Structure of cryptic reef fish assemblages: relationships with habitat characteristics and predator density
By Trevor J. Willis, Marti J. Anderson. 2003
201 citations recorded by the source corpus.
Subfields: Global and Planetary Change
View Paper: https://www.semanticscholar.org/paper/f4984494e90e6395a8da3138f96220ef8cc5c88a
How researchers see this paper
The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.
In Global and Planetary Change
- Euan Harvey
- D. Watson
- Kimberly van Niel
- Cordelia Moore
- Gary A. Kendrick
- K. Nardi
- Marti J. Anderson
- J. Wraith
Citations in the corpus
- Protection from fishing alters the species composition of fish assemblages in a temperate-tropical transition zone (2007, background): “Increased abundances inside MPAs may also be related to the ability of these small fish species to utilise habitat as refuge from predators (Roberts and Ormond 1987; Beukers and Jones 1997; Willis and Anderson 2003 ).”
- The application of predicted habitat models to investigate the spatial ecology of demersal fish assemblages (2010, background): “Linking demersal Wsh assemblages to accurate and continuous benthic habitat information can be used to understand and predict the richness and abundance of these assemblages at Wne scales (Choat and Ayling 1987; Jenkins and Sutherland 1997; Jenkins and Wheatley 1998; Hyndes et al. 1999; O’Hara 200”
- Spatial prediction of demersal fish distributions: enhancing our understanding of species–environment relationships (2009, background): “However, the majority previous studies have relied upon categorical or linear descriptors of relief (Ebeling et al. 1980, Cole 1994, McCormick 1994, Friedlander & Parrish 1998, Moser et al. 1998, Babcock et al. 1999, Willis 2001, Curley et al. 2002, Westera et al. 2003, Willis & Anderson 2003).”
- Marine reserves: size and age do matter. (2008, unknown): “Thus, any response of non-commercial fishes must arise through indirect effects, such as changes in the food web (Micheli et al. 2005) or habitat availability (Willis & Anderson 2003).”
- A comparison of temperate reef fish assemblages recorded by three underwater stereo-video techniques (2005, background): “As the uses of destructive sampling techniques are, for the most part, prohibited in marine protected areas (MPAs) (Lipej et al. 2003; Willis et al. 2000; Willis and Anderson 2003 ), the application of observational techniques is widespread.”
- Spatial and temporal variation in reef fish assemblages of marine parks in New South Wales, Australia—baited video observations (2007, background): “…successfully used for a variety of applications along the continental shelf, such as monitoring the recovery of fishes in MPAs (Westera et al. 2003, Willis et al. 2003), indexing abundance of commercially important juvenile fish compared to long line catch per unit effort (Ellis & DeMartini 1995),…”