Full text: Resource and environmental monitoring

  
  
  
scale analogue spatial data bases on natural resources 
since the eighties on a national level, e.g. Plan National 
d'Aménagement du Territoire (PNAT, Senegal), Projet 
d'Inventaire des Ressources Terrestres (PIRT, Mali). On 
the other hand regional to subregional approaches to 
monitoring specific regions of interest in a more holistic 
and comparative manner are rare. 
Especially Sahelian regions of high ecological and 
economic value need permanent observation via medium- 
to-high resolution spaceborne remote sensing. 
Sophisticated methods of collection, integration, 
maintainance and analysis of spatial data have to be 
adjusted to regional and local environmental action plans. 
Harmonized and standardized data of specific networks 
of regions have to be integrated with national and 
international environmental action plans. Some pilote 
activities are in progress, e.g. the programme for 
managing the environment locally in Sub-Saharan Africa 
(MELISSA) of the World Bank Africa Region Environment 
Group or the subregional action programme (SRAP) of 
CILSS, IGAD, SADC, UMA and UNSO (UNSO, 1992, 
‘SADC et al, 1994, CILSS/PNUE, 1996, Prévost et 
Gilruth 1997). Nevertheless the efficiency of the 
comparative analysis of landcover and landuse change in 
seriously affected regions of Sahelian Africa is still at a 
low level. 
2. REGIONALIZATION OF REMOTE SENSING AND GIS 
IN THE SAHEL 
Approaches to large-to-medium scale monitoring of 
Sahelian regions have to combine field work, 
interpretation of aerial photography and classification of 
satellite imagery with informations extracted from 
topographic maps, thematic maps and statistical surveys 
(figure 1). 
Field mapping of soils and vegetation has to focus on 
keywords like taxonomy, soil erosivity, diversity, 
structure both horizontally and vertically and interactions 
with patterns of human impact on herbaceous and 
ligneous vegetation strata (Blanck et Tricart, 1991). 
The (semi-)detailed analysis of vegetation structure is 
supported by the interpretation of multitemporal aerial 
photography. Medium scale mapping of vegetation 
functional types and of regional landcover units is 
contributed by the analysis of satellite imagery. 
Integrated approaches to terrain analysis and remote 
sensing for desertification monitoring benefit from a 
specific variety of sensors with different spectral, spatial 
and temporal resolutions. Topographic and thematic 
maps with project-driven or nation-wide coverages are 
available in scales of 1:200000 and smaller. 
Local to regional dynamics of impact patterns have to be 
analysed. The visual stereoscopic interpretation and the 
computer-assisted multi-spectral as well as textural 
image classification of remotely sensed data support 
multi-thematic cartographic models of Sahelian regions 
by creating spatio-temporal landuse and landcover data 
layers. Modeling regional dynamics of degradation and 
desertification is above all supported by time series of 
remotely sensed data. Topo-chronological maps of land- 
cover change since about 1950 (aerial photography) and 
1972 (satellite imagery) respectively can be established 
(Csaplovics, 1990, Csaplovics, 1992), (figures 2,3). 
The impact of the severe droughts in the West African 
Sahel from 1968-1973 and 1983 to 1985 as well as the 
increase of anthropozoic pressure on the Sahelian 
grasslands can thus be documented by remotely sensed 
data analysis. Multi-temporal maps of the degradation of 
soils and vegetation will help to establish GIS data bases 
of the landcover status and change of Sahelian regions. 
Case studies improved the presented design of a 
complex methodology for multi-temporal regional 
investigations. The regions of the river Niger are key 
regions of the West African Sahel in geographical and 
hydrological terms as well as in terms of specific socio- 
economic and socio-ecological impact. The inter- and 
intrarelations of environmental impact patterns and their 
effects on destabilization are documented and analysed 
by the fusion of multitemporal earth observation data of 
different sensors and in different scales and by 
integrating map and ground truth informations via GIS- 
technology (Csaplovics, 1996, Csaplovics 1997). 
3. OUTLOOK 
Local and regional planning for restoration and 
sustainable development depends on powerful tools for 
monitoring and modeling the dynamics of landcover 
change. Remote sensing and GIS facilities have to be 
developed in terms of appropriate technologies. Providing 
regional planning with high-quality spatio-temporal geo- 
informations increases the efficiency of substituting 
information for non effective energy by matching 
resources to specific requirements 
Regional centers of remote sensing and GIS have to be 
established in the Sahelian countries. Plans to launch 
small non-profit remote sensing platforms with on-board 
sensors designed for medium (to large) scale monitoring 
of Sahelian regions should be executed as soon as 
possible. Fast accessibility to and low prices of remotely 
sensed data have to be guaranteed. Connecting regional 
GIS working units with national and global networks 
should increase the awareness of the correlation of 
processes of local, regional and continental variations of 
degradation and desertification (figure 4). 
Regional planning needs up-to-date environmental 
information systems for approaching real time evaluation, 
prediction and prevention. Main support is contributed by 
establishing operationalized methods of data exchange at 
a multi-regional level. Networking facilitates cooperation 
and coordination of monitoring and planning at 
subregional, regional and international levels in both a 
horizontal and vertical direction. The success of 
subregional and regional initiatives depends on finding 
the knot to connect high-tech internet tools with 
concepts of low-cost appropriate technology as well as 
with concepts of participation. 
REFERENCES 
Blanck, J.P., Tricart, J., 1991. Quelques types de 
dégradation des milieux sahéliens. Zeitschrift für 
Geomorphologie. Supplement-Band 83:17-21. 
CILSS/PNUE, 1996. Systèmes d “information 
environnementale dans la sous-région  sahélienne. 
Rapport final. 
Csaplovics, E., 1990. Monitoring desertization dynamics 
in the Canal du Sahel region (Mali) using Landsat TM and 
MSS data. In: Coulson MG (ed) Remote sensing and 
global change, Proceedings of the 16th Conference of 
the RSS, Swansea, pp. 31-40. 
104 International Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998 
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