Yield and Protein Response of Wheat Cultivars to Polymer-Coated Urea and Urea
Wheat growth simulation and yield prediction with seasonal forecasts and a numerical model
Transcript of Wheat growth simulation and yield prediction with seasonal forecasts and a numerical model
Wheat growth simulation and yield prediction with seasonal
forecasts and a numerical model
Vittorio Marletto a, Francesca Ventura b,*, Giovanna Fontana c, Fausto Tomei a
a ARPA Emilia-Romagna, Servizio IdroMeteorologico, v.le Silvani 6, 40122 Bologna, Italyb Universita di Bologna, Dipartimento Scienze e Tecnologie Agroambientali, v. Fanin 44, 40137 Bologna, Italy
c Universita di Palermo, Dipartimento Colture Arboree, Viale delle Scienze, Edificio 4, 90128 Palermo, Italy
Received 22 January 2007; received in revised form 29 June 2007; accepted 2 July 2007
www.elsevier.com/locate/agrformet
Agricultural and Forest Meteorology 147 (2007) 71–79
Abstract
Wheat is a major winter crop in northern Italy. Italian agricultural markets and government agencies would undoubtedly benefit
from the early availability of wheat yield forecasts at the regional and national scales as useful support in decision making. In this
study we tested the skill of seasonal weather forecasts, in combination with observed weather data, as input to a crop model working
in water limited conditions. The observations were used to simulate wheat growth from sowing up to 2 months before harvest, while
seasonal forecasts were used afterwards to predict final yields. Observations included climatic variables and water table levels from
a location in the Po river plain (Bologna, Italy), while seasonal forecasts came from the Demeter EU project and consisted of a
dataset of downscaled multi-model ensemble hindcasts.
The Criteria/Wofost simulation model used for this work includes a new numerical scheme for the soil water balance (Criteria)
and incorporates a modified version of the Wofost crop growth model. Median wheat yield forecasts were compared with field data
collected at the experimental farm of Bologna University during 1977–1987. Forecast yields showed satisfactory agreement with
observed ones (MBE 816 kg ha�1, RMSE 1185 kg ha�1, R2 0.65**). In our view, with this result there is a good prospect for
extending the proposed methodology to the regional and national scale for the production of operational seasonal forecasts of
agricultural yields.
# 2007 Elsevier B.V. All rights reserved.
Keywords: Crop model; Soil water flow model; Ensemble prediction; Downscaling; Northern Italy
1. Introduction
Forecasting crop yields one or more months before
harvest is a very important task for agrometeorologists
involved in operational work. Farmers, markets and
public authorities are highly interested in this type of
information, justifying the efforts made in obtaining it.
Examples of operational crop yield forecasting at the
* Corresponding author. Tel.: +39 051 2096658;
fax: +39 051 2096241.
E-mail address: [email protected] (F. Ventura).
0168-1923/$ – see front matter # 2007 Elsevier B.V. All rights reserved.
doi:10.1016/j.agrformet.2007.07.003
continental and national level can be found in Europe
(Genovese, 1998; http://agrifish.jrc.it/marsstat/default.
htm) and the USA (Vogel and Bange, 1999; http://
www.usda.gov/nass/nassinfo/pub1554.htm). In the lat-
ter case they use statistical models fed with climatic
means for unobserved data. In the former case they use a
combination of the Wofost process-based dynamic crop
growth model (van Diepen et al., 1989) with statistical
regression techniques, linking early partial simulation
results to the final ones in previous years.
The feasibility of early yield assessment with a
dynamic crop growth model fed with observed weather
data up to a point, and with daily data obtained running
V. Marletto et al. / Agricultural and Forest Meteorology 147 (2007) 71–7972
Fig. 1. A three-tier validation system, where boxes represent sources
of data and ovals indicate the different validation types (from Morse
et al., 2005). A comparison of seasonal hindcasts with the correspond-
ing observed/reanalysed variables is carried out in a Tier-1 validation.
Simulated yields obtained from the crop growth model using hindcasts
as input can be compared with the output obtained using observed
weather data (Tier-2 validation) or with field data (Tier-3 validation,
the object of this paper).
a weather generator afterwards, has been recently
demonstrated (Marletto et al., 2005; Lawless and
Semenov, 2005). This paper concentrates instead on
testing an application of seasonal weather forecasts
versus independent field data for the same purpose.
Due to the intrinsically chaotic behaviour of the
atmosphere, at the moment the only feasible approach
to seasonal prediction appears to be the ensemble
stochastic technique, that requires weather models to be
run in a number of replicates starting from slightly
different initial conditions. Moreover, using at the same
time several ocean-atmosphere coupled models, differ-
ing both in the physics and the numerics, has been
shown to effectively improve ensemble seasonal
prediction performance (Hagedorn et al., 2005). In this
respect a large framework to produce multi-model
ensemble seasonal forecasts for past years (henceforth
called hindcasts) was set up during the Demeter EU
project (Palmer et al., 2004). Applications of these data
in a number of case studies, notably in the health sector
(Thomson et al., 2006) and in agriculture (Cantelaube
and Terres, 2005; Challinor et al., 2005b), are available
in the literature. For a complete coverage of the
Demeter project concept and results see the freely
available special issue of the Tellus A journal
(www.blackwell-synergy.com/toc/tea/57/3).
Marletto et al. (2005) showed that global hindcasts
need to be downscaled, i.e. regionalized, for skilful
application to early wheat yield assessment in the very
complex orographic context of northern Italy, where the
Alps and Apennine mountain ranges almost completely
surround the very productive agricultural lowland of the
Po river plain. This plain is where most of the Italian
cereal production is obtained, but where the weather is
difficult to forecast even at the usual short and mid-term
time scales (Tibaldi and Molteni, 1990).
This paper addresses the so-called Tier 3 of the
seasonal forecast validation and quality assessment
strategy, traced by Morse et al. (2005) and shown in
Fig. 1. Tier 1 consists of the comparison of direct model
output with meteorological observations and analyses.
It is usually carried out by weather centres and, at least
for the case of Europe, does not show very satisfactory
skill in seasonal forecasting output, even after down-
scaling (Pavan et al., 2005). Tier 2 is based on a user
application model which is first fed with seasonal
forecasts, then with observed weather data, and consists
of the comparison of the respective outputs. As far as
Tier 2 is concerned, the feasibility and practical interest
of seasonal forecast applications for early agricultural
production prediction was shown by Marletto et al.
(2005) using a calibrated wheat growth and soil water
balance model, fed with observations up to a date (3, 2,
1 months before harvest), and with downscaled seasonal
forecasts afterwards. Tier 3, the object of this paper,
concentrates instead on the more exacting task of
comparing independently obtained field data with user
application model output, fed with seasonal forecasts.
In particular, we intend to show that downscaled multi-
model ensemble seasonal forecasts of daily surface air
temperature and precipitation can be successfully used
in the last 2 months of the growing season, to simulate
local crop growth and to assess final yield of winter
wheat with a numerical model, in good agreement with
field crop data.
The purpose of this work is first to verify the model
reliability, comparing winter wheat yield simulated by
means of a formerly and independently calibrated
model (Marletto et al., 2005) and observed weather data
with actual yields measured in the field (Toderi et al.,
1982). After having obtained satisfactory results, the
last 2 months of observed temperature and precipitation
data are removed from the data sets and substituted with
downscaled hindcasts of the same variables from the
Demeter project, in order to check the skill of seasonal
forecasts in early wheat yield assessment even at the
local scale.
2. Materials and methods
2.1. Meteorological data
The meteorological data used in this work were
collected at the agrometeorological station of the
Agricultural Faculty of the University of Bologna, in
the experimental farm of Cadriano (448 330 0300 N, 118
V. Marletto et al. / Agricultural and Forest Meteorology 147 (2007) 71–79 73
Fig. 2. Map of Italy with detail of Emilia-Romagna region, Bologna in the centre. The Cadriano experimental farm is in the northern outskirts of the
city.
Fig. 3. Water table depth (m) measured weekly at Cadriano in the
years 1976–1987.
240 3600 E, 33 m asl, Fig. 2). The instruments were set
in a grass-covered area of 30 m � 40 m, including
hygrothermograph, rainfall recorder, phreatimeters to
the depth of 2.5 m, as well as anemometers, radio-
meters, and class A pan evaporimeter. The mechanical
instruments are still in use, together with new electronic
sensors, and are periodically checked and calibrated
(Ventura et al., 2002). For this work we made use of the
daily maximum and minimum air temperature and
rainfall data, together with the weekly groundwater
levels, recorded from 1977 to 1987. Data were quality-
controlled, with uncertain data compared to data from
other instruments in the same station or from other
stations nearby. Temperature data analysis revealed that
year 1985 shows unusually low minimum air tempera-
ture in January (less than �20 8C) and very cold
temperatures up to April, so that it was decided not to
consider that year in this data elaboration.
Daily maximum temperature data show the highest
monthly mean during the wheat growing season of June
1982 (28.7 8C) while the highest total annual precipita-
tion was recorded in 1984 (943 mm).
Water table depth data show an oscillating behaviour
(Fig. 3) during the year (Rossi Pisa and Kerschbaumer,
1998) ranging from �0.8 m (winter) to �2.5 m
(summer). This trend is typical of the Po river plain,
limiting root expansion during winter and has a high
effect on soil structure and moisture. In the main
simulation experiment, carried out to test the skill of the
Demeter hindcasts, water table depth during May and
June was kept at the average value of 1.2 m, typical of
springtime in our experimental area.
2.2. Crop data
An extensive set of data was collected from 1972 to
1999 in a long term experiment on winter wheat (cv
Argelato) carried out at the above mentioned Cadriano
experimental farm, to study the effects of nitrogen
fertilization and straw burying on productivity and soil
properties in the sugarbeet (Beta vulgaris L.) – winter
wheat (Triticum aestivum L.) – barley (Hordeum
vulgare L.) crop rotation, as extensively detailed by
Toderi et al. (1982). The crops, all grown every year on
6 m � 9 m plots, were fertilized with ammonium nitrate
at various nitrogen rates, according to their different
nutritional demand. The straw was buried after harvest
only in the barley plots. A split plot design with three
replicates was used. The soil is an Acquic Haplustalf
(Soil Taxonomy), with clay 28%, sand 52%, silt 20%;
pH (water) 6.6; N (Kjeldhal) 0.9%, OM (Walkey-Black)
V. Marletto et al. / Agricultural and Forest Meteorology 147 (2007) 71–7974
1.4%, CEC (meq/100 g) 22.2. Yields and yield compo-
nents were measured at harvest.
For this work we considered only wheat data from
the 200 kg N ha�1 with straw burial treatment, a
fertilization amount surely not limiting production,
for years 1977–1987, when the seasonal forecast data
were available (see below). In this period the mean yield
was 6355 kg ha�1, with a standard deviation of
1128 kg ha�1. The lowest yields were recorded in the
years 1977 and 1978, due to extensive lodging.
2.3. Seasonal weather forecasts
In the framework of the Demeter EU project the
European Centre for Medium-range Weather Forecasts
(ECMWF) produced hindcasts spanning the 1958–2001
period and deriving from a multi-model ensemble of
seven coupled ocean-atmosphere global models (Pal-
mer et al., 2004). Each model was run four times a year
with a set of 9 perturbed initial conditions, producing 63
member ensembles for every seasonal hindcast.
For this work we used numerical Demeter output for
years 1977–1987, a period for which monthly hindcasts
of air temperature and precipitation downscaled to
northern Italy were made available to us by other project
partners for four models and nine initial conditions (36
replicates). Details on the statistical technique and
climatic data used for downscaling are given by
Feddersen and Andersen (2005). A weather generator
was used by Marletto et al. (2005) to convert monthly
downscaled temperatures and precipitation data into
daily values. The number of replicates doubled to 72
because of the generation of two daily series from the
weather generator for each ensemble member. Down-
scaled Demeter output refers to the 1st February runs,
spanning 6 months, up to 31st July, including the May
and June temperature and precipitation data used here,
instead of observed weather data, to produce hindcasted
wheat yields 2 months before harvest. This time lag was
decided upon after consideration of previous work
(Marletto et al., 2005): wheat yields simulated with
seasonal hindcasts 3 months before harvest show
high dispersion and very low forecasting skill (worse
than climatology), while 1 month before harvest the
dominance of observed weather data is so high that
seasonal hindcasts add practically no value to yield
forecasts.
2.4. The model
The Criteria/Wofost integrated soil water balance
and crop growth model was developed during the
Demeter project (Marletto et al., 2001) including crop
growth routines from the Wofost model (van Diepen
et al., 1989) and already existing Criteria water balance
routines (Marletto and Zinoni, 1996). The Wofost
model version used here was calibrated in the northern
Italy environment. Data used and calibration results are
described in a former paper (Marletto et al., 2005). Due
to the critical role played by the shallow water table in
both the water balance and the crop growth, a physically
based numerical routine for water flow simulation was
integrated in the model for this work, based on a
recently developed 3D surface and soil water flow
model. The soil water flow sub-model described here is
a mono-dimensional version of the hydrological model
CRITERIA3D (Pistocchi and Tomei, 2003). The model
aims to describe all the phenomena connected with the
hydrological balance of soil, like superficial flows,
infiltration, redistribution, drainage and capillary rise in
a three-dimensional domain. CRITERIA3D is based on
the solution of a partial derivatives equation system,
expressing the mass and momentum balance, but
belongs to the category of ‘‘mediating models’’ because
it describes the laws of motion with the empirical
equations of Darcy for subterranean flows and of
Manning for superficial flows. The model is furthermore
based on the empirical equations of van Genuchten
(1980) and Mualem (1976) to express the u(H) and K(H)
relations between the potential H, water content u and
hydraulic conductivity K. The one-dimensional restric-
tion of the original model described here computes only
the vertical phenomena connected with infiltration. The
routine solves the Richards equation using an integrated
finite difference scheme. Details of the equations and
numerical methods used in the flow routine can be
found in the Appendix.
3. Results
3.1. Model verification
A comparison of simulated wheat phenology (head-
ing date) versus observed data from 1977 to 1987 is
presented in Fig. 4. Heading date of year 1983 was not
recorded and year 1985 was not considered, due to
extremely unusual cold temperatures and phenological
sub model failure in accounting for them. Observed
heading date ranges between day of year (DOY) 117
and 137, while simulated heading ranges between DOY
114 and 135, with a mean bias error (MBE) of �1.6
days and a root mean square error (RMSE) of 3.5 days.
A good simulation of heading date is essential in crop
growth modelling and we deemed these errors small
V. Marletto et al. / Agricultural and Forest Meteorology 147 (2007) 71–79 75
Fig. 4. Comparison of wheat heading dates observed at Cadriano in
the years 1977–1987 (1983 was not recorded and 1985 is missing due
to very bad weather) and dates simulated with the Criteria/Wofost
model (development stage 1).
enough to ensure proper computation of dry matter
accumulation in storage organs, a process dominating
crop growth after heading.
Verification went on with the comparison of field
data versus yield simulated with the Criteria/Wofost
model in the version described by Marletto et al. (2005).
Model results (Fig. 5, diamonds) show a pronounced
overestimation (MBE �2440 kg ha�1), practically as
large as the RMSE (2570 kg ha�1).
It is well known (Marletto, 1983; Ashraf et al., 2005)
that a shallow water table limits root growth and carbon
Fig. 5. Comparison of observed wheat yields at Cadriano in the years
1977–1987 (1985 is missing due to very bad weather and poor crop)
vs. yields simulated by Criteria/Wofost with the conceptual water
balance routine (squares) and with the physically based routine
(triangles).
uptake for long periods of active growth and can result
in abnormally low yields. We then attributed the large
yield overestimates to the lack of a routine computing
the effects of a shallow water table on soil moisture. In
order to correct this inability of the model, the
numerical and physically based soil water routine
described above, and detailed in the Appendix, was
added to the model suite and additional tests were
performed with the new version of the water balance
routine. The wheat yields obtained this way can be seen
in Fig. 5 (triangles). The error was significantly reduced
(MBE �330 kg ha�1, RMSE 710 kg ha�1, R2 0.70**)
compared with the previous water balance. The new
version of the model was therefore used for the
evaluation of Demeter data for early assessment of final
yield.
3.2. Seasonal forecast verification
Fig. 6 shows percentiles (n 5, 10, 25, 50, 75, 90 and
95) from the distribution of the 72 replicates of wheat
yields obtained from the Demeter hindcasts for years
1977–1987 (with the exception of 1985), compared
with yields simulated using observed weather data only
(squares) and with actual yields from field experiments
(triangles).
Distributions of results obtained from downscaled
seasonal Demeter hindcasts are generally skewed, so
the comparison between simulations and field data was
carried out using central values (50th percentile, i.e.
median yields), instead of arithmetic means. The
comparison showed errors (MBE 816 kg ha�1, RMSE
1185 kg ha�1, R2 0.65**) higher than those obtained
simulating with observed weather data but close to the
standard deviation of experimental yields (1128 kg
ha�1). For comparison, results from the other percen-
tiles shown in Fig. 6 are visible in Table 1.
Table 1
Error statistics of percentile winter wheat yields simulated with
weather data up to the end of April and with downscaled multi-model
ensemble seasonal forecasts up to harvest date compared with experi-
mental yields
Percentile R2 RMSE (kg ha�1) MBE (kg ha�1)
5 0.32ns 2802 2615
10 0.37ns 2417 2195
25 0.59* 1601 1361
50 0.65** 1185 816
75 0.65** 1025 352
90 0.66** 1029 �65
95 0.67** 1107 �294
Note. Significance levels: ns (P > 0.05), *(P < 0.05), **(P < 0.01).
V. Marletto et al. / Agricultural and Forest Meteorology 147 (2007) 71–7976
Fig. 6. Final yields as measured at Cadriano (triangles, 1985 is missing due to very bad weather and poor crop), simulated with the Criteria/Wofost
model fed with observed weather data (squares), and simulated with observed data up to the end of April and with downscaled multi-model ensemble
seasonal forecasts up to harvest date (circles, box and whiskers showing percentiles computed on the 72 members distribution).
4. Discussion
One of the purposes of this work was to verify the
reliability of a water limited wheat growth simulation
model (Marletto et al., 2005). Comparing measured and
simulated winter wheat yields we understood that a
numerical water flow routine was needed to take into
proper account the effects of a shallow water table on
wheat growth. The new version of the model so obtained
performed much better than the older one, reducing MBE
from 2440 to 330 kg ha�1 and RMSE from 2570 to
710 kg ha�1. We then felt confident enough to tackle the
second and most important task of this work, i.e.
verifying the practical applicability of seasonal weather
predictions to early wheat yield assessment. According to
Morse et al. (2005) this work can be considered as Tier 3
validation of seasonal forecasts by means of user models
and field data, and follows a former successful Tier 2
verification work (Marletto et al., 2005).
Seasonal forecasts of daily surface air temperature
and precipitation, properly downscaled, used instead of
measurements and compared with field data 2 months
before harvest, showed a reasonable predictive power of
final winter wheat yield. Not only the errors of median
predictions look acceptable but the determination
coefficient (0.65) is close to the one obtained simulating
with observed weather data (0.70). De-biasing the
assessed median yield, i.e. removing the absolute value
of the systematic error from the RMSD, led to a residual
error (368 kg ha�1) slightly smaller than the one
obtained simulating with observed weather data
(380 kg ha�1).
In our opinion the results here obtained look
particularly interesting because no papers comparing
crop yields from weather seasonal forecasts with field
data are available in the literature, while more
commonly comparisons are against agricultural statis-
tical data at the district or regional level (e.g. Challinor
et al., 2005a,b).
5. Conclusions
In this paper a combination of observed data and
downscaled multi-model ensemble seasonal forecasts,
from the Demeter EU project dataset, was used to
simulate wheat growth in water limited conditions in the
Po river plain (Bologna, Italy) and to predict final yield
2 months before harvest.
The Criteria/Wofost model used for this work
includes a new numerical scheme for the soil water
balance (Criteria) and incorporates a modified version
of the Wofost crop growth model.
Median yield forecasts, compared with field data
collected at the experimental farm of Bologna University
in the years 1977–1987 showed good agreement with
observed yields.
V. Marletto et al. / Agricultural and Forest Meteorology 147 (2007) 71–79 77
In our view this result shows that wheat yields can be
reasonably well assessed 2 months before harvest using
downscaled multi-model ensemble seasonal forecasts.
There is thus a good prospect for the application of
operational seasonal forecasts to early agricultural
production prediction, even at the local scale, especially
in view of expected improvements in seasonal fore-
casting and downscaling techniques and of the possible
extension of the Criteria/Wofost model to other regions.
Acknowledgements
We are deeply indebted to Prof. Giovanni Toderi and
his research staff, who provided wheat field data. We are
also grateful to Tomaso Tonelli, who was very helpful in
software development, Gabriele Antolini, who helped
with the figures, and with Enrico Ceotto, who reviewed
an early draft of this paper. This work was carried out
within the Ph.D. thesis of Giovanna Fontana in
Agrometeorology and Ecophysiology of Agricultural
and Forest Systems, University of Sassari, coordinated
by Prof. Pietro Deidda. Financial support for this work
came from the research projects DEMETER (EU Fifth
Framework Programme, contract EVK/CT/1999/
00024) and ENSEMBLES (EU Sixth Framework
Programme, contract 505539).
Appendix A
The mono-dimensional soil water flow model used
here solves the pointwise continuity equation:
divðuÞ þ @ðWuÞ@t¼ q (1)
where u is the flux density, W the total available volume
at a point, u the fraction of W occupied by water
(volumetric water content) and q is the water input or
output. This general equation is solved adopting two
different laws to describe fluxes within the soil matrix
and fluxes on the soil surface. In the first case, it
becomes Richards’ equation:
du
dH
@H
@t¼ div½KðhÞ gradðHÞ� þ q (2)
where K(h) is the hydraulic conductivity and H the total
hydraulic head. H in turn is given by the sum of
elevation z (or gravitational component) and the hydrau-
lic matric component h = p/rw, where rw is the water
density, p the soil matric potential and t is the time. For
saturated flow, Eq. (2) reduces to the Laplace equation
for groundwater flow.
The solution of the governing equations is based on
the integrated finite difference method which consists of
the integration of the differential continuity equation
over a finite domain D, as described by de Marsily
(1986), leading to the integral equation (limited to the
one-dimensional case):Z
divðuÞ dzþZ
@ðWuÞ@t
dz ¼Z
q dz (3)
The mass balance is computed for the spatial unit D
of the model domain. Based on integral properties,
Eq. (3) can be written asZ
G D
un dSþZ
@ðWuÞ@t
dz ¼Z
q dz (4)
where GD is the surface of the computational domain D,
and n its normal unit vector. Eq. (3) can be applied over
a simulation volume within which the material proper-
ties are constant.
If the simulation domain is approximated by a three-
dimensional (or one-dimensional) grid of nodes, Eq. (4)
is equivalent to the mass balance equation for the
volume surrounding each node:
@Vi
@t¼Xn
j¼1
Qi j þ qi 8 i 6¼ j (5)
where Vi is the amount of stored water in the volume
surrounding the node, Qij the flux between the i-th and
the j-th node, and qi is the input flux at the i-th node. We
can write a system of equations for all nodes with the
unknowns being the hydraulic potentials, H.
The flux Qij is described by Darcy’s law in the finite
difference form:
Qi j ¼ �Ki jSi jðHi � H jÞ
Li j(6)
where Sij is the interfacial area between nodes i and j, Lij
the distance between the two nodes, Hi the hydraulic
potential at node i, and Kij is the internode conductivity.
The model uses the geometric mean of nodal conduc-
tivities
Ki j ¼ffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiffiKiðHÞK jðHÞ
q; (7)
where Ki(Hi) is the hydraulic conductivity at the i-th
node. The model uses the approach proposed by van
Genuchten (1980) and Mualem (1976) for the charac-
terization of the soil water retention (SWR) and the
hydraulic conductivity (K) curves.
The model allows time and space varying boundary
conditions to each node to be specified:
V. Marletto et al. / Agricultural and Forest Meteorology 147 (2007) 71–7978
(1) n
odes with fixed hydraulic head (H = constant),(2) n
odes set at atmospheric boundary conditions,(3) n
odes with prescribed flux,(4) n
odes with no flux in any given direction.Boundary conditions of type (1) can be used to
represent various conditions, such as deep drainage at
the lower boundary, or prescribed heads given by the
presence of ponding areas, lakes or other bodies.
Atmospheric boundary conditions (2) allow prescribed
precipitation and evapotranspiration to be assigned.
Precipitation is assigned per unit area of the land surface
equivalent to the boundary area of a subsurface volume.
Regarding the coupling between surface and subsurface
flow, precipitation water is applied to the surface nodes.
The coupling between surface and subsurface nodes
occurs through the application of Richards’ equation
with different options on the calculation of the inter-
nodes conductivity.
The numerical formulation of the model produces a
strongly non-linear system, to be solved by means of
successive approximations. Every time step corre-
sponds to the computation of more approximations,
each solving a linearized system by means of a solving
method. It can be shown that the matrix produced by the
model is positive definite so the main iterative solving
methods are convergent. In particular we chose the
Gauss–Seidel algorithm, whose computational cost
seems optimal for the matrix produced by the model
(Tomei, 2005).
We faced the necessity of developing an adaptive
algorithm able to adapt time step to system condi-
tions. The main reference to monitoring the state of
the system is represented by the mass balance, that is
evaluated on the base of the mass balance ratio
(MBR). This variable is computed within the time
step as the ratio of soil water storage variation to
the sum of incoming (precipitation) and outgoing
(surface and subsurface, evaporation and transpira-
tion) flows.
MBR ¼ Dstorage
fluxin � fluxout
(7)
The two values represent the same phenomenon,
therefore in a fully conservative algorithm one should
have MBR = 1. When incoming and outgoing flows are
very low or equal the equation produces a numerical
overflow, so we prefer to use the expression:
MBR ¼ storagetþDt
storaget þ fluxin � fluxout
(8)
avoiding numerical problems, as water content never
gets to zero. The mass balance error E is then defined as
E ¼ 1�MBR (9)
that can be easily used as a parameter to evaluate the
quality of the system solution produced by every
approximation, setting a tolerance threshold below
which the balance is considered correct and the time
step is accepted.
The numerical model was implemented as a dynamic
link library (DLL) daily coupled with the Criteria/
Wofost environment. The environment inputs to the
DLL are soil data, boundary conditions (impermeable
bottom or water table depth), initial soil moisture
conditions and daily precipitation. The DLL then
computes profile water content and returns it to the
environment, which in turn simulates evaporation and
transpiration flows, root growth and above ground
biomass accumulation.
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