SciELO - Scientific Electronic Library Online

 
vol.42 issue2Environmental factors influencing the distribution of three species within the genus Persephona Leach, 1817 (Crustacea, Decapoda, Leucosiidae) in two regions on the northern coast of São Paulo State, BrazilProximate composition of marine invertebrates from tropical coastal waters, with emphasis on the relationship between nitrogen and protein contents author indexsubject indexarticles search
Home Pagealphabetic serial listing  

Services on Demand

Journal

Article

Indicators

Related links

  • On index processCited by Google
  • Have no similar articlesSimilars in SciELO
  • On index processSimilars in Google

Share


Latin american journal of aquatic research

On-line version ISSN 0718-560X

Lat. Am. J. Aquat. Res. vol.42 no.2 Valparaíso May 2014

 

Research Article

 

How marine upwelling influences the distribution of Artemesia longinaris (Decapoda: Penaeoidea)?

¿Cómo influye la surgencia marina en la distribución de Artemesia longinaris (Decapoda: Penaeoidea)?

 

Gustavo S. Sancinetti1, Alexandre Azevedo2, Antônio L. Castilho1 Adilson Fransozo1 & Rogério C. Costa3

1 Núcleo de Estudos em Biologia, Ecologia e Cultivo de Crustáceos (NEBECC) Departamento de Zoologia, Instituto de Biociências, Universidade Estatal Paulista CEP 18618-000, Botucatu, São Paulo, Brazil
2
Universidade Federal do Rio de Janeiro (NUPEM), CEP 27971-550, Macaé, RJ, Brazil
3
Laboratório de Biologia de Camarões Marinhos e de Água Doce (LABCAM) Departamento de Ciências Biológicas, Faculdade de Ciências, Universidade Estatal Paulista
CEP 17033-360 Bauru, São Paulo, Brazil
Corresponding author: Gustavo S. Sancinetti (sancinetti@ibb.unesp.br)


ABSTRACT. Upwelling events can occur in most of the oceans altering the water physical, chemical and sediment conditions and consequently the species communities dwelling the areas. For better understanding the behavior of populations inhabiting upwelling regions, the spatial and temporal distribution of a Penaeoidea shrimp was studied correlating it with the abiotic factors that vary during upwelling and non-upwelling periods in an area under influence of Cabo Frio upwelling. Bottom salinity and temperature, organic matter and sediment type from each station were sampled from March 2008 to February 2010, in six stations located between 5 and 45 m depth. The lowest temperatures were recorded during spring and summer for both years with temperature values lower than 19oC. A total of 26,466 Artemesia longinaris shrimps were captured mainly in 10-35 m depth. Upwelling periods showed significant differences in abundance in relation to non-upwelling periods. The spatial distribution among stations varied according to the temperature with higher abundance in stations with values between 19 and 21oC. The highest abundance of A. longinaris was recorded in spring and summer when intrusions of the cold waters of South Atlantic Central Waters (SACW) were frequent. Thus, the effect of cold water of SACW boosted by the upwelling was a determinant factor in the spatial and temporal distribution of A. longinaris in the studied region.

Keywords: Artemesia longinaris, Penaeoidea, distribution, environmental factors, SACW, Brazil, South Atlantic Ocean.


RESUMEN. Los eventos de surgencia pueden ocurrir en la mayoría de los océanos alterando las condiciones físicas y químicas del agua y del sedimento, y por consiguiente a las comunidades de especies que viven en la zona. Para una mejor comprensión del comportamiento de las poblaciones que habitan en las regiones de surgencia, se estudió la distribución espacial y temporal de un camarón peneido y se correlacionó con los factores abióticos que varían durante los períodos de surgencia y sin surgencia, en una zona bajo la influencia de la surgencia de Cabo Frío. La salinidad y temperatura del fondo, materia orgánica y el tipo de sedimento de cada estación fueron muestreados entre marzo 2008 y febrero 2010, en seis estaciones ubicadas entre 5 y 45 m de profundidad. Las temperaturas más bajas se registraron durante primavera y verano para ambos años, cuando los valores de temperatura fueron inferiores a 19°C. Un total de 26.466 camarones de Artemesia longinaris se capturó principalmente entre 10 y 35 m. Los períodos de surgencia mostraron diferencias significativas en la abundancia en relación con los períodos sin surgencia. La distribución espacial entre estaciones varió según la temperatura con las mayores abundancias en las estaciones con valores entre 19 y 21°C. La mayor abundancia de A. longinaris se registró en primavera y verano, cuando las intrusiones de las frías aguas del Agua Central del Atlántico Sur (SACW) fueron frecuentes. Por lo tanto, el efecto del agua fría del SACW impulsada por la surgencia fue un factor determinante en la distribución espacial y temporal de A. longinaris en la región estudiada.

Palabras clave: Artemesia longinaris, Penaeoidea, distribución, factores ambientales, SACW, Brasil, Océano Atlántico Sur.


 

INTRODUCTION

The tropical continental shelf ecosystem is little known due to its great extension and there is scarce information about the distributional models of organisms and the factors influencing this distribution. A vast variety of environmental processes (luminous intensity, salinity, temperature, oxygen concentration, and others) contributes to the marine communities pattern of response to the environment that they dwell (Bertness et al., 2001). Therefore, the study of the interaction of these factors with the populations leads to a greater understanding about the dynamic of marine communities.

Thus, benthic ecosystems are influenced by complex interactions among oceanographic process, organic input and its use by populations, and hydrological and sediment conditions (Barry & Dayton, 1991), which may influence juveniles recruitment, growth, survival, and fecundity of benthic species (Peterson, 1979; Ambrose, 1991). The spatial and temporal distribution of shrimps, as well as the onset at sexual maturity, growth, longevity, and spawning are affected by temperature, salinity, food availability, sediment structure and intrinsic factors (Bauer 1992; Castilho et al., 2007a, 2007b; Castro et al., 2005; Costa et al., 2005a, 2005b, 2007; Simões et al., 2010).

Artemesia longinaris Bate, 1888 is a species endemic to the western area of the South Atlantic occurring from Atafona (21oS) (Rio de Janeiro, Brazil), to the Province of Chubut (43oS) (Argentina) (Boschi, 1969a). This shrimp is commonly found in shallow waters up to 30 m of depth (Boschi, 1997; Costa et al., 2003). Boschi (1963, 1969a) stated that this species is typical of colder regions, occurring in a temperature range from 15 to 21oC and salinity above 33. The density of A. longinaris increases with latitude from the Rio de Janeiro coast to the South (Magalhães, 1944; Boschi, 1969b). This pattern has also been confirmed in other studies, given that the species is occasionally detected in minor amounts on the coast of Rio de Janeiro (Iwai, 1973) and São Paulo States (Mistakidis & Neiva, 1964; Iwai, 1973; Costa et al., 2005b). However, from the coast of Rio Grande do Sul State to Argentina (Boschi, 1969b; Nascimento, 1983), this species is caught all year long. It lives exclusively in the marine environment throughout its life cycle, without any period linked to continental brackish waters (Boschi, 1997; Branco, 2005; Costa et al., 2005b).

The southeast region of Brazil is influenced by the oceanic currents of Brazil (T > 20oC, S > 36) and Malvinas (T < 15oC, S < 34). Due to the confluence of both currents between latitudes 25°S and 45°S of the western South Atlantic observed in certain periods of the year, there is the formation of water masses like the South Atlantic Central Water (SACW; T < 20°C, S < 36.4), accounting for part of the convergence of the subtropical gyre and giving rise to the Cabo Frio upwelling, which extends between 23oS and 29oS (Castro-Filho et al., 1987; Campos et al., 1996, 2000; Silveira et al., 2000; Acha et al., 2004). This upwelling is enhanced by coastal winds and by the break in the continental shelf (approximately 50 km from the coast) driven by the meandering pattern and eddy of the Brazil Current (Castro & Miranda, 1998; Campos et al., 2000). The combination of these effects results in a strong mechanism capable of carrying cold and nitrate-rich SACW waters to the coast (Acha et al., 2004), altering the physical conditions and also enhancing water nutrient concentrations (Valentin, 1984). Consequently, the primary productivity of the Brazilian Southeast Bight increases, particularly in Cabo Frio, Rio de Janeiro (23°S) (De Léo & Pires-Vanin, 2006).

The upwelling in Cabo Frio area is an uncommon case. Most of the coastal upwelling regions in the world are located on the west coast of the oceans, like in Peru, Equator, California and Oregon (Pacific coast), and the Northeast of South Africa and Bengal in the Atlantic Ocean. On the other hand, Cabo Frio upwelling occurs on the west coast of the Atlantic Ocean, which is very important for biological enrichment and consequently for fishing activities in the area (Franchito et al., 2007). Generally, physical processes can affect the primary productivity in a time and space scales, causing variations in food availability affecting the growth and survival of organisms (Scheltema, 1986; Morgan et al., 2001).

The distinctive environmental characteristics, caused by the inflow of SACW, found in Cabo Frio region and adjacent areas may provide different results about spatial and temporal abundance of A. longinaris when compared to results from other localities, especially where its occurrence is seasonal such as in São Paulo State coast (Costa et al., 2005b; Castilho et al., 2008a).

Thus, the aim of this study was to analyze the spatial and temporal distribution of the shrimp Artemesia longinaris correlating abiotic factors that vary in periods with and without influence of Cabo Frio upwelling.

MATERIALS AND METHODS

Sampled shrimps

Shrimps were collected monthly from March 2008 to February 2010 (Autumn: March-May; and so on) at six stations located in the Inside Area (5, 10 and 15 m deep) and the Outside Area (25, 35 and 45 m deep), in Macaé northern coast of Rio de Janeiro State (22o22'33''S, 41o46'30''W) (Fig. 1). The inside area and outside area terms were used only to characterize less and larger depths of the stations, respectively. A shrimp fishing boat equipped with otter-trawl nets (3.5 m mouth width, mesh size 20 and 15 mm in the cod end) was used for trawling. The stations were trawled over a 15 min period at a constant speed of 2.1 knots through a 1 kilometer distance per trawl.

 

Figure 1. Study area evidencing the upwelling region and the sampling area. Location of stations (5-35 m of depth) and major ocean currents of the South Atlantic. AC: Antarctic Circumpolar Current, MC: Malvinas Current, SAC: South Atlantic Current, SEC: South Equatorial Current, BC: Brazilian Current (Modified from Peterson & Stramma, 1991).

Sampling and abiotic environmental data collection

Salinity and temperature (°C) were measured on surface and bottom-water samples, obtained monthly in each station using a Van Dorn bottle. In the laboratory, the salinity was verified with a manual salinometer calibrated with distilled water. The water temperature was verified with a mercury thermometer immediately after sampling in a thermic isolated container in the shade. An ecobathymeter coupled with a GPS (Global Positioning System) was used to record depth at sampling sites. Sediment samples were collected in each season with a 0.06 m2 Van Veen grab. Grain-size categories followed the American standard, and sample sediments were sieved at 2.0 mm (gravel), 1.0 mm (very coarse sand), 0.5 mm (coarse sand), 0.25 mm (intermediate sand), 0.125 mm (fine sand), 0.0625 mm (very fine sand) and smaller particles, which were classified as silt-clay. Grain-size fractions were expressed on the phi (Φ) scale, accounting for the central tendency of sediment samples. Procedures for sediment analysis followed Hákanson & Jansson (1983) and Tucker (1988).

The organic matter content (%) was obtained by ash weighing: three aliquots of 10 g each per station, placed in porcelain crucibles for 3 h at 500°C, and the samples were weighed one more time (see Mantelatto & Fransozo, 1999).

Data analysis

Water masses and periods under upwelling influence were identified through Temperature-Salinity diagram (T-S) and monthly difference between the highest surface temperature and the lowest bottom temperature.

Coastal Water (CW) shows high temperature and low salinity (T > 20°C, S < 36.4), Tropical Water (TW) shows both high temperature and salinity (T > 20°C, S > 36.4), and South Atlantic Central Water (SACW) shows both low temperature and salinity (T < 20°C, S < 36.4) (Mascarenhas et al, 1971; Campos et al., 1996; 2000; Castro-Filho & Miranda, 1998; Silveira et al, 2000).

The abundance of shrimps was compared among stations and between upwelling and non-upwelling periods using analysis of variance (TWO-WAY ANOVA), and the post-hoc Tukey's test was used to indicate the difference between stations. The differences of shrimp abundance in each class of environmental factor were tested by ANOVA and post-hoc Tukey's. Homoscedasticity and normality of the data set were evaluated and found satisfactory after data logarithmic transformation (Zar, 1999).

RESULTS

Environmental factors analysis

Three water masses were identified in the studied region, i.e., Coastal Water (CW), Tropical Water (TW) and South Atlantic Central Water (SACW). The influence of SACW was evident in spring-summer months in both years, and in autumn (March-April) of the second year (Figs. 2, 3).

 

Figure 2. T-S Diagram showing the seasonal variation of water temperature and salinity during the sampling period at upwelling area studied, southeastern coast of Brazil. CW: Coastal Water, TW: Tropical Water, SACW: South Atlantic Central Water. Autumn: March-May, winter: June-August, spring: September-November and summer: mean December-February.

 

Figure 3. Highest surface and lowest bottom temperatures, showing the upwelling periods (SACW) in the study area.

The environmental factors varied in spatial-temporal gradients. In bottom salinity, the smallest mean value was detected during March 2009, mainly in Inside Area (27.0 ± 1.00), when compared to Outside Area (31.7 ± 3.21). Contrarily, the greater values were verified in October 2009 (37.0 ± 1.00) in Inside Area, and April 2009 and Mach 2008 (37.7 ± 0.58 e 37.3 ± 0.58) in Outside Area (Fig. 4).

 

Figure 4. Mean, maximum and minimum salinity values for each month in "Inside area" and "Outside area", sampled from March 2008 to February 2010.

In both years, smaller mean values of bottom temperature were registered in spring and summer seasons, mainly in January 2010 and November 2009 in Inside and Outside Area, respectively. The opposite was observed in winter with greater mean bottom temperature values (Fig. 5).

 

Figure 5. Mean, maximum and minimum temperature (°C) values for each month in "Inside area" and "Outside area" sampled from March 2008 to February 2010.

The stations distributed in the Inside Area showed sediment composed mainly of medium and fine sand, and a low percentage of organic matter. In Outside Area the sediment was composed mainly of silt and clay and a greater content of organic matter (Fig. 6).

 

Figure 6. Mean values and standard deviation of phi and organic matter content, recorded in each station, sampled from March 2008 to February 2010.

Spatial-temporal distribution

A total of 26,366 A. longinaris specimens were captured in all stations sampled in Inside and Outside Area, with greater amount of shrimps between depths 10 to 35 m. The greatest captures occurred during summer months in both years (2,907 and 6,779, respectively). In spring of YEAR I (2008) the smallest captures (611) were obtained. Contrarily, the spring of YEAR II (2010) was the second season with the greatest number of shrimps (Table 1). The analysis of variance showed a significant difference only between stations (ANOVA, F = 10.32; P = 0.000) and between upwelling and non-upwelling periods (ANOVA, F = 6.85; P = 0.009).

Table 1. Number of individuals in each month and station sampled from March 2008 to February 2010, indicating the results of the Tukey test (*Results of the Tukey test. Different letters indicate statistical significant difference (P > 0.05)). Dashed boxes indicate upwelling periods.
 

For all environmental factors, ANOVA analysis indicated significant difference with abundance of individuals (Table 2). The greatest concentration of individuals in sites and/or months occurred in the temperature classes 19 and 21oC, salinity higher than 31, and granulometry composed of medium sand (1 phi 2). It can be noticed a lower abundance of A. longinaris in intermediate values (3 and 9%) of organic matter in the sediment, however it was not found a pattern for differences among classes. In this study water samples for salinity between 28.5 and 31 were not recorded (Fig. 7).

Table 2. Results of the analysis of variance (ANOVA) of the number of shrimp per trawl for each class of environmental variable. Different letters indicate statistical significant difference (P > 0.05).
 

 

Figure 7. Distribution of mean number of shrimp per trawl and standard deviation (SD) for each class of environmental variable, along with variance analysis results indicating results of Tukey test (P > 0.05). Different letters indicate statistical significant difference. (*) No samples were collected with this particular salinity value in this class.

DISCUSSION

The distribution of megabenthonic community in the study area is closely connected to seasonality of the thermic front of SACW and upwelling. The deepest area (100 m) is influenced by high sedimentation, while shallower regions are more influenced by cold water (De Léo & Pires-Vanin, 2006). According to Pires-Vanin et al. (2013) changes on water temperature and salinity affect the distribution pattern of the macrofauna of benthonic invertebrates. Additionally, Dall et al. (1990) and Costa & Fransozo (2003) affirm that the temperature is considered one of the main determinant parameters in the temporal distribution of organisms, mainly for penaeid shrimps.

Even though factors like migration, predation and food availability may influence the distribution and abundance of A. longinaris, the presence of the SACW, propelled by Cabo Frio upwelling, and could be a very strong modulating factor in the region, despite the influence of salinity and sediment composition. This is supported by the fact that the species shows evolutionary origin linked to cold waters of temperate regions.

In this study, salinity values higher than 31 positively influenced the increase of A. longinaris abundance. This pattern suggests that A. longinaris presents a life cycle of type III (proposed by Dall et al., 1990) in this studied region. Within this category, individuals complete their life cycle in coastal marine regions, where post-larvae settle in protected areas near the coast, which does not include estuaries or low salinity areas.

The organic matter did not influence the distribution of A. longinaris once it occurred in all value classes. For Penaeoidea, the grain particle size may be more important in shrimp distribution than the amount of organic matter available in the substrate (Ruello, 1973; Costa & Fransozo, 2004; Costa et al., 2004). This may be due to the fact that shrimp are generalist and they do not feed only on organic matter dissolved in the sediment.

Feeding diversification showed by Penaeoidea shrimps may explain the preference of A. longinaris for sediment composed by medium sand in which the content of organic matter is lower. Boschi (1969a, 1969b), Fransozo et al. (2004) and Costa et al. (2005b) observed preference for sediment composed of very fine sand. This preference for fine sediment is common in most of the peneid species like Penaeus esculentus Haswell, 1879, Metapenaeus endeavouri (Schmitt, 1926) (Gribble et al., 2007), Sicyonia dorsalis Kingsley, 1878 (Castilho et al., 2008b) and A. longinaris (Costa et al., 2005b). Very fine sand enables the shrimp's strategy of burying themselves to protect against predators and thus to decrease their energetic expenditure (Ameeri & Cruz, 1998; Simões et al., 2010).

The results obtained regarding sediment allow proposing that A. longinaris individuals do not totally bury themselves and their greater abundance in sediment with medium sand is due to the influence of environmental factors.

According to Fenucci (1988), Artemesia longinaris rests on the substrate and they do not bury themselves. Such information may be reinforced once A. longinaris are translucent when alive, evidencing in their body only brownish spots that resemble sand grains enabling them to be unnoticed by a potential predator.

The results found for organic matter content and sediment texture reinforce the greater effect of temperature in spatial distribution of A. longinaris. The variation of temperature made the individuals move to areas with less than 15 m of depth when the temperature was colder, however as the temperature increased, the individuals moved to deeper areas regardless the sediment type. Artemesia longinaris displaced specially between depths of 10 to 35 m, following the water temperature variation. In periods when the temperature decreased (<20°C) due to the SACW intrusion and the upwelling phenomena in the region (mainly in spring and summer), most of the individuals were collected in depths of less than 14 m. While in winter, when the retraction of the SACW happened and temperature values were higher than 22°C, individuals were collected in greater amounts in depths of more than 25 m.

The pronounced thermocline verified in the upwelling months, together with an abrupt drop of bottom temperature values (<20oC), triggered a substantial increase of A. longinaris during these periods. Similar results were obtained by Fransozo et al. (2004) and Costa et al. (2005b) on the North coast of São Paulo State. According to Costa et al. (2005a), the species is considered migratory following the cold water mass SACW.

According to the results obtained, the studied region refutes the theory that the abundance of A. longinaris increases towards higher latitude (Magalhães, 1944; Boschi, 1969b; Iwai, 1973). The favorable conditions, especially low temperatures, found in Cabo Frio/RJ region and adjacent areas provide the continuous establishment of A. longinaris, differing from seasonal captures described by Fransozo et al. (2004) and Costa et al. (2005b) in Ubatuba region (23oS), Sao Paulo State coast.

Stramma & England (1999) and Silveira et al. (2000) proposed a flow of ACAS from north to south in the Southwestern Atlantic Ocean. These authors stated that the Subtropical Gyre originates the SACW and part of it flows toward south along Brazilian coast from Cabo de São Tomé (22oS). This study propose the hypothesis that possibly there is an established population on the north coast of the State of Rio de Janeiro due to favorable conditions with low temperature, and this population migrates with the SACW to lower latitudes, and it may populate the coast of Sao Paulo State. Therefore, the species success in the studied region is related to local physical conditions responsible for creating an environmental scenario similar to the cold waters of a cold temperate region, such as the Argentine coast.

ACKNOWLEDGEMENTS

We are grateful to the "Fundação de Amparo à Pesquisa do Estado de São Paulo" (FAPESP) for providing financial support (N°09/54672-4 and 010/50188-8-RCC), Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) (Research Scholarships N°306304/2008-2 and 304784/2011-7 RCC), Fundação de Amparo à Pesquisa do Estado do Rio de Janeiro (FAPERJ) and to the Financiadora de Estudos e Projetos (FINEP/MCT). We also thank the co-workers (NuPEM and LABCAM) for their help with the field work, and Universidade Federal do Rio de Janeiro/NUPEM for the infrastructure to carry out this work. All experiments conducted in this study comply with current applicable state and federal laws (Authorization of the Instituto Chico Mendes de Biodiversidade/ICMBio number 11274).

 

REFERENCES

Acha, E.M., H.W. Mianzan, R.A. Guerrero, M. Favero & J. Bava. 2004. Marine fronts at the continental shelves of austral South America physical and ecological processes. J. Mar. Syst., 44: 83-105.         [ Links ]

Ameeri, A.A. & E.M. Cruz. 1998. Effect of sand substrate on growth and survival of Penaeus semisulcatus de Haan juveniles. J. Aquacult. Trop., 13(4): 239-244.         [ Links ]

Ambrose Jr., W.G. 1991. Are infaunal predators important in structuring marine soft-bottom communities? Am. Zool., 31: 849-860.         [ Links ]

Barry, J.P. & P.K. Dayton. 1991. Physical heterogeneity and the organization of marine communities. In: J. Kolasa & S.T.A. Pickett (eds.). Ecological heterogeneity. Springer-Verlag, New York, pp. 270-320.         [ Links ]

Bauer, R.T. 1992. Testing generalizations about latitudinal variation in reproduction and recruitment patterns with sicyoniid and caridean shrimp species. Invertebr. Reprod. Dev., 22: 139-202.         [ Links ]

Bertness, M.D., S.D. Gaines & M.E. Hay. 2001. Marine community ecology. Sinauer Associate, Sunderland, Massachusetts, 550 pp.         [ Links ]

Boschi, E.E. 1963. Los camarones comerciales de la família Penaeidae de la costa Atlántica de la América del Sur. Bol. Inst. Biol. Mar., 3: 1-39.         [ Links ]

Boschi, E.E. 1969a. Estudio biológico pesquero del camarón Artemesia longinaris Bate de Mar del Plata. Bol. Inst. Biol. Mar., 18: 1-47.         [ Links ]

Boschi, E.E. 1969b. Crecimiento, migración y ecología del camarón comercial Artemesia longinaris Bate de Mar del Plata. FAO Fish. Rep., 57(3): 833-846.         [ Links ]

Boschi, E.E. 1997. Las pesquerías de crustáceos decápodos en el litoral de la República Argentina. Invest. Mar., Valparaíso, 25: 19-40.         [ Links ]

Branco, J.O. 2005. Biologia e pesca do camarão sete-barbas Xiphopenaeus kroyeri (Heller) (Crustacea, Penaeidae), na Armação do Itapocoroy, Penha, Santa Catarina, Brasil. Rev. Bras. Zool., 22: 1050-1062.         [ Links ]

Campos, E.J.D., D. Velhote & I.C.A. Silveira. 2000. Shelf break upwelling driven by Brazil Current cyclonic meanders. Geophys. Res. Lett., 27: 751-754.         [ Links ]

Campos, E.J.D., Y. Ikeda, B.M. Castro-Filho, S.A. Gaeta, J.A. Lorenzzetti & M.R. Stevenson. 1996. Experiment studies circulation in the western South Atlantic. EOS Trans. Am. Geophys. Union, 77: 253-259.         [ Links ]

Castilho, A.L., R.C. Costa, A. Fransozo & E.E. Boschi. 2007b. Reproductive pattern of the South American endemic shrimp Artemesia longinaris (Decapoda, Penaeidae) off the coast of São Paulo State, Brazil. Rev. Biol. Trop., 55: 39-48.         [ Links ]

Castilho, A.L., M.A. Gavio, R.C. Costa, E.E. Boschi, R.T. Bauer & A. Fransozo. 2007a. Latitudinal variation in population structure and reproductive pattern of the endemic South American shrimp Artemesia longinaris. J. Crust. Biol., 27(4): 548-552.         [ Links ]

Castilho, A.L., M.R. Pie, A. Fransozo, A.P. Pinheiro & R.C. Costa. 2008a. The relationship between environmental variation and species abundance in shrimp communities (Crustacea: Decapoda: Penaeoidea) in south-eastern Brazil. J. Mar. Biol. Assoc. U.K., 88: 119-123.         [ Links ]

Castilho, A.L., M. Furlan, R.C. Costa & V. Fransozo. 2008b. Abundance and temporal-spatial distribution of the rock shrimp Sicyonia dorsalis Kingsley, 1878 (Decapoda, Penaeoidea) from the northern coast of São Paulo State, Brazil. Senckenb. Marit., 38(1): 75-83.         [ Links ]

Castro, R.H., R.C. Costa, A. Fransozo & F.L.M. Mantelatto. 2005. Population structure of seabob shrimp Xiphopenaeus kroyeri (Heller, 1862) (Crustacea: Penaeoidea) in the littoral of São Paulo. Sci. Mar., 69: 105-112.         [ Links ]

Castro-Filho, B.M. & L.B. Miranda. 1998. Physical oceanography of the western Atlantic continental shelf located between 4oN and 34oS. In: A.R Robinson & K.H. Brink (eds.). The sea. Wiley, New York, 2: 209-251.         [ Links ]

Castro-Filho, B.M., L.B. Miranda & S.Y. Miyao. 1987. Condições hidrográficas na plataforma continental ao largo de Ubatuba: Variações sazonais e em média escala. Bol. Inst. Oceanogr. São Paulo, 35(2): 135-151.         [ Links ]

Costa, R.C. & A. Fransozo. 2004. Abundance and ecologic distribution of the shrimp Rimapenaeus constrictus (Crustacea: Penaeidae) in the northern coast of São Paulo State, Brazil. J. Nat. Hist., 38(7): 901-912.         [ Links ]

Costa, R.C., A. Fransozo & A.P. Pinheiro. 2004. Ecologic distribution of the shrimp Pleoticus muelleri (Bate, 1888) (Decapoda: Penaeoidea) of Southeastern Brazil. Hydrobiologia, 529: 195-203.         [ Links ]

Costa, R.C., A. Fransozo, G.A.S. Melo & F.A.M. Freire. 2003. Chave ilustrada para identificação dos camarões Dendrobranchiata do litoral norte do estado de São Paulo, Brasil. Biota Neotrop., 3: 1-12.         [ Links ]

Costa, R.C., A. Fransozo & M.L. Negreiros-Fransozo. 2005a. Ecology of the rock shrimp Sicyonia dorsalis Kingsley, 1878 (Crustacea: Sicyoniidae) in a subtropical region of Brazil. Gulf. Caribb. Res., 17(1): 49-56.         [ Links ]

Costa, R.C., A. Fransozo, A.L. Castilho & F.A.M. Freire. 2005b. Annual, seasonal and spatial variation of abundance of Artemesia longinaris (Decapoda, Penaeoidea) in a region a southeastern region of Brazil. J. Mar. Biol. Assoc. U.K., 85(1): 107-112.         [ Links ]

Costa, R.C., A. Fransozo, F.A.M. Freire & A.L. Castilho. 2007. Abundance and ecological distribution of the "sete-barbas" shrimp Xipohpenaeus kroyeri (Heller, 1862) (Decapoda: Penaeoidea) in three bays of the Ubatuba region, South-eastern Brazil. Gulf Caribb. Res., 19: 33-41.         [ Links ]

Dall, W., B.J. Hill, P.C. Rothlisberg & D.J. Sharples. 1990. The biology of the Penaeidae. Adv. Mar. Biol., 27: 1-489.         [ Links ]

De Leo, F.C. & A.M.S. Pires-Vanin. 2006. Benthic megafauna communities under the influence of the South Atlantic Central Water intrusion onto the Brazilian SE shelf: a comparison between an upwe-lling and a non-upwelling ecosystem. J. Mar. Syst., 60: 268-284.         [ Links ]

Fenucci, J.L. 1988. Manual para la cria de camarones peneidos. FAO Project Reports, Rome, 8: 93 pp.         [ Links ]

Franchito, S.H., T.O. Oda, V.B. Rao & M.T. Kayano. 2007. Interaction between coastal upwelling and local winds at Cabo Frio, Brazil: an observational study. J. Appl. Meteorol. Clim., 47: 1590-1598.         [ Links ]

Fransozo, A., R.C. Costa, A.L. Castilho & F.L. Mantelatto. 2004. Ecological distribution of the shrimp camarão serrinha Artemesia longinaris (Decapoda, Penaeidea) in Fortaleza Bay, Ubatuba, Brazil, in relation to abiotic factors. Rev. Invest. Des. Pesq., 16: 43-50.         [ Links ]

Gribble, N.A., T.J. Wassenberg & C. Burridge. 2007. Factors affecting the distribution of commercially exploited penaeid prawns (shrimp) (Decapod: Penaeidae) across the northern Great Barrier Reef, Australia. Fish. Res., 85: 174-185.         [ Links ]

Hakanson, L. & M. Jansson. 1983. Principles of lake sedimentology. Springer-Verlag, London, 316 pp.         [ Links ]

Iwai, M. 1973. Pesca exploratória e estudo biológico sobre camarão na costa centro-sul do Brasil do N/O Prof. Besnard em 1969-1971. São Paulo, SUDELPA, 71 pp.         [ Links ]

Magalhães, E. 1944. Notas sobre a ocorrência da Artemesia longinaris na costa brasileira. A voz do mar, 190: 148.         [ Links ]

Mantelatto, F.L.M. & A. Fransozo. 1999. Characterization of the physical and chemical parameters of Ubatuba bay, northern coast of São Paulo state, Brazil. Rev. Bras. Biol., 59: 23-31.         [ Links ]

Mascarenhas Jr., A.S., L.B. Miranda & N.J. Rock. 1971. A study of oceanographic conditions in the region of Cabo Frio. In: J.D. Costlow (ed.). Fertility of the sea. Gordon & Breach, New York, 1: 285-308.         [ Links ]

Mistakids, M.N. & G. Neiva. 1964. Occurrence of two penaeid shrimp Artemesia longinaris Bate and Hymenopenaeus mulleri (Bate), and some of lesser known shrimps in coastal waters of South America. Nature, 202: 471-472.         [ Links ]

Morgan, I.J., D.G. McDonald & C.M. Wood. 2001. The cost of living for freshwater fish in a warmer, more polluted world. Global Change Biol., 7: 345-355.         [ Links ]

Nascimento, P.A.M. 1983. Observações preliminares sobre a bionomia do camarão Artemesia longinaris Bate, 1888 (Decapoda, Penaeidea) no Atlântico Ocidental (Lat. 29°S35°־S). Naturalia, 8: 33-47.         [ Links ]

Peterson, C.H. 1979. Predation, competitive exclusion and diversity on soft-sediment benthic communities of estuaries and lagoons. In: R.J. Livingston (ed.). Ecological processes in coastal marine systems. Plenum Press, New York, pp. 233-264.         [ Links ]

Pires-Vanin, A.M., E. Arasaki & P. Muniz. 2013. Spatial pattern of benthic macrofauna in a sub-tropical shelf, São Sebastião Channel, southeastern Brazil. Lat. Am. J. Aquat. Res., 41(1): 42-56.         [ Links ]

Ruello, N.V. 1973. Burrowing, feeding, and spatial distribution of the school prawn Metapenaeus macleayi (Haswell) in the Hunter River region, Australia. J. Exp. Mar. Biol. Ecol., 13: 189-206.         [ Links ]

Scheltema, R.S. 1986. On dispersal and planktonic larvae of benthic invertebrates: an eclectic over view and summary of problems. Bull. Mar. Sci., 39(2): 290-322.         [ Links ]

Silveira, I.C.A., A.C.K. Schmidt, E.J.D. Campos, S.S. Godoi & Y. Ikeda. 2000. A Corrente do Brasil ao largo da costa leste brasileira. Bull. Inst. Paul. Oceanogr., 48(2): 171-183.         [ Links ]

Simões, S.M., R.C. Costa, A. Fransozo & A.L. Castilho. 2010. Diel variation on the abundance and size of seabob shrimp Xiphopenaeus kroyeri (Heller, 1862) (Crustacea, Penaeoidea) in Ubatuba Region, Southeastern of Brazil. An. Acad. Bras. Ciênc., 82(2): 369-378.         [ Links ]

Stramma, L. & M. England 1999. On the water masses and mean circulation of the South Atlantic Ocean. J. Geophys. Res., C.104(C9): 20863-20883.         [ Links ]

Tucker, M. 1988. Techniques in sedimentology. Blackwell Scientific Publications, Oxford, 394 pp.         [ Links ]

Valentin, J.L. 1984. Analyses des parameters hydrobiologiques dans la remontée de Cabo Frio (Brasil). Mar. Biol., 82: 259-276.         [ Links ]

Zar, J.H. 1999. Biostatistical analysis. Prentice Hall, New Jersey, 663 pp.         [ Links ]


Received: 21 May 2013; Accepted: 16 December 2013

Creative Commons License All the contents of this journal, except where otherwise noted, is licensed under a Creative Commons Attribution License