Copepoda source details

Symons, C.C., M.T. Pedruski, S.E. Arnott & J.N. Sweetman. (2014). Spatial, Environmental, and Biotic Determinants of Zooplankton Community Composition in Subarctic Lakes and Ponds in Wapusk National Park, Canada. Arctic, Antarctic, and Alpine Research. 46(1):159–190.
515062
10.1657/1938-4246-46.1.159 [view]
Symons, C.C., M.T. Pedruski, S.E. Arnott & J.N. Sweetman
2014
Spatial, Environmental, and Biotic Determinants of Zooplankton Community Composition in Subarctic Lakes and Ponds in Wapusk National Park, Canada.
Arctic, Antarctic, and Alpine Research
46(1):159–190.
Publication
Available for editors  PDF available [request]
Northern regions are expected to experience large environmental change over the next few decades. The response of biota will depend on changes in the local environment, regional processes that in?uence lake connectivity, and species interactions. In 2008, we surveyed 92 lakes and ponds across Wapusk National Park, located on the southwestern shore of Hudson Bay. At each site we assessed water chemistry and zooplankton community composition. In an effort to understand how the aquatic ecosystems will respond to future environmental change, we determined local characteristics (e.g., water chemistry), regional spatial factors (e.g., dispersal), and biotic interactions (e.g., species associations) in?uencing community composition. Important environmental variables included lake area, pH, ionic composition, total phosphorus, and chlorophyll a; however, spatial variables explained more variation than environmental variables, suggesting that dispersal is an important driver of zooplankton composition in this region. Additionally, species exhibited negative co-occurrence patterns, suggesting biotic interactions are important in structuring the zooplankton communities. As environmental conditions change and the distribution of habitat (i.e., coastal fen, interior peatland, and spruce forest) shifts, evidence that the park’s zooplankton community is spatially structured coupled with our suspicion that zooplankton are likely to experience high dispersal levels in Wapusk leads us to suggest zooplankton may indeed be able to track changing environmental conditions within the park, although it remains unclear how species interactions will modify this expectation.
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Acanthocyclops robustus (Sars G.O., 1863) represented as Acanthocyclops robustus robustus (Sars G.O., 1863) (additional source)
Cyclops scutifer Sars G.O., 1863 represented as Cyclops scutifer scutifer Sars G.O., 1863 (additional source)
Diacyclops navus (Herrick, 1882) (additional source)
Diacyclops thomasi (Forbes S.A., 1882) (additional source)
Diaptomus (Hesperodiaptomus) novemdecimus Wilson M.S., 1953 accepted as Hesperodiaptomus novemdecimus Wilson M.S., 1953 (additional source)
Diaptomus nudus Lilljeborg in Guerne & Richard, 1889 accepted as Leptodiaptomus nudus (Marsh, 1904) (additional source)
Diaptomus wilsonae Reed, 1958 accepted as Hesperodiaptomus wilsonae (Reed, 1958) (additional source)
Epischura lacustris Forbes S.A., 1882 (additional source)
Eucyclops serrulatus (Fischer, 1851) represented as Eucyclops serrulatus serrulatus (Fischer, 1851) represented as Eucyclops (Eucyclops) serrulatus (Fischer, 1851) represented as Eucyclops (Eucyclops) serrulatus serrulatus (Fischer, 1851) (additional source)
Hesperodiaptomus arcticus (Marsh, 1920) (additional source)
Heterocope septentrionalis Juday & Muttkowski, 1915 (additional source)
Leptodiaptomus minutus (Lilljeborg in Guerne & Richard, 1889) (additional source)
Leptodiaptomus tyrrelli (Poppe, 1888) (additional source)
Microcyclops rubellus (Lilljeborg, 1901) represented as Microcyclops (Microcyclops) rubellus (Lilljeborg, 1901) (additional source)
Skistodiaptomus oregonensis (Lilljeborg in: Guerne & Richard, 1889) (additional source)