Author: Santana, Fábio Magno da Silva; Severi, William; Feitosa, Caroline Vieira; de Araújo, Maria Elisabeth
Date published: July 1, 2013
Coastal zones are areas of ecological transition sites that enable a connection between terrestrial and marine ecosystems, through genetic and biomass exchanges, characterizing them as dynamic and biologically diverse environments (Robertson & Lenanton 1984, Monteiro-Neto et al. 2008). Sandy beaches can occur in any type of coast subject to the availability and sufficient volume of sediments to be deposited by the waves above the sea level (Veloso & Neves 2009). Many marine species, such as most of Haemulidae and the juveniles of Carangidae, use these sites for different purposes (e.g. breeding, feeding, for shelter and migration) at different stages of their development (Blaber 2002).
Surf zones may be defined as dynamic environments, characterized by the turbulence and the high energy from waves, tides and currents motion (Römer 1990). They are considered as a part of the foreshore, which is the submerged portion of the beach profile, extending from the wave break line up to the lower border of the beach face. The kind of wave break depends on the declivity of the bottom and is produced by the destabilization of the waves originated with the reduction of depth (Veloso & Neves 2009).
Studies on the ichthyofauna have demonstrated the presence of many species in surf zones, mainly in the juvenile stage, highlighting its importance for these species in this stage of life cycle (Robertson & Lenanton 1984, Godefroid et al. 2001). However, feeding and also shelter are another important use of the surf zone area by fishes (Blaber & Blaber 1980, Lasiak 1984a, b, Whitfield 1996). Fish species living in these places are represented by active planktivores, detritivores, piscivores, beach nesters and migrants from adjacent ecosystems (Moyle & Cech 2000). The understanding of the trophic relationships between species, as well as the strategies, used to reduce mortality in early stages of their life cycle can be monitored by tracking the spatial and temporal variations of ichthyofauna in sandy environments (Pessanha & Araújo 2003, Falcäo et al. 2006).
Despite the relevance of the recruitment of coastal fish, there are few studies on the composition of fish assemblages in surf zones, in comparison with other coastal habitats (Wilber et al. 2003). And there is a lot of doubt about the factors that influence and control temporal variations of these assemblages in such areas (Clark et al. 1996). In Brazilian waters, researches aimed to understand the ecological role of species that reside or temporarily inhabit this ecosystem. In northeastern Brazil, for example, it can be mentioned studies on the composition of the ichthyofauna of three sandy beaches of Maceió, Alagoas (Teixeira & Almeida 1998) and Jaguaribe Beach, Pernambuco (Lira & Teixeira 2008, Santana & Severi 2009). Nevertheless, there is no publication that compares the composition and temporal variation on the fish assemblage structure in the surf zone in relation to other coastal environments, distribution of their life stages, or identification of those that are residents. Actually, most of the coastal zone is heavily human populated (Beatley et al. 2002) and the surf zones hold an increasing encumbrance as the focal area of recreation and suffer pollution from nearby urban centers (Chant et al. 2008). Determining the degree, to which surf-zone assemblages vary temporally, as well as the knowledge on the ichthyofauna in coastal areas and its use at any time, may serve as parameters for further observations and gathering of diagnoses about these sites. These information will help scientists better understand about the ecology and dynamics of the fauna, which can be critical to coastal and ocean management.
The present study aimed to characterize the ichthyofauna of the surf zone in Jaguaribe beach, Itamaracá-PE, analyzing the day and night parameters, as well as moon phases, and identifying the resident species and their seasonal use.
Material and Methods
1. Study area
Jaguaribe beach (Figure 1) is located in the northern portion of Itamaracá island (Pernambuco) (07° 43' 08" and 07° 45' 32" S, 034° 50' 14"and 034° 51' 05" W). It constitutes a flat area at low altitude (30-60 m) with sharp drop near the coast. The adjacent coastal marine environment, locally called "inner sea", is sheltered by a reef line parallel to the shore, about 3-4 km from the beach front, with a profile perpendicular to it, with low declivity and maximum depth of 5 m, usually less than 2 m (Kempf 1970). The benthos are characterized by little active or dead coralline formations and encrusting coralline algae, sitting on sandstone foundation (Medeiros & Kjerfve 1993). It presents waves predominantly towards southeast, with the mainstream to the north (Santana & Severi 2009). Its substrate consists of sandy bottom with high content of calcium carbonate derived from the decomposition of the rock formation originated from coastal erosion, and sediment composed of quartz sand, shells of mollusks, foraminifera and fragments of Halimeda and Lithothamnium calcareous algae (Lopes 1999, Guerra et al. 2005). Extensive stands of seagrass beds Halodule wrightii are associated with mixed banks interspersed with Caulerpa, Sargassum and Halimeda (Kempf 1970).
2. Field collection
Collections were performed monthly between March 2006 and February 2007, at new and first quarter moons, encompassing spring and neap tides, in day and night periods, always at low tide. A beach seine net, 20 m long, 1.5 m high and 5 mm intemode mesh, was used. Two manual trawling were made in day and night periods, totaling 8 trawling/month, each lasting about 10 minutes. Trawling was parallel to the coast and towards north, at depth inferior to 1.50 m, along a 25 m segment of beach strip (07° 43' 42.9" S, 034° 49' 32.1" W).
The specimens were fixed in 10% fonnalin and preserved in 70% ethanol. The taxonomic identification was based on Figueiredo (1977), Figueiredo & Menezes (1978, 1980, 2000), Menezes & Figueiredo (1980, 1985), Carpenter (2002a, b), Araújo et al. (2004) and Marceniuk (2005) and the classification of families according to Nelson (2006). The specimens were stored in the ichthyological collection at the Laboratory of Ichthyology, Department of Fisheries and Aquaculture, Federal Rural University of Pernambuco.
3. Rainy and dry seasons
Since the pluviométrie distribution showed no well-defined pattern, the rainy season was considered as the months with rainfall exceeding 100 imn, being the remaining months regarded as dry season, according to the data obtained from Laboratorio de Metereologia de Pernambuco (Laboratorio. ..2011). During the study period, the rainy season was established including the months from March to August of 2006 and February of 2007, and the dry season from September 2006 to January 2007.
4. Data analysis
The abundance and frequency of occurrence for each fish species were based on the pooled samples from the two trawlings made in each collection, which were analyzed per period and tide, and later grouped for the analysis per month and season (dry and wet). The combined influence of tide and period of the day on data was evaluated per month and season. The Kolmogorov-Smimov test (PO.05) was used to verity data normality. For normally distributed data, it was used the One-Way ANOVA and the Fisher's post hoc test (PO.05). When the data were not distributed normally, the nonparametric tests Mann-Whitney and Kruskal-Wallis (P <0.05) were used, employing the Statistica software (StatSoft 2008).
The characterization of abundance and occurrence frequency of species was adapted from Garcia & Vieira (2001). It was considered abundant, in a certain season, the species that had a percentage of individuals (PN%) higherthanthe ratio 100/S, where S is the nmnber of species present in that season. The species that had an occurrence frequency (OF%) higher than 50% at that season were considered frequent. From this point, the species were classified and grouped according to their values of PN% and FO% in: (1) Abundant and frequent (AF) (PN% > 100/S and FO% > 50); (2) Abundant and little frequent (ALF) (PN%> 100/S andFO%<50); (3) little abundant and frequent (LAF) (PN% < 100/S and FO% > 50) and (4) little abundant and infrequent (LAI) (PN% <100 /S and FO% < 50).
The abundant and frequent species (AF) were considered resident. Those that were AF both in the rainy and in the dry seasons were treated as annual resident (AR). Those which were abundant and frequent (AF), in only one of the seasons were considered resident in the dry (RD) or in the rainy season (RR), accordingly.
For the analysis of life stages and Bray-Curtis similarity, the resident species were also selected. Two phases of life were considered: juvenile and adult. To determine the age limit for adult phase, scatter plots were made with the cut corresponding to 25% of the maximum size of the species (Vazzoler et al. 1999), period at which the animal is presumably able to breed, therefore being considered an adult. Animals that were below this line were considered juvenile. The maximum size of each species (Lmax) was based on Figueiredo & Menezes (1978), Menezes & Figueiredo (1980, 1985) and Carpenter (2002a, b).
In the analysis of grouping between species, a matrix of Bray- Curtis similarity was elaborated and the data of monthly abundance were transfonned by the fourth root. The results were expressed as a dendrogram, using the grouping by unweighted arithmetic mean (UPGMA), employing the PRIMER statistical package version 4.0 (Primer-E 2000).
Atotal of6,407 individuals were sampled belonging to 90 species and 35 families. The families, which are most representative in nmnber of species, were Sciaenidae (10), Engraulidae, Haemulidae (9), Carangidae (8), Achiridae, Ariidae, Clupeidae, Gerreidae (4), and Cynoglossidae (3). These nine families represented about 62% of all species caught. The 15 most numerically abundant species amounted to almost 91% of total individuals. They were Anchoviella lepidentostole, Bairdiella ronchus, Lycengraulis grossidens, Polydactylus virginicus, Larimus breviceps, Anchoa tricolor, Chiro centro don bleekerianus, Pomadasvs corvinaeformis, Stellifer stellifer, Stellifer rastrifer, Lile piquitinga, Conodon nobilis, Menticirrhus americanas, Pellona harroweri and Anchoa marinii (Table 1)
Figure 2 illustrates the classification of the fish species caught in the surf zone regarding their abundance and frequency in the rainy and dry seasons and year-round. Only A. tricolor, B. ronchus, L. breviceps and P virginicus showed 100% occurrence (Table 1). It is observed that the rarest and least abundant species correspond to nearly70% of the fish sampled.
Between dry and rainy seasons the total nmnber of fish did not differ significantly (F = 1.39, p = 0.265). Regarding daytime and nighttime collections the total number of fish was significantly different (U = 11,500, p = 0.00048) in the annual analysis, as well as in the dry (F = 10.54, p = 0.012) and in the rainy season (U = 6,500, p = 0.02145), with the highest nmnber of fish being found during the day in all cases analyzed. In the analysis that groups moon-day data a significant difference in the total nmnber of fish was found (KW = 16.0337, p = 0.0011). Daytime showed a higher nmnber of fish (5078) compared to night time (1329) in crescent and new moons. Regarding seasonality of all species analyzed, seven were annual residents (A. tricolor, A. lepidentostole, B. ronchus, L. breviceps, L. grossidens, P. virginicus and P. con'inaeformis), three were resident probably only in the dry season (C. nobilis, L. piquitinga and AI. americanas) and two (C. spixii and N. asta) in the rainy season, and the latter one was recorded only in this season (Table 2).
Considering the life stage of species, three of them (A. tricolor; C. spixii andL. piquitinga) were recorded only in adulthood in both rainy and dry seasons. Bairdiella ronchas, M. americanas and N. asta were present only in juvenile stage. For the other species, the stages of life varied according to the season (Table 2).
The analysis of similarity between species originated two main groups separating the annual resident species (A) from the seasonal resident (B) ones, except fori5, cotvinaefotmis, an annual resident, although it seems to have been gathered in the latter group for presenting a total abundance quite lower than that of annual resident species (Figure 3).
The grouping of annual resident species (A) was subdivided into two subgroups: one with a regular (Al) and another with an irregular distribution in the seasons (A2 ). The subgroup with resident species with an irregular distribution has a subgroup (A3) formed by L. grossidens and P. vitginicus, which, although being annual residents, presented their abundance peak during the dry season, while A. tricolor and L. breviceps (subgroup A4) did not show the same pattem (Figure 3).
Within the other group (B), N. asta and C. spixiii (subgroup Bl) were considered residents of the surf zone during the rainy season, whereas L. piquitinga, M. americanas, C. nobilis and P. cotvinaefotmis formed subgroup B2, containing only the dry season resident species, except for the annual resident P. cotvinaefotmis. The subgroup B3, included in the latter subgroup, encompasses L. piquitinga and M. americanas which were detached from subgroup B4 because they presented low number of individuals in the rainy season (Figure 3).
The number of families (35) and species found (90) was higher than the 15 families and 25 species found by Lira & Teixeira (2008) in this same beach. Although the same fishing gear was used in both studies (beach seine net), the differences between them seem to be related to divergences in net size and collecting period, both larger in our study. This research performed manual trawling and this is the best methodology when compared with trawling realized by motor boat, once the motor noise can drive off some individuals (Pereira et al. 2010).
The occurrence of rare species is constant in surf zones ( Veloso & Neves 2009). Among those recorded in the present study, some stood out for their varied life habits: Achiras achiras, Chilomycterus spinosus spinosus, Genyatremus lateas, Isophistus patvipinis, Stellifer brasiliensis, Thalassophyme nattereri, Trichiums lepturus, Ocyurus cinysurus, Selene setapinnis, Alphestes afet; Archosargus probatocephalus, Chaetodiptemsfaber, Carangoides bartholomaei, Carangoides cinysos, Holocentrus adscencionis, H. aurolineatuni, H. squamipinna, Scomberomorus cavalla, Sphoeroides spengleri and Sphyraena barracuda. It is also noteworthy mentioning that the latter eleven species are usually found near or associated to reefs, and have been recorded along reef formations off the southern coast of Pernambuco and northern coast of Alagoas states (Ferreira & Cava, 2001). However, the relative occurrence of reef fish species cited above were not discussed in this manuscript as these species were considered little abundant and infrequent (LAI ). The exception was N. asta, because although it was rare, was classified as annual resident.
As most of the dominant species in the surf zone (Anchoviella lepidentostole, Anchoa tricolor, Bairdiella ronchas, Larimus breviceps, Lycengraulis grossidens) form shoals and have an annual occurrence, they seem to have contributed for the total number of individuals not having differed between the dry and rainy seasons. The number of individuals was higher during the day in both annual and seasonal analysis. During the day phytoplankton activity enables a greater supply of food thus attracting many consumer individuals. Being prominently shallow regions, surf zones concentrate an even greater amount of these microorganisms ( Schlacher et al. 2008). Fish species with nocturnal habits are generally predators (Helfman et al. 2009), and are less abundant than lowtrophic level ones. Furthermore, many carnivorous or omnivorous species are planktivorous as juveniles (Helfman et al. 2009). Considering that the surf zone is dominated by juvenile or small individuals (Robertson & Lenaton 1984), file highest total abundance for the ichthyofauna is indeed expected at daytime, independent of moon phase. Besides, fishes alter their behavior between periods by a vertical migratory activity, which bring them from near the bottom during the day into midwater at night (Beamish 1966). Differences in fish fauna composition and abundance between periods of the day also have been attributed to foraging and predator avoidance strategies (Gibson et al. 1996, Félix-Hackradt et al. 2010). The ability to shoal and the role of dominant species in total abundance associated to differences in their use of interconnected habitats throughout the day, such as estuaries/ mangroves (Faimce & Serafy 2006) and seagrass meadows (Parrish 1989) in the "inside sea", may explain the predominant abundance reduction during night period in the study area.
Among the species analyzed, seven species were considered annual residents: Anchoa tricolor, Anchoviella lepidentostole, Bairdiella ronchas, Conodon nobilis, Larimus breviceps, Lycengraulis grossidens, Polydactylus vitginicus and Pomadasys corvinaeformis, as they are abundant and frequent (AF) in both seasons. For Anchoa tricolor and Larimus bre\nceps file largest samples and individuals were captured at the end of the rainy season and early dry season. Within Itamaracá ecosystem, A. tricolor is characterized as a marine dependent species, which means its uses estuarine waters for feeding or to accomplish a late phase of its reproductive cycle (Vasconcelos Filho & Oliveira 1999), and Larimus breviceps was also regarded as resident by Fagundes et al. (2007) in the surf zone of Santos Bay, Sào Paulo. It is probable that Anchoa tricolor inhabit file surf zone and spawn in the estuary, also used for nursery and recruitment phases (El-Deir 2005 ). Larimus bre\nceps might use this area as a nursery as well and when adult (late rainy season and early dry season) migrate to areas of greater depth known on the Island of Itamaracá as "outer sea".
The species Anchoviella lepidentostole and Bairdiella ronchas were found in the surf zone during almost the whole period of the study, with the later one being represented mainly by juveniles. Both are common in ichthyofaunal surveys for this ecosystem in other areas of the Brazilian coast (Godefroid et al. 2004, Oliveira- Neto et al. 2008). However A. lepidentostole was not recorded on file assessment of ichthyofauna conducted with the same fishing gear on Jaguaribe beach (Lira & Teixeira 2008) and in the Channel of Santa Cruz (Vasconcelos Filho & Oliveira 1999), both located on Itamaracá Island. This might be due to the lower sampling effort evidenced in these studies in relation to the present one, since A. lepidentostole is commonly found in estuarine areas along the Brazilian coast (Paiva Filho et al. 1986, Paiva Filho & Giaimini 1990, Chaves & Vendel 2008), including Pernambuco (Paiva & Araujo 2010). Concerning the use of estuaries, A. lepidentostole is a semi-anadromous fish and its arrival in the estuary is through shoals composed by older individuals, whereas the younger ones remain in file sea to feed and grow, entering the estuary later, when they reach sexual maturity (Camara et al. 2001 ). B. ronchas has been regularly recorded to breed in this ecosystem (Chaves & Bouchereau 2004). The surf zone is used asa feeding and growing ground ( Santana & Severi 2009) by A. lepidentostole, as well as a nursery area by B. ronchas. This species is known to use different coastal habitats for completion of file reproductive cycle, such as mangroves, estuaries and adjacent coastal environments, as previously reported elsewhere (Chaves 1995, Castro et al. 1999). Due to the predominance of juveniles throughout file whole year, it can be stated that Polydactylus vitginicus uses the surf zone as a nursery and growing place as the species cited above. Adults occurred in a smaller number and had two peaks, one at the beginning and another one at the end of the dry season. These might be file periods when they migrate to marine demersal regions, where they complete their life cycle. The individuals that live in demersal areas of some parts of the Brazilian coast (Souza & Chaves 2007, Moraes et al. 2009) have larger sizes than those found in this study.
Regarding the occurrence of life phases between seasons, a different pattem was observed in the resident species Lycengraulius grossidens and Pomadasys corvinaeformis in the study area. L. grossidens is a marine (Anacleto & Gomes 2006) and estuarine (Schifino et al. 2004) species, and is well distributed in the estuaries of Pernambuco (Paiva & Araujo 2010), including that of Jaguaribe river - Itamaracá (El-Deir 2005). In our study, only adult individuals were found in the rainy season and only juveniles in the dry season. In file estuary of Lagoa dos Patos (RS), eggs and larvae of this species are file most numerous and abundant ones among the collected species. They occur during the summer because water temperature, instead of salinity, presents a stronger influence on spawning (Anacleto & Gomes 2006).
During the rainy season in the northeastern region, adult fish might use the surf zone to feed and then migrate to the estuary at file end of this season. The recruitment in the surf zone occurs during the dry season. The opposite was recorded for Pomadasys corvinaeformis. This species inhabits demersal, marine and estuarine areas (Cervigón 2003), with records for the Jaguaribe river estuary (El-Deir 2005), Itamaracá. Although juveniles prevailed during the rainy season, January represented the peak for this life phase, and the predominance of adults occurred during the dry season. The results of this study corroborate with those of Costa et al. (1995) on the coast of Ceará, which associated the abundance of the species with rainfall. Elowever, Chaves (1998) disagreed with Costa et al. (1995) because the abundance of the species in Guaratuba Bay (PR) depended more on the reduction of water temperature rather than the pluviométrie indicators. It is noteworthy the divergences between the climates of the two areas, given that there are only two seasons in northeast and four in south Brazil, which make difficult a direct ecological comparison.
In this study, five species showed seasonal residence: Cathorops spixii, Conodon nobilis, Lile piquitinga, Menticitrhus anieticanus and Nicholsina usta. Cathorops spixii and N. usta were considered resident of the rainy season. The first one is the most common catfish species on the Brazilian coast, preferably living in estuaries (Carvalho-Filho 1999). In the Channel of Santa Cruz, Itamaracá, this species is known to spend its entire life cycle in such environments, but it can also be found in coastal marine habitats and fresh waters (Vasconcelos Filho & Oliveira 1999). Its residence on the rainy season, corroborating with Lira &Teixeira (2008), was represented only by adult individuals in the surf zone, with a peak between May and July. According to Chalom et al. (2008), C. spixii is opportunistic, eating most of the available food in the environment, and shrimp being one of the most representative items of its diet. Therefore, the large amount of specimens found in the rainy season in Jaguaribe beach seems to be related to the high abundance of penaeid shrimp, also found during this season in the surf zone, in accordance with personal observations made throughout this research. Differing from C. spixii, N. usta is characteristic of coral reefs (Randall 1990), occurring in the surf zone exclusively in this season. Only juvenile individuals represented this species, with its peak in March and April. The species lives associated with marine phanerogam meadows (Arrivillaga & Baltz 1999, Ordóñez-López & García-Hemández 2005, Allen et al. 2006, Prado & Heck Junior 2011). Since there is no record of this species in the estuaries of Pernambuco (Paiva & Araujo 2010), and the surf zone of Jaguaribe beach is rich in Halodule wtightii marine phanerogam (Kempf 1970), the species possibly migrates from the reef areas to graze in the surf zone during its recruitment period.
Some species had higher frequency in a determinate season. These were the case oí Li le piquitinga saàMenticirrhus anieticanus. Lile piquitinga is a characteristic species of the Northeastern region (Figueiredo & Menezes 1978). It occurred in the surf zone of Jaguaribe beach, even though it was not registered in this site by Lira & Teixeira (2008). Considered as marine dependent on the Santa Cruz Channel estuary (Vasconcelos Filho & Oliveira 1999), it is widely found in the estuaries of Pernambuco (Paiva & Araujo 2010). In the surf zone, it was represented by adults and showed a well-defined seasonal pattem of occurrence, being frequent in the dry season, with its peak in December. In the Jaguaribe River estuary, this species was found in the rainy season (El-Deir 2005 ), suggesting that it is using the estuary in this season and the surf zone during the dry season, before migrating to deeper areas. Differently, M. anieticanus, represented only by juveniles, was little abundant, although frequent in the rainy season, and abundant and frequent during the dry season. The results of this study indicate the surf zone as a nursery area for this species, corroborating with Godefroid et al. (2001 ), who noted the presence of larvae and juveniles in Pontal do Sul beach (PR). Adults do not usually occur in the surf zone, but are regularly caught in deeper water (Souza & Chaves 2007). The species depends on the estuary to complete its reproductive cycle (Vasconcelos Filho & Oliveira 1999), and has been recorded in several estuaries of Pernambuco (Paiva & Araujo 2010). M. anieticanus possibly alternates the type of ecosystem used as nursery, according to the season of the year: the surf zone (dry period) and estuary (rainy period).
The haemulid Conodon nobilis was represented in both seasons, mainly by juvenile individuals, with its peak in January (end of the dry season). Adults of this species are commonly caught incidentally in demersal areas during shrimp fishing (Viamia et al. 2004, Souza & Chaves 2007), considering that juvenile individuals might use the surf zone as nursery, and the month of January being the recruitment period. In the region of Itamaracá, this species was considered as a visitor to the Santa Cruz Channel (Vasconcelos Filho & Oliveira 1999) and as frequent in Jaguaribe beach (Lira & Teixeira 2008), corroborating with the present study.
Although not being a resident species in either of the seasons, some species showed a defined pattem of occurrence, such as Chirocentrodon bleekerianus, Hyporhamphus roberti, Stellifer rastrifer and Trinectes paulistatuts. Chirocentrodon bleekerianus presented a regular abundance in determinate months (July to October). It is a characteristic species of coastal areas (Carvalho- Filho 1999), but there are only two previous records for the coast of Pernambuco (Lira & Teixeira 2008, Santana et al. 2009). Adults might reach the surf zone in search for food, as they eat some fish and crustaceans (Corróa et al. 2005), preys commonly found in this ecosystem. The time of higher incidence of C. bleekerianus coincided with the peak of juvenile Engraulidae and post-larvae of penaeid shrimp (personal observation) in this season ( July-October). Stellifer rastrifer also prey on penaeid shrimp (Camargo & Isaac 2004), and has its peak of abundance coinciding with the time when the peak of such prey occurred (in August). This species occurs in coastal shallow waters (Carvalho-Filho 1999), characteristic of estuarine areas (Araujo et al. 2004), being registered in the Santa Cruz Channel (Vasconcelos Filho & Oliveira 1999). It is occasionally found in Jaguaribe beach (Lira & Teixeira 2008, Santana & Severi 2009). This species occurred from July to October, peaking in August, being represented by juvenile and adults. Hyporhamphus robetii was represented only by adults during the year of study, peaking in July. As this species occurs in estuarine areas (Carpenter 2002a), having been recorded in the estuary of Jaguaribe River (El-Deir 2005), it probably comes to shore to eat shrimps, which are abundant in the rainy season (personal note). Hiatt & Strasburg ( 1960) cited in Randall (1967) reported small fish and planktonic crustaceans as food items for fish of this genus. Trinectes paulistanus was little abundant in Jaguaribe beach, corroborating with Mendonça & Araujo (2002) that analyzed the temporal distribution of this species in Sepetiba Bay (RJ). It occurs in estuarine and marine environments (Figueiredo & Menezes 2000), being present in the northeastern coast (Araujo et al. 2004). Only the adults occupied the surf zone in both seasons (wet and dry). The occurrence of larvae and juveniles of this species is recorded in estuarine areas (Michele & Uieda 2007), whereas adults inhabit different areas, including shores (Godefroid et al. 2004). The species possibly uses the surf zone environment as an intermediary one between the Jaguaribe River estuary and the "outer sea".
Coastal marine systems are among the most ecologically and social-economically vital ones for the planet, therefore subject to the cumulative effects of global change, including climate change, increased population, pollutant discharge and eutrophication (Harvey et al. 2006, Rabalais et al. 2009). Thus, estuarine and coastal waters are potentially bound to biodiversity loss and community disruption, with unpredictable consequences on fish stocks and fishery sustainability, unless surf zones' role on coastal fishes' life cycle is better understood and incorporated in conservation practices and environmental management actions.
The surf zone of Jaguaribe beach presents an ecological importance as it encompass a great diversity of fishes, including species considered rare for this ecosystem, as well as species which are resident annually or seasonally. The distribution patterns of species found in this study show that the ichthyofauna of the surf zone in Jaguaribe beach is rich, mainly dominated by small-sized individuals including juvenile phase of several species, with the presence of species most commonly found in neighboring environments, such as seagrass beds, estuaries and reefs. The role of surf zones as an integrated component of interconnected environments in coastal areas of Pernambuco, and their function in the life cycle of coastal fishes is probably a common ecological pattem for the beaches on tropical coastal.
The authors are grateful to Fundaçào Apolônio Salles de Desenvolvimento Educacional (FADURPE), for its essential logistical support for the accomplishment of this work; Fundaçào de Amparo à Ciência do Estado de Pernambuco (FACEPE), PELD and Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq), for having granted a PhD scholarship to the fonner author, and a researcher scholarship to the latter; and Biologist Anailza Cristina, for her invaluable assistance during collection activities.
ALLEN. T.. JIMÉNEZ. M. & VILLAFRANCA. S. 2006. Estructura y categorías tróficas de peces asociados a praderas de Thalassia testudinum (Hydrocharitales, Hydrocharitaceae) en el golfo de Cariaco, Estado de Sucre, Venezuela. Invest. Mar. 34(2): 125-136.
ANACLETO, E.I. & GOMES, E.T. 2006. Relaçôes tróficas no plâncton em um ambiente estuarino tropical: Lagoa dos Patos (RS), Brasil. Saúde Amb. Rev.l(2):26-39.
ARAÚJO, M.E., TEIXEIRA, J.M.C. & OLIVEIRA, A.M.E. 2004. Peixes estuarinos marinhos do nordeste brasileiro: Guia Ilustrado. Editora UFC, Fortaleza.
ARRIVILLAGA, A. & BALTZ, D.M. 1999. Comparison of fishes and macro invertebrate s on seagrass and bare-sand sites on Guatemala's Atlantic Coast. Bull. Mar. Sei. 65(2):301-319.
BEAMISH, F.W.H. 1966. Vertical migration by demersal fish in the Northwest Atlantic. J. Fish. Res. Board Can. 23:109-139. http://dx.doi.org/10.1139/ 056-009
BEATLEY, T, BROWER, D. J. & SCHWAB, A. K. 2002. An introduction to coastal zone management. 2nd ed. Island Press, 329p.
BLABER, S.J.M. 2002. 'Fish in hot water': the challenges facing fish and fisheries research in tropical estuaries. J. Fish Biol. 61(A): 1-20.
BLABER, S.J.M. & BLABER, T.J. 1980. Factors affecting the distribution of juvenile estuarine and inshore fish. J. Fish Biol. 17:143-162. http://dx.doi. org/10.1111/j. 1095-8649.1980.tb02749.x
CAMARA, J.J.C., CERGOLE, M.C., CAMPOS, E.C. & BARBIERI, G. 2001. Estruturapopulacional, crescimento, mortalidade e taxa de explotaçao do estoque de manjuba, Anchoviella lepi dentó stole (Pisces, Engraulidae), do rio Ribeira de Iguape, sudeste do estado de Sao Paulo, Brasil, durante o período de 1993 a 1996. Bol. Inst. Pesca 27(2):219 -230.
CAMARGO, M. & ISAAC, V. 2004. Food categories reconstruction and feeding consumption estimates for the Sciaenid Macrodon ancyiodon (Bloch & Schneider), and the congeneric fishes Stellifer rastrifer (Jordan) and Stellifer naso (Jordan) (Pisces, Perciformes) in the Caeté Estuary, Northern Coast of Brazil. Rev. Bras. Zool. 21(l):85-89.
CARPENTER, K.E. (ed.). 2002a. The living marine resources of the Western Central Atlantic.Volume 2: Bony fishes part 1 (Acipenseridae to Grammatidae). FAO, Rome.
CARPENTER, K.E. (ed.). 2002b. The living marine resources of the Western Central Atlantic. Volume 3: Bony fishes part 2 (Ophistognathidae to Molidae), sea turtles and marine mammals. FAO, Rome.
CARVALHO-FILHO, A. 1999. Peixes: costa brasileira. Melro, Säo Paulo.
CASTRO, L.T., SANTOS-MARTINEZ, A. & ACERO, P.A. 1999. Reproducción de Bairdiella ronchus (Pisces: Sciaenidae) em la Ciénaga Grande de Santa Marta, Caribe Colombiano. Rev. Biol. Trop. 47(3): 1-7.
CERVIGON, F. 1993. Los peces marinos de Venezuela. Volume 2. Fundación Científica Los Roques, Caracas.
CHALOM, A., MUTO, E.Y. & SOARES, L.S.H. 2008. Variabilidade trófica na alimentaçâo do bagre-amarelo Cathorops spixii (Agassiz, 1829) no litoral do estado de Säo Paulo. In Oceanografía e mudanças globais III Simposio brasileiro de oceanografía (E.S. Braga, coord.). Instituto Oceanógrafico da Universidade de Säo Paulo, Säo Paulo, p.257-272.
CHANT, R.J., WILKIN, J., WEIFENG, Z., CHOI, B., HUNTER, E., CASTELAO, R., GLENN, S., JURISA, J., SCHOFIELD, O., HOUGHTON, R., KOHUT, J., FRAZER, T.K. & MONLINE, M.A. 2008. Dispersal of the Hudson River Plume on the New York Bight. Oceanography 21(4): 149-162. http://dx.doi.org/10.5670/oceanog.2008.ll
CHAVES, PTC. 1995. Atividade reprodutiva de Bairdiella ronchus (Cuvier) (Pisces, Sciaenidae) na Baía de Guaratuba, Paraná, Brasil. Rev. Bras. Zool. 12(4):759-766.
CHAVES, PTC. 1998. Estrutura populacional de Pomadasys corvinaeformis (Steindachner) (Teleostei, Haemulidae) na Baía de Guaratuba, Paraná, Brasil. Rev. Bras. Zool. 15(l):203-209.
CHAVES, PTC. & BOUCHEREAU, J.L. 2004. Trophic organization and functioning of fish population in the Bay of Guaratuba, Brazil, on the basis of atrophic contribuction factor. Acta Adriat. 45(1): 83-94.
CHAVES, PT. & VENDEL, A.L. 2008. Análise comparativa da alimentaçâo de peixes (Teleostei) entre ambientes de marisma e de manguezal num estuário do sul do Brasil (Baía de Guaratuba, Paraná). Rev. Bras. Zool. 25(1):10-15.
CLARK, B.M., BENETT, B.A. & L AM BERTH, S.J. 1996a. Factors affecting spatial variability in the seine net catches of fish in the surf zone of False Bay, South .Africa. Mar. Ecol., Prog. Ser. 131:17-34.
CORRÊA, C.E., CHAVES, P.T.& GUIMARÄES, P.R.B. 2005. Biology of Chirocentrodon hleekerianus (Poey, 1867) (Clupeiformes: Pristigasteridae) in a Continental Shelf Region of Southern Brazil. Braz. .Arch. Biol. Technol. 48(3):419-427.
COSTA, P.S.R., SANTOS, M.A.M., ESPÍNOLA, M.F.A. & MONTEIRO- NETO, C. 1995. Biología e biometria do coró, Pomadasys corvinaeformis (Steindachner) (Teleostei: Pomadasyidae), em Fortaleza, Ceará, Brasil. Arq. Cieñe. Mar. 29(l-2):20-27.
EL-DEIR, A.C.A. 2005. Composiçâo e distribuiçâo espaço-temporal de formas iniciáis de peixes no estuário do rio Jaguaribe, Itamaracá, litoral norte de Pernambuco, Brasil. Tese de doutorado, Universidade Federal da Paraiba, Joäo Pessoa.
FAGUNDES, L., TOMÁS, A.R.G., CASARINI, L.M., BUENO, E.F., LOPES, G.M., MACHADO, D.A.L., ROSA, R.A., BRAGA, A.C.A., CAMARGO, F.B.F., OBERG, I.M.F. & PELLEGRINI, S.O.P. 2007. A pesca de arrasto-de-praia na ilhade Säo Vicente, Säo Paulo, Brasil. Série Relatónos Técnicos, Säo Paulo, v.29, p.1-45.
FALCÄO, M.G., SARPÈDONTI, V, SPACH, H.L., OTERO, M.E.B., QUEIROZ, G.M.L.N. & SANTOS, C. 2006. A ictiofauna em planicies de maré das Baías das Laranjeiras e de Paranaguá, Paraná, Brasil. Rev. Bras. Zoocienc. 8(2): 125-138.
FAUNCE, C.H. & SERAFY, J.E. 2006. Mangroves as fish habitat: 50 years of field studies. Mar. Ecol., Prog. Ser. 318:1-18
FÉLIX-HACKRADT, F.C., SPACH, H.L., MORO, PS., PICHLER, H.A., MAGGI, A.S., HOSTIM-SILVA, M.& HACKRADT, C.W. 2010. Diel and tidal variation in surf zone fish assemblages of a sheltered beach in southern Brazil. Lat. .Am. J. Aquat. Res. 38(3):447-460.
FERREIRA, B.P & CAVA, F. 2001. Ictiofauna marinha da Apa Costa dos Coráis: lista de espécies através de levantamento da pesca e observaçôes subaquáticas. Bol. Téc. Cient. CEPENE 9:25-36.
FIGUEIREDO, J.L. 1977. Manual de peixes marinhos do sudeste do Brasil. I. Introduçao. Caçôes, raias e quimeras. Museu de Zoología, Universidade de Säo Paulo, Säo Paulo.
FIGUEIREDO, J.L. & MENEZES, N.A. 1978. Manual de Peixes Marinhos do Sudeste do Brasil. II. Teleostei (1). Museu de Zoología, Universidade de Säo Paulo, Säo Paulo.
FIGUEIREDO, J.L. & MENEZES, N.A. 1980. Manual de Peixes Marinhos do Sudeste do Brasil. III. Teleostei (2). Museu de Zoología, Universidade de Säo Paulo, Säo Paulo.
FIGUEIREDO, J.L. & MENEZES, N.A. 2000. Manual de Peixes Marinhos do Sudeste do Brasil. VI. Teleostei (5). Museu de Zoología, Universidade de Säo Paulo, Säo Paulo.
GARCIA, A.M. & VIEIRA, J.P 2001. O aumento da diversidade de peixes no estuário da Lagoa dos Patos durante o episodio El Niño 1997-1998. Atlántica 23:85-96.
GIBSON, R.N., ROBB, L., BURROWS, M.T. & ANSELL, A.D. 1996. Tidal, diel and long term changes in the distribution of fishes on a Scottish sandy beach. Mar. Ecol., Prog. Ser. 130:1-17. http://dx.doi.org/10.3354/ meps130001
GODEFROID, R.S., SANTOS, C., HOFSTAETTER, M. & SPACH, H.L. 2001. Occurrence of Larvae and Juveniles of Eucinostomus argenteus, Eucinostomus gula, Menticirrhus americanus, Menticirrhus littoralis, Umbrina coroides and Micropogonias furnieri at Pontal do Sul beach, Paraná. Braz. .Arch. Biol. Technol. 44(4):411-418.
GODEFROID, R.S., SPACH, H.L., SANTOS, C., MacLAREN, G. & SCHWARZ JUNIOR, R. 2004. Mudanças temporais na abundância e diversidade da fauna de peixes de um infralitoral raso de urna praia, sul do Brasil. Iheringia, Zool. 94(1):95-104. http://dx.doi.org/10.1590/ S0073-47212004000100017
GUERRA, N.C., KIANG, C.H. & SIAL, A.N. 2005. Carbonate cements in contemporaneous beachrocks, Jaguaribe beach, Itamaracá island, northeastern Brazil: petrographic, geochemical and isotopic aspects. .Ann. N.Y. Acad. Sei. 77(2):343-352.
HARVEY, C.D.G., HUGHES, A.R., HULTGREN, K.M., MINER, B.G., SORTE, C.J.B., THORNBER, C.S., RODRIGUEZ, L.F., TOMANEK, L. & WILLIAMS, S.L. 2006. The impacts of climate change in coastal marine systems. Ecol. Lett. 9:228-241. PMid: 16958887. http://dx.doi. org/10.1111/j. 1461-0248.2005.00871.x
HELFMAN, G., COLLETTE, B.B., FACEY, D.E. & BOWEN, B. 2009. The diversity of fishes. Biology, evolution and ecology. 2nd ed. John Wiley & Sons, Willey-Blackwell.
HIATT, R.W. & STRASBURG, D.W. 1960. Ecological relationships of the fish fauna on coral reefs of the Marshall Islands. Ecol. Monogr. 30(1):65-127.
KEMPF, M. 1970. Nota Preliminar Sobre os Fundos Costeños da Regiäo de Itamaracá (Norte do Estado de Pernambuco, Brasil). Trab. Oceanogr. Univ. PE (9):95-110.
LABORATORIO DE METEOROLOGIA DE PERNAMBUCO - LAMEPE. http://www.itep.br/LAMEPE. (último acesso em 20/06/2011).
LASIAK, T.A. 1984a. Structural aspects of the surf-zone fish assemblage at King's beach Algoa Bay, South .Africa: long-term fluctuations. Estuar. Coast. Shelf Sei. 18:459-483.
LASIAK, T.A. 1984b. Structural aspects of the surf zone fish assemblage at King's Beach, Algoa Bay, South .Africa: Short - term fluctuations. Estuar. Coast. Shelf Sei. 18(4):347-360.
LIRA, A.K.F. & TEIXEIRA, S.F. 2008. Ictiofauna da Praia de Jaguaribe, Itamaracá, Pernambuco. Iheringia, Zool. 98(4):785-780.
LOPES, P.R.D. 1999. Nota sobre a alimentaçâo dsAlbula vulpes (Linnaeus, 1758) (Actinopterygii: Albulidae) na Praia de Jaguaribe (Ilha de Itamaracá), Pernambuco. Stientibus 20:15-22.
MARCENIUK, A.P 2005. Chave para identificaçâo das espécies de bagres marinhos (Siluriformes, ariidae) da costa brasileña. Bol. Inst. Pesca. 31(2):89-101.
MEDEIROS, C. & KJERFVE, B. 1993. Hydrology of a tropical estuarine system: Itamaracá, Brazil. Estuar. Coast. Shelf Sei.36:495-515. http:// dx.doi.org/10.1006/ecss. 1993.1030
MENDONÇA, P. & ARAUJO, F.G. 2002. Composiçâo das populaçôes de linguados (Osteichthyes, Pleuronectiformes) da Baía de Sepetiba, Rio de Janeiro, Brasil. Rev. Bras. Zool. 19(2):339-347.
MENEZES, N.A. & FIGUEIREDO, J.L. 1980. Manual de Peixes Marinhos do Sudeste do Brasil. IV. Teleostei (3). Museu de Zoología, Universidade de Säo Paulo, Säo Paulo.
MENEZES, N.A. & FIGUEIREDO, J.L. 1985. Manual de Peixes Marinhos do Sudeste do Brasil. IV. Teleostei (4). Museu de Zoología, Universidade de Säo Paulo, Säo Paulo.
MICHELE, O.D. A& UIEDA, V.S. 2007. Diet of the ichthyofauna associated with marginal vegetation of a mangrove forest in southeastern Brazil. Iheringia, Zool. 9(4):486-497.
MONTEIRO-NETO, C., TUBINO, R.A., MORAES, L.E.S., NETO, J.P.M., ESTEVES, G.V. & FORTES, W. L. 2008. Associaçôes de peixes na regiäo costeirade Itaipu, Niterói, RJ. Iheringia, Zool. 98(l):50-59. http://dx.doi. org/10.1590/S0073-47212008000100007
MORAES, L.E., ROMERO, R.M., ROCHA, G.R.A.& MOURA, R.L. 2009. Ictiofauna demersal da plataforma continental interna ao largo de Ilhéus, Bahia, Brasil. Biota neotrop. 9(4): http://www.biotaneotropica. org.br/v9n4/pt/abstract?inventory+bn01409042009 (último acesso em 31/08/2012)
MOYLE, PB. & CECH, J.J. 2000. Fishes: an Introduction to Ichthyology. 4th ed. Upper Saddle River, Prentice Hall.
NELSON, J.S. 2006. Fishes of the World. 4th ed. John Wiley & Sons Inc., New York.
OLIVEIRA-NETO, J.F., SPACH, H.L., SCHWARZ-JR, R. & PICHLER, H. A. 2008. Diel variation in fish assemblages in tidal creeks in southern Brazil. Braz. J. Biol. 68(l):37-43.
ORDOÑEZ-LÓPEZ, U. & GARCÍA-HERNÁNDEZ, V.D. 2005. Ictiofauna juvenil associada a Thalassia testudinum en Laguna Yalahau, Quintana Roo. Hidrobiológica 15(2): 195-204.
PAIVA, A.C.G. & ARAÚJO, M.E. 2010. Environmental characterization and spatial distribution of fish fauna in estuaries in the state of Pernambuco, Brazil. Trop. Oceanogr. 38(1): 1-46.
PAIVA-FILHO, A.M., ZANI-TEIXEIRA, M.L. & KIHARA, PK. 1986. Contribuiçâo ao conhecimento da biología da manjuba, Anchoviella lepidentostole (Fowler, 1911), no estuário de Säo Vicente, SP (Osteichthyes, Engraulidae). Bol. Inst. Oceanogr. 34(único):71-77.
PAIVA-FILHO, A.M. & GIANNINI, F.B.R. 1990. A pesca da manjuba Anchoviella lepidentostole (Engraulidae) no estuário de Säo Vicente, SP. Rel. Int. Inst. Oceanogr. 29(1): 1-6.
PARRISH, J.D. 1989. Fish communities of interacting shallow water habitats in tropical oceanic regions. Mar. Ecol., Prog. Ser. 58: 143-160.
PEREIRA, P.H.C., FERREIRA, B.P & REZENDE, S.M. 2010. Community structure of the ichthyofauna associated with seagrass beds (Halodule wrightii) in Formoso River estuaiy - Pernambuco, Brazil. An. Acad. Bras. Ciênc. 82(3):617-628
PESSANHA, A.L.M. & ARAÚJO, F.G. 2003. Spatial, temporal and diel variations offish assemblages at two sandy beaches in the Sepetiba Bay, Rio de Janeiro, Brazil. Estuar. Coast. Shelf Sei. 57:1-12. http://dx.doi. org/10.1016/S 0272-7714(02)00411 -0
PRADO, P. & HECK JUNIOR, K.L. 2011. Seagrass selection by omnivorous and herbivorous consumers: determining factors. Mar. Ecol., Prog. Ser. 429:45-55. http://dx.doi.org/10.3354/meps09076
PRIMER-E. 2000. Plymouth Routines in Multivariate Ecological Research. Plymouth: Plymouth Marine Laboratory.
RABALAIS, N.N., TURNER, R., DÍAZ, R.J. & JUSTIC, D. 2009. Global change and eutrophication of coastal waters. ICES J. Mar. Sei. 66:1528- 1537. http://dx.doi.org/10.1093/icesjms/fsp047
RANDALL, J.E. 1967. Food habits of reef fishes of the West Indies. Stud. Trop. Oceanogr. 5:665-847.
RANDALL, J.E. 1990. Scaridae. In Check-list of the fishes of the eastern tropical Atlantic (CLOFETA) (J.C. Quero, J.C. Hureau, C. Karrer, A. Post & L. Saldanha, eds.). JNICT, Lisbon; SEI, Paris; UNESCO, Paris, v.2, p.883-887.
ROBERTSON, A.L & LENANTON, R.C.J. 1984. Fish community structure and food chain dynamics in the surf-zone of sandy beaches: the role of detached macrophyte detritus. J. Exp. Mar. Biol. Ecol.84:265-283. http:// dx.doi. org/10.1016/0022-0981(84)90185-0
RÖMER, G.S. 1990. Surf zone fish community and species response to wave energy gradient. J. Fish Biol. 36:279-287. http://dx.doi. org/10.1111/j. 1095-8649.1990.tb05609.x
SANTANA, F.M.S. & SEVERI, W. 2009. Composiçao e estrutura da assembléia de peixes da zona de arrebentaçao da praia de Jaguaribe, Itamaracá - Pernambuco. Bioikos 23(1):3-17.
SANTANA, F.M., SILVA-FALCÄO, E.C. & SEVERI, W. 2009. Ocorrência de Chirocentrodon bleekerianus (Teleostei; Pristigasteridae) na costa do estado de Pernambuco - Brasil. Rev. Bras. Eng. Pesca 4(1): 144-154.
SCHIFINO, L.C., FIALHO, C.B. & VERANI, J.R. 2004. Fish community composition, seasonality and abundance in Fortaleza Lagoon, Cidreira. Braz. .Arch. Biol. Technol. 47(5):755-763.
SCHLACHER, T.A, SCHOEMAN, D.S, DUGAN, J., LASTRA, M., JONES, A., SCAPINI, F. & McLACHLAN, A. 2008. Sandy beach ecosystems: key features, sampling issues, management challenges and climate change impacts. Mar. Ecol. 29(l):70-90. http://dx.doi.org/10.1111/j. 1439- 0485.2007.00204.x
SOUZA, L.M. & CHAVES, PT. 2007. Atividade reprodutiva de peixes (Teleostei) e o defeso da pesca de arrasto no litoral norte de Santa Catarina, Brasil. Rev. Bras. Zool.24(4):1113-1121.
STATSOFT. 2008. S TATI STIC A (data analysis software system), version 7.0. www.statsoft.com. StatSoft Inc., Tulsa.
TEIXEIRA, R.L. & ALMEIDA, G.I. 1998. Composiçao da ictiofauna de très praias arenosas de Maceió-AL, Brasil. Bol. Mus. Biol. Mello Leitao 8:21-38.
VASCONCELOS FILHO, A.L. & OLIVEIRA, A.M.E. 1999. Composiçao e ecologia da ictiofauna do canal de Santa Cruz (Itamaracá - PE, Brasil). Trab. Oceanogr. Univ. PE27(1): 101-113.
VAZZOLER, A.E.M., SOARES, L.S.H. & CUNNINGHAM, PM. 1999. Ictiofauna da Costa brasileira. In Estudos ecológicos de comunidades de peixes tropicais (R.C. Lowe McConnell, ed.). Editora da Universidade de Sao Paulo, Sao Paulo, p. 424-467.
VELOSO, V.G. & NEVES, G. 2009. Praias arenosas. In Biologia Marinha (R.C. Pereira & A. Soares-Gomes, eds.). Interciência, Rio de Janeiro, p.339-360.
VI ANN A, M, COSTA, F.E.S & FERREIRA, C.N. 2004. Length-weight relationship of fish caught as by-catch by shrimp fishery in the southeastern coast of Brazil. Bol. Inst. Pesca 30(l):81-85.
WHITFIELD, A.K. 1996. A review of estuarine ichthyology in South .Africa over the past 50 years. Trans. R. Soc. S.Afr. 51:79-89. http://dx.doi. org/10.1080/00359199609520601
WILBER, D.H., CLARK, D.G., BURLOS, M.H., RUBEN, H. & WILL, R.J. 2003.Spatial and temporal variability in surf zone fish assemblages on the coast of northern New Jersey. Estuar. Coast. Shelf Sei. 56:291-304. http://dx.doi.org/10.1016/S0272-7714(02)00163-4
Fábio Magno da Silva Santana14-5, William Severi2, Caroline I ieira Feitosa3 & Maria Elisabeth de Araujo1
3Gñipo de Ictiología Marinha Tropical - IMAT, Departamento de Oceanografía,
Universidade Federal de Pernambuco - UFPE, Av. Prof. Alomes Regó, 1235, Cidade Universitária,
CEP 50670-901, Recife, PE, Brazil, http://www.ufpe.br/docean
2Laboratório de Ictiología, Departamento de Pesca e Aquicultura,
Universidade Federal Rural de Pernambuco - UFRPE, Rua Dorn Klanoel de Medeiros, s/n, Dois Itmäos,
CEP 52171-900, Recife, PE, Brazil, http://www.depaq.ufipe.br
3Instituto de Ciencias do Alar, Universidade Federal do Ceará - UFC,
Av. da Aboliçào, 3207, Meireles, CEP 60165-081, Fortaleza, CE, Brazil.
http://www.labomar.ufc.br - Grupo de Ictiología Marinha Tropical - IMAT
4Unidade Académica Especializada em Ciéncias Agrárias, Escola Agrícola de Jundiaí,
Universidade Federal do Rio Grande do Norte- UFRN, Rod. RN 160, Km 03, Distrito de Jundiaí,
CEP 59280-000, Macaíba, RN, Brazil, http://www.eaj.ufrn.br/site/
sCotresponding author: Fábio Magno da Silva Santana, e-mail: email@example.com