2016
DOI: 10.1371/journal.pone.0157861
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Structure of Mesophotic Reef Fish Assemblages in the Northwestern Hawaiian Islands

Abstract: Mesophotic coral ecosystems (MCEs) support diverse communities of marine organisms with changes in community structure occurring along a depth gradient. In recent years, MCEs have gained attention due to their depths that provide protection from natural and anthropogenic stressors and their relative stability over evolutionary time periods, yet ecological structures of fish assemblages in MCEs remain largely un-documented. Here, we investigated composition and trophic structure of reef fish assemblages in the … Show more

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Cited by 47 publications
(46 citation statements)
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“…temperature, hydrodynamics, and sedimentation could also affect the distribution of organisms in mesophotic depths, these remain unaddressed in the scope of this work (Locker et al, 2010;Kahng et al, 2014). Community shifts similar to patterns observed in other tropical (e.g., Red Sea, Marshall Islands, Puerto Rico, Honduras) and sub-tropical ecosystems, (e.g., South Africa, NWHI), included declines in herbivore abundance with depth, even in mesophotic habitats hosting high levels of macroalgal cover (Thresher and Colin, 1986;Feitoza et al, 2005;Brokovich et al, 2010;Bejarano et al, 2014;Kane et al, 2014;Andradi-Brown et al, 2016;Fukunaga et al, 2016). While planktivore relative abundance and richness measures were relatively similar across depth strata (Figure 6B), their proportional abundances was highest in the lower mesophotic zone (Figure S1), aligning with depth-based planktivore density and/or biomass peaks recorded in other mesophotic studies (Thresher and Colin, 1986;Feitoza et al, 2005;Fukunaga et al, 2016).…”
Section: Discussionmentioning
confidence: 75%
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“…temperature, hydrodynamics, and sedimentation could also affect the distribution of organisms in mesophotic depths, these remain unaddressed in the scope of this work (Locker et al, 2010;Kahng et al, 2014). Community shifts similar to patterns observed in other tropical (e.g., Red Sea, Marshall Islands, Puerto Rico, Honduras) and sub-tropical ecosystems, (e.g., South Africa, NWHI), included declines in herbivore abundance with depth, even in mesophotic habitats hosting high levels of macroalgal cover (Thresher and Colin, 1986;Feitoza et al, 2005;Brokovich et al, 2010;Bejarano et al, 2014;Kane et al, 2014;Andradi-Brown et al, 2016;Fukunaga et al, 2016). While planktivore relative abundance and richness measures were relatively similar across depth strata (Figure 6B), their proportional abundances was highest in the lower mesophotic zone (Figure S1), aligning with depth-based planktivore density and/or biomass peaks recorded in other mesophotic studies (Thresher and Colin, 1986;Feitoza et al, 2005;Fukunaga et al, 2016).…”
Section: Discussionmentioning
confidence: 75%
“…Mesophotic reef fish community breaks have been proposed at ∼60 m (Slattery et al, 2011;Fukunaga et al, 2016), with community, functional group, and assessed environmental structural outputs generally supporting this premise. However, community compositions were largely distinct between shallow water and upper mesophotic zones, indicating the potential for depth-based refugia may be limited to depth-generalists and not depth-zone specialists, e.g., specific mobile invertivores and generalist macropiscivores that are equally, if not more abundant in 30-53 than in <30 m, with the possibility of refugia further declining when transitioning to more comparably depauperate lower mesophotic communities.…”
Section: Discussionmentioning
confidence: 91%
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