Intertidal seawalls—new features of landscape in intertidal environments

By M. Chapman, F. Bulleri. 2003

294 citations recorded by the source corpus.

Subfields: Ecology, Management, Monitoring, Policy and Law, Oceanography

View Paper: https://www.semanticscholar.org/paper/4e176da9a82f32087b3fc87101ef061c1f878d5c

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Citations in the corpus

Ecology of freshwater shore zones (2010, background): “Surface topography determines the availability of micro-and mesohabitats in the shore zone, some of which (e.g., crevices, supralittoral pools) are hot spots for biodiversity and biogeochemical processing (e.g., Pieczyn´ska 1972; Chapman and Bulleri 2003; Le Hir and Hily 2005).”
Sydney Harbour: a review of anthropogenic impacts on the biodiversity and ecosystem function of one of the world’s largest natural harbours (2015, background): “Furthermore,,22% of the total 50 km2 area of the estuary has been reclaimed, mainly for industrial, recreational and residential uses (Birch 2007) and more than 50% of the shoreline has been replaced with artificial structures such as seawalls (Chapman and Bulleri 2003).”
Drill-cored rock pools: An effective method of ecological enhancement on artificial structures (2016, background): “2013b) and different relative abundances of taxa (Chapman and Bulleri 2003; Pinn et al. 2005; Moschella et al. 2005) compared with adjacent rocky shores.”
The importance of water‐retaining features for biodiversity on artificial intertidal coastal defence structures (2013, background): “Despite the potential for these structures to provide habitat, they generally support lower biodiversity than adjacent natu-ral rocky habitats (Chapman & Bulleri, 2003; Moschella et al. , 2005; Pister, 2009).”
Seawalls do not sustain viable populations of limpets (2006, methodology): “Egg-ribbons and all Siphonaria denticulata were counted and measured in 5 random quadrats (25 cm alongshore and 20 cm upshore) at each site (Chapman & Bulleri 2003).”
Intertidal assemblages on artificial and natural habitats in marinas on the north-west coast of Italy (2004, background): “Even though artificial and natural habitats can be composed of the same material, they do not necessarily support similar assemblages of intertidal organisms ( Chapman and Bulleri 2003 ).”
Paucity of mobile species on constructed seawalls: effects of urbanization on biodiversity (2003, methodology): “The vertical extent of different assemblages on seawalls is small because of the relatively small tidal range in Sydney Harbour.”
Urban marine ecology in southern California: the ability of riprap structures to serve as rocky intertidal habitat (2009, background): “Chapman and Bulleri (2003) found just such a situation on seawalls, where intertidal communities displayed diVerences at high and mid-shore levels, but not at lower levels.”