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Please use this identifier to cite or link to this item: http://hdl.handle.net/11375/31042
Title: Effects of Forestry and Beaver Reservoirs on Mercury Dynamics in Boreal Stream Food Webs
Authors: Lajoie, Celine Marie Emanuelle
Advisor: Kidd, Karen
Department: Biology
Keywords: Mercury;Forestry;Beaver;Boreal
Publication Date: 2025
Abstract: Mercury (Hg) binds to organic matter (OM) within boreal forest soils. Land disturbances, such as forest harvesting, alter the export of OM and nutrients to nearby streams. This can affect the structure of stream communities and their food webs by changes to basal resource availability, and consumer reliance on these resources. It may also impact the uptake and biomagnification of Hg within streams. Beaver impoundments often co-occur with forestry and can similarly influence Hg in streams. However, their combined effects are unknown. Most research on the effects of forest harvesting on Hg have focused on abiotic factors with little attention given to Hg dynamics in food webs, particularly in Canada’s boreal. This thesis examined the effects of forest harvest on macroinvertebrate communities and leaf litter decomposition (Chapter 2), and on Hg bioaccumulation and biomagnification temporally and regionally across streams (Chapter 3) and upstream and downstream of beaver reservoirs in harvested and non-harvested landscapes (Chapter 4). In Chapter 2, no effects of harvest on leaf litter decomposition were observed, yet results suggested that effects on macroinvertebrate communities within harvested landscapes were site-specific and most severe (i.e., declines in diversity, evenness, and in sensitive taxa) in streams with narrow buffer zones and higher amounts of harvest within their watershed. Chapter 3 showed that Hg concentrations ([Hg]) in macroinvertebrates were elevated in harvested landscapes, likely because of higher [Hg] in food sources, and that streams afforded less protection are at greater risk of increased [Hg] in water and consumers. Chapter 4 revealed that while [Hg] of consumers and biomagnification rates were elevated in harvested landscapes upstream of reservoirs, they did not persist downstream, indicating that effects of reservoirs and harvest were not additive, and were instead site-specific. This thesis provides novel and impactful information on Hg cycling and may assist foresters to develop guidelines to minimize Hg risk to stream ecosystems.
URI: http://hdl.handle.net/11375/31042
Appears in Collections:Open Access Dissertations and Theses

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