490
Table 1. Values for the coefficients a and b in eq.
(2) for a number of crops with crop height H (after
Thunnissen 1984a)
Crop
H
(cm)
a
or 1 )
b
(K 1 -m 1 •s)
Grass
<15
0.050
0.010
Grass
>15
0.050
0.017
Potatoes
Sugar beet
60-,
60'
0.050
0.023
Cereals
100
0.090
0.030
Maize
200
0.100
0.047
le 24 /le 24 = 1 - B r (T -T*). (1)
p C C 1
24 24
where LE and LE are respectively the actual and
potential 24 hour P evapotranspiration rate (mm-d - ^),
B r (K _1 ) is a calibration constant and the subscript
i indicates instantaneous values. By means of eq. (1)
differences in radiation temperature of a certain
crop derived from thermal images can be directly
transformed into reductions in evapotranspiration.
Values for the calibration constant B r in eq. (1)
have been determined with the aid of TERGRA-model cal
culations (Thunnissen 1984a). It was found that B r
can be described by a linear function of the wind
velocity (u) at a height of 2.0 m above ground sur
face :
B r = a + b . u (K -1 ) (2)
Values for coefficients a and b were calculated for
different types of crops and crop heights (table 1).
For agrohydrological purposes heat images are usual
ly taken on clear days in the summer period. It was
found that for such days eqs. (1) and (2) can be ap
plied for the meteorological conditions prevailing in
the Netherlands.
2.2 Mapping of evapotranspiration from digitally tak
en reflection and thermal images
The relationship between the crop temperature and 24
hour evapotranspiration rate is crop dependent. This
means that crop temperatures derived from thermal
images have to be translated into evapotranspiration
rates for each crop type separately. Consequently a
crop map is necessary to compose an evapotranspiration
map. Several investigators have applied methods for
computer-assisted crop classification procedures with
the aid of digitally taken reflection images (e.g.
Crist and Malila 1981, Badhwar et al. 1982, Batista
et al. 1985).
Especially for grassland one has to account for
crop height. The Vegetation Index as defined by Tucker
(1977) can be applied for this purpose.
Afterwards with eqs. (1) and (2) differences in
radiation temperature for each crop type as derived
from thermal images can be transformed into reductions
in evapotranspiration. With the method developed
digitally taken reflection and thermal images can be
translated into evapotranspiration maps with the aid
of operational image processing systems.
2.3 Simulation of the water balance of a cropped soil
With a model such as SWATRE (Feddes et al. 1978,
Belmans et al. 1983) the use of water by agricultural
crops can be simulated during the entire growing
season, hence it can be used to investigate how far
the moisture conditions at particular times as deter
mined with remote sensing are representative for the
entire growing season. The SWATRE-model is a tran
sient one-dimensional finite difference soil-water-
root uptake model.
There are also three-dimensional models in which
saturated and unsaturated groundwater flow is link
ed. With these models also information about regional
evapotranspiration is obtained. The GELGAM-model
(De Laat and Awater 1978) is such a model.
Remote sensing images supply a synoptic view about
the location of areas with shortage of water and the
degree of the occurrence of drought damage. The
causes of drought damage can be diverse. The avail
able soil moisture for crop evapotranspiration is
determined by:
- the depth of the root zone;
- the available moisture capacity in the root zone;
- the hydraulic conductivity of the subsoil;
- the groundwater level during the growing season;
- additional water supply (rainfall, sprinkling
irrigation).
The first three factors are mainly dependent on soil
properties. One has to realize that no reliable in
formation about soil physical characteristics and
groundwater table depth can be obtained if sprinkling
irrigation is applied.
By simulating the water flow in the soil-plant-
atmosphere system the influence of the mentioned
factors on crop water supply can be determined under
different circumstances. This means that for the ex
planation of the occurrence of drought damage as de
tected with remote sensing, calculations with agro
hydrological simulation models can be applied.
2 RESULTS AND DISCUSSION
3.1 Determination of soil physical characteristics
Figure 2 shows a thermal image taken after a dry
period in the summer of 1983 of a part of the peat
area in the northeastern part of the Netherlands
(study area 1 in Figure 1), where mainly potatoes
(50%) , sugar beet (25%) and cereals (20%) are grown.
In Figure 2 boundaries as derived from the available
soil map (1:50,000) have been indicated as well.
Crops grown on Haplaquod soils (Hn21) show high tem
peratures. This means that severe drought conditions
prevailed. Relatively low-situated and more peacy
soils (iWp, iWz and iVz in Figure 2) show lower tem
peratures. This means that crops on these soils are
better supplied with water. Especially crops grown
on soils with a thick peat layer (more than 40 cm
peaty material between 0.0 and 0.8 m below soil sur
face; indicated with iVz) show an optimal water sup-
Figure 2. Thermal image of a part of study area 1
(see Figure 1) taken on 8 August 1983 at 13.30 MET.
Black is cold and white is warm. For the indicated
soil codes see text