y interest in this topic was initially aroused by two matters that came
under consideration at the tenth Conference of the Parties to CITES, held in
Harare, Zimbabwe in 1997.
CITES is the Convention which governs international trade in endangered
species. For example, no international trade is permitted in species listed in
CITES' Appendix I. With what are such species "endangered"? The
criteria governing CITES listings make clear that "endangered" refers
to "threatened with extinction". Furthermore, lest there be any
doubt about the meaning of "extinction" in this context, this is
clarified by the Red List Categories for threatened species developed by IUCN,
the International Union for Conservation of Nature and Natural Resources, which
defines a taxon as "extinct" when there is no reasonable doubt
"that the last individual has died" (IUCN, 1994).
Currently, all species of baleen whales are listed on CITES' Appendix I.
Proposals were made to the Harare CITES meeting to downlist some populations of
whales, including the Western North Pacific stock of Bryde's whales. In IUCN's
formal recommendations on proposals to that CITES meeting (TRAFFIC, 1997), they
stated that the International Whaling Commission's (or IWC's) Scientific
Committee estimated the mature female component of this Bryde's whale population
to be 51% of its pre-exploitation level. They went on to comment that this
indicated the population to be "borderline with respect to meeting the
biological criteria for inclusion in CITES Appendix I."
There are two important elements of the rationale underlying IUCN's comments
in this case which merit attention. Both are arguably quite consistent with
CITES' present listing criteria. First, the 51% figure quoted was the most
conservative of a number of alternative estimates evaluated by the IWC
Scientific Committee at that time (IWC, 1997). (This is an aspect whose linkage
to the Precautionary Principle will be discussed further below.) And secondly,
the criterion applied for recommending an Appendix I listing for the population,
was a reduction to below 50% of its pre-exploitation level.
At that same CITES meeting, a proposal for the establishment of a Working
Group for Marine Fish Species was made. This eventually failed to gain
acceptance, but it is not that proposal itself that is of pertinence to the
topic of this paper. Rather, it is one of the arguments offered by its
proponents: that some marine fish species, subject to large scale commercial
harvesting, currently qualified for inclusion in CITES Appendices.
It was in linking these two matters – the motivation given for the Marine
Fish Species Working Group and the criterion argued to apply to the Bryde's
whale proposal – that my concerns arose. Because, under such arguments, there
would be few marine fish species currently under commercial harvest which would
NOT be placed on CITES Appendix I. The consequent suspension of all
international trade in such species would have enormous deleterious
socio-economic consequences.
Nor could I see genuine biological justification for such listings. Typically
in fisheries, reduction of a population to somewhere in the range of some 30-60%
of its pre-exploitation level is considered appropriate for optimal utilization
to secure a maximum sustainable yield. Certainly many fish populations have been
reduced below such levels. But that doesn't mean that they cannot continue to
produce sustainable, although not optimal yields, nor that all harvesting has to
cease while management secures their recovery to higher levels capable of
producing larger sustainable yields, nor (most certainly) does it mean that they
are necessarily in any imminent danger of extinction.
Extinction occurs when a population is reduced below what is termed its
"critical depensation" level – the level below which it cannot
sustain itself even in the absence of a harvest. Empirical studies to estimate
what that level might be for marine species harvested commercially, are perhaps
not as advanced as they could be (see Butterworth, 1999, for further discussion
of this matter). But even so, typically such levels hardly seem likely to exceed
some 10%, at most, of pre-exploitation abundance, rather than 50% which relates
more to a desired target for optimal utilization.
This contradiction between reality, and what the current CITES criteria
apparently imply, suggests that these criteria merit closer inspection.