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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)
Anoplostoma viviparum (Bastian, 1865) Bütschli, 1874 (ecology source)
Ascolaimus Ditlevsen, 1919 (ecology source)
Ascolaimus elongatus (Bütschli, 1874) Shuurmans Stekhoven & de Coninck, 1932 (ecology source)
Atrochromadora microlaima (de Man, 1889) Wieser, 1954 (ecology source)
Axonolaimus paraspinosus Schuurmans Stekhoven & Adam, 1931 (ecology source)
Axonolaimus spinosus (Bütschli, 1874) de Man, 1889 (ecology source)
Camacolaimus tardus de Man, 1889 accepted as Deontolaimus tardus (de Man, 1889) Holovachov & Boström, 2015 (ecology source)
Chromadora macrolaima de Man, 1889 (ecology source)
Chromadora nudicapitata Bastian, 1865 (ecology source)
Desmolaimus zeelandicus de Man, 1880 (ecology source)
Dichromadora cephalata (Steiner, 1916) Kreis, 1929 (ecology source)
Dichromadora cucullata Lorenzen, 1973 (ecology source)
Dichromadora geophila (de Man, 1876) Kreis, 1929 (ecology source)
Dichromadora hyalocheile De Coninck & Schuurmans Stekhoven, 1933 (ecology source)
Enoplus brevis Bastian, 1865 (ecology source)
Halalaimus de Man, 1888 (ecology source)
Halichoanolaimus robustus (Bastian, 1865) de Man, 1886 (ecology source)
Hypodontolaimus balticus (G. Schneider, 1906) Filipjev, 1918 (ecology source)
Leptolaimus de Man, 1876 (ecology source)
Leptosomatidae Filipjev, 1916 (additional source)
Metachromadora Filipjev, 1918 (ecology source)
Metachromadora vivipara (de Man, 1907) Allgen, 1928 accepted as Chromadoropsis vivipara (de Man, 1907) Allgen, 1928 (ecology source)
Metalinhomoeus de Man, 1907 (ecology source)
Molgolaimus cuanensis (Platt, 1973) Jensen, 1978 (ecology source)
Monhysteridae de Man, 1876 (additional source)
Odontophora Bütschli, 1874 (additional source)
Odontophora setosa (Allgén, 1929) (ecology source)
Oncholaimus oxyuris Ditlevsen, 1911 (ecology source)
Oxystomina elongata (Bütschli, 1874) Filipjev, 1921 (ecology source)
Paracanthonchus Micoletzky, 1924 (additional source)
Paracanthonchus caecus (Bastian, 1865) Micoletzky, 1924 (ecology source)
Paracanthonchus heterodontus (Schulz, 1932) Vincx et al., 1982 (ecology source)
Prochromadorella ditlevseni (de Man, 1922) Wieser, 1954 (ecology source)
Ptycholaimellus Cobb, 1920 (ecology source)
Sabatieria celtica Southern, 1914 (ecology source)
Sabatieria longisetosa (Kreis, 1929) (ecology source)
Sabatieria pulchra (Schneider, 1906) Riemann, 1970 (ecology source)
Sabatieria punctata (Kreis, 1924) (ecology source)
Sphaerolaimus balticus Schneider, 1906 (ecology source)
Sphaerolaimus gracilis de Man, 1876 (ecology source)
Sphaerolaimus hirsutus Bastian, 1865 (ecology source)
Spilophorella candida Gerlach, 1951 (ecology source)
Spirinia Gerlach, 1963 (additional source)
Spirinia parasitifera (Bastian, 1865) Gerlach, 1963 (ecology source)
Terschellingia de Man, 1888 (ecology source)
Terschellingia communis de Man, 1888 (ecology source)
Terschellingia longicaudata de Man, 1907 (ecology source)
Thalassoalaimus septentrionalis Filipjev, 1927 (ecology source)
Theristus blandicor Rachor, 1971 (ecology source)
Theristus longus Platt, 1973 (ecology source)
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