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 Projects: Mount Oku and Ijim Ridge (Cameroon)

Methodology

The methodology flowchart shows the different processing steps that have been taken in order to be able to merge the entire data set together. The processing has been divided into four main blocks:

  1. Classification
  2. In the classification stage, a supervised classification procedure was applied to each image using a maximum likelihood algorithm. The selection of the training sites was aided with the results of a first unsupervised classification, which helped to determine those classes spectrally separable, and NDVI analysis used to determine areas of high biomas and shadows in the images due to topographic effects. Also, the display of false colour composites helped determining areas covered by vegetation. Images were classified into 5 different groups: water, montane forest, grassland, scrub/tree savannah and farmland.

     

  1. Geometric corrections
  2. Due to the mountainous nature of the area (a volcanic cone ranging from 800 to 3000 meters), important distortions due to relief displacement were present in the images, especially in the aerial photographs. For this reason, image orthorectification was required. For both aerial photos and satellite images, a single frame orthorectification was carried out using a DEM derived from a Radarsat stereo-pair. Ground control points (GCP’s) were obtained from a topographic map of the area and the entire dataset was registered to the Universal Transverse Mercator (UTM) projection.

     

  3. Image manipulation

The image manipulation stage was different for aerial photos and satellite images. For aerial photographs, since the forest boundaries were quite discernible, no other processing technique apart from "heads up" on-screen digitising was necessary. The output of the digitising process is a vector layer that was converted into a raster image in order to merge the entire data set together.

For the satellite images, after orthorectification, the five categories in which the original images were classified were merged and re-coded to create binary images of "forest" / "non forest". These binary images showed pixels that were classified as forest but located outside the forest boundaries. These mis-classified pixels were masked out using the rasterised 1958 image (the earliest data available) as a binary mask. This approach, therefore, assumed that no regeneration had taken place outside the forest limits defined in 1958.

  1. GIS integration

At this point we have a set of five binary images showing the forest extension at different dates. These images were then combined in a GIS environment. Image couples of successive dates were analysed in order to obtain information about change trajectories, (i.e. deforestation or regeneration patterns). For this purpose, the images in each of the four combinations were re-coded. The first date image kept the 0/1 coding for "forest/ non forest" and the second date image was then re-coded into 0/2 for "forest/ non forest". Consequently, when images were combined (by addition), the output image presented four different values (0-3) related to number of times each pixel of the final output appeared in the input images:

0 for "non forest"

1 for those pixels classified as forest only in the first image à deforestation

2 for those pixels classified as forest only in the second image à regeneration

3 forest in both the first and second images à no change

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