Abstract
Determination of the growth parameters of a species is an indispensable requirement for understanding its biology and consequently the management of its fishery. In fisheries science, calculations of longevity, mortality rates and stock-assessment models depend on the availability of growth data. Genidens genidens, one of the most common ariid species in Brazil, is a potential sentinel species for biomonitoring in Guanabara Bay, one of the country’s most degraded estuarine ecosystems. The present study investigated the growth parameters of G. genidens, providing supporting information for its management. Individuals were measured, sexed, and the number of rings in the lapillus otolith counted. The periodicity in the formation of the rings was determined by the monthly ratio of the edge type. Individuals from 0 to 11.5 years old were captured, including some that were older than previously reported. Our results showed that this species forms two growth rings per year, one in summer and the other in winter; the summer ring is formed one month later in males than in females, due to the period of oropharyngeal incubation of the offspring. Sexual dimorphism was also observed in the growth rate: males grow faster, and consequently reach smaller sizes than females. We can conclude that the parental care carried out by males and the high energy expenditure in forming the large oocytes by females mark the otoliths and reveal life-cycle particularities differently in each sex.
Similar content being viewed by others
Avoid common mistakes on your manuscript.
Introduction
The family Ariidae is widely distributed along the Brazilian coast (Araújo 1988; Fischer et al. 2011), where their members are an important resource in artisanal fisheries, mainly the estuarine (Reis 1986b; Gomes and Araújo 2004a; Silva-Junior et al. 2013). The catfish Genidens genidens (Cuvier 1829) is one of the most common ariid species along the eastern coast of South America from the Guianas to the La Plata River in Argentina (Marceniuk and Menezes 2007; Fischer et al. 2011). This catfish is highly abundant in estuarine systems (Araújo et al. 1998; Azevedo et al. 1999; Silva-Junior et al. 2013) and is a possible sentinel species for biomonitoring in Guanabara Bay, since it completes its entire life cycle within the estuary and is resistant to eutrophication and other anthropogenic impacts (Silva-Junior et al. 2013). The estuary of Guanabara Bay, the second-largest bay on the Brazilian coast, is one of the most degraded estuarine systems in Brazil (Meniconi et al. 2012; Begot and Vianna 2014), but still supports the most productive estuarine fishery in the region (Prestrelo and Vianna 2016). Although the vulnerability of G. genidens to overfishing is recognized in management regulations for the state of São Paulo and southern Brazil (SUDEPE 1984; MMA 2004), no specific regulations for this catfish have been developed for Guanabara Bay or for the rest of Brazil.
Effective fishery management depends on accurate information on species biology, especially the age and growth pattern (Conand et al. 1995; Vaz-dos-Santos 2015a). Age information is the basis for calculating growth rates, productivity and mortality (Campana 2001). Age and growth are fundamental to understanding a species’ biology (individual development), population dynamics (how the set of individuals grows and their abundance), community structure (how each population grows) and ecosystem functioning (age brackets that are preyed on or fished, etc.) (Labropoulou and Papaconstantinou 2000; Vaz-dos-Santos 2015a).
Birth time, growth rate, and interruptions of growth or transitions reflecting migration, reproductive activities, and changes in life history can be recognized in otoliths, allowing them to be widely used to evaluate the demographics of various species of fishes and answer questions about ecology, evolution and fisheries (Bell 2001). Otoliths are calcareous structures in the inner ear of teleost fishes, and function in balance and hearing (Campana 1999; Panfili et al. 2002; Vaz-dos-Santos 2015a). Fish have three pairs of otoliths, sagitta, lapillus and asteriscus, which are metabolically inert, do not act as calcium reserves, are not reabsorbed, and maintain a complete sequence of growth marks (Panfili et al. 2002). The lapilli otoliths are the least studied (Morales-Nin et al. 1999; Fuchs and Volpedo 2009; Oliveira et al. 2014). However, in the Siluriformes (catfishes) these otoliths are larger than the other pairs, differentiating this group from other teleosts (Fuchs and Volpedo 2009). Therefore, most of the work with this pair was conducted with Siluriformes, for example, studies of age and growth (Reis 1986a; Amaral et al. 1999; Oliveira and Novelli 2005; Velasco et al. 2007), otolith description (Carvalho et al. 2014), habitat use (Avigliano et al. 2015, 2016, 2017a) and stock identification (Avigliano et al. 2017b).
Investigation of sexual dimorphism in exploited species is essential for adequate fishing management, since this depends on the accuracy of the calculated growth parameters, which may be influenced by differing environmental and biological pressures on males and females. Ariids, including G. genidens, possess a peculiar reproductive biology in which females produce large oocytes (Wallace and Selman 1981) and males carry out oral incubation of the offspring, during which time they do not feed (Chaves 1994; Garcia et al. 2006; Silva-Junior et al. 2013). Since in the ariid Genidens barbus, reproductive effort is one of the main factors influencing changes in growth rates (Reis 1986a; Velasco and Reis 2004; Velasco et al. 2007) and sexual dimorphism in growth parameters has been detected in other siluriform species (Reis 1986a; Alonso and Fabré 2003; Pérez and Fabré 2009), this aspect of their biology suggests that the species may show sexual dimorphism in growth, which should be detectable by a change in the pattern of formation of growth rings. Therefore, the present study analyzed the otoliths of G. genidens, generating information on the age and growth pattern, and verifying the existence of sexual dimorphism throughout development as a function of the reproductive strategy.
Methods
Collection and processing of material
Specimens of G. genidens were obtained biweekly from artisanal fishery landings in the Guanabara Bay estuary (Fig. 1), caught with various types of gear including fish corral, longline, gillnet and bottom-trawl. In the laboratory the individuals were measured (total length – LT, precision of 1 mm) and sexed by observation of the gonads.
The age of individuals was determined as proposed by Panfili et al. (2002) and Vaz-dos-Santos (2015a). The otolith pair was removed by sectioning the cranial cavity. The otoliths were cleaned of adherent tissue in 70% ethanol, air-dried, and stored dry. For the growth analysis, whenever possible five left lapilli were selected for each sex, length class (2-cm interval) and sampling month. The lapilli were embedded in crystal-clear epoxy resin and cross-sectioned through the core, using a low-speed metallographic saw (IsoMet™), to obtain a 1.5 mm thick section. The otolith sections were immersed in water and photographed with a camera attached to a stereoscopic microscope (Fig. 2).
To determine the age of individual fish, three independent blind readings were performed by the same observer. The set consisting of a hyaline zone and an opaque zone were considered as one growth ring. The radius of each ring (Rn) and the radius of the otolith (Ro) were measured from the nucleus to the opaque margin of the growth ring, using the AxioVision LE 4.8 program. The opaque or hyaline border type of each otolith was recorded (Fig. 2).
Data analysis
The accuracy of the readings was determined by calculating the average percent error (APE) (Beamish and Fournier 1981) and Coefficient of Variation (CV) (Chang 1982). The coincidence percentage of the border type between the three readings was also determined (Vaz-dos-Santos 2015a). Individual otoliths with discrepant ring numbers or types of edges among the readings were reanalyzed and a final reading was determined. With this reading, the difference in the position of the rings (ring radius) between males and females was tested by two-way ANOVA with repeated measures (F; α = 0.05), with assumptions verified through residue analysis (Zar 2010). Sex and ring were considered random variables.
For the validation and subsequent determination of an individual’s age, the relative border-type method was used for each sex individually, taking care to use the numerically and temporally most important ring groups (Beamish and McFarlane 1983; Campana 2001), in this case ring groups 10 to 15 together. The large dark hyaline zones were considered fast-growing zones, and the narrow white opaque zones were considered slow-growing zones. The significance between the proportions of border types was tested by a log-likelihood ratio goodness-of-fit test with Williams correction (G; α = 0.05) (Zar 2010). Based on the reproductive biology and frequency of formation of opaque zones, the average date of birth of individuals was fixed as March, when occurs the peak period of oral incubation by males (Chaves 1994; García et al. 2006). The proportion of each sex by age was tested in relation to the expected ratio of 1:1, with the chi-square test (χ2; α = 0.05) with Yates correction (Zar 2010). Back-calculated lengths were estimated using the model of Monastyrsky (Vigliola and Meekan 2009):
where, LBC is the back-calculated length, Rn is the radius of the ring, Ro is the radius of the otolith, b is the coefficient from the relationship between total length and otolith radius (LT = a Rob), adjusted by the non-linear least-squares iterative method, and LT is the total length. To quantify the growth of individuals, the age-length relationship was adjusted by the von Bertalanffy growth model. Several different simulations were conducted, using observed and back-calculated lengths and different combinations and seed parameters (Velasco et al. 2007). The best fits were obtained based on back-calculated lengths using the fixed value of L∞ calculated with the formula L∞ = Lmax/0.95 (Taylor 1958), where Lmax is the maximum total length observed in the sample. The non-linear least-squares iterative method was used for adjustments, performed for both sexes together and for males and females separately (Vaz-dos-Santos 2015b). This procedure was applied twice, the first time to detect and remove residuals (values <−1.96 and > +1.96) and the second time to make the final adjustments. The consistency of the final adjustments was checked by means of the standard errors of the regressions (SE) (Zar 2010; Vaz-dos-Santos 2015b). The significant difference between the models for males and females was assessed by comparing the residual analysis for growth curves (Haddon 2011).
Results
A total of 1107 individuals of G. genidens were obtained, including 730 females with LT of 6–47 cm and 377 males with LT 5–38 cm. Based on the criteria used to compose the subsample for the study of age and growth, a total of 428 left otoliths were read, 240 from females and 188 from males. All otoliths were legible, with their opaque and hyaline zones quite visible. The readings were self-consistent, with APE of 9.99 and 8.3% and CV of 13.52 and 11.46% (mean and median).
The coincidence in the classification of the opaque and hyaline edges was high in all the readings and increased from the first to third reading (86.95% between readings 1 and 2 and 89.51% between readings 2 and 3).
The maximum number of rings observed per otolith ranged from zero to 23 rings for females and zero to 22 rings for males. The mean radius of each ring, which determines its position in the otolith, was also highly coherent with growth, with a difference between the position of each ring (ANOVA, F = 3520.93, p < 0.001) and between males and females (ANOVA, F = 4.06, p = 0.044). The ring radii reflected the dimorphism in the growth of females and males. However, the interaction between factors was not significant (ANOVA, F = 0.63, p = 0.893) (Fig. 3).
The O:H ratio varied significantly for females (G = 26.842, p = 0.0081) along the period analyzed, but not for males (G = 20.548, p = 0.0574), whose p value was slightly above the cut line (0.05). Opaque edges were more frequent in January through March, beginning to increase in December, and from June through August in females, and in February through March and August through October in males. Therefore, this species forms two rings per year, one in summer and one in winter, with the males forming both rings one month later than the females (Fig. 4). Based on this diagnosis, the age of each individual of G. genidens could be assigned.
Table 1 shows the age structure of G. genidens in Guanabara Bay. Most of the population was composed of individuals aged 5 to 7 years, and the oldest and youngest age groups were composed of fewer individuals. Up to about two years, the majority of individuals were males, with females predominating in the older age groups (Fig. 5).
The von Bertalanffy growth models fitted were: Lt = 49.47 [1 – e −0.123 (t + 0.198)] (N = 2828, S = 2.716) for females, Lt = 40 [1 – e −0.185 (t + 0.002)] (N = 2013, S = 2.708) for males and Lt = 49.47 [1 – e −0.124 (t + 0.210)] for both sexes (N = 4830, S = 2.772) (Table 2 and Fig. 6). The models for females and males were different (F = 502.63; p < 0.0001), indicating sexual dimorphism in the growth of the species, with males having a faster growth rate (K) than females and a lower maximum theoretical size (L∞).
Discussion
Although lapilli are not the most commonly used otoliths in the age-estimation studies, in this case the growth rings were quite visible in all otoliths of G. genidens examined, making it possible to determine the age of all the specimens. Lapilli proved to be good indicators of age, since the three blind readings, performed independently for each otolith, showed low APE and CV values, indicating that the readings were adequate (Campana 2001; Vaz-dos-Santos 2015a). Although these values are slightly higher than the reference values for precision (APE ~5% and CV 6–7% sensu Campana 2001), they are empirical and were derived from studies with sagitta, whereas the pattern for lapillus may be different. The use of lapilli otoliths for estimates of age and growth in teleosts is extremely rare, accounting for less than 10% of the studies in Brazil (Oliveira et al. 2014). Due to this lack of information, studies with lapilli generally adopt the methods proposed for sagittae. However, this practice may not always be appropriate and further studies on lapilli are needed in order to develop an own standard.
For the lapillus otolith of G. genidens, the narrow opaque zones represent slow growth, while the wide hyaline zones represent rapid growth, since the daily increments in the thickness of the otolith are directly related to body growth (Bell 2001). This pattern was also observed in the lapillus otoliths of other species of Siluriformes. Reis (1986a) considered wide zones as fast-growing and narrow zones as slow-growing for Genidens barbus, and Gibbs et al. (2013) also observed narrow opaque zones related to periods of slow growth and wide hyaline zones related to periods of rapid growth for Pterygoplichthys disjunctivus.
In the present study, this pattern reported for lapillus otoliths was confirmed by comparing the frequency of formation of opaque and hyaline edges (Fig. 4) with the information available in the literature on the biology of the species (Barbieri et al. 1992; Chaves 1994; Gomes and Araújo 2004a, b; Garcia et al. 2006; Silva-Junior et al. 2013, 2016). The percentage of border type was the most suitable method for the validation, since the marginal increment would not be appropriate because the lapilli did not show the progressive reduction of ring radii in older fish that is indispensable for using this method, originating from studies with sagittae (Panfili et al. 2002). Although it was not possible to apply this technique for each ring group separately (cf. Beamish and McFarlane 1983; Campana 2001; Vaz-dos-Santos 2015a), the analysis of ring groups 10 to 15 together was enough to reach a correct diagnosis.
G. genidens formed two growth rings per year. One ring was formed in the summer, related to the reproduction in the same period (Barbieri et al. 1992; Chaves 1994; Gomes and Araújo 2004a, b; Garcia et al. 2006), which is a critical factor for decreases in growth rate in ariids, given the high energy expenditure (Reis 1986a; Velasco et al. 2007). The other ring was formed in the winter, perhaps because of a slower metabolism due to the cooler water temperature in the inner bay at this time of year (Silva-Junior et al. 2016). The formation of two rings per year, with the ring formed in the summer also related to the reproductive effort, has been described in calcified structures of other tropical species of Siluriformes, such as Brachyplatystoma flavicans (Alonso and Fabré 2003), Hypophthalmus marginatus (Cutrim and Batista 2005) and Calophysus macropterus (Pérez and Fabré 2009). In addition, the average date of birth of individuals was fixed as March, i.e., the peak of oral incubation of the offspring by males (Chaves 1994; García et al. 2006), thus allowing attribution of individual ages.
Comparing the data obtained here with previously published information suggest that the time when the rings are formed differs between females and males. The opaque edges, formed in females from January through March, beginning to increase in December, coincided with the spawning peak (Barbieri et al. 1992; Gomes and Araújo 2004a, b) as a consequence of energy diversion to form the large oocytes. In males, the opaque edges appear most often formed in February–March, i.e., one month later than in females and coinciding with the peak period of oropharyngeal incubation of offspring, when the males may pass two to three months without feeding (Barbieri et al. 1992; Chaves 1994; Garcia et al. 2006). We also identified a delay in the formation of the winter rings, i.e., in June through August in females and in August through October in males, although the cause of this delay is unknown.
The individuals of G. genidens analyzed in Guanabara Bay reached a maximum age of 11.5 years, with a predominance of intermediate ages, from 5 to 7 years. This age structure results from the natural rarity of older individuals in the population and the unlikelihood that younger individuals will be caught by fishing gear (Coggins et al. 2013). These age values are higher than those observed for the species by Oliveira and Novelli (2005) in Barra do Açu Lagoon (RJ), where the maximum age was 5 years, with individuals from 2 to 4 years predominating. This difference can be attributed to the capture of larger individuals in the present study, which may indicate that the population of Guanabara Bay is more stable, with more size classes and age groups.
The parameters L∞ and K obtained adequately represented the growth of G. genidens in Guanabara Bay. The individuals showed a low growth rate (K) and reached large values of asymptotic length (L∞), as expected, since low growth rates are associated with larger body sizes and vice-versa (Vaz-dos-Santos 2015a). Regarding the theoretical age at zero length, obviously the values obtained have no biological significance, as they do not reflect development time before hatching (Ricker 1975). However, the initial growth of larvae and young-of-the-year is usually different from that of adults (Pauly 1984), and in the present case, the estimate of t0 has statistical significance, to adjust the beginning of the curve. The marked reduction in length increase with increasing age and the few specimens in the larger length classes indicate that the asymptotic length fixation, calculated from the formula of Taylor (1958), was a suitable strategy for fitting the model. This strategy allowed the representation of dimorphism between males and females with very different maximum lengths (47 cm for females and 38 cm for males), associated with the low growth rates common in ariids (Reis 1986a; Conand et al. 1995; Velasco et al. 2007). This is an acceptable and efficient procedure for siluriforms (Velasco and Oddone 2004; Cutrim and Batista 2005; Velasco et al. 2007). Besides, the largest G. genidens ever recorded (47 cm LT) were caught in this study.
The present study also identified sexual dimorphism in absolute growth. Males grow faster and consequently reach a smaller body size than females. Converting the calculated values for the size at first gonadal maturation of this catfish in Guanabara Bay, 15.9 cm for females and 17.6 cm for males (Maciel et al. 2018), to age indicates that females mature at 2.9 years and males at 3.1 years. However, Maciel et al. (2018) reported that G. genidens females smaller than 20 cm skipped spawning. Therefore, although females reach L50 at 15.9 cm, they begin to divert energy to reproductive activity at 20 cm, which converted into age represents 4 years. This allows females to reach larger sizes, probably as an adaptation to increase fecundity, since larger and older females are more fecund (Haimovici and Reis 1984; Pandian 2010; Wootton and Smith 2015). For the males, due to the parental-care behavior that prevents the fish from feeding for a long period (Chaves 1994; Garcia et al. 2006; Silva-Junior et al. 2013) and makes them more susceptible to predation (Wootton and Smith 2015), even younger fish reach larger sizes because they can fit more eggs and young in the oral cavity, and the risk of predation is lower because of their greater length.
For this catfish, we identified the occurrence of sexual dimorphism in the growth, the ring radius in the otoliths, the ring-formation period, the age structure, and the growth parameters, as a consequence of the different reproductive energy expenditure of females and males, demonstrating that otoliths can be used as tools in distinguishing life-cycle patterns between the sexes of the same species.
References
Alonso JC, Fabré NN (2003) Spatial and temporal pattern of the population structure and current state of fishing exploitation of the dourada (Brachyplatystoma flavicans, Lichtenstein, 1819) along the system estuary-Amazonas-Solimões. In: Welcomme R, Petr T (eds) The second international symposium on the Management of Large Rivers for fisheries. FAO & Mekong River Commission, Phnom Penh, p 14
Amaral MF, Aranha JMR, Menezes MS (1999) Age and growth of Pimelodella pappenheimi (Siluriformes, Pimelodidae) from an Atlantic Forest stream in southern Brazil. Braz Arch Biol Technol 42:1–5. https://doi.org/10.1590/S1516-89131999000400010
Araújo FG (1988) Distribuição, abundância relativa e movimentos sazonais de bagres marinhos (Siluriformes, Ariidae) no estuário da Lagoa dos Patos (RS), Brasil. Rev Bras Zool 5:509–543. https://doi.org/10.1590/S0101-81751988000400002
Araújo FG, Cruz-Filho AG, Azevedo MCC, Santos ACA (1998) Estrutura da comunidade de peixes demersais da Baía de Sepetiba, RJ. Rev Bras Biol 58:417–430. https://doi.org/10.1590/S0034-71081998000300007
Avigliano E, Carvalho BM, Velasco G, Tripodi P, Vianna M, Volpedo AV (2016) Nursery areas and connectivity of the adults anadromous catfish (Genidens barbus) revealed by otolith-core microchemistry in the South-Western Atlantic Ocean. Mar Freshw Res 68:931. https://doi.org/10.1071/MF16058
Avigliano E, Leisen M, Romero R, Carvalho B, Velasco G, Vianna M, Barra F, Volpedo AV (2017a) Fluvio-marine travelers from South America: cyclic amphidromy and freshwater residency, typical behaviors in Genidens barbus inferred by otolith chemistry. Fish Res 193:184–194. https://doi.org/10.1016/j.fishres.2017.04.011
Avigliano E, Carvalho BM, Leisen M et al (2017b) Otolith edge fingerprints as approach for stock identification of Genidens barbus. Estuar Coast Shelf Sci 194:92–96. https://doi.org/10.1016/j.ecss.2017.06.008
Avigliano E, Velasco G, Volpedo AV (2015) Use of lapillus otolith microchemistry as an indicator of the habitat of Genidens barbus from different estuarine environments in the southwestern Atlantic Ocean. Environ Biol Fish 98:1623–1632. https://doi.org/10.1007/s10641-015-0387-3
Azevedo MCC, Araújo FG, Cruz-Filho AG et al (1999) Variação espacial e temporal de bagres marinhos (Siluriformes, Ariidae) na Baía de Sepetiba, Rio de Janeiro. Rev Bras Biol 59:443–454. https://doi.org/10.1590/S0034-71081999000300009
Barbieri LR, dos Santos RP, Andreata JV (1992) Reproductive biology of the marine catfish, Genidens genidens (Siluriformes, Ariidae), in the Jacarepaguá lagoon system, Rio de Janeiro, Brazil. Environ Biol Fish 35:23–35. https://doi.org/10.1007/BF00001154
Beamish RJ, Fournier DA (1981) A method for comparing the precision of a set of age determinations. Can J Fish Aquat Sci 38:982–983. https://doi.org/10.1139/f81-132
Beamish RJ, McFarlane GA (1983) The forgotten requirement for age validation in fisheries biology. Trans Am Fish Soc 112(6):735–743. https://doi.org/10.1577/1548-8659(1983)112<735:TFRFAV>2.0.CO;2
Begot LH, Vianna M (2014) Legislação pesqueira costeira: o caso da Baía de Guanabara, RJ. Bol Inst Pesca 40:497–520
Bell MA (2001) Fish do not lie about their age … but they might lose count. Trends Ecol Evol 16:599–600. https://doi.org/10.1016/S0169-5347(01)02307-2
Campana SE (1999) Chemistry and composition of fish otoliths: pathways, mechanisms and applications. Mar Ecol Prog Ser 188:263–297
Campana SE (2001) Accuracy, precision and quality control in age determination, including a review of the use and abuse of age validation methods. J Fish Biol 59:197–242. https://doi.org/10.1006/jfbi.2001.1668
Carvalho BM, Corrêa MFM, Volpedo AV (2014) Lapillus otoliths of the Cathorops spixii (Spix & Agassiz, 1829) and Genidens genidens (Cuvier, 1829) (Actinopterygii - Ariidae). Acta Scientiarum. Acta Sci Biol Sci 36:343–347. https://doi.org/10.4025/actascibiolsci.v36i3.21117
Chang WYB (1982) A statistical method for evaluating the reproducibility of age determination. Can J Fish Aquat Sci 39:1208–1210. https://doi.org/10.1139/f82-158
Chaves PTC (1994) A incubação de ovos e larvas em Genidens genidens (Valenciennes) (Siluriformes, Ariidae) da Baía de Guaratuba, Paraná, Brasil. Rev Bras Zool 11:641–648. https://doi.org/10.1590/S0101-81751994000400008
Coggins LG, Gwinn DC, Allen MS (2013) Evaluation of age-length key sample sizes required to estimate fish total mortality and growth. Trans Am Fish Soc 142:832–840. https://doi.org/10.1080/00028487.2013.768550
Conand F, Camara SB, Domain F (1995) Age and growth of three species of Ariidae (Siluriformes) in coastal waters of Guinea. Bull Mar Sci 56:58–67
Cutrim L, Batista VDS (2005) Determinação de idade e crescimento do mapará (Hypophthalmus marginatus) na Amazônia Central. Acta Amazon 35:85–92. https://doi.org/10.1590/S0044-59672005000100013
Fischer LG, Pereira LED, Vieira JP (2011) Peixes Estuarinos e Costeiros, 2nd edn. Luciano Gomes Fischer, Rio Grande
Fuchs DV, Volpedo AV (2009) Morfología de Lapillus de Siluriformes Parano-Platenses. Biol Acuat 26:97–108
Garcia AM, Vieira JP, Burns MDM (2006) Genidens genidens (Cuvier) (Pisces, Ariidae), oral incubation of eggs. Panam J Aquat Sci 1(2):I
Gibbs MA, Kurth BN, Bridges CD (2013) Age and growth of the loricariid catfish Pterygoplichthys disjunctivus in Volusia blue spring, Florida. Aquat Invasions 8:207–218. https://doi.org/10.3391/ai.2013.8.2.08
Gomes ID, Araújo FG (2004a) Reproductive biology of two marine catfishes (Siluriformes, Ariidae) in the Sepetiba Bay. Rev Biol Trop 52:143–156
Gomes ID, Araújo FG (2004b) Influences of the reproductive cycle on condition of marine catfishes (Siluriformes, Ariidae) in a coastal area at southeastern Brazil. Environ Biol Fish 71:341–351. https://doi.org/10.1007/s10641-004-1265-6
Haddon M (2011) Modelling and quantitative methods in fisheries, 2nd edn. CRC Press, Boca Raton
Haimovici M, Reis EG (1984) Determinação de idade e crescimento da Castanha Umbrina canosai, (Pisces, Sciaeinidae) do Sul do Brasil. Atlântica 7:25–46
Labropoulou M, Papaconstantinou C (2000) Comparison of otolith growth and somatic growth in two macrourid fishes. Fish Res 46:177–188. https://doi.org/10.1016/S0165-7836(00)00144-2
Maciel TR, Vaz-dos-Santos AM, Caramaschi, EP, Vianna M (2018) Management proposal based on the timing of oral incubation of eggs and juveniles in the sentinel species Genidens genidens (Siluriformes: Ariidae) in a tropical estuary. Neotrop Ichthyol (in press)
Marceniuk AP, Menezes NA (2007) Systematics of the family Ariidae (Ostariophysi, Siluriformes), with a redefinition of the genera. Zootaxa 1416:1–126
Meniconi MFG, Silva TA, Fonseca ML, et al (2012) Baía de Guanabara: Síntese do Conhecimento Ambiental - v. 2. Biodiversidade. PETROBRÁS, Rio de Janeiro
MMA (2004) Instrução Normativa No 17, de 17 de outubro de 2004. Diário Oficial da União
Morales-Nin B, Stefano M, Potoschi A et al (1999) Differences between the sagitta, lapillus and vertebra in estimating age and growth in juvenile Mediterranean dolphinfish (Coryphaena hippurus). Sci Mar 63:327–336
Oliveira MR, Hawkins SJ, Trueman C, Yamamoto ME, Sathyabama S (2014) Revisão de estudos sobre determinação da idade através de otólitos dos peixes marinhos brasileiros. Biota Amazônica 4:125–131
Oliveira MR, Novelli R (2005) Idade e crescimento do bagre Genidens genidens na barra da Lagoa do Açú, norte do estado do Rio de Janeiro. Trop Oceanogr 33:57–66
Pandian TJ (2010) Sexuality in fishes. Science Publishers, Enfield
Panfili J, Pontual H, Troadec H, Wright P (2002) Manual of fish sclerochronology. Ifremet-IRD, Brest
Pauly D (1984) Fish population dynamics in tropical waters: a manual for use with programmable calculators. International Center for Living Aquatic Resources Management, Manila
Pérez A, Fabré NN (2009) Seasonal growth and life history of the catfish Calophysus macropterus (Lichtenstein, 1819) (Siluriformes: Pimelodidae) from the Amazon floodplain. J Appl Ichthyol 25:343–349. https://doi.org/10.1111/j.1439-0426.2008.01104.x
Prestrelo L, Vianna M (2016) Identifying multiple-use conflicts prior to marine spatial planning: a case study of a multi-legislative estuary in Brazil. Mar Policy 67:83–93. https://doi.org/10.1016/j.marpol.2016.02.001
Reis EG (1986a) Age and growth of the marine catfish, Netuma barba (Siluriformes, Ariidae), in the estuary of the Patos lagoon (Brasil). Fish Bull 84:679–686
Reis EG (1986b) A pesca artesanal de bagres marinhos (Siluriformes, Ariidae) no estuário da Lagoa Dos Patos, RS, Brasil. FURG, Rio Grande
Ricker WE (1975) Computation and interpretation of biological statistics of fish populations. Bulletin of the Fisheries Research Board of Canada, Ottawa
Silva-Junior DR, Carvalho DMT, Vianna M (2013) The catfish Genidens genidens (Cuvier, 1829) as a potential sentinel species in Brazilian estuarine waters. J Appl Ichthyol 29:1297–1303. https://doi.org/10.1111/jai.12280
Silva-Junior DR, Paranhos R, Vianna M (2016) Spatial patterns of distribution and the influence of seasonal and abiotic factors on demersal ichthyofauna in an estuarine tropical bay. J Fish Biol 89:821–846. https://doi.org/10.1111/jfb.13033
SUDEPE (1984) Portaria No 42, de 18 de outubro de 1984. Diário Oficial da União
Taylor CC (1958) Cod growth and temperature. ICES J Mar Sci 23(3):366–370. https://doi.org/10.1093/icesjms/23.3.366
Vaz-dos-Santos AM (2015a) Otolitos en estudios de edad y crecimiento en peces. In: Volpedo AV, Vaz-dos-Santos AM (eds) Métodos de estudios con otolitos: principios y aplicaciones. Buenos Aires, pp 303–332
Vaz-dos-Santos AM (2015b) Métodos cuantitativos aplicados al estudio de otolitos. In: Volpedo AV, Vaz-dos-Santos AM (eds) Métodos de estudios con otolitos: principios y aplicaciones. Buenos Aires, pp 167–185
Velasco G, Oddone MC (2004) Growth parameters and growth performance indexes for some populations of marine catfishes (Actinopterygii, Siluriformes, Ariidae). Acta Biologica Leopoldensia 26(2):307–313
Velasco G, Reis EG (2004) Changes in growth seasonality throughout Netuma barba (Lacépède, 1803) (Siluriformes, Ariidae) ontogeny. Braz J Biol 64:913–914. https://doi.org/10.1590/S1519-69842004000500024
Velasco G, Reis EG, Vieira JP (2007) Calculating growth parameters of Genidens barbus (Siluriformes, Ariidae) using length composition and age data. J Appl Ichthyol 23:64–69. https://doi.org/10.1111/j.1439-0426.2006.00793.x
Vigliola L, Meekan MG (2009) The back-calculation of fish growth from otoliths. In: Green B, Mapstone B, Carlos G, Begg G (eds) Tropical fish otoliths: information for assessment, management and ecology. Springer, Dordrecht, pp 174–211
Wallace RA, Selman K (1981) Cellular and dynamic aspects of oocyte growth in teleosts. Am Zool 21:325–343. https://doi.org/10.1093/icb/21.2.325
Wootton RJ, Smith C (2015) Parental care. In: Reproductive biology of teleost fishes. Wiley-Blackwell, Oxford, pp 251–279
Zar JH (2010) Biostatistical analysis, 5th edn. Prentice Hall, New Jersey
Acknowledgments
The authors are grateful to the team of Laboratório de Biologia e Tecnologia Pesqueira, UFRJ for their assistance in obtaining the specimens, processing the material in the laboratory, and for their helpful comments in the discussions, especially Sérgio Santos and Luana Prestrelo. We are also grateful to the team of Laboratório de Esclerocronologia, UFPR for their help in preparing the otoliths, and to the artisanal fishermen for their participation in obtaining biological material. Finally, we thank CNPq (MV, AMVS and TRM) and FAPERJ (MV) for the grants awarded, and the PELD-Baía de Guanabara (CNPq PELD 403809/2012-6), FAPERJ (E26/112.636/2012, E26/110.114/2013 and E26/201.334/2014).
Author information
Authors and Affiliations
Corresponding author
Rights and permissions
About this article
Cite this article
Maciel, T.R., Vaz-dos-Santos, A.M. & Vianna, M. Can otoliths of Genidens genidens (Cuvier 1829) (Siluriformes: Ariidae) reveal differences in life strategies of males and females?. Environ Biol Fish 101, 1589–1598 (2018). https://doi.org/10.1007/s10641-018-0804-5
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10641-018-0804-5