| one publication added to basket [57417] | Predicting indirect effects of fishing in Mediterranean rocky littoral communities using a dynamic simulation model
Pinnegar, J.K.; Polunin, N.V.C. (2004). Predicting indirect effects of fishing in Mediterranean rocky littoral communities using a dynamic simulation model. Ecol. Model. 172(2-4): 249-267 In: Ecological Modelling. Elsevier: Amsterdam; Lausanne; New York; Oxford; Shannon; Tokyo. ISSN 0304-3800; e-ISSN 1872-7026, more Also appears in:Christensen, V.; Maclean, J.L. (Ed.) (2004). Placing fisheries in their ecosystem context. Ecological Modelling, 172(2-4). Elsevier: Amsterdam. 103-440 pp., more |   |
| Keywords | Marine parks
Trophic levels
Marine/Coastal |
| Authors | | Top | - Pinnegar, J.K.
- Polunin, N.V.C.
| | |
| Abstract | Modelling may significantly enhance our understanding of the potential impacts of fisheries at larger spatial scales and ongroups that would otherwise be very difficult to study. An aggregated biomass-based simulation model of a Mediterraneaninfralittoral zone was developed and used to carry out fishing ‘experiments’ where fishing intensity and catch selection werevaried. The model was constructed for the Bay of Calvi, Corsica, using the Ecopath with Ecosim software, and was composed of27 compartments, including seabirds, 11 groups of fish, 12 groups of invertebrates, 2 primary producers, bacteria and detritus.Several instances of indirect fishing effects (‘trophic cascades’ and ‘keystone predation’) have been proposed from anecdotalevidence in the western Mediterranean. Model outcomes provided little support for the widely accepted paradigm that fishing,by removing invertebrate-feeding fish, allows increases in the biomass of sea urchins and as a consequence the formation ofovergrazed ‘barrens’ of bare substrate. Simulated harvesting of sea urchins by humans did, however, results in an increase ofmacroalgal biomass as reported previously. Intensified fishing pressure on ‘macrocarnivorous’ fish resulted in a ‘release’ of smallfish species (e.g. blennies), and as a consequence a decline in the biomass of some small invertebrates on which they feed (e.g.amphipods). Increased fishing on large ‘piscivores’ resulted in increases in other small fish groups and consequential effects onother benthic invertebrate groups (e.g. polychaetes). Depletion of piscivorous fish resulted in a dramatic increase in the biomassof seabirds, which apparently compete with piscivores for small demersal and pelagic fish. An intensification of fishing pressureoverall resulted in an increase in cephalopod biomass.Responses of target species to increased fishing pressure were most marked within the first 5 years of the new fishing regime.Indirect responses exhibited varying degrees of inertia, and biomasses of many groups did not assume a new equilibrium withinthe first 20 years of the simulation.The Mediterranean infralittoral rocky-bottom ecosystem was predicted to be relatively resilient to pulses of increased fishingand exhibited a high degree of detritus recycling. However, the speed and magnitude of ecosystem responses was shown todepend greatly on the extent of ‘top-down’ or ‘bottom-up’ control assumed for components within the system. |
|
