首页> 外文会议>International Symposium on Managroves as Fish Habitat; 20060419-21; Miami,FL(US) >JUVENILE BLUE CRAB ABUNDANCES IN NATURAL AND MAN-MADE TIDAL CHANNELS IN MANGROVE HABITAT, TAMPA BAY, FLORIDA (USA)
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JUVENILE BLUE CRAB ABUNDANCES IN NATURAL AND MAN-MADE TIDAL CHANNELS IN MANGROVE HABITAT, TAMPA BAY, FLORIDA (USA)

机译:佛罗里达坦帕湾曼格罗夫栖息地天然和人工潮汐通道中的少年蓝蟹数量

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The blue crab (Callinectes sapidus M. J. Rathbun, 1896) is an ecologically and commercially important species common in the Gulf of Mexico and Western Atlantic Ocean (Virnstein, 1977; Hines et al, 1990; Guillory et al., 1998). The life cycle of the blue crab is considered to be classically estuarine-dependent with females mating within the estuary then migrating offshore to spawn. Larvae are transported back into estuarine habitats where they settle and grow to adult sizes (Tagatz, 1968). Studies of habitat utilization by juvenile blue crabs have focused largely on seagrass, saltmarsh, and unvegetated habitats. Previous studies indicate that seagrass and salt-marsh habitats are important to juvenile blue crabs: researchers report higher juvenile densities, decreased predation, and/or faster growth rates compared to unvegetated habitats (Orth and van Montfrans, 1987, 2002; Thomas et al., 1990; Williams et al., 1990; Perkins-Visser et al., 1996; Rozas and Minello, 1998; Rozas and Zimmerman, 2000). While the use of saltmarsh and seagrass by juvenile blue crabs is relatively well understood, knowledge of mangrove wetlands as habitat for blue crabs is limited. In Rookery Bay, Florida, blue crab densities were lowest in intertidal mangrove habitat, and higher in seagrass and open water (Sheridan, 1992). However, a study comparing mangrove and saltmarsh habitats in Caminada Bay, Louisiana found that blue crabs were more closely associated with mangrove habitat and suggested that this relationship was due to the greater structural complexity offered by mangroves (Caudill, 2005). However, juvenile densities were not reported in these two studies.
机译:蓝蟹(Callinectes sapidus M. J. Rathbun,1896)是在墨西哥湾和西大西洋上常见的具有生态和商业意义的物种(Virnstein,1977; Hines等,1990; Guillory等,1998)。蓝蟹的生命周期被认为是经典的河口依赖,雌性在河口内交配,然后迁移到近海产卵。幼虫被运回河口栖息地,在那里定居并成长为成年大小(Tagatz,1968)。幼年蓝蟹对栖息地利用的研究主要集中在海草,盐沼和无植被的栖息地上。先前的研究表明,海草和盐沼栖息地对幼小的蓝蟹很重要:研究人员报告说,与无植被的栖息地相比,幼体密度更高,捕食减少和/或生长速度更快(Orth和van Montfrans,1987,2002; Thomas等。 ,1990; Williams等,1990; Perkins-Visser等,1996; Rozas和Minello,1998; Rozas和Zimmerman,2000)。虽然相对较了解幼稚的蓝蟹使用盐沼和海草,但对红树林湿地作为蓝蟹的栖息地的了解却很有限。在佛罗里达州的洛克里湾,潮间带红树林栖息地的蓝蟹密度最低,海草和开阔水域的蓝蟹密度更高(Sheridan,1992)。但是,一项对路易斯安那州卡米纳达湾的红树林和盐沼栖息地进行比较的研究发现,蓝蟹与红树林栖息地的联系更为紧密,并表明这种关系是由于红树林提供的更大的结构复杂性造成的(Caudill,2005)。但是,这两项研究均未报告少年密度。

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