Comparative analysis of trophic structure of commercial fishery species off Central Chile in 1992 and 1998

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Abstract

Trophic interactions and community structure of commercial fishery species off Central Chile (33°–39°S) were analyzed and compared for 1992 and 1998 by ecotrophic modelling, using the Ecopath modelling software. The model encompasses the fishery, pinnipeds (sea lions), small pelagic fish (anchovy, pilchard), medium-sized pelagic fish (horse mackerel), demersal fish (e.g. Chilean hake, black conger), benthic invertebrates (carrot prawn, yellow prawn), and other groups such as zooplankton, phytoplankton, and detritus. Input information for the model was gathered from published and unpublished reports and our own estimates. Also, the effects of fishing and predation on fishery resources and on the most important components of the system were investigated, within an ecotrophic framework.

Predators consumed the greater part of the production of the most important fishery resources, particularly juvenile stages, and the fishery removed a large fraction of adult production. Mortality by predation is an important component of natural mortality, especially in recruit and prerecruit groups. Analysis of direct and indirect trophic impact shows that adult Chilean hake have a negative impact on juvenile Chilean hake through cannibalism, and on pilchard, anchovy, and carrot prawn through predation. Also, fishing has a strong impact on fishery resources, such as Chilean hake, pilchard, and anchovy. Total biomass in 1998 was 1.5 times higher than in 1992. However, total catches in 1998 were about 80% of those in 1992. Changes in biomass and total yields of the system between 1992 and 1998 can be observed in such properties as total flows, consumption, respiration, and production. It is concluded that ecotrophic modelling is an useful tool for fishery management, since it can improve our understanding of the predator–prey interactions among the exploited (fishery resources) and unexploited but potential fishery resources of the system.

Introduction

Although short-term fishery management objectives may be partially fulfilled in the absence of ecosystem information, long-term strategies necessarily require placing fisheries in their ecosystem context, that is by incorporating knowledge of interspecific interactions of both exploited and unexploited populations, their physical environment and their habitat (Christensen et al., 1996, Sinclair et al., 1997).

The Humboldt Current system of Central Chile is a typical upwelling ecosystem that sustains some of the most productive fisheries of the world (FAO, 1995) due to coastal upwelling (Vergara, 1992).

Arancibia, 1989, Arancibia, 1992 and Quiñones et al. (1997), analyzed interspecific relationships between fishery resources and their prey in Central Chile, and concluded that most species that are fishery resources play important ecological roles in the marine system. Nonetheless, research on the trophic relationships between the main components, such as Chilean hake (Merluccius gayi) and horse mackerel (Trachurus symmetricus), have been both sporadic and short-term (Arancibia, 1987, Arancibia, 1991, Miranda et al., 1998). Additionally, some species that are not fishery resources could have important roles as either predators or preys (Neira and Arancibia, 2000).

Since the early 1980’s, the development and later westward expansion of an important purse-seine horse mackerel fishery has influenced total landing in Central Chile. During the 1990’s horse mackerel landings ranged from 2.4 million tonnes to a historical maximum of more than 4 million tonnes in 1995 (Fig. 1a). During 1997–1998, remarkable changes occurred in the length structure of jack mackerel catches, as juveniles dominated the fishing grounds. This has been attributed to both the entrance of one or two strong year classes and changes in oceanographic conditions associated with the ENSO event of 1997–1998 (Cubillos et al., 1999, Arcos et al., 2001). The dramatic drop in horse mackerel landings in the later years was accompanied by an increasing trend in landings of other important fishery resources, such as Chilean hake, pilchard (Strangomera bentincki), and anchovy (Engraulis ringens) (Fig 1b). The ecosystem effects of these changes in landings of the most important fishery resources—especially those of horse mackerel—are still poorly understood in Central Chile.

Consequently, the objective of this paper is to investigate changes in the trophic interactions and the community structure of the Central Chile marine ecosystem (33°–39°S) between early 1990’s—when the horse mackerel fishery was plenty—and late 1990’s—when the horse mackerel fishery had collapsed. To accomplish this objective, we constructed two mass-balanced ecotrophic models summarizing biomass, catches and production of the main trophic groups, with emphasis on fishery resources in the Central Chile marine ecosystem in 1992 and 1998.

Section snippets

Materials and methods

The study area is located off Central Chile (33°–39°S) and extends 65 km offshore, covering a total surface area of 50,042 km2 (Fig. 2). The area defined is the main fishing ground of both the purse-seine and the trawling industrial fishing fleets.

To reduce the time-scale limitations of the mass-balance model Ecopath (Christensen and Pauly, 1992a), changes have been analyzed in one-year periods. The analyses covered the years 1992 and 1998 as the best records were available for those years.

The

Results

Table 2, Table 3 summarize the input parameters and the results of the balanced ecotrophic model for the Central Chile marine ecosystem in 1992 and 1998. Table 4 shows the diet matrices for the predators in the system for both years. Overall, pelagic species such as horse mackerel, pilchard, and anchovy dominated the system. Chilean hake was the dominant species in the demersal environment.

Closer examination shows changes in both biomass and yields for the main groups between 1992 and 1998 (

Discussion

Fish and other fishery resources have trophic pathways with differing lengths for their sustenance (Fig. 4) and, like all groups in the ecosystem, have more than one predator and more than one kind of prey (Wyatt, 1976). This is an important point, since both competition and predation have been reported as biological interactions that can potentially decrease the biomass of species of economic importance (Lalli and Parsons, 1993, Sinclair et al., 1997). For instance, Chilean hake, horse

Acknowledgements

We thank M. George Nascimento and R. Pinochet, for valuable information for the modelling. We are grateful to the EU INCO-DC concerted action ERBIC18CT97175 through which funding was provided for a workshop in Brazil in 1998 and the symposium at Galapagos in 2000, where the authors were able to improve their model, interpret and analyze the results, and present these to colleagues. We also thank Dr. G. Rocha and two anonymous referees for their comments and suggestions for an earlier draft of

References (38)

  • D.F Arcos et al.

    The jack mackerel fishery and El Nino 1997–1998 effects off Chile

    Prog. Oceanogr.

    (2001)
  • V Christensen et al.

    ECOPATH II. A software for balancing steady state ecosystem models and calculating network characteristics

    Ecol. Model.

    (1992)
  • M Wolff

    A trophic model for Tongoy Bay. A system exposed to suspend scallop culture (Northern Chile)

    J. Exp. Mar. Biol. Ecol.

    (1994)
  • K.R Allen

    Relation between production and biomass

    J. Fish. Res. Bd. Canada

    (1971)
  • H Arancibia

    Alimentación de peces concurrentes en la pesquerı́a de Pleuroncodes monodon Milne Edwards

    Investigación Pesquera (Chile)

    (1987)
  • Arancibia, H., 1989. Distribution Patterns, Trophic Relationships and Stock Interactions in the Demersal Fish...
  • H Arancibia

    Análisis ecológico-pesquero del recurso langostino colorado (Pleuroncodes monodon) y su interacción con merluza común (Merluccius gayi) y lenguado de ojos grandes (Hipoglossina macrops)

    Biologı́a Pesquera (Chile)

    (1991)
  • H Arancibia

    Distribution patterns of the demersal fish assemblage off Central Chile

    Biologı́a Pesquera (Chile)

    (1992)
  • H Arancibia et al.

    Análisis de la alimentación de Merluccius gayi gayi (Guichenot, 1848) de Chile central, en el largo plazo

    Biologı́a Pesquera (Chile)

    (1993)
  • Arancibia, H., Catrilao, M., Farı́as, B., 1998. Evaluación de la demanda de alimento en merluza común y análisis de su...
  • A Arrizaga et al.

    Hábitos tróficos de dos especies de peces pelágicos: Strangomera bentincki (Norman, 1936) y Engraulis ringens Jenyns, 1842 en el litoral de la Región del Bio-Bio, Chile

    Bol. Soc. Biol. Concepción, Chile

    (1993)
  • N.J Bax

    A comparison of the fish biomass flow to fish, fisheries, and marine mammals in six marine ecosystems

    ICES Mar. Sci. Symp.

    (1991)
  • N.J Bax

    The significance and prediction of predation in marine fisheries

    ICES J. Mar. Sci.

    (1998)
  • Christensen, V., Pauly, D., 1992b. A Guide to the ECOPATH II Program (Version 2.1) ICLARM Software 6, 72...
  • V Christensen et al.

    Fish production, catches and the carrying capacity of the world oceans

    Naga

    (1995)
  • N Christensen et al.

    Report of the Ecological Society of American Committee on the scientific basis for ecosystem management

    Ecol. Applic.

    (1996)
  • Christensen, V., Walters, C.J., Pauly, D. 2000. Ecopath with Ecosim: A User’s Guide. Fisheries Centre, University of...
  • Córdova, J., Barbieri, M.A., Miranda, H., Espejo, M., Rojas, M., Núñez, S., Ortiz, J., Catasti, V., Valenzuela, V.,...
  • Cubillos, L., Sepúlveda, A., Gálvez, M., Arcos, D., 1999. Situación actual de los principales recursos pesqueros de la...
  • Cited by (0)

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