Foraging behaviour of top predators mediated by pollution of psychoactive pharmaceuticals and effects on ecosystem stability
Language English Country Netherlands Media print-electronic
Document type Journal Article
PubMed
30703723
DOI
10.1016/j.scitotenv.2019.01.295
PII: S0048-9697(19)30338-9
Knihovny.cz E-resources
- Keywords
- Citalopram, Functional response, Maximum feeding rate, Predator-prey interaction, Tramadol, WWTP,
- MeSH
- Models, Biological MeSH
- Water Pollutants, Chemical adverse effects MeSH
- Citalopram adverse effects MeSH
- Serotonin and Noradrenaline Reuptake Inhibitors adverse effects MeSH
- Carps physiology MeSH
- Nymph drug effects growth & development physiology MeSH
- Wastewater analysis MeSH
- Food Chain MeSH
- Predatory Behavior drug effects MeSH
- Selective Serotonin Reuptake Inhibitors adverse effects MeSH
- Tramadol adverse effects MeSH
- Avoidance Learning drug effects MeSH
- Odonata drug effects growth & development physiology MeSH
- Animals MeSH
- Check Tag
- Animals MeSH
- Publication type
- Journal Article MeSH
- Names of Substances
- Water Pollutants, Chemical MeSH
- Citalopram MeSH
- Serotonin and Noradrenaline Reuptake Inhibitors MeSH
- Waste Water MeSH
- Serotonin Uptake Inhibitors MeSH
- Tramadol MeSH
Although pharmaceuticals are recognized as a major threat to aquatic ecosystems worldwide, little is known about their ecological effect on aquatic biota and ecosystems. Drug-induced behaviour changes could have a substantial impact on consumer-resource interactions influencing stability of the community and ecosystem. We combined laboratory experiments and functional response modelling to investigate effects of real wastewater treatment plant (WWTP) effluent, as well as environmentally relevant concentrations of the antidepressants citalopram and opioid pain medication tramadol, on trophic interactions. Our biological system consisted of dragonfly Aeshna cyanea larvae as predator of common carp Cyprinus carpio fry. Exposure to WWTP effluent significantly increased A. cyanea maximum feeding rate, while those parameters in tramadol and citalopram-exposed larvae were significantly lower from unexposed control group. This suggested the potential of all tested pollutants to have an effect on consumer-resource equilibrium in aquatic ecosystems. While WWTP effluent strengthened interaction strength (IS) of consumer-resource interaction dynamics making the food web more vulnerable to fluctuation and destabilization, tramadol and citalopram could inhibit the potential oscillations of the consumer-resource system by weakening the IS. Similar studies to reveal the potential of pervasive pharmaceuticals to change of consumer-resource interactions dynamics are needed, especially when real WWTP effluent consisting of mixture of various pharmaceuticals displayed very different effect from single compounds tested.
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