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4.
Assessment of Proposals
4.3 - Proposal 11.49. Basking shark (Cetorhinus
maximus)
(see Annex 3)
Currently not on the Appendices. Add to
Appendix II pursuant to criteria A and Bi of Annex 2 (Resolution Conf.
9.24) (United Kingdom).
Status: IUCN lists the global
population of C. maximus as Vulnerable (criterion A1: a population
reduction of at least 20% in three generations has been observed,
estimated, inferred or suspected, based on (a) an index of abundance, (d)
actual or potential levels of exploitation; criterion A2: the population
reduction specified in A1 is suspected to continue to be met over the next
three generations).
Trade: C. maximus are
currently in international trade; liver oil and fins being the two main
trade products. Basking shark fins are one of the most valuable sold in
Singapore (Walker 1998). The only directed fishery (operated by Norway)
uses much of its catch for national consumption, extracting squalene from
the liver oil for cosmetics and health supplements (C. maximus
proposal).
Population size and declines:
Commercial fisheries are reported to have resulted in significant long-term
localised declines in many areas. Past declines indicate localised stock
reductions of 50–90% over short periods, followed by a lack of apparent
recovery several decades after exploitation ceased (C. maximus
proposal). In terms of meeting the criteria:
Annex 2a, Criteria A: It
is known, inferred or projected that unless trade in the species is subject
to strict regulation, it will meet at least one of the criteria of Annex 1
in the near future.
There is no evidence indicating that the
species will meet the Criteria for Appendix I in the near future – the
global population size is large, and projected declines are unlikely to be
of sufficient magnitude.
Annex 2, Criteria B: It is
known, inferred or projected that the harvesting of specimens from the wild
for international trade has, or may have, a detrimental impact on the
species by: i) exceeding, over an extended period, the level that can be
continued in perpetuity.
In most cases of local population decline,
there is insufficient information on trends in CPUE to determine the extent
of reduction, and the degree to which they are related to exploitation.
This is further complicated by poorly known migratory movements, a lack of
understanding of stock size and structure, and an inability to account for
what are apparently significant natural fluctuations in local abundance
regardless of exploitation. For example, exceptionally high numbers of C.
maximus were recorded France and south-west England in 1998, but not in
other areas of the UK. They have been reported as both "rare" and
"abundant" off California in different years. Aerial surveys off
California have found them to be more abundant before 1970 than recently,
despite no significant fishing having taken place since 1950 (FAO fact
sheet).
Conclusion: Cetorhinus maximus
may meet the criteria for Appendix II Bi on a local level (European waters
for the Norwegian fleet), but the global population is not significantly
threatened. The current EC quota (~200 sharks PA) may be sufficient for
ensuring current exploitation is not excessive and monitoring associated
with this harvest could be important for quantifying the status of this
local population in the future. The proposal does not justify listing of
the global population on Appendix II. |