Grant: Discovery Grants Program - Individual
University of New Brunswick
$50,000.00
Effects of nutrient cycling on contaminant fate in aquatic food webs
FY 2016-17
Summary
There is ongoing global concern about increasing anthropogenic releases of mercury (Hg) because it is deposited into aquatic systems, transformed by bacteria to methyl Hg (MeHg), and biomagnified (increases in concentration from prey to predator) through aquatic food chains to concentrations that may be toxic for fish-eating consumers or the fish themselves. Stable nitrogen isotopes (delta15N) are commonly used to understand the relative trophic position of aquatic organisms and the rate at which contaminants such as Hg are transferred through food webs. In diverse ecosystems, mercury concentrations in aquatic biota are significantly and positively related to their delta15N, but the rate (slope) of this transfer varies across systems for reasons that remain unexplained. The fate of Hg in aquatic systems is linked to the abiotic and biotic cycling of sulphur. Methyl Hg binds to the S-containing amino acid cysteine for uptake into bacteria and for storage in proteins of fish and plants. Although little information exists for aquatic food webs, terrestrial organisms at high trophic levels contain the greatest amounts of cysteine in their proteins, and cysteine content in plants is affected by water chemistry. This suggests that cysteine content of organisms varies in aquatic food webs and across systems, perhaps explaining among-system differences in Hg biomagnification. The next five years of my NSERC Discovery program will continue to refine our understanding of the food web processes affecting contaminant transfer through aquatic ecosystems. Both within and across lakes and streams that vary in their chemical characteristics (high through low nutrients; acidic through near neutral pH), we will examine whether MeHg in primary consumers is predicted by their cysteine content, and whether cysteine is better predictor of the food web transfer of MeHg than delta15N. Results will be used to develop and refine models to better describe among-system variability in concentrations of this contaminant, and to contrast this process in systems that vary in their chemical, physical and biological characteristics.
Program
Discovery Grants Program - Individual
Recipient
Location
New Brunswick, Canada
Recipient Type
Academia
Type
Grant
Source
NSERC's Awards Data
As published
Application id
312237-2012
Name nom
Kidd, Karen
Department département
Biology (Saint John)
Organization id
75
Institution établissement
University of New Brunswick
Province en
New Brunswick
Province fr
Nouveau-Brunswick
Country en
CANADA
Country fr
CANADA
Fiscal year exercice financier
2016
Competition year année de concours
2012
Award amount
50000
Program id
RGPIN
Program name en
Discovery Grants Program - Individual
Program name fr
Programme de subventions à la découverte - individuelles
Group en
Discovery grants programs
Group fr
Programmes de subventions à la découverte
Committee code
1503
Committee name en
Evolution and Ecology
Committee name fr
Évolution et écologie
Area of application code
1002
Area of application group en
Northern development
Area of application group fr
Développement du nord
Area of application en
Environment
Area of application fr
Environnement
Research subject code
4705
Research subject group en
Evolution and ecology
Research subject group fr
Évolution et écologie
Research subject en
Ecotoxicology
Research subject fr
Écotoxicologie
Partie
5
Nb partie
7
Application title
Effects of nutrient cycling on contaminant fate in aquatic food webs
Keyword
NSERC
Application summary
There is ongoing global concern about increasing anthropogenic releases of mercury (Hg) because it is deposited into aquatic systems, transformed by bacteria to methyl Hg (MeHg), and biomagnified (increases in concentration from prey to predator) through aquatic food chains to concentrations that may be toxic for fish-eating consumers or the fish themselves. Stable nitrogen isotopes (delta15N) are commonly used to understand the relative trophic position of aquatic organisms and the rate at which contaminants such as Hg are transferred through food webs. In diverse ecosystems, mercury concentrations in aquatic biota are significantly and positively related to their delta15N, but the rate (slope) of this transfer varies across systems for reasons that remain unexplained. The fate of Hg in aquatic systems is linked to the abiotic and biotic cycling of sulphur. Methyl Hg binds to the S-containing amino acid cysteine for uptake into bacteria and for storage in proteins of fish and plants. Although little information exists for aquatic food webs, terrestrial organisms at high trophic levels contain the greatest amounts of cysteine in their proteins, and cysteine content in plants is affected by water chemistry. This suggests that cysteine content of organisms varies in aquatic food webs and across systems, perhaps explaining among-system differences in Hg biomagnification. The next five years of my NSERC Discovery program will continue to refine our understanding of the food web processes affecting contaminant transfer through aquatic ecosystems. Both within and across lakes and streams that vary in their chemical characteristics (high through low nutrients; acidic through near neutral pH), we will examine whether MeHg in primary consumers is predicted by their cysteine content, and whether cysteine is better predictor of the food web transfer of MeHg than delta15N. Results will be used to develop and refine models to better describe among-system variability in concentrations of this contaminant, and to contrast this process in systems that vary in their chemical, physical and biological characteristics.