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Using tree- ring analysis to study the growth performance from saplings to trees for five savanna species in West Africa

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par Cocou A. F. Sinsin
Université d'Abomey- Calavi (Bénin ) - Master of science  2009
  

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4.3. Fire regime analysis from tree -rings of investigated species

4.3.1. Fire master chronology in CNP and UAC

The analysis of fire scars on investigated stem discs with dendrochronology techniques helped to have the master fire chronology in both sites as experienced by sampled tree that was presented in Figure 14 and 15.

Fire history in Comoe National Park

Number of scarred
tree

4

2

6

5

3

0

1

Forest border (A. leiocarpus, N = 8) Savanna (D. microcarpum, N = 10) Forest (D.abyssinica, N = 8)

Year

Figure 14: Fire history in Comoé National Park as experienced by sampled trees. In Common

legend, N means the number of tree analyzed for each species.

Number of scarred tree

18

16

14

12

10

4

2

8

6

0

1995 1996 1997 1998 1999 2000 2001

Fire history in Upper Aguima Catchment

Number of scarred tree Number of tree analyzed

Year

Figure 15: Fire history in Upper Aguima Catchment as experienced by sampled trees.

4.3.2. Fire interval

In Comoé National Park, 19 different fire dates were identified. The earliest fire of 1976 was recorded on two D. abyssinica trees (D1-105 and D1-108). The first tree germinated in 1971 and has only one fire scars and the other one germinated in 1974 with two different fire scars. The recent fire in this park was recorded in 2001 on D. microcarpum (DE-103; DE-105) and A. leiocarpa trees (AN-103; AN-105). The highest number of fire scars was observed on D. abyssinica tree (D1-104) that had five different fire scars (1981, 1985, 1987, 1990 and 1 992) followed by one of A. leiocarpa tree (AN-104) which was scarred at four different years (1988, 1991, 1995 and 1999).

Specifically, D. abyssinica trees that were collected from forest area in CNP allowed us to date fire from 1976 to 1997. During this p eriod, the fire interval varied from one to four years. Most of sampled wood of D. abyssinica had their youngest fire scars before 1993. In 1997, only two samples were scarred by fire. After this year, no fire scars was observed on sampled cross wood of this species, indicating that fire experienced by the sampled tree in forest of Comoé National Park was restricted from 1997. This area was probably protected against fire by technical forest management disposition.

About fire history in forest border, we estimated it from A. leiocarpa samples from 1985 to 2001, the year before collecting samples. It was estimated to be between four and six years until 2001. Thus, we conclude that forest border of CNP was always treated by fire. A. leiocarpa was described in CNP by Klaus (2006) as pioneer species. Thus we suppose that the forest border was cleaned for fire breaks building. This observation confirms the hypothesis that from 1997, forest area of CNP was protecte d against fire. Its effectively was proven since 1997.

Concerning savanna area of this park, the fire past was reconstructed from D. microcarpum species. All sampled trees for this species were originated after 1985 and the earliest fire date in this area was from 1992. From this year to 2001, the fire in terval varied between one and five years. That could be a positive management action either for ensuring grazing for herbivorous mammals or as to facilitate tourism. However, the regular use of fire in CNP savanna area could also be due to the destructive pressure of poachers during game searching.

In upper Aguima Catchment, the oldest tree collected from this second studied area was twelve years old in 2002. The fire interval was from 1995 to 2001 with four different dates (1995, 1998, 1999 and 2001). On any of samples, we identified more than one fire scar. However, like all samples were collected in open mosaic forest, we can reconstruct fire history in this area by dating the fire scar for each sa mple as shown in the figure 9. Thus, fire interval in open mosaic forest of Upper Aguima Catchment was estimated between one to three years. However, the all estimated fire interval depend of the sampled tree that could escape fire event during the supposed -non fire period even if bush fire occurs on year round cycle.

Figure 16: Example of different year's fire scars on wood stem discs

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