Scientia Marina 87 (1)
March 2023, e059
ISSN: 0214-8358, eISSN: 1886-8134
https://doi.org/10.3989/scimar.05322.059

Life history and population dynamics of the enigmatic tanaid Chondrochelia dubia (Tanaidacea: Leptocheliidae) in a tropical seaweed bed

Ciclo de vida y dinámica poblacional de la enigmática tanaide Chondrochelia dubia (Tanaidacea: Leptocheliidae) en un lecho de algas tropicales

Rodrigo V. A. Alves

Laboratório de Bentos, Departamento de Oceanografia, Universidade Federal de Pernambuco, Av. Prof. Moraes Rego, 1235, 50740-550, Recife, Pernambuco, Brazil.

https://orcid.org/0000-0002-3288-5582

Flávia Lucena Frédou

Laboratório de Estudos de Impactos Antrópicos na Biodiversidade marinha e Estuarina, Departamento de Pesca e Aquicultura, Universidade Federal Rural de Pernambuco. Rua Manuel de Medeiros, s/n, 52171-900, Recife, Pernambuco, Brazil.

https://orcid.org/0000-0001-5492-7205

Nykon Craveiro

Laboratório de Bentos, Departamento de Oceanografia, Universidade Federal de Pernambuco, Av. Prof. Moraes Rego, 1235, 50740-550, Recife, Pernambuco, Brazil.

https://orcid.org/0000-0001-8296-5217

Leandro Nolé Eduardo

Research Unit of Marine Biodiversity, Exploitation and Conservation (MARBEC), Univ. Montpellier, CNRS, Ifremer, IRD, Sète, France.

https://orcid.org/0000-0003-2369-4175

José S. Rosa Filho

Laboratório de Bentos, Departamento de Oceanografia, Universidade Federal de Pernambuco, Av. Prof. Moraes Rego, 1235, 50740-550, Recife, Pernambuco, Brazil.
The Marine Biological Association of the UK, The Citadel Hill Laboratory, Plymouth, Devon, PL1 2PB, UK.

https://orcid.org/0000-0002-5496-7706

Summary

The present study describes the population dynamics and life history parameters of the enigmatic tanaid Chondrochelia dubia collected in Paiva Beach, tropical coast of Brazil. The region was impacted by a large, unexpected oil spill from August to October 2019. Samples were taken monthly between July 2019 and July 2020 in beds of the red seaweed Jania capillacea. The abundance of individuals was negatively correlated with monthly rainfall, with higher abundances in drier months. There was an unexpected significant drop in abundance in September, possibly caused by contact with the crude oil, but the population recovered fully within two months. The parameters of the von Bertallanfy growth equation, calculated for the first time for the species, were Linf =5.26 mm; k=3.36 year-1; t0=0.0. Compared with other studies, the specimens are very small (2.04 ± 0.95 mm in length), females reach sexual maturity very early (L50=2.3 mm), and natural mortality is high (Z=M=5.77 year-1), indicating an opportunistic life strategy. This study reinforces the bioindication potential of C. dubia and the use of bootstrapped length-based methods to estimate key population parameters in small marine invertebrates.

Keywords: 
epifauna; Peracarida; Brazilian oil spill; reef; macroalgae; leptocheliids
Resumen

El presente estudio describió la dinámica poblacional y los parámetros del ciclo de vida del enigmático tanaidáceo Chondrochelia dubia recolectado en la playa de Paiva, costa tropical de Brasil. La región se vio afectada por un gran derrame de petróleo inesperado de agosto a octubre de 2019. Se tomaron muestras mensualmente entre julio de 2019 y julio de 2020 en lechos de algas rojas Jania capillacea. La abundancia de individuos se correlacionó negativamente con la precipitación mensual, con mayor abundancia en los meses más secos. Hubo una inesperada caída significativa de la abundancia en septiembre, posiblemente causada por el contacto con el petróleo crudo, sin embargo, la población se recuperó por completo en dos meses. Los parámetros de la ecuación de crecimiento de von Bertallanfy, calculados por primera vez para la especie, fueron: Linf =5.26 mm; k=3.36 año-1; t0=0,0. En comparación con otros estudios, los ejemplares son muy pequeños (2.04 ± 0.95 mm de longitud), las hembras alcanzan la madurez sexual muy temprano (L50=2.3 mm), y la mortalidad natural es relativamente alta (Z=M=5.77 año-1), lo que indica una estrategia de vida oportunista. Este estudio refuerza el potencial de bioindicación de C. dubia y el uso de métodos bootstrap basados en la longitud para estimar parámetros de población clave en pequeños invertebrados marinos.

Palabras clave: 
epifauna; Peracarida; derrame de petróleo brasileño; arrecife; macroalgae; leptoquelidos

Received: July  29,  2022. Accepted: December  9,  2022. Published: March  6,  2023

Editor: J.S. Troncoso.

Citation/Cómo citar este artículo: Alves R.V.A., Frédou F.L., Craveiro N., Eduardo L.N., Rosa Filho J.S. 2023. Life history and population dynamics of the enigmatic tanaid Chondrochelia dubia (Tanaidacea: Leptocheliidae) in a tropical seaweed bed. Sci. Mar. 87(1): e059.  https://doi.org/10.3989/scimar.05322.059

CONTENT

INTRODUCTION

 

Marine vegetated habitats such as seaweed and seagrass beds harbour diverse and abundant epifaunal communities as they act as shelter, feeding and reproduction grounds for many species ( Carvalho et al. 2018 Carvalho N., Grande H., Rosa Filho J., Jacobucci G. 2018. The structure of gammarid amphipod (Crustacea, Peracarida) assemblages associated with Sargassum (Phaeophyta, Fucales) and their link with the structural complexity of algae. Hydrobiologia. 820: 245-254. https://doi.org/10.1007/s10750-018-3661-5 , Martínez-Laiz et al. 2018 Martínez-Laiz G., Ros M., Navarro-Barranco C., Guerra-García J. 2018. Habitat selection of intertidal caprellid amphipods in a changing scenario. Behav. Process. 153: 16-24. https://doi.org/10.1016/j.beproc.2018.05.005 , Tano et al. 2016 Tano S., Eggertsen M., Wikström S., et al. 2016. Tropical seaweed beds are important habitats for mobile invertebrate epifauna. Estuar. Coast. Shelf Sci. 183: 1-12. https://doi.org/10.1016/j.ecss.2016.10.010 ). Epifauna is usually dominated by crustaceans of the superorder Peracarida, such as amphipods, isopods and tanaids ( Carvalho et al. 2018 Carvalho N., Grande H., Rosa Filho J., Jacobucci G. 2018. The structure of gammarid amphipod (Crustacea, Peracarida) assemblages associated with Sargassum (Phaeophyta, Fucales) and their link with the structural complexity of algae. Hydrobiologia. 820: 245-254. https://doi.org/10.1007/s10750-018-3661-5 , Tano et al. 2016 Tano S., Eggertsen M., Wikström S., et al. 2016. Tropical seaweed beds are important habitats for mobile invertebrate epifauna. Estuar. Coast. Shelf Sci. 183: 1-12. https://doi.org/10.1016/j.ecss.2016.10.010 ). These organisms contribute to the elevated secondary production in macrophyte habitats and act as an important link between primary producers and consumers from higher trophic levels ( Tano et al. 2016 Tano S., Eggertsen M., Wikström S., et al. 2016. Tropical seaweed beds are important habitats for mobile invertebrate epifauna. Estuar. Coast. Shelf Sci. 183: 1-12. https://doi.org/10.1016/j.ecss.2016.10.010 ). Tanaidacea is a diverse order of small peracarid crustaceans with more than 1500 described species worldwide, which occur from intertidal to abyssal zones, inhabiting soft, interstitial and biogenic substrates in a wide variety of ecosystems (e.g. estuaries, mangroves, seagrass meadows, coral reefs and deep sea) ( Blazewicz-Paszkowycz et al. 2012 Blazewicz-Paszkowycz M., Bamber R., Anderson G. 2012. Diversity of Tanaidacea (Crustacea: Peracarida) in the world’s oceans - how far have we come? PLoS ONE. 7: 1-11. https://doi.org/10.1371/journal.pone.0033068 , Kakui et al. 2021 Kakui K., Fleming J., Mori M., et al. 2021. Comprehensive Transcriptome Sequencing of Tanaidacea with Proteomic Evidences for Their Silk. Genome Biol. Evol. 13: 1-11. https://doi.org/10.1093/gbe/evab281 ).

Several complex reproductive and parental behaviours have been observed in Tanaidacea, such as ritualistic fights between males, courtship and the maintenance of a brood nursery for “newborn” larvae ( Buckle Ramirez 1965 Buckle Ramirez L.F. 1965. Untersuchungen über die Biologie von Heterotanais oerstedi Kröyer (Crustacea, Tanaidacea). Zeitschrift Für Morphologie Und Ökologie Der Tiere. 55: 714-482. https://doi.org/10.1007/BF00406235 , Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 , Johnson and Attramadal 1982 Johnson S., Attramadal Y. 1982. Reproductive Behaviour and Larval Development of Tanais cavolinii (Crustacea: Tanaidacea). Mar. Biol. 71: 11-16. https://doi.org/10.1007/BF00396987 ). In tube-dwelling species such as Chondrochelia dubia and Tanais dulongii, successful males enter the female tube, where copulation takes place ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 , Johnson and Attramadal 1982 Johnson S., Attramadal Y. 1982. Reproductive Behaviour and Larval Development of Tanais cavolinii (Crustacea: Tanaidacea). Mar. Biol. 71: 11-16. https://doi.org/10.1007/BF00396987 ). Fertilized eggs develop within the female marsupium until the first postmarsupial stage (manca II) is achieved ( Masunari 1983) Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 . In Tanais dulongii, released manca II larvae keep contact with the mother until manca III stage, when they leave the mother’s brood nursery to build their own tubes ( Johnson and Attramadal 1982 Johnson S., Attramadal Y. 1982. Reproductive Behaviour and Larval Development of Tanais cavolinii (Crustacea: Tanaidacea). Mar. Biol. 71: 11-16. https://doi.org/10.1007/BF00396987 ). Tanaid postmarsupial development is usually divided into two or three larval (manca) stages, neutrum, and preparatory and copulatory males and females, with slight variations ( Holdich and Jones 1983 Holdich D., Jones J. 1983. Tanaids (Synopses of the British Fauna) (Vol. 27). Cambridge University Press, Cambridge, 112 pp., Leite et al. 2003 Leite F., Turra A., Souza, E. 2003. Population biology and distribution of the tanaid Kalliapseudes schubarti Mañé-Garzon, 1949, in an intertidal flat in southeastern Brazil. Braz. J. Biol. 63: 469-479. https://doi.org/10.1590/S1519-69842003000300013 , Toniollo and Masunari 2007 Toniollo V., Masunari S. 2007. Postmarsupial development of Sinelobus stanfordi (Richardson, 1901) (Tanaidacea: Tanaidae). Nauplius. 15: 15-41.).

Leptocheliids such as Chondrochelia dubia ( Krøyer, 1842 Krøyer H. 1842. Nye Arter af Slaegten Tanais. Naturhistorisk Tidsskrift Ser. I. 4: 167-188.) are frequently found in high abundance in many shallow-water habitats such as seaweeds, corals and soft sediment worldwide ( Guțu 2016 Guțu M. 2016. Systematic Novelties of the Enigmatic Universe of the Leptocheliids: Crustacea: Tanaidacea. ePublishers, Bucharest, 205 pp., Mendoza 1982 Mendoza J. 1982. Some Aspects of the Autecology of Leptochelia dubia (Krøyer, 1842) (Tanaidacea). Crustaceana. 43: 225-240. https://doi.org/10.1163/156854082X00164 , Stoner 1986 Stoner A. 1986. Cohabitation on Algal Habitat Islands by Two Hermaphroditic Tanaidacea (Crustacea: Peracarida). J. Crustac. Biol. 6: 719-728. https://doi.org/10.1163/193724086X00523 ). These organisms are typically tube-dwellers that build their tubes from sediment particles and faecal pellets held together by secreted mucus with the help of the pereopods ( Krasnow and Taghon 1997 Krasnow L., Taghon, G. 1997. Rate of tube building and sediment particle size selection during tube construction by the tanaid crustacean, Leptochelia dubia. Estuaries. 20: 534-546. https://doi.org/10.2307/1352612 , Mendoza 1982 Mendoza J. 1982. Some Aspects of the Autecology of Leptochelia dubia (Krøyer, 1842) (Tanaidacea). Crustaceana. 43: 225-240. https://doi.org/10.1163/156854082X00164 ). Most tanaids are raptorial feeders that consume detritus and its associated organisms (e.g. diatoms, bacteria and nematodes) by seizing and breaking up food particles with their mouthparts ( Holdich and Jones 1983 Holdich D., Jones J. 1983. Tanaids (Synopses of the British Fauna) (Vol. 27). Cambridge University Press, Cambridge, 112 pp.). As in other species of Leptocheliidae, C. dubia show strong sexual dimorphism, with males having much larger antennules (first antenna), chelae, eyes and walking legs (pereopods) ( Bamber 2010 Bamber R. 2010. In the footsteps of Henrik Nikolaj Krøyer: The rediscovery and redescription of Leptochelia savignyi (Krøyer, 1842) sensu stricto (Crustacea: Tanaidacea: Leptocheliidae). Proc. Biol. Soc. Wash. 123: 289-311. https://doi.org/10.2988/10-14.1 , Mendoza 1982 Mendoza J. 1982. Some Aspects of the Autecology of Leptochelia dubia (Krøyer, 1842) (Tanaidacea). Crustaceana. 43: 225-240. https://doi.org/10.1163/156854082X00164 , Stoner 1986 Stoner A. 1986. Cohabitation on Algal Habitat Islands by Two Hermaphroditic Tanaidacea (Crustacea: Peracarida). J. Crustac. Biol. 6: 719-728. https://doi.org/10.1163/193724086X00523 ). The female has short antennules with only three longer articles and also short gnathopods with small chelae, whereas the male has large gnathopods with a prominent propodus and each antennule has a long flagellum. Males also have reduced mouthparts ( Gardiner 1975 Gardiner L. 1975. The Systematics, Postmarsupial Development, and Ecology of the Deep-Sea Family Neotanaidae (Crustacea: Tanaidacea) (Vol. 170). Smithsonian Institution Press, City of Washington, 274 pp . https://doi.org/10.5479/si.00810282.170 ).

The taxonomic history of Chondrochelia dubia goes back to over 180 years ago when Krøyer (1842) Krøyer H. 1842. Nye Arter af Slaegten Tanais. Naturhistorisk Tidsskrift Ser. I. 4: 167-188. described Tanais dubia (now C. dubia) from specimens collected in Salvador, northeastern Brazil, and Tanais savignyi (now C. savignyi) from Madeira, Portugal. These species were later transferred to the genus Leptochelia, and then Chondrochelia by Guțu (2016) Guțu M. 2016. Systematic Novelties of the Enigmatic Universe of the Leptocheliids: Crustacea: Tanaidacea. ePublishers, Bucharest, 205 pp.. In the last century, many new species of the genus were described, while the Brazilian taxon Chondrochelia dubia was “found” in very distinct places worldwide ( Bamber 2010 Bamber R. 2010. In the footsteps of Henrik Nikolaj Krøyer: The rediscovery and redescription of Leptochelia savignyi (Krøyer, 1842) sensu stricto (Crustacea: Tanaidacea: Leptocheliidae). Proc. Biol. Soc. Wash. 123: 289-311. https://doi.org/10.2988/10-14.1 ). Most of these species were synonymized under the wide “Leptochelia dubia group”, which may include several cryptic species in many continents ( Bamber 2010) Bamber R. 2010. In the footsteps of Henrik Nikolaj Krøyer: The rediscovery and redescription of Leptochelia savignyi (Krøyer, 1842) sensu stricto (Crustacea: Tanaidacea: Leptocheliidae). Proc. Biol. Soc. Wash. 123: 289-311. https://doi.org/10.2988/10-14.1 . All members of the “Leptochelia dubia group” were then synonymized under the cosmopolitan L. dubia by Sieg (1983), which started a debate over whether the senior synonym should be L. dubia or L. savignyi ( Bamber 2010 Bamber R. 2010. In the footsteps of Henrik Nikolaj Krøyer: The rediscovery and redescription of Leptochelia savignyi (Krøyer, 1842) sensu stricto (Crustacea: Tanaidacea: Leptocheliidae). Proc. Biol. Soc. Wash. 123: 289-311. https://doi.org/10.2988/10-14.1 ). Two major efforts were recently made to solve the problematic “Leptochelia dubia group”: Bamber (2010) Bamber R. 2010. In the footsteps of Henrik Nikolaj Krøyer: The rediscovery and redescription of Leptochelia savignyi (Krøyer, 1842) sensu stricto (Crustacea: Tanaidacea: Leptocheliidae). Proc. Biol. Soc. Wash. 123: 289-311. https://doi.org/10.2988/10-14.1 made a redescription of C. savignyi and synonymized some North Atlantic and Mediterranean species under C. savignyi, and a robust revision made by Guțu (2016) Guțu M. 2016. Systematic Novelties of the Enigmatic Universe of the Leptocheliids: Crustacea: Tanaidacea. ePublishers, Bucharest, 205 pp. added a new subfamily, seven genera and 21 species to the Leptocheliidae family. Consequently, the “Leptochelia dubia group” was to a large extent dissolved into several different taxa, including the “Brazilian species” discovered by Krøyer (1842) Krøyer H. 1842. Nye Arter af Slaegten Tanais. Naturhistorisk Tidsskrift Ser. I. 4: 167-188. that is now named Chondrochelia dubia. It is now evident that C. savignyi and C. dubia should no longer be considered synonymous ( Bamber 2010 Bamber R. 2010. In the footsteps of Henrik Nikolaj Krøyer: The rediscovery and redescription of Leptochelia savignyi (Krøyer, 1842) sensu stricto (Crustacea: Tanaidacea: Leptocheliidae). Proc. Biol. Soc. Wash. 123: 289-311. https://doi.org/10.2988/10-14.1 , Jarquín-González and Carrera-Parra 2022 Jarquín-González J., Carrera-Parra L. 2022. Chondrochelia Guţu, 2016 (Crustacea, Peracarida, Tanaidacea, Leptocheliidae) from North America: new species, redescription and distribution using morphological and molecular data. PeerJ. 10: 1-47. https://doi.org/10.7717/peerj.12773 ) and that C. dubia is not a cosmopolitan species, since Jarquín-González and Carrera-Parra (2022) Jarquín-González J., Carrera-Parra L. 2022. Chondrochelia Guţu, 2016 (Crustacea, Peracarida, Tanaidacea, Leptocheliidae) from North America: new species, redescription and distribution using morphological and molecular data. PeerJ. 10: 1-47. https://doi.org/10.7717/peerj.12773 recently rejected its hypothetical occurrence in the Mexican Caribbean and Gulf Coast with molecular data.

Though it is very common in several shallow-water environments, only a few studies have focused on the population dynamics of Leptocheliidae ( Buckle Ramirez 1965 Buckle Ramirez L.F. 1965. Untersuchungen über die Biologie von Heterotanais oerstedi Kröyer (Crustacea, Tanaidacea). Zeitschrift Für Morphologie Und Ökologie Der Tiere. 55: 714-482. https://doi.org/10.1007/BF00406235 , Masunari 1983 Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 , Modlin and Harris 1989 Modlin R., Harris P. 1989. Observations on the natural history and experiments on the reproductive strategy of Hargeria rapax (Tanaidacea). J. Crustac. Biol. 9: 678-586. https://doi.org/10.1163/193724089X00593 , Stoner 1986 Stoner A. 1986. Cohabitation on Algal Habitat Islands by Two Hermaphroditic Tanaidacea (Crustacea: Peracarida). J. Crustac. Biol. 6: 719-728. https://doi.org/10.1163/193724086X00523 ). Population dynamics studies combined with life histories and morphometric data are powerful tools for understanding ecosystem function at different spatial and temporal scales, managing harvested and threatened species, and quantifying biotic responses to environmental change ( Pennafirme and Soares-Gomes 2009 Pennafirme S., Soares-Gomes A. 2009. Population biology and reproduction of Kalliapseudes schubartii Mañé-Garzón, 1949 (Peracarida, Tanaidacea) in a tropical coastal Lagoon, Itaipu, Southeastern Brazil. Crustaceana 82: 1509-1526. https://doi.org/10.1163/001121609X12487811051589 , Rumbold et al. 2015 Rumbold C., Obenat S., Spivak E. 2015. Comparison of life history traits of Tanais dulongii (Tanaidacea: Tanaididae) in natural and artificial marine environments of the south-western Atlantic. Helgol. Mar. Res. 69: 231-242. https://doi.org/10.1007/s10152-015-0432-9 ). In late 2019, the Brazilian coast was heavily impacted by the largest oil spill in tropical oceans so far ( Soares et al. 2020 Soares M., Teixeira C., Bezerra L., et al. 2020. Oil spill in South Atlantic (Brazil): Environmental and governmental disaster. Marine Policy. 115: 1-8. https://doi.org/10.1016/j.marpol.2020.103879 ), enabling us to study the potential impacts of this disaster in coastal marine biota. Herein, we aim to describe the population dynamics and life history parameters of Chondrochelia dubia on the northeast coast of Brazil (Paiva Beach). Additionally, we make inferences about the effects of the 2019 oil spill on the populations of C. dubia. This is also the first study to estimate the natural mortality rate, longevity, maturation and parameters of von Bertalanffy’s growth equation (L , k and t 0) for the tanaid C. dubia. Unlike previous studies on Tanaidacea, we used robust bootstrapped versions of the classical length-based methods to quantify key population parameters.

MATERIALS AND METHODS

 

Study area

 

Paiva Beach (8°16’S, 34°56’W) is an open ocean tropical sandy beach approximately 7.8 km long located in the Cabo de Santo Agostinho municipality (Pernambuco State, northeast Brazil) (Holanda 2020). The sandstone reefs of Paiva Beach are elongated and occur parallel to the shore ( Laborel 1970 Laborel J. 1970. Les peuplements de madréporaires des côtes tropicales du Brésil. Annales de l’Universit’e d’Abidjan (Ecologie), Abidjan, 265 pp.). The reef line closest to the beach is 2.5 km long and 1 km wide and densely colonized by macroalgal assemblages that are typically found in the tropical phycogeographic region ( Horta et al. 2001 Horta P., Amancio E. Coimbra C., Oliveira E. 2001. Considerações sobre a distribuição e origem da flora de macroalgas marinhas brasileiras. Hoehnea. 28: 243-265.). The climate is tropical hot/humid, with average annual temperatures above 25°C throughout the year ( Domingues et al. 2017 Domingues E.C., Schettini C.A.F., Truccolo E.C., Oliveira Filho J.C. de. 2017. Hidrografia e correntes da Plataforma Continental de Pernambuco. Rev. Bras. de Recur. Hidr. 22: 1-17. https://doi.org/10.1590/2318-0331.0217170027 ). The tidal regime can be classified as a mesotidal semi-diurnal type, with tide height averaging 0.7 m (neap tide) to 2.5 m (spring tide) ( Domingues et al. 2017 Domingues E.C., Schettini C.A.F., Truccolo E.C., Oliveira Filho J.C. de. 2017. Hidrografia e correntes da Plataforma Continental de Pernambuco. Rev. Bras. de Recur. Hidr. 22: 1-17. https://doi.org/10.1590/2318-0331.0217170027 ). The reefs and their diverse intertidal communities were severely impacted by the 2019 Brazilian Oil Spill. In only one week (19-28 October 2019), more than 1000 t of crude oil were collected from the Cabo de Santo Agostinho municipality alone ( Craveiro et al. 2021 Craveiro N., Alves R., Menezes J., et al. 2021. Immediate effects of the 2019 oil spill on the macrobenthic fauna associated with macroalgae on the tropical coast of Brazil. Mar. Pollut. Bull. 165: 1-8. https://doi.org/10.1016/j.marpolbul.2021.112107 ). Although less perceptible, oil strains started appearing in Pernambuco’s beaches in August 2019 ( Soares et al. 2020 Soares M., Teixeira C., Bezerra L., et al. 2020. Oil spill in South Atlantic (Brazil): Environmental and governmental disaster. Marine Policy. 115: 1-8. https://doi.org/10.1016/j.marpol.2020.103879 ), months before the main sheet of crude oil arrived at Paiva Beach.

Sampling design and laboratory procedures

 

Sampling was performed monthly from July 2019 to July 2020. In March 2020, samples were not taken because of COVID-19 lockdown restrictions. On each sampling occasion, ten fronds of the red seaweed Jania capillacea were collected in intertidal tide pools. The fronds were wrapped with plastic bags to prevent motile animals from escaping and then removed from the substrate. Samples were fixed with 4% saline formalin. In the laboratory, the samples were sieved (0.3 mm mesh size) and the retained epifaunal organisms were sorted under the stereomicroscope. Specimens of C. dubia were separated, counted and preserved in 70% ethanol. For each month, approximately 120 to 170 individuals were randomly chosen (in some months fewer than 120 individuals were found) to be measured from the tip of the carapace to the end of the telson with a stereo microscope with an eyepiece reticle (body length, mm). For males, the length and width of chelae were measured. The individuals were classified into five categories, as proposed by Masunari (1983) Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 : juveniles/mancas (larval MII and MIII stages); pre-ovigerous (preparatory) females (those with oostegites); ovigerous females (those with marsupia); non-reproductive females (those with adult appearance but no sign of reproductive activity); and males (those with characteristic male features) ( Fig. 1 ).

medium/medium-SCIMAR-87-01-e059-gf1.png
Fig. 1.  - Fixed specimens of Chondrochelia dubia (Krøyer, 1842) collected in Paiva Beach, northeastern Brazil: adult male (♂) (left); manca III juvenile (centre) and ovigerous female () (right). L, chela length; W, chela width. Scale bar, 1 mm.

Statistical analysis

 

Monthly densities and lengths of C. dubia were log-transformed and compared by one-way ANOVA followed by pairwise Tukey tests. Chi-square tests (χ2) were performed to compare sex ratio between months and size classes. The parameters of the von Bertalanffy growth function (VBGF) were estimated through the ELEFAN_GA_Boot method, which is based on a bootstrapped genetic algorithm that provides a range of likely best fits for the VBGF parameters ( Schwamborn et al. 2019 Schwamborn R., Mildenberger T., Taylor, M. 2019. Assessing sources of uncertainty in length-based estimates of body growth in populations of fishes and macroinvertebrates with bootstrapped ELEFAN. Ecol. Modell. 393: 37-51. https://doi.org/10.1016/j.ecolmodel.2018.12.001 ). This approach is highly applicable for rapid assessment in data-poor situations such as data collected from short time periods (e.g. one year) ( Mildenberger et al. 2017 Mildenberger T., Taylor M., Wolff M. 2017. TropFishR: an R package for fisheries analysis with length-frequency data. Methods Ecol. Evol. 8: 1520-1527 https://doi.org/10.1111/2041-210X.12791 ). Intervals of L, k and t0 (pooled data) were chosen based on published studies about similar species from the southwestern Atlantic Ocean ( Almeida 1994 Almeida M. 1994. Kalliapseudes schubartii Mañé-Garzón, 1949 (Tanaidecea-Crustacea): Dinâmica populacional e interações com a macrofauna bêntica no Saco do Limoeiro, Ilha do Mel (Paraná, Brasil). MSc thesis, Universidade Federal do Paraná, 75pp., Fonseca and D’Incao 2003 Fonseca D., D’Incao F. 2003. Growth and reproductive parameters of Kalliapseudes schubartii in the estuarine region of the Lagoa dos Patos (southern Brazil). J. Mar. Biolog. Assoc. U.K. 83: 931-935. https://doi.org/10.1017/S0025315403008087h , Leite et al. 2003 Leite F., Turra A., Souza, E. 2003. Population biology and distribution of the tanaid Kalliapseudes schubarti Mañé-Garzon, 1949, in an intertidal flat in southeastern Brazil. Braz. J. Biol. 63: 469-479. https://doi.org/10.1590/S1519-69842003000300013 , Pennafirme and Soares-Gomes 2017 Pennafirme S., Soares-Gomes A. 2017. Population dynamics and secondary production of a key benthic tanaidacean, Monokalliapseudes schubarti (Mañé-Garzón, 1949) (Tanaidacea, Kalliapseudidae), from a tropical coastal lagoon in southeastern Brazil. Crustaceana. 90: 1483-1499. https://doi.org/10.1163/15685403-00003704 , Rumbold et al. 2015 Rumbold C., Obenat S., Spivak E. 2015. Comparison of life history traits of Tanais dulongii (Tanaidacea: Tanaididae) in natural and artificial marine environments of the south-western Atlantic. Helgol. Mar. Res. 69: 231-242. https://doi.org/10.1007/s10152-015-0432-9 ). Analyses were made in the TropFishR ( Mildenberger et al. 2017 Mildenberger T., Taylor M., Wolff M. 2017. TropFishR: an R package for fisheries analysis with length-frequency data. Methods Ecol. Evol. 8: 1520-1527 https://doi.org/10.1111/2041-210X.12791 ) and fishboot ( Schwamborn et al. 2019 Schwamborn R., Mildenberger T., Taylor, M. 2019. Assessing sources of uncertainty in length-based estimates of body growth in populations of fishes and macroinvertebrates with bootstrapped ELEFAN. Ecol. Modell. 393: 37-51. https://doi.org/10.1016/j.ecolmodel.2018.12.001 ) packages.

The growth performance index (Φ’) was calculated from von Bertalanffy’s equation parameters as Pauly and Munro (1984) Pauly D., Munro J. 1984. Once more on the comparison of growth in fish and invertebrates. Fishbyte. 2: 1-21.:

ϕ = log k + 2 log L i n f  

The length at which 50% of females are sexually mature (L50) was estimated through a logistic function using two sets of variables: length-frequency (LFQ) data and categorical “gonadal maturation stages” ( Torrejon-Magallanes 2020 Torrejon-Magallanes J. 2020. sizeMat: Estimate Size at Sexual Maturity (R package version 1.1.2).). Since the mean length of the individuals at MIII stage (1.75 mm) is lower than the smallest reproductive female (2.1 mm), all specimens in this category were treated as “immature”. L50 was calculated as

P i = A 1 + e - r L t - L 50 - 1  

where Pi is the proportion of reproductive females for each (0.2 mm) size class; A is the curve asymptote; r is a rate parameter related to the speed of size change from non-reproductive to reproductive status; Lt is the total length (mm); and L50 is the size at first maturity (mm) ( Fontoura et al. 2009 Fontoura N., Braun A., Milani P. 2009. Estimating size at first maturity (L50) from Gonadossomatic Index (GSI) data. Neotrop. Ichthyol. 7: 217-222. https://doi.org/10.1590/S1679-62252009000200013 ).

Morphometric maturity in males was estimated using a regression analysis where X (body length) is considered the explanatory variable and the classification of maturity (juveniles, 0; adults, 1) is considered the response variable (binomial) through the form ( Torrejon-Magallanes 2020 Torrejon-Magallanes J. 2020. sizeMat: Estimate Size at Sexual Maturity (R package version 1.1.2).):

P c s = 1 / 1 + e - ( β 0 + β 1 X )  

where Pcs is the probability of an individual being mature at a determinate X length. β0 (intercept) and β1 (slope) are estimated parameters. Both gonadal (females) and morphometric (males) maturities were calculated using the “sizeMat” package ( Torrejon-Magallanes 2020 Torrejon-Magallanes J. 2020. sizeMat: Estimate Size at Sexual Maturity (R package version 1.1.2).).

The instantaneous mortality rate (Z) was calculated through a linear capture curve based on length composition data ( Sparre and Venema 1998 Sparre P., Venema S. 1998. Introduction to tropical fish stock assessment - Part I: Manual. FAO, Rome, 423 pp.). Estimates for maximum individual age within the population were based on Taylor (1958) Taylor C. 1958. Cod Growth and Temperature. ICES J. Mar. Sci. 23: 366-370. https://doi.org/10.1093/icesjms/23.3.366 . The maximum longevity (tmax) was calculated from 95% of the asymptotic length, where

t m a x = ( 2.996 / k ) + t 0  

All data analyses were performed using R software ( R Core Team 2022 R Core Team. 2022. R: A language and environment for statistical computing.). For all tests a significance level of 5% was considered.

RESULTS

 

A total of 1513 individuals (583 females, 34 males and 896 mancas) were included in the analysis. The abundance of C. dubia varied significantly between months (F=10.55; p<0.01) and was negatively correlated with monthly rainfall (S=458, Rho=-0.601; p=0.04). Months with the highest abundances were August, November and December 2019 ( Fig. 2A ).

medium/medium-SCIMAR-87-01-e059-gf2.png
Fig. 2.  - A, abundances of Chondrochelia dubia between July 2019 and July 2020 (black line) and cumulative rainfall (grey bars). B, body length (mm) of C. dubia between July 2019 and July 2020. The light grey rectangle indicates the period of weak oil arrival at the location (August and September 2019) and the dark grey rectangle indicates the period of strong oil arrival (October 2019). Vertical bars represent standard errors and letters indicate the results of Tukey tests (p<0.05).

Body lengths varied significantly between months (F=19.9; p<0.01). In general, the smallest individuals were found in August 2019 (1.58±0.99 mm), whereas the largest ones were found in February (2.63±0.93 mm) and April 2020 (2.61±0.9 mm) ( Fig. 2B ). Specimens were categorized into six developmental stages ( Fig. 3 ): MII (0.99±0.2 mm), MIII (1.75±0.3 mm), neutrum (3.05±0.48 mm), males (2.82±0.4 mm), pre-ovigerous females (2.87±0.35 mm) and ovigerous females (3.16 ± 0.39 mm).

medium/medium-SCIMAR-87-01-e059-gf3.png
Fig. 3.  - Violin plot combined with boxplot of length distributions within different developmental stages in Chondrochelia dubia. Grey dots are the mean values.

The population was dominated by non-reproductive individuals. Those with clear sexual characteristics (males and ovigerous and pre-ovigerous females) accounted for less than 10% of the total. Chondrochelia dubia had multiple cohorts throughout the year. Reproductive individuals had discrete abundance peaks throughout the year, especially in December ( Fig. 4 ). Except for February and April, juveniles (MII and MIII stages) accounted for more than 50% of all individuals in all months. The sex ratio was significantly female-biased in all months and size classes. The general sex ratio was approximately 17:1 and maximum female dominance occurred in November 2019 (no males) and July 2020 (56 females: 1 male) ( Table 1 ).

medium/medium-SCIMAR-87-01-e059-gf4.png
Fig. 4.  - A, number of juvenile, non-reproductive and reproductive individuals (males, pre-ovigerous and ovigerous females) per month. B, proportion of different sex categories of Chondrochelia dubia between July 2019 and July 2020.
Table 1.  Number of males and females, sex ratio of Condrochelia. dubia between July 2019 and July 2020, and results of chi-squared tests per month and size class.
Months Females Males F:M ratio Chi-squared p-value
2019/07 57 2 33.5:1 59.362 <0.01
2019/08 40 1 40:1 36.214 <0.01
2019/09 21 2 12.5:1 17.926 <0.01
2019/10 38 2 19:1 42.481 <0.01
2019/11 34 - - 34.028 <0.01
2019/12 47 9 5.2:1 31.641 <0.01
2020/01 46 5 9.2:1 37.123 <0.01
2020/02 84 3 28:1 77.538 <0.01
2020/04 92 3 30.6:1 87.485 <0.01
2020/05 36 3 12:1 35.021 <0.01
2020/06 32 3 10.6:1 27.225 <0.01
2020/07 56 1 56:1 51.158 <0.01
Total 583 34 17.14:1 453.17 <0.01
Size classes (mm) Females Males F:M ratio Chi-squared p-value
1.5 2 1 2:1 - -
2 34 4 8.5:1 20.25 <0.01
2.5 229 16 14.3:1 184.44 <0.01
3 162 12 13.5:1 127.59 <0.01
3.5 129 1 129:1 124.07 <0.01
4 26 - - 24.038 <0.01
4.5 1 - - - -

Female size at first maturity was 2.3 mm ( Fig. 5A ). For males, the inflection point, which indicates the size of morphometric maturity, was 3.0 mm ( Fig. 5B ). Longevity (tmax) was 0.89 years (10-11 months) and natural mortality (M=Z), 5.77 year-1. There was a positive and significant correlation between body size and chela length (R2=0.64; p<0.01) and body size and chela width (R2=0.57; p<0.01) in males. The parameters of the von Bertalanffy growth formula were L =5.26 mm; k=3.36 year-1; t 0=0.0 ( Fig. 6 ).

medium/medium-SCIMAR-87-01-e059-gf5.png
Fig. 5.  - A, logistic curve and size at first maturity (L 50) for females of Chondrochelia dubia. Blue envelope represents the 95% confidence interval. B, regression lines indicating morphometric maturity in males of C. dubia.
medium/medium-SCIMAR-87-01-e059-gf6.png
Fig. 6.  - Von Bertalanffy growth curve and parameters for Chondrochelia dubia (pooled sexes). CI=95% confidence interval.

DISCUSSION

 

Populational fluctuations and morphometry

 

The maximum abundance of C. dubia in Paiva Beach (tropical Brazilian coast) occurred in drier months, particularly in August, November and December 2019. Despite the stable conditions of tropical environments, even slight variations in temperature, photoperiod, salinity and nutrient concentration might cause perceptible oscillations in population size and structure ( Pandian 2016 Pandian T. 2016. Reproduction and Development in Crustacea. CRC Press, India, 316 pp. https://doi.org/10.1201/b20080 ). Estuarine tanaid species have generally shown abundance peaks in rainy periods and under mesohaline conditions ( Modlin and Harris 1989 Modlin R., Harris P. 1989. Observations on the natural history and experiments on the reproductive strategy of Hargeria rapax (Tanaidacea). J. Crustac. Biol. 9: 678-586. https://doi.org/10.1163/193724089X00593 , Pennafirme and Soares-Gomes 2009 Pennafirme S., Soares-Gomes A. 2009. Population biology and reproduction of Kalliapseudes schubartii Mañé-Garzón, 1949 (Peracarida, Tanaidacea) in a tropical coastal Lagoon, Itaipu, Southeastern Brazil. Crustaceana 82: 1509-1526. https://doi.org/10.1163/001121609X12487811051589 ). Marine species, in contrast, are generally more abundant during the dry season, when salinity is higher ( de Souza et al. 2013 de Souza F., Gilbert E., de Camargo M., Pieper W. 2013. The spatial distribution of the subtidal benthic macrofauna and its relationship with environmental factors using geostatistical tools: A case study in Trapandé Bay, southern Brazil. Zoologia 30: 55-65. https://doi.org/10.1590/S1984-46702013000100007 , Tuya et al. 2001 Tuya F., Pérez J., Medina L., Luque A. 2001. Seasonal variations of the macrofauna from three seagrass meadows of Cymodocea nodosa off Gran Canaria (Central-eastern Atlantic Ocean). Cienc. Mar. 27: 223-234. https://doi.org/10.7773/cm.v27i2.462 ). Warmer temperatures in the dry season may also enhance microbial growth ( Longo et al. 2019 Longo P., Mansur K., Leite F., Passos F. 2019. The highly diverse gastropod assemblages associated with Sargassum spp. (Phaeophyceae: Fucales) habitats. J. Mar. Biolog. Assoc. U.K. 99: 1295-1307. https://doi.org/10.1017/S0025315419000304 ), which might contribute to the detritus chain, which is useful for both feeding and tube-building in Tanaidacea ( Krasnow and Taghon 1997 Krasnow L., Taghon, G. 1997. Rate of tube building and sediment particle size selection during tube construction by the tanaid crustacean, Leptochelia dubia. Estuaries. 20: 534-546. https://doi.org/10.2307/1352612 ). In the rainy season, wave action, river discharge and sediment resuspension are considerably higher (Medeiros et al. 2001), which may cause higher mortality owing to physical and chemical stressors and reduction of available algal biomass.

There was a significant reduction in the size of individuals in August and October/November 2019. Despite the arrival of oil in these months, abundances continued to grow, so the lower body lengths might be a consequence of the recruitment of new juveniles into the population instead of a mass mortality event. The months of August (end of the rainy season), October and November (peak of the dry season) coincide with the highest salinities. However, other factors rather than just salinity might help to explain this pattern, such as the decrease in predators and/or competitors, or better conditions for the seaweed that provides refuges. However, a significant reduction in abundance was observed in September, the beginning of the dry season. This unusual decrease might have been caused by the contact with the oil that killed mainly juveniles, who are more vulnerable to harmful effects of pollutants than adults ( Keesing et al. 2018 Keesing J., Gartner A., Westera M., et al. 2018. Impacts and Environmental Risks of Oil Spills on Marine Invertebrates, Algae and Seagrass: A Global Review from an Australian Perspective. In: Hawkins S., Evans A., et al. (eds), Oceanography and Marine Biology. CRC Press, pp. 2-61. https://doi.org/10.1201/9780429454455-5 ). However, the population continued to grow and quickly recovered in the following months, which can be seen as the second peak in November/December. In laboratory experiments, C. dubia has shown to be relatively tolerant to changes in water chemistry ( Araújo-Silva et al. 2022 Araújo-Silva C., Sarmento V., Santos P. 2022. Climate change scenarios of increased CO2 and temperature affect a coral reef peracarid (Crustacea) community. Mar. Environ. Res. 173: 1-11. https://doi.org/10.1016/j.marenvres.2021.105518 ). Much of its resistance is attributed to the construction of tubes, which keep these animals protected from external agents and may help them colonize a wide variety of habitats within medium and infralittoral zones ( Araújo-Silva et al. 2022 Araújo-Silva C., Sarmento V., Santos P. 2022. Climate change scenarios of increased CO2 and temperature affect a coral reef peracarid (Crustacea) community. Mar. Environ. Res. 173: 1-11. https://doi.org/10.1016/j.marenvres.2021.105518 ).

Male size of morphometric maturity was 3.0 mm, and males larger than that were very rare. When males moult into their mature phase, they lose their functional mouthparts and cannot feed anymore, so they must die soon after reproduction ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 , Gardiner 1975 Gardiner L. 1975. The Systematics, Postmarsupial Development, and Ecology of the Deep-Sea Family Neotanaidae (Crustacea: Tanaidacea) (Vol. 170). Smithsonian Institution Press, City of Washington, 274 pp . https://doi.org/10.5479/si.00810282.170 ), which explains the almost complete absence of males larger than 3 mm. Also, a positive correlation was observed between body length and chela length in males. The differential growth rate of chelae has an important role in crustacean reproduction ( Ewers-Saucedo 2019 Ewers-Saucedo C. 2019. Evaluating reasons for biased sex ratios in Crustacea. Invertebr. Reprod. Dev. 63: 222-230. https://doi.org/10.1080/07924259.2019.1588792 ). In Tanaidomorpha, chelipeds are used to access the female tube, hold females during mating and fight with other males ( Buckle Ramirez 1965 Buckle Ramirez L.F. 1965. Untersuchungen über die Biologie von Heterotanais oerstedi Kröyer (Crustacea, Tanaidacea). Zeitschrift Für Morphologie Und Ökologie Der Tiere. 55: 714-482. https://doi.org/10.1007/BF00406235 , Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 , Johnson and Attramadal 1982 Johnson S., Attramadal Y. 1982. Reproductive Behaviour and Larval Development of Tanais cavolinii (Crustacea: Tanaidacea). Mar. Biol. 71: 11-16. https://doi.org/10.1007/BF00396987 ). The copulatory male is considered the only free walking instar, so developed chelipeds are essential to climb and hold onto algae in turbulent environments ( Johnson and Attramadal 1982 Johnson S., Attramadal Y. 1982. Reproductive Behaviour and Larval Development of Tanais cavolinii (Crustacea: Tanaidacea). Mar. Biol. 71: 11-16. https://doi.org/10.1007/BF00396987 ). These features might give a reproductive advantage to larger males ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 ). Another possible function of male aggression in leptocheliids is the exclusion of other males of sympatric species that might cohabit the algal frond ( Stoner 1986 Stoner A. 1986. Cohabitation on Algal Habitat Islands by Two Hermaphroditic Tanaidacea (Crustacea: Peracarida). J. Crustac. Biol. 6: 719-728. https://doi.org/10.1163/193724086X00523 ).

A large size overlap between the sexes, mainly among more advanced developmental stages, was recorded. This is mainly because of the progressive decrease in growth rate with age ( Sparre and Venema 1998 Sparre P., Venema S. 1998. Introduction to tropical fish stock assessment - Part I: Manual. FAO, Rome, 423 pp.). Pre-ovigerous females have a very small growth from the preparatory to marsupial stages because they allocate more resources to reproduction than to somatic growth ( Masunari 1983 Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 ). The largest individuals in our samples were female. This is probably because of the low survival rate and premature deaths of males ( Mendoza 1982 Mendoza J. 1982. Some Aspects of the Autecology of Leptochelia dubia (Krøyer, 1842) (Tanaidacea). Crustaceana. 43: 225-240. https://doi.org/10.1163/156854082X00164 ). More specifically, the largest individuals found were in fact non-reproductive adult females. It is very likely that they were multiparous females with interspaced “pregnancies” ( Masunari 1983 Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 ). The wide overlap between non-reproductive individuals with adult appearance (neuters) and reproductive ones suggests the existence of at least one intermediary instar between successive marsupial stages in C. dubia ( Fig. 3 ). However, we did not find external marks (as in Johnson and Attramadal 1982 Johnson S., Attramadal Y. 1982. Reproductive Behaviour and Larval Development of Tanais cavolinii (Crustacea: Tanaidacea). Mar. Biol. 71: 11-16. https://doi.org/10.1007/BF00396987 ) or any direct sign of previous “pregnancies” in large non-reproductive females.

Reproduction and sex ratios

 

The scarcity of reproductive individuals was notable. A few observations might explain this annual pattern, such as high natural mortality (5.77 year-1) and possible competition among individuals to mate; the aggressiveness of males and possible formation of “harems” or highly condensed mating aggregations ( Stoner 1986 Stoner A. 1986. Cohabitation on Algal Habitat Islands by Two Hermaphroditic Tanaidacea (Crustacea: Peracarida). J. Crustac. Biol. 6: 719-728. https://doi.org/10.1163/193724086X00523 ); interspaced “pregnancies” with intermediary instars (multiparity); and pre-ovigerous females with microscopic oostegites in early development, only visible through histological analysis ( Masunari 1983 Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 ). The last two factors might have produced a bias in the counting of reproductive/non-reproductive individuals.

The maintenance of a skewed sex ratio towards females during the entire year has also been observed in many previous studies on tanaids (e.g. Leite et al. 2003 Leite F., Turra A., Souza, E. 2003. Population biology and distribution of the tanaid Kalliapseudes schubarti Mañé-Garzon, 1949, in an intertidal flat in southeastern Brazil. Braz. J. Biol. 63: 469-479. https://doi.org/10.1590/S1519-69842003000300013 , Masunari 1983 Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 , Modlin and Harris 1989 Modlin R., Harris P. 1989. Observations on the natural history and experiments on the reproductive strategy of Hargeria rapax (Tanaidacea). J. Crustac. Biol. 9: 678-586. https://doi.org/10.1163/193724089X00593 ). Biased sex ratios have long been observed in several crustacean species ( Ewers-Saucedo 2019 Ewers-Saucedo C. 2019. Evaluating reasons for biased sex ratios in Crustacea. Invertebr. Reprod. Dev. 63: 222-230. https://doi.org/10.1080/07924259.2019.1588792 ). Some evolutionary and ecological mechanisms might explain the highly female-biased sex ratio in C. dubia ( Ewers-Saucedo 2019 Ewers-Saucedo C. 2019. Evaluating reasons for biased sex ratios in Crustacea. Invertebr. Reprod. Dev. 63: 222-230. https://doi.org/10.1080/07924259.2019.1588792 ):

  1. Local mate competition: Because males add little to increase the mother’s fitness, this favours the production of the lowest number of males sufficient to fertilize the highest number of females possible. This strategy is common in brooding and low-dispersive taxa, where brothers frequently compete for mating. Stoner (1986) Stoner A. 1986. Cohabitation on Algal Habitat Islands by Two Hermaphroditic Tanaidacea (Crustacea: Peracarida). J. Crustac. Biol. 6: 719-728. https://doi.org/10.1163/193724086X00523 proposed that aggregations with high densities of females might actually benefit males, since it would be easier for them to find partners.

  2. Sexual selection: Producing males is a high-cost activity, because they have to grow up and compete to have a chance of mating-because of this, only females in good condition are likely to generate more males, making them less frequent in the population.

  3. Environmental sex determination: Warm temperatures can turn the sex ratio towards females ( Masunari 1983 Masunari S. 1983. Postmarsupial development and population dynamics of Leptochelia Sa Vignyi (Kroyer, 1842) (Tanaidacea). Crustaceana. 44: 151-162. https://doi.org/10.1163/156854083X00776 ), and the stable, tropical climate of the study area might help maintain the female-skewed sex ratio year-round despite the seasonal oscillations.

  4. Sex specific mortality: In Tanaidacea, the small relative number of males has been mainly attributed to their sexual behaviour: males experience higher mortality than females as a result of competition and aggressive behaviour with other males and are more vulnerable to predators because they have to walk to the female tube to mate ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 ). Developed males also lack functional mouthparts, which might significantly decrease their lifespan ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 ).

  5. Sex reversal: Diverse reproductive strategies are observed in Tanaidomorpha and Apseudomorpha, including gonochoristic development and simultaneous, protandrous and protogynous hermaphroditism ( Gardiner 1975 Gardiner L. 1975. The Systematics, Postmarsupial Development, and Ecology of the Deep-Sea Family Neotanaidae (Crustacea: Tanaidacea) (Vol. 170). Smithsonian Institution Press, City of Washington, 274 pp . https://doi.org/10.5479/si.00810282.170 ).

The last strategy has been widely proposed to occur in many species of Tanaidacea ( Gardiner 1975 Gardiner L. 1975. The Systematics, Postmarsupial Development, and Ecology of the Deep-Sea Family Neotanaidae (Crustacea: Tanaidacea) (Vol. 170). Smithsonian Institution Press, City of Washington, 274 pp . https://doi.org/10.5479/si.00810282.170 ). It has been theorized that protogyny is an effective strategy for maximizing fitness (reproductive success) in all life stages ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 ). Basically, males take too long to be able to reproduce (they must grow enough to fight with other males), whereas females mate as soon as they reach maturity. There is therefore a selective pressure for being a female at small (younger) stages and then becoming a male at larger (older) stages, because only the large males will be successful ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 ). Alternatively, protogyny may also have evolved as a mechanism for counterbalancing the high mortality of males ( Leite et al. 2003 Leite F., Turra A., Souza, E. 2003. Population biology and distribution of the tanaid Kalliapseudes schubarti Mañé-Garzon, 1949, in an intertidal flat in southeastern Brazil. Braz. J. Biol. 63: 469-479. https://doi.org/10.1590/S1519-69842003000300013 ).

Although it is observed in many tanaids, there is no clear evidence that C. dubia is a sequential hermaphroditic species. If that were true, it would be expected to observe a dominance of one sex in smaller size classes and a gradual shift towards the other sex in larger size classes ( Ewers-Saucedo 2019 Ewers-Saucedo C. 2019. Evaluating reasons for biased sex ratios in Crustacea. Invertebr. Reprod. Dev. 63: 222-230. https://doi.org/10.1080/07924259.2019.1588792 ). The opposite occurred in Paiva Beach, where the sex ratio was strongly female-biased in all size classes. However, this might still be true if only a small percentage of females is able to become male. It has been observed in similar species that dominant males can inhibit sex reversal of nearby females ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 ), which might keep the number of males in the aggregation low. The presence of two types of males based on their size differences has been treated as more evidence of protogynous hermaphroditism in Tanaidacea. The smallest males were considered gonochoristic (male-born) whereas the largest ones were protogynous (female-born) ( Gardiner 1975 Gardiner L. 1975. The Systematics, Postmarsupial Development, and Ecology of the Deep-Sea Family Neotanaidae (Crustacea: Tanaidacea) (Vol. 170). Smithsonian Institution Press, City of Washington, 274 pp . https://doi.org/10.5479/si.00810282.170 ). Interestingly, individuals identified as “Leptochelia dubia” collected from different parts of the West Coast of the USA have been treated either as dioecious ( Mendoza 1982 Mendoza J. 1982. Some Aspects of the Autecology of Leptochelia dubia (Krøyer, 1842) (Tanaidacea). Crustaceana. 43: 225-240. https://doi.org/10.1163/156854082X00164 ) or hermaphroditic ( Highsmith 1983 Highsmith R. 1983. Sex Reversal and Fighting Behavior: Coevolved Phenomena in a Tanaid Crustacean. Ecology. 64: 719-726. https://doi.org/10.2307/1937194 ) on different occasions. Considering the lack of detailed natural observations, the taxonomic uncertainties and the geographic distances (tanaids are known to have low dispersive capacity; Bamber 2010 Bamber R. 2010. In the footsteps of Henrik Nikolaj Krøyer: The rediscovery and redescription of Leptochelia savignyi (Krøyer, 1842) sensu stricto (Crustacea: Tanaidacea: Leptocheliidae). Proc. Biol. Soc. Wash. 123: 289-311. https://doi.org/10.2988/10-14.1 ), the best way to solve questions regarding the reproductive behaviour of C. dubia in the tropics would be to cultivate these organisms under controlled and realistic conditions.

Life histories and population growth

 

The year-long presence of reproductive adults and juveniles indicates continuous reproductive activity, a common pattern observed in many crustacean species, especially in the tropics ( Pandian 2016 Pandian T. 2016. Reproduction and Development in Crustacea. CRC Press, India, 316 pp. https://doi.org/10.1201/b20080 , Pennafirme and Soares-Gomes 2009 Pennafirme S., Soares-Gomes A. 2009. Population biology and reproduction of Kalliapseudes schubartii Mañé-Garzón, 1949 (Peracarida, Tanaidacea) in a tropical coastal Lagoon, Itaipu, Southeastern Brazil. Crustaceana 82: 1509-1526. https://doi.org/10.1163/001121609X12487811051589 ). Specimens in Paiva Beach are much smaller (2.04±0.95 mm in length) than other tanaid species from the southwestern Atlantic ( Table 2 ), and their natural mortality is relatively high. C. dubia also has multiple short cohorts, a relatively high growth rate (k) and a short lifespan (<11 months). All of these features indicate that it has a short and opportunistic life strategy ( Pennafirme and Soares-Gomes 2009 Pennafirme S., Soares-Gomes A. 2009. Population biology and reproduction of Kalliapseudes schubartii Mañé-Garzón, 1949 (Peracarida, Tanaidacea) in a tropical coastal Lagoon, Itaipu, Southeastern Brazil. Crustaceana 82: 1509-1526. https://doi.org/10.1163/001121609X12487811051589 ).

Table 2.  Tanaid species and their respective von Bertallanfy population growth parameters estimated in previous studies from the southwestern Atlantic. M, natural mortality; SST, sea surface temperature (mean) ( Boyer et al. 2018 Boyer T., Baranova O., Coleman C., et al. 2018. NOAA Atlas NESDIS 87, Silver Spring, MD, 207 pp.).
Species Location Coordinates SST (°C) L (mm) k (year-1) t0 L50 (mm) ɸ’ Longevity (year) M (year-1) Reference
Tanais dulongii Mar del Plata, Argentina 38°02’S; 57°32’W-38°10’S; 57°38’W 14-15 7-8 0.55-0.63 - - - - - Rumbold et al. 2015 Rumbold C., Obenat S., Spivak E. 2015. Comparison of life history traits of Tanais dulongii (Tanaidacea: Tanaididae) in natural and artificial marine environments of the south-western Atlantic. Helgol. Mar. Res. 69: 231-242. https://doi.org/10.1007/s10152-015-0432-9
Monokalliapseudes schubartii Patos Lagoon, Rio Grande do Sul, Brazil 32°01’S; 52°07’W 19 13.22 4.54 0 6.6 2.9 1 - Fonseca and DIncao 2003 Fonseca D., D’Incao F. 2003. Growth and reproductive parameters of Kalliapseudes schubartii in the estuarine region of the Lagoa dos Patos (southern Brazil). J. Mar. Biolog. Assoc. U.K. 83: 931-935. https://doi.org/10.1017/S0025315403008087h
Monokalliapseudes schubartii Mel Island, Paraná, Brazil 25°33’S; 48°19’W 21 11 3 0 - 2.6 0.66 - 1 - Almeida 1994 Almeida M. 1994. Kalliapseudes schubartii Mañé-Garzón, 1949 (Tanaidecea-Crustacea): Dinâmica populacional e interações com a macrofauna bêntica no Saco do Limoeiro, Ilha do Mel (Paraná, Brasil). MSc thesis, Universidade Federal do Paraná, 75pp.
Monokalliapseudes schubartii Araçá Region, São Paulo, Brazil 23°49’S; 45°24’W 23 10.7 3 0 - 2.5 1 - Leite et al. 2003 Leite F., Turra A., Souza, E. 2003. Population biology and distribution of the tanaid Kalliapseudes schubarti Mañé-Garzon, 1949, in an intertidal flat in southeastern Brazil. Braz. J. Biol. 63: 469-479. https://doi.org/10.1590/S1519-69842003000300013
Monokalliapseudes schubartii Itaipu Lagoon, Rio de Janeiro, Brazil 22°58’S; 43°02’W 25 11.74 2.91 -0.04 5.9 2.6 0.84 0.99 Pennafirme and Gomes 2017 Pennafirme S., Soares-Gomes A. 2017. Population dynamics and secondary production of a key benthic tanaidacean, Monokalliapseudes schubarti (Mañé-Garzón, 1949) (Tanaidacea, Kalliapseudidae), from a tropical coastal lagoon in southeastern Brazil. Crustaceana. 90: 1483-1499. https://doi.org/10.1163/15685403-00003704
Chondrochelia dubia Paiva Beach, Pernambuco, Brazil 8°16′ S; 34°56′W 27-28 5.26 3.36 0 2.3 1.97 0.89 5.77 Present study

Latitudinal trends in life history parameters are commonly observed in Tanaidacea ( Pennafirme and Soares-Gomes 2017 Pennafirme S., Soares-Gomes A. 2017. Population dynamics and secondary production of a key benthic tanaidacean, Monokalliapseudes schubarti (Mañé-Garzón, 1949) (Tanaidacea, Kalliapseudidae), from a tropical coastal lagoon in southeastern Brazil. Crustaceana. 90: 1483-1499. https://doi.org/10.1163/15685403-00003704 ). Warmer temperatures generally accelerate growth and maturity in ectotherms ( Sudo 2003 Sudo H. 2003. Effect of temperature on growth, sexual maturity and reproduction of Acanthomysis robusta (Crustacea: Mysidacea) reared in the laboratory. Mar. Biol. 143: 1095-1107. https://doi.org/10.1007/s00227-003-1160-2 ), and tropical marine invertebrates generally have shorter lifespans and smaller individual sizes than their temperate counterparts ( Cardoso and Defeo 2004 Cardoso R., Defeo O. 2004. Biogeographic patterns in life history traits of the Pan-American sandy beach isopod Excirolana braziliensis. Estuar. Coast. Shelf Sci. 61: 559-568. https://doi.org/10.1016/j.ecss.2004.06.021 ). Furthermore, unlike Monokalliapseudes schubartii and Tanais dulongii ( Table 2 ), C. dubia is a seaweed-dweller, meaning that its size is highly dependent upon the interstitial size and volume of the host algae ( Hacker and Steneck 1990 Hacker S., Steneck R. 1990. Habitat Architecture and the Abundance and Body-Size-Dependent Habitat Selection of a Phytal Amphipod. Ecology. 71: 2269-2285. https://doi.org/10.2307/1938638 ). However, in a subtropical area in southern Brazil, Fonseca and D’Incao (2003) Fonseca D., D’Incao F. 2003. Growth and reproductive parameters of Kalliapseudes schubartii in the estuarine region of the Lagoa dos Patos (southern Brazil). J. Mar. Biolog. Assoc. U.K. 83: 931-935. https://doi.org/10.1017/S0025315403008087h found a growth rate (k) of 4.54 year-1 for M. schubartii. It is possible that other factors rather than temperature, such as food quality/availability ( Berrigan and Charnov 1994 Berrigan D., Charnov E. 1994. Reaction Norms for Age and Size at Maturity in Response to Temperature: A Puzzle for Life Historians. Oikos. 70: 474-478. https://doi.org/10.2307/3545787 ), were responsible for the higher growth rate of this species than of our tropical species. The population studied by Fonseca and D’Incao (2003) Fonseca D., D’Incao F. 2003. Growth and reproductive parameters of Kalliapseudes schubartii in the estuarine region of the Lagoa dos Patos (southern Brazil). J. Mar. Biolog. Assoc. U.K. 83: 931-935. https://doi.org/10.1017/S0025315403008087h inhabits a nutrient-rich protected estuarine bay (Patos Lagoon), which is very different from the open, nutrient-variable waters of tropical Brazilian beaches.

The absence of other studies that address the population parameters of C. dubia makes it difficult to evaluate the influence of environmental variables and regional variability in the growth of this species. However, compared with other Tanaidacea species of the southwestern Atlantic, C. dubia also showed the lowest growth performance index (Φ’). Zamora-Sarabia et al. (2022) Zamora-Sarabia F., Arreguín-Sánchez F., de Anda-Montañez, J.A., Jacob-Cervantes M. 2022. Effect of sea surface temperature on the growth performance of the thread herring Opisthonema libertate (Günther, 1868) in the southern Gulf of California. Lat. Am. J. Aquat. Res. 50: 31-38. https://doi.org/10.3856/vol50-issue1-fulltext-2746 found a negative correlation between Φ’ and sea surface temperature for a commercially important fish species in the southern Gulf of California. This correlation might explain the low Φ’ value compared with other tanaid populations from colder areas at higher latitudes ( Table 2 ). Combined with the high mortality rate and low percentage of reproductive individuals, C. dubia apparently faces harsh environmental conditions at Paiva Beach, such as resource limitation, high temperatures, predation and strong hydrodynamics ( Domingues et al. 2017 Domingues E.C., Schettini C.A.F., Truccolo E.C., Oliveira Filho J.C. de. 2017. Hidrografia e correntes da Plataforma Continental de Pernambuco. Rev. Bras. de Recur. Hidr. 22: 1-17. https://doi.org/10.1590/2318-0331.0217170027 ). Moreover, the size of the largest individual found (4.6 mm in length) was about 87% of the theoretical maximum length (Linf =5.26 mm). It is possible that these natural stressors are a strong limitation for the growth and survival of these organisms. This may make the studied population of C. dubia vulnerable to extreme climatic events caused by anthropogenic warming and/or El Niño oscillations ( Zamora-Sarabia et al. 2022 Zamora-Sarabia F., Arreguín-Sánchez F., de Anda-Montañez, J.A., Jacob-Cervantes M. 2022. Effect of sea surface temperature on the growth performance of the thread herring Opisthonema libertate (Günther, 1868) in the southern Gulf of California. Lat. Am. J. Aquat. Res. 50: 31-38. https://doi.org/10.3856/vol50-issue1-fulltext-2746 ), although Araújo-Silva et al. (2022) Araújo-Silva C., Sarmento V., Santos P. 2022. Climate change scenarios of increased CO2 and temperature affect a coral reef peracarid (Crustacea) community. Mar. Environ. Res. 173: 1-11. https://doi.org/10.1016/j.marenvres.2021.105518 showed that this species is still more tolerant to warming effects than other tropical peracarids. Growth parameters such as Φ’ are often used as an important reference for stock management and choosing appropriate species for aquaculture ( Mathews and Samuel 1990 Mathews C., & Samuel, M. 1990. Using the growth performance index Φ’ to choose species aquaculture: an example from Kuwait. Aquabyte 3: 2-4., Pauly and Munro 1984 Pauly D., Munro J. 1984. Once more on the comparison of growth in fish and invertebrates. Fishbyte. 2: 1-21., Zamora-Sarabia et al. 2022 Zamora-Sarabia F., Arreguín-Sánchez F., de Anda-Montañez, J.A., Jacob-Cervantes M. 2022. Effect of sea surface temperature on the growth performance of the thread herring Opisthonema libertate (Günther, 1868) in the southern Gulf of California. Lat. Am. J. Aquat. Res. 50: 31-38. https://doi.org/10.3856/vol50-issue1-fulltext-2746 ). Because peracarids have been recently studied as a valuable food resource for aquaculture ( Abundez et al. 2021 Abundez J., Moreno G., Simoes N., et al. 2021. Marine amphipods (Parhyale hawaiensis) as an alternative feed for the lined seahorse (Hippocampus erectus, Perri 1810): Nutritional value and feeding trial. PeerJ. 9: 1-28. https://doi.org/10.7717/peerj.12288 , Guevara et al. 2005 Guevara M., Lodeiros C., Donato M., et al. 2005. Nutritional quality of Metamysidopsis insularis Brattegard (Crustacea: Mysidacea). Aquac. Nutr. 11: 315-319. https://doi.org/10.1111/j.1365-2095.2005.00361.x ), the present study should be taken into consideration for future decisions regarding the commercial use of this species.

In conclusion, C. dubia at Paiva Beach (tropical Brazilian coast) has a short-living, opportunistic life history that may be favoured by high-salinity conditions. The sex ratios are heavily female-skewed throughout all months and size classes. The species was apparently little impacted by the 2019 Oil Spill at the populational level, a sign of high tolerance to environmental impacts and great plasticity of lifestyle, which are interesting features of a possible bioindicator species. This study reinforces the need for cultivation techniques in order to solve key questions regarding the reproductive behaviour of the species and the high applicability of robust, bootstrapped length-based methods in population studies of small marine invertebrates.

ACKNOWLEDGEMENTS

 

The authors are grateful to the Brazilian National Research Council (CNPq) for providing a MSc scholarship to the first author and a Research Productivity Fellowship to Flávia Lucena-Frédou, and to the Ray Lankester Research Fellowships for a grant to José S. Rosa Filho. We also thank UFPE (Proc. 23076.058083/2019-66), FACEPE (APQ-0628-1.08/19) and CNPq (Proc. 440826/2020-9) for financial support. We are grateful to Juliana Menezes da Silva for helping in field and laboratory work, to Dr Catarina Araújo-Silva for her help in the Taxonomy section and to Dr Alex Souza Lira for insights in the statistical analysis and data interpretation. The authors wish to thank the anonymous reviewers for their fruitful comments on the manuscript.

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