Fish assemblages of Castro Marim salt marsh Pedro Veiga, Constança Bexiga, Lina Vieira1, Rita Sá1 & Karim Erzini1 1 CCMAR/FCMA, Universidade do Algarve, Campus de Gambelas, 8000-117 Faro, Portugal. Corresponding author: [email protected]. INTRODUCTION Castro Marim salt marsh is a wetland located in the southeast part of the Algarve, adjacent to the mouth of the Guadiana river. It is classified as a protected area since 1975, mainly due to its importance as a breeding area for birds. Although salt marshes are known to be very productive ecosystems and important nursery areas for many species (Kneib, 1997), fish communities using salt marshes have rarely been studied in Europe (Laffaille et al., 2000), with few studies in Castro Marim salt marsh (e.g. Machado, 1978; Gonçalves and Beldade, 2000). The present work focused on the structure and dynamics of the fish assemblages of Castro Marim salt marsh. h MATERIAL AND METHODS Sampling was conducted monthly at five sampling sites (A and B: Lezíria creek; C and D: Carrasqueira creek; E: outer adjacent area of salt marsh) (Figure 1), from September 2000 to August 2001. Samples were taken at night during rising neap tides using a 40 m long beach seine (Figure 2), In the laboratory, fishes were identified, counted, measured d (total (t t l length l th to t the th nearestt millimetre) illi t ) and d weighed i h d (wet ( t weight with 0.001g precision). Relative abundances and weight were determined for each fish species and total mean abundances and species richness were determined per month. Figure 1- Location of Castro Marim salt marsh and sampling sites. Source: RNSCMVRSA (2002). An ecological guild, adapted from Mathieson et al. (2000) and based on the occurrence, distribution and abundance of fish in the present study, was attributed to each fish species: resident (R); Marine juvenile migrants (“nursery” species) (MJ); marine adventitious visitors (MA); diadromous (catadromous (CA)/anadromous(AN)) migrants and freshwater adventitious visitors (FW). RESULTS AND DISCUSSION A total of 7955 fish specimens (37995,7g), comprising 34 species and 17 families were sampled (Table I). Fish composition is similar to those found in other salt marshes, estuaries and coastal lagoons in Portugal and Europe (Mathieson et al., 2000). Most of the species in this study were marine adventitious visitors or marine juvenile migrants, being present only in some periods of the year. However, the resident species Pomatoschistus microps (51.9%) and Atherina spp. (10.3%) dominated the fish fauna, together accounting for 60.2% of total abundance. Unlike other studies (e.g. Ambrose and Meffert, 1999; Lazzari et al., 1999), abundance did not show a clear seasonal pattern (Figure 3A), as seen for species richness (Figure 3B). Temporal variations in mean abundance reflected fluctuations in the dominant species. Jackson and Jones (1999) suggested that the consistent presence of many of the dominant species masks the influence of any monthly immigrations and emigrations. emigrations Table I- Species ecological guilds (EG), percentage in number (%N) and Weight (%W), length range and percentage of juveniles, for the fish species caught in Castro Maim salt marsh from September 2000 to August 2001. EG %N %W R R MJ MJ MJ MJ MJ MJ MJ MJ MJ MA MJ R MA MJ R MA AN CA MA AN FW MA FW MA MA R MA MA MA MA 51,9 10,3 6,6 6,6 5,4 4,3 3,9 2,9 2,4 1,5 1,0 0,6 0,5 0,3 0,3 03 0,3 0,3 0,2 0,2 0,1 0,1 0,1 0,1 0,1 0,0 0,0 0,0 0,0 0,0 00 0,0 0,0 0,0 0,0 7955 5,8 7,8 4,1 13,4 3,9 9,4 15,9 13,5 0,5 4,6 2,3 1,1 1,4 1,7 0,5 04 0,4 0,2 0,0 0,3 0,2 0,6 2,1 0,1 9,7 0,0 0,0 0,0 0,1 0,0 03 0,3 0,0 0,0 0,2 37995,7 Length range (cm) % JUV 2,0-6,0 3,95-12,3 2,4-6 6,0-19,6 2,7-10,7 4,1-11,7 6,0-39,7 5,0-15,8 3,8-9,0 6,4-22,5 5,2-17,2 4,0-10,7 2,05-20,8 7,1-22,3 6-9,95 8 4 11 7 8,4-11,7 4,1-8,2 2,5-5,9 7,0-9,8 8,95-13 3,1-32,9 36,3-68,2 9,9-11 44,1-46,3 9,4-9,7 5,5-7,9 8,2 3,2 18,55 61 6,1 23 7,3 11,9 2,2 100 100 100 100 96,9 100 100 98,3 100 100 100 100 18,5 15 100 77,8 100 24,0 100 0 100 100 100 - The majority of species were represented mostly by juveniles, emphasising the nursery function of this ecosystem, as suggested by various authors for other salt marshes (e.g. Lazzari et al. 1999; Mathieson, 2000). Castro Marim salt marsh constitutes an important ecosystem for fishes, since it provides habitat for many species, mostly juveniles, which find here suitable conditions for their development. catch per haul (nu umber) Species Pomatoschistus microps Atherina spp. Mugilidae n.id. Liza aurata Diplodus sargus Spondyliosoma cantharus Liza ramada Mullus surmuletus Sardina pilchardus Liza saliens Dicentrarchus labrax Diplodus vulgaris Halobatrachus didactylus Chelon labrosus Gobius niger E Engraulis li encrasicolus i l Diplodus bellottii Pomatoschistus minutus Mullus barbatus Alosa alosa Anguilla anguilla Belone belone Alosa fallax Cyprinus carpio Syngnathus acus Tinca tinca Dicentrarchus punctatus Diplodus annularis Fundulus heteroclitus Mugil cephalus Parablennius gattorugine Pomatomus saltatrix Solea senegalensis Total 700 600 500 400 300 200 100 0 species per haul (n number) The proportion of juveniles was determined based on length at maturity reported for the species (Cabral et al. (2000). Figure 2- Beach seine used in the present study to sample the fish. A Set Nov Jan Fev Mar Abr Mai Jun Jul Ago month 20 15 B 10 5 0 Set Nov Jan Fev Mar Abr Mai Jun Jul Ago month Figure 3- Monthly variations in mean (+ SD) abundance (A) and species richness (B) in Castro Marim salt marsh, from September 2000 to August 2001. REFERENCES:: REFERENCES Ambrose, R.F. & Meffert, D.J. 1999. Fish-assemblage dynamics in Malibu lagoon, a small, hydrologically altered estuary in southern California. Wetlands, 19: 327-340. Cabral, H.N.; Duque, J. and Costa, M.J. 2000. Importance of the coastal zone adjacent to the Tagus estuary as a nursery area for fish. Thalassas, 16: 27-32. Gonçalves, E. and Beldade, R. 2000. Avaliação do Estado de Conhecimento e Inventariação das Comunidades Ictiológicas da Reserva Natural do Sapal de Castro Marim e Vila Real de Santo António. Relatório Final- ISPA, ICN, RNSCMVRSA. Lisboa. 26 p. Kneib, R.T. 1997. 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