EUROPEAN CETACEAN BYCATCH CAMPAIGN |
In recognition of the severe threat posed by unsustainable levels of bycatch impacting on the Baltic harbour porpoise population there was a specific operative calling for action in the Baltic Sea. Parties and Range States in the Baltic Sea were invited to develop, by 2000, a recovery plan for porpoises in the Baltic Sea, one element of which should be to identify human activities which are potential threats to the recovery of this species in the Baltic and that the competent authorities consider appropriate methods to limit such threats. |
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By the time of the 7th ASCOBANS Advisory Committee (AC) meeting (March 2000), the last AC meeting prior to the third meeting of Parties held in July 2000, concern was raised by delegates that Parties had failed to produce a recovery plan. This was despite the fact that separate action plans were submitted to the first ASCOBANS meeting of Parties in 1994 for both the Baltic (CMS/ASCOBANS/1/DOC.5), and Swedish waters (CMS/ASCOBANS/1/INF.2). These were never progressed by ASCOBANS or within Sweden. |
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At the third meeting of Parties in 2000, Parties were still no further forward. Instead what was agreed was a process by which this recovery plan would be developed. Parties agreed that in winter 2000/2001 a workshop aimed at drafting a recovery plan for harbour porpoises in the Baltic Sea should be held. The 8th Advisory Committee meeting of ASCOBANS (April 2-5, 2001) should then consider the matter with a view to producing recommendations for Parties and Range States. |
Consequently four years after the first call for a recovery plan for porpoises in the Baltic Sea, and seven years after being presented with action plans for consideration, ASCOBANS Parties are still a year away from even establishing such a plan. Nor has a recovery plan been developed domestically within Sweden. It is our view that this lack of progress reflects that Sweden does not take its obligations under either ASCOBANS or the Habitats & Species Directive seriously. |
Porpoise bycatch in other Swedish Fisheries |
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The study in the Swedish Kattegat and Skagerrak was carried out in 1996 and 1997 and the report completed by 1998. The study of fisheries in the Swedish Kattegat and Skagerrak revealed bycatch levels in the fisheries studied representing 1.2% and 2.4% of the respective porpoise abundance. The former is considered high enough to merit further investigation for potential remedial action while the latter is considered to be beyond sustainable limits (ASCOBANS 2000c). This is based on one fishery investigated to date (set nets for cod and pollock) for which we understand the effort has decreased in recent years due to declines in the fish stocks. However, no observer based estimates exist for the porpoise bycatch at the current effort levels. Moreover bycatch is known to exist in ten additional fisheries in the same areas (Harwood et al. 1999).but no observer based estimates of bycatch have been undertaken for these fisheries to date. |
Under the section entitled “Implementation of methods to reduce bycatch”, the Swedish entry in its 2000 report to ASCOBANS is recorded as: “No action”. |
Conclusion |
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That it has failed to establish a system to monitor the incidental capture and killing of harbour porpoises; |
That despite available information indicating that bycatch levels in certain fisheries will further reduce populations, Sweden has failed to take any action to actively reduce the levels of bycatch of harbour porpoises known to occur in Swedish fisheries and therefore the requirement to ensure that bycatches do not have a significant negative impact on this species.. |
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