2018
DOI: 10.1051/kmae/2017055
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Artificial ponds in Central Europe do not fall behind the natural ponds in terms of macrophyte diversity

Abstract: -We studied macrophyte composition and 24 environmental variables in 69 ponds of both natural and artificial origin in Slovakia. We tested differences in a and g diversity and b similarity between natural and artificial ponds for helophytes, hydrophytes, red list species and all species. We also assessed effects of environmental variables on species richness of studied ponds by generalised linear models (GLM). For local diversity, the significant difference was obtained only in case of helophytes. Beta similar… Show more

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Cited by 8 publications
(7 citation statements)
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“…For example, gravel pit ponds were calculated to host 57% of the regional species pool of waterbirds in southern France (Santoul et al 2009), while irrigation ponds hosted 40% of the regional richness in aquatic insects in south-western France (Ruggiero et al 2008), and a slightly lower relative contribution was reported for water beetles in irrigation and watering ponds in south-eastern Spain (Picazo et al 2010). In the case of macrophyte assemblages, artificial ponds were seen to support 65% of regional diversity in Central Europe, although the contribution was significantly lower than for natural ponds (Bubíková & Hrivnák 2018). If well designed, artificial ponds can provide suitable habitats even for threatened J o u r n a l P r e -p r o o f species, as is the case for beetles and dragonflies in small Alpine reservoirs (Fait et al 2020) and for amphibians in small manmade waterbodies in semiarid regions of Spain (Egea-Serrano et al 2006).…”
Section: Introductionmentioning
confidence: 89%
“…For example, gravel pit ponds were calculated to host 57% of the regional species pool of waterbirds in southern France (Santoul et al 2009), while irrigation ponds hosted 40% of the regional richness in aquatic insects in south-western France (Ruggiero et al 2008), and a slightly lower relative contribution was reported for water beetles in irrigation and watering ponds in south-eastern Spain (Picazo et al 2010). In the case of macrophyte assemblages, artificial ponds were seen to support 65% of regional diversity in Central Europe, although the contribution was significantly lower than for natural ponds (Bubíková & Hrivnák 2018). If well designed, artificial ponds can provide suitable habitats even for threatened J o u r n a l P r e -p r o o f species, as is the case for beetles and dragonflies in small Alpine reservoirs (Fait et al 2020) and for amphibians in small manmade waterbodies in semiarid regions of Spain (Egea-Serrano et al 2006).…”
Section: Introductionmentioning
confidence: 89%
“…Their surface areas range from a minimum of 2 m 2 to a maximum of 2395 m 2 , and their altitudes from 193 to 838 m a.s.l. Only mountain ponds (8)(9)(10)(11)(12) fall within a protected area, the Monte San Calogero Regional Natural Reserve, which is also a Natura2000 site (code ITA020033) according to the EU 92/43/CEE "Habitats" Directive. Chemical and isotopic analyses on the stored water bodies were carried out on a subset of 10 sites, representative of the different managing and construction criteria, geo-climatic conditions and water origins.…”
Section: Methodsmentioning
confidence: 99%
“…Farm ponds are usually considered artificial poor habitats, although it has been shown that sometimes they host a significant biodiversity, contributing to maintain rich trophic webs, from producers to consumers and decomposers [ 4 , 5 , 6 , 7 ]. Although biodiversity of these habitats is usually poorer than that of natural ones [ 8 , 9 ], it has been shown that the two groups are rather comparable as far as hydrophytes and red-listed species is concerned [ 9 ].…”
Section: Introductionmentioning
confidence: 99%
“…Deeper water bodies generally occur at lower altitudes due to the morphological characteristics of the Apennines. The few helophytes and hydrophytes found at higher altitudes may be explained by steep slopes and a lack of lakes, while the wettest areas are often the most low-lying and gently sloped (Bubíková and Hrivnák, 2018). However, plant species and their attributes changed significantly along the altitudinal gradient in both wetland subsystems, following an expected trend of species turnover: therophytes and Mediterranean and European chorotypes were more common at lower altitudes, whereas boreal or Eurasiatic species at higher altitudes, in relation to different temperature and drought values (Angiolini et al, 2011;Nucci et al, 2012b).…”
Section: Floristic Composition and Environmental Factors In Palustrinmentioning
confidence: 98%
“…It has been recognized as a primary regional determinant of wetland plant communities (e.g. Lougheed et al, 2001;Bubíková and Hrivnák, 2018). The sandstone/arenaceous marls geological type is mainly composed of arenaceous and pelitic-arenaceous lithofacies, and its low permeability, defined by the succession of sandstones and marls, limits the percolation of rainwater, creating superficial runoff (Galassi et al, 2011).…”
Section: Main Environmental Factors Driving Species Compositionmentioning
confidence: 99%