Rotifera VIII: A Comparative Approach 1998
DOI: 10.1007/978-94-011-4782-8_33
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Planktonic rotifers of Samborombón River Basin (Argentina)

Abstract: The rotifer fauna of the river Samborombón and its tributaries (La Plata river basin) was analysed, and 47 species of monogonont rotifers were identified. Results indicate that differences in salinity and ion composition between waters of the main river and that of its tributaries account for differences in the species composition.

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Cited by 11 publications
(22 citation statements)
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“…The specific richness was found to be higher than other lowland river of the province -Samborombón River- (Modenutti 1998) and environments from Santa Fe province -Salado River and Santa Fe River -(José de Paggi & Paggi 1998). Moreover, it is similar to that reported for the Delta subbasin belonging to the Río de la Plata estuary basin (Modenutti & Claps 1988).…”
Section: Discussionmentioning
confidence: 86%
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“…The specific richness was found to be higher than other lowland river of the province -Samborombón River- (Modenutti 1998) and environments from Santa Fe province -Salado River and Santa Fe River -(José de Paggi & Paggi 1998). Moreover, it is similar to that reported for the Delta subbasin belonging to the Río de la Plata estuary basin (Modenutti & Claps 1988).…”
Section: Discussionmentioning
confidence: 86%
“…The majority of the species found can develop in waters with a wide range of pH, whereas others prefer neutral to alkaline values. Variations in species number and density are associated with the river conductivity, since salinity is a limitation for rotifers (Guisande & Toja 1988, Green 1993, Modenutti 1998 The number of species differed between the main river channel and its tributaries, with maximum values in the middle sector and one affluent (Saladillo-Vallimanca stream). The lowest specific richness was recorded in the headwaters.…”
Section: Discussionmentioning
confidence: 99%
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“…(Trematoda) y Diorchis americana Ransom, 1909 (Cestoda) en Fulica ardesiaca Tschudi 1843 (Guillen & Morales 2003), moluscos como Physa venustula (Gould 1847), Drepanotrema kermatoides (Orbigny, 1835) y Ancylus concentricus (Orbigny 1835) (Vivar et al 1998), arañas como Tetragnathidae, Araneidae, Sicariidae y Palpimanidae (Duárez 1998), insectos acuáticos, principalmente Belostomatidae, Libellulidae, Dytiscidae e Hydrophilidae (García et al 1996), y aves como Podicipedidae, Pelecanidae, Sulidae, Ardeidae, Anatidae, Cathartidae, Falconidae, Rallidae, Charadriidae, Scolopacidae, Columbidae, Cuculidae, Strigidae, Furnariidae, Tyraniidae, Troglodytidae, Ploceidae y Fringillidae (Guillen & Barrio 1995, Valqui 2004, entre otros. Sin embargo, a pesar que los organismos zooplanctónicos son utilizados para monitorear la calidad del agua (Modenutti 1998, Riofrio 2002, Ramos 2004, Rejas et al 2005, éstos han sido pobremente evaluados en los Pantanos de Villa (Grosspietsh 1999). La composición y abundancia de las comunidades zooplanctónicas puede ser influenciada por numerosos factores físicos, químicos y biológicos (Bini et al 2001, Bledzki & Ellison 2003, Rejas et al 2005, Suárez-Morales et al 2005.…”
Section: Introduccionunclassified