Full text: XVIIIth Congress (Part B7)

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LAND DEGRADATION RISK MAPPING USING NOAA NDVI DATA 
Shiro OCHI(*) and Shunji MURAI(**) 
* Assistant Prof, Dept. of Forestry, Utsunomiya Univ. 
350 Mine, Utsunomiya 321 Japan 
Tel:+81-28-649-5537/Fax:+81-28-649-5545 
E-mail:ochi@cc.utsunomiya-u.ac.jp 
** Professor, Institute ofIndustrial Science, Univ. of Tokyo 
7-22, Roppongi, Manatoku, Tokyo 106 Japan 
Tel:+81-3-3402-6231(ext.2560)/Fax:+81-3-3479-2762 
E-mail:murai@shunji.iis.u-tokyo.ac.jp 
Commission VII, Working Group 6 
KEY WORDS: Land Degradation, NDVI, GVI, Land Cover, Vegetation, Global Data set 
ABSTRACT : 
Land degradation risk map was tried to be generated using NOAA 8k NDVI 10 days composite data set of 10 years from 
1983 to 1992, and Global data set such as climate data, elevation data, and thematic maps. Before proceeding the time series 
analysis, the data quality was examined using the technique of moving average for 12 months(36 scenes). The quality ofthe 
NOAA 8km NDVI data was estimated as good enough to use fortime series analysis with little data modification. 
The fluctuation pattern of NDVI forseveral land cover type were defined fromexisting eco-regions map, and the map was 
resampled to low resolution to 8km resolution. In combination with the eco-region map with digital elevation data and 
precipitation data, soil erodability is checked. And eco-region classification map and vegetation degradation map shows the 
risk against the desertification, land degradation. The accuracy verification is not undertaken, however, the methodology 
can be applied to the LAC or GAC data set. 
1. INTRODUCTION 
Due to the increase of population pressure, climate change, 
etc, Land Degradation can be seen in many places on the 
earth. The importance forthe assessment ofland degradation 
and desertification by means of Remote Sensing technology 
is pointed out in Agenda-21, however, the methodology has 
not been established yet. In order to detect the land 
degradation using satellite imageries, an analysis is 
necessary with data which has high spatial resolution, and 
long observing period as possible. Data analysis, using the 
accumulated NOAA LAC(1km resolution) and GAC(4km 
resolution), are expected for global land cover change 
analysis. But we have to wait more some years until the 
compiled LAC and GAC data sets are distributed to us, and 
an advanced methodology and facilities should be developed 
for the management of such huge data scts volume. 
At this moment, we can obtain NOAA complied data with 
8km spatial resolution which includes daily data set as well 
as 10 days composite data set for more than 10 years 
observing period from1981. The methodology by using 
rather long time series data set must be developed for global 
land cover change analysis. And it can be followed by a 
aludy using more high resolution data set such as GAC and 
LAC. As the basic analysis forlong time series data set of 
NOAA data, this study aims following goal: 
-to develop a methodology, which can be applied to LAC or 
GAC data set in the future, forthe time series analysis on land 
degradation and vegetation degradation in continental scale 
as well as global scale, and 
-10 estimate the land degradation risk by monitoring long 
term land cover change using technology of GIS. 
2. DATA 
In this paper, 8km NDVI data of 10 days composite for 10 
years from1983 to 1992 which are distributed by NOAA are 
used to monitor the global vegetation degradation, and some 
GIS data such as average monthly temperature and 
precipitation data fromLeemans and CramerIIASA Climate 
data(30 minutes pixel resolution), Baily Ecoregions of 
Continents(10 minutes pixel resolution) and elevation data 
fromGLOBE data set. 
Before using 8km NDVI data for time series analysis, the data 
quality must be examined because the intensity ofthe NDVI 
is not sameon the same vegetation conditions due to the 
differences ofsatellites(sensors), positions ofsensor and so 
on. 10 points fromthe land of Japan were selected in order to 
examine the quality. Those are: 
(a) Deciduous Conifer Forest Dominant areca 
(b) Deciduous Broad Leaf Forest area 
(c) Rice Paddy Dominant area 
(d) Urban Area 
(e) Monsoon Evergreen Forest Dominant area 
Fluctuation pattern of Figure-1 shows the NDVI fluctuation 
pattern for deciduous conifer forest in Hokkaido, Japan. Each 
curve forselected 5 points clearly demonstrate the 
characteristics ofeach land cover type, however there are 
some scattering points due to the climate variety and data 
error. To avoid such scasonal and annual data variety, moving 
average method are used to evaluate the tendency ofthe 
pattern as well as to examine the data quality. The moving 
average were calculated using one year data(36 scenes). 
Figure-2 shows the moving average using 12 months for 
  
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International Archives of Photogrammetry and Remote Sensing. Vol. XXXI, Part B7. Vienna 1996 
 
	        
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