In: Wagner W., Székely, B. (eds.): ISPRS TC VII Symposium - 100 Years ISPRS, Vienna, Austria, July 5-7, 2010, IAPRS, Vol. XXXVIII, Part 7B
2. STUDY SITE AND DATA COLLECTION
Two sites were selected near Ottawa, Ontario, Canada for field
and satellite data collection, the Canadian Food Inspection
Agency (CFIA) research farm and a region of private producers
east of Casselman, Ontario. The terrain across these two study
sites can be considered level to very gently sloping (<2%) with
an average field size of 23 hectares. This region of eastern
Canada consists largely of com and soybean annual crop
production.
Ground truth measurements were performed on several selected
sites. Within the CFIA site, 13 fields including 16 com and 21
soybean sample sites were selected. At the Casselman site, 20
fields including 10 com and 10 soybean sample sites were
visited. Total LAI was measured at each sample site using an
LAI-2000 (Li-Cor, Inc., Lincoln, NE) plant canopy analyser
throughout the growing season. Volumetric surface soil
moisture was measured coincident with each SAR acquisition,
using Delta-T Theta probes with 6-cm waveguides. At each
site, mean soil moisture was calculated from ten replicate
moisture measurements.
SAR images were acquired by TerraSAR-X, PALSAR/ALOS,
and RADARSAT-2 satellites. During the 2008 growing season,
two RADARS AT-2 Fine beam mode quad-pol images (July 6
and 9) and one PALSAR/ALOS (July 2) were acquired over the
CFIA site; two RADARS AT-2 Fine beam mode quad-pol
images (August 23 and August 26) and one TerraS AR-X
stripmap image (August 21) were acquired over the Casselman
site. The pixel spacing of TerraSAR-X, PALSAR/ALOS, and
RADARSAT-2 is 3 m, 12.5 m and 8 m, respectively.
Characteristics of the SAR images used in this study are
summarized in table 1.
Date
SAR sensor
mode
poi.
incident
angle
07-02-
2008
PALSAR
LI.5
HH,HV
34°
05-23-
2007
PALSAR
LI.5
HH,HV
21°
07-09-
2008
Radarsat-2
FQ20
Quad-
pol
o
O
07-06-
2008
Radarsat-2
FQ6
Quad-
pol
26°
08-21-
2008
TerraSAR-X
stripmap
HV/VV
44°
Table l.Main characteristics of SAR images used in this study.
Optical images were acquired by the Compact Airborne
Spectragrahic Imager (CASI) and SPOT-4 multi-spectral
satellite. CASI hyperspectral data were acquired on August 21,
2008 over the Casselman site. SPOT-4 multi-spectral data were
acquired on July 6, 2008 over the CFIA site. From the CASI
and SPOT-4 data, the Modified Triangular Vegetation Index
(MTVI2) (Haboudane et al., 2004) was calculated. A non-linear
curve fitting procedure was used to establish an empirical
equation for LAI estimation from MTVI2 (Liu et al., 2009):
LAI = -6.247 x ln(0.946 - 0.643 x MTVI2)
Using this formula, LAI maps for the entire study site were
generated from the optical data, with an RMSE of 0.76 and an
R 2 of 0.85.
3. METHODOLOGY
3.1 Image processing
Radiometric calibration of TerraSAR-X and PALSAR/ALOS
images was carried out using the follow equations. These
equations were used to convert the digital number of each pixel
DNi into a backscatter coefficient ( a ).
For TerraSAR-X,
cr° (dB) = 201og 10 DN. + 101og l0 (CalFact) + lOlog lo (sin(0 ( .))
CalFactor is given in thè TerraSAR-X data delivery package
annotation file. It is processor and product type dependent.
For PALSAR/ALOS,
of (dB) = 101o glo (DN? ) 4- CF
The calibration factor (CF) for PALSAR L1.5 products is -83
dB. The ALOS and TerraSAR data products were delivered in
ground range. A 3 X 3 Enhance Lee filter was applied to both
the ALOS and TerraSAR data to reduce speckle noise.
RADARSAT-2 fine quad-pol SLC data were provided as
compressed stokes matrix values for each slant range pixel.
Prior to extracting the backscatter information, a boxcar filter
with a 5 by 5 kernel size was applied to the polarimetric SAR
scattering matrix data to suppress SAR speckle. After filtering
the covariance matrix was converted to a symmetrized
covariance matrix. From the symmetrized 3 by 3 covariance
matrix, intensity backscatter (HH/HV/W) was extracted. All
the data were then geometrically corrected and geo-referenced
using national road network vector data.
3.2 Water cloud model
The water cloud model was introduced first by Attema and
Ulaby (1978). In the general version of the water cloud model,
the power backscattered by the whole canopy (cr°) can be
represented as the incoherent sum of contributions of the
vegetation, ( a o ) ; and the underlying soil, ( a 0 ). This study
veg soi
selected the model modified by (Prévôt et al., 1993) as it
incorporates LAI as a descriptor of vegetation development. In
this model, SAR backscatter from a canopy at a given incidence
angle can be written as:
cr° = AL e cos é?(l - exp(-2BL t cos 9)) + o° oi¡ exp(-2BL / cos(0)
where x is the two-way attenuation through the canopy layer, L
is the LAI, expressed in (m 2 m' 2 ) , the backscatter coefficients
a 0 , and are expressed in power units. A,B, C,D and E are
model coefficients to be defined by experimental data. A, B and