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Breeding period in the mangrove crab Goniopsis cruentata (decapoda: grapsidae) in Northeast Brazil.

Reproduction is one of the most studied topics on life history of an organism (Stearns 1976, Stearns 2000). It is distinguished in two extreme strategies, semelparity and iteroparity (Cole 1954, Gadgil & Bossert 1970, Stearns 1976, Bryant & Hartnoll 1995). Among iteroparous organisms, the reproduction may be subdivided in two categories: 1) reproduction restricted to specific(s) period(s) of the year, known as seasonal iteroparity or seasonal reproduction or 2) continuous reproduction throughout the year, known as continuous iteroparity (Bell 1976, Sastry 1983, Pinheiro & Fransozo 2002, Negreiros-Fransozo et al. 2002, Litulo 2005). These iteroparity categories evolve in response to the survival of the offspring (Bell 1976). Therefore, seasonal iteroparity may emerge when the offspring experienced higher survival rates only in one, or more, periods of year, whereas continuous iteroparity is the strategy expected to occur when the offspring presents high rates of survival during the entire year.

Brachyuran crabs are iteroparous species which present a high diversification of reproduction patterns (Hartnoll & Gould 1988), which may have evolved as a species-specific response to environmental conditions. Some of them, such as photoperiod, rainfall, lunar cycle, temperature, and food supply have proved to be strongly related to the reproductive period (Sastry 1983, Adiyodi 1988, Litulo 2005, Skov et al. 2005, Castiglioni & Negreiros-Fransozo 2006). These factors (also known as extrinsic factors) act as signals of suitable and unsuitable periods for reproduction, whereas the physiological aspects (the intrinsic factors) are the interface between the organism and its environment (Zera & Harshman 2001, Ricklefs & Wikelski 2002). Both extrinsic and intrinsic factors trigger the ecdysis, mating and gonadal development (Sastry 1983) in order to overlap periods of high habitat quality for larval development (Boolootian et al. 1959, Sastry 1983, Cobo 2002a, Cobo 2002b).

Some authors have stated that the reproductive periodicity in Goniopsis cruentata (Latreille, 1803) (Grapsidae) follows a continuous pattern in subtropical mangroves (Silva & Oshiro 2002, Cobo & Fransozo 2003), region that present a well-known seasonal variation in environmental conditions. In these studies, however, ovigerous females did not occur in every month of collection effort. Therefore, reproduction is not completely aseasonal.

Mangroves are characterized by high salinity variation. This variation is due to tidal fluctuations (Hogarth 2007) and rainfall variations, both causing changes in salinity. Even though its effects are less pronounced in a latitudinal gradient than others, such as those from temperature and photoperiod (Sastry 1983), salinity is an important factor regulating biological activity in estuarine areas (Alvarez & Ewald 1990).

The aim of the present study is to evaluate the breeding period of the crab Goniopsis cruentata in Northeastern Brazil and also the influence of water salinity, pluviosity and air and water temperature on it.

MATERIAL AND METHODS

Study site and species: The study was performed in the Mundau/Manguaba Esturine Complex (Fig. 1), City of Maceio, State of Alagoas, Brazil (35[degrees]42'30" - 35 [degrees]57'00"W and 9[degrees]35'00" - 9 [degrees]45'00"S) (Calado & Sousa 2003). The climate is tropical, with an annual mean temperature of 25[degrees]C from 2000 to 2006, and an annual mean rainfall of 1 504 [mm.sup.3] from 1998 to 2008. These data were provided by the Secretaria de Estado do Meio ambiente e dos Recursos hidricos-SEMARHN, state of Alagoas, Brazil. The area presents two well-defined seasons, the rainy season, from March to August, and the dry season, from September to February (Eskinazi-Leca 1976, Calado & Sousa 2003, Araujo & Calado 2008). From 1965, the lowest values of salinities always occur during the rainy period with values as lower as 2. In the canals, salinities are often around 28, and near the outfall closely to 37 (Calado & Sousa 2003). Marques (2001) designated the area as an eco-complex for the presence of estuaries, lagoons, mangroves, rivers, tropical forests, dunes, and sandbars. The species Goniopsis cruentata is a mangrove crab typically found wandering on the substratum above the tide level, in burrows of other crabs crevices and climbing in mangrove trees, practically occupying every microhabitat in the mangrove ecosystem (Cobo & Fransozo 2003). According to Melo (1996), the distribution of G. cruentata ranges from Bermudas to Brazil (Western Atlantic), and from Senegal to Angola (Eastern Atlantic), also occurring in the Panama Pacific coast (Abele & Kim 1989).

Field procedures: Samplings were monthly accomplished from August-2007 to July-2008 in four areas (Fig. 1), to maximize the number of collected individuals, by three collectors during 50 minutes in each region. These regions were chosen taking into account the accessibility and the abundance of the species. For the statistical analysis, however, the data were grouped, since there was no difference among the sampling stations according to previous statistical tests. Therefore, the collected crabs were considered as a unique population. The crabs were manually captured during full moon diurnal tides, starting during the ebb and finishing at the flood tide. Air and water temperature were measured with a toluene thermometer. Samples of water from the lagoons were obtained at the margin of the mangrove of each station, for salinity measurement. These procedures were accomplished before crab catching effort. In April-2008 there was no collection for reasons beyond control. The rainfall data to the studied period were provided by the SEMARHN.

Laboratory procedures: The salinity measurement was done in the hydrochemistry laboratory of the Federal University of Alagoas, Brazil. The captured crabs were sexed by abdomen morphology, being triangular shaped in the males and round shaped in the females. The female crabs had their carapace width measured by a Vernier calliper (precision of 0.05mm) and the egg-bearing condition was recorded to assess the breeding period of the species, following the classification proposed by Pinheiro & Fransozo (2002). The egg stage of development was established as a way to infer the optimal time for spawning. Hence, the embryonic development was determined in two stages, according to Okamori & Cobo (2003): (1) initial stage, when there was no sign of cleavage or cellular differentiation, and egg totally filled with yolk; (2) final stage, when the embryo is fully differentiated, with clear segmentation of limbs and well-developed eyes. The breeding period was assessed by the monthly proportion of ovigerous females in relation to total females. To test the association between the monthly proportions of ovigerous females in relation to the total females with the rainfall, and the mean values of water salinity and air and water temperature, multiple regression analysis were performed. This proportion was arc-sin transformed to meet the assumptions of Zar (1999). The rainy and dry periods were defined a priori, based on Eskinazi-Leca (1976). Among rainy and dry periods (as defined a priori), the absolute frequency of ovigerous was compared by applying a chi-square test ([chi square]). Salinity, rainfall and air and water temperature were compared among these two periods by a Kruskall-Wallis ANOVA. Each statistical test was performed using the program Statistica 7.0, with a significance level of 5%. The tests were applied after normality analysis of the data.

RESULTS

A total of 554 females were captured, being 71 ovigerous females. The ranged from 22.45 to 42.45, with a mean size of 31.85 [+ or -] 4.80. The number of the total females and the percentage of the ovigerous females in each month are shown in the table 1. The ovigerous females were recorded almost all over the year, with higher proportions from December-2007 to March-2008 and they were not found in August and October-2007 and May-2008 (Fig. 1). From the 71 egg-bearer females collected, 76% were incubating eggs in initial stage and 24% in final stage of development, the majority of the latter occurring from November to December-2007.

The salinity ranged from 0.53 to 27.75, with a mean of 17.40 [+ or -] 8.5. The lower water temperature was 19.88[degrees]C, the highest 29.13 [degrees]C, with mean of 26.19 [+ or -] 2.91. The temperature ranged from 19.5[degrees]C to 30.63 [degrees]C, with a mean of 26.45 [+ or -] 3.23. The monthly rainfall varied from 5.4 to 569 [mm.sup.3], with mean of 173.89 [+ or -] 184.97. No association between the monthly proportion of ovigerous females and the analyzed environmental parameters was observed ([F.sub.46]=0.67, p>0.05) (Fig. 1). A higher frequency of ovigerous females was found during the dry period (from September to February) ([chi square]=4.2, d.f=1, p=0.04), in which were observed higher salinity ([H.sub.1,11]=4.80, p=0.029), water ([H.sub.1,11]=4.03, p=0.044) and air temperatures ([H.sub.1,11]=4.03, p=0.044) and lower rainfall ([H.sub.1,11]=7.5, p=0.006). Salinity and rainfall presented significant oscillations during the sampling period, as it can be seen in figure 2A and B, while temperature was stable (Fig. 2C).

DISCUSSION

The ovigerous females of G. cruentata occurred throughout the year with a peak in the dry period. Therefore, the present population followed a seasonal-continuous breeding, according to the classification of Pinheiro & Fransozo (2002). A continuous breeding season guarantees a year-round larvae supply, ensuring a continuous recruitment pattern to the population (Diaz & Conde 1989, Negreiros-Fransozo et al. 2002, Litulo et al. 2005). Additionally, prolonged reproduction indicates that individuals produce several broods during the breeding period or breed asynchronously (Litulo et al. 2005) and that the species presents high genetic tolerance to environmental conditions (Cobo 2002a).

The continuous breeding period of the present population is similar to others of the same species, in low (Moura et al. 2000) and high latitudes (Silva & Oshiro 2002; Cobo & Fransozo 2003), even though the reproductive period can vary along a latitudinal gradient (Sastry 1983, Jones & Simons 1983, Diaz & Conde 1989, Emmerson 1994, Bryant & Hartnoll 1995, Lardies et al. 2004, Cobo 2002a, Cobo 2002b, Castiglioni et al. 2007). Factors that are independent of latitude, such as intertidal zonation, can lead to this non-variance of the breeding period. Species that live upper on the shore tend to breed in restricted periods and species living lower on the shore, such as G. cruentata, may present extended breeding activity (Boolootian et al. 1959, Pillay & Ono 1978, Sastry 1983, Emmerson 1994, Morgan & Christy 1995, Yamaguchi 2001).

The low frequency of egg-bearer females throughout the study period was also observed to this species (Silva & Oshiro 2002, Cobo & Fransozo 2003), and is not an uncommon result among brachyuran crabs (Seiple & Salmon 1987, Mantelatto & Fransozo 1997, Negreiros-Fransozo et al. 2002, Pinheiro & Fransozo 2002, Mantelatto et al. 2003, Lima et al. 2006, Castiglioni et al. 2007, Cesar et al. 2007), what can be due to a cryptic habit of these crabs in relation to the non-ovigerous females. Additional catch effort is totally not recommended since it will cause bias in the determination of the period of breeding activity. Therein, even though one can think that there is a lack of data, it must be the biological pattern of a species, but still offering valuable data for the understanding of the reproduction of the species.

The monthly proportion of ovigerous females was not correlated to any of the analyzed environmental parameters. However, other authors have observed a correlation between the abiotic factors and the abundance of ovigerous females, as Cobo & Fransozo (2003) for G. cruentata and Castiglioni et al. (2011) for Sesarma rectum Randall, 1840. This difference probably occurs due to the more stable environment conditions in the present area, which may mask their influence on the biological activities in the populations located at lower latitudes.

The higher frequency of ovigerous females observed in the dry period suggests that higher salinity and air and water temperatures, and lower rainfall may promote an intensification of the breeding activity. In fact, there is some empirical evidence that higher salinities favor a shorter period of larval development and improve the larvae survival in the initial stages of development (Saigusa 1981, Alvarez & Ewald 1990, Anger et al. 1990, Steele & Steele 1991, Anger et al. 1998, Bas & Spivak 2000, Gelin et al. 2001, Paula et al. 2001, Spivak & Cuesta 2009). Therefore, offspring released in the dry period may experience higher survival rates than that released in the rainy period. Water temperature, higher in the dry period, may also provide a shorter larval development (Emmerson 1994, Paula et al. 2001, Christy 2003). Hence, breeding in periods of both higher salinities and water temperatures may represent a predation avoidance tactic, since larvae is too vulnerable to predation (Emmerson 1994). On the other hand, the sudden elevation of rainfall and a small decrease of the temperature between February and March may have compelled to come back to the ordinary production of eggs after two months, in May (or after one month, in April when no collection was done).

In the case of terrestrial and semi-terrestrial crabs, air temperature is of greater importance than water temperature to the adult life. It acts as a trigger to the gonad development (Wear 1974, Sastry 1983, Zimmerman & Felder 1991, Lardies et al. 2004), and crabs exposed to low temperatures present a longer embryogenesis, leading to a longer incubation period (Wear 1974, Yamaguchi 2001). A faster gonad development, which may occur in tropical areas due to higher temperatures, enables the crab hatches more than one batch of eggs in the optimal time for egg release, maximizing its reproductive effort (Jones & Simons 1983, Ituarte et al. 2004). This fact may represent a selective advantage to breed in the dry period.

The breeding period clearly occurs when rainfall was lower, i.e. in the dry period, even though not correlated to the monthly values of rainfall. This data did not corroborate with that of Cobo & Fransozo (2003) to the same species, in a higher latitude tropical area, when highest proportion of ovigerous females occurred in periods of higher rainfall. In fact, breeding is commonly assumed to be positively correlated with the rainfall (Litulo 2004, Litulo 2005, Liu & Jeng 2005), when the channels in the estuary are deeper and the larvae reach the sea more easily to complete its development (Saigusa 1981), being less susceptible to predation (Morgan & Christy 1995). The rainfall increases the flux of river water, enlarging the lading of nutrients to the estuary, favoring the productivity of the phytoplankton (Mallin et al. 1993) and, hence, the larval development.

Although not measured in the present study, the major food availability (phytoplankton) to the larvae in the summer (dry period the present area), may also favors breeding activity (Boolootian et al. 1959, Sastry 1983, Emmerson 1994, Castiglioni et al. 2007). This higher nutrition source is due to the higher photoperiod in this season (Cobo & Fransozo 2003, Litulo et al. 2005), which favors phytoplankton productivity. Sunlight is, in fact, a limiting factor to phytoplankton production. However, in the Northeastern Brazil, the photoperiod does not present significant differences among stations of the year (Passavante & Feitosa 2004). The phytoplankton production is mainly affected by the suspended material on the surface water, higher on the rainy period. It leads to a decrease in the photic layer and, consequently, in the phytoplankton production (Resurreicao et al. 1996).

The fourteen ovigerous females incubating eggs in final stage of development in November and December, within the dry period, can indicate that it is, in fact, the most suitable period for larval release. A low occurrence of ovigerous females was observed in the rainy period, indicating that this period, on the other hand, is not so favorable for larval survival. In fact, breeding all over the year may be a strategy to guarantee reproduction during non-favorable environmental conditions (Litulo 2005), what can be considered as a risk-spreading strategy (Stearns 1976). In general, is assumed that the breeding season is timed to reach the best conditions for larval survival and recruitment (Pillay & Ono 1978, Diaz & Conde 1989, Cobo 2002a, Cobo 2002b).

Bas & Spivak (2000), studying species of Grapsids from Argentina, cited that the salinity tolerance of the embryos can vary in different broods of females of the same species. Thus, each female can incubate their eggs in a different occasion, probably in periods similar to that in which their parental female released them. The larvae tolerance to salinity depends on the previous history experienced by the parental female (Bas & Spivak 2000), and that fact may explain the continuous breeding activity of G. cruentata.

We conclude that the breeding period of G. cruentata is seasonal-continuous, being not regulated by temporal fluctuations of air and water temperature, salinity and rainfall. However, the dry period provide the best conditions to breeding activity of this species (higher air and water temperature, higher salinity and lower rainfall). Future researches may focus on the response of physiological characteristics, gametogenesis, incubation period, and on the larval ecology and recruitment pattern to environmental variations for a completely understand of breeding activity.

ACKNOWLEDGMENT

The authors are thankful to Paulo Cardoso and Cristiane Farrapeira, for their suggestions to this manuscript. The first author is grateful to the Conselho Nacional de Desenvolvimento Cientifico e Tecnologico-CNPq, for the fellowship granted (process number 112334/2007-5).

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Jose Jonathas Pereira Rodrigues de Lira (1), Tereza Cristina dos Santos Calado (2) & Marina de Sa Leitao Camara de Araujo (3)

(1.) Universidade Federal do Ceara (UFC), Departamento de Biologia, Laboratorio de Histologia e Reproducao Animal, Av. Humberto Monte, s/n, Campus do Pici, Pici, CEP 60455-900-Fortaleza, Ceara, Brazil; jose.jonathas@hotmail.com

(2.) Universidade Federal de Alagoas (UFAL), Laboratorios Integrados de Ciencias do Mar e Naturais (LABMAR), Av. Aristeu de Andrade, 452, Farol, CEP 57051-090-Maceio, Alagoas, Brazil; terezacalado@hotmail.com

(3.) Universidade Federal de Pernambuco (UFPE), Departamento de Oceanografia (DOCEAN), Laboratorio de Carcinologia (Labcarci), Av. Arquitetura, s/n, Cidade Universitaria, CEP 50670-901-Recife, Pernambuco, Brazil; mslc.araujo@gmail.com

Received 01-III-2012.

Corrected 03-VII-2012.

Accepted 09-VIII-2012.

TABLE 1

Monthly changes in the total number of females
and egg bearer females of Goniopsis cruentata in
the the Mundau/Manguaba Estuarine Lagunar Complex,
Maceio, Alagoas, Brazil

Year   Month    Total      Total     Egg-bearer
               females   ovigerous   females (%)
                          females

2007    Aug      65          0            0
        Sep      55          9          16.36
        Oct      61          0            0
        Nov      60          5          8.33
        Dec      49         14          28.57
2008    Jan      53         18          33.96
        Feb      53         10          18.86
        Mar      59         11          18.64
        May      37          0            0
        Jun      39          1          2.56
        Jul      23          3          13.04
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Title Annotation:articulo en ingles
Author:Pereira Rodrigues de Lira, Jose Jonathas; dos Santos Calado, Tereza Cristina; de Sa Leitao Camara de
Publication:Revista de Biologia Tropical
Date:Mar 1, 2013
Words:4721
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