCI indices for</title>
        <p>early diagnosis of stresses in plant development as well as their maximum values for forecasting future
yields. However, modeling the accumulation of vegetation index values using logistic regression
dependencies is difficult due to the weak predictive properties of logistic curves. At the same time, modeling
logistic curves using Monod differential equation systems is a recognized tool for describing growth
processes that are limited by resources, making it more realistic than exponential growth. Adapting the
Monod model to experimental conditions and observed values requires its structural and parametric
identification.</p>
      </sec>
      <sec id="sec-1-5">
        <title>Therefore, implementing methods of structural and parametric identification of the Monod model for predicting the dynamics of vegetation indices NDVI and MTCI becomes an important tool for supporting decision-making regarding agronomic measures to ensure optimal development of agricultural plants, which is the focus of this research.</title>
      </sec>
    </sec>
    <sec id="sec-2">
      <title>2. Literature review</title>
      <p>The issue of identifying parameters of the Monod model has been addressed in recent years in open
publications [7-11]. In the work [7], dedicated to finding a thermodynamic interpretation of the Monod
equation, a key model relationship between the specific growth rate of microorganisms  and substrate
concentration S is examined. It limits the mentioned growth in a bulk solution according to the following
relationship:
 =</p>
      <p>
        +
(
        <xref ref-type="bibr" rid="ref1">1</xref>
        )
It is shown that
      </p>
      <p>is a constant, inverse to the equilibrium constant of the balanced microbial growth
reaction. When the equilibrium constant is very large, meaning 
is very small,  in this case it will
is very large, an extremely small amount of biomass is formed,
approach</p>
      <p>. On the other hand, when 
variations observed in 
and the equilibrium position lies far from the substrate volume. This study provides insight into the large
values typically reported in the literature.</p>
      <p>In the work [8], it is noted that
identifying parameter values of the Monod model based on experimental data is a complex problem, which
is proposed to be solved through experimental planning organization. In the work [9], explicit and implicit
schemes for solving the identified system of Monod differential equations are presented. To eliminate the
stiffness phenomenon</p>
      <p>when the concentration of microorganisms approaches zero, an asymptotic
representation is used to construct the solution for this section.</p>
      <sec id="sec-2-1">
        <title>In the work [10], a simplifie d</title>
      </sec>
      <sec id="sec-2-2">
        <title>Monod</title>
        <p>model is considered, presenting only the dynamics of
microorganisms. Through certain transformations, it is reduced to a linear regression model, which allows
for a simple parameter identification procedure. In the work [11], processes in a bioreactor are analyzed
using the complete Monod model. Matlab package tools are used to construct its solutions, however, the
issues of model parameter identification are not addressed.</p>
      </sec>
      <sec id="sec-2-3">
        <title>Thus, despite their importance, the issues of structural and parametric identification of the Monod model in application to representing vegetation index dynamics are insufficiently covered.</title>
        <p>3. Structural and Parametric Identification of Vegetation Index Dynamics</p>
      </sec>
    </sec>
    <sec id="sec-3">
      <title>Model in the Form of Monod Differential Equations System</title>
      <p>In the structure of the vegetation index dynamics model depending on the cumulative GDD index, we will
account for the irreversibility of vegetation index value accumulation, therefore the microorganism
concentration reduction coefficient in the model is set to zero. Let's denote the current level of the vegetation
index as X, the volume of the GDD indicator as t, and also introduce some resource value S of the
agrobiological system, which can provide only a certain limited yield during one season. In this case, the</p>
      <sec id="sec-3-1">
        <title>Monod system will take the form</title>
        <sec id="sec-3-1-1">
          <title>In this model, the parameter  1</title>
          <p>determines the impact of the interaction intensity between the current
index growth. The parameter  3 determines the intensity of yield resource depletion,  0
starting value of the modeled vegetation index, and  0 represents the volume of potential yield.
indicator level and the current system resource level  2, being the aforementioned characteristic of balanced
determines the</p>
          <p>
            The task of parametric identification of model (
            <xref ref-type="bibr" rid="ref2">2</xref>
            )-(
            <xref ref-type="bibr" rid="ref3">3</xref>
            ) is to select values of its parameters that best align
with experimental data. Considering that according to the nature of the analyzed processes, the modeled
variables do not demonstrate sharp random fluctuations, the quality of approximation of observed values
can be evaluated using the mean square criterion:


  ( ) =  1
  ( ) = − 3
 ( ) ( )
 2+ ( ) ,
 ( ) ( )
 2+ ( ) ,
 (0) =  0,  (0) =  0
 ( ⃗) = ∑ =1    , ⃗ −    2
          </p>
          <p />
        </sec>
      </sec>
      <sec id="sec-3-2">
        <title>When the model parameters were known, according to relationships (2)-(3), to construct the values of</title>
        <p>model variables, it would be necessary to solve a system of nonlinear differential equations.</p>
        <sec id="sec-3-2-1">
          <title>In the general case, the system parameter values are unknown. The parameter  2</title>
          <p>enters the differential
equations of the system nonlinearly and can vary over a wide range. These changes lead to cardinal changes
in the nature of the system solution. Therefore, on a sufficiently coarse grid of parameter values  2, the
sequence of values of the model identification quality functional demonstrates the property of unimodality.</p>
        </sec>
        <sec id="sec-3-2-2">
          <title>As parameter  2</title>
          <p>values increase, their influence on the result decreases. This means that for an effective
search for optimal values of this parameter, it is necessary to use a grid with different steps. In particular,
the step of changing values on the grid should increase with the increase of the parameter itself. For this
purpose, a geometric progression can be applied</p>
        </sec>
      </sec>
      <sec id="sec-3-3">
        <title>Parameter B is selected experimentally to ensure sufficient shift in the process activity maximum when</title>
        <p>
          parameter  2 values move along grid nodes (
          <xref ref-type="bibr" rid="ref5">5</xref>
          ). Other model parameters are determined based on the
selected limiting parameter and approximate difference representation of differential equations for
individual time points. The minimum of this function with a single extremum outlines the search zone for
parameters of the model being identified.
        </p>
      </sec>
      <sec id="sec-3-4">
        <title>In the defined area, minimization of the quality criterion depends not only on changes in one parameter</title>
        <p>2, but also on the interaction of all parameters. Therefore, the search zone for parameter  2 values is
covered with a uniform grid. For each parameter value, corresponding values of other parameters are
calculated using difference relations. These values are then refined by a modified gradient method. Among
the refined parameter sets, the one that minimizes the maximum relative error between modeled and actually
observed data is chosen.</p>
        <p>
          Let's now proceed to the analysis of the system equations (
          <xref ref-type="bibr" rid="ref2">2</xref>
          )-(
          <xref ref-type="bibr" rid="ref3">3</xref>
          ). They contain only one unknown
parameter. Therefore, by constructing an approximate representation of the equation at one point, we can
estimate the value of this parameter. For construction, we will select the point of reaching the mean value
of the vegetative indicator variable, where its change tendency is close to linear. First, let's estimate the
derivatives of the indicator and yield reserve at the selected point using the following relationships:
  , = (   +1 −    −1)⁄(  +1 −   −1),
        </p>
        <p>20, 

2
   0 .</p>
        <p>
          (
          <xref ref-type="bibr" rid="ref2">2</xref>
          )
(
          <xref ref-type="bibr" rid="ref3">3</xref>
          )
(
          <xref ref-type="bibr" rid="ref4">4</xref>
          )
(
          <xref ref-type="bibr" rid="ref5">5</xref>
          )
(
          <xref ref-type="bibr" rid="ref6">6</xref>
          )
        </p>
      </sec>
      <sec id="sec-3-5">
        <title>The obtained values allow constructing an approximate representation of the differential equations at the moment of reaching the mean value of the vegetative indicator variable:</title>
        <p>, ≈  1   
   ⁄  2 +    ,
  , ≈ − 3   
   ⁄  2 +    .</p>
      </sec>
      <sec id="sec-3-6">
        <title>Based on the constructed relationships, we build an estimation of model parameters:</title>
        <sec id="sec-3-6-1">
          <title>The selected parameter  2</title>
          <p>a uniform grid of the form</p>
          <p>value determines the base point and step for constructing a set of points for
Which means that under the following condition,
  

   , .</p>
          <p>2,    =</p>
          <p>argmin
 2∈ 2( 
, max)</p>
          <p>{ ( 2)}
 2, 
  ,  
4,  
≡ { − 
    0} =31</p>
        </sec>
        <sec id="sec-3-6-2">
          <title>The basis of the Monod model identification method lies in iterating through values of parameter  2</title>
          <p>
            a certain uniform grid, for each value of which corresponding initial values of other model parameters are
on
constructed using established difference relationships. Subsequently, all initial model parameter values are
refined by the gradient method according to the minimum criterion of functional, presented by relationship
(
            <xref ref-type="bibr" rid="ref4">4</xref>
            ).
          </p>
          <p>
            Let's examine in more detail the process of constructing the mentioned uniform grid. Based on the
proposed progression (
            <xref ref-type="bibr" rid="ref5">5</xref>
            ), we build a non-uniform grid for selecting the base point for constructing the next
uniform grid of refined search. The non
          </p>
          <p>-uniform grid, built on the basis of geometric progression, is
described by the representation:
 2( 
,  
) =

2
   0
important processes.</p>
          <p>The construction of the non-uniform grid begins from the point associated with half of the initial yield
reserve, since such a parameter  2 value is a satisfactory initial value for a large number of practically
 2  0
,  0
=  40, 0 ,
 0
=  0
=  0 = −1,
established experimentally.</p>
          <p>Further, we supplement the non-uniform grid by decreasing and increasing the parameter  2
provided that the relative decrease of the minimum value on the expanded grid relative to the minimum
value,
value of the previous grid configuration obtains a relative decrease greater than the value   , which is
the lower limit of the orders of elements of the geometric progression that form the grid decreases by
one, and when the condition is met
 2∈ 2( 
min , 0)  ( 2)−
 2∈ 2( 
min −1, 0)</p>
          <p>( 2)
min
 2∈ 2( 
, 0)
 ( 2)
&gt;   ⇒  
≔  
− 1,
 2∈ 2( 
min , max)
 ( 2)−
 2∈ 2(</p>
          <p>+1)  ( 2)
min
 2∈ 2( 
, max)
min</p>
          <p>, 
 ( 2)
&gt;   ⇒  
≔  
+ 1, (15)
the upper limit of the orders of elements of the geometric progression increases by one. After completing
the process of filling the non-uniform grid, the minimum value of the quality functional on it indicates the
base value of the nonlinear parameter of the Monod model  2,  
first value of which is less than the value of the base point (for the base point = [ /2]),), and the last value
approaches the node of the non-uniform grid, which comes after the base one (for the point following the
base one  = [ /2])B ).</p>
        </sec>
        <sec id="sec-3-6-3">
          <title>Each value from the grid is assigned to parameter  2, with which approximate estimates of other model</title>
          <p>
            parameters are constructed based on established difference relationships (
            <xref ref-type="bibr" rid="ref10">10</xref>
            )-(
            <xref ref-type="bibr" rid="ref11">11</xref>
            ). Subsequently, they are
refined using the modified Levenberg-Marquardt gradient method based on criterion (
            <xref ref-type="bibr" rid="ref4">4</xref>
            ). Among these initial
model parameter values, the one that provides the minimum of the smallest of the maximum relative errors
at the model identification points is selected.
          </p>
        </sec>
      </sec>
    </sec>
    <sec id="sec-4">
      <title>Numerical experiments</title>
      <p>The effectiveness of the proposed approach in modeling the dynamics of the NDVI vegetation index is clearly
demonstrated by the graphs in Figure 1.</p>
      <sec id="sec-4-1">
        <title>Data for modeling were taken from work [6], which presented observations of vegetation index dynamics</title>
        <p>when growing rice under normal conditions and under conditions with excess average daily temperatures
throughout the season. As a result of applying the described Monod model identification methodology,
acceptable levels of maximum relative modeling errors were achieved, which were 6.15% for the case of
normal growth and 4.70% for the case of temperature shock.</p>
      </sec>
    </sec>
    <sec id="sec-5">
      <title>Conclusions</title>
      <p>The paper analyzes the role and characteristics of monitoring vegetation index dynamics based on remote
observations. It proposes modeling such dynamics using the Monod system of differential equations. The
structure of this system has been established to correspond to the nature of the observed data. A method for
identifying the constructed system based on the minimum mean square error criterion is proposed, with the
main element being an algorithm for forming initial model parameter values taking into account its
nonlinearity. Subsequently, the initial model values were refined using the Levenberg-Marquardt gradient
method. The effectiveness of the proposed methodology has been confirmed experimentally. A maximum
relative error level of approximately 5-6% was recorded.</p>
      <p>The effectiveness of the proposed methodology has been confirmed experimentally, with a maximum
relative error level of approximately 5-6% recorded. Despite the limitations of the study to data for rice
cultivation under normal and temperature stress conditions, the developed methods demonstrate significant
potential for further expansion to other vegetation indices and integration into geographic information
systems. Promising directions for further research include studying the influence of different types of
stresses on model parameters, developing methods for early diagnosis of plant stresses, and creating
software to automate the process of modeling vegetation index dynamics and making agronomic decisions.</p>
    </sec>
    <sec id="sec-6">
      <title>Declaration on Generative AI</title>
      <sec id="sec-6-1">
        <title>The authors have not employed any Generative AI tools.</title>
        <p>[15] J. J. See, S. S. Jamaian, R. M. Salleh, M. E. Nor, F. Aman. Parameter estimation of Monod model by the</p>
      </sec>
      <sec id="sec-6-2">
        <title>Least-Squaresmethod for microalgae Botryococcus Braunii sp. Journal of Physics: Conf. Series 995</title>
        <p>(2018) 012026.
[16] Hanna Molin. Optimal steady-state design of bioreactors in series with Monod growth kinetics. Master
thesis. Uppsala University. 2017</p>
      </sec>
    </sec>
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