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Salamander loss alters montane stream ecosystem functioning and structure through top-down effects
Summary
This study tested how removing fire salamanders — key predators in European mountain streams — affects the structure and functioning of the aquatic ecosystem. The experiment provides insight into how amphibian population declines cascade through freshwater food webs, with implications for how microplastic contamination affecting amphibians may indirectly alter stream ecosystems.
<title>Abstract</title> Amphibians are among the most endangered taxa worldwide, but little is known about how their disappearance can alter the functioning and structure of freshwater ecosystems, where they live as larval stages. This is particularly true for urodeles, which often are key predators in these ecosystems. The fire salamander (<italic>Salamandra salamandra</italic>) is a common predator in European fresh waters, but the species is declining due to habitat loss and the infection by fungal pathogens. We studied the consequences of fire salamander loss from three montane streams, by comparing two key ecosystem processes (periphyton accrual and leaf litter decomposition) and the structure of three communities (periphyton algae, aquatic hyphomycetes and invertebrates) using instream enclosures with and without salamander larvae. Salamander loss did not cause changes in invertebrate abundance or community structure, except for one stream where abundance increased in the absence of salamander larvae. However, salamander loss led to lower periphyton accrual, changes in algal community structure and slower leaf litter decomposition, with no associated changes in fungal communities or microbial decomposition. The changes observed may have been caused by release of salamander larvae predatory pressure on invertebrates, which could have promoted their grazing on periphyton, in contrast to their preference for leaf shredding in the presence of salamander. Our study demonstrates an important role of salamander larvae in montane streams through top-down control of lower trophic levels and thus in regulating key stream ecosystem processes.
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