SC/

66b
Cruise report of the second phase of the Japanese
Whale Research Program under Special Permit in the /SPxwestern North Pacific (JARPN II) in 2015 (Part III) –Coastal component off Kushiro
TOSHIYA KISHIRO1, HIDEYOSHI YOSHIDA2, NOBUYUKI ITO3, TOSHIHIRO MOGOE4, GEN NAKAMURA5, HIKARI
MAEDA2, NAOKO MIYAKAWA5, AYUMI HIROSE5, MASAYOSHI OTA5, KOICHIRO KATO5, RYOTARO HAYASHI5,
KOUHEI YOSHII5, YUJIN KIM5, TOMIO MIYASHITA6, SAEKO KUMAGAI3,HITOMI SATO3, YUKA KIMURA3,HISOKA
HIRUDA3, TAIKI KATSUMATA5, KAZUYOSHI NAKAI4, AND HIDEHIRO KATO5
1

Headquarters of Japan Fisheries Research and Education Agency, 15F Queen's Tower B, 2-3-3 Minato Mirai,
Nishi-ku, Yokohama, Kanagawa, 220-6115, Japan
2
National Research Institute of Far Seas Fisheries, Japan Fisheries Research and Education Agency, 2-12-4
Fukuura, Kanazawa-ku, Yokohama, Kanagawa, 236-8648, Japan
3
Association for Community-Based Whaling, Hakata-Eki-Higashi, Hakata-ku, Fukuoka 812-0013, Japan
4
The Institute of Cetacean Research, 4-5 Toyomi-cho, Chuo-ku, Tokyo, 104-0055, Japan
5
Tokyo University of Marine Science and Technology, 4-5-7 Konan, Minato-ku, Tokyo 108-0075, Japan
6
National Research Institute of Far Seas Fisheries, Japan Fisheries Research and Education Agency, 5-7-1 Orido,
Shimizu-ku, Shizuoka, Shizuoka, 424-8633, Japan
ABSTRACTThe JARPN II coastal component off Kushiro, northeast Japan (the sub-area 7CN) was conducted from 5 September to 22 October
2015, with additional dedicated sighting surveys for biopsy sampling in 2 September and 23 October. The surveys were carried out
using four small-type whaling catcher boats, in the coastal waters within the 50 nautical miles from the Kushiro port. All whales
sampled were landed on the land station in the Kushiro port for biological examination. During the survey, a total of 5,811.9 n.
miles (587.1 hours) was searched, 88 schools/ 94 individuals of common minke whales were sighted and 51 whales were sampled.
Average body length of sampled whales was 6.67m (SD=0.91, n=35) for males and 6.07m (SD=1.35, n=16) for females, respectively.
The 21 animals of 35 males (60.0%) and four of 16 females (25.0%) were sexually mature. The dominant prey species found in thestomach was Japanese sardine Sardinops melanostictus (51.0%), followed by mackerel Scomber japonicas and S. australasicus(19.6%), krill Euphausia pacifica (9.8%), walleye pollock Gadus chalcogrammus (7.8%), and Japanese common squid Todarodes
pacificus (2.0%). The dominant occurrence of Japanese sardine and mackerel observed in the stomach in recent years suggested
that the change in main prey species with reflect to the environmental change in the waters have been occurred as suggested by theprevious 2012-2014 surveys. During the surveys, faecal searching was made for 31.4 hours on 59 animals encountered, and one
case of excretion was observed, but no sample was collected. A total of 65.4 hours (11.1% of a total searching efforts) was allocatedto the dedicated sighting surveys for biopsy sampling. Seven animals encountered were targeted, and four biopsy darts were hit,
however no sample was collected.

BACKGROUND
The objectives of the second phase of the Japanese Whale Research Program under Special Permit in the western
North Pacific (JARPN II) are: i) feeding ecology and ecosystem studies, involving prey consumption bycetaceans, prey preferences of cetaceans and ecosystem modelling, ii) monitoring environmental pollutants incetaceans and marine ecosystem, and iii) stock structure of whales (Government of Japan, 2002).
The JARPN II involves two survey components; ‘offshore’ which is covered by the Nisshin Maru
research vessels and ‘coastal’ which is covered by small-type whaling catcher boats, and the latter one isnecessary to cover the temporal and spatial gaps, which cannot be covered by the Nisshin maru research vessels(Government of Japan, 2002).
After the two-year feasibility surveys of the coastal component conducted in 2002 off Kushiro and 2003
off Sanriku district (Kishiro, et al., 2003, Yoshida, et al., 2004, Government of Japan, 2004a), the coastal
component has been conducted twice a year, with 60 common minke whales being sampled in each of spring off
Sanriku and autumn off Kushiro (Government of Japan, 2004b). The survey off Kushiro was conducted annuallyfrom 2004 to 2013 (Kishiro, et al., 2005, 2006, 2008, 2010, 2012, 2014: Yoshida, et al., 2007, 2009, 2011,2013).
In 2014, following the 31 March 2014 Judgement of the International Court of Justice (ICJ) in the case
Whaling in the Antarctic (Australia v. Japan: New Zealand intervening), the Government of Japan voluntarily
reviewed the state of JARPN II, which resulted in modification of maximum lethal sample size of 60 to 51 for1each survey, and non-lethal method was introduced into the surveys. These modifications were applied in the2014 surveys (Mogoe, at al., 2015, and Yoshida, et al., 2015). The 2015 survey was conducted following thesame framework and modifications introduced in 2014.
This paper summarized results of the 2015 survey off Kushiro. The National Research Institute of Far
Seas Fisheries (NRIFSF), Japan Fisheries Research and Education Agency, planned and conducted the survey
cooperate with the Institute of Cetacean Research (ICR), Tokyo University of Marine Science and Technology,
and the Association for Community-Based Whaling.
MATERIALS AND METHODS
Research area
The research area was same to the previous surveys (Kishiro, et al., 2003, 2005, 2006, 2008, 2010, 2012, 2014,
Yoshida, et al., 2007, 2009, 2011, 2013, 2015, Yasunaga et al., 2012), i.e. the coastal waters off Kushiro, within
the 50 nautical miles from the Kushiro port (Fig. 1). This area is included in the middle part of the sub-area 7CN,
established by the IWC.

Research vessels, land station, and research period
Four small-type whaling catcher boats were used: Taisho Maru No. 28 (47.3GT), Koei Maru No.8 (32.0GT),
Sumitomo Maru No.51 (30.0GT), and Katsu Maru No.7 (32.0GT). All the whales collected were landed on theland station (the JARPN II research station) in the Kushiro port for biological examination. Research period forwhale sampling was set for 50 days in advance, from 5 September to 24 October 2015, and actual period forsampling of 51 animals was 48 days from 5 September to 22 October. In addition, dedicated sighting surveys forbiopsy sampling were conducted four days (2 and 6 September, and 22 and 23 October).

Searching and sampling methods
Searching and sampling methods were almost same with those for the first coastal survey off Kushiro in 2002
(Kishiro et al. 2003). The research head office was placed in the research station and controlled the sampling
vessels during the survey. All catcher boats were engaged as the sampling vessels. To avoid the concentration ofsampling location, the research head office arbitrarily determined the searching area and route (direction fromthe port) for each sampling vessel in every day, based on the information of the whale distribution. Weather
conditions and information on fishing grounds of prey species were also considered. In each vessel, a researcher
was on board and recorded the cruise tracks, searching time on effort, sea weather conditions and sighting data.
Sighting data would be collected for all baleen whales and sperm whales. The vessel principally continued to
cruise and search along the predetermined direction until arrived at 15-30 n. miles from the port, and then freely
cruised in the waters within the 50 n. miles radius from the port. Searching was carried out during the day andthe vessels returned to the port every night. Sighting was conducted from the top barrel and upper bridge by all
the crews and researcher with vessel speed at about 11 knots. All common minke whales sighted were targeted
for sampling, except for the cow-calf pair. When a sighting consisted of more than one animal, first targetedanimal was selected following the random sampling digits. Sampling was made by 50 mm whaling cannon.
Once a vessel caught a whale, it returned to the Kushiro port to transport the animal to the research station.
While returning to the port, other common minke whales sighted were also targeted for sampling, if the situation
allowed. At the port, the sampled whale was lift up from the vessel using wire nets and a crane and transported tothe station by an 11 tons freight trailer. At that time, body weight of the whale was measured with the truck
scale.

Non-lethal sampling methods
Biopsy sampling and faecal sampling trials for common minke whales was carried out by small-type whaling
catcher boats. Biopsy sampling was tried during the dedicated sighting surveys conducted in the outside of thewhale sampling activities. Searching and chasing methods was same as the whale sampling survey mentioned
above. The compound crossbow and Larsen guns were used for sampling. Faecal searching was conducted asmuch as possible for the whales encountered and chased during both the whale sampling survey and dedicatedsighting survey. If the excretion were observed, faecal samples were planned to be collected using a handy longpole with a plankton net.

2

Biological research on common minke whales collected
All the whales sampled were biologically examined by researchers at the research station. Research items of thebiological studies are summarized in Table 2, with the number of data and samples obtained. These items wererelated to studies on feeding ecology, stock structure, life historical biology and pollutions.

RESULTS
Searching effort made by vessels
All cruise tracks during the surveys are shown in Figure 2. The searching areas covered widely coastal waters
within 30 nautical miles from the Kushiro port. Searching distance and time are shown in Table 1. Here, we
defined the searching distance and time as that with sighting effort, i.e. the periods of the searching conductedfrom the top barrel. During the research period, total searching distance and time were 5,811.9 n. miles and587.1 hours, respectively.

Sightings and sampling of common minke whales
Figure 2 shows distribution of common minke whales sighted. Sighting positions distributed in inshore areas off
Kushiro port to the waters in around 30 n. miles from the port, and apparent concentration was not observed in
the research area. During the survey, a total of 88 schools/ 94 individuals of common minke whales weresighted, consisting of 79 schools/ 85 individuals of primary sightings and 9 schools/ 9 individuals of secondarysightings (Table 1). These figures probably include some duplicated sightings because sampling vessels searchedalmost same areas in every day. Density index of common minke whales was calculated as 1.46 for DI (thenumber of primary sightings per 100 nautical miles searching) and 0.14 for SPUE (the number of primarysightings per 1 hour searching). Of the 94 common minke whales sighted, 51 common minke whales were
sampled. In the sampling process, there were no struck and lost animals. Fig.2 showed sighting positions ofsampled whales. Distribution of these whales almost covered all of the areas where the sightings were madeduring the survey period.

Non-lethal sampling of common minke whales
Biopsy sampling
A total of 65.4 hours (11.1% of a total searching efforts) was allocated to the dedicated sighting surveys for biopsy
sampling of common minke whales. Seven animals encountered during the survey were targeted, and four biopsy
darts were shot and hit on three animals using Larsen guns, however one dart did not contain the skin sample when
it was retrieved, and one was lost at the sea (could not be retrieved). Two darts were damaged, when they hit the
animal body. From these, no samples were collected.

Faecal sampling
During the surveys, faecal searching was made for 31.4 hours on 59 animals encountered, and one case of excretion
was observed. However, faecal was disappeared before sampling, and could not be collected.

Sightings of other large cetacean
During the survey, a total of 14 schools/ 19 individuals of humpback whales, 9 schools/ 10 individuals of fin
whale, and 2 schools/ 3 individuals of sperm whales were sighted (Table 1). Sighting positions of those whales
are shown in Figure 3.

Sex ratio, body length and maturity of common minke whales caught
51 sampled whales were consisted of 35 males and 16 females (sex ratio of males was 0.69). Average bodylength of the whales was 6.67m (max=8.00, min=4.85, SD=0.91) for males, and 6.07m (max=8.17, min=4.28,
SD=1.35) for females, respectively (Table 3). Composition of sex and sexual maturity of the whales is listed inTable 4. Male with a single testis weight of 290g or more, and female had at least one corpus luteum or albicans
in their ovaries were determined as sexually mature. In males, 21 of 35 individuals (60.0%) were sexually3mature. In females, four of 16 individuals (25.0%) were sexually mature. Mature females were consisted of one
resting animal and three pregnant animals. Among them, one pregnant female had twin foetus (125cm male and103cmm male). Other two pregnant females had 111cm (female) and 180cm (male) foetus, respectively.

Prey species of common minke whale found in the stomach
Following the same methods used in the JARPN II feasibility surveys (Fujise, et al., 2002), stomach contents
were weighted to the nearest 0.1 Kg by each four chamber in both cases of including and excluding liquid. Then,a sub-sample of stomach contents was collected and frozen for the later laboratory work. The weights offorestomach contents including liquid ranged from 1.2Kg to 72.1Kg, and average weight was 23.9Kg.
Table 5 shows the forestomach contents of the 51 collected whales. Dominant prey species was
Japanese sardine Sardinops melanostictus (51.0%), followed by mackerel Scomber japonicas and S.
australasicus (19.6%), krill Euphausia pacifica (9.8%), walleye pollock Gadus chalcogrammus (7.8%), andJapanese common squid Todarodes pacificus (2.0%). Among them, Japanese sardine was found throughout the
research period from September to October. Other prey species (Mackerel, krill, walleye pollock and Japanesecommon squid) were found in only September. Japanese anchovy Engraulis japonicas, which was one of the
major prey species found in the stomach in the previous 2002-2011 surveys, was not detected in the present
survey. Pacific saury Cololabis saira was also not detected.

Observation of marine debris
Marine debris was detected from stomach of three animals. One animal had a plastic sheet (ca. 15cm x 40cm),
one animal had a plastic tape and an empty can (ca. 7cm x 12 cm), and one animal had a small piece of plastics
product (3cm x 9cm). The other 48 animals had no debris in their stomach.

DISCUSSION
As same as the previous surveys, bad weather conditions such as typhoons, low atmospheric pressures and thickfog often disturbed the research activities. During the 48 days survey period, sampling vessels could conduct the
research for 25 days or 52.1% of a total survey period. This figure was lower than that of the last 2014 survey(77.3%). The density index of common minke whales in the present survey (DI=1.46) was also lower than thatof the 2014 survey (DI=3.30), but almost same with those of the 2007 and 2008 surveys (DI=1.24 to 1.67).
Figure 4 shows the body length compositions of common minke whales caught in 2015, withcomparison to the results of the previous 2002-2014 surveys. In the present survey, large male (7m in lengthclass) was frequently caught, and body length composition was similar to those in the 2013 and 2004 to
2007surveys. These results implied that mature males frequently migrated to the coastal waters in mid-2000th,
and migrated again in recent years.
Figure 5 shows the yearly change in the composition of prey species found in the stomach of common
minke whales through the 2002 to 2015 surveys. Until 2011, Japanese anchovy was one of the major preyspecies found in the stomach. Japanese sardine was first detected in 2012, and became the dominant prey species
in recent years, instead of Japanese anchovy. Pacific saury in the stomach has been disappeared since 2008, andMackerel has been appeared since 2012. Further in 2015, frequency of Mackerel became high compared withthose in previous years. The apparent changes in the prey species compositions were well coincided withfisheries catch information (Tamura, et al., 2016), and distributed abundance of prey species in the waters(Kishiro, et al., 2016). These results suggested that the stomach contents of the whales could reflect theenvironmental changes in the waters, and the regime shift of the marine ecosystem or the alternation of the fish
species has been occurred in recent years.
Japanese sardine was taken by both immature and mature animals (Fig.6). This suggested thatJapanese sardine could be attracted both immature and mature common minke whales, as same as Japanese
anchovy in the past (Kishiro, et al., 2009). Although sample size was small, Mackerel was frequently taken by
mature animals, and walleye pollock was frequently taken by immature animals. As same as previous surveys,
Japanese common squid was taken by only mature animal. Difference in prey preference observed here might
be explained by the trade-offs of the cost for foraging activity and energy demands between immature andmature animals as suggested in previous surveys (Kishiro, et al., 2009).

4Figure 7 shows geographical positions of the whales by their maturity status and prey species found in
the stomach. Mature animals distributed slightly offshore region, compared with immature animals, but both
immature and mature animals taking Japanese sardine were distributed widely in nearshore to offshore waters,
while both immature and mature animals taking walleye pollock were concentrated along the 200-500m isobathson the continental slop region. These results indicated that the stomach contents of the whale was also affectedby the distribution of prey species.
Regarding the aspects on the non-lethal methods, no biopsy samples could be obtained in the present
survey, though four darts hit the whale body. One of the reason was thought to be the damage of the darts caused
from the short distance shooting. The technical improvements in darts are considered for future surveys. In the
faecal searching, the present survey revealed that the encounter of faeces was rare as same as in the previous
survey. Contents of the intestine were collected at the biological research on the sampled animals, and thesesamples will be analysed for the comparative studies on the stomach contents. Tissues samples including skin by
the biological research will be also used in the feasible examination on the stable isotope and fatty acids
analyses. These trials will be continued in the next year survey, and the results of these trials in the three years
from 2014 to 2016 will be summarized and presented at the future IWC meetings.

ACKNOWLEDGMENTS
The authors are greatly indebted to Dr. Seiji Ohsumi (ICR) and Messrs. Hideki Moronuki, Yukito Narisawa andShinichi Tashiro, the Fisheries Agency of Japan for their guidance and implementation of the research. We thankto all crew of the research vessels and all staff of the land station and the Japanese small-type whaling
association. We also thank to the staff of the Kushiro City and the Kushiro Fisheries Cooperative Union for theirkind assistance in the implementation of the research.

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Table 1. Searching days, hours, distances, and number of sightings in the 2015JARPN II coastal component off
Kushiro.

6

Table 2. Summary of biological data and samples collected during the 2015 JARPN II coastal component off
Kushiro.

7

Table 3. Body length (m) of common minke whales sampled by the 2015 JARPN II coastal component off
Kushiro.

Table 4. Composition of sex and sexual maturity of common minke whales sampled by the 2015 JARPN II
coastal component off Kushiro.

Table 5. Number of common minke whales by major prey species found in their forestomach contents sampled
by the 2015 JARPN II coastal component off Kushiro.
Number of whales (%)
Period
5 Sept.- 15 Sept.
16 Sept.- 30 Sept.
1 Oct.- 15 Oct.
16 Oct.- 22 Oct.
Total

Walleyepollock

Krill

JapanesesardineMackerelCommonsquid

Empty orunknownTotal

2 (13.2)
2 (11.1)
0(-)0(-)

1 ( 6.7)
4 (22.2)
0(-)0(-)

7 (46.7)
3 (16.7)
2 (66.7)
14 (93.3)

4 (26.7)
6 (33.3)
0(-)
0(-)

0(-)
1 ( 5.6)
0(-)0(-)

1 ( 6.7)
2 (11.1)
1 (33.3)
1 ( 6.7)

15
18
3
15

4 ( 7.8)

5 ( 9.8)

26 (51.0)

10 (19.6)

1 ( 2.0)

5 ( 9.8)51

8

Fig.1. The IWC sub-area for western North Pacific minke whales (upper) and research area for the 2015 JARPN
II coastal component off Kushiro (lower).

Fig.2. Cruise tracks (left) and sighting positions of common minke whales (right) during the 2015 coastal
component off Kushiro. Closed circles are sighting position of whales taken.
.

9Fig.3. Sighting positions of humpback (closed triangle), fin (open square), and sperm whales (open triangle), in
the 2015 coastal component off Kushiro.

Fig 4. Body length frequency of common minke whales sampled during the 2015 coastal component off
Kushiro, with comparison to the results of the previous surveys

10Fig. 5. Composition of prey species of common minke whales sampled during the 2015 coastal component off
Kushiro, with results of the previous surveys.

Fig.6. Sexual maturity and body length frequency of common minke whales by their major prey species found in
the forestomach in the 2015 coastal component off Kushiro.

11

Fig.7. Sighting positions of common minke whales in the 2015 coastal component off Kushiro, by their sexual
maturity and major prey species found in the forestomach

12