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System overview
1)
Input data
2)
Pre-processing
3) Energy Balance Mapping
Calibration
VIS atmospheric correction
TIR atmospheric correction
Air temperature mapping
Cloud detection
Global radiation
Net radiation
Sensible heat flux
Actual evapotranspiration
4) Rainfall mapping
5) Drought and desertification monitoring
6) Crop yield forecasting
7) Further reading
tip:
order the EWBMS final report on the EWBMS
site
System
overview
The
flowchart shows the whole process from input to the creation of the final early
warning products. It starts with the processing of images from METEOSAT
geostationary satellite and WMO-GTS precipitation data by the energy balance
monitoring and rainfall mapping systems. These two systems generate the energy
and water balance products, which are then used as input for the desertification
monitoring and crop growth simulation models. The final output, desertification
indices and crop yield forecasts, mainly find their use in drought, food and
famine early warning applications. Products generated by the energy balance
monitoring and rainfall mapping systems are especially useful for hydrological
and meteorological applications.
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1) Input
data
-
Hourly received
visible(VIS) and
thermal infrared(TIR) images from the METEOSAT geostationary satellite. The visible band covers the
wavelengths from 0.3 to 1.05 μm. The thermal infrared band covers the
wavelengths from 10.0 to 13.1 μm.
- Precipitation data from the Global Telecom System of the World Meteorological
Organisation (WMO-GTS)
2) Pre-processing
-
Cloud level estimation using temperature thresholding
-
Counting cloud level durations (CD)
-
Extracting local noon and local midnight sub-frames
-
Detection, statistics and repair of defect scanlines
3)
ENERGY
BALANCE MAPPING
Calibration
TIR
channel :
based on calibration coefficients provided with the satellite data
VIS
channel :
vicarious calibration using Cumulonimbus cloud albedo as reference
Calibration
converts satellite VIS counts into
planetary albedo (A') and satellite TIR counts into planetary temperature (T0')
VIS atmospheric correction
Based
on a two-flux global radiation transmission model as proposed by Kondratyev
(1969). The model was extended to include both absorption and scattering. The
effect of the atmosphere is parameterized in terms of optical depth (t
or tau). Once the optical depth is known, the model allows to derive the atmospheric
transmissivity (t) and the surface albedo (A) from the planetary albedo (A').
The fraction of solar radiation absorbed at the earth surface then follows from
t*(1-A). The following figures show the surface albedo (A) and the absorbed
radiation t*(1-A) as a function of the planetary albedo (A').

Atmospheric
correction comes down to determining the optical depth (t).
This is done using the darkest land pixels in the image as a reference. These
represent dense forest with a typical surface albedo of 7%.
TIR atmospheric correction
The
relation between the planetary temperature (T0') and surface
temperature (T0) may be represented by:
k = cos
im * (T0-Ta) / (T0'-Ta)
Here,
k is an atmospheric correction coefficient and im is the satellite
zenith angle. The air temperature Ta is also derived from the
satellite data, as explained in the next section. The atmospheric correction
comes down to finding a corresponding pair of T0 and T0'
values and then calculating k. This is done by finding the driest pixels
(highest temperatures), for which we assume LE= 0. In this specific case the
actual surface temperature may be calculated from the net radiation (In) with
T0=Ta+In/a,
where a
is the heat transfer coefficient.
Air temperature mapping
A
plot of noon planetary temperatures (T0'n) versus midnight
temperatures (T0'm) shows a linear relation. This relation
is determined by means of regression analysis: T0'n = a.T0'm
+ b. Along this line heat exchange wit the atmosphere is variable. In case of
perfect heat exchange there is no temperature difference between the surface and
the atmosphere and consequently : T0'n = T0'm
= Ta. Combining these two relations, the air temperature is found
from the regression constants with Ta=b/(1-a). This air temperature
is to be interpreted as the temperature at the top of the atmospheric boundary
layer. The procedure is applied to a sub-window and the air temperature is
assigned to the center pixel. Subsequently the window is shifted over the image
and the procedure is repeated for each pixel. In this way
a complete air temperature map is obtained.
Cloud detection
A
cloud detection algorithm is used which discriminates clear and cloudy pixels. A
minimum albedo map (Amin) is extracted from a sequence of
10 days noon visible images. A maximum noon surface temperature map (Tmax)
is obtained by searching the highest temperature within a shifting window of
200*200 pixels. Both are considered to represent cloud free conditions.
Subsequently several tests are carried out to determine if a pixel is cloudy or
not. The most important ones are:
1) A' ³
Amin + DA
2) T0' £
Tmax -
DT
DA
and DT
are thresholds, which have been determined empirically.
Global radiation
The
transmissivity of the atmosphere (t) is derived together with the surface albedo
as discussed in section 4. The global radiation at noon (Ign) is then
obtained with:
Ign = S . t . cos is
where
S is the solar constant (1355 W/m2) and is the solar zenith angle.
The solar zenith angle is a function of longitude, latitude, time of the day and
day number. The daily average global radiation Ig is obtained by
integrating the function cos is from sunrise to sunset. When a pixel
is flagged cloudy, the radiation transmission through the cloud (tc)
is estimated from the cloud albedo using a relation from Kubelka-Munk theory. tc
is then used in stead of t in the previous equation.
Net radiation
The
net radiation is calculated with:
In = (1-A).Ig + Ln
Ln
is the net thermal radiation flux, consisting of an upward component emitted by
the surface and a downward component emitted by the atmosphere.
Ln = e0
ea
sTa4–
e0
sTo4
e0
is the surface emissivity. A value of 0.9 is assumed. The atmospheric emissivity
ea
is estimated with the Brunt equation on the basis of climatic values of air
humidity. Below clouds the upward and downward fluxes almost cancel (Ln
»
0).
Climatic net radiation
It
is convenient to express the long wave radiation flux as:
Ln »
e0
(1- ea)
s
Ta4 + 4 e
s
T3 (T0-Ta) = Lnc + Hr
The
first part on the right side is the climatic net long wave radiation (Lnc).
The second part is the radiative heat flux (Hr). Our net radiation
product is the climatic net radiation. Hr is treated as a part of the
sensible heat flux.
Sensible heat flux
The
sensible heat may be written as:
H = Hc + Hr = C.va (T0-Ta)
+ 4 e
s
T3 (T0-Ta)
Hc
is the convective sensible heat flux. T0-Ta is the
surface-air temperature difference as measured by satellite at noon (sections 5,
6). C is a convective heat exchange coefficient, which depends on the roughness
of the earth surface. For bare land (LE=0) a value of
C=1 is used. For vegetated surfaces (LE¹0)
the value is allowed to grow slowly in line with the vegetation development,
until a maximum value of 2.4. The daily average of the sensible heat flux is
obtained assuming constant energy partitioning (constant Bowen ratio). The
default output of the system is the convective daily sensible heat flux Hc.
This product is most convenient for comparison with convective flux
measurements, for example based on eddy correlation or scintillometry.
Actual evapotranspiration
The
daily actual evapotranspiration is obtained as the residual term in the energy
balance equation.
LE = In - H
At
daily time scale the soil heat flux can be neglected. If pixels are cloudy, the
sensible heat flux cannot be determined. However, as discussed in section 8, the
net radiation under clouds is estimated. The actual evapotranspiration is then
estimated using the energy partitioning determined at the last cloud free day.

Often, the NDVI or another vegetation index is used for drought early warning or
as a crop growth indicator. However, the NDVI lags behind the actual
evapotranspiration, which represents the real actual crop growth conditions. For
example, in the case of a dry spell the spectral behavior of vegetation in the
visible and near infrared part of the spectrum (NDVI) will not change
immediately, but the actual evapotranspiration will do so, because when
experiencing water stress the stomata of leaves respond immediately and will
close partly or fully.
Further reading on energy balance mapping, click here.
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4) Rainfall mapping
Rainfall
mapping is based on the discrimination of cloud top levels in hourly satellite
imagery, using temperature thresholds.
|
Cloud
level
|
IR
counts range
|
Temperature
range
|
Approximate
Height range
|
|
Cold
|
< 45
|
< 226 K
|
> 10.8 km
|
|
High
|
45 –
59
|
226
– 240 K
|
8.5
– 10.8 km
|
|
Medium
high
|
60 –
89
|
240
– 260 K
|
5.2
– 8.5 km
|
|
Medium
low
|
90 –
119
|
260
– 279 K
|
2.2
– 5.2 km
|
|
Low
|
119
– air count
|
279
– air temp. K
|
<
2.2 km
|
For
each level the Cloud Duration (CD) is counted hourly during a period of 10 days.
Rain
gauge data are obtained daily from the WMO-GTS system. A local regression
equation is established for each rainfall station;
R = S aij CDij
+ dj
where
aij is the regression coefficient for the cloud duration at level i
at rainfall station j. dj is the residual at rainfall station j. The
regression is based on the observations in station j and the closest 11
surrounding rainfall stations. The regression coefficients and the residual are
subsequently interpolated between the rainfall stations for each pixel.
Hereafter the rainfall is determined on a pixel by pixel basis.
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5) Drought and desertification monitoring
Two drought and desertification indices are generated: the climatic moisture
index (CMI) and the soil moisture index (SMI). The CMI was defined by the United
Nations Convention to Combat Desertification (UNCCD) in 1994 as:
CMI
= L.R / LEp
LEp is the potential evapotranspiration in
energy units. This quantity is closely related to the net radiation (LEp
» 0.8 * In ). It can also be
obtained from satellite observed air temperatures using the Thornthwaite
equation. The result is almost the same.
The CMI indicates a climatic condition. To
characterize the actual drought or desertification status of the ground, the
relative evapotranspiration or soil moisture index (SMI) is used.
SMI = LE / LEp »
1.25 LE/In
The difference between drought and desertification
indices is just a matter of time scale. Desertification indices are at least
yearly, drought indices are 10 daily or monthly.
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6) Crop yield
forecasting
Crop
yield forecasting is based on a a newly developed crop growth model, which uses
the satellite derived radiation and actual evapotranspiration data as input. The
model is based on the observation by Monteith, that all crops have about the
same growth rate per unit leaf area and that differences
in production can be explained by differences in crop geometry and
corresponding light interception. This model was extended to include the
effects of drought and photosynthetic efficiency.

The
gross photosynthesis (P) is given by:
P
= c * e
* Ig * C * R
where
c is a conversion factor, e
is the photosynthetic efficiency of light, Ig the global radiation, C
the crop coverage and R the crop relative growth. The crop coverage is estimated
from the biomass: C = B/BM, where BM is the biomass at
full cover. The relative growth (R) is derived from the relative
evapotranspiration using the formula of Stewart as presented by Doorenbos and
Kassam (1979)
R = (1-k) + k * (LE/LEp)
Here
k is a crop specific constant. The light efficiency is calculated with (Rosema et al. 1998)
e
= 1 / (1.25 + const * Ig)
Here
the constant is also crop specific. The maintenance respiration (M) is expressed
as a function of the relative evapotranspiration and is proportional to the
biomass (B):
M
= cresp * B * f(LE/LEp)
The
calculation of R and M is done on a daily basis. Every day net biomass increase
is added to the total biomass
Bi+1 = Bi + P - M
The
simulated crop biomass is used as an indicator of the final economic yield at
any stage of the growth cycle. For yield forecasting a relative approach is
usually followed. This implies that the biomass development is simulated two
times: (1) for the actual evapotranspiration (->B) and once for potential
evapotranspiration (->Bp). Subsequently the relative economic
yield is assumed to be equal to the relative biomass production.
Y/Yp = B/Bp
The actual economic yield (Y in kg/ha) can be
obtained after estimating the potential economic yield (Yp) in the
area considered. This value may be obtained on the basis of local information
such as historic records of reported yield data.
The relative biomass production (B/Bp)
stabilizes already halfway the growing season. For this reason satellite derived
values of relative biomass production (relative yield) can be used for crop
yield forecasting and early warning.
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7)
Further
reading
Doorenbos, J. and A.H. Kassam
(1979) "Yield response to water" FAO Irrigation and Drainage Paper 33,
FAO, Rome, 193 pp.
EWBMS final report (2001) "European Energy and
Water Balance Monitoring System" project
ENV4-CT97-0478,
European Commission, Research and Development, Programme in the field of
Environment and Climate, Theme 3. 148 pages.
For further reading on
rainfall and energy balance mapping , order this report on the EWBMS
site.
Kondratyev, K.Y. (1969) "Radiation in the atmosphere", New York,
London: academic Press.
Monteith, J.L. (1977)
"Climate and the efficiency of crop production in Britain",
Philosophical Transactions of the Royal Society, London B, 281, 277-294
Rosema A. (1986a)
"Results of the Group Agromet Monitoring Project (GAMP)", ESA-Journal,
vol. 10, no. 1, 1986, p 17-41.
Rosema A. (1993)
"Using METEOSAT for Operational Evapotranspiration and Biomass Monitoring
in the Sahel region", Remote Sens. Envir. 45:1-25 (1993)
Rosema A., R.
Roebeling, S. Peter, S. Garrido, H.A.R. de Bruin, M.J.M. Saraber,
J.N. Roozekrans, F. Garcia, K. Kok, F. Stolle and M.C. Bronsveld (1994)
"Assessment and Monitoring of Desertification in the Mediterranean
area" (ASMODE), summary final report", project EV5V-CT91-0029,
European Commission, Research and Development (XII), Programme in the field of
Environment, Topic IV.3.
Rosema, A., R. Roebeling and D. Kashasha (1996)
"Using Meteosat for Water Budget Monitoring and Crop Early Warning",
in Agrometeorological Applications for Regional Crop monitoring and Production
Assessment", Rijks, Terres and Vossen, eds., pp 161-175, EUR 17735 EN
Rosema, A., J.F.H. Snel, H. Zahn, W.F. Buurmeijer
and L.W.A. van Hove (1998) "The relation between laser induced chlorophyll
fluorescence and photosynthesis", Remote Sens. Environ. 65:143-154 (1998).
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