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Karlin et al. [ 22] suggested that the differences in PTS systems in different genomes are probably due to differences in habitats, lifestyle, and nutrient sources.
However, the adult Flathead Catfish does not pose a significant threat because of the differences in habitats of the two species within the river; the juvenile catfish, which share the same habitat as the shiner, may pose a larger threat.
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Although habitats differed with respect to reproductive performance, differences in habitat-specific population growth were largely due to differences in adult and first-year survival rates, as shown by a life table response experiment (LTRE).
Here we build upon this previous work to test the hypothesis that cosmopolitan marine genera and genera that are endemic to a large continental-scale region experience different macroevolutionary pressures exerted by systematic differences in habitat breadth.
While wing morphology is similar between the two lineages of bats examined in this study, more information is required to determine if differences in habitat use can account for the different extinction patterns of these two lineages.
Nevertheless, different recent studies have consistently provided evidence against differences in habitat availability, lending further support to the hypothesis that lentic species have a higher propensity for dispersal than lotic species [ 91- 93].
However, all five variables differed between red fox and bobcat sighting areas, indicating considerable differences in habitat affiliation between this pair-group.
These differences in habitat conditions present a basis for hypothesising that different provenances of N. glauca may result in different germination response and growth capacities and that most of the variation is explained by differences within provenances.
To check for differences in habitat perception by each host (e.g. different type occupancy in each site) we tested for significant differences in host densities at the vegetation classes available on each site.
Due to the differences in habitat structure, we hypothesized that belowground biocontrol services will differ between gardens and vacant lots and the influence of habitat structure would differ with the type of biocontrol organism.
These spatiotemporal differences in habitat-use should lead to complementary impacts on prey, by encouraging different predator species to attack different subsets of the prey population.
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