THE EXTENT OF THE LOUISIANA RED SWAMP CRAYFISH
(Procambarus clarkii) INVASION AND ITS EFFECT
ON THE AFRICAN CLAWLESS OTTER (Aonyx
capensis) THROUGHOUT ITS RANGE IN KENYA

This project is concerned
with the distribution, status and conservation of the African clawless otter
(Aonyx capensis) and will also examine the affect of the introduction of the
Louisiana red swamp crayfish (Procambarus clarkii) and other exotic
species, such as the brown trout (Onchorhynchus mykiss). It will also
investigate the possible existence of the
Congo clawless otter (Aonyx congicus)
in Western Kenya.
It has
already
been
established that the spread of the crayfish has negatively affected the African
clawless otter in riverine habitats.
Over
extraction of water in the dry season exposes the otters’ niche to other
predators, i.e. crayfish are being eaten by monitor lizards, herons, genets and
baboons. Crayfish have therefore had a negative effect on otters by exposing
them to competition that is absent in habitats where they live on
crabs.
In August
2004 evidence of crayfish invasion was found in water below 14oC,
which was previously thought to be the threshold below which crayfish could not
survive. This indicates that the geographical spread of crayfish is beyond what
was previously thought, and new habitats are being invaded as they adapt to
colder water. The
African clawless otter is highly sensitive to fluctuations in the abundance and
availability of crustacean prey.
In addition, the exact
identity of the otter species in western Kenya is uncertain as this forms part
of the Congo rainforest and it is indeed possible that the Congo clawless otter
(Aonyx congicus) may be present.
This project is especially
important to conservation outside protected areas because the nature of otters
demands that they occupy linear habitats (rivers) around which human activities
are concentrated because of our need for water. It will also highlight the
extent of otter habitats in Kenya and provide more accurate information for
targeting conservation and research efforts.
Geographic
Location:
Rift Valley, central, and northeastern Provinces, Kenya
Project
Objectives
1.
To
determine the geographical extent to which the
Louisiana red swamp
crayfish (Procambarus clarkii) and other exotic fauna have invaded
freshwater ecosystems and affected clawless otter populations in Kenya.
2.
To
determine the species of clawless otters present in Kenya and make a case for
their protection and prudent management of aquatic ecosystems in Kenya, and
other parts of Africa.
This study will
investigate the effects of invasions of crayfish on otter populations and
recommend ways in which these can be minimized, including stiffer regulations on
the activities of sport fishermen, who are behind most of these introductions.
The project will also
incorporate the exploration of unknown areas of otter range. Foremost among
these is the Lorian Swamp in eastern Kenya. This is where the Ewaso Ng’iro river
ends, and was identified as a priority area by the Africa meeting at the 9th
International Otter Colloquium. It will also investigate two wetland areas in
western Kenya to verify whether they are inhabited by A. capensis or the
Congo clawless otter A. congicus. These are the Saiwa Swamp and the
Kingwal Swamp. These are both fragments of the eastern arc of the Congo
rainforest. This is further confirmed by the presence of two Congo basin
species, the sitatunga antelope (Tragelaphus spekei) and De Brazza’s
monkey (Cercopithecus neglectus). The Saiwa swamp is a protected area,
and otters have been reported to exist there by the Kenya Wildlife Service, but
they are unable to confirm the species. Information is highly deficient on the
range of A. congicus, and according to Kingdon (1997) this does not
extend beyond the Albertine rift in western Uganda.
Methods
Otter prey species will be
sampled using funnel-mouth traps already used in a previous study at Ewaso
Ng’iro. These are made using ¾ inch size wire mesh reinforced with binding
wire. They are weighted with stones, placed on the bottom of the river, baited
with meat and secured to the riverbank. Water in swamp sites (< 50cm deep) will
be sampled using scoop nets every 0.5 km in a transect along the longer aspect
of the swamp. This will be interspersed with trap sampling wherever it is deep
enough. Traps will be emptied, moved and rebaited every 24 hours.
The aquatic fauna caught
in the traps will be counted, measured and weighed. This will be compared to the
proportion found in otter faeces collected in the same area. The composition,
abundance, and frequency of the faecal samples in the study area will be an
additional indicator of fluctuations in the distribution of the otters and their
prey.
Sampling sites will be
assessed for vegetation, substrate composition, water depth and simple chemical
composition in order to examine the possible effects of abiotic factors on otter
prey distribution.
Otters will be
live-trapped in Tomahawk, single-door, rigid live traps baited with fish (Wilson
et al. 1996), weighed, measured, marked and released. Trapped animals
will be anaesthetized using etorphine hydrochloride by means of a pole syringe
and the clinical effects will be reversed using the specific antagonist
diprenorphine. The anaesthetized animal will be marked and released: two marks
will be made on each animal, one on the back of the head and one at the base of
the tail. These are the most visible sites when an otter is running or swimming
away from the observer. The two spots are washed first with ethyl acetate to
remove the natural oils from the fur, and then the marks will be made using
‘ABRO’ brand automotive spray paint. This mark will last at least six months.
This method is preferable to plastic rings and ear tags, because the otters
could easily remove these, and the plastic rings could get caught in riverbank
vegetation.
The three motion sensor
cameras will be moved from holt to holt in order to confirm and extend our
estimates of otter home range sizes obtained from observation and trapping.
More emphasis will be
placed on spraint collection and camera trap photography as indicators than
trapping and marking of otters. This is because repeated trapping at latrine
sites could cause the otters to abandon them, thus depriving the study of a
valuable data source.
Sightings of otters and
locations of spraints will be recorded using a Global Positioning System (GPS).
Spraints will be collected and returned to the laboratory where they will be
dried, sorted and their contents identified. Using antennule base size, the size
distribution of prey will be compared to the size distribution obtained from
trapping, to see if otters selectively take different sizes (ages) of prey. A
mathematical relationship between the antennule base size and overall weight of
live caught crayfish was formulated in a previous study and this can also be
used to deduce the mass of crayfish being taken by otters at the various field
sites.
Project Outputs:
1.
Scientific papers
and a report
indicating the
extent of the threat to otters from the invasion of Louisiana crayfish and other
exotic fauna.
2.
Conservation
recommendations –
Recommendations
will be made for ways to minimize the effects of introductions of crayfish and
other exotic species. Most of these introductions are by sport fishermen and it
will be necessary to impose stiffer regulations on their activities and to
ensure that these are enforced.
3.
Benefits to
indigenous people
- The Kingwal
swamp is on community-owned land and the recent (2002) discovery of a population
of sitatunga antelope in the area has raised tourism interest in the area.
Already, local youth are forming groups to initiate projects like swamp walkways
and market it as an ecotourism destination. It also has a high density and
diversity of wetland birds. The confirmed presence of otters there would raise
the interest level of both tourists and the Kenya Wildlife Service and help the
local people gain from tourism enterprises.
4.
Public awareness
– Part of the project will include giving talks to school children in schools
around the study areas so that local people will learn to appreciate the
importance of otters and wildlife in their own area.
5.
Education/Training
-
Students in the
University of Eastern Africa, Baraton Biological Sciences Department will also
be trained to do aquatic biology studies under this project. This university
borders the Kingwal swamp.
Budget
(please include a detailed budget for the entire project):