Community structure of ground-water breeding mosquitoes driven by land use in a temperate wetland of Argentina
Wetlands have traditionally been associated with harbouring mosquitoes, but the effect of the land use on their communities has not been thoroughly studied. We characterized the ground-water habitat availability and mosquito species richness and composition during a year-round survey in the predomin...
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2011
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| LEADER | 15198caa a22018977a 4500 | ||
|---|---|---|---|
| 001 | PAPER-10403 | ||
| 003 | AR-BaUEN | ||
| 005 | 20230518204026.0 | ||
| 008 | 190411s2011 xx ||||fo|||| 00| 0 eng|d | ||
| 024 | 7 | |2 scopus |a 2-s2.0-79960572510 | |
| 024 | 7 | |2 cas |a Water, 7732-18-5 | |
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 030 | |a ACTRA | ||
| 100 | 1 | |a Cardo, M.V. | |
| 245 | 1 | 0 | |a Community structure of ground-water breeding mosquitoes driven by land use in a temperate wetland of Argentina |
| 260 | |c 2011 | ||
| 270 | 1 | 0 | |m Cardo, M.V.; Dto de Ecologia, Genetica y Evolucion, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Ciudad Universitaria, Pabellon 2, 4 piso, (C1428EHA) Buenos Aires, Argentina; email: victoriacardo@ege.fcen.uba.ar |
| 506 | |2 openaire |e Política editorial | ||
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| 520 | 3 | |a Wetlands have traditionally been associated with harbouring mosquitoes, but the effect of the land use on their communities has not been thoroughly studied. We characterized the ground-water habitat availability and mosquito species richness and composition during a year-round survey in the predominant land uses (domestic areas, Salicaceae plantations, secondary forests and Scirpus giganteus marshes) of the Paraná Lower Delta, Argentina. Each land use presented a characteristically different number, composition, and diversity of ground-water habitats, and harboured mosquitoes throughout the year. Nearly half of the 824 habitats examined, consisting of 10 types, were positive for immatures. We identified 23 species from 7 genera, with Culex and Ochlerotatus species accounting for 81.7% of all samples. Species richness was significantly lower in marshes than in the other land uses. Some species such as Culex dolosus s.l. and Ochlerotatus crinifer exhibited no habitat-type restrictions, while Uranotaenia nataliae and Mansonia indubitans presented specific habitat requirements. Our results strongly suggest that land use within temperate wetlands drives species richness and composition of ground-water mosquito communities through larval habitat availability. © 2011 Elsevier B.V. |l eng | |
| 536 | |a Detalles de la financiación: Universidad de Buenos Aires, UBACYT X608 | ||
| 536 | |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas, PIP 112-200801-00743 | ||
| 536 | |a Detalles de la financiación: This study was partially supported by Consejo Nacional de Investigaciones Científicas y Técnicas (PIP 112-200801-00743) and University of Buenos Aires (UBACYT X608). We thank the authorities of Estación Experimental Agropecuaria Delta del Paraná-INTA, Las Carabelas-Papel Prensa S.A., Automovil Club Argentino, Felicaria camp of San Fernando Municipality, Luz y Fuerza camp, Parque Lyfe camp, La Posada de Posadas hostel, El Sol hostel and Gabi and Lili for allowing us to work at the study sites. Special thanks to Interisleña S.A. for transportation facilities. MVC is fellow of CONICET, and DV and AEC are members of the Research Career of CONICET. | ||
| 593 | |a Unidad de Ecologia de Reservorios y Vectores de Parasitos, Departamento de Ecologia, Genetica y Evolucion, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Argentina | ||
| 690 | 1 | 0 | |a ANTHROPIC INTERVENTION |
| 690 | 1 | 0 | |a CULEX |
| 690 | 1 | 0 | |a CULICIDAE |
| 690 | 1 | 0 | |a DELTA OF PARANA RIVER |
| 690 | 1 | 0 | |a OCHLEROTATUS |
| 690 | 1 | 0 | |a RICHNESS |
| 690 | 1 | 0 | |a GROUND WATER |
| 690 | 1 | 0 | |a COMMUNITY STRUCTURE |
| 690 | 1 | 0 | |a GROUNDWATER |
| 690 | 1 | 0 | |a HABITAT AVAILABILITY |
| 690 | 1 | 0 | |a HABITAT TYPE |
| 690 | 1 | 0 | |a LAND USE |
| 690 | 1 | 0 | |a LARVA |
| 690 | 1 | 0 | |a MOSQUITO |
| 690 | 1 | 0 | |a SPECIES RICHNESS |
| 690 | 1 | 0 | |a WETLAND |
| 690 | 1 | 0 | |a AEDEOMYIA |
| 690 | 1 | 0 | |a AEDEOMYIA SQUAMIPENNIS |
| 690 | 1 | 0 | |a ANIMAL EXPERIMENT |
| 690 | 1 | 0 | |a ANOPHELES |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a BREEDING |
| 690 | 1 | 0 | |a CANAL |
| 690 | 1 | 0 | |a CULEX |
| 690 | 1 | 0 | |a CULEX BIDENS |
| 690 | 1 | 0 | |a CULEX CHIDESTERI |
| 690 | 1 | 0 | |a CULEX DOLOSUS |
| 690 | 1 | 0 | |a CULEX INTRINCATUS |
| 690 | 1 | 0 | |a CULEX LAHILLEI |
| 690 | 1 | 0 | |a CULEX MAXI |
| 690 | 1 | 0 | |a CULEX MOLLIS |
| 690 | 1 | 0 | |a CULEX PIPIENS |
| 690 | 1 | 0 | |a CULEX TATOI |
| 690 | 1 | 0 | |a DOMESTIC AREA |
| 690 | 1 | 0 | |a GEOGRAPHIC AND GEOLOGICAL PHENOMENA |
| 690 | 1 | 0 | |a GUTTER |
| 690 | 1 | 0 | |a HABITAT STRUCTURE |
| 690 | 1 | 0 | |a IRRIGATION (AGRICULTURE) |
| 690 | 1 | 0 | |a IRRIGATION DITCH |
| 690 | 1 | 0 | |a LAND USE |
| 690 | 1 | 0 | |a MANSONIA INDUBITANS |
| 690 | 1 | 0 | |a MARSH |
| 690 | 1 | 0 | |a MOSQUITO |
| 690 | 1 | 0 | |a NONHUMAN |
| 690 | 1 | 0 | |a OCHLEROTATUS |
| 690 | 1 | 0 | |a OCHLEROTATUS ALBIFASCIATUS |
| 690 | 1 | 0 | |a OCHLEROTATUS CRINIFER |
| 690 | 1 | 0 | |a OCHLEROTATUS SCAPULARIS |
| 690 | 1 | 0 | |a OCHLEROTATUS SERRATUS |
| 690 | 1 | 0 | |a ORGANISM COMMUNITY |
| 690 | 1 | 0 | |a POND |
| 690 | 1 | 0 | |a POOL UNDER FALLEN TREE ROOT |
| 690 | 1 | 0 | |a POPULATION ABUNDANCE |
| 690 | 1 | 0 | |a PSOROPHORA |
| 690 | 1 | 0 | |a PSOROPHORA ALBIGENU |
| 690 | 1 | 0 | |a PSOROPHORA DISCRUCIANS |
| 690 | 1 | 0 | |a PSOROPHORA FEROX |
| 690 | 1 | 0 | |a PSOROPHORA VARIPES |
| 690 | 1 | 0 | |a SALICACEAE PLANTATION |
| 690 | 1 | 0 | |a SCIRPUS GIGANTEUS MARSH |
| 690 | 1 | 0 | |a SECONDARY FOREST |
| 690 | 1 | 0 | |a SPECIES COMPOSITION |
| 690 | 1 | 0 | |a SPECIES DIVERSITY |
| 690 | 1 | 0 | |a SPECIES IDENTIFICATION |
| 690 | 1 | 0 | |a SPECIES RICHNESS |
| 690 | 1 | 0 | |a STREAM (RIVER) |
| 690 | 1 | 0 | |a TEMPERATE WETLAND |
| 690 | 1 | 0 | |a URANOTAENIA APICALIS |
| 690 | 1 | 0 | |a URANOTAENIA NATALIAE |
| 690 | 1 | 0 | |a URANOTAENIA PULCHERRIMA |
| 690 | 1 | 0 | |a VEGETATION |
| 690 | 1 | 0 | |a WETLAND |
| 690 | 1 | 0 | |a ANIMALS |
| 690 | 1 | 0 | |a BIODIVERSITY |
| 690 | 1 | 0 | |a CULICIDAE |
| 690 | 1 | 0 | |a ECOSYSTEM |
| 690 | 1 | 0 | |a HUMAN ACTIVITIES |
| 690 | 1 | 0 | |a WATER |
| 690 | 1 | 0 | |a WETLANDS |
| 690 | 1 | 0 | |a PARANA DELTA |
| 690 | 1 | 0 | |a CRINIFER |
| 690 | 1 | 0 | |a CULICIDAE |
| 690 | 1 | 0 | |a SALICACEAE |
| 690 | 1 | 0 | |a SCIRPUS |
| 651 | 4 | |a ARGENTINA | |
| 651 | 4 | |a ARGENTINA | |
| 651 | 4 | |a ARGENTINA | |
| 700 | 1 | |a Darío, V. | |
| 700 | 1 | |a Eduardo, C.A. | |
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