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Figure 19: Land capability and economic returns from
land use in Namibia

Figure 26: Options, problems and solutions for managing
elephant in Namibia
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At present no factor is preventing an increase in numbers
of elephants.
Several measures might enable Elephant populations to increase
faster, e.g.
- the addition of more waterpoints (for example, in the
multiple use zone of Babwata);
- the removal of veterinary fences, e.g. removal of the
international boundary fence along the southern boundary
of Babwata and along the eastern boundary of Khaudum and
Nyae Nyae would greatly facilitate east-west linkages in
the regional elephant range;
- less competition from cattle (Schlettwein et al 1991);
But, even with these constraints in place, elephant are increasing
at a rate close to the maximum possible.
A potential threat to elephants is the inception of a wave
of illegal hunting by dissatisfied people.
The benefits which communities are receiving from elephants
on their land are small.The number of elephants hunted as
trophies and problem animals is low and does not come close
to compensating communities or individuals for their losses.
Farmers are not free to defend their livelihoods from elephant
depredations and the current arrangements for control of problem
elephants are too tardy to be effective. O'Connell (1995)
found an extremely hostile attitude towards wildlife amongst
the Caprivi peoples and the inception of conservancy projects
did little to ameliorate this attitude. With all conservancies
being in a fledgling stage, there is a 'wait-and-see' attitude
amongst their members. The recent rapid increase in the numbers
of elephant in the Caprivi may be due to a temporary tolerance
of elephants while conservancies are in their formative stage.
The situation is finely balanced and it would require little
in the way of disincentives for the entire edifice to collapse.
Namibia's short-term problem is to accommodate the current
increase in elephants.
In the long term elephants have a propensity to eat themselves
(and other species) out of house and home no matter how great
the range available to them – a process which culminates in
population crashes. Some would argue that this is 'natural'
and that no management is necessary. Such arguments tend to
put elephant conservation in a vacuum and ignore the alternative
options for accommodating elephants within larger sustainable
development systems.
In the long term population reductions may be necessary.
In the north-west, the management requirement may simply be
to increase the range available to elephants: in north-central
and north-east Namibia not only does the range need to be
increased but, in some areas, the population may need to be
reduced (Figure 26).
Technically, there are no good reasons why more land in Namibia
should not be available to elephants. Brown (2004) and Martin
(2004b) have pointed out that, given land capability in the
arid situation of Namibia,
the highest valued land uses over most of the country are
those based on management of natural resources (Figure
19). Moreover, the full potential is far from being realised
at present due to national and international policy constraints
which place wildlife at a competitive disadvantage with land
use based on exotic species. Were subsidies to be removed
from the domestic livestock industry and were it possible
for elephant to play their full economic rôle in land use
systems, it could reasonably be expected that large additional
areas of land would be converted to wildlife management –
for example, most of the northern Kavango and Owambo provinces
and the Eastern Caprivi. This would remove the short-term
limiting factor of providing additional range for elephant.
There is a corollary to this optimistic vision for the future.
Failure to implement the necessary devolutionary measures
will not simply result in the status quo being maintained.
Since the 1970s, elephant populations have collapsed in an
apparently inexorable process across Africa. Amongst the more
spectacular population crashes have been those in Kenya, Tanzania,
Uganda and Zambia (Martin 1986; AfrESG 1998). The monotonous,
repetitive nature of the phenomenon has caused depression
amongst conservationists – but resulted in few cold-blooded
analyses of the underlying causes. Invariably it has happened
in countries where the State asserts that it owns all wildlife
and attempts to regulate
- the State's "authoritative reach exceeds its implementational
grasp";
- extended bureaucracies are incapable of linking inputs
and outputs; and
- the incentives for individuals lie largely in the enhancement
of their own powers.
Degeneration into State corruption appears inevitably to accompany
centralised governance (Martin 2003a). Parker (2004) documents
the influence of corruption on the ivory trade in Kenya and
the changes which took place in the national wildlife agency
to facilitate this. Namibia may feel it is exempt from the process
but the events which took place during the era of the South
African Defence Force in the late 1970s and early 1980s should
stand as a salutary reminder. There would seem to be only one
antidote to the malaise and that is the creation of powerful,
selfgoverning wildlife constituencies at the local level. |