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Multidecadal fishers’ knowledge reveals overexploitation of sharks in southeastern Brazil

Abstract

Assessing the impacts caused by fisheries requires long-term data series and continuous landing monitoring, which are still scarce in several low and middle-income countries. Alternative approaches, such as fishers’ local ecological knowledge (LEK) have been employed to assess the history of marine resources and overcome the challenges of missing data. We documented temporal changes over the last 60 years in small-scale fisheries in Arraial do Cabo, Brazil. Interviews with 155 fishers revealed the capture of six shark species (one genus), all under extinction risk according to the global and the national Red Lists. Among these, Carcharhinus brevipinna, Carcharhinus plumbeus, and Isurus oxyrinchus are commercially important. While LEK suggests an increase in fishing efforts, with new fishing grounds emerging after 2006, the number of individuals caught has decreased over time. Historical shark exploitation has led to substantial declines in the catches of C. plumbeus and C. brevipinna, which have rare occurrences in the region. Although landing data are critical information for building local fisheries management plans and setting conservation strategies, monitoring in the region is discontinuous and should be prioritized by public policies.

Keywords:
Anthropogenic impacts; Fisheries management; Local ecological knowledge; Shark populations; Small-scale shark fisheries

Resumo

Avaliar os impactos causados pela pesca requer dados de longo prazo e monitoramento contínuo das capturas, os quais ainda são escassos em vários países de baixa e média renda. Abordagens alternativas, como o conhecimento ecológico local dos pescadores (CEL), têm sido utilizadas para avaliar a história dos recursos marinhos e superar os desafios da ausência de dados. Documentamos mudanças temporais ao longo dos últimos 60 anos na pesca artesanal em Arraial do Cabo, Brasil. Entrevistas com 155 pescadores revelaram a captura de seis espécies de tubarões e um gênero, todas em risco de extinção de acordo com as Listas Vermelhas global e nacional. Entre essas espécies, Carcharhinus brevipinna, Carcharhinus plumbeus e Isurus oxyrinchus são comercialmente importantes. Embora o CEL tenha revelado um aumento nos esforços de pesca, com novos locais de pesca surgindo após 2006, o número de indivíduos capturados diminuiu ao longo do tempo. A exploração histórica de tubarões levou a declínios substanciais nas capturas de C. plumbeus e C. brevipinna, os quais possuem ocorrências raras na região. Embora os dados de desembarque sejam informações críticas para elaborar planos de gestão pesqueira local e estabelecer estratégias de conservação, o monitoramento na região é descontínuo e deveria ser priorizado por políticas públicas.

Palavras-chave:
Conhecimento ecológico local; Impactos antrópicos; Manejo pesqueiro; Pesca artesanal de tubarões; Populações de tubarões

INTRODUCTION

Elasmobranchs, which include sharks and rays, are one of the planet’s most ancient vertebrate groups, dating back approximately 400 million years (Andreev et al., 2015Andreev PS, Coates MI, Shelton RM, Cooper PR, Smith MP, Sansom IJ. Upper Ordovician chondrichthyan-like scales from North America. Palaeontology. 2015; 58(4):691–704. https://doi.org/10.1111/pala.12167
https://doi.org/10.1111/pala.12167...
). Sharks play fundamental ecological roles in marine environments, shaping the structure of marine food webs and contributing to the maintenance of balance and diversity in marine ecosystems (Roff et al., 2016Roff G, Doropoulos C, Rogers A, Bozec Y-M, Krueck NC, Aurellado E et al. The ecological role of sharks on coral reefs. Trends Ecol Evol. 2016; 31(5):395–407. https://doi.org/10.1016/j.tree.2016.02.014
https://doi.org/10.1016/j.tree.2016.02.0...
). However, the future of elasmobranch species has been threatened due to the global expansion of fishing practices (Myers, Worm, 2005Myers RA, Worm B. Extinction, survival or recovery of large predatory fishes. Philos Trans R Soc Lond B Biol Sci. 2005; 360(1453):13–20. https://doi.org/10.1098/rstb.2004.1573
https://doi.org/10.1098/rstb.2004.1573...
). In addition, life history traits such as slow growth and reproductive rates make them highly vulnerable to overexploitation (Worm et al., 2013Worm B, Davis B, Kettemer L, Ward-Paige CA, Chapman D, Heithaus MR et al. Global catches, exploitation rates, and rebuilding options for sharks. Mar Policy. 2013; 40:194–204. https://doi.org/10.1016/j.marpol.2012.12.034
https://doi.org/10.1016/j.marpol.2012.12...
). On the other hand, there are several examples of non-extractive use of sharks through diving tourism, generating economic benefits while promoting shark conservation (Torres et al., 2017Torres P, Bolhão N, Cunha RT, Vieira JAC, Rodrigues AS. Dead or alive: The growing importance of shark diving in the Mid-Atlantic region. J Nat Conserv. 2017; 36:20–28. https://doi.org/10.1016/j.jnc.2017.01.005
https://doi.org/10.1016/j.jnc.2017.01.00...
; Zimmerhackel et al., 2019Zimmerhackel JS, Kragt ME, Rogers AA, Ali K, Meekan MG. Evidence of increased economic benefits from shark-diving tourism in the Maldives. Mar Policy. 2019; 100:21–26. https://doi.org/10.1016/j.marpol.2018.11.004
https://doi.org/10.1016/j.marpol.2018.11...
). Despite that, fishing pressure and human consumption continue to pose threats to shark populations at a global scale (Dulvy et al., 2014Dulvy NK, Fowler SL, Musick JA, Cavanagh RD, Kyne PM, Harrison LR et al. Extinction risk and conservation of the world’s sharks and rays. eLife. 2014; 3:e00590. https://doi.org/10.7554/eLife.00590
https://doi.org/10.7554/eLife.00590...
; Dent, Clarke, 2015Dent F, Clarke S. State of the global market for shark products. FAO Fisheries and Aquaculture Technical Paper No 590. Rome, FAO; 2015. ; Davidson et al., 2016Davidson LN, Krawchuk MA, Dulvy NK. Why have global shark and ray landings declined: improved management or overfishing? Fish Fish. 2016; 17(2):438–58. https://doi.org/10.1111/faf.12119
https://doi.org/10.1111/faf.12119...
; Pacoureau et al., 2021Pacoureau N, Rigby CL, Kyne PM, Sherley RB, Winker H, Carlson JK et al. Half a century of global decline in oceanic sharks and rays. Nature. 2021; 589(7843):567–71. https://doi.org/10.1038/s41586-020-03173-9
https://doi.org/10.1038/s41586-020-03173...
). This pressing issue highlights the immediate necessity for conservation efforts and sustainable management strategies to protect these ancient and ecologically vital species.

Brazil is one of the world’s largest consumers and importers of shark meat and other by-products (Dent, Clarke, 2015Dent F, Clarke S. State of the global market for shark products. FAO Fisheries and Aquaculture Technical Paper No 590. Rome, FAO; 2015. ; Bornatowski et al., 2018Bornatowski H, Braga RR, Barreto RP. Elasmobranchs consumption in Brazil: impacts and consequences. In: Advances in marine vertebrate research in Latin America. Springer, Cham; 2018. p.251–62. ). For example, the average annual production of elasmobranchs represented 21,127 tons from 2000 to 2003, which corresponded to ~4.3% of the total fish production for that period (Brasil, 2014Brasil. Ministério do Meio Ambiente. Instituto Chico Mendes de Conservação da biodiversidade. Plano de Ação Nacional para a Conservação dos Tubarões e Raias Marinhos Ameaçados de Extinção. (Processo nº 02070.002911/ 2011-34). Portaria nº 125, de 04 de dezembro de 2014.). Such catches mostly supply meat consumption and the fin trade (Barreto et al., 2017Barreto RR, Bornatowski H, Motta FS, Santander-Neto J, Vianna GMS, Lessa R. Rethinking use and trade of pelagic sharks from Brazil. Mar Policy. 2017; 85:114–22. ), both of which have been shown to be major drivers of shark population decline worldwide. Over the past few decades, the shark meat trade has seen a rise, which is closely associated with the increased import of shark meat into Brazil (Dent, Clarke, 2015Dent F, Clarke S. State of the global market for shark products. FAO Fisheries and Aquaculture Technical Paper No 590. Rome, FAO; 2015. ). This increase in demand could be an outcome of the implementation of shark finning restrictions, as it has incentivized the complete utilization of sharks, thus exposing the resource to a new source of exploitation (Pincinato et al., 2022Pincinato RBM, Gasalla MA, Garlock T, Anderson JL. Market incentives for shark fisheries. Mar Policy. 2022; 139:105031. https://doi.org/10.1016/j.marpol.2022.105031
https://doi.org/10.1016/j.marpol.2022.10...
). Despite the growing shark meat trade in Brazil, there is a lack of accurate, species-specific fishing data, which often hampers quantitative stock assessment.

Landing data are fundamental for assessing and managing fisheries. However, long-term data series are mostly available for high-income countries in the northern hemisphere (Beaudreau et al., 2014Beaudreau AH, Levin PS. Advancing the use of local ecological knowledge for assessing data-poor species in coastal ecosystems. Ecol Appl. 2014; 24(2):244–56. https://doi.org/10.1890/13-0817.1
https://doi.org/10.1890/13-0817.1...
). In low and middle-income countries, it is typical to have either non-existent monitoring or fragmented data where landings are not described at species level (Bornatowski et al., 2014aBornatowski H, Braga RR, Vitule JRS. Threats to sharks in a developing country: the need for effective simple conservation measures. Nat Conserv. 2014a; 12(1):11–18. https://doi.org/10.4322/natcon.2014.003
https://doi.org/10.4322/natcon.2014.003...
; Freire et al., 2021Freire KMF, Almeida ZS, Amador JRET, Aragão JA, Araújo ARR, Ávila-da-Silva AO et al. Reconstruction of marine commercial landings for the Brazilian industrial and artisanal fisheries from 1950 to 2015. Front Mar Sci. 2021; 8:659110. https://doi.org/10.3389/fmars.2021.659110
https://doi.org/10.3389/fmars.2021.65911...
). Implementing fisheries monitoring programs in countries with limited resources, where fisheries are complex and involve multiple gears and species, poses a significant challenge (Beaudreau et al., 2014Beaudreau AH, Levin PS. Advancing the use of local ecological knowledge for assessing data-poor species in coastal ecosystems. Ecol Appl. 2014; 24(2):244–56. https://doi.org/10.1890/13-0817.1
https://doi.org/10.1890/13-0817.1...
). Data-poor scenarios hide the magnitude of impacts derived from fishing activities. Alternatively, non-conventional approaches have been used to circumvent the difficulties imposed by the lack of fisheries landing data (Eddy et al., 2010Eddy TD, Gardner JP, Pérez-Matus A. Applying fishers’ ecological knowledge to construct past and future lobster stocks in the Juan Fernández Archipelago, Chile. PLoS ONE. 2010; 5(11):e13670. https://doi.org/10.1371/journal.pone.0013670
https://doi.org/10.1371/journal.pone.001...
; Paterson, 2010Paterson B. Integrating fisher knowledge and scientific assessments. Anim Conserv. 2010;13(6):536–37. https://doi.org/10.1111/j.1469-1795.2010.00419.x
https://doi.org/10.1111/j.1469-1795.2010...
; Tesfamichael et al., 2014Tesfamichael D, Pitcher TJ, Pauly D. Assessing changes in fisheries using fishers’ knowledge to generate long time series of catch rates: a case study from the Red Sea. Ecol Soc. 2014; 19(1):18. http://dx.doi.org/10.5751/ES-06151-190118
http://dx.doi.org/10.5751/ES-06151-19011...
). These include historical information accessed from the gray literature, local ecological knowledge (LEK) of resource users (Sáenz-Arroyo et al., 2005Sáenz-Arroyo A, Roberts CM, Torres J, Cariño-Olvera M. Using fishers’ anecdotes, naturalists’ observations and grey literature to reassess marine species at risk: the case of the Gulf grouper in the Gulf of California, Mexico. Fish Fish. 2005; 6(2):121–33. https://doi.org/10.1111/j.1467-2979.2005.00185.x
https://doi.org/10.1111/j.1467-2979.2005...
; Taylor et al., 2017Taylor SM, Braccini JM, Bruce BD, McAuley RB. Reconstructing Western Australian white shark (Carcharodon carcharias) catches based on interviews with fishers. Mar Freshw Res. 2017; 69(3):366–75. https://doi.org/10.1071/MF17140
https://doi.org/10.1071/MF17140...
), old photographs (McClenachan, 2009McClenachan L. Historical declines in goliath grouper in south Florida. Endanger Species Res. 2009; 7:175–81. https://doi.org/10.3354/esr00167
https://doi.org/10.3354/esr00167...
), and logbooks (Martínez-Candelas et al., 2020Martínez-Candelas IA, Pérez-Jiménez JC, Espinoza-Tenorio A, McClenachan L, Méndez-Loeza I. Use of historical data to assess changes in the vulnerability of sharks. Fish Res. 2020; 226:105526. https://doi.org/10.1016/j.fishres.2020.105526
https://doi.org/10.1016/j.fishres.2020.1...
), all can be valuable sources. Fisher’s LEK may reveal fisheries catch trends, habitat preference, migration patterns, and changes in body size of targeted species (Braga et al., 2018Braga HO, Azeiteiro UM, Oliveira HMF, Pardal MA. Conserving Brazilian sardine: Fisher’s attitudes and knowledge in the Marine Extractive Reserve of Arraial do Cabo, Rio de Janeiro State, Brazil. Fish Res. 2018; 204:402–11. ; Leduc et al., 2021Leduc AOHC, Carvalho FHD, Hussey NE, Reis-Filho JA, Longo GO, Lopes PFM. Local ecological knowledge to assist conservation status assessments in data poor contexts: a case study with the threatened sharks of the Brazilian Northeast. Biodivers Conserv. 2021; 30(3):819–45. https://doi.org/10.1007/s10531-021-02119-5
https://doi.org/10.1007/s10531-021-02119...
). Indeed, fishers’ LEK studies have been proved critical to inform on the collapse of marine resources (Venkatachalam et al., 2010Venkatachalam AJ, Price ARG, Chandrasekara S, Senaratna Sellamuttu S, Kaler J. Changes in frigate tuna populations on the south coast of Sri Lanka: evidence of the shifting baseline syndrome from analysis of fisher observations. Aquat Conserv Mar Freshw Ecosyst. 2010; 20(2):167–76. https://doi.org/10.1002/aqc.1068
https://doi.org/10.1002/aqc.1068...
; Nazareth et al., 2022Nazareth E, D’Souza E, Arthur R, Jabado RW. Distribution of the Critically Endangered giant guitarfish (Glaucostegus typus) based on local ecological knowledge in the Andaman Islands, India. Ocean Coast Manag. 2022; 220:106075. https://doi.org/10.1016/j.ocecoaman.2022.106075
https://doi.org/10.1016/j.ocecoaman.2022...
). In Brazil, fishers’ knowledge has helped to reveal past scenarios of marine stocks, circumventing the difficulties caused by the lack of fishing data (Giglio et al., 2015Giglio VJ, Luiz OJ, Gerhardinger LC. Depletion of marine megafauna and shifting baselines among artisanal fishers in eastern Brazil. Anim Conserv. 2015; 18(4):348–58. https://doi.org/10.1111/acv.12178
https://doi.org/10.1111/acv.12178...
; Silvano et al., 2017Silvano RAM, Nora V, Andreoli TB, Lopes PFM, Begossi A. The ‘ghost of past fishing’: small-scale fisheries and conservation of threatened groupers in subtropical islands. Mar Policy. 2017; 75:125–32. https://doi.org/10.1016/j.marpol.2016.10.002
https://doi.org/10.1016/j.marpol.2016.10...
; Fogliarini et al., 2021Fogliarini CO, Ferreira CEL, Bornholdt J, Barbosa MC, Giglio VJ, Bender MG. Telling the same story: Fishers and landing data reveal changes in fisheries on the Southeastern Brazilian Coast. PLoS ONE. 2021; 16(6):e0252391. https://doi.org/10.1371/journal.pone.0252391
https://doi.org/10.1371/journal.pone.025...
).

Fishers’ knowledge has contributed to our understanding of shark biology, ecology, and conservation in numerous cases. In Fiji (South Pacific), fishers’ LEK revealed the presence of large sharks (e.g., Sphyrna spp.) near river mouths, providing reliable information on shark occurrence (Rasalato et al., 2010Rasalato E, Maginnity V, Brunnschweiler JM. Using local ecological knowledge to identify shark river habitats in Fiji (South Pacific). Environ Conserv. 2010; 37(1):90–97. https://www.jstor.org/stable/44520003
https://www.jstor.org/stable/44520003...
). In the Mediterranean Sea, the empirical knowledge of fishers helped reconstruct angel shark catches (Squatina spp.) in the last six decades, providing important data on a highly threatened fish taxonomic group (Giovos et al., 2019Giovos I, Stoilas V-O, Al-Mabruk SAA, Doumpas N, Marakis P, Maximiadi M et al. Integrating local ecological knowledge, citizen science and long-term historical data for endangered species conservation: Additional records of angel sharks (Chondrichthyes: Squatinidae) in the Mediterranean Sea. Aquat Conserv. 2019; 29(6):881–90. https://doi.org/10.1002/aqc.3089
https://doi.org/10.1002/aqc.3089...
). In the Strait of Sicily, also in the Mediterranean Sea, interviews with fishers were used to reconstruct abundance trends of shark populations over six decades (Colloca et al., 2020Colloca F, Carrozzi V, Simonetti A, Di Lorenzo M. Using local ecological knowledge of fishers to reconstruct abundance trends of elasmobranch populations in the Strait of Sicily. Front Mar Sci. 2020; 7:508. https://doi.org/10.3389/fmars.2020.00508
https://doi.org/10.3389/fmars.2020.00508...
). Fishers reported that shark catches have diminished since the 1940s and commercially important species have been depleted or locally extinct. In Brazil, fishers’ LEK revealed historical decreases in the body size of sharks (Giglio et al., 2015Giglio VJ, Luiz OJ, Gerhardinger LC. Depletion of marine megafauna and shifting baselines among artisanal fishers in eastern Brazil. Anim Conserv. 2015; 18(4):348–58. https://doi.org/10.1111/acv.12178
https://doi.org/10.1111/acv.12178...
; Leduc et al., 2021Leduc AOHC, Carvalho FHD, Hussey NE, Reis-Filho JA, Longo GO, Lopes PFM. Local ecological knowledge to assist conservation status assessments in data poor contexts: a case study with the threatened sharks of the Brazilian Northeast. Biodivers Conserv. 2021; 30(3):819–45. https://doi.org/10.1007/s10531-021-02119-5
https://doi.org/10.1007/s10531-021-02119...
). Given the absence of historical data on shark catches, we investigated temporal and spatial patterns of catches of coastal sharks in Arraial do Cabo, Brazil, as determined by local ecological knowledge of fishers. We provide data that can inform conservation and management measures, and guide research focusing on these species.

MATERIAL AND METHODS

Study site. Arraial do Cabo, located in the state of Rio de Janeiro, southeastern Brazil (Fig. 1), is known as a historical fishing area that is home to people that use of beach seine, line and hook, gill nets, and spears among other equipment types (Barreto et al., 2019Barreto PS, Andrade AC, Silva WL, Silva A, Kruel VSF. As canoas de boçarda em Arraial do Cabo (RJ). In: Melo JCF, Kruel VSF, Hanazaki N, editors. Árvores e madeiras na cultura naval tradicional. Joinville, SC: Editora Univille; 2019. p.162. ). The use of beach seine is a secular fishing practice in the region and has been used to catch several pelagic species (i.e., jacks, blue fish, mullets, scombrids) and sharks. Historically, the most important species for local fishing are groupers (e.g., Epinephelusmarginatus (Lowe, 1834), Mycteroperca acutirostris (Valenciennes, 1828)), jacks (Caranx spp.), Seriola spp.), mullets (Mugil liza Valenciennes, 1836) and blue fish (Pomatomus saltatrix (Linnaeus, 1766)) (Bender et al., 2014Bender MG, Machado GR, Silva PJA, Floeter SR, Monteiro-Netto C, Luiz OJ, Ferreira CEL. Local ecological knowledge and scientific data reveal overexploitation by multigear artisanal fisheries in the Southwestern Atlantic. PLoS ONE. 2014; 9(10):e110332. https://doi.org/10.1371/journal.pone.0110332
https://doi.org/10.1371/journal.pone.011...
; Fogliarini et al., 2021Fogliarini CO, Ferreira CEL, Bornholdt J, Barbosa MC, Giglio VJ, Bender MG. Telling the same story: Fishers and landing data reveal changes in fisheries on the Southeastern Brazilian Coast. PLoS ONE. 2021; 16(6):e0252391. https://doi.org/10.1371/journal.pone.0252391
https://doi.org/10.1371/journal.pone.025...
). In 1997, Arraial do Cabo became a partially protected marine area, the Marine Extractive Reserve of Arraial do Cabo (RESEXMar). Despite its status as a marine protected area, the RESEXMar lacks designated no-take zones, and enforcement for threatened species is poorly applied. The region is influenced by upwelling events (Valentin, 2001Valentin JL. The Cabo Frio upwelling system, Brazil. In: Seeliger U, Kjerfve B, editors. Coastal marine ecosystems of Latin America. Ecological Studies (Analysis and Synthesis). Springer; 2001.) and is considered a transition zone between the tropical and subtropical provinces, rendering Arraial do Cabo a hotspot of marine biodiversity in the Brazilian Province (Cordeiro et al., 2016Cordeiro CAMM, Mendes TC, Harborne AR, Ferreira CEL. Spatial distribution of nominally herbivorous fishes across environmental gradients on Brazilian rocky reefs. J Fish Biol. 2016; 89(1):939–58. https://doi.org/10.1111/jfb.12849
https://doi.org/10.1111/jfb.12849...
). In addition to fishing, the region has shown an intense coastal tourism, with consequences that include disturbance due to excessive noise, increasing production of solid and liquid wastes, compromising the health of corals (Rogers et al., 2014Rogers R, Correal GO, Oliveira TC, Carvalho LL, Mazurek P, Barbosa JEF et al. Coral health rapid assessment in marginal reef sites. Mar Biol Res. 2014; 10(6):612–24. https://doi.org/10.1080/17451000.2013.841944
https://doi.org/10.1080/17451000.2013.84...
) and other benthic organisms (Cassola et al., 2016Cassola GE, Pacheco MSC, Barbosa MC, Hansen DM, Ferreira CEL. Decline in abundance and health state of an Atlantic subtropical gorgonian population. Mar Pollut Bull. 2016; 104(1–2):329–34. https://doi.org/10.1016/j.marpolbul.2016.01.022
https://doi.org/10.1016/j.marpolbul.2016...
).

Data collection. Individual face-to-face interviews through semi-structured questionnaires were conducted with 155 small-scale fishers between July 2018 and July 2019 in six fishing communities: Figueira, Monte Alto, Praia Grande, Praia dos Anjos, Prainha, and Praia do Pontal (Fig. 1). Questionnaires included a general question (e.g., which species of sharks were the most frequently caught during their fishing careers) and specific questions targeting three shark species, the spinner shark (Carcharhinus brevipinna (Valenciennes, 1839)), the shortfin mako shark (Isurus oxyrinchus Rafinesque, 1810), and the sandbar shark (Carcharhinus plumbeus (Nardo, 1827)) (Tab. S1). Due to the richness of common names for Brazilian fish, we used photographs to enable shark species identification during the interviews (Freire, Carvalho-Filho, 2009Freire KMF, Carvalho-Filho A. Richness of common names of Brazilian reef fishes. Pan-Am J Aquat Sci. 2009; 4(2):96–145. Available from: https://panamjas.org/pdf_artigos/PANAMJAS_4(2)_96-145.pdf
https://panamjas.org/pdf_artigos/PANAMJA...
). When fishers recognized and had already captured any of these species, he was asked about: i) the best day catch (number of individuals), ii) the site, iii) and the year in which this catch was made. In addition, we asked about the fisher’s age and experience in fishing (e.g., years of practice). During interviews, fishers provided general information about the species’ breeding season, feeding behavior and other ecological aspects. This information was registered as observations (Tab. S2). We assessed the threat categories according to the Global Red List (IUCN, 2023International Union for Conservation of Nature (IUCN). Standards and petitions committee. Guidelines for using the IUCN Red List categories and criteria. Version 15.1 [Internet]. Gland; 2022. Available from: http://www.iucnredlist.org/documents/RedListGuidelines.pdf.
http://www.iucnredlist.org/documents/Red...
) and the National Red List of Threatened Species (MMAMinistério do Meio Ambiente (MMA). Portaria MMA nº 148, de 7 de junho de 2022. Altera os Anexos da Portaria nº 443, de 17 de dezembro de 2014, da Portaria nº 444, de 17 de dezembro de 2014, e da Portaria nº 445, de 17 de dezembro de 2014, referentes à atualização da Lista Nacional de Espécies Ameaçadas de Extinção. 2022., 2018Ministério do Meio Ambiente (MMA). Instituto Chico Mendes de Conservação da Biodiversidade. Livro Vermelho da Fauna Brasileira Ameaçada de Extinção: Volume VI - Peixes. In: Instituto Chico Mendes de Conservação da Biodiversidade (Org.). In: Livro Vermelho da Fauna Brasileira Ameaçada de Extinção. Brasília: ICMBio; 2018., 2023Ministério do Meio Ambiente (MMA). Portaria MMA nº 354, de 27 de janeiro de 2023. Revoga as Portarias MMA nº 299, de 13 de dezembro de 2022, e nº 300, de 13 de dezembro de 2022, e dá outras providências. Diário Oficial da União. 2023.) for all species mentioned by fishers. The fishers were informed of the research purpose before each interview. We also informed them that all information provided in interviews would be anonymized.

Data analysis. From the information on the best day catch obtained through interviews with local fishers, we estimated the temporal decline in catches of each shark species. For that, we applied regressions and plotted the best day catch (number of individuals) versus the year in which such catch occurred. We tested distinct regression types (exponential, polynomial, and linear regressions) and values of coefficient of determination were compared to assess the quality of the regression fit to data distribution.

To analyze changes in spatial distribution of best day catches we use a nautical chart (Fig. S3) of the region. Interviewees were asked to mark in the chart the sites where they caught shark species (Fig. S3). To compare past and present periods, we grouped fisher’s reports in two different periods: before 2006 and after 2006. We established this division because in 2006, Alkalis Company, an important local producer of calcium carbonate, closed. After this event, the municipality’s economy experienced an exponential increase in fishing, once again making it the predominant activity in the primary sector (Carneiro et al., 2012Carneiro AMM, Vieira LF, Moraes EA. Conhecimentos tradicionais da pesca artesanal para a conservação sustentável do mar: valores patrimoniais do espaço marítimo na Reserva Extrativista Marinha de Arraial do Cabo–RJ. Rio de Janeiro: Editora COPPE/UFRJ; 2012. ). As a result, many people began relying on fishing as their main source of income, increasing the exploitation of marine resources throughout the region (Carneiro et al., 2012Carneiro AMM, Vieira LF, Moraes EA. Conhecimentos tradicionais da pesca artesanal para a conservação sustentável do mar: valores patrimoniais do espaço marítimo na Reserva Extrativista Marinha de Arraial do Cabo–RJ. Rio de Janeiro: Editora COPPE/UFRJ; 2012. ).

Maps of spatial distributions of best day catches were built using the Quantum GIS software (QGis, 2019QGIS Development Team. QGIS Geographic Information System. Version 3.16.2. Chicago, IL: Open-Source Geospatial Foundation Project; 2019. Available from: http://qgis.osgeo.org
http://qgis.osgeo.org...
). To verify temporal changes in spatial distribution, the catches in number of individuals were compared by fishing site/ground and period (before 2006 and after 2006). Statistical analyzes were performed using R software v. 3.6.1 (R Development Core Team, 2019R Development Core Team. R: A language and environment for statistical computing. Vienna, Austria: R Foundation for statistical Computing; 2019. Available from: https://www.r-project.org/
https://www.r-project.org/...
).

FIGURE 1 |
Map of Arraial do Cabo region, Rio de Janeiro, Brazil, and study sites.

RESULTS

We interviewed 155 small-scale fishers, of which their age ranged 17 to 82 years old, (average = 50 ±12 years) (±s.d.) and their experience ranged three to 64 years (average = 31 ±13 years). Fishers identified six shark species (one genus) which are considered at risk of extinction (Tab. 1). The most frequently caught sharks were spinner shark (Carcharhinus brevipinna), the sandbar shark (Carcharhinus plumbeus), and the shortfin mako shark (Isurus oxyrinchus). Of these sharks, there were no significant declines in C. brevipinna caught with beach seine (Fig. 2) and there were no significant differences over time for both C. brevipinna and I. oxyrinchus caught with hook and line (Figs. 3A, B). By contrast, the number of C. plumbeus individuals was significantly reduced over the last 50 years from an average of 9.56 ±5.13 individuals in 1968 to 2.82 ±1.7 individuals in 2019 (Fig. 3C).

TABLE 1 |
Shark species reported by fishers as most captured during their careers. Conservation status according to the global (IUCN, 2023) and national (MMA 2018, 2022, 2023) red lists of threatened species. Conservation status: CR = Critically Endangered; VU = Vulnerable; EN = Endangered; NT = Near Threatened.
FIGURE 2 |
Spinner shark, Carcharhinus brevipinna, catches according to beach seine fishers in Arraial do Cabo (with second order polynomial regression line shown r2 = 0.09, p = 0.5).
FIGURE 3 |
Best day’s catches (number of individuals caught) according to hook and line fishers of Arraial do Cabo. A. Spinner shark, Carcharhinus brevipinna, with fourth order polynomial regression (r² = 0.02, p = 0.8); B. Shortfin mako shark, Isurus oxyrinchus, with second order polynomial regression (r² = 0.14, p = 0.46); C. Sandbar shark, Carcharhinus plumbeus, with third order polynomial regression (r² = 0.08, p = 0.02).

Fishers’ knowledge revealed temporal changes in the fishing grounds of three investigated shark species (Fig. 4). The spatial distribution of shark catches revealed that new fishing grounds have been exploited over time. For instance, eight new fishing grounds of C. brevipinna were reported after 2006 (Figs. 4A, B). In some fishing grounds, such as Praia Grande, the number of individuals caught decreased over time (Fig. 4B). Between 1979 and 2005, beach seine fishers caught around 2000 individuals. After this period (2006–2019), the number of individuals declined to a maximum of 500 individuals caught on the best day’s catch (Figs. 4A, B). The number of fishing grounds where the interviewees reported catches of I. oxyrinchus also increased; six new sites appeared from 1962 to 2019 (Figs. 4C, D). Finally, for C. plumbeus, four new fishing grounds were reported after 2006. In Praia Grande, where 11–12 individuals were caught between 1968 and 2005, no C. plumbeus individuals were captured between 2006 and 2019 (Fig. 4F).

FIGURE 4 |
Spatial distribution of fishing grounds of best day’s shark catches in Arraial do Cabo (number of individuals caught). A. Spinner shark, Carcharhinus brevipinna, catches from 1979 to 2005 and B. 2006 to 2019; C. Shortfin mako shark, Isurus oxyrinchus, catches from 1962 to 2005 and D. 2006 to 2019; E. Sandbar shark, Carcharhinus plumbeus, catches from 1968 to 2005 and F. 2008 to 2019.

DISCUSSION

During the last 60 years in Arraial do Cabo, shark catches and fishing grounds have changed. Fish stocks have experienced changes in this region (Fogliarini et al., 2021Fogliarini CO, Ferreira CEL, Bornholdt J, Barbosa MC, Giglio VJ, Bender MG. Telling the same story: Fishers and landing data reveal changes in fisheries on the Southeastern Brazilian Coast. PLoS ONE. 2021; 16(6):e0252391. https://doi.org/10.1371/journal.pone.0252391
https://doi.org/10.1371/journal.pone.025...
), where target top and mesopredators, such as sharks, groupers, and tunas, have declined and fishers have concentrated on new ones (Bender et al., 2014Bender MG, Machado GR, Silva PJA, Floeter SR, Monteiro-Netto C, Luiz OJ, Ferreira CEL. Local ecological knowledge and scientific data reveal overexploitation by multigear artisanal fisheries in the Southwestern Atlantic. PLoS ONE. 2014; 9(10):e110332. https://doi.org/10.1371/journal.pone.0110332
https://doi.org/10.1371/journal.pone.011...
; Fogliarini et al., 2021Fogliarini CO, Ferreira CEL, Bornholdt J, Barbosa MC, Giglio VJ, Bender MG. Telling the same story: Fishers and landing data reveal changes in fisheries on the Southeastern Brazilian Coast. PLoS ONE. 2021; 16(6):e0252391. https://doi.org/10.1371/journal.pone.0252391
https://doi.org/10.1371/journal.pone.025...
). In general, shark fisheries have changed over time. A small portion of the fleet currently focuses on shark fishing seasonally, operating fishing grounds located farther away from the coast to maintain profitability. However, despite the increased effort, this has not resulted in a corresponding increase in catches. Our research, in fact, has revealed a decline in the number of sharks caught in some fishing grounds closer to the coast. Fishers reported the best day catch of over 2,000 sharks using beach seine at Praia Grande beach. Due to unsustainable captures, catch events with hundreds of individuals have become increasingly rare (Fig. 5).

Off the Brazilian coast, catches on pregnant sharks, including juveniles and immature individuals using beach seine and other gill nets are common (Vooren, Klippel, 2005Vooren CM, Klippel S,editors. Ações para a conservação de tubarões e raias no sul do Brasil. Sandro Klippel; 2005.; Yokota, Lessa, 2006Yokota L, Lessa RP. A nursery area for sharks and rays in Northeastern Brazil. Environ Biol Fish. 2006; 75:349–60. https://doi.org/10.1007/s10641-006-0038-9
https://doi.org/10.1007/s10641-006-0038-...
; Bornatowski et al., 2014aBornatowski H, Braga RR, Vitule JRS. Threats to sharks in a developing country: the need for effective simple conservation measures. Nat Conserv. 2014a; 12(1):11–18. https://doi.org/10.4322/natcon.2014.003
https://doi.org/10.4322/natcon.2014.003...
). We verified that pregnant individuals of C. brevipinna and I. oxyrinchus were frequently captured between June and July (Tab. S2). Patterns of reproduction, migration, and feeding habitats of these shark species are poorly known for the Brazilian Province. In South Africa, the capture of pregnant C. brevipinna was confirmedin beach nets between March and August (Allen, Gliff, 2000Allen BR, Cliff G. Sharks caught in the protective gill nets off KwaZulu-Natal, South Africa. 9. The spinner shark Carcharhinus brevipinna (Müller and Henle). Afr J Mar Sci. 2000; 22:199–215. https://doi.org/10.2989/025776100784125654
https://doi.org/10.2989/0257761007841256...
). In our study, fishers also reported large catches of this species during upwelling events and following large mullet shoals (Mugil sp.) (Tab. S2). According to reports, sharks are attracted to the coastline to feed on mullets, typically occurring between April and August. Along the African coast, spinner sharks were captured during feeding aggregations, especially in austral winter months, also coinciding with the abundance of sardines (Sardinops sagax) in coastal waters (Allen, Gliff, 2000Allen BR, Cliff G. Sharks caught in the protective gill nets off KwaZulu-Natal, South Africa. 9. The spinner shark Carcharhinus brevipinna (Müller and Henle). Afr J Mar Sci. 2000; 22:199–215. https://doi.org/10.2989/025776100784125654
https://doi.org/10.2989/0257761007841256...
). This feeding aggregation behavior has also been observed in Florida, where C. brevipinna formed “packs” behind shrimp boats (Dodrill, 1977Dodrill JW. A hook and line survey of the sharks found within five hundred meters of shore along Melbourne Beach, Brevard County, Florida [Master Dissertation]. Melbourne: Florida Institute of Technology; 1977).

Shark fishing in Arraial do Cabo sustained an international shark finning market until the 1990s, when this market was banned in Brazil (Amorim et al., 1998Amorim AD, Arfelli CA, Fagundes L. Pelagic elasmobranchs caught by longliners off southern Brazil during 1974–97: an overview. Mar Freshw Res. 1998; 49(7):621–32. https://doi.org/10.1071/MF97111
https://doi.org/10.1071/MF97111...
; Hazin et al., 2008Hazin HV, Broadhurst MK, Amorim AF, Arfelli CA, Domingo A. Catches of pelagic sharks by subsurface longline fisheries in the South Atlantic Ocean during the last century: A review of available data with emphasis on Uruguay and Brazil. In: Camhi MD, Pikitch EK, Babcock EA, editors. Sharks of the open ocean: Biology, fisheries and conservation. Blackwell Publishing; 2008. p.213–29. ). As in other countries, management of shark fishing in Brazil has not prevented population declines (Bornatowski et al., 2014aBornatowski H, Braga RR, Vitule JRS. Threats to sharks in a developing country: the need for effective simple conservation measures. Nat Conserv. 2014a; 12(1):11–18. https://doi.org/10.4322/natcon.2014.003
https://doi.org/10.4322/natcon.2014.003...
,bBornatowski H, Navia AF, Braga RR, Abilhoa V, Corrêa MFM. Ecological importance of sharks and rays in a structural foodweb analysis in southern Brazil. ICES J Mar Sci. 2014b; 71(7):1586–92. https://doi.org/10.1093/icesjms/fsu025
https://doi.org/10.1093/icesjms/fsu025...
). By 2018, the National Red List of Threatened species included 30 shark species (MMA, 2018Ministério do Meio Ambiente (MMA). Instituto Chico Mendes de Conservação da Biodiversidade. Livro Vermelho da Fauna Brasileira Ameaçada de Extinção: Volume VI - Peixes. In: Instituto Chico Mendes de Conservação da Biodiversidade (Org.). In: Livro Vermelho da Fauna Brasileira Ameaçada de Extinção. Brasília: ICMBio; 2018.). In 2023, five other species were added to this list. Among these, the spinner shark, C. brevipinna, categorized as Vulnerable (VU), and the shortfin mako I. oxyrinchus, listed as Critically Endangered (CR) (MMA, 2023Ministério do Meio Ambiente (MMA). Portaria MMA nº 354, de 27 de janeiro de 2023. Revoga as Portarias MMA nº 299, de 13 de dezembro de 2022, e nº 300, de 13 de dezembro de 2022, e dá outras providências. Diário Oficial da União. 2023.). The spinner shark is a common coastal-pelagic species that occurs in warm-temperate and tropical areas of the Western and Eastern Atlantic and the Western Indo-Pacific (IUCN, 2023International Union for Conservation of Nature (IUCN). Standards and petitions committee. Guidelines for using the IUCN Red List categories and criteria. Version 15.1 [Internet]. Gland; 2022. Available from: http://www.iucnredlist.org/documents/RedListGuidelines.pdf.
http://www.iucnredlist.org/documents/Red...
). This species is highly susceptible to fisheries due to its low biological productivity, and its breeding area which overlaps with areas of intensive and unregulated fisheries (Diop, Dossa, 2011Diop M, Dossa J. 30 Years of shark fishing. IUCN Shark Specialist Group. Dakar. 2011. Available from: http://www.iucnssg.org/uploads/5/4/1/2/54120303/30years_eng.pdf
http://www.iucnssg.org/uploads/5/4/1/2/5...
; Doumbouya et al., 2017Doumbouya A, Camara OT, Mamie J, Intchama JF, Jarra A, Ceesay S et al. Assessing the effectiveness of monitoring control and surveillance of illegal fishing: The case of West Africa. Front Mar Sci. 2017; 4:50. https://doi.org/10.3389/fmars.2017.00050
https://doi.org/10.3389/fmars.2017.00050...
). A global estimate suggests that spinner shark populations have suffered reductions of 30–49% in the recent decades (IUCN, 2023International Union for Conservation of Nature (IUCN). Standards and petitions committee. Guidelines for using the IUCN Red List categories and criteria. Version 15.1 [Internet]. Gland; 2022. Available from: http://www.iucnredlist.org/documents/RedListGuidelines.pdf.
http://www.iucnredlist.org/documents/Red...
). Similarly, studies have indicated the depletion of shortfin makostocks in various marine regions, including the South Atlantic (Ferretti et al., 2008Ferretti F, Myers RA, Serena F, Lotze HK. Loss of large predatory sharks from the Mediterranean Sea. Conserv Biol. 2008; 22(4):952–64. https://doi.org/10.1111/j.1523-1739.2008.00938.x
https://doi.org/10.1111/j.1523-1739.2008...
; Barreto et al., 2016Barreto R, Ferretti F, Flemming JM, Amorim A, Andrade H, Worm B et al. Trends in the exploitation of South Atlantic shark populations. Conserv Biol. 2016; 30(4):792–804. https://doi.org/10.1111/cobi.12663
https://doi.org/10.1111/cobi.12663...
; ICCAT, 2017International Commission for the Conservation of Atlantic Tunas (ICCAT). Report of the 2017 ICCAT Shortfin Mako Assessment Meeting. Madrid, Spain 12-16 June 2017. ; Brunel et al., 2018 Brunel T, Coelho R, Merino G, Ortiz de Urbina J, Rosa D, Santos C, et al. A preliminary stock assessment for the shortfin mako shark in the Indian Ocean using data-limited approaches. In: IOTC - 14th Working Party on Ecosystems and Bycatch. Cape Town, South Africa; 2018. p. 18. Available from: http://www.iotc.org/documents/WPEB/14/37
http://www.iotc.org/documents/WPEB/14/37...
). An assessment has revealed a 99% decline in the average CPUE (Catch per unit effort) of shortfin mako caught in longline fisheries over the last 30 years (Barreto et al., 2016Barreto R, Ferretti F, Flemming JM, Amorim A, Andrade H, Worm B et al. Trends in the exploitation of South Atlantic shark populations. Conserv Biol. 2016; 30(4):792–804. https://doi.org/10.1111/cobi.12663
https://doi.org/10.1111/cobi.12663...
).

FIGURE 5 |
Photographs showing past and present of beach seine catches of spinner shark, Carcharhinus brevipinna, caught in Arraial do Cabo, Brazil. A. Individuals caught in 1979; B. In 1996; C. In 2005; and D. In 2014. Images were kindly provided by interviewed fishers of Arraial do Cabo.

In conclusion, we observed a shift in shark fishing practices in Arraial do Cabo over the past 60 years. The shark fleet has moved further away from the coast due to overexploitation. However, this change has not been accompanied by an increase in catches. A fundamental step in managing the cross-scale overfishing scenario for sharks in Brazil is the establishment of protected areas in nursery and breeding sites. However, given that most of these sharks exhibit high mobility, migrating through long distances during their life cycle, which includes feeding and breeding areas (Capapé et al., 2003Capapé C, Hemida F, Seck AA, Diatta Y, Guélorget O, Zaouali J. Distribution and reproductive biology of the spinner shark, Carcharhinus brevipinna (Muller and Henle, 1841) (Chondrichthyes: Carcharhinidae). Isr J Ecol Evol. 2003; 49(4):269–86.; Stevens, 2008Stevens JD. The biology and ecology of the shortfin mako shark, Isurus oxyrinchus. In: Camhi MD, Pikitch EK, Babcock EA, editors. Sharks of the open ocean: biology, fisheries and conservation. Blackwell Publishing; 2008. p.87–94.; Letessier et al., 2017Letessier TB, Bouchet PJ, Meeuwig JJ. Sampling mobile oceanic fishes and sharks: implications for fisheries and conservation planning. Biol Rev. 2017; 92(2):627–46. https://doi.org/10.1111/brv.12246
https://doi.org/10.1111/brv.12246...
), effective protection for these species will solely be effective though a network of protected areas and shark fishing bans, coupled with effective monitoring and education initiatives. Since 2007, Brazil has lacked a systematic nationwide fishing monitoring program (IBAMA, 2007Instituto Brasileiro do Meio Ambiente e dos Recursos Naturais Renováveis (IBAMA). Estatística da Pesca. Grandes Regiões e Unidades da Federação. Brasília: IBAMA; 2007. ), lacking basic data to support fisheries management. We strongly recommend that the Brazilian government accelerates the establishment of monitoring programs, integrating scientific guidance, stakeholders’ knowledge, and leadership. Alarmingly, increasing evidence indicates a decline in fish stocks targeted by both industrial and small-scale fisheries along the Brazilian coast (Freire et al., 2021Freire KMF, Almeida ZS, Amador JRET, Aragão JA, Araújo ARR, Ávila-da-Silva AO et al. Reconstruction of marine commercial landings for the Brazilian industrial and artisanal fisheries from 1950 to 2015. Front Mar Sci. 2021; 8:659110. https://doi.org/10.3389/fmars.2021.659110
https://doi.org/10.3389/fmars.2021.65911...
). Additionally, shark species and other targeted fisheries such as groupers possess life history traits that render them even more susceptible to fishing impacts (Bender et al., 2013Bender MG, Floeter SR, Hanazaki N. Do traditional fishers recognize reef fish species declines? Shifting environmental baselines in Eastern Brazil. Fish Manag Ecol. 2013; 20(1):58–67. https://doi.org/10.1111/fme.12006
https://doi.org/10.1111/fme.12006...
; Ceretta et al., 2020Ceretta BF, Fogliarini CO, Giglio VJ, Maxwell MF, Waechter LS, Bender MG. Testing the accuracy of biological attributes in predicting extinction risk. Perspect Ecol Conserv. 2020; 18(1):12–18. https://doi.org/10.1016/j.pecon.2020.01.003
https://doi.org/10.1016/j.pecon.2020.01....
). Fisheries landing data across long time-series also remain scarce for sharks in Brazil. However, through fishers’ LEK, we may fill in gaps in fisheries landing data for some species. Combining different data sources can help us improve our understanding of shark population trends in complex and multi-specific fisheries. This approach can provide insight into data-poor sites where information is absent or fragmented over time. Biological and social approaches are complementary, and their integration has gained increased recognition, providing relevant information for fisheries management and the conservation of threatened species. The public in general is unaware about the key role of top predators like sharks. This fact reinforces the constant need for public awareness to value sharks alive, considering the multiple examples of revenues where sharks are protected (Vianna et al., 2018Vianna GMS, Meekan MG, Rogers AA, Kragt ME, Alin JM, Zimmerhackel JS. Shark-diving tourism as a financing mechanism for shark conservation strategies in Malaysia. Mar Policy. 2018; 94:220–26. https://doi.org/10.1016/j.marpol.2018.05.008
https://doi.org/10.1016/j.marpol.2018.05...
; Gonzáles-Mantilla et al., 2022Gonzáles-Mantilla PG, Gallagher AJ, León CJ, Vianna GMS. Economic impact and conservation potential of shark-diving tourism in the Azores Islands. Mar Policy. 2022; 135:104869. https://doi.org/10.1016/j.marpol.2021.104869
https://doi.org/10.1016/j.marpol.2021.10...
). These recommendations collectively underscore the need for a holistic approach that integrates various strategies and stakeholders to ensure the sustainability and conservation of Brazil’s shark populations.

ACKNOWLEDGEMENTS

We thank fishers for their collaboration and shared knowledge, especially Luiz and Paulo Cordeiro. ICMBio provides continuous support to work in Arraial do Cabo RESEXMar. First author acknowledges Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) for financial support. CELF is supported by grants from FAPERJ and CNPq. Costão Rochoso Project (FUNBIO Grant Pesquisa Marinha 020/2017) has provided financial and logistic support during field sampling in Arraial do Cabo. This work is part of a research program supported by Serrapilheira Institute (grant number Serra-1708-15364) awarded to Guilherme Ortigara Longo (PI).

REFERENCES

  • Allen BR, Cliff G. Sharks caught in the protective gill nets off KwaZulu-Natal, South Africa. 9. The spinner shark Carcharhinus brevipinna (Müller and Henle). Afr J Mar Sci. 2000; 22:199–215. https://doi.org/10.2989/025776100784125654
    » https://doi.org/10.2989/025776100784125654
  • Amorim AD, Arfelli CA, Fagundes L. Pelagic elasmobranchs caught by longliners off southern Brazil during 1974–97: an overview. Mar Freshw Res. 1998; 49(7):621–32. https://doi.org/10.1071/MF97111
    » https://doi.org/10.1071/MF97111
  • Andreev PS, Coates MI, Shelton RM, Cooper PR, Smith MP, Sansom IJ. Upper Ordovician chondrichthyan-like scales from North America. Palaeontology. 2015; 58(4):691–704. https://doi.org/10.1111/pala.12167
    » https://doi.org/10.1111/pala.12167
  • Barreto R, Ferretti F, Flemming JM, Amorim A, Andrade H, Worm B et al. Trends in the exploitation of South Atlantic shark populations. Conserv Biol. 2016; 30(4):792–804. https://doi.org/10.1111/cobi.12663
    » https://doi.org/10.1111/cobi.12663
  • Barreto RR, Bornatowski H, Motta FS, Santander-Neto J, Vianna GMS, Lessa R. Rethinking use and trade of pelagic sharks from Brazil. Mar Policy. 2017; 85:114–22.
  • Barreto PS, Andrade AC, Silva WL, Silva A, Kruel VSF. As canoas de boçarda em Arraial do Cabo (RJ). In: Melo JCF, Kruel VSF, Hanazaki N, editors. Árvores e madeiras na cultura naval tradicional. Joinville, SC: Editora Univille; 2019. p.162.
  • Beaudreau AH, Levin PS. Advancing the use of local ecological knowledge for assessing data-poor species in coastal ecosystems. Ecol Appl. 2014; 24(2):244–56. https://doi.org/10.1890/13-0817.1
    » https://doi.org/10.1890/13-0817.1
  • Bender MG, Floeter SR, Hanazaki N. Do traditional fishers recognize reef fish species declines? Shifting environmental baselines in Eastern Brazil. Fish Manag Ecol. 2013; 20(1):58–67. https://doi.org/10.1111/fme.12006
    » https://doi.org/10.1111/fme.12006
  • Bender MG, Machado GR, Silva PJA, Floeter SR, Monteiro-Netto C, Luiz OJ, Ferreira CEL. Local ecological knowledge and scientific data reveal overexploitation by multigear artisanal fisheries in the Southwestern Atlantic. PLoS ONE. 2014; 9(10):e110332. https://doi.org/10.1371/journal.pone.0110332
    » https://doi.org/10.1371/journal.pone.0110332
  • Bornatowski H, Braga RR, Vitule JRS. Threats to sharks in a developing country: the need for effective simple conservation measures. Nat Conserv. 2014a; 12(1):11–18. https://doi.org/10.4322/natcon.2014.003
    » https://doi.org/10.4322/natcon.2014.003
  • Bornatowski H, Navia AF, Braga RR, Abilhoa V, Corrêa MFM. Ecological importance of sharks and rays in a structural foodweb analysis in southern Brazil. ICES J Mar Sci. 2014b; 71(7):1586–92. https://doi.org/10.1093/icesjms/fsu025
    » https://doi.org/10.1093/icesjms/fsu025
  • Bornatowski H, Braga RR, Barreto RP. Elasmobranchs consumption in Brazil: impacts and consequences. In: Advances in marine vertebrate research in Latin America. Springer, Cham; 2018. p.251–62.
  • Braga HO, Azeiteiro UM, Oliveira HMF, Pardal MA. Conserving Brazilian sardine: Fisher’s attitudes and knowledge in the Marine Extractive Reserve of Arraial do Cabo, Rio de Janeiro State, Brazil. Fish Res. 2018; 204:402–11.
  • Brasil. Ministério do Meio Ambiente. Instituto Chico Mendes de Conservação da biodiversidade. Plano de Ação Nacional para a Conservação dos Tubarões e Raias Marinhos Ameaçados de Extinção. (Processo nº 02070.002911/ 2011-34). Portaria nº 125, de 04 de dezembro de 2014.
  • Brunel T, Coelho R, Merino G, Ortiz de Urbina J, Rosa D, Santos C, et al. A preliminary stock assessment for the shortfin mako shark in the Indian Ocean using data-limited approaches. In: IOTC - 14th Working Party on Ecosystems and Bycatch. Cape Town, South Africa; 2018. p. 18. Available from: http://www.iotc.org/documents/WPEB/14/37
    » http://www.iotc.org/documents/WPEB/14/37
  • Capapé C, Hemida F, Seck AA, Diatta Y, Guélorget O, Zaouali J. Distribution and reproductive biology of the spinner shark, Carcharhinus brevipinna (Muller and Henle, 1841) (Chondrichthyes: Carcharhinidae). Isr J Ecol Evol. 2003; 49(4):269–86.
  • Carneiro AMM, Vieira LF, Moraes EA Conhecimentos tradicionais da pesca artesanal para a conservação sustentável do mar: valores patrimoniais do espaço marítimo na Reserva Extrativista Marinha de Arraial do Cabo–RJ. Rio de Janeiro: Editora COPPE/UFRJ; 2012.
  • Cassola GE, Pacheco MSC, Barbosa MC, Hansen DM, Ferreira CEL. Decline in abundance and health state of an Atlantic subtropical gorgonian population. Mar Pollut Bull. 2016; 104(1–2):329–34. https://doi.org/10.1016/j.marpolbul.2016.01.022
    » https://doi.org/10.1016/j.marpolbul.2016.01.022
  • Ceretta BF, Fogliarini CO, Giglio VJ, Maxwell MF, Waechter LS, Bender MG. Testing the accuracy of biological attributes in predicting extinction risk. Perspect Ecol Conserv. 2020; 18(1):12–18. https://doi.org/10.1016/j.pecon.2020.01.003
    » https://doi.org/10.1016/j.pecon.2020.01.003
  • Colloca F, Carrozzi V, Simonetti A, Di Lorenzo M. Using local ecological knowledge of fishers to reconstruct abundance trends of elasmobranch populations in the Strait of Sicily. Front Mar Sci. 2020; 7:508. https://doi.org/10.3389/fmars.2020.00508
    » https://doi.org/10.3389/fmars.2020.00508
  • Cordeiro CAMM, Mendes TC, Harborne AR, Ferreira CEL. Spatial distribution of nominally herbivorous fishes across environmental gradients on Brazilian rocky reefs. J Fish Biol. 2016; 89(1):939–58. https://doi.org/10.1111/jfb.12849
    » https://doi.org/10.1111/jfb.12849
  • Davidson LN, Krawchuk MA, Dulvy NK. Why have global shark and ray landings declined: improved management or overfishing? Fish Fish. 2016; 17(2):438–58. https://doi.org/10.1111/faf.12119
    » https://doi.org/10.1111/faf.12119
  • Dent F, Clarke S. State of the global market for shark products. FAO Fisheries and Aquaculture Technical Paper No 590. Rome, FAO; 2015.
  • Diop M, Dossa J. 30 Years of shark fishing. IUCN Shark Specialist Group. Dakar. 2011. Available from: http://www.iucnssg.org/uploads/5/4/1/2/54120303/30years_eng.pdf
    » Available from: http://www.iucnssg.org/uploads/5/4/1/2/54120303/30years_eng.pdf
  • Dodrill JW. A hook and line survey of the sharks found within five hundred meters of shore along Melbourne Beach, Brevard County, Florida [Master Dissertation]. Melbourne: Florida Institute of Technology; 1977
  • Doumbouya A, Camara OT, Mamie J, Intchama JF, Jarra A, Ceesay S et al. Assessing the effectiveness of monitoring control and surveillance of illegal fishing: The case of West Africa. Front Mar Sci. 2017; 4:50. https://doi.org/10.3389/fmars.2017.00050
    » https://doi.org/10.3389/fmars.2017.00050
  • Dulvy NK, Fowler SL, Musick JA, Cavanagh RD, Kyne PM, Harrison LR et al. Extinction risk and conservation of the world’s sharks and rays. eLife. 2014; 3:e00590. https://doi.org/10.7554/eLife.00590
    » https://doi.org/10.7554/eLife.00590
  • Eddy TD, Gardner JP, Pérez-Matus A. Applying fishers’ ecological knowledge to construct past and future lobster stocks in the Juan Fernández Archipelago, Chile. PLoS ONE. 2010; 5(11):e13670. https://doi.org/10.1371/journal.pone.0013670
    » https://doi.org/10.1371/journal.pone.0013670
  • Ferretti F, Myers RA, Serena F, Lotze HK. Loss of large predatory sharks from the Mediterranean Sea. Conserv Biol. 2008; 22(4):952–64. https://doi.org/10.1111/j.1523-1739.2008.00938.x
    » https://doi.org/10.1111/j.1523-1739.2008.00938.x
  • Fogliarini CO, Ferreira CEL, Bornholdt J, Barbosa MC, Giglio VJ, Bender MG. Telling the same story: Fishers and landing data reveal changes in fisheries on the Southeastern Brazilian Coast. PLoS ONE. 2021; 16(6):e0252391. https://doi.org/10.1371/journal.pone.0252391
    » https://doi.org/10.1371/journal.pone.0252391
  • Freire KMF, Carvalho-Filho A. Richness of common names of Brazilian reef fishes. Pan-Am J Aquat Sci. 2009; 4(2):96–145. Available from: https://panamjas.org/pdf_artigos/PANAMJAS_4(2)_96-145.pdf
    » https://panamjas.org/pdf_artigos/PANAMJAS_4(2)_96-145.pdf
  • Freire KMF, Almeida ZS, Amador JRET, Aragão JA, Araújo ARR, Ávila-da-Silva AO et al. Reconstruction of marine commercial landings for the Brazilian industrial and artisanal fisheries from 1950 to 2015. Front Mar Sci. 2021; 8:659110. https://doi.org/10.3389/fmars.2021.659110
    » https://doi.org/10.3389/fmars.2021.659110
  • Giglio VJ, Luiz OJ, Gerhardinger LC. Depletion of marine megafauna and shifting baselines among artisanal fishers in eastern Brazil. Anim Conserv. 2015; 18(4):348–58. https://doi.org/10.1111/acv.12178
    » https://doi.org/10.1111/acv.12178
  • Giovos I, Stoilas V-O, Al-Mabruk SAA, Doumpas N, Marakis P, Maximiadi M et al. Integrating local ecological knowledge, citizen science and long-term historical data for endangered species conservation: Additional records of angel sharks (Chondrichthyes: Squatinidae) in the Mediterranean Sea. Aquat Conserv. 2019; 29(6):881–90. https://doi.org/10.1002/aqc.3089
    » https://doi.org/10.1002/aqc.3089
  • Gonzáles-Mantilla PG, Gallagher AJ, León CJ, Vianna GMS. Economic impact and conservation potential of shark-diving tourism in the Azores Islands. Mar Policy. 2022; 135:104869. https://doi.org/10.1016/j.marpol.2021.104869
    » https://doi.org/10.1016/j.marpol.2021.104869
  • Hazin HV, Broadhurst MK, Amorim AF, Arfelli CA, Domingo A. Catches of pelagic sharks by subsurface longline fisheries in the South Atlantic Ocean during the last century: A review of available data with emphasis on Uruguay and Brazil. In: Camhi MD, Pikitch EK, Babcock EA, editors. Sharks of the open ocean: Biology, fisheries and conservation. Blackwell Publishing; 2008. p.213–29.
  • Instituto Brasileiro do Meio Ambiente e dos Recursos Naturais Renováveis (IBAMA). Estatística da Pesca. Grandes Regiões e Unidades da Federação. Brasília: IBAMA; 2007.
  • International Commission for the Conservation of Atlantic Tunas (ICCAT). Report of the 2017 ICCAT Shortfin Mako Assessment Meeting. Madrid, Spain 12-16 June 2017.
  • International Union for Conservation of Nature (IUCN). Standards and petitions committee. Guidelines for using the IUCN Red List categories and criteria. Version 15.1 [Internet]. Gland; 2022. Available from: http://www.iucnredlist.org/documents/RedListGuidelines.pdf
    » http://www.iucnredlist.org/documents/RedListGuidelines.pdf
  • Leduc AOHC, Carvalho FHD, Hussey NE, Reis-Filho JA, Longo GO, Lopes PFM. Local ecological knowledge to assist conservation status assessments in data poor contexts: a case study with the threatened sharks of the Brazilian Northeast. Biodivers Conserv. 2021; 30(3):819–45. https://doi.org/10.1007/s10531-021-02119-5
    » https://doi.org/10.1007/s10531-021-02119-5
  • Letessier TB, Bouchet PJ, Meeuwig JJ. Sampling mobile oceanic fishes and sharks: implications for fisheries and conservation planning. Biol Rev. 2017; 92(2):627–46. https://doi.org/10.1111/brv.12246
    » https://doi.org/10.1111/brv.12246
  • Martínez-Candelas IA, Pérez-Jiménez JC, Espinoza-Tenorio A, McClenachan L, Méndez-Loeza I. Use of historical data to assess changes in the vulnerability of sharks. Fish Res. 2020; 226:105526. https://doi.org/10.1016/j.fishres.2020.105526
    » https://doi.org/10.1016/j.fishres.2020.105526
  • McClenachan L. Historical declines in goliath grouper in south Florida. Endanger Species Res. 2009; 7:175–81. https://doi.org/10.3354/esr00167
    » https://doi.org/10.3354/esr00167
  • Ministério do Meio Ambiente (MMA). Instituto Chico Mendes de Conservação da Biodiversidade. Livro Vermelho da Fauna Brasileira Ameaçada de Extinção: Volume VI - Peixes. In: Instituto Chico Mendes de Conservação da Biodiversidade (Org.). In: Livro Vermelho da Fauna Brasileira Ameaçada de Extinção. Brasília: ICMBio; 2018.
  • Ministério do Meio Ambiente (MMA). Portaria MMA nº 148, de 7 de junho de 2022. Altera os Anexos da Portaria nº 443, de 17 de dezembro de 2014, da Portaria nº 444, de 17 de dezembro de 2014, e da Portaria nº 445, de 17 de dezembro de 2014, referentes à atualização da Lista Nacional de Espécies Ameaçadas de Extinção. 2022.
  • Ministério do Meio Ambiente (MMA). Portaria MMA nº 354, de 27 de janeiro de 2023. Revoga as Portarias MMA nº 299, de 13 de dezembro de 2022, e nº 300, de 13 de dezembro de 2022, e dá outras providências. Diário Oficial da União. 2023.
  • Myers RA, Worm B. Extinction, survival or recovery of large predatory fishes. Philos Trans R Soc Lond B Biol Sci. 2005; 360(1453):13–20. https://doi.org/10.1098/rstb.2004.1573
    » https://doi.org/10.1098/rstb.2004.1573
  • Nazareth E, D’Souza E, Arthur R, Jabado RW. Distribution of the Critically Endangered giant guitarfish (Glaucostegus typus) based on local ecological knowledge in the Andaman Islands, India. Ocean Coast Manag. 2022; 220:106075. https://doi.org/10.1016/j.ocecoaman.2022.106075
    » https://doi.org/10.1016/j.ocecoaman.2022.106075
  • Pacoureau N, Rigby CL, Kyne PM, Sherley RB, Winker H, Carlson JK et al. Half a century of global decline in oceanic sharks and rays. Nature. 2021; 589(7843):567–71. https://doi.org/10.1038/s41586-020-03173-9
    » https://doi.org/10.1038/s41586-020-03173-9
  • Paterson B. Integrating fisher knowledge and scientific assessments. Anim Conserv. 2010;13(6):536–37. https://doi.org/10.1111/j.1469-1795.2010.00419.x
    » https://doi.org/10.1111/j.1469-1795.2010.00419.x
  • Pincinato RBM, Gasalla MA, Garlock T, Anderson JL. Market incentives for shark fisheries. Mar Policy. 2022; 139:105031. https://doi.org/10.1016/j.marpol.2022.105031
    » https://doi.org/10.1016/j.marpol.2022.105031
  • QGIS Development Team. QGIS Geographic Information System. Version 3.16.2. Chicago, IL: Open-Source Geospatial Foundation Project; 2019. Available from: http://qgis.osgeo.org
    » http://qgis.osgeo.org
  • Rasalato E, Maginnity V, Brunnschweiler JM. Using local ecological knowledge to identify shark river habitats in Fiji (South Pacific). Environ Conserv. 2010; 37(1):90–97. https://www.jstor.org/stable/44520003
    » https://www.jstor.org/stable/44520003
  • R Development Core Team. R: A language and environment for statistical computing. Vienna, Austria: R Foundation for statistical Computing; 2019. Available from: https://www.r-project.org/
    » https://www.r-project.org/
  • Roff G, Doropoulos C, Rogers A, Bozec Y-M, Krueck NC, Aurellado E et al. The ecological role of sharks on coral reefs. Trends Ecol Evol. 2016; 31(5):395–407. https://doi.org/10.1016/j.tree.2016.02.014
    » https://doi.org/10.1016/j.tree.2016.02.014
  • Rogers R, Correal GO, Oliveira TC, Carvalho LL, Mazurek P, Barbosa JEF et al. Coral health rapid assessment in marginal reef sites. Mar Biol Res. 2014; 10(6):612–24. https://doi.org/10.1080/17451000.2013.841944
    » https://doi.org/10.1080/17451000.2013.841944
  • Sáenz-Arroyo A, Roberts CM, Torres J, Cariño-Olvera M. Using fishers’ anecdotes, naturalists’ observations and grey literature to reassess marine species at risk: the case of the Gulf grouper in the Gulf of California, Mexico. Fish Fish. 2005; 6(2):121–33. https://doi.org/10.1111/j.1467-2979.2005.00185.x
    » https://doi.org/10.1111/j.1467-2979.2005.00185.x
  • Silvano RAM, Nora V, Andreoli TB, Lopes PFM, Begossi A. The ‘ghost of past fishing’: small-scale fisheries and conservation of threatened groupers in subtropical islands. Mar Policy. 2017; 75:125–32. https://doi.org/10.1016/j.marpol.2016.10.002
    » https://doi.org/10.1016/j.marpol.2016.10.002
  • Stevens JD. The biology and ecology of the shortfin mako shark, Isurus oxyrinchus. In: Camhi MD, Pikitch EK, Babcock EA, editors. Sharks of the open ocean: biology, fisheries and conservation. Blackwell Publishing; 2008. p.87–94.
  • Taylor SM, Braccini JM, Bruce BD, McAuley RB. Reconstructing Western Australian white shark (Carcharodon carcharias) catches based on interviews with fishers. Mar Freshw Res. 2017; 69(3):366–75. https://doi.org/10.1071/MF17140
    » https://doi.org/10.1071/MF17140
  • Tesfamichael D, Pitcher TJ, Pauly D. Assessing changes in fisheries using fishers’ knowledge to generate long time series of catch rates: a case study from the Red Sea. Ecol Soc. 2014; 19(1):18. http://dx.doi.org/10.5751/ES-06151-190118
    » http://dx.doi.org/10.5751/ES-06151-190118
  • Torres P, Bolhão N, Cunha RT, Vieira JAC, Rodrigues AS. Dead or alive: The growing importance of shark diving in the Mid-Atlantic region. J Nat Conserv. 2017; 36:20–28. https://doi.org/10.1016/j.jnc.2017.01.005
    » https://doi.org/10.1016/j.jnc.2017.01.005
  • Valentin JL. The Cabo Frio upwelling system, Brazil. In: Seeliger U, Kjerfve B, editors. Coastal marine ecosystems of Latin America. Ecological Studies (Analysis and Synthesis). Springer; 2001.
  • Venkatachalam AJ, Price ARG, Chandrasekara S, Senaratna Sellamuttu S, Kaler J. Changes in frigate tuna populations on the south coast of Sri Lanka: evidence of the shifting baseline syndrome from analysis of fisher observations. Aquat Conserv Mar Freshw Ecosyst. 2010; 20(2):167–76. https://doi.org/10.1002/aqc.1068
    » https://doi.org/10.1002/aqc.1068
  • Vianna GMS, Meekan MG, Rogers AA, Kragt ME, Alin JM, Zimmerhackel JS. Shark-diving tourism as a financing mechanism for shark conservation strategies in Malaysia. Mar Policy. 2018; 94:220–26. https://doi.org/10.1016/j.marpol.2018.05.008
    » https://doi.org/10.1016/j.marpol.2018.05.008
  • Vooren CM, Klippel S,editors. Ações para a conservação de tubarões e raias no sul do Brasil. Sandro Klippel; 2005.
  • Worm B, Davis B, Kettemer L, Ward-Paige CA, Chapman D, Heithaus MR et al. Global catches, exploitation rates, and rebuilding options for sharks. Mar Policy. 2013; 40:194–204. https://doi.org/10.1016/j.marpol.2012.12.034
    » https://doi.org/10.1016/j.marpol.2012.12.034
  • Yokota L, Lessa RP. A nursery area for sharks and rays in Northeastern Brazil. Environ Biol Fish. 2006; 75:349–60. https://doi.org/10.1007/s10641-006-0038-9
    » https://doi.org/10.1007/s10641-006-0038-9
  • Zimmerhackel JS, Kragt ME, Rogers AA, Ali K, Meekan MG. Evidence of increased economic benefits from shark-diving tourism in the Maldives. Mar Policy. 2019; 100:21–26. https://doi.org/10.1016/j.marpol.2018.11.004
    » https://doi.org/10.1016/j.marpol.2018.11.004

ADDITIONAL NOTES

  • HOW TO CITE THIS ARTICLE

    Fogliarini CO, Giglio VJ, Bender MG, Ferreira CEL. Multidecadal fishers’ knowledge reveals overexploitation of sharks in southeastern Brazil. Neotrop Ichthyol. 2024; 22(1):e230087. https://doi.org/10.1590/1982-0224-2023-0087

Edited-by

Toby Daly-Engel

Data availability

Data citations

R Development Core Team. R: A language and environment for statistical computing. Vienna, Austria: R Foundation for statistical Computing; 2019. Available from: https://www.r-project.org/

Publication Dates

  • Publication in this collection
    08 Mar 2024
  • Date of issue
    2024

History

  • Received
    25 July 2023
  • Accepted
    20 Nov 2023
Sociedade Brasileira de Ictiologia Neotropical Ichthyology, Núcleo de Pesquisas em Limnologia, Ictiologia e Aquicultura, Universidade Estadual de Maringá., Av. Colombo, 5790, 87020-900, Phone number: +55 44-3011-4632 - Maringá - PR - Brazil
E-mail: neoichth@nupelia.uem.br