Sound production in wild Mediterranean blonde ray Raja brachyura

IF 4.4 2区 环境科学与生态学 Q1 ECOLOGY Ecology Pub Date : 2024-10-07 DOI:10.1002/ecy.4440
Adèle Barroil, Julie Deter, Florian Holon, Frédéric Bertucci
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Based on approximation, half of the fish families of coral reefs for example have at least one known sound producing species (Parmentier et al., <span>2021</span>). Sound production is therefore a key behavioral feature of bony fish, and the ever-increasing number of reports on sound production in various species and contexts continues to highlight this important aspect (Amorim, <span>2006</span>; Ladich &amp; Schulz-Mirbach, <span>2016</span>).</p><p>In comparison, evidence for active sound production in elasmobranchs (cartilaginous fish), that is, sharks, rays, and skates, remains scarce (Looby et al., <span>2022</span>). The first case of active sound production was reported more than 50 years ago in captive cownose rays <i>Rhinoptera bonasus</i> which produced clicks as a result of human harassment (Fish &amp; Mowbray, <span>1970</span>). Subsequently there have been no proven and confirmed examples of active sound production in any species of elasmobranchs. Although recently, Fetterplace, Esteban, et al. (<span>2022</span>) reported the first evidence of active sound production in two species of stingray, that is, the mangrove whipray <i>Urogymnus granulatus</i> (Macleay 1883) and the cowtail stingray <i>Pastinachus ater</i> (Macleay 1883), recorded in the wild in Indonesia and Australia. Both species produced a series of short broadband loud clicks in response to an observer's approach and ceased producing sound when the distance with the observer increased. This founding paper therefore paved the way and encouraged further research on sound production in elasmobranchs. Here we present the first evidence of active sound production in a new species, that is, the blonde ray <i>Raja brachyura</i> (Lafont 1873) opportunistically recorded off the coast of Corsica in the Mediterranean (Figure 1).</p><p>Sound was extracted from a video recording made on 30 March 2023 with a Hero 8 Black action camera (GoPro, Inc., USA) placed at the end of a rope and lowered at −40 m depth from a boat in the first instance in order to find <i>Spicara smaris</i> (L. 1758) spawning grounds off the eastern coast of Corsica (42°14.720′ N; 9°35.330′ E). <i>S. smaris</i> males build their nest on soft bottoms seabed. Spawning ground covers large areas (2.2–28 ha) from the lower limit of <i>Posidonia oceanica</i> (Delile 1813) seagrass meadows to near −50 m depth (Andromède océanologie, <span>2023</span>, <span>2024</span>; Deter et al., <span>2024</span>). This video was therefore captured in this zone, over a substrate made of coarse sand. When touching the ground, and after an initial move to the left, the camera landed next to a first individual whose pectoral fin could be seen while another individual is visible in the distance. In a second movement, the camera is moved between these two individuals and a series of high-pitched pulses can be heard as the substrate is agitated. As the gravel settles, the camera is moved again and an individual that was standing near the camera flees. Three individuals present in the area were observed when the camera finally moved away (Barroil, <span>2024</span>). No other species were observed on the video. The sound track was digitized at 44.1 kHz (16-bit resolution) using Goldwave v6.80 (Goldwave Inc) and analyzed with RavenPro 1.6.5 software (The Cornell Lab of Ornithology, Ithaca, NY). A band-pass filter between 20 Hz and 15 kHz was applied. Sound consisted of a series of pulses, and the following acoustic features were measured: the sound duration (from the beginning of the first pulse to the end of the last pulse), the number of pulses in the sound, the pulse duration, the pulse period (peak-to-peak interval between two consecutive pulses), and the dominant frequency of the pulses (Figure 2). Temporal features were measured from oscillograms, whereas frequencies were obtained from power spectra (Fast Fourier Transform FFT, 1024 points, Hamming window, no overlap). The sound lasted 5.86 s and was made of a series of 11 pulses which lasted 0.015 ± 0.003 s (mean ± SD; min–max = 0.010–0.020 s) with a pulse period of 0.58 ± 0.10 s (0.50–0.83 s). The pulses' dominant frequency was 6.93 ± 0.26 kHz (6.28–7.22 kHz) (Figure 2).</p><p>Despite <i>R. brachyura</i> not being visible when the sound was recorded, the sound is similar to the ones already reported in <i>U. granulatus</i> in terms of pulse duration, that is, 0.010–0.025 s and number of pulses within a series, that is, 5–11 pulses. Sound frequency appears higher than in both <i>U. granulatus</i> and <i>P. ater</i>, which showed frequencies ranging from 1031 to 1875 Hz, and from 1406 to 1500 Hz, respectively (Figure 3). In addition, this sound is different from boat noise that could be heard and clearly identified on the video when the clutch is engaged (BN, Figure 2). It is also unlikely that the sound results from the movement and fall of the camera, which continues to be shaken or hit the substrate after the rays have left without any sound being detected. We are therefore confident in stating that this sound was indeed produced by the blonde ray.</p><p>Subsequently to our observations, similar soniferous behaviors were observed later in 2023 in two other batoid species in the Mediterranean, that is, the rough skate <i>Raja radula</i> (Delaroche 1809) and the marbled electric ray <i>Torpedo marmorata</i> (Risso 1810) (Rodriguez &amp; Barría, <span>2024</span>). Sounds also consist of series of broadband clicks lasting 0.025–0.082 s with a mean peak frequency of 3146 Hz in <i>R. radula</i>, and lasting 0.004–0.013 s with a peak frequency of 8387 Hz in <i>T. marmorata</i>.</p><p>Elasmobranchs are sensitive to frequencies between 40 and 1500 Hz, with peak sensitivities between 200 and 400 Hz (Chapuis &amp; Collin, <span>2022</span>; Mickle et al., <span>2020</span>; Myrberg, <span>2001</span>; Parmentier et al., <span>2020</span>). While the high frequency of <i>R. brachyura</i>'s sound may fall outside its hearing range, suggesting this signal is intended to other species (e.g., marine mammals), the large bandwidth of the sound spans the hearing range of elasmobranchs which may allow conspecifics or predators (e.g., sharks) to hear this sound. As in the mangrove whipray and the cowtail stingray, sound production in the blonde ray is probably related to the warning of conspecifics present in the area or intended to repel a threat. In <i>U. granulatus</i> and <i>P. ater</i>, conspecifics have been observed to approach the emitter in response to sound and to flee from divers (Fetterplace, Esteban, et al., <span>2022</span>). Likewise, in the rough skate and the marbled electric ray, sound production was presumably associated with agonistic displays directed toward the divers when they were close (Rodriguez &amp; Barría, <span>2024</span>). Many sharks are known to respond to sounds, either being attracted by the sounds produced by preys or being repelled by the sounds of their predators (e.g., Chapuis et al., <span>2019</span>; Gardiner et al., <span>2012</span>; Myrberg, <span>2001</span>). Besides the fleeing behavior of what may be the sound-producing individual, one individual could subsequently be observed to come quickly close to the camera. Divers also reported being “charged” by rays (<i>Raja</i> sp.) or by common smooth-hounds <i>Mustelus mustelus</i> (L. 1758) when they hit a metallic post with a hammer (Holon, personal observation). This may align with the fact that free-ranging sharks were attracted to broadband and irregularly pulsed sounds (which may become repulsive when transmitted with a sudden 20-dB increase or more in intensity) (Myrberg, <span>2001</span>). Finally, in Fetterplace, Esteban, et al. (<span>2022</span>), sound production was associated with movements of the spiracles and cranial area, while in Rodriguez and Barría (<span>2024</span>), clicks were produced when individuals open and closed their mouths, accompanied by the movement of their pectoral fins. Unfortunately, the present sound production event could not be captured on film. Further observations may thus help to clarify both the emitter's behavior (e.g., sound production mechanism) and the behavioral response of the receivers (e.g., auditory capacities and social role of sound).</p><p>Further standardized recordings with proper hydrophones are required to better describe sound signals and their social role in elasmobranchs. The present paper as well as those of Fetterplace, Esteban, et al. (<span>2022</span>) and Rodriguez and Barría (<span>2024</span>) highlight the usefulness of using passive acoustic monitoring in biodiversity assessment and management plans as it may provide valuable information on a so far overlooked portion of bioacoustic diversity in fish.</p><p>Video contribution was made by Adèle Barroil and Julie Deter. The original draft was written by Adèle Barroil and Frédéric Bertucci, with further review and editing by Julie Deter and Florian Holon. Analysis of the video and sounds was made by Frédéric Bertucci.</p><p>The authors declare no conflicts of interest.</p>","PeriodicalId":11484,"journal":{"name":"Ecology","volume":"105 11","pages":""},"PeriodicalIF":4.4000,"publicationDate":"2024-10-07","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1002/ecy.4440","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Ecology","FirstCategoryId":"93","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1002/ecy.4440","RegionNum":2,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ECOLOGY","Score":null,"Total":0}
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Abstract

Sound production, or soniferous behavior, is linked to an active and intentional communication process between individuals of the same or different species, rather than being a by-product of activities like feeding or locomotion (i.e., incidental sounds). In ray-finned fishes (Actinopterygii), a clade comprising 34,200 species (Froese & Pauly, 2019) from 488 families (Fricke et al., 2019), sound production has independently evolved approximately 33 times, encompassing nearly 29,000 species (Rice et al., 2022). More precisely, intentional sound production has been identified in 989 bony fish species, belonging to 133 families and 33 orders (Looby et al., 2022; Rice et al., 2022). Based on approximation, half of the fish families of coral reefs for example have at least one known sound producing species (Parmentier et al., 2021). Sound production is therefore a key behavioral feature of bony fish, and the ever-increasing number of reports on sound production in various species and contexts continues to highlight this important aspect (Amorim, 2006; Ladich & Schulz-Mirbach, 2016).

In comparison, evidence for active sound production in elasmobranchs (cartilaginous fish), that is, sharks, rays, and skates, remains scarce (Looby et al., 2022). The first case of active sound production was reported more than 50 years ago in captive cownose rays Rhinoptera bonasus which produced clicks as a result of human harassment (Fish & Mowbray, 1970). Subsequently there have been no proven and confirmed examples of active sound production in any species of elasmobranchs. Although recently, Fetterplace, Esteban, et al. (2022) reported the first evidence of active sound production in two species of stingray, that is, the mangrove whipray Urogymnus granulatus (Macleay 1883) and the cowtail stingray Pastinachus ater (Macleay 1883), recorded in the wild in Indonesia and Australia. Both species produced a series of short broadband loud clicks in response to an observer's approach and ceased producing sound when the distance with the observer increased. This founding paper therefore paved the way and encouraged further research on sound production in elasmobranchs. Here we present the first evidence of active sound production in a new species, that is, the blonde ray Raja brachyura (Lafont 1873) opportunistically recorded off the coast of Corsica in the Mediterranean (Figure 1).

Sound was extracted from a video recording made on 30 March 2023 with a Hero 8 Black action camera (GoPro, Inc., USA) placed at the end of a rope and lowered at −40 m depth from a boat in the first instance in order to find Spicara smaris (L. 1758) spawning grounds off the eastern coast of Corsica (42°14.720′ N; 9°35.330′ E). S. smaris males build their nest on soft bottoms seabed. Spawning ground covers large areas (2.2–28 ha) from the lower limit of Posidonia oceanica (Delile 1813) seagrass meadows to near −50 m depth (Andromède océanologie, 2023, 2024; Deter et al., 2024). This video was therefore captured in this zone, over a substrate made of coarse sand. When touching the ground, and after an initial move to the left, the camera landed next to a first individual whose pectoral fin could be seen while another individual is visible in the distance. In a second movement, the camera is moved between these two individuals and a series of high-pitched pulses can be heard as the substrate is agitated. As the gravel settles, the camera is moved again and an individual that was standing near the camera flees. Three individuals present in the area were observed when the camera finally moved away (Barroil, 2024). No other species were observed on the video. The sound track was digitized at 44.1 kHz (16-bit resolution) using Goldwave v6.80 (Goldwave Inc) and analyzed with RavenPro 1.6.5 software (The Cornell Lab of Ornithology, Ithaca, NY). A band-pass filter between 20 Hz and 15 kHz was applied. Sound consisted of a series of pulses, and the following acoustic features were measured: the sound duration (from the beginning of the first pulse to the end of the last pulse), the number of pulses in the sound, the pulse duration, the pulse period (peak-to-peak interval between two consecutive pulses), and the dominant frequency of the pulses (Figure 2). Temporal features were measured from oscillograms, whereas frequencies were obtained from power spectra (Fast Fourier Transform FFT, 1024 points, Hamming window, no overlap). The sound lasted 5.86 s and was made of a series of 11 pulses which lasted 0.015 ± 0.003 s (mean ± SD; min–max = 0.010–0.020 s) with a pulse period of 0.58 ± 0.10 s (0.50–0.83 s). The pulses' dominant frequency was 6.93 ± 0.26 kHz (6.28–7.22 kHz) (Figure 2).

Despite R. brachyura not being visible when the sound was recorded, the sound is similar to the ones already reported in U. granulatus in terms of pulse duration, that is, 0.010–0.025 s and number of pulses within a series, that is, 5–11 pulses. Sound frequency appears higher than in both U. granulatus and P. ater, which showed frequencies ranging from 1031 to 1875 Hz, and from 1406 to 1500 Hz, respectively (Figure 3). In addition, this sound is different from boat noise that could be heard and clearly identified on the video when the clutch is engaged (BN, Figure 2). It is also unlikely that the sound results from the movement and fall of the camera, which continues to be shaken or hit the substrate after the rays have left without any sound being detected. We are therefore confident in stating that this sound was indeed produced by the blonde ray.

Subsequently to our observations, similar soniferous behaviors were observed later in 2023 in two other batoid species in the Mediterranean, that is, the rough skate Raja radula (Delaroche 1809) and the marbled electric ray Torpedo marmorata (Risso 1810) (Rodriguez & Barría, 2024). Sounds also consist of series of broadband clicks lasting 0.025–0.082 s with a mean peak frequency of 3146 Hz in R. radula, and lasting 0.004–0.013 s with a peak frequency of 8387 Hz in T. marmorata.

Elasmobranchs are sensitive to frequencies between 40 and 1500 Hz, with peak sensitivities between 200 and 400 Hz (Chapuis & Collin, 2022; Mickle et al., 2020; Myrberg, 2001; Parmentier et al., 2020). While the high frequency of R. brachyura's sound may fall outside its hearing range, suggesting this signal is intended to other species (e.g., marine mammals), the large bandwidth of the sound spans the hearing range of elasmobranchs which may allow conspecifics or predators (e.g., sharks) to hear this sound. As in the mangrove whipray and the cowtail stingray, sound production in the blonde ray is probably related to the warning of conspecifics present in the area or intended to repel a threat. In U. granulatus and P. ater, conspecifics have been observed to approach the emitter in response to sound and to flee from divers (Fetterplace, Esteban, et al., 2022). Likewise, in the rough skate and the marbled electric ray, sound production was presumably associated with agonistic displays directed toward the divers when they were close (Rodriguez & Barría, 2024). Many sharks are known to respond to sounds, either being attracted by the sounds produced by preys or being repelled by the sounds of their predators (e.g., Chapuis et al., 2019; Gardiner et al., 2012; Myrberg, 2001). Besides the fleeing behavior of what may be the sound-producing individual, one individual could subsequently be observed to come quickly close to the camera. Divers also reported being “charged” by rays (Raja sp.) or by common smooth-hounds Mustelus mustelus (L. 1758) when they hit a metallic post with a hammer (Holon, personal observation). This may align with the fact that free-ranging sharks were attracted to broadband and irregularly pulsed sounds (which may become repulsive when transmitted with a sudden 20-dB increase or more in intensity) (Myrberg, 2001). Finally, in Fetterplace, Esteban, et al. (2022), sound production was associated with movements of the spiracles and cranial area, while in Rodriguez and Barría (2024), clicks were produced when individuals open and closed their mouths, accompanied by the movement of their pectoral fins. Unfortunately, the present sound production event could not be captured on film. Further observations may thus help to clarify both the emitter's behavior (e.g., sound production mechanism) and the behavioral response of the receivers (e.g., auditory capacities and social role of sound).

Further standardized recordings with proper hydrophones are required to better describe sound signals and their social role in elasmobranchs. The present paper as well as those of Fetterplace, Esteban, et al. (2022) and Rodriguez and Barría (2024) highlight the usefulness of using passive acoustic monitoring in biodiversity assessment and management plans as it may provide valuable information on a so far overlooked portion of bioacoustic diversity in fish.

Video contribution was made by Adèle Barroil and Julie Deter. The original draft was written by Adèle Barroil and Frédéric Bertucci, with further review and editing by Julie Deter and Florian Holon. Analysis of the video and sounds was made by Frédéric Bertucci.

The authors declare no conflicts of interest.

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地中海野生金鳐鱼 Raja brachyura 的声音产生。
声音频率似乎比 U. granulatus 和 P. ater 都要高,后者的频率分别为 1031 至 1875 Hz 和 1406 至 1500 Hz(图 3)。此外,这种声音不同于离合器接合时可听到并可在视频中清晰辨别的船声(BN,图 2)。这种声音也不太可能是摄像机的移动和掉落造成的,因为摄像机在鳐鱼离开后仍在继续晃动或撞击底层,而没有探测到任何声音。因此,我们有信心指出,这种声音确实是由金魟发出的。在我们的观察之后,2023 年在地中海的另外两种蝠鲼,即粗鳐 Raja radula(Delaroche 1809)和大理石纹电鳐 Torpedo marmorata(Risso 1810)身上也观察到了类似的发声行为(Rodriguez &amp; Barría, 2024)。鳐鱼的声音也由一系列宽带咔嗒声组成,持续时间为 0.025-0.082 秒,平均峰值频率为 3146 赫兹;鱼雷的声音持续时间为 0.004-0.013 秒,峰值频率为 8387 赫兹。虽然蛙声的高频率可能在其听力范围之外,这表明该信号是向其他物种(如海洋哺乳动物)发出的,但声音的大带宽跨越了鞘鳃类的听力范围,这可能使同类或捕食者(如鲨鱼)听到这种声音。与红树林鞭魟和牛尾魟一样,金魟发出的声音可能与警告该区域存在的同类或驱赶威胁有关。在 U. granulatus 和 P. ater 中,已观察到同种鱼类在听到声音后会靠近发射器,并逃离潜水者(Fetterplace、Esteban 等人,2022 年)。同样,在粗鳐鱼和大理石纹电鳐鱼中,当潜水员靠近时,声音的产生可能与针对潜水员的攻击行为有关(Rodriguez &amp; Barría, 2024)。众所周知,许多鲨鱼会对声音做出反应,要么被猎物发出的声音所吸引,要么被捕食者的声音所驱赶(例如,Chapuis 等人,2019 年;Gardiner 等人,2012 年;Myrberg,2001 年)。除了可能是发声个体的逃离行为外,随后还观察到一只个体快速靠近摄像机。潜水员还报告说,当他们用锤子敲打金属柱时,鳐鱼(Raja sp.)或普通平滑猎犬 Mustelus mustelus(L. 1758)也会 "充电"(Holon,个人观察)。这可能与自由活动的鲨鱼会被宽带和不规则脉冲声音吸引的事实一致(当声音强度突然增加 20 分贝或更多时,可能会变得具有排斥性)(Myrberg,2001 年)。最后,在 Fetterplace、Esteban 等人(2022 年)的研究中,声音的产生与脊柱和颅骨区域的运动有关,而在 Rodriguez 和 Barría(2024 年)的研究中,当个体张开和闭合嘴巴时会产生咔嗒声,同时伴随着胸鳍的运动。遗憾的是,目前的发声过程未能被拍摄下来。因此,进一步的观察可能有助于澄清发声者的行为(如发声机制)和受声者的行为反应(如听觉能力和声音的社会作用)。本论文以及 Fetterplace、Esteban 等人(2022 年)和 Rodriguez、Barría 等人(2024 年)的论文都强调了在生物多样性评估和管理计划中使用被动声学监测的实用性,因为它可以提供有关鱼类生物声学多样性中迄今被忽视的部分的有价值信息。原稿由 Adèle Barroil 和 Frédéric Bertucci 撰写,Julie Deter 和 Florian Holon 进一步审阅和编辑。视频和声音分析由 Frédéric Bertucci 完成。作者声明无利益冲突。
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来源期刊
Ecology
Ecology 环境科学-生态学
CiteScore
8.30
自引率
2.10%
发文量
332
审稿时长
3 months
期刊介绍: Ecology publishes articles that report on the basic elements of ecological research. Emphasis is placed on concise, clear articles documenting important ecological phenomena. The journal publishes a broad array of research that includes a rapidly expanding envelope of subject matter, techniques, approaches, and concepts: paleoecology through present-day phenomena; evolutionary, population, physiological, community, and ecosystem ecology, as well as biogeochemistry; inclusive of descriptive, comparative, experimental, mathematical, statistical, and interdisciplinary approaches.
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