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Soetaert, K.. M. Vinckx, J. Wittoeck & M.Tulkens. (1995). Meiobenthic distribution and nematode community structure in five European estuaries. Hydrobiologia. 311: 185-206.
181067
Soetaert, K.. M. Vinckx, J. Wittoeck & M.Tulkens
1995
Meiobenthic distribution and nematode community structure in five European estuaries.
Hydrobiologia
311: 185-206.
Publication
NeMys doc_id: 16533
NeMys doc_id: 16588
Available for editors  PDF available
Meiofauna from the intertidal zone of five European estuaries (Ems, Westerschelde, Somme, Gironde, Tagus) was investigated. Samples represented a cross section of various benthic habitats from near-freshwater to marine, from pure silts to fine-sandy bottoms . The meiobenthic community comprised everywhere a fauna strongly dominated by nematodes, with meiobenthic density increasing with increasing salinity . The Ems differed from the other estuaries due to the presence of a well developed community of Copepods, Gastrotrichs, large Ciliates and/or soft-shelled Foraminiferans in some sites . The Westerschelde stood out due to the near-absence of harpacticoid copepods and, as in the Tagus, the lower meiobenthic densities in the marine part of the estuary. For nematode community analysis, we also included data from the Tamar which were obtained from the literature (Warwick & Gee, 1984) . This resulted in the enumeration of 220 species, belonging to 102 genera, each with a characteristic distribution along the salinity, sedimentary and latitudinal gradients . Using the multivariate technique CANOCO, a zonation along these different physicochemical determinants was observed as well although salinity and sediment characteristics (scale of hundreds of meters to kilometers) proved to be more important in explaining community structure than latitudinal differences (scale of hundreds of kilometers) . Nematode diversity was nearly entirely determined on the genus level and was positively related to salinity. Deviations from this general trend in the Gironde and the Tamar were attributed to sedimentary characteristics or to low macrobenthic predation . The presence of a typical opportunistic colonizing nematode species Pareurodiplogaster pararmatus in the low-salinity region of the Gironde could indicate (organic?) pollution or disturbance of the intertidal mud-flats .
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Aegialoalaimus elegans de Man, 1907 (ecology source)
Atrochromadora microlaima (de Man, 1889) Wieser, 1954 (ecology source)
Camacolaimus tardus de Man, 1889 accepted as Deontolaimus tardus (de Man, 1889) Holovachov & Boström, 2015 (ecology source)
Campylaimus gerlachi Timm, 1961 (ecology source)
Desmoscolex falcatus Lorenzen, 1972 (ecology source)
Dichromadora cucullata Lorenzen, 1973 (ecology source)
Diplopeltis incisus Southern, 1914 accepted as Diplopeltula incisa (Southern, 1914) Gerlach, 1962 accepted as Neodiplopeltula incisa (Southern, 1914) Holovachov & Boström, 2018 (ecology source)
Halalaimus de Man, 1888 (ecology source)
Leptolaimus de Man, 1876 (ecology source)
Leptosomatidae Filipjev, 1916 (additional source)
Megadesmolaimus Wieser, 1954 (additional source)
Metachromadora Filipjev, 1918 (ecology source)
Metalinhomoeus de Man, 1907 (ecology source)
Metalinhomoeus biratus Vitiello, 1969 (ecology source)
Monhysteridae de Man, 1876 (additional source)
Neotonchus cupulatus Vitiello, 1970 (ecology source)
Odontophora Bütschli, 1874 (additional source)
Paracanthonchus Micoletzky, 1924 (additional source)
Praeacanthonchus Micoletzky, 1924 (additional source)
Sabatieria celtica Southern, 1914 (ecology source)
Sabatieria pulchra (Schneider, 1906) Riemann, 1970 (ecology source)
Sabatieria punctata (Kreis, 1924) (ecology source)
Setosabatieria hilarula (de Man, 1922) (ecology source)
Sphaerolaimus hirsutus Bastian, 1865 (ecology source)
Spirinia Gerlach, 1963 (additional source)
Terschellingia de Man, 1888 (ecology source)
Terschellingia longicaudata de Man, 1907 (ecology source)
Trichotheristus Wieser, 1956 accepted as Daptonema Cobb, 1920 (ecology source)
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