Complementary Nature of SAR
and Optical Data for Land Cover/Use Mapping in the State of Johore,
Malaysia
Z. A. Hasan, K. M. N. Ku
Ramil, I. Selamat and K. F. Loh Malaysian Centre for Remote Sensing
(MACRES) 5th Floor, City Square Centre, Jalan Tun Razak, 50400 Kuala
Lumpur Lot CB 100, 5th Floor, City Square Centre, Jalan Tun
Razak, 50400 Kuala Lumpur, Malaysia Fax: 603-2645650, Tel:
603-2635640 E-mail: IPA@MACRES.GOV.MY
Abstract Under the EC-ASEAN ERS-1
Programme, MACRES has undertaken a pilot project to assess the
complementarity of Landsat TM and ERS-1 data for land cover/use mapping in
the state of Lahore, Malaysia. Three conclusions were arrived at. These
where-ERS-1 data by themselves are of limited use for land cover mapping
due to insignificant difference (less than 2.0 decibels) in backscatter
returns of the major cover types found in the study area. The HIS
composite of TM 453 with the ERS-1 substituting for the intensity gives
the best differentiation of cover types visually, and ERS-1 temporal data
has potential for effective land cover change detection, making it a
useful tool for updating existing land use/cover digital data derived from
optical remote sensing.
Results substantiating the above
conclusions are highlighted in the paper. Of particular interest are the
temporal backscatter signatures obtained from the cover types in the study
area.
Introduction Optical data such as SPOT and Landsat
TM, complementing aerial photography are presently used for land use/cover
mapping in Malaysia by the Department of Agriculture (DOA). Apart from the
advantages of using these data, there are two major problems encountered:
-(i) The availability of cloud free data for regular updating particularly
in Johor and (ii) The difficulty to differentiate some land use/cover
types such as rubber and oil palm which are having almost similar spectral
response (Loh, et. al, 1995; Brown. Et. al, 1995). SAR data with the
capability to penetrate through the clouds becomes more important
especially in those areas with persistent cloud covers. However, the
understanding and processing of SAR data is still at its infancy stage and
this will limit the use of SAR data in Malaysia for the time
being.
A pilot project entitled "Complementary Nature of SAR and
Optical Data for Land Use/Cover Mapping in Johor (MAL-1) was implemented
during 1993-96 under the auspices of EC-ASIAN collaboration. The main aim
of the project was to effect the transfer of technology on the use SAR
data from the EC to ASIAN nationals to meet developmental and
environmental needs. The Objectives of this paper were:
- To develop a methodology for complementary use of ERS-I SAR and
optical data for land use/ cover mapping
- To analyse the complementarity of ERS-1 and optical data for land
cover change detection.
Material and Methods
- Description of Study Area
Johor State was selected because
the experiences extensive cloud covers problem throughout the year and
flat terrain of most the area except at the Gunung. However due to
limited availability and late delivery of ERS-I data, the project tem
could only focused on areas covered in topographic map sheets 124, 125,
129 and 130 series L 7010 at the scale of 1: 63 360 as shown in Figure
1. However, full processing of SAR data was done only on map sheet 130.
The land use/cover of Johor are predominantly plantation crops such as
oil palm, rubber, coconut, forest and pineapples. Most of the vegetation
is therefore perennial with little seasonal change.
Figure 1: Location of
Study Area
- Materials
ERS-I SAR Imagery PRI
images were used for the study PRI images were considered as second
level data where the basic corrections - the reduction of speckles using
multi-lock images and slant to ground range conversion have already been
performed by the ground station. A total of 16 frames were delivered to
MACRES out of which 8 images (Table 1), covered over the same area and
used in further processing of ERS-I data
Table 1 : ERS-I SAR data used for
the processing
Orbit/Frame |
Date |
Phase |
Processing Station |
10512/3573 |
20.07.93 |
C |
German |
10714/3573 |
05.08.93 |
C |
German |
11013/3573 |
24.08.93 |
C |
German |
12244/3573 |
18.11.93 |
C |
German |
12917/3573 |
04.01.94 |
D |
Thailand |
13218/3573 |
25.01.94 |
D |
Thailand |
13519/3573 |
15.02.94 |
D |
Thailand |
13562/3573 |
18.02.94 |
D |
Thailand
| Notes:
Phase C- First Ice Phase - Apr. 1992 to Dec. 1992
Phase D-
Multi-disciplinary Phase- Dec. 1993 to Mar. 1994 Landsat
TM Imagery Three imageries were available for the
project;
Path/Row |
Date of Acquisition |
125/59 |
11.03.1991 |
125/59 |
26.06.1995 |
126/59 |
22.06.1995 | The images were
printed at the scale of 1:250000 for the full scene and also 1:50000 for
smaller area corresponding to topographic map sheet
size.
Ancillary Data The ancillary data used for
the study were topographic maps, landuse maps and field survey data.
Topographic maps at the scale of 1:63 360 were used as a reference for
fieldwork and preliminary abstraction of landuse/cover information for
the area. Landuse maps prepared by DOA were used for the fieldwork. For
better discrimination of crop boundary the digital landuse vectors were
overlaid on the images.
Several field works were conducted at the
site selected based on the availability of the data. Images of ERS-1 SAR
data, Landsat TM and combination of both were used for tile
fieldwork.
- Methods
Data Processing The
processing was carried out using Meridian, Ergo-Vista and MICSIS
software available at MACRES.
Compression The 16 bit
ERS-I data were compressed to 8 bit data due to the limitation of
Meridian software in processing 16 bit data. The higher digital numbers
correspond to urban areas and corner reflectors. However the region of
interest, vegetative covers have DN's ranging from 0 to 1500. These
values were maintained during vegetation cover a wide dynamic range in
DN values.
Geo-Referencing The Landsat TM imagery scene
125/59 dated 1 1.03.91 was geometrically rectified to conform to the
Malaysian map projection using 20 control points digitized from
topographic maps at the scale of 1:63360. The geocoded images was then
resampled to 12.5 pixel to correspond to the pixel size of ERS-I SAR
data. Then all the SAR data were rectified using images to image
registration techniques with the geocoded Landsat TM data as the
reference image.
Filtering Speckles of noise were
resulted from the coherent nature of radar waves. The presence of
speckles in the image reduces the ability of the user to interpret the
images. Several filters were evaluated. These included few common
filters such as mean, median, average, low pass and high pass filters.
However, these filters were not suitable for SAR data. Attention was
given to the special SAR filters such as Lee, I Frost, Map and Map
Refined developed in Ergo-Vista software. The analysis was based only on
visual interpretation not al all based on Stastical
approach.
Visual Analysis Six panchromatic ERS-I
images, four multi-dates ERS-I, SAR, two images from combination of
Landsat TM and ERS-I and two images from Intensity, hue and saturation
transformation were produced for visual interpretation. The analysis was
made by comparing, the images generated with existing land cover map
cover and ground survey data. Results and Discussions
- Filters
Generally the filter kernel size of (7 x7) and
smaller gave better visualization compared to bigger filter kernel
sizes. The blurring increased as the size of the filter kernel
increases.
Lee filter was found to be effective in smoothing
homogeneous areas and at the same time blurring fine features. Frost
filter was effective in retaining fine details and edges but slightly
lower performance in homogeneous areas. Mp filters showed better results
than the other two filters especially its ability to enhance linear
features, field boundaries land also smoothing in homogeneous
areas.
- Visual Analysis
Single Data SAR
Data Six panchromatic images were produced for
interpretation. Single data images did not provide good discrimination
among features on the ground and therefore are not useful for visual
analysis. The image 10512/3573 dated 20.7.93 was found to be brighter
than the other five images. This was due to the strong wind that caused
the ruffle on the water resulting in a strong return to the sensor and
hence the image appeared brighter. This is clear indication of the
sensitivity of SAR data to surface roughness.
Multi-dates
SAR Data Four colour composites have been generated for
multi-dates ERS-I SAR. These composites improved the visual
interpretability of land cover features compared to the single data SAR
data. With the correct choice of dates for combination, the information
extraction could be maximized.
ERS-1/Landsat TM
Combination Two combinations were generated Two SAR data with
one. TM data and two TM data with one SAR data. The information on the
images was dominated by Landsat TM data especially band 4 which was an
infrared band and very sensitive to vegetation cover. Contribution from
SAR data was more conspicuous in hilly areas where the effects from
relief were accentuated.
HIS Transformation The
national of this transformation was to replace the intensity image,
which was the least sensitive to the human eyes compared to Hue and
Saturation, with ERS-I SAR data. Bands 3, 4 and 5 of Landsat TM data
were converted to HIS and the Intensity i e replaced wit one selected
SAR data and reconverted to RGB. As a result, an image with better
delineation of crop boundary was generated.
Oil
Palm Oil palms when mature is generally distinguishable by a
high backscatter and there fore appear as bright colours on
multi-temporal images. It also tends to be uniformed in brightness with
little variation between dates. Young oil palm up to three years from
planting is more variable due to changes in ground cover and soil
conditions and can be confused with rubber and forest. The backscatter
of young oil palm was less than that of mature oil palm. Therefore it
looks darker compared to colour of mature oil palm (Brown. Et. al,
1995).
Figure 2 : Different ages
of oil palm as seen on Landsat TM dated 1991 (a) and ERS-1 SAR data dated
4 Jan. 1994, 25 Jan. 1994 and 18 Feb. 1994 (b). A: Oil palm planted in
1968 B: Oil palm approximately 30 years old in 1991 and replanted
before 1994
Figure
3: Different ages of oil palm on ERS-1 SAR data ERS-1 SAR image,
Lee filtered 3x3 Red : 4 January 1994 Green : 25 January
1994 Blue : 18 February 1994 Phase 5, 6, 7 :planted 1964 Phase 4
: planted 1993
Figure 4: Rubber and palm on
multi-temporal ERS-1 SAR data, Lee filtered 3 x 3.
with 1990 land
cover map Red : 4 January 1994 Green : 25 January 1994 Blue : 18
February 1994
Figure 5: Banana plantation
on ERS-1 SRS image Red and Green : 24 Aug. 1993 Blue : 20 Jul.
1993
Figure
6: HIS image with 1990 land cover map Intensity from ERS-1 SAR data-20
Jul 1993 . Hue and saturation from Landsat TM data bands 3, 4,
5- 22 Feb. 1994
Figure 7: Pineapples as seen on
Landsat TM (a), ERS-1 SAR (b) and HIS images (c)
Multi-temporal ERS
images by themselves are of a limited value for land cover classification
of perennials because of small differences in their backscattering and
temporal stability (or lack of seasonal change)
ERS SAR is capable
of discriminating major land cover type such as oil palm and rubber. With
the exception of bananas the discrimination is not better than optical
imagery. Bananas show very clearly on SAR due to the very high
backscatter.
There is little advantage in combining ERS SAR with
optical imagery for land cover classification. There may be marginal
improvement in discriminating between land cover types and they are not
generally for dates close enough to exclude the possibility of changes
having occurred between the dates of the two sources.
The best way
of the two data types to complement each other would seem to use optical
imagery when available for baseline mapping, and to use multi-temporal ERS
SAR for change detection and map updating. This seems particularly
relevant for changes in large plantation and in forest cover.
An
approach that has been tried in the UK (Slater, Brown and Wooding, 1995)
is to create a multi temporal composites with image from different years
rather than from different months. With seasonal changes being for minor
importance, a three-year composite would effectively detect changes over a
throe-year period over large areas for relatively low
cost.
References
- Brown, R. E., Wooding, M. G., Batts, A. J., Loh, K. F., Ku Mohd Noh
Ku Ramli, Nordin, L., (1995) Complementary Use of ERS SAR and Optical
Data for Land Cover Mapping in Johore, Malaysia. Paper presented at ERS
Application Workshop, London, and September 6-8, 1995.
- ESA Publications, (1992) ERS-I Systems,ESA SP-1146
- Loh K. F., Ku Mohd Noh Ku Ramli and Nordin. L., (1995).
Complementary Nature of SAR and Optical Data for Land Cover Mapping,
Paper Presented at the Conf. On Remote Sensing and GIS for Environmental
Resources Management, Jakarta, Indonesia, June 6-8, 1995
- LOH, K. F., I. Selamat, Z. A. Hasan, Ku Mohd Noh Ku Ramli, S. Ahmad
(1996) Updating of Land Cover Maps Using SAR Data, Paper presented at
the 9th ASIAN Remote Sensing Experts Group Meeting, Jakarta, July 22-34,
1996
- Slater J., Brown R. E, and Wooding, M. G. The use of ERS- I SAR for
Monitoring of Environmentally Sensitive Areas in England, Processing's
of the Second ERS Publications Workshops, London, 6-8 December 1995. ESA
Publications.
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