| CRD 01-16
APPENDIX
5
ASSESSMENT
OF CURRENT REPRODUCTIVE DATA
FOR THE WESTERN NORTH ATLANTIC RIGHT WHALE
T.R. Frasier,* M.W. Brown,** S.D. Kraus,*** and B.N.
White*
* Department of Biology, McMaster University, Hamilton,
Ontario, L8S 4K1, Canada
** Center For Coastal Studies, PO Box 1036, Provincetown,
MA 02657, USA and
East Coast Ecosystems, PO Box 36, Freeport, Nova Scotia, B0V 1B0, Canada
*** New England Aquarium, Central Wharf, Boston,
MA 02110, USA
Since 1980, the birth of a total of 221 right whale calves has been documented
in the western North Atlantic. Of these, seven are known to have died and
54 were not photographically identified (Table 1). An analysis
of sighting data shows that 57% of the calves were brought to the Bay of
Fundy by their mothers (Fundy calves, Table 1) and 43% were not taken to
the Bay of Fundy (Non-Fundy calves, Table 1). The mothers of non-Fundy calves
use a yet unknown summering and nursery location (Malik et al, 1999). Since
1987, genetic analyses have been used to assess population structure and
reproduction in the North Atlantic right whale. Eighty-five mother-calf pairs
have been sampled and genetically analyzed (Total genotyped, Table
2). These 85 pairs comprise 52% of the total mother-calf pairs for which
the calf was photo-identified (Table 2). Of the mother-calf pairs that have
been sampled, 60.0% of those seen in the Bay of Fundy have been sampled,
and 32.5% of those not seen in the Bay of Fundy have been sampled (Table
3). Genetic analyses of these samples, using both mitochondrial DNA (mtDNA)
and nuclear DNA, have shown that there is significant population substructuring
between calves that are brought to the Bay of Fundy and calves that are not
brought to the Bay of Fundy in their first year by their mothers (Malik et
al, 1999, Waldick 1999). This substructuring is the result of site fidelity
to a specific summer habitat area on the part of right whale mothers. They
bring their calves either to the Bay of Fundy (Fundy calves) or to an unknown
summer area (Non-Fundy calves). Offspring tend to show the same site fidelity
as their mothers. This pattern of differential habitat use means that some
lineages use the Bay of Fundy in summer and others use an unknown area. Genetic
studies show that there is also a degree of reproductive isolation between
these two groups, suggesting that they could be using different mating areas
and that they are therefore more distinct than previously thought (Waldick
1999).
The population substructuring described above is of increasing interest
when considering reproduction over the past three years, during which
time no mothers from the Fundy subgroup have produced offspring (Table
1, plus data from the calving season of 2000; Phil Hamilton, pers. comm.).
This skew in reproductive performance could indicate that there are recent
and crucial differences in other aspects of the two subgroups, such as
habitat quality and mortality due to anthropogenic factors. Such differences
between subpopulations within the North Atlantic right whale population
should be of primary consideration in all future studies of this population
as conservation efforts are often futile when population structure is
not taken into account (Taylor and Dizon 1999).
References
Malik, S., M.W. Brown, S.D. Kraus, A.R. Knowlton, P.K. Hamilton, and
B.N. White. 1999. Assessment of mitochondrial DNA structuring and nursery
use in the North Atlantic right whale (Eubalaena glacialis). Can.
J. Zool. 77:1-6.
Taylor, B.L. and A.E. Dizon. 1999. First policy then science: why a
management unit based solely on genetic criteria cannot work. Molecular
Ecology 8: S11-S16.
Waldick, R.C. 1999. Assessing the status of the endangered North Atlantic
right whale using genetic and demographic data. Ph.D. thesis, McMaster
University. 172 pp.
Table 1: Numbers of right whale calves photographed
from Fundy and non-Fundy population. $=calves which did not die in the
calving ground. *Calves for which photos are inadequate to permit individual
identification. |
|
Year |
Calves born |
Calves alive$ |
Fundy calves |
Non-Fundy |
Unknown calves* |
|
1980 |
5 |
5 |
3 |
2 |
3 |
|
1981 |
8 |
8 |
7 |
1 |
0 |
|
1982 |
12 |
11 |
6 |
5 |
2 |
|
1983 |
9 |
9 |
4 |
5 |
2 |
|
1984 |
12 |
12 |
11 |
1 |
1 |
|
1985 |
11 |
11 |
5 |
6 |
3 |
|
1986 |
13 |
13 |
6 |
7 |
2 |
|
1987 |
11 |
11 |
7 |
4 |
0 |
|
1988 |
8 |
7 |
4 |
3 |
0 |
|
1989 |
19 |
16 |
11 |
5 |
1 |
|
1990 |
12 |
12 |
9 |
3 |
2 |
|
1991 |
17 |
17 |
9 |
8 |
5 |
|
1992 |
12 |
12 |
4 |
8 |
4 |
|
1993 |
8 |
6 |
4 |
2 |
1 |
|
1994 |
8 |
8 |
3 |
5 |
3 |
|
1995 |
7 |
7 |
3 |
4 |
4 |
|
1996 |
21 |
21 |
14 |
7 |
7 |
|
1997 |
19 |
19 |
11 |
8 |
7 |
|
1998 |
5 |
5 |
0 |
5 |
3 |
|
1999 |
4 |
4 |
0 |
4 |
4 |
| Total |
221 |
214 |
121 |
93 |
54 |
| Table 2: Genotyped mother-calf pairs from Fundy and
non-Fundy populations |
|
Year |
Possible Pairs* |
Total Genotyped |
Fundy |
Non-Fundy |
|
1980 |
2 |
0 |
0 |
0 |
|
1981 |
8 |
3 |
3 |
0 |
|
1982 |
9 |
4 |
2 |
2 |
|
1983 |
7 |
2 |
2 |
0 |
|
1984 |
11 |
6 |
6 |
0 |
|
1985 |
8 |
2 |
1 |
0 |
|
1986 |
11 |
5 |
3 |
2 |
|
1987 |
11 |
6 |
5 |
1 |
|
1988 |
7 |
3 |
3 |
0 |
|
1989 |
15 |
11 |
9 |
2 |
|
1990 |
10 |
4 |
4 |
0 |
|
1991 |
12 |
8 |
8 |
0 |
|
1992 |
8 |
7 |
4 |
3 |
|
1993 |
5 |
3 |
3 |
0 |
|
1994 |
5 |
2 |
1 |
1 |
|
1995 |
3 |
2 |
2 |
0 |
|
1996 |
14 |
9 |
9 |
0 |
|
1997 |
12 |
7 |
7 |
0 |
|
1998 |
2 |
2 |
0 |
2 |
|
1999 |
0 |
0 |
0 |
0 |
|
Total |
160 |
86 |
72 |
13 |
| Table 3: Percentage of genotyped cow-calf pairs from
Fundy and non-Fundy population |
|
Year |
Identified Fundy |
Genotyped Fundy |
%-Fundy |
Identified Non-Fundy |
Genotyped Non-Fundy |
%-Non-Fundy |
|
1980 |
2 |
0 |
N/A |
0 |
0 |
N/A |
|
1981 |
7 |
3 |
42.8571 |
1 |
0 |
N/A |
|
1982 |
6 |
2 |
33.3333 |
3 |
2 |
66.66667 |
|
1983 |
4 |
2 |
50 |
3 |
0 |
N/A |
|
1984 |
11 |
6 |
54.5455 |
0 |
0 |
N/A |
|
1985 |
5 |
1 |
20 |
3 |
0 |
N/A |
|
1986 |
6 |
3 |
50 |
5 |
2 |
40 |
|
1987 |
7 |
5 |
71.4286 |
4 |
1 |
25 |
|
1988 |
4 |
3 |
75 |
3 |
0 |
N/A |
|
1989 |
11 |
9 |
81.8182 |
4 |
2 |
50 |
|
1990 |
9 |
4 |
44.4444 |
1 |
0 |
N/A |
|
1991 |
9 |
8 |
88.8889 |
3 |
0 |
N/A |
|
1992 |
4 |
4 |
100 |
4 |
3 |
75 |
|
1993 |
4 |
3 |
75 |
1 |
0 |
N/A |
|
1994 |
3 |
1 |
33.3333 |
2 |
1 |
50 |
|
1995 |
3 |
2 |
66.6667 |
0 |
0 |
N/A |
|
1996 |
14 |
9 |
64.2857 |
0 |
0 |
N/A |
|
1997 |
11 |
7 |
63.6364 |
1 |
0 |
N/A |
|
1998 |
0 |
0 |
N/A |
2 |
2 |
100 |
|
1999 |
0 |
0 |
N/A |
0 |
0 |
N/A |
| Total |
120 |
72 |
60 |
40 |
13 |
32.5 |
|