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Acoustic Behaviors in Hawaiian Coral Reef Fish Communities

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Acoustic Behaviors in Hawaiian Coral Reef Fish Communities Vol. 511: 1–16, 2014 MARINE ECOLOGY PROGRESS SERIES Published September 24 doi: 10.3354/meps10930 Mar Ecol Prog Ser FREEREE FEATURE ARTICLE ACCESSCCESS Acoustic behaviors in Hawaiian coral reef fish communities Timothy C. Tricas1,2,*, Kelly S. Boyle1,2,3 1Department of Biology (formerly Zoology), 2538 The Mall, Edmondson Hall, University of Hawai’i at Manoa, Honolulu, HI 96822, USA 2Hawai’i Institute of Marine Biology, 46-007 Lilipuna Rd., Kane‘ohe, HI 96744, USA 3Present address: Département d’Ecologie et de Gestion de la Biodiversité, Muséum National d’Histoire Naturelle, 57 rue Cuvier, Case postale 55, 75231, Paris Cedex 5, France ABSTRACT: Coral reef fish communities often include hundreds of sympatric species which are of great inter- est to reef conservation and fisheries managers. Long- term acoustic monitoring of fish sounds can be used to infer periodic reproductive activity and changes in pop- ulation abundance. However, limited records of sound production by coral reef species have precluded the ap- plication of acoustic monitoring at the population or community levels. We used rebreather and digital acoustic/video techniques to produce a sound library for fishes on coral reefs of west Hawai’i Island, HI, USA. We documented 85 sounds produced by 45 (47%) of the 96 resident species that were associated with agonistic interactions and resource defense, reproduction, nest defense, feeding, and vigilance behaviors. Most non- feeding sounds consisted of single or trains of pulse Rebreather divers record sounds produced by coral reef fish events <100 ms long that were distributed across a during resource defense, reproduction, predator avoidance spectrum of <100 to 1000 Hz with the majority of peak and feeding for acoustic monitoring of population activities. frequencies between 100 and 300 Hz. Agonistic sounds Images: Timothy C. Tricas and Kelly S. Boyle created during competitive interactions over food, space, or nest brood resources were identified for dam- selfishes, surgeonfishes, butterflyfishes, and trigger- fishes, among others. Reproductive sounds associated with courtship, spawning, or nest defense were pro- INTRODUCTION duced by damselfishes, goatfishes, butterflyfishes, par- rotfishes, and surgeonfishes, as well as wrasses and Coral reef fish communities include sympatric pop- Moorish idols. The distinct adventitious feeding sounds ulations of hundreds of species that are concentrated recorded for some parrotfishes and triggerfishes oc- in small geographic areas (Allen & Werner 2002, curred in a higher frequency band (2−6 kHz) and may Bellwood & Wainwright 2002). Fish acoustic behav- be useful indicators of feeding activity and rates of reef iors are a prominent feature of coral reef environ- bioerosion. This is the first study to characterize the spe- cies-specific behavior soundscape that can be applied ments and provide a potential tool for monitoring and to acoustic monitoring of a coral reef fish community. management of fish populations. Many fish produce sounds during agonistic interactions with competi- KEY WORDS: Bioacoustics · Rebreather · Reef fish · tors, responses to predators or threats, and during Sound production · Fish behavior · Coral reef courtship and spawning (reviewed by Fine et al. Resale or republication not permitted without 1977, Myrberg 1981). Passive acoustic recordings of written consent of the publisher *Corresponding author: [email protected] © Inter-Research 2014 · www.int-res.com 2 Mar Ecol Prog Ser 511: 1–16, 2014 such species-specific sounds can provide valuable Lobel 1998, Lobel & Kerr 1999, Maruska et al. 2007), information on the onset, duration, and periodicity of 1 trunkfish (Lobel 1996), 2 wrasses (Boyle & Cox reproductive activities and changes in abundance of 2009), 3 butterflyfishes (Tricas et al. 2006, Boyle & local fish populations (Rountree et al. 2003a,b, 2006, Tricas 2010, 2011), and 1 triggerfish (Salmon et al. Luczkovich et al. 2008). However, despite the many 1968). The purpose of this study was to develop an thousands of fish species known to inhabit coral reefs acoustic library of the acoustic behavior of fish worldwide, sound production is currently described species on shallow Hawaiian coral reefs for future (or hypothesized to exist) for fewer than 300 species, use in the interpretation of long-term passive which represents a great underestimate (Lobel et al. acoustic monitoring data. We used closed-circuit 2010). Furthermore, the majority of coral reef fish rebreathers to closely approach visually identified sounds are anecdotal, qualitative, and lack infor - species and record sound production in synchrony mation on sound waveforms with few records taken with their natural behavior. Results show that ap- from sympatric populations (e.g. Steinberg et al. proximately half of the observed species produce 1965, Bright 1972). Thus, much work is needed to sound in biologically relevant contexts that may be adequately characterize sonic species, sound reper- used for identification of social interactions, repro- toires, acoustic features, and behavioral contexts duction, and activity patterns of species in Hawaiian that contribute to the soundscape of coral reef fish coral reef fish communities. communities. The application of sound libraries to passive acoustic monitoring of fish communities was previ- MATERIALS AND METHODS ously limited by several factors. In many cases, the bioacoustic capabilities of marine species are only Study locations partially characterized, and the identities of sonic species are often inferred, misidentified, or unknown Acoustic behaviors of fish were recorded at Puako (e.g. Steinberg et al. 1962, McCauley & Cato 2000, Reef on the island of Hawai’i (19.93° N, 155.86° W) Sprague & Luczkovich 2001, Mann & Jarvis 2004, during the spring and summer of 2008 and 2009. Anderson et al. 2008). For many coral reef species, This fish management area is characterized by large the behavioral context of specific sounds in wild fields of hard corals that slope to a reef edge at about populations is often unknown or incomplete (Fish & 15 m and extend steeply to a sand interface at about Mowbray 1970, Myrberg & Fuiman 2002, Lobel et al. 30 m. Many species engage in feeding and social 2010). One important feature of fish sounds is their interactions in the water column, near the reef sur- low-frequency spectrum (<50 Hz to several kHz) and face, on sand patches, and in caves. Large aggrega- competing background noise from wind, waves, and tions of fishes were observed in periodic broadcast other sources in this frequency band (Wenz 1962, spawning activities along the reef edge and deeper Cato 1980). The direct observation of bioacoustic slope areas. We also obtained some fish sounds at behaviors by scuba divers is limited by the ex- Papawai Bay in Kona, Hawai’i (19.64° N, 156.02° W), halant bubble noise and limited bottom time. This and the outer reefs of Kaneohe Bay and Honolulu affords a great advantage for the use of rebreather on the island of Oahu. life-support systems that produce no exhalant bubble noise and provide extended bottom time (Bright 1972, Lobel 2005, Radford et al. 2005) and also Dives and data recording for recent digi tal video/audio recording equipment and analysis software. These technological enhance- Divers used Evolution (Ambient Pressure Diving) ments now facilitate the creation of species-specific closed-circuit rebreathers that do not release exhaust and context-specific acoustic libraries for coral reef bubbles that interfere with acoustic recordings, fish communities. extend bottom time up to 3 h, and allow very close More than 600 species of marine fishes inhabit the approach to fish. Most dives were conducted at 8 to inshore and reef areas of Hawai’i, HI, USA (Randall 40 m depth with 1 decompression excursion to rocky 2007), but details of sound production (waveforms, outcroppings at 80 m. Acoustic behaviors were re - intensity, frequency spectra) are reported for only a corded with digital video cameras (Sony TRV-950 few species: 2 soldierfish Myripristis spp. (Salmon and Canon Optura) in Amphibico underwater 1967); 2 bigeyes Priacanthus spp. (Salmon & Winn housings equipped with an external hydrophone 1966); 3 damselfishes (Lobel & Mann 1995, Mann & (HTI min96 High-Tech) that recorded coincident Tricas & Boyle: Coral reef fish community acoustics 3 sounds on 1 audio channel (48 kHz sample rate, event train that consisted of a series of sound events 20−24 000 Hz audio band pass). Dives were con- (such as single pulses in series or growls with short ducted between 09:00 and 19:30 h and were often silent intervals between portions of the overall scheduled to observe spawning behaviors in the sound) separated by inter-event intervals <0.5 s. For afternoon, dusk, or on outgoing tides. We evoked sound event trains (most commonly pulse trains), the aggressive sounds from the normally shy coral- total number of separate wave events (events or feeding blue-eye damselfish Plectroglyphidodon john- pulses train−1) was first enumerated. The onset and stonianus by placement of a coral-feeding multiband offset times of the first 4 events (or the entire train butterflyfish Chaetodon multicinctus within a glass if ≤4 wave events) were then measured for calcula- bottle near the territory. The animal use protocol was tion of (1) mean event duration, (2) event train seg- approved by the University of Hawai’i Institutional ment duration (for entire trains with 2 to 4 events or Animal Care and Use Committee. the first 4 events in longer trains), (3) event rate s−1, and (4) mean inter-event interval. Previously unreported sounds were first assigned a Video and acoustic analyses descriptive name type based primarily on its acoustic features (e.g. pulse, high-frequency pulse, blended Digital video recordings were imported to a com- pulse, half-pulse) in order to avoid onomatopoeias puter in the lab with Windows Movie Maker and and anthropomorphic interpretations that have added saved as an uncompressed AVI file. The entire video to the great non-uniformity of sound nomenclature in and audio recordings were then pre-screened indi- the literature as reviewed by Lobel et al.
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