500
sing may alter in all cases the different shades
of grey or colour and become a real source of dif
ficulty .
4 GEOMORPHOLOGY AND WETLAND LANDSCAPES
American authors recognize five major landscapes
for Florida mangroves : overwash, basin, fringe,
riverine, dwarf based on stand morphology, topography
and inundation conditions. This system can be deve
loped adding floristic and soil information, espe
cially salinity. Five samples of airphotos are com
mented along these lines. The largest wetlands occur
around Grand Cui de Sac (G.C.S.). The most striking
geomorphological features are :
- A weak development of hydrography on the eastern
side of G.C.S. and the existence of man-built canals.
Because of moderate rainfall and karst relief of
Grande Terre, silting is low and shore lines are
static.
- On the western side of G.C.S. the large river
Grande Rivière à Goyaves (G.R.G.) brings some silt
and builds a fluctuating (small) delta. Erosion
by currents is visible on the northern side of
Lamentin Bay whereas silt is deflected on the northern
coast of the G.R.G. complex facing the open sea.
This complex is composed of four units : two clay
tables slightly above sea level bearing Avicennia,
a lower Pterocarpus unit and an Acrostichum unit
clearly seen on photos. The mouth of G.R.G. is mainly
Rhizophora.
- Impeded drainage north of Ravine Gachet because
of a low sand dune behind which a basin mangrove
has developed (East of G.C.S.). Southwards down
to Rivière Salée seawater has free access to a fringe
mangrove. Coral reefs underlined by islands (Fajou,
Macou) emphasize the opposition between these two
shorelines and the load of the sea-currents (sand
or mud).
- A more or less buried karstic relief quite visible
on photos is covered with deciduous or semi evergreen
vegetation and suggests that the eastern coast of
G.C.S. is sinking ; further evidence is brought
by soil studies.
- Wind does not generate dune movement (cf. Mexico,
Venezuela) and cyclones are periodically destructive
(1966, 1979).
Pocket mangroves, mainly fringe and riverine
are located along the southern coast of Grande Terre,
SW and NW coasts of Basse Terre. The eastern coast
of Grande Terre (one exception at Le Moule) and
western coast of Basse Terre are practically without
mangroves.
5 NEED FOR EXTRA FIELD OBSERVATIONS
What has been explained under 3 and 4 is only a
framework. Field checks must correct the interpre
tation and ease the extrapolation for mapping. Extra
ecological observations will provide explanations
for the present spatial distribution of vegetation
and its evolution in time.
The interest of transects lies in the continuous
correlation established between the tones of the
photos the corresponding vegetation and environmental
factors. Several transects are self commented by
the legend of figures 2-3-4-5 _ 7.
An ecological interpretation needs at least a
mud auger and a pocket salinometer (additional field
measurements and laboratory analyses if it can be
afforded).
Salinity is the most significant factor to determine
the ecological range of the species. Beyond 8,5%
salt in soil solution any vegetation will die leaving
a saltflat ("étang bois sec"), resulting from the
evaporation of trapped seawater after cyclones during
severe dry seasons.
Figure 1. Grand Cui de Sac Marin (G.C.S.)
Besidei the 4 areas shown, two others are studied:
the mouth of Grande Rivière à Goyaves and Morne
Rouge on its western side.
Tides are \yeak in the Caribbean area and inundation
classes are not useful ; most significant is the
conjunction of the highest tides (0.5 m) and climax
of the rainy season (Imbert, 1985). The accumulation
of organic matter and intensive evaporation in
a well marked dry season generate dwarf Rhizophora
mangrove on saline peats (5,0 to 5,5 % salinity).
Drilling the soil 1 to 2 m deep shows that below
Rhizophora peat Cyperacea peat occur, hence the
evidence of a vegetation chronosequence that can
be refined with C14 and pollen analysis over the
2000 or even 4000 past years.
6 DYNAMICS OF WETLANDS
We are concerned here with recent and present modi
fications by comparing air-photos over the last
20 to 35 years. In this period no drastic changes
happened. Local progression of forest are not uncom
mon. Nevertheless the general tendency is a slow
insidious regression of forested areas. It is rather
difficult to imagine what was the pre-colonization
situation of Pterocarpus and marshlands. Nowadays
the most important factor in the regression is
urbanization and road construction, well seen in
the vicinity of Pointe à Pitre, the main city,
also quite visible in any town near the sea. Next
in importance is agriculture : reclamation through
drainage was active in the past (Abymes, Morne-
à-1'Eau). To day the pressure is constant on the
outer margins of Pterocarpus for dasheen (Colocasia)
crops under the trees without felling. If trees
are cleared and cultivation abandoned later cyperaceae
come first maintained by hunter-fires. If fires
stop Laguncularia or Pterocarpus recolonize. Fire
sweeps are obvious on photos. Cyclones play an
important role : local chablis in Pterocarpus and
Laguncularia, killed Rhizophora induce thickets