- 1Faculty of Marine Sciences, University of Kyrenia, Girne, Turkish Republic of North Cyprus (TRNC), Türkiye
- 2Fisheries Faculty, Firat University, Elazig, Türkiye
Editorial on the Research Topic
The biology and conservation of elasmobranchs and chimaeras
Encompassing a staggering array of species, elasmobranchs (sharks and rays) and chimaeras are ecologically vital creatures that have long played an important role in maintaining healthy marine ecosystems. Hailed by some as God-like creatures (Baughman, 1948), they have been feared by others due to their negative portrayal throughout history. Unfortunately, as is the case with many aquatic species, in recent years climate change, anthropogenic pressures, and habitat degradation have significantly threatened their populations. On top of this, their life traits and opportunistic feeding behaviors make them vulnerable to commercial fishing (Bengil and Basusta, 2018). As a result, today many species are endangered, some are data-deficient or nearly extinct and urgently need knowledge for their conservation (Dulvy et al., 2014, 2021). Sadly, the IUCN has already declared the first elasmobranch, Urolophus javanicus (Martens, 1864), the Java Stingaree, as extinct due to human activities (Constance et al., 2023). Therefore, producing information on elasmobranchs through scientific sampling or contemporary approaches, is crucial. Any contribution to their biology, ecology, distribution, migration and many other aspects is essential knowledge that will provide a basis for action, globally, regionally or locally.
But at what cost?
Conventionally, the methodologies commonly used to produce scientific information are mostly lethal but effective (Heupel and Simpfendorfer, 2010) and “convenient”. However, does this justify lethal sampling? Traditionally, the primary objective of the majority of studies is not conservation but simply to produce scientific information. Such efforts target a few charismatic species, resulting in the “neglect” of Data-Deficient species while overstressing the focused populations (Ducatez, 2019). A recent study by Ducatez (2019) analyzed research efforts on 509 shark species, showing biases toward subjects, taxa, and species, and shedding some light on species and areas in urgent need of information. In addition to correctly addressing information gaps and planning “efficient” sampling -with minimal sample size but high information yield-, studies like this can minimize the pressure of lethal scientific sampling. Utilizing bycaught individuals can provide “samples” for further biological examinations if retained (Wosnick et al.), and if alive when released could provide ecological information. Such opportunistic sampling has proven effective in some aspects of species physiology and bioecology, but has its pros and cons (Braccini et al., 2006; Bengil, 2020; Rosa et al.).
Is there any other way?
The diversity of elasmobranchs is increasing relatively quickly with new discoveries (Randhawa et al., 2015). Smartphones and the “to post” have provided a new digital database for scientists (Eryasar and Saygu, 2022) and aided these discoveries. People, whether members of the public, recreational divers, or fishermen, are eager to share on social media what they have observed, seen, or caught (Kabasakal and Bilecenoglu, 2020; Boldrocchi and Storai, 2021; Eryasar and Saygu, 2022; Saltzman et al., 2022; O’Keefe et al.). These “posts” reveal public perception, species distribution, morphology (in some cases), evidence of predation, or basically presence (Barnes et al., 2016; Roemer et al., 2016; Kabasakal and Bilecenoglu, 2020; Bengil et al., 2021; Boldrocchi and Storai, 2021; Saltzman et al., 2022). Additionally, utilizing local ecological knowledge (LEK) from fishers or on-board observations can provide information on reproduction, aggregation areas, general ideas about population trends, etc (Bengil, 2020; O’Keefe et al.). Citizen science, leveraging LEK and social media, is now pinpointing critical habitats for endangered species, like the recent discovery of new areas for guitarfish in the eastern Mediterranean (Bengil et al., 2018; Giovos et al., 2018; Bengil et al., 2020). Studies utilizing local news alongside social media and LEK have effectively tracked species biodiversity, status, habitat use, and public perception (Roemer et al., 2016; Kabasakal and Bilecenoglu, 2020; Boldrocchi and Storai, 2021; Papageorgiou et al., 2022; Saltzman et al., 2022, Rosa et al., O’Keefe et al.). Saltzman et al. (2022) have emphasized how social media posts have helped raise awareness of endangered elasmobranch species that have had conservation efforts implemented, which would otherwise have been unknown or less known. Data mining is also a good method to understand population status, trends, and shifts in addition to compiling, analyzing, and simplifying classic sources (Tsikliras and Stergiou, 2014; Colloca et al., 2017; Carpenter et al.).
One of the recently practiced non-invasive manual methods, which can also easily be performed by fishermen, is returning egg cases that have live embryos (Hof et al., 2018). This can provide information on the egg-laying grounds of some egg-laying species. Additionally, researchers have altered technologies or developed methodologies to determine maturity to provide information on reproductive status such as pregnancy without harming the individual (Carrier et al., 2003; Awruch et al., 2008; McMillan et al., 2019; Campbell et al.; Hoyos-Padilla et al.) or from carefully stored samples (Anderson et al.). Acoustic monitoring (Simpfendorfer and Heupel, 2004), photo identification (Meekan et al., 2006), mark-recapture (Simpfendorfer et al., 2008), baited remote underwater video surveys (Brooks et al., 2011), mucus swabs for genetic sampling (Lieber et al., 2013), and diet composition identification with DNA metabarcoding from cloacal swabs (van Zinnicq Bergmann et al., 2021) are some other non-lethal methodologies.
On the other hand, the importance of scientific surveys cannot be disregarded because of their analytic value; however, we should keep our minds open to such contemporary approaches and possible new technological integrations. Nonetheless now more than ever these types of contemporary approaches for biological or ecological information are important as scientific surveys, are a destructive methodology in terms of fishing operations, in addition to being logistically difficult to obtain and expensive (Bengil and Basusta, 2018; Bengil, 2020). Furthermore, given their continued commercial value, there is an opportunity to test and refine new contemporary approaches in locations where they are fished sustainably. Local or regional knowledge gaps can be reduced by supplementing gathered knowledge with different data sources, allowing conservation measures or management plans to be implemented more quickly.
Author contributions
EB: Conceptualization, Methodology, Visualization, Writing – original draft, Writing – review & editing. NB: Conceptualization, Writing – original draft, Writing – review & editing.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
References
Awruch C. A., Frusher S. D., Pankhurst N. W., Stevens J. D. (2008). Non-lethal assessment of reproductive characteristics for management and conservation of sharks. Mar. Ecol. Progress Series 355, 277–285.
Barnes M. L., Lynham J., Kalberg K., Leung P. (2016). Social networks and environmental outcomes. Proc. Natl. Acad. Sci. 113, 6466–6471. doi: 10.1073/pnas.1523245113
Baughman J. L. (1948). Sharks, sawfishes, and rays: their folklore. Am. Midland Nat. 39, 373–381. doi: 10.2307/2421591
Bengil E. G. T., Başusta A., Başusta N. (2018). Length-weight relationships of Glaucostegus cemiculus (Geoffroy Saint-Hilaire, 1817) from the Aegean Sea and northeastern Mediterranean coasts of Turkey. J. Black Sea/Mediterranean Environment, 24 (1), 1–9.
Bengil E. G. T., Bengil F., Ozaydin O. (2020). Feeding ecology and reproduction biology of Glaucostegus cemiculus (Geoffroy Saint-Hilaire, 1817) from the eastern Aegean Sea. Regional Stud. Mar. Sci. 33, 100952. doi: 10.1016/j.rsma.2019.100952
Bengi̇l E. G. T., Godley B. J., Gillham R. L., Hood A. R., Snape R. (2021). “Mediterranean angel sharks: subRegional action plan (SubRAP) GSA 25* (Cyprus – Northern Cyprus),” in Mediterranean angel sharks: sub-regional action plans. Plymouth, UK: The Shark Trust.
Bengil E. (2020). Can opportunistic methodologies provide information on elasmobranchs? A case study from Seas around Turkey. J. Wildlife Biodiversity 4, 68–77. doi: 10.22120/jwb.2020.136094.1185
Bengil E. G. T., Basusta N. (2018). Chondrichthyan species as by-catch: A review on species inhabiting Turkish waters. J. Black Sea/Mediterranean Environ. Vol. 24 No. 3, 288–305.
Boldrocchi G., Storai T. (2021). Data-mining social media platforms highlights conservation action for the Mediterranean Critically Endangered blue shark Prionace glauca. Aquat. Conservation: Mar. Freshw. Ecosyst. 31, 3087–3099. doi: 10.1002/aqc.3690
Braccini J. M., Gillanders B. M., Walker T. I. (2006). Determining reproductive parameters for population assessments of chondrichthyan species with asynchronous ovulation and parturition: piked spurdog (Squalus megalops) as a case study. Mar. Freshw. Res. 57, 105–119. doi: 10.1071/MF05076
Brooks E. J., Sloman K. A., Sims D. W., Danylchuk A. J. (2011). Validating the use of baited remote underwater video surveys for assessing the diversity, distribution and abundance of sharks in the Bahamas. Endangered Species Res. 13, 231–243. doi: 10.3354/esr00331
Carrier J. C., Murru F. L., Walsh M. T., Pratt Jr H. L. (2003). Assessing reproductive potential and gestation in nurse sharks (Ginglymostoma cirratum) using ultrasonography and endoscopy: an example of bridging the gap between field research and captive studies. Zoo Biology: Published in affiliation with the American Zoo and Aquarium Association 22 (2), 179–187.
Colloca F., Enea M., Ragonese S., Di Lorenzo M. (2017). A century of fishery data documenting the collapse of smooth-hounds (Mustelus spp.) in the Mediterranean Sea. Aquat. Conservation: Mar. Freshw. Ecosyst. 27, 1145–1155. doi: 10.1002/aqc.2789
Constance J., Ebert D. A., Finucci B., Simeon B., Kyne P. M. (2023).Urolophus javanicus. In: The IUCN red list of threatened species (Accessed 28 December 2023).
Ducatez S. (2019). Which sharks attract research? Analyses of the distribution of research effort in sharks reveal significant non-random knowledge biases. Rev. Fish Biol. Fisheries 29, 355–367. doi: 10.1007/s11160-019-09556-0
Dulvy N. K., Fowler S. L., Musick J. A., Cavanagh R. D., Kyne P. M., Harrison L. R., et al. (2014). Extinction risk and conservation of the world’s sharks and rays. elife 3, e00590. doi: 10.7554/eLife.00590
Dulvy N. K., Pacoureau N., Rigby C. L., Pollom R. A., Jabado R. W., Ebert D. A., et al. (2021). Overfishing drives over one-third of all sharks and rays toward a global extinction crisis. Curr. Biol. 31, 4773–4787. doi: 10.1016/j.cub.2021.08.062
Eryaşar A. R., Saygu İ. (2022). Using social media to identify recreational bluefish angling in the Mediterranean and Black Sea. Mar. Policy 135, 104834. doi: 10.1016/j.marpol.2021.104834
Giovos I., Chatzispyrou A., Doumpas N., Stoilas V., Moutopoulos D.K. (2018). Using unconventional sources of information for identifying critical areas for the endangered guitarfish in Greece. J. Black Sea/Mediterr. Environ. 24 (1), 38–50.
Heupel M. R., Simpfendorfer C. A. (2010). Science or slaughter: need for lethal sampling of sharks. Conserv. Biol. 24, 1212–1218. doi: 10.1111/j.1523-1739.2010.01491.x
Hof M., Dahlke R. I., Dandekar T., Kaltdorf M., Beck L. A. (2018). A non-invasive manual method for the assessment of pregnancy in female Scyliorhinus canicula catsharks. Mediterr. Mar. Sci. 19, 201–208. doi: 10.12681/mms.13838
Kabasakal H., Bilecenoğlu M. (2020). Shark infested internet: an analysis of internet-based media reports on rare and large sharks of Turkey. FishTaxa 16, 8–18.
Lieber L., Berrow S., Johnston E., Hall G., Hall J., Gubili C., et al. (2013). Mucus: aiding elasmobranch conservation through non-invasive genetic sampling. Endangered Species Res. 21, 215–222. doi: 10.3354/esr00524
McMillan M. N., Huveneers C., Semmens J. M., Gillanders B. M. (2019). Partial female migration and cool-water migration pathways in an overfished shark. ICES J. Mar. Sci. 76, 1083–1093. doi: 10.1093/icesjms/fsy181
Meekan M. G., Bradshaw C. J., Press M., McLean C., Richards A., Quasnichka S., et al. (2006). Population size and structure of whale sharks Rhincodon typus at Ningaloo Reef, Western Australia. Mar. Ecol. Progress Series 319, 275–285.
Papageorgiou M., GT E. B., Snape R., Hadjioannou L. (2022). Increased knowledge affects public attitude and perception towards elasmobranchs and support for conservation. Mediterranean Marine Science 23 (3), 637–649.
Randhawa H. S., Poulin R., Krkošek M. (2015). Increasing rate of species discovery in sharks coincides with sharp population declines: implications for biodiversity. Ecography 38, 96–107. doi: 10.1111/ecog.00793
Roemer R. P., Gallagher A. J., Hammerschlag N. (2016). Shallow water tidal flat use and associated specialized foraging behavior of the great hammerhead shark (Sphyrna mokarran). Mar. Freshw. Behav. Physiol. 49, 235–249. doi: 10.1080/10236244.2016.1168089
Saltzman J., Graham J., Wester J., White E. R., Macdonald C. C. (2022). # Sawfish: Social media to assess public perceptions, behaviors, and attitudes towards a critically endangered species. Front. Conserv. Sci. 3, 987909. doi: 10.3389/fcosc.2022.987909
Simpfendorfer C. A., Heupel M. R. (2004). Assessing habitat use and movement. Biology of sharks and their relatives. (Boca Raton: CRC Press). 553–572.
Simpfendorfer C. A., Poulakis G. R., O’Donnell P. M., Wiley T. R. (2008). Growth rates of juvenile smalltooth sawfish Pristis pectinata Latham in the western Atlantic. J. Fish Biol. 72 (3), 711–723.
Tsikliras A. C., Stergiou K. I. (2014). Size at maturity of Mediterranean marine fishes. Rev. fish Biol. fisheries 24, 219–268. doi: 10.1007/s11160-013-9330-x
Keywords: conservation, management, contemporary approaches, elasmobranchs, chimaeras
Citation: Bengil EGT and Başusta N (2024) Editorial: The biology and conservation of elasmobranchs and chimaeras. Front. Mar. Sci. 11:1465027. doi: 10.3389/fmars.2024.1465027
Received: 15 July 2024; Accepted: 04 September 2024;
Published: 30 September 2024.
Edited and Reviewed by:
Bronwyn M. Gillanders, University of Adelaide, AustraliaCopyright © 2024 Bengil and Başusta. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Elizabeth Grace Tunka Bengil, tunkaeronat@hotmail.com