The analysis of the resulting image of the ratio in TM4 (1993)
and TM4(1984) led to the following relation :
Objects with unchangeable reflectance have a value close to 1;
Objects with significant change have a ratio different from 1.
Two thresholds of change Tmin and Tmax Were determined on
the histogram of the ratio image using mean digital number of
some objects with significant change between the dates of
acquisition. Hence, the area of change was extracted regarding
the following relation :
- values comprised between the DNmin and Tmin represent
objects with decreasing reflectance. Values comprised between
the Tmax and DNpax -represent objects with increasing
reflectance.
- non change area is represented by values comprised between
Tmin and T max-
3.2.1. Results
According to the thresholds of change and the relation given
above, a forest change image corresponding to TM4 band was
obtained (see figure below).
It is however necessary to find out a relationship between
reflectance change and ground truth.
Figure. change detection map
175200 180900 384900
|
GR decrmaced vaties
mcreased vabies
272000
C non-change area
2689000
264.000
4. CONCLUSION
The adopted model takes into account the topographic features
of each pixel. However, slope and aspect maps were used. The
estimation of the coefficients of the linear regression led to
atmospherically comparable images. Then a ratio between the
corrected images was calculated to find out significant change
of each pixel.
The change map obtained, therefore, allowed us to localise the
change occurred in the study area. However, this was not
sufficient enough to say that the change really happened unless
it is confirmed by ground truth. This study constitute a topic of
further research.
REFERENCE
Andrieu B., 1982, Evaluation des données fournies par
télédétection aérospatiale pour l’étude multithématique d’un
massif forestier, Thèse de Docteur-Ingénieur de l’Université de
Pierre et Marie Curie, Paris VI, 189p.
Beaubien J.G., 1990, Application de la télédétection spatiale
à la cartographie des formations forestières et au suivi de leur
évolution, IFN, Options Méditerranéennes Série A N°4, 1990,
pp. 145-149.
Cavayas F., 1984 Correction radiométrique des effets
topographiques sur des images Landsat de territoires forestiers,
Thèse de Ph.D de l’Ecole des Gradués, Université Laval. 177
p.
Chamignon C., 1990,Evaluation comparée des satellites à
haute résolution spatiale en zone de moyenne et haute
montagne méditerranéenne, Thèse de Doctorat de l’Université
de Droit, d'Economie et des Sciences d' Aix-Marseille III, 377
p.
Danson F. M., Curran P. J., 1993,Factors Affecting the
Remotly Sensed Response of Coniferous Forest Plantations,
Remote Sensing Environment, N?43, 1993, pp. 55-65
Durrieu S., 1994, Utilisation de la télédétection satellitaire
pour la mise à jours de la carte des types de peuplements de
l’IFN: Application à une région forestière diversifiée de
moyenne montagne, Thèse de Doctorat de l’Ecole Nationale de
Génie Rural des Eaux et des Forêts 202 p.
Hakan O., 1994, Reflectance Calibration of Thematic Mapper
data for Forest Change Detection, Swedish University of
Agricultural Sciences (Part IV), pp. 1-21.
Hakan O., 1994, Relative Calibrated Landsat TM data for
Standwase Change Detection in Forestry, A pilot study on
Scots pine infected by Gremmeniella abietina, Swedish
University of Agricultural Sciences(Part-I), Remote Sensing
Laboratory, S-901 83 Umeä, pp. 1-9.
Kusaka T., Kakehi T., Ootuka M., 1996, Change detection
using relative atmospheric correction of satellite images at
different times, XVIII ISPRS-Congress, Vienna, 9-19 july 96,
Article, 5 p.
678 International Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998
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