Abstract
In 1999 and 2000, the number of gray whale (Eschrichtius robustus)
strandings from Mexico to Alaska increased to seven times the mean annual stranding between 1995
and 1998. Two hundred and eight-five whale carcasses were reported in 1999 and 377 in 2000. The
previous high was 89 animals in the 1980s. By 2001 strandings decreased again to 20 whales in
total. The majority of the dead whales occurred in the breeding lagoons in Baja California,
Mexico. In the U.S., mortality occurred throughout the migration route, with a cluster of
animals (about 30) found floating dead in San Francisco Bay in April and May 2000. The emaciated
condition of many of the carcasses, coupled with the increase in the total gray whale
population, lead to speculation that the whale population has reached carrying capacity and is
starving2. Although this explanation is possible, insufficient data exist to support
or refute this contention.
Only limited data on stranded animals are available. Carcass examination
often was limited because of inaccessibility or stage of decomposition of the carcasses. In 1999
and 2000, adult animals were the most common age class to strand, whereas in previous years,
calves were the most common age class observed. Blubber thickness in animals examined ranged
from 4.6 to 17 cm. Only three animals that stranded in the U.S. received complete post mortem
examinations. These three animals stranded alive in California, and were euthanized due to poor
prognosis based upon their emaciated condition and prolonged stranding. All three were young
emaciated animals, one had severe intestinal parasitism with a granulomatous
enteritis1, one had histological changes in the cerebrum suggestive of viral
encephalitis, the third had the biotoxin, domoic acid, in blood, urine and feces, suggesting
intoxication, as well as transmural abscesses in the gut-associated lymphoid tissue. All three
animals were emaciated, with blubber thickness over the sternum between 7 and 10 cm. Whales that
were found dead in San Francisco Bay were mostly observed in or adjacent to the main shipping
channels. One of these animals that beached had propeller wounds along its dorsum. A second
whale was reported to have been hit by a tug-boat, but the carcass was not recovered.
It is likely that malnutrition was an important predisposing factor in the
mortality of each of these cases. Malnutrition may cause immunosuppression or alter feeding
behavior. The former may enhance susceptibility to infectious agents. The latter may result in
whales feeding in locations or on prey not historically consumed, so that they could be in
shipping channels and get struck by vessels, or ingest atypical parasites or toxins such as
domoic acid. The ultimate cause of the malnutrition of gray whales is unexplained. Possible
explanations are decreased availability of prey in the summer feeding grounds due to El
Niño, decadal climatic changes, changes in seasonal ice cover3, global warming,
overgrazing of the benthos due to increased gray whale numbers, or over-fishing by humans.
Detailed examination of stranded animals, coupled with long term monitoring of gray whale
populations and their prey base are needed to determine the ultimate cause of the increased
strandings in 1999 and 2000.
Acknowledgements
We thank all the staff of the National Marine Fisheries Service and
members of the National Stranding Network who collected data on stranded whales in the U.S.,
especially Joe Cordaro, Brent Norberg, Pat Gearin, Merril Gosho, John Calambokidis, Kate Wynne,
Kaja Brix and Sue Moore; as well as Ed Lochbaum in Canada and Lorenzo Rojas and Jorge Urban and
their staff in Mexico.
References
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2000. Prey, parasites and pathology associated with the mortality of a juvenile gray whale
(Eschrichtius robustus) stranded along the northern California coast. Diseases of
Aquatic Organisms, 42: 111-117.
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Wade, L Rojas-Bracho, T Rowles, 2001. Are gray whales hitting "k" hard? Marine Mammal
Science, 17: 954-958.
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