Long-term (2002-2011) changes on Cetengraulis edentulus (Clupeiformes: Engraulidae) fisheries in Guanabara Bay, Brazil
Variaciones a gran escala (2002-2011) de las pesquerías de Cetengraulis edentulus (Clupeiformes: Engraulidae) en la bahía de Guanabara, Brasil
Ana Clara Sampaio Franco1*, Daniel Shimada Brotto2*, David Man Wai Zee3* & Luciano Neves dos Santos1
Abstract
C. edentulus accounts for the major ]]>
C. edentulus catches in Guanabara Bay, focusing especially on temporal variation on capture effort, boat storage temperature, and fish price and size.We assessed the 2002-2011 database of fish landings at the pier of Rubi S.A., with records of year, month, total catch (kg), number of fish per kg, boat storage temperature (oC), and price per kg to boat owner (US$). Those variables differed among years and months (ANOVA; p<0.01) with strong yearXmonth interactions for all, probably ]]>
C. edentulus reproductive and recruitment seasons and environmental conditions of Guanabara Bay. Generalized additive models revealed that high C. edentulus catches were associated with few boat ]]>
C. edentulus fishery were related to changes on boat storage temperature, fish size, price paid per kg, and frequency of landings, and that these descriptors are correlated with C. edentulus ecological traits and high phytoplankton availability. Nevertheless, further studies should be performed to address whether less evident factors, such as the fluctuation of concurrent Sardinella brasiliensis stock, would explain the temporal dynamics of C. edentulus stocks in Guanabara Bay.
Cetengraulis edentulus se distribuye por todo ]]>
C. edentulus al propietario de la embarcación (US$). Todas las variables ]]>
C. edentulus y a las condiciones ambientales de la bahía. Modelos aditivos generalizados indicaron que capturas más elevadas de C. ]]>
estuvieron asociadas con un menor número de desembarques, pero de peces más grandes, los cuales fueron conservados a temperaturas más elevadas y obtuvieron precios más altos de mercado. Aunque los cambios en los descriptores estén relacionados con los atributos ecológicos de C. edentulus y la ]]>
Sardinella brasiliensis, pueden afectar la dinámica temporal de los stocks de C. edentulus en la bahía.
Engraulid fishes, ]]>
Engraulis ringens in Peru, Engraulis anchoita in Argentina, and Cetengraulis ]]>
in Venezuela (Whitehead, 1977) and Guanabara Bay, Brazil (Jablonski, Azevedo, & Moreira, 2006).
The Atlantic anchoveta C. edentulus ]]>
C. edentulus first matures at 118mm total length (L50 for both sexes), reaching 200mm at maximum (Silva et al., 2003; Souza-Conceição, Rodrigues-Ribeiro, & Castro-Silva, 2005). This species feeds mainly on phyto- plankton and ]]>
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C. edentulus began to be used as human food and fish meal since early 1980s, in part due to declining stocks of other traditionally exploited species, such as Sardinella brasiliensis (Whitehead et al., 1988; Jablonski et al., 2006), currently accounting for the major fishery resource in coastal bays of Rio de Janeiro, Southeastern Brazil (Araújo et al., 2008). ]]>
C. edentulus but also other small pelagic fish species (i.e. S. brasiliensis) within the area (Vianna, 2009). Fish are captured near the surface, often together with a few benthic species, because of the shallow waters where those fishing operations are performed.
C. edentulus is the dominant exploited species in Guanabara Bay (12 427t in 2004), accounting for 69% of total fish production. Despite its low value per kilogram, the significant bulk of Atlantic anchoveta landings in Guanabara Bay provided more than US$1 million for local trade (Jablonski et al., 2006). While economically important, the dynamics of C. edentulus catches in Guanabara Bay is barely known, especially in relation to interannual population trends and seasonal fluctuations on its capture. In this sense, this study aims to analyze the long term changes on C. edentulus catches in Guanabara Bay, focusing especially on temporal ]]>
Materials and Methods
Guanabara Bay is an estuary around ]]>
2 located on the coast of Rio de Janeiro state (22°50’ S - 43°10’ W; Fig. 1). The climate is tropical-humid with a warm-rainy season (December-March) and a cold-dry sea- son (July-August) (Paranhos & Mayr, 1993; Valentin et al., 1999). Guanabara Bay is 36km long and has 3x109m3 of water volume, mean depth of 7.6m, and maximum depth of 30m at the entrance channel (Valentin et al., 1999). Tidal currents ]]>
The statistical data examined proceed from a period of ten years of fish landings at the pier of Rubi S.A., a fish processing industry located near Guanabara Bay at Rio de Janeiro state. Fish was caught by boats that operate with purse seines in the region from January of 2002 to June of 2011. Digital database for each fish landing with records of year, month, total catch (kg), number of fish per kg, boat storage temperature (oC), and price paid per kg to boat owner (US$) was assessed. Two-way analysis of variance (ANOVA) were applied on those variables to detect interannual and seasonal variations, followed by Tukey tests (p<0.05) whenever significant differences were recorded.
Generalized additive models (GAMs) were applied to analyse the relationship of C. edentulus catches with others variables. GAMs are an extension of generalized linear models that do not assume a particular functional relationship between the response variable and the predictor. The model complexity of GAMs was chosen by the stepwise selection procedure using the Akaike information criterion (AIC). AIC considers not only the goodness of fit but also parsimony, penalizing more complex models (Burnham & Anderson, 1998).
Results
The catches of C. edentulus varied significantly among years (F7, 7 866=80.9, p<0.01) and months (F10, 7 866=4.2, p<0.01), with a strong year × month interaction (F87, 7 866=11.2, p<0.01). Overall, the catches increased progressively through years, with low yields being recorded in 2002-2003, intermediate values within the 2004-2009 period, and greater catches at 2010-2011 (Tukey test, p<0.05 for all, Fig. 2). High C. edentulus yields were found in May-June whereas low values were recorded during February and September-November (Tukey test, p<0.05 for all), a trend that was not clearly observed for any year separately.
The amount of C. edentulus per kg differed significantly with years (F7, 7 866=2 947.3, p<0.01) and months (F10, 7 866=187.6, p<0.01), with a significant year × month interaction (F87, 7 866=56.7, p<0.01). Higher numbers of C. edentulus per kg were recorded during 2003-2004, indicating a greater contribution of relatively small-sized individuals in the catches (Tukey test, p<0.05 for all, Fig. 3). Since 2004, the number of C. edentulus per kg decreased progressively with years, suggesting increased contributions of larger fishes after that. Small C. edentulus were particularly abundant in the catches of February-April, with a trend of increased contributions of larger fishes toward September, when the lowest numbers of C. edentulus per kg were recorded (Tukey test, p<0.05 for all, Fig. 3). This monthly trend was only clearly observed for 2004, with high among-years variance.
The value paid per kg of C. edentulus differed significantly with years (F7, 7 866=13 356.4, p<0.01) and months (F10, 7 866=67.8, p<0.01), and a significant year × month interaction was also detected (F87, 7 866=270.8, p<0.01). High values were recorded during 2002-2004, with a sharp decrease after April, 2005 (Tukey test, p<0.05 for all, Fig. 4). C. edentulus remained at low values per kg until the middle of 2007, when the values began to increase progressively, reaching at 2011 the similar high values before 2005. The highest values were recorded during December-April, peaking at February and April (Tukey test, p<0.05 for all).This temporal trend was not clearly detected for any separated year, probably because of the high monthly variation among years, as observed especially in May.
Boat storage temperature changed significantly among years (F7, 7 839=77.5, p<0.01) and months (F10, 7 839=17.8, p<0.01), with a strong year × month interaction (F87, 7 839=15.8, p<0.01). Higher temperatures were recorded during 2004-2005 and in 2010 (Tukey test, p<0.05 for all), with a broad variation among ]]>
Fig. 5). Low storage temperatures were observed during July-September whereas high temperatures were recorded in February and March.
The response curves (GAMs) of boat landings, number of C. edentulus
per kg, stor- age temperature and value of C. edentulus per kg also varied with the catches (Fig. 6). The AIC revealed a negative linear trend and April (Tukey test, p<0.05 for all).This temporal trend was not ]]>
1, 111=5.2, p=0.02) with C. edentulus catches, while a positive linear trend was selected for the storage temperature (F1,111=3.8, p=0.05).A non-linear response was found for the number of C. ]]>
per kg (AIC, F1, 110=5.6, p=0.02), with an exponential decrease with the catches. A non-linear relationship was also found for the value paid per kg of C. edentulus (AIC, F1, 110=28.7, p<0.01), with a trend of great values at the extremes of the catches and a broad oscillation of values at ]]>
No relationship (AIC, GAM) was found between the catches for C. edentulus (our data) and S. brasiliensis (data retrieved from CEPSUL Rio de Janeiro state from 2001 to 2007: http://www.icmbio.gov.br/cepsul/biblioteca/acervo-digital/37-download/estatistica/111-estatistica.html “Accessed 20 Sep 2013”). However, AIC selected a negative linear response (AIC, F1, 6=4.4; p=0.09) between the mean values of C. edentulus
per kg and S. brasiliensis catches (time lag of a year; Fig. 7). This trend indicates that C. edentulus ]]>
S. brasiliensis in the preceding year.
Discussion
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Our findings revealed significant interannual and seasonal changes on C. edentulus catches, which can be explained by non-mutually exclusive reasons. Although not directly assessed in this study, the increasing catches of
C. edentulus from 2002 to 2011 could be related to the environmental changes experienced by Guanabara Bay (Paranhos & Mayr, 1993; Caddy, 2000). Changes were reported in the trophic chain of eutrophicated semi-enclosed marine systems, toward the dominance of planktivorous fish, in response to the increased nutrient enrichment, bottom hypoxia episodes, and top predator removal (Caddy, 2000). Guanabara Bay has undergone a continuous eutrophication process, mostly because of its location in the Rio de Janeiro city, one of the most urbanized areas of ]]>
C. edentulus were found (Ribeiro & Kjerfve, 2002). Therefore, ]]>
C. edentulus stocks, since its planktivorous-pelagic habit allow a successful use of food resources with few risks for this species to face bottom anoxic conditions.
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Seasonal changes on C. edentulus catches could be explained by sociocultural and bio- logical effects. Captures peaked on May and June, which is probably related to Holy Week, the most important Christian festival characterized by remarkable increase on fish product consumption. However, the lowest catches of C. edentulus on October and February could be influenced by spawning season and recruit- ment, respectively. The reproductive season of this species occurs from September to Decem- ber (spring) at Guanabara Bay (ACS Franco, personal observations) when adults seem to migrate for spawning, decreasing C. edentulus availability. The spawning site of
C. edentulus in Guanabara Bay is rather controversial on whether adult fish migrate to inner estuarine areas or outer oceanic zones to breed. However, the rare occurrence of C. edentulus at outside bay habitats, the preference of this species for mud bottoms, and the presence of eggs and juveniles in Guanabara Bay, ]]>
The amount of C. edentulus per kg was considered here as an estimation of fish size. According to this descriptor, it was clear that catches consisted mainly of relatively small- sized individuals within 2003 and 2004, sug- gesting stock overexploitation or the use of weak criteria for minimum fish size commercialized at the industry until 2004. Since then, the number of C. edentulus per kg decreased progressively through years, which can be related to an increased contribution of large-sized fishes. Seasonal changes on fish size agree with the temporal trend found for C. edentulus catches, with a dominance of large individuals in September (i.e. reproduction) and small-sized individuals in February (i.e. recruitment). ]]>
Storage temperature fluctuated considerably through years in our study, with a trend of stabilization in 2006 to 2008, when industry supported fishermen with ice. Seasonal changes were also found for temperature, which are mostly related to climate, with high temperatures in warmer months (December to February; summer) and low temperatures in colder months (June to August; winter). The storage temperature and time are ]]>
Engraulis encrasicolus to high temperatures after catching may lead to histamine production, which can cause human intoxication if consumed (Rossano, Mastrangelo, Ungaro, & Riccio, 2006). The ideal storage condition for E. encrasicolus is a 3:2 ice/fish proportion, a temperature of 4°C or less and a maximum storage time of 2 days (Köse & Erdem, 2004; ]]>
Our results also revealed the importance of catch success to the four major descriptors of C. edentulus fisheries in Guanabara Bay. When assessed in conjunction, GAMs revealed that great C. edentulus catches were associated with few boat loadings, compounded mostly of large-sized fishes, which were conserved in higher boat storage temperatures and attained high market prices. The unexpected relationship between few boat landings and great catches could be related to periods of
C. edentulus over abundance, in which the boat storage could be fulfilled with a single purse seine set, resulting in a single landing. On the other hand, several boat landings and low catches might be associated with periods of high stock scattering, requiring more purse seine sets to compensate the failures or low individual and temperature. Although GAMs suggested that highest prices were paid for low and high C. edentulus
catches, those trends seems to be more related to industry strategies and market demand than to species ecological traits.
Other variables than those directly assessed in the present study could also have influence on C. edentulus fisheries. The growth of C. edentulus fisheries in Guanabara Bay was apparently triggered by the collapse, since the later 1990s, of Sardinella brasiliensis stocks (a higher prized target) in the ]]>
2002). C. edentulus also attained lower market prices in response to increased catches of S. brasiliensis in Rio de Janeiro State at the preceding year, suggesting important ]]>
C. edentulus fishery, in a system of multiple exploited stocks.
Our long-term study ]]>
C. edentulus fishery were related to changes on boat storage temperature, fish size, price paid per kg, and frequency of landings. Our findings also stressed that these descriptors are influenced by C. edentulus
ecological traits (i.e. reproductive and recruitment seasons) and changes on ecosystem conditions (i.e. eutrophication). Nevertheless, further studies should be performed to address whether less evident (i.e. the fluctuation of concurrent stocks) or even commonly dismissed (i.e. fleet characteristics, improvement of boat and fishing gears) factors would explain the long and short scale temporal dynamics of C. edentulus
stocks in Guanabara Bay.
Acknowledgments
We especially thank Conservas Rubi Ltda and Marítima Pescados SA for providing financial support ]]>
C. edentulus database. We are also grateful to Graduate Course in Neotropical Biodiversity (PPGBIO-UNIRIO), Laboratory of Theoretical and Applied Ichthyology (LICTA-UNIRIO), and Veiga de Almeida University (UVA) for providing the logistic support. This work was also funded by Fundação Carlos Chagas Filho de Amparo à Pesquisa do Estado do Rio de Janeiro, Brazil (research grant to LN Santos, ]]>
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1. UNIRIO - Universidade Federal do Estado do Rio de Janeiro, Programa de Pós-graduação em Biodiversidade Neotropical. Avenida Pasteur, 458 sala 314A, 22290-240, Rio de Janeiro, Brasil; anaclara306@gmail.com, luciano.santos@unirio.br 2. UVA – Universidade Veiga de Almeida, Departamento de Ciências da Saúde. Rua Ibituruna, 108, 20271-901, Rio de Janeiro, Brasil; danshima@ig.com.br 3. UERJ – Universidade do Estado do Rio de Janeiro, Departamento de Oceanografia Física. Rua São Francisco Xavier 524, sala 4025-E, 20020-100, Rio de Janeiro, Brasil; davidzee.mw@gmail.com
Received 22-XI-2014. Corrected 30-IV-2014. Accepted 28-V-2014.