Grant: Strategic Projects - Group
University of Windsor
$151,000.00
Adaptive genetic and physiological responses to aquatic contaminant stress
FY 2007-08
Summary
Canadian aquatic environments are increasingly stressed as a result of contaminant loads from industry, agriculture and urbanization. Chemicals eventually end up in aquatic environments where biological availability is high. The high level of stress in contaminated aquatic habitats will elicit an adaptive response in the resident fauna: either short-term physiological change (acclimation), genetic change driven by selection (evolution), or both. Such adaptive responses are not considered when we look for population- or ecosystem-level effects of contaminant exposure and may explain the rarity of negative population-level effects. This project examines the response of brown bullhead from contaminated and clean sites to contaminant (PAH) challenges. We propose that the energetic and survival costs of living in contaminated environments drive physiological and genetic changes that maximize the survival of the stressed fish; however, acclimation has high energetic costs and is thus a short-term solution, while evolutionary responses are longer-term solutions that drive other life history changes. Using novel methodologies developed for quantifying contaminant response across levels of biological organization (molecular, cellular, physiological, behavioural, and population) in this model catfish species, we will partition the toxicological stress response into physiological and genetic adaptive components. The goal of the project is to quantify and integrate stress response measures, and generalize our results by estimating the energetic costs of adaptive contaminant responses to explicitly incorporate such costs into a bioenergetic model.We will use integrated interdisciplinary approaches to evaluating population-level effects of contaminated environments to provide regulatory recommendations for contaminated aquatic ecosystems: for example, ecosystems exhibiting primarily acclimation are likely not stable, and immediate intervention would be indicated, while ecosystems exhibiting adaptive genetic change are more stable, and longer term action plans would be appropriate.
Program
Strategic Projects - Group
Recipient
Location
Ontario, Canada
Recipient Type
Academia
Type
Grant
Source
NSERC's Awards Data
As published
Application id
350920-2007
Name nom
Heath, Daniel
Department département
Biological Sciences
Organization id
37
Institution établissement
University of Windsor
Province en
Ontario
Province fr
Ontario
Country en
CANADA
Country fr
CANADA
Fiscal year exercice financier
2007
Competition year année de concours
2007
Award amount
151000
Program id
STPGP
Program name en
Strategic Projects - Group
Program name fr
Projets stratégiques - De groupe
Group en
Research partnerships programs
Group fr
Programmes de partenariat
Committee code
1045
Committee name en
Strategic Projects Selection Panel - Environment
Committee name fr
Comité de sélection des projets stratégiques - Environnement
Area of application code
400
Area of application group en
Environment
Area of application group fr
Environnement
Area of application en
Environment
Area of application fr
Environnement
Research subject code
4700
Research subject group en
Evolution and ecology
Research subject group fr
Évolution et écologie
Research subject en
Evolution and ecology
Research subject fr
Évolution et écologie
Partie
1
Nb partie
3
Application title
Adaptive genetic and physiological responses to aquatic contaminant stress
Keyword
NA
Application summary
Canadian aquatic environments are increasingly stressed as a result of contaminant loads from industry, agriculture and urbanization. Chemicals eventually end up in aquatic environments where biological availability is high. The high level of stress in contaminated aquatic habitats will elicit an adaptive response in the resident fauna: either short-term physiological change (acclimation), genetic change driven by selection (evolution), or both. Such adaptive responses are not considered when we look for population- or ecosystem-level effects of contaminant exposure and may explain the rarity of negative population-level effects. This project examines the response of brown bullhead from contaminated and clean sites to contaminant (PAH) challenges. We propose that the energetic and survival costs of living in contaminated environments drive physiological and genetic changes that maximize the survival of the stressed fish; however, acclimation has high energetic costs and is thus a short-term solution, while evolutionary responses are longer-term solutions that drive other life history changes. Using novel methodologies developed for quantifying contaminant response across levels of biological organization (molecular, cellular, physiological, behavioural, and population) in this model catfish species, we will partition the toxicological stress response into physiological and genetic adaptive components. The goal of the project is to quantify and integrate stress response measures, and generalize our results by estimating the energetic costs of adaptive contaminant responses to explicitly incorporate such costs into a bioenergetic model.We will use integrated interdisciplinary approaches to evaluating population-level effects of contaminated environments to provide regulatory recommendations for contaminated aquatic ecosystems: for example, ecosystems exhibiting primarily acclimation are likely not stable, and immediate intervention would be indicated, while ecosystems exhibiting adaptive genetic change are more stable, and longer term action plans would be appropriate.