PRINCIPLES FOR THE DESIGN OF MARINE RESERVES

By L. Botsford, Fiorenza Micheli, Alan Hastings. 2003

476 citations recorded by the source corpus.

Subfields: Ecology, Global and Planetary Change

View Paper: https://www.semanticscholar.org/paper/a16edbfb1990590274b9cc3f3f810412945b778d

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Citations in the corpus

Effort distribution and catch patterns adjacent to temperate MPAs (2005, background): “These adaptations can be critically important to the achievement of management objectives, particularly if fishing effort becomes inappropriately concentrated near the boundaries owing to the effects of the closures ( Botsford et al., 2003; Halpern and Warner, 2003; Halpern et al., 2004).”
Evidence-based marine protected area planning for a highly mobile endangered marine vertebrate (2013, background): “Hence, significant gaps often remain in the design and functioning of MPAs (Agardy et al., 2011; Botsford et al., 2003; Pullin et al. 2004; Sale et al., 2005).”
Limited realized dispersal and introgressive hybridization influence genetic structure and conservation strategies for brown rockfish, Sebastes auriculatus (2005, background): “For sustaining biodiversity, it is a priority to design reserves greater than average dispersal distance so that the reserve will be selfseeding with larvae (Botsford et al. 2001, 2003).”
Modeling population connectivity by ocean currents, a graph-theoretic approach for marine conservation (2007, background): “…a methodological framework does not exist for directly incorporating dispersal connectivity in the design of an effective reserve network topology, such as the span of the network, spacing of individual sites, number of reserves, and their placement (Botsford et al. 2003; Lubchenco et al. 2003).”
Managing mobile species with MPAs: the effects of mobility, larval dispersal, and fishing mortality on closure size (2009, result): “This theoretical result contrasts with other studies that suggest that closures will not be effective for highly mobile populations ( Botsford et al., 2003; Gell and Roberts, 2003; Hilborn et al., 2004).”
Designing marine reserve networks for both conservation and fisheries management (2010, background): “Adult movement Reserves may increase yield if properly sized relative to adult movement (33).”
MARINE RESERVES AND OCEAN NEIGHBORHOODS: The Spatial Scale of Marine Populations and Their Management (2004, background): “Simple mathematical models of marine reserves show that in order for the protection afforded within a reserve to create the optimal increase in population, the neighborhood size of a species should be less than about twice the size of the reserve (27, 28).”
Importance of Metapopulation Connectivity to Restocking and Restoration of Marine Species (2008, background): “Hence, significant advances in the use of restocking and stock enhancement to conserve and restore exploited species demand examination of their potential to augment recruitment (Carr and Reed, 1993; Morgan and Botsford, 2001; Botsford et al., 2003).”
Paradigm shifts in marine fisheries genetics: ugly hypotheses slain by beautiful facts (2008, background): “…on MPAs as a tool for marine conservation, the question of realized dispersal of pelagic larvae has found renewed importance, as the function of MPAs in a regional context depends critically on the demographic exchange between the MPA and surrounding areas (Botsford et al. 2003; Palumbi 2003).”
Connectivity, sustainability, and yield: bridging the gap between conventional fisheries management and marine protected areas (2009, background): “As a result, MPAs are likely to be most effective in building up a localized spawning stock for species with low rates of juvenile and adult mobility and limited home ranges (Botsford et al. 2003).”
Spillover of spiny lobsters Palinurus elephas from a marine reserve to an adjoining fishery (2006, unknown): “…Polunin 1991, Dugan & Davis 1993, Rowley 1994, Sánchez-Lizaso et al. 2000, Côté et al. 2001, Jennings 2001, Halpern & Warner 2002), recent work highlights the meagre evidence available for protection effects outside marine protected areas (MPAs) (Botsford et al. 2003, Russ 2002, Russ et al. 2004).”
Molecular genetic structure suggests limited larval dispersal in grass rockfish, Sebastes rastrelliger (2003, background): “Understanding the magnitude and pattern of dispersal among marine populations is a key element for effective placement of management boundaries and design of marine protected area (MPA) networks ( Botsford et al. 2003 ).”
Multi-level governance for large marine commons: Politics and polycentricity in Palau's protected area network (2013, background): “While there has been a proliferation of research on the biophysical dimensions of MPA networks (e.g., Airamé et al., 2003; Botsford et al., 2003; Gaines et al., 2010; Moffitt et al., 2011; Roberts et al., 2003), there has been comparatively little research on the political and institutional…”
Abundance-distribution relationships and conservation of exploited marine fishes (2004, background): “Consideration of design, establishment and monitoring criteria for MPAs continues (NRC 2000, Botsford et al. 2003, Hastings & Botsford 2003).”