Pharmaceutical pollutants are commonly detected in surface waters and have the potential to affect non-target organisms. However, there is limited understanding of how these emerging contaminants may affect macroinvertebrate communities. The pharmaceutical carbamazepine is ubiquitous in surface waters around the world and is a pollutant of particular concern due to its recalcitrance and toxicity. To better understand the potential effects of carbamazepine on natural macroinvertebrate communities, we related stream macroinvertebrate abundance to carbamazepine concentrations. Macroinvertebrate and water samples were collected from 19 streams in central Indiana in conjunction with other stream physiochemical characteristics. Structural equation modeling (SEM) was used to relate macroinvertebrate richness to carbamazepine concentrations. Macroinvertebrate richness was positively correlated with increasing concentrations of carbamazepine. From the SEM we infer that carbamazepine influences macroinvertebrate richness through indirect pathways linked to Baetidae abundance. Baetidae abundance influenced ephemeropteran abundance and FBOM percent organic matter, both of which altered macroinvertebrate richness. The pharmaceutical carbamazepine may alter freshwater macroinvertebrate species composition, which could have significant consequences to ecosystem processes.
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http://dx.doi.org/10.1016/j.scitotenv.2014.07.086 | DOI Listing |
J Environ Manage
January 2025
Department of Life Sciences, Kathmandu University, Dhulikhel, Nepal.
The extent of alien taxa impacts on river ecosystem health is unclear, but their frequency continues to rise. We investigated 1) the prevalence of including alien taxa in common bioindicators used in river bioassessment, 2) the effect of alien taxa on the richness and abundance of natives, and 3) whether including alien taxa in bioassessment tools increased their sensitivity to river degradation. In the 17 countries analyzed fish represented the greatest number of alien species (1726), followed by macrophytes (925), macroinvertebrates (556), and diatoms (7).
View Article and Find Full Text PDFSci Total Environ
January 2025
INRAE, UR RiverLy, Villeurbanne F-69625, France.
Since recent years, an increasingly large number of toxic chemicals enters watercourses threatening freshwater biodiversity. But ecological studies still poorly document the quantitative patterns linking exposure to complex mixture of toxic chemicals and species communities' integrity in the field. In this context, French monitoring authorities have recently deployed at a national scale in situ biotests using the feeding inhibition of the crustacean Gammarus as toxicity indicator.
View Article and Find Full Text PDFEnviron Sci Pollut Res Int
January 2025
South African Institute for Aquatic Biodiversity, Makhanda, 6140, South Africa.
Sci Total Environ
January 2025
Programa de Pós-Graduação em Engenharia Civil e Ambiental, Universidade Federal de Campina Grande, 58429-900 Campina Grande, PB, Brazil.
In the current environmental crisis scenario, it becomes increasingly important to understand the hydroclimatic effects on the availability and quality of water resources and their impacts on aquatic biodiversity. The understanding of how these components are interconnected is necessary to support initiatives for monitoring and managing water resources and protecting biodiversity. In this study, we analyzed the hierarchical effects and dissociated the complex relationships between the storage volume of tropical semi-arid reservoirs on water quality and the diversity of benthic macroinvertebrates.
View Article and Find Full Text PDFMar Environ Res
November 2024
University of the South Pacific, School of Marine Studies. Laucala, Suva, Fiji.
Six sandy beaches located on the south coast of Viti-Levu, Fiji, were sampled to provide as a first aim, an environmental description based upon their physical and biological attributes, to serve as a reference tool for further monitoring programs. Beach face slopes were measured at 4 replicated transects stretching from the front dunes or the seaward reach of the tree vegetation (upper shore level) to the low tide level. Samples for analyses of sand particle size were collected at 4 tidal levels: the upper shore, the drift and effluent lines, and the low tide level.
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