The 2016 meeting of the IWC Scientific Committee will be held at the Hotel Golf, Bled, Slovenia from 4th June to 20th June.
A major new development is the IWC's involvement in whalewatching as a sustainable use of cetacean resources.
In 1993, the IWC invited Contracting Governments to undertake a preliminary assessment of the extent, and economic and scientific value, of whalewatching activities.
These reports on the value and potential of whalewatching were consolidated by the Secretariat and considered by a Working Group at the 1994 meeting.
As a result the IWC has reaffirmed its interest in the subject, encouraged some scientific work and adopted a series of objectives and principles for managing whalewatching proposed by the Scientific Committee.
Population table | The IWC's figures for estimated whale populations | |
Comprehensive Assessment | The comprehensive assessment of current whale stocks | |
Status of whales | A brief overview of the ‘status’ of whale populations |
Good conservation and management requires and understanding of the status of populations. A key component of this is, of course, an estimate of present abundance (and ideally trends in abundance) against which possible threats can be evaluated.
Estimating the abundance of animals that spend most of their time below the surface is difficult. The Scientific Committee has developed guidelines on how to best estimate abundance of whales from ships and aeroplanes for use in the RMP. Other methods include a combination of visual and acoustic techniques (e.g. bowhead whales off Alaska) or mark- recapture techniques using the natural marks found on some species that allow individuals to be identified (e.g. humpback whales in the North Atlantic). Because of the considerable scientific uncertainty over the numbers of whales of different species and in different geographical stocks, the International Whaling Commission decided in 1989 that it would be better not to give whale population figures except for those species/stocks which have been assessed in some detail. This does not mean that there are not other published estimates of some species or populations or areas.
The Scientific Committee is undertaking a major compilation and review of abundance estimates that is expected to be completed by mid-2013. Meanwhile, below is a selection of approximate ‘best’ estimates (and their associated approximate 95 % confidence intervals) for some species and areas.
|
Year(s) to which estimate applies |
‘Best’ estimate |
Approximate 95% CI |
---|---|---|---|
Southern Hemisphere |
1985/86-1990/91 |
720,000 |
510,000 - 1,010,000 |
|
1992/93-2003/04 |
515,000 |
360,000 – 730,000 |
North Atlantic |
|
|
|
Northeastern |
1989 |
64,000 |
50,000 - 80,000 |
|
1995 |
112,000 |
95,000 - 130,000 |
|
1996-2000 |
80,000 |
65,000 - 100,000 |
|
2003-2007 |
81,000 |
60,000 - 110,000 |
2008-13 |
90,000 |
60,000 - 130000 |
|
Central |
2005-2007 |
50,000 |
30,000-85,000 |
West Greenland |
2007 |
17,000 |
7,000 – 40,000 |
North Pacific |
|||
North West Pacific and Okhotsk Sea |
1989-90 |
25,000 |
12,800 - 48,600 |
|
2003 |
Ca 22,000+ |
Under review |
Year(s) to which estimate applies |
Approximate point estimate |
Approximate 95% confidence limits |
|
---|---|---|---|
Southern Hemisphere (excluding pygmy blue) |
1997/98
|
2,300
|
1,150 - 4,500
|
The estimated rate of increase is 8.2% (95% confidence interval 3.8-12.5%) per year between 1978/79 and 2003/04
|
Year(s) to which estimate applies |
‘Best’ estimate |
Approximate 95% CI |
---|---|---|---|
North Atlantic |
|
|
|
East Greenland to Faroes |
1987-9 |
15,000 |
11,000 – 20,000 |
|
1995 |
22,000 |
16,000 – 30,000 |
|
2001 |
26,000 |
20,000 – 33,000 |
|
2007 |
22,000 |
16,000 – 30,000 |
West Greenland |
2007 |
4,500 |
1,900 – 10,000 |
|
Year(s) to which estimate applies |
‘Best’ estimate |
Approximate 95% CI |
---|---|---|---|
North Pacific |
|
|
|
Eastern |
1997/98 |
21,000 |
18,000 – 24,000 |
|
2000/01 |
16,500 |
14,000 – 18,000 |
|
2001/02 |
16,000 |
14,000 – 18,000 |
|
2006/07 |
19,000 |
17,000 – 22,000 |
Western |
2007 |
121 |
112 - 130 |
|
Year(s) to which estimate applies |
‘Best’ estimate |
Approximate 95% CI |
---|---|---|---|
North Pacific |
|
|
|
Bering-Chukchi- Beaufort Seas stock |
2001 |
10,500 |
8,000 – 13,000 |
|
2004 |
12,600 |
8,000 – 20,000 |
2011 |
17,000 |
15,700 - 19,000 |
|
North Atlantic |
|||
West Greenland feeding area |
2012 |
1,300 |
900 – 1,600 |
|
Year(s) to which estimate applies |
‘Best’ estimate |
Approximate 95% CI |
---|---|---|---|
Southern Hemisphere |
|||
Partial coverage of Antarctic feeding grounds |
1997/98 |
42,000 |
34,000 – 52,000 |
Eastern South America |
2005 |
6,200 |
4,600 – 8,500 |
|
Rate of increase of around 7% |
||
Western South America |
2003-4 |
2,900 |
2,000 – 4,200 |
Western Australian |
2008 |
29,000 |
24,000 – 40,000 |
|
Rate of increase of around 10% 1999-2008 |
||
Western Africa |
2005 |
9,800 |
7,000 – 12,000 |
|
Rate of increase of around 4-5% |
||
Eastern Africa breeding stock(s) |
2006 |
14,000 |
11,000 – 19,000 |
North Atlantic |
|
|
|
Western North Atlantic |
1992-93 |
11,600 |
10,000 – 13,500 |
West Greenland |
2007 |
2,700 |
1,400 – 5,200 |
|
Rate of increase of around 9% 1984-2007 |
||
North Pacific |
2007 |
22,000 |
19,000 – 23,000 |
Arabian Sea |
2007 |
80 |
60 - 110 |
|
Year(s) to which estimate applies |
‘Best’ estimate |
Approximate 95% CI |
---|---|---|---|
Southern Hemisphere |
2009 |
12,000 |
|
Southwest Atlantic |
2009 |
3,300 |
|
|
Rate of increase around 7% |
||
Southern Africa |
2009 |
3,900 |
|
|
Rate of increase around 7% |
||
Sub-Antarctic New Zealand |
2009 |
2,700 |
|
South central and Western Australia |
2009 |
2,000 |
|
|
Rate of increase around 7% |
||
North Atlantic |
2010 |
490 |
|
|
Year(s) to which estimate applies |
‘Best’ estimate |
Approximate 95% CI |
---|---|---|---|
North Pacific |
|
|
|
Western |
1999-2002 |
21,000 |
11,000 – 38,000 |
|
Year(s) to which estimate applies |
Approximate point estimate |
Approximate 95% confidence limits |
---|---|---|---|
Central & Eastern North Atlantic |
1989 |
780,000 |
440,000 - 1,370,000 |
When, at its 1982 meeting, the IWC agreed to a pause in commercial whaling (or to use popular terminology, a 'moratorium') from 1986, the amendment to the regulations included a clause that 'the Commission will undertake a 'comprehensive assessment' of the effects of this decision on whale stocks and consider modification of this provision and the establishment of other catch limits'.
The term 'Comprehensive Assessment' had not been defined by the Commission and eventually the Scientific Committee defined it to be:
'an in-depth evaluation of the status of all whale stocks in the light of management objectives and procedures... that ... would include the examination of current stock size, recent population trends, carrying capacity and productivity'.
To date the Committee has completed or is still undertaking such in-depth analyses of: