Linking water quality with amphibian breeding and development: a case study comparing natural ponds and Sustainable Drainage Systems (SuDS) in East Kilbride, Scotland
Abstract:Amphibians have declined due to habitat loss and alteration. Sustainable Drainage Systems (SuDS) provide potential habitat for amphibians in urban landscapes. However, the contaminants they accumulate may cause increased pollutant exposure, and limited research has addressed whether differences in water quality between SuDS and natural ponds might restrict their use by amphibians. This study aimed to explore the effects of water quality on amphibian breeding and development in SuDS and natural ponds in East Ki… Show more
“…Although biodiversity enhancement is not the prime motivation behind SuDS installation, there is growing evidence that they can provide habitat for a wide range of wild species, amphibians included. Scottish studies include: O'Brien, ; O'Brien, Hall, Miro, Rae, & Jehle, ; Miro, Hall, Rae, & O'Brien, ; and Bird et al, . Hassall and Anderson () have reported similar results from Canadian urban storm‐water management ponds.…”
Section: Protection Enhancement and Mitigationmentioning
confidence: 89%
“…In the Pyrenees, Miro, Sabas, and Ventura () found a strong negative association between introduced trout and four out of six amphibian species, especially the common frog, but also that some amphibians could co‐exist with fish. In Scotland also, research has shown that some amphibians are capable of breeding successfully in the presence of at least some species of fish (Bird, Paterson, Downie, & Mable, ).…”
Section: Threatsmentioning
confidence: 99%
“…The effects of pollutants on amphibian breeding and development remain relatively under‐researched. In Scotland, Bird et al () surveyed 19 peri‐urban ponds for heavy metal pollutants, salt, and chlorophyll (as an indicator of plant nutrient levels): frog breeding occurred successfully over a wide range of pollutant concentrations, but high levels of aluminium were shown to be detrimental to development. We know of no Scottish study that has reported the effects of agrichemicals, as demonstrated elsewhere, such as: alteration of tadpole brain development by exposure to sublethal concentrations of the pesticide chlorpyrifos (Woodley, Mattes, Yates, & Relyea, ); reduced tadpole survival and damage to the cutaneous bacterial community by the herbicide glyphosate (Krynak, Burke, & Benard, ); and feminization of male gonadal development by the herbicide atrazine (Orton & Tyler, ).…”
The distributions and conservation status of the six native amphibian species in Scotland are reviewed. Issues of under‐recording and false recording are noted, and steps to remedy these problems are described.
Threats to amphibians in Scotland include diseases (a minor impact so far), road deaths, habitat loss, and climate change (to which populations may be resilient). Exploitation, competition, and pollution do not appear to be significant threats to amphibians in Scotland.
Legal protection is currently strongest for the great crested newts (Triturus cristatus) and natterjack toads (Epidalea calamita), but the natterjack toads have only a small localized Scottish population. The ponds at Gartcosh hold the largest great crested newt population in Scotland. Translocation to a specially created reserve appears to have been successful but a new road across the site is an additional hazard, for which monitoring is in progress.
Amphibian habitat enhancement in Scotland includes pond‐creation programmes, which have successfully increased the diversity of plants and invertebrates as well as amphibians. The value of Sustainable Drainage Systems (SuDS) for amphibians and other wildlife is reviewed. The Eurasian beaver reintroduction programme may benefit amphibians in the longer term, but research is currently lacking. Road tunnels combined with fences are a vital mitigation for road‐traffic impacts on amphibians and have been monitored at one Scottish site. Amphibian ladders in road drains are another potentially helpful mitigation.
The amphibians of Scotland need more long‐term monitoring. A national strategy is imminent and should stimulate the required research and action.
“…Although biodiversity enhancement is not the prime motivation behind SuDS installation, there is growing evidence that they can provide habitat for a wide range of wild species, amphibians included. Scottish studies include: O'Brien, ; O'Brien, Hall, Miro, Rae, & Jehle, ; Miro, Hall, Rae, & O'Brien, ; and Bird et al, . Hassall and Anderson () have reported similar results from Canadian urban storm‐water management ponds.…”
Section: Protection Enhancement and Mitigationmentioning
confidence: 89%
“…In the Pyrenees, Miro, Sabas, and Ventura () found a strong negative association between introduced trout and four out of six amphibian species, especially the common frog, but also that some amphibians could co‐exist with fish. In Scotland also, research has shown that some amphibians are capable of breeding successfully in the presence of at least some species of fish (Bird, Paterson, Downie, & Mable, ).…”
Section: Threatsmentioning
confidence: 99%
“…The effects of pollutants on amphibian breeding and development remain relatively under‐researched. In Scotland, Bird et al () surveyed 19 peri‐urban ponds for heavy metal pollutants, salt, and chlorophyll (as an indicator of plant nutrient levels): frog breeding occurred successfully over a wide range of pollutant concentrations, but high levels of aluminium were shown to be detrimental to development. We know of no Scottish study that has reported the effects of agrichemicals, as demonstrated elsewhere, such as: alteration of tadpole brain development by exposure to sublethal concentrations of the pesticide chlorpyrifos (Woodley, Mattes, Yates, & Relyea, ); reduced tadpole survival and damage to the cutaneous bacterial community by the herbicide glyphosate (Krynak, Burke, & Benard, ); and feminization of male gonadal development by the herbicide atrazine (Orton & Tyler, ).…”
The distributions and conservation status of the six native amphibian species in Scotland are reviewed. Issues of under‐recording and false recording are noted, and steps to remedy these problems are described.
Threats to amphibians in Scotland include diseases (a minor impact so far), road deaths, habitat loss, and climate change (to which populations may be resilient). Exploitation, competition, and pollution do not appear to be significant threats to amphibians in Scotland.
Legal protection is currently strongest for the great crested newts (Triturus cristatus) and natterjack toads (Epidalea calamita), but the natterjack toads have only a small localized Scottish population. The ponds at Gartcosh hold the largest great crested newt population in Scotland. Translocation to a specially created reserve appears to have been successful but a new road across the site is an additional hazard, for which monitoring is in progress.
Amphibian habitat enhancement in Scotland includes pond‐creation programmes, which have successfully increased the diversity of plants and invertebrates as well as amphibians. The value of Sustainable Drainage Systems (SuDS) for amphibians and other wildlife is reviewed. The Eurasian beaver reintroduction programme may benefit amphibians in the longer term, but research is currently lacking. Road tunnels combined with fences are a vital mitigation for road‐traffic impacts on amphibians and have been monitored at one Scottish site. Amphibian ladders in road drains are another potentially helpful mitigation.
The amphibians of Scotland need more long‐term monitoring. A national strategy is imminent and should stimulate the required research and action.
“…Details of biochemical and histopathological changes in Indian frog caused by metal contamination can also be found in Jayawardena et al [189]. Bird et al [190] have however highlighted that the effect of metals on amphibians depends on the combination of metals present. Some of these effects are presented in Table 5.…”
Section: Mozambique Tilapia (Oreochromis Mossambicus) Common Carp (Cy...mentioning
Acid mine drainage (AMD) is a low pH, high conductivity, high metals, and sulphate ion concentration liquid formed by the oxidation of sulphide minerals in pyrite-bearing mine wastes. The generation of AMD has been associated mostly with coal and gold mining but mining of other sulphidic metal ores such as tin, silver, copper, and iron are also known to generate AMD [1][2][3]. A series of studies [4-9] have reported on AMD generation and the microbes involved in the process with all these studies indicating that AMD forms when sulphide-rich mine wastes get exposed to oxygen-rich conditions. Sulphur containing minerals associated with the generation of AMD according to Li et al. [10] and Chopard et al. [11] include pyrite (FeS 2 ), arsenopyrite (FeAsS), chalcopyrite (CuFeS 2 ), galena (PbS), gersdorffite (NiAsS), pyrrhotite, and sphalerite
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.