Apparent changes in the trophic composition of world marine harvests: the perspective from the FAO capture database

Abstract Almost 50 yr of global multispecies harvests are represented in the FAO capture production database, and offer a broad perspective on events that underlie the major observed changes in global marine harvests. The likely relevance of top–down and bottom–up trophic interactions, versus the impacts of changes in fishing technology and markets on the trophic level of landings, are discussed on a regional basis. Despite the low resolution of this global data set, several common features emerge. Rapid increases in fleet size and technological advance, and imperfect fisheries management measures, are probably responsible for declines in peak multispecies production in many areas since the 1970s, and internal evidence suggests that peak production is not far away in the remainder. Staggered dates of peak landings in different world areas seem to reflect the spread of industrial fishing fleets from `core areas’ to the rest of the world's oceans, which largely took place from the 1960s to 1990s. A general move to higher exploitation of piscivores in global landings is implied in some areas. The hypothesis that top–down removal of predators is affecting lower trophic production is however only one explanation for declining mean trophic levels, and is more likely to emerge from local food web studies. In some regions an increased proportion of short-lived invertebrates in harvests later in the time series supports a move downwards in trophic level targeting. In the North Atlantic and some other areas, fishing down marine food webs may be a likely cause of the increase in landings of shelf planktivores. A shift from depleted apical resources to species lower in the food web may have been made on economic grounds however, independent of possible effects of a release of predatory pressure. Sharp increases in planktivores later in the time series show up in the Eastern Central Atlantic and in the Southeast Pacific and do not appear to be primarily related to depletion of predators. They seem to reflect intermittent strength of upwelling systems, and hence bottom–up effects on food web production, together with changes in harvest technology. For some areas, piscivore landings increased later in the time series than those of planktivores. In the Mediterranean, this seems mainly a bottom–up response to increased marine productivity associated with land run-off and consequent improvements in predatory foraging. In some tropical areas, later increases in piscivorous landings mainly result from expansion of distant water tuna fleets, and are probably unrelated to exploitation of forage fishes. The technological revolution of the 1950s and 1960s involved rapid application of synthetic fibres to improved gear. This led to large-scale mid-water trawling and purse seining by industrial fleets and has especially increased vulnerability of small pelagic stocks over the last few decades. This appears mainly responsible for the apparent decline in mean trophic level of harvests in areas with large stocks of these resources. From an analysis of variances of the sample data set, `Punctuated equilibrium', involving actual changes in ecosystems, rather than just continuous change in the relative harvest rates of species in a given ecosystem, is suggested as an important phenomenon, reflecting both ecological change and changing exploitation strategies.

[1]  R. Beverton,et al.  The fisheries resources of the Mediterranean , 1985 .

[2]  R. O’Driscoll Feeding and schooling behaviour of barracouta (Thyrsites atun) off Otago, New Zealand , 1998 .

[3]  Villy Christensen,et al.  ECOPATH II − a software for balancing steady-state ecosystem models and calculating network characteristics , 1992 .

[4]  R. Mahon Fishery management options for Lesser Antilles countries (Antigua and Barbuda, Barbados, Dominica, Grenada, Saint Kitts and Nevis, Saint Lucia, Saint Vincent and the Grenadines). , 1990 .

[5]  D. Pauly,et al.  Fishing down marine food webs , 1998, Science.

[6]  D. Pauly Theory and management of tropical multispecies stocks: a review, with emphasis on the Southeast Asian demersal fisheries , 1979 .

[7]  D. L. Alverson A global assessment of fisheries bycatch and discards , 1994 .

[8]  Toyomi Takahashi,et al.  Food Habits of Walleye Pollock Inhabiting the Mesopelagic Zone in the Northern Japan Sea in Spring and Autumn , 1997 .

[9]  J. Csirke,et al.  How Pervasive is "Fishing Down Marine Food Webs"? , 1998 .

[10]  G. Kruse Proceedings of the International Symposium on Management Strategies for Exploited Fish Populations, October 21-24, 1992, Anchorage, Alaska , 1993 .

[11]  Daniel Pauly,et al.  The Peruvian upwelling ecosystem: dynamics and interactions , 1989 .

[12]  J. F. Caddy,et al.  Toward a comparative evaluation of human impacts on fishery ecosystems of enclosed and semi‐enclosed seas , 1993 .

[13]  Claude Roy,et al.  Global versus local changes in upwelling systems , 1998 .

[14]  J. Caddy,et al.  An Ecological Framework for Marine Fishery Investigations , 1987 .

[15]  Y. Ishida,et al.  Change in chum salmon (Oncorhynchus keta) stomach contents associated with fluctuation of pink salmon (O. gorbuscha) abundance in the central subarctic Pacific and Bering Sea , 1996 .

[16]  J. Caddy Marine catchment basin effects versus impacts of fisheries on semi-enclosed seas , 2000 .

[17]  I. Nakamura,et al.  Fao Species Catalogue , 1972 .

[18]  D. Kitagawa,et al.  Diets of the demersal fishes on the shelf off Iwate, northern Japan , 1995 .

[19]  Napp,et al.  Contrasting years of prey levels, feeding conditions and mortality of larval walleye pollock Theragra chalcogramma in the western Gulf of Alaska , 1995 .

[20]  P. Spencer,et al.  Patterns of population variability in marine fish stocks , 1997 .

[21]  J. Boreman Northwest Atlantic groundfish : perspectives on a fishery collapse , 1997 .

[22]  T. P. Barnett,et al.  Causes of Decadal Climate Variability over the North Pacific and North America , 1994, Science.

[23]  A. Lombarte,et al.  Influence of Benguela upwelling on the structure of demersal fish populations off Namibia , 1990 .

[24]  Quay Dortch,et al.  Nutrient changes in the Mississippi River and system responses on the adjacent continental shelf , 1996 .

[25]  J. Caddy,et al.  Have Peak Fishery Production Levels beenPassed in Continental Shelf Area? Some Perspectives Arising from Historical Trends in Production per Shelf Area , 1998 .

[26]  L. Jacobson,et al.  Regimes and stock-recruitment relationships in Japanese sardine (Sardinops melanostictus), 1951-1995 , 1998 .

[27]  F. Thurow Estimation of the total fish biomass in the Baltic Sea during the 20th century , 1997 .

[28]  J. Caddy,et al.  Is the pelagic-demersal ratio from fishery landings a useful proxy for nutrient availability? A preliminary data exploration for the semi-enclosed seas around Europe , 2000 .

[29]  J. Caddy,et al.  Productivity estimates for the Mediterranean: evidence of accelerating ecological change , 1995 .

[30]  R. Elst,et al.  A guide to the common sea fishes of southern Africa , 1981 .

[31]  D. Cushing The decline of the herring stocks and the gadoid outburst , 1980 .

[32]  W. Wooster,et al.  Year‐to‐year variations in Bering Sea ice cover and some consequences for fish distributions , 1998 .

[33]  J. A. Gulland,et al.  Historical patterns of fish stocks , 1983 .

[34]  Y. Zaitsev,et al.  Recent changes in the trophic structure of the Black Sea , 1992 .

[35]  P. Cury,et al.  The recruitment of the Chilean sardine ( Sardinops sagax ) and the "optimal environmental window" , 1998 .

[36]  S. Kifani Climate dependent fluctuations of the Moroccan sardine and their impact on fisheries , 1998 .

[37]  S. Levitus,et al.  Structure and Cycle of Decadal Variability of Upper-Ocean Temperature in the North Pacific , 1997 .

[38]  K. Radway Allen,et al.  Proceedings of the International Symposium on Management Strategies for Exploited Fish Populations , 1996 .

[39]  D. A. Dwyer,et al.  Feeding Habits and Daily Ration of Walleye Pollock (Theragra chalcogramma) in the Eastern Bering Sea, with Special Reference to Cannibalism , 1987 .

[40]  G. Sharp,et al.  FISHERIES, EL NI1KIo-SOUTHERN OSCILLATION AND UPPER-OCEAN TEMPERATURE RECORDS: AN EASTERN PACIFIC EXAMPLE , 1993 .

[41]  V. Christensen,et al.  Comparative modelling of trophic flows in four large upwelling ecosystems : global versus local effects , 1998 .

[42]  P. Fréon,et al.  Sardinella aurita population dynamics related to environmental parameters in the Southern Caribbean (Venezuela) , 1998 .

[43]  R. J. M. Crawford,et al.  Food and population variability in five regions supporting large stocks of anchovy, sardine and horse mackerel , 1987 .

[44]  R. May,et al.  Stability and Complexity in Model Ecosystems , 1976, IEEE Transactions on Systems, Man, and Cybernetics.

[45]  A. E. Caton,et al.  Review of aspects of Southern bluefin tuna biology, population, and fisheries , 1994 .

[46]  B. Collette,et al.  FAO species catalogue. Volume 2. Scombrids of the world. An annotated and illustrated catalogue of tunas, mackerels, bonitos and related species known to date. , 1983 .