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feed on alive prey of higher trophic levels but also at lower trophic levels
(i.e. plants and detritus).
A third group was made up of herbivorous crawling benthic predators
(n
¼
34), swimming omnivorous benthopelagic (n
¼
1) and swimming pelagic
predators (n
23): this included all those species that feed on lower trophic
levels (i.e. plants and detritus).
The fourth groups were omnivorous crawling benthic predators and sca-
vengers (n
¼
¼
¼
¼
75), swimming benthopelagic (n
40), swimming pelagic (n
22)
¼
and swimming land-based (n
4) omnivorous benthic predators and scaven-
gers, which included all those species that feed on alive prey but also recently
killed prey items.
Finally, there was a fifth group that included herbivorous/detritivorous
crawling benthic grazers (n
¼
39), swimming herbivorous/detritivorous pelag-
ic grazers (n
¼
12) and sessile herbivorous/detritivorous benthic suspension
feeders (n
112).
There was not a significant relationship between a species body mass and
trophic level across all consumer species ( Figure 3 ). However, if we separated
the data using the feeding classifications listed above, it became clear that
there were certain functional groups in which a relationship exists, and others
where it was absent. The relationship between trophic level and body size
was significant in all true carnivorous predator types (carnivorous pelagic
predators r 2 : 0.46, p: 0.0056; carnivorous benthic predators r 2 : 0.49,
p: 0.0527) and in all land-based predator types (carnivorous land-based
predators r 2 : 0.49, p: 0.0453) ( Figure 4 , Table 2 ). In all other trophic types,
especially omnivorous predator/scavenger types as well as detritivorous
¼
5
4
3
2
1
- 10
0
1
Mean mass (log 10 )
Figure 3 Pairwise relationships between body mass and trophic position across all
species of the high Antarctic Weddell Sea.
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