Illegal hunting
In examining the effects of different levels of illegal
harvest it is assumed that mortality would affect both sexes
and all ages equally. In practice this is not likely to be
the case if the hunting is primarily for ivory: it may be
true if the hunting is for meat or, for example, if the intent
were to eradicate the elephant population. The exercise effectively
simulates the impact on the population of a harvest which
is spread evenly over the entire population - which could
happen in a sustainable cropping programme.24 The 'doubling
time' is the number of years it would take for the population
to double its numbers and the 'halving time is the number
of years it would take for the population to decline to half
its original size at the given rate of harvest.
| Illegal
harvest % |
0 |
1 |
2 |
3 |
4 |
4 |
4.4 |
4.5 |
5 |
6 |
7 |
8 |
9 |
10 |
| Pop.
growth rate % |
5 |
4 |
3 |
1 |
0.4 |
0 |
0 |
-0 |
-1 |
-2 |
-3 |
-4 |
-5 |
-6 |
| Years |
16 |
21 |
29 |
49 |
193 |
" |
922 |
371 |
98 |
40 |
25 |
18 |
14 |
12 |
|
DOUBLING
TIME (years) |
HALVING
TIME (years) |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Using a fecundity
of 0.25 and a central
mortality of 0.5% the population grows at 4.56% with no
illegal hunting. The population growth rate decreases with
each increment in the illegal hunting offtake and reaches
zero as the illegal offtake approaches the intrinsic growth
rate of the population. At a 10% offtake the population halves
in twelve years.
Illegal hunting has no effect on the setting of sport hunting
quotas because the population age structure does not change
shape from a stable age distribution. All that alters is the
population growth rate. Even when the level of illegal hunting
is unsustainable, a quota of 0.5% can be set for sport hunting.
Martin (2005) shows that 869 trophy males would be taken over
50 years from a population subject to no management offtakes
or illegal hunting: when the illegal harvest is 4% the number
of trophies drops to 266.
This is not particularly relevant to the present Namibian
situation. Illegal killing of elephants is low - less than
0.1% of the total population (MET 2004). However, should the
mood of local communities in the Caprivi change or if people
in neighbouring countries decide to obtain benefits from elephants
which they are not getting at the moment, it could become
highly relevant.
Inexplicably, many CITES Parties seem to think that if elephants
are being killed illegally, this is a sufficient reason to
ban trade in ivory in the country concerned. The opposite
is needed: if illegal hunting is taking place, even greater
is the need to trade in ivory to provide the funds to combat
the challenge.
Sport Hunting
At the outset, it is assumed that sport hunting will be restricted
to male elephants. The implications of hunting female elephants
in the safari industry are discussed after the subject of
male hunting quotas.
The proportion of an elephant population which can be sustainably
hunted to satisfy the safari hunting industry is surprisingly
low. If it is assumed that the minimum tusk weight for an
elephant trophy is about 15kg (per tusk) and that elephant
hunting will not be marketable below this weight, this restricts
hunting to males 30 years of age and older. In a population
of 10,000 elephants which is not hunted, the number of males
of age 30 years and older is slightly over 800 animals or
about 8% of the population. This is not the important statistic,
however. If one imagines these 800 animals as bulls in a paddock
from which it is desired to take an annual offtake, the key
factor is the number of 30 year-olds entering the paddock
in each year. For hunting to be sustainable, this is the number
which cannot be exceeded - and it is about 60 animals per
year in a population of 10,000. However, if quotas were set
as high as this, after a short while the only animals in the
paddock would be the annual influx of 30 year old males and
they would all be killed in the year in which they entered
the paddock.
|

Figure 4 Relationship between age and tusk size adapted
from Pilgrim & Western (1986)

Figure 21: Effects of hunting quotas on an elephant
population

Analysis of effects of hunting female elephant
|
The maximum sustainable offtake of male hunting trophies
from an elephant population is about one-half a percent of
the total population. At this level, there will always be
some males in the population surviving to 40 years of age.
If it is desired to have a few males in the population reaching
50 years old (at which age it is assumed they will die naturally
anyway), quotas have to be less than 0.3% of the total population.
To some extent, the hunter is competing with Old Father Time
to get a trophy before the animal expires from natural senescence.
Martin (2005) analysed the effects of increasing levels of
hunting quotas on the age structure of an elephant population
(Figure 21). Martin (2005) built a slight selectivity for
animals with larger tusks into the model. The maximum typical
trophy tusk weight declines from about 30kg/tusk in the unhunted
population to about 21kg/tusk when the quota is set at 0.5%.
The hunting causes the stable age structure of the population
to become slightly skewed.in favour of females. For a given
size of population (in this case 10,000 animals), the number
of males in the 29 year-old age class actually increases from
the number in the unhunted population but this is purely an
artefact based on the redistribution of the animals in all
the age classes to fit the new population profile. The total
number of males in a population of 10,000 animals decreases
from 4,994 in the no-hunting situation to 4,556 when it is
attempted to extract a quota of 0.8% (80 animals) from the
population.
Safari operators are able to market the sport hunting of
elephant females and will put pressure on the authorities
to grant a quota for this purpose. The arguments against hunting
females are several:
- The killing of an adult female in a cow herd is socially
disruptive.
- As with males, the size of female tusks increases with
age (Figure
4) making it likely that the matriarchs of herds will
be preferentially selected. The loss of the accumulated
knowledge of such older members of the population could
affect elephant survival - particularly in arid environments.
- Even where very modest quotas have been set for hunting
cow elephant, within a few years of the inception of hunting
most of the cows with large tusks will have been eliminated
from the population.30 Since the genes for large male
trophy tusks are carried by both females and males in
a population, it can be expected that this selective practice
will eventually lower the quality of male trophy hunting.
- In a long tradition of sport hunting ethics, the killing
of females is generally eschewed;
- Elephants, rightly or wrongly, have attained the status
of 'totem' animals and any killing of elephants upsets
a large public. Sport hunting of male elephants is bad
enough: many times more so is the notion of killing females
- who will almost certainly be mothering offspring. This
becomes a political issue through which entire elephant
management programmes may be derailed simply because of
the emotions aroused
Martin (2005) analysed the changes in population dynamics which result
from hunting female elephants. There are some unexpected
outcomes which, over a long enough time period and ignoring
the arguments against hunting females, could actually allow
greater quotas of males. However, the practice is not recommended:
more factors enter the decision than the simple consideration
of age structures and population growth rates. |