214
effectivelyrepelcetaceans.Therefore, it is necessary
to identify the audible frequency range of cetacean
species which is considered to cause the collision
withvessels.Currently,therearenodirectmeasures
ofaudiblerangeforanylargecetaceansbecausethey
cannot be investigated with conventional
audiometric techniques of psychoacoustical or
electrophysiological analysis. However, the audible
rangecanbeassessedindirectlybythefollowingtwo
procedures,(1)indirect‐estimationfromrelationship
between cetaceans audibility and vocalization, and
(2) indirect‐estimation from measurements on the
cochlear basal membrane. It can be assessed by
vocalization, as to correspond the dominant
frequenciesofthe
vocalization(e.g.calls)tothemost
sensitiveregionofreceptorsysteminvertebratetaxa
(Green and Marler 1979). Alternatively, a
comparativeanatomyapproachistheusefulwayto
estimate the audible range because anatomical
structureofinnerearcorrelatestofrequencyrangein
multiplemammalianspecies(Echteleretal.,1994).
Shakata et al. (2008) and Tsuji et al. (2013)
identified sperm whale (Physeter macrocephalus),
Bairdʹs beaked whale (Berardius bairdii), common
minke whale (Balaenoptera acutorostrata), Brydeʹs
whale (Balaenoptera edeni) and humpback whale
(Megapteranovaeangliae)aspossiblecausalspeciesof
thecollision on the sea
route ofthe HF in Japanese
water.Thevocalizationfrequency range were made
referencetopreviousresearchofspermwhaleinthe
southeastern coast of Chichijima, the Bonin
(Ogasawara) Islands of Japan and Bryde’s whale in
the waters of Kochi on the south western coast of
Japan(Yamada et al.
2012) and humpback whale in
theRyukyuregionofJapan(Maedaetal.2000).This
study estimates the audible range of sperm whale
beaked whale by describing the anatomy used the
Kawamotofilm‐sectioningmethod(Kawamoto2003)
oftheirinnerearsandapplyingthemodeldescribed
byKetten(2000)extendedYamada
etal.2012dataof
common minke whale and Bairdʹs beaked whale
(Table1).
However, since the maximum sensitivity of the
current UWS is 8kHz‐30kHz, sound pressure of
frequencies below 8kHz characteristic tends to
decrease. Therefore, considering the maximum
sensitivityofthespeakershardware,thefrequencyof
the
newUWSsoundwassetat5kHz,themaximum
dominantaudiblefrequencyofthespermwhaleand
the humpback whale that pose a particularly high
collisionrisk(Katoetal.2012),whichisadownward
shift by 1kHz from the currently used frequency
rangeof6‐18kHz.
As far as
the Brydeʹs whale is concerned, the
challenge lies in how to infer its audible frequency
range using the anatomical predictions since its
dominant audible frequency is significantly lower
thanthefrequencyofthenewUWSsound.However,
given that the audible range of the common minke
whale, which belongs
to the same family, is 0.12‐
15.93kHz, it is extrapolated that 5kHz might be fit
wellwithintheaudiblerangeoftheBryde’swhales.
3 SYNTHESIZINGOFNEWSOUNDSFORTHE
EFFECTIVEUWS
Usingorsynthesizingapotentialrepellingsoundfor
cetaceans would be effective for making large
cetaceansavoidancefrom
HF.Forexample,Watkins
(1986)reportedthat cetaceans often react tosudden
or loud sounds of vessel, such as from an engine
starting, a close approach, changes in direction,
putting engine in and out of gear, and propeller
cavitations during reverse or sharp turns. We
synthesizedthetwosoundsources
inordertoinstall
theUWS1)dieselengineshipnoiseoftheJapanese
whale research vessel 2) the clang sound produced
byhittingthemetalpolewithahammer,whichwe
canpotentiallyexpectanavoidancewithcetaceans.It
is described below in detail about the two sounds
thatwere
usedinthesynthesis.
1 Shipnoisewhaleresearchvessel:Weusedahigh‐
passfilterwith0.12kHzforcruisingnoiseatthe
time of the maximum speed (16.7kt, 200rpm) by
theJapanese whale research vessel Yushin Maru
No.2 (747t , 69.6m, Owned by Kyodo Senpaku
Co.,Ltd.)with2
cycleslow‐speeddieselengine.
2 Theclangsoundproducedbyhittingtheametal
pole: We recorded clanging sound by hitting a
metal pole in the water and adjusted the
frequencyandsoundinterval.Forfrequency,we
modulated2.00kHzasanoriginalsoundto5.00
kHz, 8.00 kHz, and
10.00 kHz, and then
alternatelyarranged3frequenciesoftheclanging
sound. This frequency was adjusted with the
maximum frequency of dominant audible
frequencybycausalcetaceansandthemaximum
speaker sensitivity. In addition, for the sound
interval, we also modulated 0.52 second of the
original sound to approximately 0.09
second in
accordance with the interval of whaling vessel’s
diesel knocking sound. The spectrograms and
frequencycharacteristicsofthesynthesizedsound
sourceareshowninfigure1and2.Thefrequency
characteristic was assessed by 1/3‐octave bands
analysis using Avisoft SASLab Pro (Avisoft
Bioacoustics, Germany.Ver.5.2.) because sound
levels in 1/3‐octave
bands are useful in
interpretingnoiseeffectsonanimals.
Table1.Summaryofaudiblerangeofcausalcetaceans.
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SpeciesDominantaudiblerangebyAudiblerangeby
vocalization(kHz)Anatomicalpredictions(kHz)
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OdontocetiSpermwhale1.87‐4.78(Yamadaetal.2011)0.29‐47.75
(toothedwhales) Bairdʹsbeakedwhale0.27‐33.09(Yamadaetal.2011)
MysticetiCommonminkewhale0.12‐15.93(Yamadaetal.2011)
(baleenwhales) Baird’sbeakedwhale 0.13‐0.37(Yamadaetal.2011)
HumpbackWhale0.03‐4.80(Maedaetal.2000)
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