ArticlePDF Available
Aquatic Mammals 2015, 41(3), 327-332, DOI 10.1578/AM.41.3.2015.327
Short Note
Insights from a Gray Whale (Eschrichtius robustus)
Bycaught in the Taiwan Strait off China in 2011
Wang Xianyan,
1
Xu Min,
1, 2
Wu Fuxing,
1
David W. Weller,
3
Miao Xing,
1
Aimee R. Lang,
3
and Zhu Qian
2
1
Third Institute of Oceanography, State Oceanic Administration, Xiamen 361005, China
2
Ocean College, Shandong University at Weihai, Weihai 264209, China
E-mail: qianzhu@sdu.edu.cn
3
Southwest Fisheries Science Center, National Oceanic and Atmospheric Administration, La Jolla, CA 92037-1022, USA
Wang Xianyan and Xu Min equally contributed in this work.
Gray whales (Eschrichtius robustus) are recog-
nized as two distinct populations in the North
Pacific Ocean: the eastern North Pacific (ENP)
population (also known as the California-Chukchi)
and the western North Pacific (WNP) population
(also known as the Korean-Okhotsk) (Andrews,
1914; Rice & Wolman, 1971; LeDuc et al., 2002;
Weller et al., 2013b). Gray whales in the Atlantic
were extirpated prior to the 19th century (Mead
& Mitchell, 1984). The ENP population migrates
from winter areas off Baja California, Mexico, to
summer feeding areas in the Bering, Beaufort, and
Chukchi Seas (Swartz et al., 2006; Weller et al.,
2013b). This population was removed from the
U.S. List of Endangered and Threatened Wildlife
in 1994 and is currently estimated to number
approximately 21,000 individuals (Durban et al.,
2013). The WNP population feeds in the Okhotsk
Sea off Sakhalin Island, Russia (Weller et al.,
1999, 2002), and also off the southeastern coast of
the Kamchatka Peninsula (Tyurneva et al., 2010).
The wintering grounds of the WNP population
remain unconfirmed but may be along the coast
of southern China based on sighting, stranding,
and catch records (Wang, 1984; Omura, 1988;
Henderson, 1990; Kato & Kasuya, 2002; Zhu,
2002; Weller et al., 2013a). A recent population
assessment using an individual-based stage-struc-
tured model resulted in a median estimate of 140
± 6 (SE) 1+ (non-calf) individuals for the WNP
population in 2012 (Cooke et al., 2013). This
population is redlisted by the International Union
for Conservation of Nature (IUCN) as Critically
Endangered (Reilly et al., 2008).
During the winter, some gray whales seen feed-
ing off Sakhalin and Kamchatka have been observed
to migrate to the west coast of North America,
including Mexico (Weller et al., 2012; Urbán
et al., 2013), while others migrate to portions of
the WNP off Asia, including the coasts of Japan
and China (Weller et al., 2008, 2013a). Despite
this level of mixing, genetic comparisons of ENP
and WNP gray whales have found significant dif-
ferences in both nuclear and mitochondrial DNA
(LeDuc et al., 2002; Lang et al., 2010, 2011) sup-
porting their management as distinct population
stocks (Weller et al., 2013b).
Gray whales are exceptionally rare off China,
with only 24 sighting, stranding, or capture records
since 1933 (Weller et al., 2013a). The gray whale
was listed in China as Category II of the National
Key Protected Animals in 1988 and was listed
under the Chinese Red List of Endangered and
Threatened Wildlife and Plants in 1994. The most
recent record of a gray whale from China is from
5 November 2011 when a dead female gray whale
(Figure 1) was found entangled in a set gillnet off
Fujian Province in the Taiwan Strait (Figure 2).
This specimen was 13.1 m in length and 21,000 kg
in weight, and represents the first gray whale
record from Chinese waters in the 21st century. To
explore the possibility of linking the 2011 Taiwan
Strait gray whale to other areas prior to its death,
skin tissue of the whale was collected for genetic
analysis, and photographs of the whale were com-
pared to the existing gray whale photo-identifica-
tion catalogs for the WNP and ENP.
Total DNA was extracted from skin tissue of
this 2011 Taiwan Strait specimen following the
recommended protocol of the TIANamp Genomic
DNA Kit (Catalog No. DP304, TIANGEN). The
extracted DNA was stored in TE buffer (10 mM
Tri-HCl, 1 mM EDTA, pH8.0). The mtDNA control
region was amplified through the polymerase chain
328 Wang et al.
reaction (PCR) using the following primer set: P1:
5’-GAATTCCCCGGTCTTGTAAACC-3’ and P2:
5’-TCTCGAGATTTTCAGTGTCTTGCTTT-3
(Hoelzel et al., 1991). PCR was carried out in a
total volume of 25 μl comprising 100 to 400 ng of
DNA template, 0.2 mM of each dNTP, 0.4 μM of
each primer, and 1.25 unit of ExTaq polymerase
(TaKaRa). The amplification program was con-
ducted as follows: preheating at 94° C for 5 min;
cycling 38 times at 94° C for 40 s, 50° C for 30 s, and
72° C for 1 min; and extending at 72° C for 5 min.
The PCR products were electrophoresed
through a 1% Agarose gel to confirm successful
amplification, and then the PCR products were
sent to Shanghai Invitrogen Biotechnology Co.,
Ltd. for direct sequencing. Cycle sequencing was
performed using the above primers, and then both
strands were sequenced independently on an ABI
3730 Automated DNA Analyzer. The resulting
sequences were edited and spliced by BioEdit,
Version 7.2.5 (Hall, 1999) with manual correction.
PCR amplification and sequencing were repeated
separately again to account for lab error. Finally,
a complete control region (D-loop) sequence, 934
bp in length, was obtained. The full length of the
D-loop sequence was used for the BLAST search
(http://blast.ncbi.nlm.nih.gov/Blast.cgi). BLAST
results indicated that the 522 bp sequence repre-
senting the 5’ end of the control region was com-
pletely identical to the haplotype R (Figure 3)
described in LeDuc et al. (2002) and reported as
haplotype 18 in Lang et al. (2011). Comparison
of the full-length sequence generated from the
China specimen with the three available gray
whale sequences (AP006471.1, AJ554053.1, and
X72200.1) that included the complete control
region indicated that the majority of variable sites
were found within the 522 bp 5’ region and, thus,
did not yield further insight into the origin of the
2011 Taiwan Strait specimen.
To date, mtDNA haplotype data are available
for 377 gray whales considered part of the ENP
population and 142 gray whales sampled in the
WNP (LeDuc et al., 2002; Lang et al., 2011).
The haplotype R was found in 12 ENP individu-
als, the majority (n = 10) of which were collected
from stranded or hunted individuals prior to 2011
(Lang, pers. comm.). However, haplotype R was
not identified among the gray whales sampled
in the WNP, all of which were biopsied on the
Figure 1. The left side (A) and right side (B) of the female gray whale (Eschrichtius robustus) found bycaught in the Taiwan
Strait, Fujian Province of China, on 5 November 2011
Gray Whale Bycaught in the Taiwan Strait 329
Sakhalin Island feeding ground between 1995 and
2007. This sample set included samples from 69%
of the individuals identified in that region through
2011 (n = 205), suggesting that the probability of
haplotype R occurring in the WNP population is
relatively low.
Based on mtDNA haplotype frequency data,
the 2011 Taiwan Strait gray whale specimen has
a higher probability of originating from the ENP
rather than the WNP. However, it is also plau-
sible that haplotype R is carried by one or more
of the individuals that utilize the Sakhalin feeding
ground or other parts of the WNP but have not
been sampled. To further examine this question,
photographs of the 2011 Taiwan Strait specimen
were compared to existing gray whale photo-
identification catalogs from the WNP and ENP.
Comparisons to photo-identification catalogs col-
lected in the WNP off Sakhalin Island and south-
eastern Kamchatka as well as catalogs from the
west coast of North America (Northern California,
Washington, Oregon, and British Columbia) and
the lagoons in Mexico did not produce a photo-
graphic match. Although the photographs of the
2011 Taiwan Strait specimen were suitable for
photo-identification purposes, they were not con-
sidered to be ideal and were additionally limited
to primarily the left side of the whale because
some epidermis on the right side had already been
removed as a result of decomposition (Figure 1B).
Some catalogs from WNP and ENP are based on
the right side; therefore, it is possible that image
quality limitations contributed to the lack of a
photographic match within the WNP or ENP.
Given that the photographs of the 2011 Taiwan
Strait whale did not match any of the individu-
als photographed off Sakhalin or Kamchatka, as
well as the absence of haplotype R among gray
whales sampled in the WNP, our results could
suggest that the 2011 Taiwan Strait whale was
a vagrant from the ENP. In recent years, there
have been sightings of two gray whales in the
Atlantic Ocean—one that was sighted twice in the
Mediterranean Sea in May 2010 (Scheinin et al.,
2011) and a second individual that was sighted
in Walvis Bay, Namibia, in May 2013 (Elwen &
Gridley, 2013). These whales were thought to be
vagrant individuals, most likely from the ENP,
14
Figure 2. Map of the western North Pacific showing: (1) location of a female gray whale
found bycaught in the Taiwan Strait, Fujian Province of China on 5 November 2011
(black star); (2) location of partial skeleton of a gray whale excavated from the Quanzhou
coast, Fujian Province of China in 1958 (black circle) (Li, 1997); (3) location of fossil
specimens of two juvenile gray whales found in the Penghu Channel of Taiwan Strait,
China (black triangle) (Tsai et al., 2014). The Taiwan Strait was shown in dark gray.
Figure 2. Map of the western North Pacific (WNP) showing (1) location of a female gray whale found bycaught in the
Taiwan Strait, Fujian Province of China, on 5 November 2011 (black star); (2) location of partial skeleton of a gray whale
excavated from the Quanzhou coast, Fujian Province of China, in 1958 (black circle) (Li, 1997); and (3) location of fossil
specimens of two juvenile gray whales found in the Penghu Channel of Taiwan Strait, China (black triangle) (Tsai et al.,
2014). The Taiwan Strait is shown in dark gray.
330 Wang et al.
15
Figure 3.
D-loop
sequence obtained in the present study was completely identical to the
Figure 3. The D-loop sequence obtained in the present study was completely identical to the AF326806 (the haplotype
R sequence) submitted to the GenBank by LeDuc et al. (2002) and Lang et al. (2010, 2011). An identical sequence is
highlighted in gray.
331 Gray Whale Bycaught in the Taiwan Strait
that had wandered into the Atlantic as a result of
diminished Arctic Sea ice cover in the northern
passageways. These records suggest that environ-
mental changes resulting from climate warming
may allow gray whales to recolonize areas used
historically or to disperse into new habitats suit-
able for living (Scheinin et al., 2011). Moreover,
without needing new ice-free passages, some gray
whales observed in the WNP have been confirmed
to migrate to the ENP (Weller et al., 2012; Urbán
et al., 2013). Therefore, it is also possible that
an ENP gray whale could disperse to the Taiwan
Strait where gray whales historically occurred.
Another possibility, however, is that an addi-
tional feeding ground (or grounds) exists in the
WNP, but it has not yet been identified or geneti-
cally characterized. Based on records from the
logbooks of 19th century ship-based whalers, gray
whales appear to have had a more extensive distri-
bution in the Okhotsk Sea, while no gray whales,
and very little search effort, were recorded in the
area of northeast Sakhalin Island that is currently
considered the primary feeding ground (Reeves
et al., 2008). While scant information is currently
available to evaluate this hypothesis, the possi-
bility that such additional WNP feeding grounds
could exist and might have been used by the 2011
Taiwan Strait whale highlights the critical impor-
tance of obtaining photographic and genetic evi-
dence, such as that presented herein, from any
gray whales recorded in areas of the WNP other
than the Sakhalin feeding ground.
Interestingly, a partial skeleton of a gray whale
was excavated from the Quanzhou coast of Fujian
Province in 1958 (Li, 1997), and fossil specimens
of two juvenile gray whales have also been found
in the Penghu Channel of Taiwan Strait (Tsai
et al., 2014) (Figure 2). Further, Henderson (1990)
summarized information from the 1869 logbooks
of New Bedford whaling ships while they were
on the “Chinese whale grounds” (p. 14). These
logbooks reported gray whales being sighted in
February at nearly an identical location as the
2011 Taiwan Strait specimen. These sources, in
combination with insights from the specimen
reported herein, suggest the possibility of a past
(and perhaps current) gray whale wintering area
in or near the Taiwan Strait region of the WNP.
Acknowledgments
The authors are grateful to Yu Xingguang, Zhang
Haifeng, Chen Jian, Tao Cuihua, and Zhao Liyuan
of Third Institute of Oceanography, State Oceanic
Administration, and Tong Shenhan of the Xiamen
Institute of Aquatic and Terrestrial Product for
their generous help and assistance during the gray
whale specimen making process.
Olga Tyurneva,
John Calambokidis, and
Jorge Urbán kindly coor-
dinated photo-identification matching to their
respective catalogs. This research was supported
by grants from the National Natural Science
Foundation for Young Scholars of China (No.
41206159) and the State Oceanic Administration
of China (SOA, No. 201105011).
Literature Cited
Andrews, R. C. (1914). Monographs of the Pacific Cetacea.
I. The California gray whale (Rhachianectes glau-
cus Cope) (Part 5, pp. 227-287). New York: American
Museum of Natural History.
Cooke, J. G., Weller, D. W., Bradford, A. L., Sychenko, O.,
Burdin, A. M., & Brownell, R. L., Jr. (2013). Population
assessment of the Sakhalin gray whale aggregation
(Paper SC/65a/BRG27). Submitted to the International
Whaling Commission Scientific Committee.
Durban, J., Weller, D., Lang, A., & Perryman, W. (2013).
Estimating gray whale abundance from shore-based
counts using a multilevel Bayesian model (Paper
SC/65a/BRG02). Submitted to the International
Whaling Commission Scientific Committee.
Elwen, S. H., & Gridley, T. (2013). Gray whale (Eschrichtius
robustus) sighting in Namibia (SE Atlantic) – First
record for southern hemisphere (Paper SC/65a/BRG30).
Submitted to the International Whaling Commission
Scientific Committee.
Hall, T. A. (1999). BioEdit: A user-friendly biological
sequence alignment and analysis program for Windows
95/98/NT. Nucleic Acids Symposium Series, 41, 95-98.
Henderson, D. A. (1990). Gray whales and whalers on the
China coast in 1869. Whalewatcher, 24, 14-16.
Hoelzel, A. R., Hancock, J., & Dover, G. (1991). Evolution
of the cetacean mitochondrial D-loop region. Molecular
Biology and Evolution, 8(3), 475-493.
Kato, H., & Kasuya, T. (2002). Some analyses on the
modern whaling catch history of the western North
Pacific stock of gray whales (Eschrichtius robustus).
Journal of Cetacean Research and Management, 4(3),
277-282.
Lang, A. R., Weller, D. W., LeDuc, R. G., Burdin, A. M.,
& Brownell, R. L., Jr. (2010). Genetic differentiation
between western and eastern gray whale populations
using microsatellite markers (Paper SC/62/BRG11).
Submitted to the International Whaling Commission
Scientific Committee.
Lang, A. R., Weller, D. W., LeDuc, R., Burdin, A. M.,
Pease, V. L., Litovka, D., . . . Brownell, R. L., Jr. (2011).
Genetic analysis of stock structure and movements of
gray whales in the eastern and western North Pacific
(Paper SC/63/BRG10). Submitted to the International
Whaling Commission Scientific Committee.
LeDuc, R. G., Weller, D. W., Hyde, J., Burdin, A. M.,
Rosel, P. E., Brownell, R. L. Jr., . . . Dizon, A. R. (2002).
Genetic differences between western and eastern gray
332 Wang et al.
whales (Eschrichtius robustus). Journal of Cetacean
Research and Management, 4(1), 1-5.
Li, S. Q. (1997). Studies on marine mammals and their
distribution along coastal waters of Fujian Province.
Journal of Oceanography in Taiwan Strait, 16(4), 479-
485.
Mead, J. G., & Mitchell, E. D. (1984). Atlantic gray whales.
In M. L. Jones, S. L. Swartz, & S. Leatherwood (Eds.),
The gray whale, Eschrichtius robustus (pp. 33-53).
Orlando, FL: Academic Press. Xxiv + 600 pp. http://
dx.doi.org/10.1016/B978-0-08-092372-7.50008-X
Omura, H. (1988). Distribution and migration of the west-
ern Pacific stock of the gray whale. Scientific Reports of
the Whales Research Institute, 39, 1-9.
Reeves, R. R., Smith, T. D., & Josephson, E. A. (2008).
Observations of western gray whales by ship-based
whalers in the 19th century. Journal of Cetacean
Research and Management, 10(3), 247-256.
Reilly, S. B., Bannister, J. L., Best, P. B., Brown, M.,
Brownell, R. L., Jr., Butterworth, D., . . . Zerbini, A.
(2008). Eschrichtius robustus (western subpopulation).
In International Union for Conservation of Nature (Ed.),
The IUCN red list of threatened species, Version 2011.1.
Available at www.iucnredlist.org/details/8097/0.
Rice, D. W., & Wolman, A. A. (1971). The life history
and ecology of the gray whale (Eschrichtius robustus)
(No. 3). Stillwater: Oklahoma American Society of
Mammalogists. viii + 142 pp.
Scheinin, A. P., Kerem, D., Macleod, C. D., Gazo, M.,
Chicote, C. A., & Castellote, M. (2011). Gray whale
(Eschrichtius robustus) in the Mediterranean Sea:
Anomalous event or early sign of climate-driven dis-
tribution change? Marine Biodiversity Records, 4, 1-5.
http://dx.doi.org/10.1017/S1755267211000042
Swartz, S. L., Taylor, B. L., & Rugh, D. J. (2006). Gray
whale Eschrichtius robustus population stock identity.
Mammal Review, 36, 66-84. http://dx.doi.org/10.1111/
j.1365-2907.2006.00082.x
Tsai, C. H., Fordyce, R. E., Chang, C. H., & Lin, L. K.
(2014). Quaternary fossil gray whales from Taiwan.
Paleontological Research, 18(2), 82-93. http://dx.doi.
org/10.2517/2014PR009
Tyurneva, O. Yu, Yakovlev, Yu M., Vertyankin, V. V., &
Selin, N. I. (2010). The peculiarities of foraging migra-
tions of the Korean-Okhotsk gray whale (Eschrichtius
robustus) population in Russian waters of the Far Eastern
seas. Russian Journal of Marine Biology, 36(2), 117-
124. http://dx.doi.org/10.1134/S1063074010020069
Urbán R., J., Weller, D., Tyurneva, O., Swartz, S., Bradford,
A., Yakovlev, Y., & Gómez-Gallardo U., A. (2013).
Report on the photographic comparison of the Sakhalin
Island and Kamchatka Peninsula with the Mexican gray
whale catalogues (Paper SC/65/BRG04). Submitted
to the International Whaling Commission Scientific
Committee.
Wang, P. L. (1984). Distribution of the gray whale
(Eschrichtius robustus) off the coast of China. Acta
Theriologica Sinica, 4(1), 21-26.
Weller, D. W., Burdin, A. M., & Brownell, R. L., Jr. (2013a).
A gray area: On the matter of gray whales in the western
North Pacific. Whalewatcher, 29-33.
Weller, D. W., Burdin, A. M., Würsig, B., Taylor, B. L., &
Brownell, R. L., Jr. (2002). The western gray whale: A
review of past exploitation, current status, and potential
threats. Journal of Cetacean Research and Management,
4(1), 7-12.
Weller, D. W., Bradford, A. L., Kato, H., Bando, T.,
Ohtani, S., Burdin, A. M., & Brownell, R. L., Jr. (2008).
Photographic match of a western gray whale between
Sakhalin Island, Russia, and Honshu, Japan: First link
between feeding ground and migratory corridor. Journal
of Cetacean Research and Management, 10(1), 89-91.
Weller, D. W., Würsig, B., Bradford, A. L., Burdin, A. M.,
Blokhin, S. A., Minakuchi, H., & Brownell, R. L., Jr.
(1999). Gray whales (Eschrichtius robustus) off Sakhalin
Island, Russia: Seasonal and annual patterns of occur-
rence. Marine Mammal Science, 15, 1208-1227. http://
dx.doi.org/10.1111/j.1748-7692.1999.tb00886.x
Weller, D. W., Bettridge, S., Brownell, R. L., Jr., Laake,
J. L., Moore, J. E., Rosel, P. E., . . . Wade, P. R. (2013b).
Report of the National Marine Fisheries Service Gray
Whale Stock Identification Workshop (NOAA Technical
Memo NOAA-TM-NMFS-SWFSC-507). Washington,
DC: National Oceanic and Atmospheric Administration,
U.S. Department of Commerce.
Weller, D. W., Klimek, A., Bradford, A. L., Calambokidis,
J., Lang, A. R., Gisborne, B., . . . Brownell, R. L., Jr.
(2012). Movements of gray whales between the western
and eastern North Pacific. Endangered Species Research,
18, 193-199. http://dx.doi.org/10.3354/esr00447
Zhu, Q. (2002). Historical records of western Pacific stock
of gray whale Eschrichtius robustus in Chinese coastal
waters from 1933 to 2002 (Paper SC/02/WGW13).
Presented to the International Whaling Commission
Scientific Committee.
... While these movements indicate that a proportion of the animals feeding off SI have, at least once, migrated to the ENP, a model-based assessment suggests that 20%-55% of SI whales do not overwinter in the ENP wintering grounds off Mexico (Cooke et al., 2019). In addition, a small number of records of gray whales off the coast of Japan (n = 22; and China (n = 2; Wang et al., 2015;Zhao, 1997;Zhu, 2012;Zhu & Yue, 1998) have been reported over the last two decades. The majority of the records from Japanese waters are from the months of March to May, when ENP whales are known to be migrating north up the west coast of North America. ...
... More recent findings showing that some of the whales that feed off SI migrate to and overwinter in the ENP (Mate et al., 2015;Urbán R. et al., 2019;Weller et al., 2012) changed this perception, raising the possibility that the recovery of the ENP gray whale may have also played a role in the recolonization of the SI feeding ground. At the same time, rare but continued sightings of gray whales off the coast of Japan and China (Nakamura et al., 2019;Wang et al., 2015;Zhao et al., 2017;Zhu, 2012;Zhu & Yue, 1998) suggest that some whales, including two first identified as calves with their mothers on the SI feeding ground (Weller et al., , 2016, overwinter in the WNP. ...
... (3) the contemporary winter and spring records of gray whales off Japan and China Wang et al., 2015;Zhao et al., 2017;Zhu, 2012;Zhu & Yue 1998), at least two of which are known to have been brought to Sakhalin by their mothers as calves (Weller et al., , 2016. Secondly, a signal of genetic differentiation could be generated if most of the Sakhalin whales overwinter in the ENP but primarily interbreed with each other. ...
Article
Recent findings that some gray whales that feed off Sakhalin Island (SI), Russia, in the western North Pacific (WNP) overwinter in the eastern North Pacific (ENP) indicate that population structure in this species is more complex than originally thought. We generated mitochondrial DNA (mtDNA) control region sequences and microsatellite genotypes (n = 12 loci) from 156 whales sampled off SI and compared them to available data from 106 ENP whales. Significant mitochondrial and nuclear genetic differentiation between the SI and ENP whales was found. Genetic cluster analysis identified two groups among the SI whales, one of which was genetically similar to ENP whales. Photographs collected from the biopsied SI whales showed that both groups comprised whales known to migrate to the ENP, suggesting that the clustering pattern was not reflective of some SI whales interbreeding while overwintering in the WNP. Instead, the genetic differentiation observed between the SI and ENP whales may be due to assortative mating of SI whales while west of eastern migratory routes. The rare but continued reports of gray whales off the coasts of Japan and China, however, confirm that some gray whales overwinter in the WNP and highlight the need to collect additional data from these whales.
... Most of these records, including sightings as recent as 2017, are from Japanese waters (Nambu et al. 2010, Nakamura et al. 2017. Only two records of gray whales in Chinese waters have been documented since the mid-1990s (Zhao 1997, Wang et al. 2015, Zhao et al. 2017, and gray whales have not been recorded in Korean waters since 1977(Park 1995, Kim et al. 2013. Genetic comparisons of the whales feeding off Sakhalin Island with whales considered part of the ENP population revealed significant genetic differences, although a limited degree of genetic exchange between these populations may take place (Lang et al. 2010(Lang et al. , 2011. ...
Technical Report
Full-text available
Gray whales in the North Pacific are divided into two populations (or stocks) known as the Eastern North Pacific (ENP) and Western North Pacific (WNP) populations. Both were severely depleted prior to the mid-20th century by harvest during the whaling era. The ENP population migrates along the Pacific coast of North America between summer feeding grounds in the Bering, Beaufort and Chukchi Seas and wintering sites along western Baja California and the southern Gulf of California in Mexico, where mating and calving occur. This stock has recovered from the impacts of whaling and was federally delisted by the U.S. in 1994. It held an estimated 26,960 whales in 2016, when it was believed to exist at or near carrying capacity, but declined to an estimated 20,580 animals in 2019-2020. Within the ENP population, a small aggregation of about 232 individuals known as the Pacific Coast Feeding Group (PCFG) has been identified. These whales show regular fidelity during the summer and fall feeding season to waters along the coasts of northern California, Oregon, Washington, and Vancouver Island, British Columbia, and occasionally as far north as Kodiak Island, Alaska. Genetic testing indicates some differentiation from the greater ENP population, but PCFG whales likely interbreed with other ENP whales, and the PCFG is still considered a feeding aggregation of the ENP population. The WNP population, which is federally classified as endangered by the U.S., primarily feeds in summer in the Sea of Okhotsk and off the southeastern coast of the Kamchatka Peninsula in the Bering Sea, and is presumed to winter off the coast of China. Abundance, calculated in 2016 to be roughly 271 to 311 individuals one year and older, remains far below pre-whaling numbers. Research since 2004 has detected some members of this population migrating along the Pacific coast of North America to feeding and wintering grounds used by the ENP population. Gray whales face a number of known or potential threats such as entanglement in fishing gear and marine debris, ship strikes, human-generated marine sound, and climate change. Because of these threats, the small size of the WNP population and its federal endangered status, and the substantial level of uncertainty pertaining to the PCFG’s possible status as a separate stock under the Marine Mammal Protection Act, it is recommended that gray whales as a species be retained as a state sensitive species in Washington. However, uplisting to a higher level of protection may be warranted in the future if continuing research determines that WNP whales regularly migrate through Washington’s waters and/or the PCFG is classified as a separate stock.
... Historical evidence indicates that the coastal waters of eastern Russia, the Korean Peninsula, and Japan were once part of the migratory route and that areas in the South China Sea may have been used as wintering grounds . Present day records of gray whales off Japan (Nambu et al., 2010;Nakamura et al., 2017aNakamura et al., , 2017b and China (Wang, 1984;Zhu, 2002;Wang et al., 2015) are occasional, and the last known record from Korea was in 1977 (Park, 1995;Kim et al., 2013) or possibly 2015 (Kim et al., 2018). In the past two decades, observations of gray whales off Japan, mostly from the Pacific coast, have been increasing (Nakamura et al., 2017b). ...
... On 5 November 2011, a 13.1 m female gray whale died from entanglement in a set net in the Taiwan Strait near the mainland coast of China (Wang et al. 2015). Comparisons of photographs of that whale with the eastern and western North Pacific gray whale photo-identification catalogues revealed no matches. ...
Article
Full-text available
Western gray whales Eschrichtius robustus (WGWs) are endangered, and their range overlaps areas where several important commercial fisheries operate in the Russian Far East (RFE). Throughout their range, gray whales commonly become entangled or entrapped in fishing gear. In the western North Pacific, they have been killed in set nets and seen entangled with ropes and float lines. Signs of fishery interactions on 28 of 150 living whales photographed near Sakhalin Island were reported in a published study. We describe characteristics of RFE fisheries that might entangle WGWs, including fishing effort based on daily catch reports from 2010-2014. We make a preliminary qualitative assessment of entanglement risk, taking into account factors including (1) evidence that the gear type has entangled large whales, (2) fishing effort, and (3) geographic and temporal overlap between WGWs and fishing activity. Fishing for salmonids with pelagic gillnets is no longer allowed in the RFE, and as long as the prohibition is being followed such fishing poses no risk to WGWs. In contrast, the coastal salmon set net fishery poses a high entanglement risk off northeastern Sakhalin and Kamchatka where WGWs feed very close to shore, and that situation should be mitigated. Bottom-set gillnet, demersal longline, snurrevad (also called Danish seine), and trap and pot fisheries overlap substantially with WGW distribution, and bycatch in those fisheries should at least be monitored. More rigorous risk assessment would require additional information on WGW distribution and movements.
... This specimen was the first gray whale record from Chinese waters in the 21st century. Wang et al. (2015b) suggested the possibility of a past (and perhaps current) gray whale wintering area was in or near the Taiwan Strait for the western North Pacific population. Omura's whale was recently recognized as a new baleen whale species and was considered as one of the most mysterious species among them (Wada et al., 2003). ...
Article
The analysis of cetacean strandings can provide fundamental information about species diversity and composition in a particular region. The present study collected and analyzed cetacean strandings, bycatches and rescues along the western coast of the Taiwan Strait, China, from 2010 to 2015. In total, 48 records, including 37 strandings, 8 bycatches and 3 rescues, involving 13 known species were collected. Among them, Indo-Pacific humpback dolphins (Sousa chinensis) and finless porpoises (Neophocaena phocaenoides) were the most common species, consisting of 31.3% and 25%, respectively. Notably, 10 out of the 48 (20.8%) records were collected from the Pingtan Island and included 3 species of Mysticeti and 4 species of Odontoceti. Finally, we compared the cetacean species composition between the western and eastern coasts of the Taiwan Strait; 31 cetacean species occurred in the Taiwan Strait, indicating a relatively high cetacean diversity in this region. Systematic field surveys are urgently needed to explore the cetacean species composition, population stock and the related habitat status in the Taiwan Strait, which may improve conservation management in the future.
Article
Full-text available
Counts of southbound migrating whales off California form the basis of abundance estimation for the eastern North Pacific stock of gray whales (Eschrichtius robustus). Previous assessments (1967–2007) have estimated detection probability (p) from the detection-non detection of pods by two independent observers. However, tracking distinct pods in the field can be difficult for single observers; resulting in biased estimates of pod sizes that needed correcting, and matching observations of the same pod by both observers involved key assumptions. Due to these limitations, a new observation approach has been adopted wherein a paired team of observers work together and use a computerised mapping application to better track and enumerate distinct pods and tally the number of whales passing during watch periods. This approach has produced consistent counts over four recently monitored migrations (with an apparent increase in p compared to the previous method. To evaluate p and estimate abundance in these four years, counts from two independent stations of paired observers operating simultaneously were compared using a hierarchical Bayesian 'N-mixture' model to jointly estimate p and abundance without the challenge of matching pods between stations. The baseline detectability p o was estimated as 0.80 (95% Highest Posterior Density Interval [HPDI] = 0.75–0.85), which varied with observation conditions, observer effects and changes in whale abundance during the migration. Abundance changes were described using Bayesian model selection between a parametric model for a normally distributed common migration trend and a semi-parametric model that estimated the time trends independently for each year; the resultant migration curve was a weighted compromise between models, allowing for key departures from the common trend. The summed estimates of migration abundance ranged from 17,820 (95% HPDI = 16,150–19,920) in 2007/08 to 21,210 (95% HPDI = 19,420–23,230) in 2009/10, consistent with previous estimates and indicative of a stable population.
Article
Full-text available
Between 2005 and 2007, four female western gray whales were accidentally entrapped and died in Japanese set nets while migrating along the Pacific coast of Honshu, Japan. Photographs of these animals were compared to a photo-identification catalogue of western gray whales from their feeding ground off Sakhalin Island, Russia, to look for matches of individuals between the two areas. Although useable quality photographs were available for only one of the four whales from Japan, a confirmed match was made to a whale photographed off Sakhalin Island. This match represents the first link between the feeding ground and a migratory corridor and highlights the importance of multinational research collaboration in the formation of range-wide conservation measures to protect this critically endangered population.
Article
Animals belonging to the small, endangered population of western gray whales (Echrichtius robustus) are observed today primarily during the summer open-water season in feeding areas off the northeastern coast of Sakhalin Island, Russia. The migration route(s) and wintering area(s) used by this population are largely unknown. Gray whales once had a fairly extensive distribution in the Sea of Okhotsk but little detailed information has been published on when and where they occurred. Open-boat, ship-based whalers from the United States and a few other countries conducted an intensive hunt for bowhead whales (Balaena mysticetus) and North Pacific right whales (Eubalaena japonica) in the Sea of Okhotsk from the 1840s to 1870s. According to entries in voyage logbooks, the American whalers regularly encountered (and sometimes hunted) gray whales in the far northeastern corner of the Okhotsk Sea (Shelikhov Bay, Gizhiginskaya Bay and Penzhinskaya Gulf) between early May-late August. They also observed gray whales in summer along the northern coast of the sea (especially Tauskaya Bay), around the Shantar Islands, in Sakhalin Bay, off Cape Elizabeth at the northern tip of Sakhalin Island and along the west coast of the Kamchatka peninsula. No evidence was found in the logbooks studied of gray whales (and indeed of whaling effort) off northeastern Sakhalin Island where most observations of gray whales occur in the present day.