ArticlePDF Available

Inshore Occurrence of Southern Right Whales (Eubalaena australis) at Subantarctic Marion Island

Authors:

Abstract and Figures

Opportunistic shore-based sightings of southern right whales Eubalaena australis for Marion Island (46°54′S, 37°45′E) were documented at five different times between 1974 and 2009. Whales were sighted between May and September and exclusively on the eastern lee side of the Island. Notwithstanding some observer biases over this time frame, the species appears to be an infrequent visitor to the inshore marine environment of Marion Island.
Content may be subject to copyright.
Inshore occurrence of southern right
whales (Eubalaena australis) at Subantarctic
Marion Island
M. Postma*, M. Wege, M.N. Bester, D.S. van der Merwe & P.J.N. de Bruyn
Mammal Research Institute, Department of Zoology and Entomology, University of Pretoria,
Private Bag X20, Hatfield, 0028 South Africa
Received 10 January 2011. Accepted 8 March 2011
Opportunistic shore-based sightings of southern right
whales Eubalaena australis for Marion Island
(46°54S, 37°45E) were documented at five different
times between 1974 and 2009. Whales were sighted
between May and September and exclusively on the
eastern lee side of the Island. Notwithstanding
some observer biases over this time frame, the species
appears to be an infrequent visitor to the inshore
marine environment of Marion Island.
Key words:Eubalaena australis, Marion Island, shore-
based sightings; Southern right whale, vagrants.
Owing to their thick blubber, southern right
whales are reluctant to venture into the tropics,
and are usually found between 20° and 64° south
(Fig. 1) (Best 2007). The fact that they float when
dead, have a superior oil and whalebone yield,
fidelity to congregate near calving grounds and
their lack of speed must all have contributed to
their exploitation by commercial whaling (Best
2007). Although protected in 1935, illegal whaling
endureduntil1971(Tormosovetal.1998).Between
1971 and 1998 the calving population off the coast
of South Africa increased with 7.1% per year,
similar to rates of increase recorded for populations
offthe coast of Argentina and Australia(Best2007).
In winter months southern right whales migrate
to more temperate coastal waters off the southern
continents, where females give birth and nurse
their newborn in these sheltered areas (Best 2007).
At other times of the year whales move south from
the calving grounds to the foraging grounds where
temperatures are cooler and overall biological
productivity is higher (Perrin et al. 2002). In the
south Indian sector of the Southern Ocean, right
whales are mainly seen between 30°S and 40°S
from October to December, between 40°S and 50°S
around the Crozet Islands (CI) mainly from Febru-
ary to March, and in the area between 50°S and
60° S from December to April (Best 2007). Here
we report on five photographically confirmed
inshore sightings of the species at Marion Island
(46°54’S, 37°45’E) over a period of 35 years.
The Prince Edward Archipelago consists of
two small islands, Marion Island (MI) and Prince
Edward Island which are located in the southern
Indian Ocean (Pakhomov & Froneman 1999).
Oceanographically, MI is situated directly in the
path of the easterly-flowing Antarctic Circumpo-
lar Current (ACC), between the Subantarctic Front
(SAF) and Antarctic Polar Front (APF) (Fig. 2)
(Lutjeharms 1985). Currently, the nearest southern
right whale calving grounds to MI are ~1950 km
distant,offtheWesternCapeProvince,SouthAfrica.
Sightings of southern right whales at MI were
primarily recorded by elephant seal researchers
during regular visits (every 7–10 days) on foot to
all the beaches on the northeastern, eastern and
southern side of the island (Fig. 3). Round island
resightswereconductedonce a month. The research
effort which is associated with the southern
elephant seal (Mirounga leonina) mark-resighting
programme has been repeated whole year round
since commencement in 1983 (see de Bruyn et al.
2008 for details). As part of this highly structured
pinniped monitoring programme, seal research-
ers were also required to record opportunistic
sightings of killer whales (Orcinus orca). Additionally,
dedicated land-based killer whale observation
sessions were performed year-round since 2008,
during which trained observers remained at set
observation points (Fig. 3) and visually searched
for killer whales for pre-determined (3-hour or
10-hour) lengths of time (Reisinger et al. 2011a).
Following annexation of MI in 1947/1948 by
SouthAfrica(Cooper&Headland1991),theearliest
reported sightings of southern right whales are
those of an adult individual of unknown sex seen
in September 1974 (Condy & Burger 1975). The
animal was noted over a period of several days
while swimming in circles approximately five
metres off the eastern coast about 1 km north of the
*Author for correspondence.
E-mail: mpostma@zoology.up.ac.za
African Zoology 46(1): 188–193 (April 2011)
meteorological station (Fig. 3). Recent examination
of photographs taken over that period confirms
that two different individuals were involved (P.
Best, pers. comm. 2010). During August 2006 an
adult of unknown sex was sighted and photo-
graphed in Storm Petrel Bay on the north coast of
the Island (Fig. 3). This animal meandered in large
circlesandrandompatternswithinthisonebayfor
Short communications 189
Fig.1.Distr ibution map for southern right whales. (Reprinted with permission from Cambridge University Press, taken
from Best, 2007.)
Fig. 2. The position of Prince Edward Islands in relation to South Africa and the CI.Major frontal systems including the
Subtropical Convergence (STC), Subantarctic Front (SAF) and Antarctic Polar Front (APF) are shown. (Reprinted
with permission from Pakhomov & Froneman 1999.)
at least an hour from initial observation. It ap-
peared to be feeding, as the animal’s mouth could
be seen to open near the surface on several occa-
sions. A juvenile animal (8–10 m) of unknown sex
was sighted in August 2008 in poor visibility (due
to snow squalls) at Ship’s Cove on the northeast-
ern coast (Fig. 3). The animal was being harassed
by three killer whales. The observed attack contin-
190 African Zoology Vol. 46, No. 1, April 2011
Fig. 3. Map of Marion Island, Southern Indian Ocean, showing the locations (Mixed Pickle Cove, Cape Davis, Goney
Beach, Pinnacles Beach, Rockhopper Bay, Kildalkey Bay and Watertunnel Beach) where dedicated killer whale
observations were made. Offshore dots indicate southern right whale sightings. (Adapted from Reisinger
et al.
2011a.). Arrows indicate elephant seal researchers’search area every 7–10 days (since 1983). Offshore dots indicate
southern right whale sightings.
Fig. 4. Photograph of a juvenile southern right whale sighted in 2009 immediately north of the meteorological station
at Marion Island.
ued for 20 min, with killer whales circling the
whale within a distance of 10 m after which they
moved off. For the next 2 hours the whale re-
mained in the cove swimming in circles showing
signs of fatigue with irregular breathing, although
this subsided as time passed. The next morning
the whale was nowhere to be seen. Most recently
(in May 2009) a juvenile of the species was re-
corded in approximately the same location as the
sightings in 1974. From photographs and the size
of the head it could be classified as a very young
animal (Fig. 4) (I. Peters, pers. comm. 2010). The
latter was sighted alone; this could be as a result of
the decreased visibility due to heavy mist on that
particular day or the absence of other individuals.
Interestingly, all animals appeared to behave simi-
larly by swimming in circles or random meanders
between about 5 m and 50 m off the coast.
The low sighting frequency of southern right
whales around the eastern and northern coasts of
MI is unlikely to be markedly biased by observer
presence given that an almost uninterrupted field
presence of primarily pinniped biologists com-
menced in 1973 (Condy 1978; de Bruyn et al. 2008).
These field workers routinely documented the
presence of any unusual or rarely seen marine
mammal species (e.g. Bester et al. 2006; de Bruyn
et al. 2007; Reisinger et al. 2009) and additionally
paid particular attention to the inshore waters for
opportunistic killer whale (Orcinus orca) sightings
(e.g. Keith et al. 2001; Tosh et al. 2008). Transients
such as leopard seals (Hydrurga leptonyx) and
humpback whales (Megaptera novaeangliae) are
occasionally sighted when they visit the inshore
area at MI (Bester et al. 2006; Ryan & Bester 2008).
Leopard seals may be benefiting from locally
abundant food resources such as penguins (Bester
etal.2006)andhumpbackwhalesmayberestingin
the calm waters. This poses but two hypotheses to
the question of why right whales visit MI:
1) Some individuals, from the pelagic concentra-
tion of southern right whales around the CI (Best
2007), are possibly swimming diagonally across
the ACC (Fig. 2) to their calving grounds off the
coast of southern Africa, on their way stopping at
MI. MI’s coastline consists mainly of cliffs on the
western side with sheltered pebble beaches on
the eastern side (Condy 1978). Right whales were
recorded only on the eastern side of MI; this could
imply that whales rest in the calmer leeward side,
although observer effort on the western side of
MI, albeit relatively constant, is lower than on the
eastern side. Sightings were in May 2009, August
2006, 2008 and September 1974 at the beginning
and at the end of winter, respectively. This timing
suggests that these animals are en route to more
temperate grounds in low latitudes at the beginning
of the austral winter and from these grounds to
higher latitudes once winter has passed. It is there-
fore tempting to speculate that MI may only be an
occasional en route stopover on an annual migra-
tion to the South African coastline (present study),
although no links between the latter and the for-
aging area around the CI have been demonstrated
(Best 2007). MI is also not in a direct line between
the known foraging area (at CI) and the east coast
of southern Africa (Fig. 1), a possible destination
(Best 2007).
2) On the other hand, the waters around MI are
frequently patrolled by killer whales (Orcinus
orca), particularly the inshore areas (Reisinger et al.
2011a). Elsewhere killer whales have been observed
attacking right whales. Such encounters are rarely
sighted, but could be fatal for young or unaccom-
panied animals, as southern right whales usually
group together for protection against killer whales
(Best et al. 2010). Killer whale sightings occur
throughout the year but peak between Septem-
ber–December and April–May (Reisinger et al.
2011a). The September to December peak coincides
with breeding of southern elephant seals (Mirounga
leonina) and penguin species (Condy et al. 1978;
Reisinger et al. 2011a, b). This potential threat to
right whales by killer whales may explain why few
sightings of right whales have been realized,
despite intensive observer presence for the past
four decades.
The APF and Subtropical Convergence are con-
sidered as popular right whale feeding grounds;
more specifically the area around CI at 45°S and
Kerguelen Islands (‘Desolation’) at 49°S (Town-
send1935).Rightwhalesmustseekoutandexploit
extremely dense patches of prey in order to feed
efficiently (Kenney et al. 1986) where they con-
sume copepods (71.4%), euphausiids (24.3%) and
crustaceans (4.3%) (Tormosov et al. 1997; Mate et al.
2010). MI lies west of these usual foraging regions
(Fig. 5) and as such may be oceanographically
unfavourable as a feeding ground. According to
ship logbooks from 1785 to 1913 no sightings of
southern right whales were made in the vicinity of
the Prince Edward Islands (Townsend 1935)
(Fig. 5). These five records between 1974 and 2009
are the only reported sightings of the species
inshore at MI. Sightings of southern right whales
at MI are infrequent and the species can be classi-
Short communications 191
192 African Zoology Vol. 46, No. 1, April 2011
fied as a rare vagrant at the Island. MI’s position in
the Southern Ocean potentially makes it a sheltered
resting stop for a few individuals en route from the
known Crozet Islands feeding grounds (February
and March) to the winter calving grounds in
southern Africa. Alternatively, passing individuals
may be exploiting unpredictable food patches
opportunistically.
We thank the South African Department of Environ-
mental Affairs for providing logistical support within the
South African National Antarctic Programme and the
Department of Science and Technology (administered
through the National Research Foundation) for funding
the marine mammal monitoring programme at Marion
Island. We are also extremely grateful to the field assis-
tants who recorded sightings when we were not in the
field.
REFERENCES
BEST, P.B. 2007. Whales and Dolphins of the Southern African
Subregion. Cambridge University Press, Cambridge.
BEST, P.B., MEYER, M.A., LOCKYER, C. 2010. Killer
whales in South African waters – a review of their bi-
ology.African Journal of Marine Science32(2):171–186.
BESTER, M.N., HOFMEYR, G.J.G., KIRKMAN, S.P.,
CHAUKE, L.F., DE BRUYN, P.J.N., FERREIRA, S.M.,
MAKHADO, A.B., MASWIME, T.A.M., MCINTYRE,
T., MULAUDZI, T.W., MUNYAI, F.M., PISTORIUS,
P.A., RADZILANI, P.M., RAMUNASI, A.J.,
TSHITHABANE, N.H., WILKINSON, I.S. 2006. The
leopard seal at Marion Island, vagrant or seasonal
transient? South African Journal of Wildlife Research
36(2): 195–198.
CONDY, P.R., BURGER, A. 1975. A southern right whale
at Marion Island. South African Journal of Science 71:
349–349.
CONDY, P.R. 1978. Distribution and abundance of
southern elephant seals Mirounga leonina on the
Prince Edward Islands. South African Journal of
Antarctic Research 8: 42–48 .
CONDY, P.R., VAN AARDE, R.J., BESTER, M.N. 1978.
Seasonal occurrence and behaviour of killer whales,
Orcinus orca at Marion Island. Journal of Zoology,
London 184: 449–469.
COOPER, J., HEADLAND, R.K. 1991. A history of South
African involvement in Antarctica and the Prince
Edward Islands. South African Journal of Antarctic
Research 21: 77–91.
DE BRUYN, P.J.N., PISTORIUS, P.A., TOSH, C.A.,
BESTER, M.N. (2007) Leucistic Antarctic fur seal
Arctocephalus gazella at Marion Island. Polar Biology
30(10): 1355–1358
DE BRUYN, P.J.N., TOSH, C.A., OOSTHUIZEN, W.C.,
PHALANNDWA, M.V., BESTER, M.N. 2008. Tempo-
Fig. 5. Distribution of northern and southern right whales based on logbook records from 1785 to 1913 with arrow
indicating Prince Edward Islands. (Adapted from Townsend 1935.)
rary marking of unweaned southern elephant seal
(Mirounga leonina L.) pups. South African Journal of
Wildlife Research 38(2): 133–137.
KEITH, M., BESTER, M.N., BARLETT, P.A., BAKER, D.
2001. Killer whales (Orcinus orca) at Marion Island,
Southern Ocean. African Zoology 36: 163–175.
KENNEY, R.D., HYMAN, M.A.M., OWEN, R.E., SCOTT,
G.P., WINN, H.E. 1986. Estimation of prey densities
required by western North Atlantic right whales.
Marine Mammal Science 2(1): 1–13.
LUTJEHARMS, J.R.E. 1985. Location of frontal systems
between Africa and Antarctica: some preliminary
results. Deep-Sea Research 32:1499–1509.
MATE, B.R., BEST, P.B., LARGERQUIST, B.A., WINSOR,
M.H. 2010. Coastal, offshore and migratory move-
ment of South African right whales revealed by
satellite telemetry. Marine Mammal Science DOI:
10.1111/j.1748–7692.2010.00412.x
PAKHOMOV, E.A., FRONEMAN, P.W. 1999. The Prince
Edward Islands pelagic ecosystem, south Indian
Ocean: a review of achievements, 1976–1990. Journal
of Marine Systems 18: 355–367.
PERRIN, W.F., WURSIG, B., THEWISSEN, J.G.M. 2002.
Encyclopedia of Marine Mammals. Academic Press, San
Diego.
REISINGER, R.R., DE BRUYN, P.J.N., BESTER, M.N.
2011b. Predatory impact of killer whales on pinniped
and penguin populations at the Subantarctic Prince
Edward Islands: fact and fiction. Journal of Zoology,
London (in press).
REISINGER, R.R., DE BRUYN, P.J.N., TOSH, C.A.,
OOSTHUIZEN, W.C., MUFANADZO, N.T., BESTER,
M.N. 2011a. Prey and seasonal abundance of killer
whales at Subantarctic Marion Island. African Journal
of Marine Science (in press).
REISINGER, R.R., MUFANADZO, N.T., DE BRUYN,
P.J.N., BESTER, M.N. 2009. Leucistic southern ele-
phant seal at Marion Island. Polar Biology 32(3):
509–511.
RYAN, P.G. & BESTER, M.N. 2008. Pelagic predators. In:
The Prince Edward Islands: Land–sea Interactions in a
Changing Ecosystem, (eds) S.L. Chown & P.W.
Froneman, 1st edn, pp. 121–164. Stellenbosch Uni-
versity Press, Stellenbosch.
TORMOSOV D.D., MIKHALIEV, Y.A., BEST, P.B.,
ZEMSKY, V.A., SEKIGUCHI, K., BROWNELL, R.L.
1998. Soviet catches of southern right whales Eubalaena
australis, 1951–1971. Biological data and conservation
implications. Biological Conservation 86: 185– 197.
TOSH, C.A., DE BRUYN, P.J.N., BESTER, M.N. 2008.
Preliminary analysis of the social structure of killer
whales, Orcinus orca, at subantarctic Marion Island.
Marine Mammal Science 24(4): 929–940.
TOWNSEND, C.H. 1935. The distribution of certain
whales as shown by logbook records of American
whaleships. Zoologica, NY 19(1): 1–50.
Responsible Editor: J.H. van Wyk
Short communications 193
... ) and again with a calf in October 1999. In May 2009 a juvenile right whale was observed and photographed from the shore alone at Marion Island, at the western edge of Area IIIE (Postma et al., 2011). It was later matched in the boat-based catalogue with a calf seen in South African waters in 2007, so assuming it was born in the normal calving season around mid-August (Best, 1994), would have been about 21 months old when seen in the SubAntarctic. ...
... The fourth was an exception both seasonally and spatially, being the only location of a South African individual in the Southern Ocean east of 20 o E and occurring in May. Given the animal's age, it is possible that this represents a wider, postweaning dispersal of juveniles, and indeed the vicinity of Marion Island was not a historically recognized concentration area for the species, either in open-boat or (illegal) modern whaling (Postma et al., 2011). ...
Article
Five right whales satellite-tagged on the South African coast in September 2001 subsequently ranged over the southeast Atlantic between 37 and 60 o S and from 13 o W to 16 o E (or Area IIE Area IIIW). Four matches were also made between whales photographed on the South African coast and individuals in the Southern Ocean: three of these were encountered in the same general area as that visited by the satellite-tagged animals in the southeast Atlantic, but the fourth (a second-year male) was photographed at Marion Island in the southwest Indian Ocean (Area IIIE). No matches were found between the South African coast and 37 individuals photographed in Area IV of the Antarctic.
... Additionally Southern Right Whales have been seen sporadically at sub-Antarctic Marion Island, a South African territory (Postma et al. 2011), which is part of the Prince Edward Islands Marine Protected Area (MPA), and movement has been recorded between South Africa and Marion Island (Best & Peters 2011). ...
... The dedicated seal research is elaborated upon in the section 'Pinniped population biology and ecology' below. Throughout, personnel were also alert to chance sightings of other cetaceans (Condy and Burger 1975, Condy et al. 1978, Ryan and Bester 2008, Postma et al. 2011), seal vagrants or transients (Kerley 1983a, Bester et al. 2006) and other unusual and/or interesting phenomena (Bester and Kerley 1983, de Bruyn et al. 2007, Bester et al. 2008, de Bruyn et al. 2008a, 2008b, Reisinger et al. 2009, 2010a, 2010b, de Bruyn et al. 2010, Wege et al. 2011). ...
Article
Full-text available
The Marine Mammal Programme (MMP) conducts research on pinnipeds and killer whales Orcinus orca at Marion Island, Prince Edward Islands, under the auspices of the Mammal Research Institute, Department of Zoology and Entomology, University of Pretoria. The history of the MMP, which has benefited from collaboration with leading national and international researchers, is described from its start through to current research. The setting up of long-term studies such as the mark-resighting of southern elephant seals Mirounga leonina commenced in 1983. The elephant seal population declined by 87% between an initial census in 1951 and 2004. This was followed by a stabilisation period and a current increase. The recovery, and subsequent increase of sympatric populations of Subantarctic fur seals Arctocephalus tropicalis and Antarctic fur seals A. gazella (following cessation of commercial sealing), are documented. Insights into many aspects of elephant seal and fur seal biology, including life history, demography, diet, growth, foraging and ranging behaviour are described. Ancillary work on morphology, genetics, anthropogenic influences and rare events are mentioned, as well as the extent of current research that addresses population dynamics in an ecosystem context. Opportunistic photographic identification of killer whales and recent dedicated observations at Marion Island are used to determine population size, seasonal abundance and sociality of this population, and to further understanding of its potential impact on resident pinniped populations.
Article
Full-text available
Killer whales (Orcinus orca) were studied using data obtained on an opportunistic basis between 1973 and 1996 at Marion Island (46°54′S, 37°45′E) in the Southern Indian Ocean. A clear seasonal pattern of occurrence with the main peak between October and December was evident. Most killer whales were observed within 5 m of the shore and adult males typically occurred further offshore than adult females. The distribution of killer whales around the island was not uniform and more than 80 % of all sightings occurred close to the base station. This was probably due to a concentration of search effort in the vicinity of the base station and to an uneven distribution of prey species. Killer whales occurred in groups with an average of 3.56 individuals and a maximum of 28 animals per group; females predominated throughout the study. Dawn-to-dusk surveys of killer whales in the near-shore waters during 1986, 1989 and 1990 showed small, statistically non-significant peaks of sightings in the early morning and late afternoon. Twenty-six killer whales were individually identified from photographs, eleven of which recurred at Marion Island. Modified photogrammetric methods may improve current photogrammetric analysis of cetacean dorsal fins.
Article
Full-text available
The distribution, seasonality and schooling behaviour of killer whales Orcinus orca in South African waters have been investigated from 785 records compiled between 1963 and 2009, and their size, morphometrics, growth, reproduction, food and feeding behaviour described from the examination of 54 individuals, 36 of which were landed at the Durban whaling station between 1971 and 1975. Qualitatively, the species appears to be more frequently encountered offshore, where it forms small schools of generally less than six animals. Seasonality of occurrence is not marked, although circumstantial evidence indicates that some individuals migrate from higher latitudes. Males reach 8.81 m and females 7.9 m, with 16.2% of males exceeding the size of the largest female. Stomach content and observational data suggest that the species can be characterised locally as an opportunistic predator of megavertebrates, rather than as the fish-feeding ecotype previously described. A stranded adult male with extreme tooth wear that was 1.5–2 m shorter than other males of equivalent age may be representative of a separate ‘offshore’ ecotype. Apparent differences between features of the popu lation's life history and those of resident killer whales in the north-eastern Pacific might be attributed to either uncertainties in age determination using dentinal growth layer groups or sampling bias. The basis for the suggestion that killer whales in South African waters should be reclassified as Vulnerable (rather than Data Deficient) is challenged.
Article
Full-text available
Between 1951/1952 and 1970/1971, a total of at least 3368 southern right whales Eubalaena australis were taken by Soviet whaling expeditions in the Southern Hemisphere, despite the species being internationally protected since 1935. These catches and the associated biological data (presented here for the first time) represent a unique source of information on the distribution, movements, size composition, reproduction and feeding of southern right whales during summer months. Revelation of these previously unreported catches also has implications for the assessment of the current status of right whale stocks. Incorporation of the Soviet catches into population assessments generally leads to higher estimates of the size of the population at protection, but the relative increase in this size depends on the intrinsic rate of increase in the population.
Article
Full-text available
Opportunistic sightings of some 19 different leopard seals Hydrurga leptonyx at Marion Island (46°54’S, 37°45’E) in the South Indian Ocean were recorded mostly in September to October between 1980 and 2005. Largely immature and both in poor and good condition, they might benefit froma locally abundant food resource. The species appear to be a regular member of the marine fauna of the region, occasionally hauling out on the island coastline as seasonal transients of the archipelago’s marine environment.
Article
Full-text available
Like many pinniped species, southern elephant seals (Mirounga leonina) are conducive to long-term population studies using mark–recapture techniques. The twenty-four year longitudinal dataset at sub-Antarctic Marion Island has already provided much insight into elephant seal population dynamics. However, a limitation of the present dataset is that mother/pup relatedness cannot be examined because pups are only tagged after their tagged mothers have abandoned them. We test the usefulness of two different temporary marking techniques (tagging and ‘strapping’), and four different marker types over two consecutive breeding seasons for use on pups with attending marked mothers. We show that strapping is an ineffective way to mark unweaned southern elephant seals. By comparison, ‘Supersmall®’ Dalton plastic tags allow quick, effective and easy marking of large numbers of pups with known mothers, without excessive marker loss.
Article
Full-text available
The diet of killer whales Orcinus orca was investigated from 48 predation events observed during 823 sightings at sub-Antarctic Marion Island between 2006 and 2009. From these events, there were 10 cases where prey could be identified. Killer whales fed on fur seals Arctocephalus tropicalis, elephant seals Mirounga leonina and penguins. Constant effort (dedicated) observations (259 hours, 2008–2009) showed that the peak in killer whale abundance was between September and December with a secondary peak between April and May, which coincided with peaks in the abundance of seals and penguins.
Book
This thorough revision of the classic first edition brings this authoritative book right up-to-date. Articles describe every species in detail, based on the very latest taxonomy, and a host of biological, ecological and sociological aspects relating to marine mammals. The latest information on the biology, ecology, anatomy, behavior and interactions with man is provided by a cast of expert authors - all presented in such detail and clarity to support both marine mammal specialists and the serious naturalist. Fully referenced throughout and with a fresh selection of the best color photographs available, the long-awaited 2nd edition remains at the forefront as the go-to reference on marine mammals. * More than 20% NEW MATERIAL includes articles on Climate Change, Pacific White-sided Dolphins, Sociobiology, Habitat Use, Feeding Morphology and more * Over 260 articles on the individual species with topics ranging from anatomy and behavior, to conservation, exploitation and the impact of global climate change on marine mammals * New color illustrations show every species and document topical articles FROM THE FIRST EDITION "This book is so good... a bargain, full of riches...packed with fascinating up to date information. I recommend it unreservedly it to individuals, students, and researchers, as well as libraries". - Richard M. Laws, MARINE MAMMALS SCIENCE "...establishes a solid and satisfying foundation for current study and future exploration" - Ronald J. Shusterman, SCIENCE.
Article
The paper describes the occurrence of Killer whales at Marion Island (Prince Edward group) in the south Indian Ocean from August 1973 to November 1976. They occur seasonally, being most numerous from October to December. Their occurrence is synchronized with the seasonal haul out of Southern elephant seals, but the seasonality of King, Rockhopper and Macaroni penguins is also likely to influence their occurrence. The largest herds occur in October, the month during which mean group size is also largest. Sex and age composition are given, adult males being significantly more numerous than adult females, while 36–3 % of the latter had calves. Hunting activity appears to be greatest between 15.00 and 17.00 hrs, and most Killer whales were seen within 100 m of the shore. Aspects of hunting, attacking, feeding and resting behaviour are discussed. The body measurements of a young male found on a beach are given.
Article
In September 2001, 21 satellite-monitored radio tags were deployed on southern right whales in South African waters, 15 of which transmitted for 25–161 d. Most coastwise movement on the south coast occurred in a westerly direction with cow-calf pairs moving slowest. Three whales tagged on the west coast and one tagged on the south coast moved north into St Helena Bay, a probable feeding ground, where residence times were 36–100 d. Five animals tracked after leaving the coast maintained a bearing of 201°–220° before branching out over the southeast Atlantic from 37° to 60°S and between 13°W and 16°E, traveling 3,800–8,200 km over the ensuing 53–110 d before transmissions ceased. Their locations were categorized as migrating or nonmigrating based on the relative orientation of the track and net speed. An average of 42% of nonmigrating locations were between 37°S and 45°S, and 53% were south of 52°S, possibly associated with the Subtropical Convergence and Antarctic Polar Front, respectively. Whaling data suggest right whales fed largely on copepods at the former and euphausiids at the latter. If the nonmigrating locations represented feeding at these frontal zones, switching between them would seem to have obvious cost-benefit implications.