Abstract:The predacious invertebrate Bythotrephes longimanus has now invaded >90 freshwater lakes in North America. There is some evidence that B. longimanus has a negative effect on summer zooplankton species richness; however, no study has examined the effect of B. longimanus throughout the ice-free season in more than one lake. We visited 10 invaded and 4 reference lakes every 2 weeks from May to September, collecting B. longimanus, crustacean zooplankton, and water chemistry samples. Composite samples were poole… Show more
“…Lack of increases in phytoplankton biomass at the whole-lake scale was also observed by Lehman (1988) in Lake Michigan and by Strecker and Arnott (2008) in a subset of our lakes. In experimental mesocosms, increases in chlorophyll (phytoplankton biomass) in the presence of Bythotrephes, consistent with trophic cascades, were observed (Strecker and Arnott 2005). Conversely, Wahlströ m and Westman (1999) observed no significant effect of Bythotrephes on chlorophyll in enclosures.…”
Section: Discussionsupporting
confidence: 76%
“…1). The compositional effects of environmental variables and Bythotrephes on crustacean zooplankton and rotifer communities have been welldescribed elsewhere (Hovius et al 2006;Strecker et al 2006); please see Fig. 2 for specific relationships between variables and communities.…”
Section: Resultsmentioning
confidence: 92%
“…Zooplankton species were grouped into size classes (0-0.4, 0.4-0.8, 0.8-1.2, 1.2-1.6, and . 1.6 mm) derived from a concurrent study in a subset of our study lakes (Strecker and Arnott 2008), and they were assigned to functional groups using the classification of Barnett et al (2007) ( Table 2). Rotifers were identified to genus, and phytoplankton were identified to species but grouped at the family level for analyses (i.e., bacillariophyceae, chlorophyceae, chrysophyceae, cryptophyceae, pyrrhophyceae, cyanophyceae).…”
Section: Methodsmentioning
confidence: 99%
“…The cladoceran zooplankter Bythotrephes longimanus is an invasive predator in North America, where it occupies a mid-trophic-level position in lakes. It has had large effects on pelagic herbivore community structure, biomass, and productivity in North American lakes (Yan et al 2002;Boudreau and Yan 2003;Strecker and Arnott 2008). Based on the strong effects of this invader on herbivorous zooplankton, we would expect to see strong cascading effects on lower trophic levels, including changes in taxonomic composition, size, and structure, and functional group composition in the phytoplankton.…”
The relative importance of top-down invader effects relative to environmental drivers was determined by sampling crustacean zooplankton, rotifer, and phytoplankton communities in a set of invaded and noninvaded reference lakes. The non-native invertebrate predator Bythotrephes had significant effects on zooplankton community size structure, rotifers, and phytoplankton taxonomic composition, but no significant effects on crustacean zooplankton taxonomic and functional group composition. Part of the variation in phytoplankton communities was explained by the presence of the invader. Because Bythotrephes is generally known to be a carnivore and to not consume phytoplankton, this effect is likely mediated by the zooplankton community's response to environmental gradients. Although Bythotrephes appears to indirectly alter phytoplankton composition in invaded lakes, there was no evidence of a trophic cascade, and edible phytoplankton biovolume did not increase in invaded lakes. These complex direct and indirect interactions suggest that effects of invaders may be highly context-dependent, and therefore pose a significant challenge for predicting wider community and ecosystem responses.
“…Lack of increases in phytoplankton biomass at the whole-lake scale was also observed by Lehman (1988) in Lake Michigan and by Strecker and Arnott (2008) in a subset of our lakes. In experimental mesocosms, increases in chlorophyll (phytoplankton biomass) in the presence of Bythotrephes, consistent with trophic cascades, were observed (Strecker and Arnott 2005). Conversely, Wahlströ m and Westman (1999) observed no significant effect of Bythotrephes on chlorophyll in enclosures.…”
Section: Discussionsupporting
confidence: 76%
“…1). The compositional effects of environmental variables and Bythotrephes on crustacean zooplankton and rotifer communities have been welldescribed elsewhere (Hovius et al 2006;Strecker et al 2006); please see Fig. 2 for specific relationships between variables and communities.…”
Section: Resultsmentioning
confidence: 92%
“…Zooplankton species were grouped into size classes (0-0.4, 0.4-0.8, 0.8-1.2, 1.2-1.6, and . 1.6 mm) derived from a concurrent study in a subset of our study lakes (Strecker and Arnott 2008), and they were assigned to functional groups using the classification of Barnett et al (2007) ( Table 2). Rotifers were identified to genus, and phytoplankton were identified to species but grouped at the family level for analyses (i.e., bacillariophyceae, chlorophyceae, chrysophyceae, cryptophyceae, pyrrhophyceae, cyanophyceae).…”
Section: Methodsmentioning
confidence: 99%
“…The cladoceran zooplankter Bythotrephes longimanus is an invasive predator in North America, where it occupies a mid-trophic-level position in lakes. It has had large effects on pelagic herbivore community structure, biomass, and productivity in North American lakes (Yan et al 2002;Boudreau and Yan 2003;Strecker and Arnott 2008). Based on the strong effects of this invader on herbivorous zooplankton, we would expect to see strong cascading effects on lower trophic levels, including changes in taxonomic composition, size, and structure, and functional group composition in the phytoplankton.…”
The relative importance of top-down invader effects relative to environmental drivers was determined by sampling crustacean zooplankton, rotifer, and phytoplankton communities in a set of invaded and noninvaded reference lakes. The non-native invertebrate predator Bythotrephes had significant effects on zooplankton community size structure, rotifers, and phytoplankton taxonomic composition, but no significant effects on crustacean zooplankton taxonomic and functional group composition. Part of the variation in phytoplankton communities was explained by the presence of the invader. Because Bythotrephes is generally known to be a carnivore and to not consume phytoplankton, this effect is likely mediated by the zooplankton community's response to environmental gradients. Although Bythotrephes appears to indirectly alter phytoplankton composition in invaded lakes, there was no evidence of a trophic cascade, and edible phytoplankton biovolume did not increase in invaded lakes. These complex direct and indirect interactions suggest that effects of invaders may be highly context-dependent, and therefore pose a significant challenge for predicting wider community and ecosystem responses.
“…Bythotrephes is a voracious predator of crustacean zooplankton, capable of altering the trophic structure of lakes (Rennie et al 2011). Its invasion is routinely associated with reductions in the species richness of crustacean zooplankton and cladoceran standing stocks (Yan and Pawson 1997, Dumitru et al 2001, Boudreau and Yan 2003, Barbiero and Tuchman 2004, Strecker et al 2006, alterations in the behaviour of the zooplankton (Pangle et al 2007, Young and Yan 2008, Bourdeau et al 2011, and the displacement of native predatory invertebrates Sprules 2009, Weisz and. Bythotrephes may compete with planktivorous fish for prey (Lehman 1991, Garton et al 1993, Hoffman et al 2001, Foster and Sprules 2010, diverting energy away from higher trophic levels (Dumitru et al 2001, Strecker and Arnott 2008, Foster and Sprules 2010.…”
The invasion of the nonindigenous zooplankter Bythotrephes longimanus in Lake Simcoe has the potential to impact overall ecosystem functioning, yet there is currently no information regarding the status and dynamics of its population. We used a combination of uni-and multivariate analyses to examine variation in Bythotrephes interannual and seasonal abundance, and life-history characteristics in Lake Simcoe from 1999 to 2007, and we explored the biotic (predators, prey) and/or abiotic (water quality, temperature) factors that may have regulated its population over this period. The mean annual abundance of Bythotrephes varied by an order of magnitude over the period of study and was significantly associated with epilimnetic temperature and prey and predator abundance. Bythotrephes typically appeared in early summer and had 2 seasonal abundance peaks, which varied in magnitude and timing within and among years. August and September Secchi depth and total phosphorus concentration predicted groups of years with similar Bythotrephes phenologies, lending further support to the role of water clarity as a significant component of this visual predator's habitat in its invaded range. Bythotrephes body size and reproductive patterns also varied seasonally, possibly reflecting the seasonal availability of cladoceran prey, predation pressure from planktivorous fish, or adaptations to avoid unfavourable conditions. Overall, a complex interaction of fish predation, food availability, temperature, and water clarity controlled the dynamics of Bythotrephes in Lake Simcoe. Changes to the Lake Simcoe ecosystem due to Bythotrephes invasion may have important consequences for the ecosystem services provided by the lake and merit further investigation.
Metabolic rate is a trait that may evolve in response to the direct and indirect effects of predator‐induced mortality. Predators may indirectly alter selection by lowering prey densities and increasing resource availability or by intensifying resource limitation through changes in prey behavior (e.g., use of less productive areas). In the current study, we quantify the evolution of metabolic rate in the zooplankton
Daphnia pulicaria
following an invasive event by the predator
Bythotrephes longimanus
in Lake Mendota, Wisconsin, US. This invasion has been shown to dramatically impact
D
.
pulicaria
, causing a ~60% decline in their biomass. Using a resurrection ecology approach, we compared the metabolic rate of
D
.
pulicaria
clones originating prior to the
Bythotrephes
invasion with that of clones having evolved in the presence of
Bythotrephes
. We observed a 7.4% reduction in metabolic rate among post‐invasive clones compared to pre‐invasive clones and discuss the potential roles of direct and indirect selection in driving this change.
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