Alexandre GANNIER. Groupe de Recherche sur les Cétacés, BP 715, Antibes cedex, France. Corresponding author:

Similar documents
~ A Behavioral Response Study in 2007 &2008 (BRS 07/08) was conducted in the Bahamas to

From Clicks to Counts

Acoustic Seaglider for Beaked Whale Detection

Biological & Behavioral Response Studies of. Marine Mammals in Southern California, BRS.org. Photos taken under NMFS permit #

Acoustic Seaglider for Beaked Whale Detection

Understanding the Foraging Ecology of Beaked and Short-Finned Pilot Whales in Hawaiian Waters

Tagging and Playback Studies to Toothed Whales

Acoustic Seaglider for Beaked Whale Detection

Fine-scale Focal DTAG Behavioral Study in the Gulf of Maine

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

Pacific Missile Range Facility (PMRF) Species Verification and Satellite Tagging Test: January Post-Test Report

Beaked Whale Group Deep Dive Behavior from Passive Acoustic Monitoring

Behavioral and Physiological Response of Baleen Whales to Ships and Ship Noise

Behavioral and physiological response of baleen whales to ships and ship noise

Do ship strikes a fatality in the Pelagos sanctuary?

Marine Mammal Acoustic Tracking from Adapting HARP Technologies

FINAL REPORT Tagging and Playback Studies to Toothed Whales

Fine-Scale Survey of Right and Humpback Whale Prey Abundance and Distribution

Final. Submitted to: Naval Facilities Engineering Command Atlantic under Contract No. N D-3011, Task Orders 14 and 21, Issued to HDR, Inc.

Baseline Behavior of Pilot Whales and their Responses to Playback of Anthropogenic and Natural Sounds

Cetacean Identification Key

Diving and Feeding Behaviour of Sperm Whales (Physeter macrocephalus) in the Northwestern Mediterranean Sea

Remote Monitoring of Dolphins and Whales in the High Naval Activity Areas in Hawaiian Waters

DIVING BEHAVIOR AND ECOLOGY OF CUVIER S (Ziphius cavirostris) AND. BLAINVILLE S BEAKED WHALES (Mesoplodon densirostris) IN HAWAI I

Acoustic Float for Marine Mammal Monitoring

Fine-scale Focal Dtag Behavioral Study of Diel Trends in Activity Budgets and Sound Production of Endangered Baleen Whales in the Gulf of Maine

Modeling Gas Dynamics in California Sea Lions

Estimating cetacean population density using fixed passive acoustic sensors: An example with Blainville s beaked whales

Sperm whale diving behavior monitored using a suction-cupattached

Acoustic and Visual Survey of Cetaceans at Palmyra Atoll

RESOLUTION 4.17 GUIDELINES TO ADDRESS THE IMPACT OF ANTHROPOGENIC NOISE ON CETACEANS IN THE ACCOBAMS AREA

Marine Mammals. James M. Price. Division of Environmental Sciences. from NOAA photograph library

No shallow talk: Cryptic strategy in the vocal communication of Blainville s beaked whales

Blue Whale Behavioral Response Study & Field Testing of the New Bioacoustic Probe

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

Using DTAGs to understand sound use, behavior, and vessel and associated noise effects in Southern Resident killer whales

COSTA RICA DOME BLUE WHALE CRUISE REPORT Todd Chandler and John Calambokidis Cascadia Research Collective November 2004

Marine Mammal Acoustic and Visual Surveys - Analysis of Neart Na Gaoithe data Table of Contents

STUDIES OF BEAKED WHALE DIVING BEHAVIOR AND ODONTOCETE STOCK STRUCTURE IN HAWAI I IN MARCH/APRIL 2006

Beaked whale foraging behavior before, during, and after sonar exposure on a Navy test range

DECEMBER 15-18, 1997 ADELAIDE, SOUTH AUSTRALIA. Douglas H. Cato. Defence Science and Technology Organisation PO Box 44, Pyrmont, NSW, 2009, Australia

The Meeting of the Parties to the Agreement on the Conservation of Cetaceans of the Black Sea, Mediterranean Sea and Contiguous Atlantic Area:

LATTE Linking Acoustic Tests and Tagging Using Statistical Estimation

BEFORE THE ENVIRONMENTAL PROTECTION AUTHORITY JOINT STATEMENT OF EXPERTS IN THE FIELD OF MARINE MAMMALS

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

Providing Field Support for the Behavior Response Study (BRS-08)

Issues Affecting the Southern Resident Orcas

TRAC. Document de référence 2011/03 Reference Document 2012/03

Providing Field Support for the Behavior Response Study (BRS-07)

NAVAL POSTGRADUATE SCHOOL

Underwater Behavior of Blue Whales Examined with Suction-cup Attached Tags

Baseline Behavior of Pilot Whales and their Responses to Playback of Anthropogenic and Natural Sounds

Report prepared by: Marine Conservation Research International 1 High Street Kelvedon Essex CO5 9AG, UK.

ABSTRACT DEEP MAPPING OF TEUTHIVOROUS WHALES AND THEIR PREY FIELDS

I. Monitoring and Adaptive Management Approach. Potential Effects, Monitoring Studies & Mitigation

Active hunting by deep-diving sperm whales: 3D dive profiles and maneuvers during bursts of speed

Final Cruise Report Marine Mammal Observer UNDET Monitoring Hawaii Range Complex, April, 2011

Fine Scale Baleen Whale Behavior Observed Via Tagging Over Daily Time Scales

LATTE Linking Acoustic Tests and Tagging Using Statistical Estimation

Acoustic and diving behavior of sperm whales (Physeter macrocephalus) during natural and depredation foraging in the Gulf of Alaska

Scanning sonar of rolling porpoises during prey capture dives

Assessment of cumulative Sound Exposure Levels (SEL) for marine piling events

New Tools for Advancing Our Understanding of Marine Mammal Behavior Ecology

3S 2 : Behavioral Response Studies of Cetaceans to Navy Sonar Signals in Norwegian Waters

Underwater noise and offshore windfarms

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

Feeding performance by sympatric blue and fin whales exploiting a common prey resource

Human-generated sound and marine mammals

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

Catch per unit effort of coastal prawn trammel net fishery in Izmir Bay, Aegean Sea

LIMPET tagging of Hawaiian odontocetes: assessing reproduction and estimating survival of tagged and non tagged individuals

FINAL REPORT. SERDP Project RC Deep Mapping of Teuthivorous Whales and Their Prey Fields JANUARY 2016

WildCat RF unit (0.5W), full 32-byte transmissions with built-in checksum

Extreme diving of beaked whales

BAJA BLUE WHALE RESEARCH 2011

Distribution and demographics of fin whales in the Southern California Bight. Final Report Contract N P-2723

Measurement of underwater noise arising from marine aggregate operations

AN ABSTRACT OF THE THESIS OF

Near-Field Sturgeon Monitoring for the New NY Bridge at Tappan Zee. Quarterly Report July 1 September 30, 2014

Trip Report, Marine Mammal Monitoring Mine Neutralization Exercise Events, September 2012 VACAPES Range Complex

Jeopardy. Diving Acoustics Survey Misc. Q $100 Q $100 Q $100 Q $100 Q $200 Q $200 Q $200 Q $200 Q $300 Q $300 Q $300 Q $300

PAPER. Insights into the Underwater Diving, Feeding, and Calling Behavior of Blue Whales from a Suction-Cup- Attached Video-Imaging Tag (CRITTERCAM)

Caltrans compendium of underwater sound data from pile driving 2014 update

ASSESSMENT OF THE WEST COAST OF NEWFOUNDLAND (DIVISION 4R) HERRING STOCKS IN 2011

Effective beam pattern of the Blainville s beaked whale (Mesoplodon densirostris) and implications for passive acoustic monitoring

Chesapeake Bay. Sea - Seek. Ebook Sailing guide / Guide nautique. Chesapeake Bay. NW Atlantic Ocean - US - East coast

Note on the yearly catches by country and gear of the FISM (France Ivory Coast Senegal - Morocco) fleet during the period

Final Report Alaska Department of Fish and Game State Wildlife Grant T July 1, 2003 June 30, 2006:

OVERVIEW OF THE ITALIAN FLEET FISHING ALBACORE (THUNNUS ALALUNGA)

Marine Acoustics Monitoring Project 2016 Summary Report

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

Introduction to Density Estimation

FINAL REPORT. Using Digital Acoustic Recording Tags to Detect Marine Mammals on Navy Ranges and Study their Responses to Naval Sonar

Can we be as clever as a sperm whale?

Effect on Marine Life by Noise of Offshore Wind Farm S.JIANG 1 & J.P. HOU 1

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

SAMBAH

Variability of SCUBA diver s Acoustic Emission

FINAL REPORT. Robin W. Baird 1, Stephen W. Martin 2, Daniel L. Webster 1, and Brandon L. Southall 3

Abondance et diversité acoustique des populations de poissons dans la baie de Calvi.

Transcription:

Sci. Rep. Port-Cros natl. Park, 29: 127-134 (2015) Cuvier s beaked whale (Ziphius cavirostris) diving behavior as obtained by visual observation methods and consequences in terms of visual detection during surveys Alexandre GANNIER Groupe de Recherche sur les Cétacés, BP 715, 06633 Antibes cedex, France. Corresponding author: alexandre.gannier@sfr.fr Abstract. We studied Cuvier s beaked whale (Ziphius cavirostris) behavior in the northern Mediterranean Sea, using conventional boat-based survey methods, including a towed hydrophone array. Between 2007 and 2012, 18 ziphius groups were sighted with suitable weather and sea conditions and data were collected during 80 minutes in average for each group. The observed surface/dive sequences followed the beaked whales specific diving pattern, with feeding dives (61 minutes long in average) separated by series of breathing phases (178 secondes long in average) and non-feeding dives (12.2 minutes long average). Our results are consistent with those obtained worldwide with tagging techniques. Keywords: Ziphius cavirostris, Mediterranean Sea, behavior, boat survey, dive cycle. Résumé. Le comportement de plongée du Ziphius de Cuvier (Ziphius cavirostris) étudié par observation visuelle - Conséquences pour la détection visuelle durant les prospections. Nous avons étudié le comportement de groupes de Ziphius de Cuvier (Ziphius cavirostris) en Méditerranée nord-occidentale, à l aide de techniques classiques d observation, avec un bateau de 12 m équipé d un hydrophone remorqué. Entre 2007 et 2012, 18 groupes de ziphius ont été étudiés avec des conditions d observation adaptées et les données ont été collectées pendant 80 minutes en moyenne pour chaque groupe. Nous avons trouvé des cycles de sonde/surface classiques pour les ziphiidés: des sondes de prédation de 61 minutes en moyenne, entrecoupées de séquences de respirations (178 secondes en moyenne) et de sondes de récupération de 12.2 minutes en moyenne. Nos résultats sont comparables à ce qui a été déterminé dans plusieurs régions du monde grâce à des techniques de taggage. Mots-clés : Ziphius cavirostris, Méditerranée, comportement, prospection en mer, cycle de sonde. Introduction Ziphiids can easily be missed during visual and acoustic surveys because they spend the majority of their time underwater and are often unconspicuous while at the surface, and they only vocalize for some 20 % of their time (Aguilar de Soto et al., 2012). This causes problems 127

to estimate their abundance from visual and acoustic surveys, because the availability bias (derived from the proportion of time a whale is visible at the surface, or vocalizing) is high and difficult to determine (Barlow et al., 2006; 2013). This is also a conservation problem during military sonar operations since most mitigation techniques rely on the visual detection of whales (Dolman et al., 2009). Tagging experiments have been intensively used to evaluate the beaked whale surface availability and dive cycle (Tyack et al., 2006; Johnson et al., 2009). It was determined that beaked whales perform complex dive cycles, comprising one deep and long feeding dive (60 minutes or more), followed by a series of shorter and shallower non-feeding dives (typically less than 20 minutes). However, the tagging technique is not widely available and requires contact with cetaceans, which may alter cetacean behavior during one full dive, or more. To study Cuvier s beaked whale (Ziphius cavirostris) surface/dive cycles, conventional boat-based visual observation is also useful, as long as weather conditions enable continuous data collection. We studied the surfacedive cycles of Cuvier s beaked whales (CBW) in the northwestern Mediterranean from 2007 to 2012, using conventional sailboat observation techniques aided with a 32 khz or 48 khz bandwidth hydrophone system. Material and methods Our survey platform was a 12 meter sailboat, powered by a 75 hp auxiliary engine: while on search, an average speed of 2.5 m.s - 1 (5 knots) could be obtained under all weather conditions. This boat has been used for Groupe de Recherche sur les Cétacés since 1995, with towed hydrophones. Ziphius schools were located by sampling an area previously identified as favorable, mostly in the northern/central Tyrrhenian Sea (Gannier, 2011), using combined visual (four active observers) and acoustic techniques (100 m stereo towed hydrophone in 2007-2008, or 200 m in 2010-2012). Sampling was carried out only with wind equal to or less than Beaufort 2. The hydrophone and pre-amplifier bandwidth was 0.2-32 khz or 0.2-48 khz (respectively for 2007-2008 and 2010-2012) in order to be compatible with CBW feeding clicks frequency range: Johnson et al. (2004) determined the spectral energy to be maximal at 40 khz, but click power started below 20 khz for CBW. Once the whales were visually detected they were approached to a distance of about 300 m, and their surface/dive activity was observed and measured with binoculars and stopwatch. This focal follow lasted as long as possible in order to document successive surface and dive episodes. The hydrophone was used to determine 128

when the whales engaged in a deep feeding dive, as Tyack et al. (2006) showed that CBW usually only click when engaged in such a feeding dive. This technique proved efficient whenever the boat was static (no water flow noise) and the diving whale at less than 500 m horizontal distance. This field work was extremely demanding in terms of (fine) weather conditions. The whales were typically observed from a minimal distance of 200 m, hence minimizing the risk of natural behavior disruption. However, on some occasions, ziphius schools closed our sailboat during several minutes. Most surface/dive observations were carried out in the Tyrrhenian Sea between 2007 and 2012. Figure 1. Locations of Cuvier s beaked whale groups, between 2007 and 2012.These locations relate to CBW groups on which focal-follow observation was carried out. Results Because very good sea conditions were required to carry out this research, only 18 ziphius groups could be studied from 2007 to 2012 (Fig. 1), among which seven were monitored over a prolonged period (global average observation duration = 80.1 minutes). A total of 24 hours and 16 minutes were spent in monitoring from 2007 to 2012, including 12 hours and 19 minutes from 2010 to 2012. Among the ziphius groups observed during our behavior study, school size 129

averaged 2.4 (range 1-8). In large groups, the behavior timing was based on focal individuals, the most conspicuous. A total of 61 dives and 63 surface sequences were timed (Table I). Table I. Data set used for the surface/dive study (2007-2012). For feeding dives, numbers in brackets indicate dives for which no duration could be determined, because whale surfacing could not be observed. Date Hour School size Number of feeding dives Number of other dives Number of surface sequences 14/07/07 13:17 2 1 5 6 15/07/07 7:59 3 (1) 3 3 15/07/07 14:16 3 (1) 4 4 16/07/07 6:25 1 (1) 1 1 16/07/08 15:58 1 (1) 3 4 24/07/08 13:05 1 1 2 2 24/07/08 14:44 2 1 (1) 4 5 31/07/08 10:52 3 (1) 4 5 19/08/08 12:27 2 0 2 2 19/08/08 17:00 3 0 1 1 19/08/08 18:19 2 (1) 2 2 09/08/10 17:47 8 1 0 1 11/07/11 10:41 3 (1) 2 3 11/07/11 13:45 5 1 (1) 8 9 12/07/11 14:30 2 0 3 3 12/07/11 19:56 1 0 2 2 18/08/11 14:42 4 1 (1) 7 8 07/08/12 13:14 2 1 1 2 - - 7 (10) 54 63 The observed surface/dive sequences followed the beaked whales specific pattern, with long feeding dives separated by series of breathing phases and non-feeding dives (Fig. 2). An average of 5.7 non-feeding dives were performed between two successive feeding dives, as determined on three occasions. Feeding dives were 61 minutes long on average (SD = 11.2). Nonfeeding dives were 12.2 minutes long average (SD = 2.7) and were followed by breathing sequences lasting 178 s on average (SD = 89 s), with one breathing event every 10 s on average. Depending on group size and synchrony, whales were not always visible during breathing phases: based on two detailed timing follow-ups, ziphius groups were visible at the surface for 2 min during every 3 min breathing phase (about 2/3 of the duration of a breathing sequence). 130

In summary, we observed surface/dive cycles consisting in one 61 minute feeding dive, followed by 5 or 6 non-feeding dive/breathing phase sequences, each lasting 15.2 min, making a total cycle of 160 minutes in average (Fig. 2). Figure 2. An average Cuvier s beaked whale dive/surface cycle. Depth values are empirical, since they were not collected during our study. Assuming that ziphius were visible 2/3 of the time during their breathing phases, and taking average dive durations as determined in our study, CBW were available at the surface about 8.4 % of the time during a typical dive-surface cycle in the Mediterranean Sea. Discussion Our results are consistent with those obtained by Tyack et al. (2006) in the Ligurian Sea, with data from DTag experiments carried out on seven whales in 2003 and 2004 (Table II). Table II. Dive cycles of Ziphius in the Ligurian Sea as obtained from tagging experiments (Tyack et al., 2006). The code of the tagged whales is composed by the year and the Julian day of the tagging followed by a letter indicating the tagging sequence of the day. Numbers in brackets indicate standard deviations. Tagged whale code Average feeding dive duration (min) Average depth during feeding dives (m) Number of shallow dives between successive deep dives Mean interval between two deep dives (min) 2003 260a 50.3 824 - - 2003 263a 55.3 (12.8) 1145 0 61.3 (47.3) 2004 160a 84.5 1322 3 72.9 2004 161a 55.0 (6.4) 937 4 65.8 (19) 2004 161b 54.8 (4.9) 1065 3 56.9 (22) 2004 175a 67.9 (0.8) 1195 1 66.4 (32) 2004 179a 50.8 737 1 98.8 average 58.0 (11.4) 1070 2.2 63.4 (31) 131

For these authors, the average duration of a complete dive cycle is 121 minutes with an average of 2.2 shallow dives of 15.2 min mean duration. The difference with our results for average number of shallow dives may reflect the methodology: in our case, a whale was considered in shallow dive when it was no longer visible at the surface for several minutes, when for Tyack et al. (2006) a shallow dive was recorded whenever a whale reached an immersion higher than 20 meters. Then, very shallow dives may explain the difference between studies. This possibility is confirmed by Baird et al. (2006), from tagging experiments in Hawaii: the authors observed very shallow dive series for CBW: from limited samples, they found an inter-deepdive interval of about 2 hours, with 3 to 4 intermediate dives between two successive deep feeding dives. Southall et al. (2014) found higher number of intermediate dives during tagging experiments off southern California. From our results and the available literature, it is clear that CBW diving cycle can be variable, depending on location and other non-geographical factors. However, there are always intermediate dives between deep and long excursions, and their determination is necessary for estimating the surface availability of ziphiids. The probability of detecting ziphius on the track line, based on this availability, was found to be 0.08, close to the value of 0.07 expressed by Barlow et al. (2006) from other surface/dive data. This value is applicable in cases of non-limiting detectability conditions, i.e. calm sea and good light, and should be considered as a maximum value in near perfect visual detection conditions. Any degradation in sea state or light conditions would result in a further decrease of the above detection probability. Therefore, it is obvious that a true absence of CBW from a given location can hardly be verified from visual survey only. Conventional boat-based behavior studies of beaked whales require very fine wind and sea conditions, which were difficult to obtain during our research in the northwestern Mediterranean Sea. From 2010 to 2012, a total of nine weeks of survey time was allocated to the study, and seven focal follows were performed during 13 survey days with Beaufort 0-2 sea conditions. In terms of sighting rates, 21 whales were counted within nine days in the Tyrrhenian Sea (effort of 787 km), giving an average of 2.7 whale/100 km, and four ziphius were sighted in four days in the gulf of Genova (419 km of effort), resulting in 1.1 whale/100 km (Gannier, 2012). Higher sighting rates (4.7 ind./100 km) were previously obtained in the central Tyrrhenian Sea (Gannier, 2011). 132

Conclusion Boat-based visual observation provides an useful method to study beaked whales surface-dive sequences. However, it requires very favourable sea conditions and consequently a long survey duration, and an adequate survey platform. Based on our study, the availability bias of Cuvier s beaked whales during visual surveys is very strong, and such surveys deliver heavily down-biased estimates when this effect is not properly accounted for. The very low surface availability of Cuvier s beaked whales also implies that visual mitigation techniques are not sufficiently efficient to mitigate potential hazardous effects during intense sound source emissions, such as military sonars. Acknowledgements. This study was supported by a funding of Sanctuaire Pelagos Partie française. Thanks to the benevolents observers participating to GREC surveys. Thanks to anonymous reviewers providing suggestions to improve the manuscript. References AGUILAR DE SOTO N., MADSEN P.T., TYACK P., ARRANZ P., MARRERO J., FAIS A., REVELLI E., JOHNSON M., 2012. No shallow talk: Cryptic strategy in the vocal communication of Blainville s beaked whales. Mar. Mamm. Sci., 28: E75-E92. BAIRD R.W., WEBSTER D.L., MCSWEENEY D.J., LIGON A.D., SCHORR G.S., BARLOW J., 2006. Diving behaviour of Cuvier s and Blainville s beaked whales in Hawai i. Can. J. of Zool., 84: 1120-1128. BARLOW J., FERGUSON M.C., PERRIN W.F., BALLANCE L., GERRODETTE T., JOYCE G., MACLEOD C.D., MULLIN K., PALKA D.L., WARING G., 2006. Abundance and densities of beaked and bottlenose whales (family Ziphiidae). J. Cetacean Res. Manage. 7(3): 263-270. BARLOW J., TYACK P.L., JOHNSON M.P., BAIRD R.W., SCHORR G.S., ANDREWS R.D., AGUILAR DE SOTO N. 2013. Trackline and point detection probabilities for acoustic surveys of Cuvier s and Blainville s beaked whales. J. Acoust. Soc. Am., 134: 2486-2496. DOLMAN S.J., WEIR C.R., JASNY M., 2009. Comparative review of marine mammal guidance implemented during naval exercises. Mar. Pollut. Bull., 58: 465-477. GANNIER A., 2011. Using existing data and focused surveys to highlight Cuvier s beaked whales favourable areas : a case study in the central Tyrrhenian Sea. Mar. Pollut. Bul., 63: 10-17. GANNIER A., 2012. Le comportement du Ziphius (cycles de sonde et de surface) - La distribution du Ziphius dans le Sanctuaire Pelagos. Final report of study 10.059 83400PC: 1-66. JOHNSON M., MADSEN P.T., ZIMMER W.M.X., AGUILAR DE SOTO N., TYACK P.L., 2004. Beaked whales echolocate on prey. Proc. R. Soc. Lond. B (Suppl.), 271: S383-S386. JOHNSON M., AGUILAR DE SOTO N., MADSEN P.T., 2009. Studying the behaviour and sensory ecology of marine mammals using acoustic recording tags: a review. Mar. Ecol. Prog. Ser., 395: 55-73. 133

SOUTHALL B., CALAMBOKIDIS J., BARLOW J., MORETTI D., FRIEDLAENDER A., STIMPERT A., DOUGLAS A., SOUTHALL K., ARRANZ P., DERUITER S., HAZEN E., GOLDBOGEN J., FALCONE E., SCHORR G., 2014. Biological and behavioral response studies of marine mammals in Southern California, 2013. ( SOCAL 13 ). Final Project Report: 1--54. TYACK P.L., JOHNSON M., AGUILAR DE SOTO N., STURLESE A., MADSEN P.T., 2006. Extreme diving of beaked whales. J. Exp. Biol., 209 : 4238-4253. 134