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Biodiversity Monitoring Program in the Mwaro ecological corridor, Mikeno Sector, Parc National des Virunga

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par - Augustin K. BASABOSE, M. Gratien BASHONGA, Z. BALEZI
- - - 2010
  

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2. METHOD

2.1. Study techniques

2.1.1. Site Selection of permanent transect and plot

From GIS shapefiles and SPOT images of the area covered by the study has been identified for the preparation of a baseline map.

This map has been enriched by a layer of contour lines which allowed us to identify the best location of the permanent transect and plot for the study of habitat variation according to an altitudinal gradient.

Using the Map Source software and Arc GIS 9.2, we created geographic coordinates of the beginning and the direction of the permanent transect. These coordinates were then uploaded into the GPS and using the «GoTo function» of GPS; thus the planned transect was established in the field.

Figure 1. Location of Mwaro ecological corridor: setting of the permanent botanical 7 km long transect and 1-ha plot

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The plot's, establishment was carried out according to the recommendations of Kuebler (2003), using a vegetation long-term monitoring method alowing to assess the biomass, the growth, the structure and composition the forest.

2.1.2. Establishment of the permanent transect and plot

2.1.2.1 Opening the transect

The coordinates created and downloaded into the GPS were: S 1.45535; E29.34112 On the ground, thanks to the «Go To» function of the GPS, we approximately located the starting point at the coordinates S1.45535, E29.3411, at an altitude of 1867 m and corresponding to the starting point of the permanent transect.

Using a compass, we ran the tracker responsible for the opening of the transect in the East of the magnetic direction corresponding to the orientation of the corridor. The tracker, who opened the transect using a machete was brought back on course at every slightest deviation. Along the transect, each 50 m was marked with a colored ribbon on which was inscribed the distance reached. The distance along the transect was known by reading the figure indicated by the pointer function "map" of GPS. This corresponds to the distances travelled measured as the crow flies (rather tan distance traveled on foot, for example), which are best suited for representation in 2 dimensions of surfaces such as those used when making maps.

2.1.2.2. Establishment of the plot

A 1 ha plot was identified and located in a vegetation of 4 ha earlier prospected on a homogenous ground in Mwaro corridor. The making of the plot started with the opening of two perpendiculars lines in the target vegetation, one towards the east and the other towards the south and each with 100m long subdivided in 5 intervals of 20cm each. The first 2 intervals of 20 m of each transects were attributed the coordinates (00, 20) and (20, 00). At 40 m of each transect the coordinates become (00, 40) et (40, 00), likewise, at 60 m they were (00, 60) and (60, 00). From this we deduce that the coordinates at the end of the transects were: (00, 100) and (100, 00).

To establish a 1ha plot easily as well as to limit 25 quadrates of 20 m X 20 m within the plot, KUEBLER (2003) recommands, to limit the first quadrat at coordinates (20, 20) which corresponds to the perpendicular point at the distances of 20 m of 2 transects. The next point of the limitation of the quadrat n° 2 had thus (40, 20) as coordinates; the third point for quadrat 3 was (60, 20, then (80, 20) for the fourth quadrat and (100, 20) for the fifth.

At this level, the next stage, according to the same method, consisted in identifying the point of limitation of quadrat n° 10 just near quadrat n° 1. This is the point of coordinates (20, 40) then the point of coordinates (20, 60), (20, 80), (20, 100). There followed the identification of point (40, 40) and in the same way the identification of point (60, 40) ; (80, 40) ; and (100,40) as well as (40, 60) and (40, 80) (40, 100). The next identified point was (60, 60) followed by (80, 60) and (100, 60) and then (80, 80) and (100, 100).

Biodiversity survey of Mwaro corridor, Altitudinal distribution of the vegetation and assessment of Gorilla food availability

Then the 25 quadrats were identified by reference numbers in 1 - 5, 5-6; 6-10; 10-11; 11-15; 15-16; 16-20; 20-21; 21-25 (figure 4).

5

6

15

16

25

4

7

14

17

24

3

8

13

18

23

2

9

12

19

22

1

10

11

20

21

 
 

20 m

Figure 2. Schematic representation of the 1-ha plot established in Mwaro corridor

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