The global wild marine fish harvest increased fourfold between 1950 and a peak value near the end of the 20th century, reflecting interactions between anthropogenic and ecological forces. Here, we examine these interactions in a bio-energetically constrained, spatially and temporally resolved model of global fisheries. We conduct historical hindcasts with the model, which suggest that technological progress can explain most of the 20th century increase of fish harvest. In contrast, projections extending this rate of technological progress into the future under open access suggest a long-term decrease in harvest due to over-fishing. Climate change is predicted to gradually decrease the global fish production capacity, though our model suggests that this is of secondary importance to social and economic factors. Our study represents a novel way to integrate human-ecological interactions within a single model framework for long-term simulations.
The global capture of wild marine ‘fish’ (including edible invertebrates, as well as true fish) appears to have peaked in the 1990s, according to a recent reconstruction1 (Fig. 1a), despite continued increases in the effort expended by the global fishery2 (Fig. 1b). The increasingly intense fishing pressure has driven marine fish biomass to a fraction of its pristine state (Fig. 1c), a depletion that is widely believed to be limiting fishing yields in many parts of the world2,3,4. These historical trends reflect the interplay of ecosystem dynamics, the demand for fish, the cost of fishing, improvements of fishing technology and climate change1,3,5,6,7, all of which will play a role in future8,9,10, but whose relative roles have been difficult to formally assess.
Here we quantitatively address the multiple influences in the global fishery, and their interactions, by explicitly including human activity within an Earth System modelling framework, and using simulation protocols typically used for climate simulations. We use the BiOeconomic mArine Trophic Size-spectrum (BOATS) model, a bio-energetically constrained macroecological-life-history fish model that is coupled directly with an economic model11,12 (Methods, see Supplementary Methods for details). The BOATS model builds on prior works that took regional13, species-specific or unidirectional coupling approaches14,15 by introducing a comprehensive two-way coupling of human and natural components of the system, using relatively simple but well-founded predictive principles applicable to multi-decadal timescales. Primary production by phytoplankton and seawater temperatures are used to predict the growth and reproduction of fish, by determining the energy available to the trophic web16 and the metabolic rates of size-structured fish populations17. The fish harvest is determined by local-biomass density and interactive fishing effort, which evolves independently in each grid cell over time. As a first-order approximation, we assume that individual fishermen are rational and profit-seeking, as generally borne-out by observations18, and that there are no property rights (Open Access (OA)), which is the expected outcome in unmanaged fisheries. The current model version does not simulate artisanal or recreational fisheries explicitly, but only industrial fisheries, which account for >80% of global harvest and most of the 20th century trend1. Although the OA dynamic is not representative of the ∼40% of fisheries where management has recently become relatively effective19, it was a reasonable approximation of global fisheries throughout most of the 20th century20 and remains reflective of at least half of fisheries today, particularly in low-income countries21,22. Poorly constrained ecological model parameters are calibrated using Monte Carlo-based approximate Bayesian computation (Methods, Supplementary Methods) by comparing simulated with observed catch and biomass, aggregated at the scale of Large Marine Ecosystems (LMEs). The use of globally distributed LMEs allows the assessment of model performance across the full range of extant environmental conditions12. We show results for an ensemble of five different combinations of parameter values that provide realistic solutions, while representing a broad range of parameter uncertainty.
Because the model resolves the dynamics of the global fishery as a function of economic and environmental conditions, historical ‘hindcast’ simulations can be conducted to attribute the historical harvest trend to possible drivers on the coupled system, analogous to the approach taken with coupled ocean-atmosphere models to identify the role of greenhouse gases in historical climate23. Given our simple but inclusive conceptual framework, the external factors influencing the long-term development of the wild capture fishery are climate, the price of fish, the cost of fishing and the technology-dependent ability of fishermen to catch fish for a given amount of fishing effort. We first consider the ability of these factors to explain broad features of the observed 20th century trend of fish harvests, and then consider their possible roles in the future of the wild capture fishery.
Our results show that the historical increase of wild fish harvest, aggregated at the global scale, can be reproduced to first order by a hindcast that includes a moderate rate of increase in the technology-dependent ability to catch fish over time, assuming open access. We also show that, were it to continue, this same rate of technological progress would dominate the future trend in fish harvest under open access, but would result in declining, rather than increasing, harvest. The future simulations also assess the relative impacts of climate change on fish harvest, with and without effective management of fisheries, and considering the possibility of increasing market demand.
We carried out a series of experiments in which the model was subjected to temporally varying histories of the three economic forcings: (1) ex-vessel fish price (that is, the price that fishermen receive per mass of catch), which has varied over time in response to market conditions; (2) cost per unit effort, which includes capital, fuel, labour and the impact of most subsidies and (3) technological progress (Supplementary Methods). Our definition of technological progress includes advances in embodied technology, including more efficient boats, more effective fishing gear, sonar and communications equipment and disembodied technology, such as better knowledge of fish behaviour and more efficient fishing practices24. The combined effect of embodied and disembodied technology is represented in a simple but inclusive way by a catchability parameter, which was increased at rates of 2, 5 and 8% per year, a range representative of progress estimated empirically from individual fisheries7,25,26,27.
As shown in Fig. 2, the simulated changes in global harvest do not reproduce the observed increasing 20th century trend when forced individually with reconstructed changes in price or cost alone. Given the open-access assumption, this implies that increasing demand for fish was not the main driver of the long-term 20th century increase in fish harvest, despite population growth, although a growing population may have helped to maintain demand in the face of an increasing fish supply. Nor could the reconstructed changes in the cost per unit effort of fishing have been the primary driver. In contrast, the three simulations with technical progress produce global histories of harvest with long-term 20th-century increases, more consistent with the observations. With increasing technology the model also simulates a global peak of harvest, as observed, which arises from the sequential development, overexploitation and/or collapse of fisheries throughout the world, a sequence that has occurred historically in poorly managed fisheries28,29 (Supplementary Methods).
The technological progress rate of 5% per year would appear most representative as a global, long-term average, given that it approximates the observed relative increase of harvest between 1950 and 1996 and is near the midpoint of estimates from individual fisheries7,27,30. Given this apparent support for a long-term average technological progress rate of roughly 5% per year, we apply it together with the historical price reconstruction to generate a standard global hindcast, shown in Fig. 3. The agreement of the hindcast simulation with the reconstructed fish harvest, effort and biomass (compare Fig. 3 with Fig. 1) is remarkable, given that these are emergent properties of the model. The effort estimated before 1970 (∼7 GW) is notably higher than that simulated by the model ensemble (1–5 GW), but given difficulties in reconstructing historical global fishing effort2, these contrasts may not be significant. The estimated rate of biomass decrease is well-reproduced by the model at ∼10% of pristine biomass per decade, but with an important difference following 1990 when the estimated rate of biomass loss slowed (Fig. 1c), in contrast with the model. This divergence would be consistent with a progressive improvement in the management of many fisheries over the past three decades, a change that is not captured by the idealized OA simulations.
The model simulations also reproduce the first-order aspects of the 20th-century spatial changes in fish harvest, first depleting the dense biomass of highly productive coastal waters31, and then moving into deeper waters of the open ocean32,33 (Fig. 4). The expansion away from the coasts arises in the model as technological progress makes open-ocean waters with low biomass density more profitable, and therefore increasingly subjected to fishing effort. It should be emphasized that this model does not account for higher costs of fishing far from port, nor does it include complex ecosystem interactions, habitat alteration, fisheries management, or spatially variable economic factors, all of which played some role in the history of the global fishery. Nonetheless, it successfully reproduces the first-order features of the historical global trends in harvest, effort, and biomass. We therefore hypothesize that technological progress, at an average rate of ∼5% per year, dominated the development of the global wild capture fishery during the 20th century, while other societal, economic and climate forces had secondary impacts.
Idealized future projections
We consider an extreme range of possible futures for the global wild-capture fishery by projecting the model forward under idealized economic scenarios, with and without climate change. First, the historical OA hindcast is projected forward to represent an extreme end-member in which management is absent, under two alternative technological progress scenarios, and with either constant or linearly increasing price (Methods). Second, the model is used to estimate the global Maximum Sustainable Yield (MSY), representing the theoretical upper limit that could be approached with perfectly effective and well-informed management aimed at maximizing food production (Supplementary Methods). We emphasize that the future of the global fishery will follow neither the purely OA nor the MSY pathway; rather, these end-members outline the boundaries of what is possible for the global wild fishery in terms of food production. For example, effective regulations aimed at maximizing economic yield would produce less than the MSY harvest, but would generate more profit for fishermen19. We simultaneously consider the impacts of climate change by using water temperatures and primary production from the Institut Pierre Simon Laplace (IPSL) Earth System model with the RCP8.5 scenario (high emissions), and compare with a stable pre-industrial climate (Methods, Supplementary Methods).
The MSY is determined exclusively by the ability of the ecosystem to produce harvestable biomass, so that this modelled upper limit of potential harvest depends only on climate. As shown by Fig. 5a, the model ensemble estimates a MSY of ∼180±60 Mt yr−1 under stable preindustrial climate, while the inclusion of historical climate change leads to a decrease of MSY to 160±50 Mt yr−1 by 2015. The present-day global MSY estimate of 123 Mt yr−1 provided by ref. 19 lies within the 1 s.d. range of the model ensemble. Under the rapid continuing climate change of the RCP8.5 scenario, MSY decreases by 20% relative to 2015 by the end of the 21st century, falling below the simulated peak harvest obtained under OA, consistent with the view that climate change will cause a significant drop in potential fish production without reduction of carbon emissions34.
However, a much more dramatic decline in global harvest occurs over the 21st century in the hypothetical cases for which effective management is absent, as illustrated by the OA scenarios. Given continued 5% per year technological progress and constant price, the peak in global harvest is followed by a long-term decline (Fig. 5a, grey). This reversal in the role of technological progress—from enhancing to reducing harvest—arises because the ability of most ecosystems to produce biomass becomes limited by the spawning stock size under intense rates of harvest, as shown in many scientific surveys of fisheries35,36, and constrained here through our calibration against observed harvests (Methods, Supplementary Methods). If technological progress is halted, the harvest stabilizes, with only a small downward drift that is due to climate change (Fig. 5a, green). In the OA simulations where future price increases, shown in Fig. 5b, the same general trajectories are maintained, but the decline of harvest is more severe because over-fishing is intensified.
Our hindcast simulations, forced with relatively simple historical scenarios, suggest that a long-term average technological progress rate of roughly 5% per year dominated the 20th century trend in global fish harvests. In reality, technological improvements did not proceed by a steady march synchronized throughout the world, but proceeded at heterogeneous rates among different fisheries according to the development and diffusion of new ideas, and access to the capital required to implement them. Nonetheless, given the large number of technological innovations that took place over the 20th century, from monofilament lines, power blocks and new hook designs37, to sonar, radar and satellite communications, it is plausible that the overall aggregate progress—integrated among industrial fisheries of the world—may have been relatively smooth.
The impact of technological progress is achieved in the model by two interdependent pathways: fish become easier to catch for a given nominal effort and fish biomass, increasing effective effort, which in turn makes fishing more profitable, thereby increasing the nominal effort as long as the ecosystem is capable of sustaining the harvest. The fact that, over a 50-year period, a 5% per year rate of technological progress would have increased catchability by an order of magnitude explains its dominance over the relatively small historical fluctuations in the ex-vessel price and the cost of fishing.
Our idealized future simulations suggest that, over the 21st century, continuing technological improvements would cause global harvest to decrease under OA. This reversal of the 20th century trend would be exacerbated by any market dynamics that raise prices. These simulated future decreases, which lead to a growing divergence between OA and MSY over time (Fig. 5), suggest that the global impact of effective regulation will become more important in future as technology improves: whereas in 2015, the simulated MSY harvest is only ∼15% greater and ∼$20 billion per year more profitable than the global OA harvest, in 2100 (given 5% per year progress and increasing prices) the MSY harvest is more than ten-fold greater and hundreds of billions per year more profitable than the OA harvest. Although this may be of only theoretical interest for fisheries where effective regulatory regimes are well-established, it could have serious food security implications for the numerous fisheries in which regulations remain ineffective. The model suggests that, if perfectly managed, the global MSY would be on the order of 25% greater than the OA historical peak under preindustrial climate, and that even with the rapid climate change of the RCP8.5 scenario, the MSY would remain greater than the OA historical peak throughout most of the 21st century. Thus, our model suggests that the global wild capture fishery could continue to provide food, throughout the 21st century, at the same rate (or better) as at the end of the 20th century, but only if effective management can be extended to the fisheries in which it remains weak or absent.
We note that if new fisheries develop for previously unexploited species (such as mesopelagic fish), not included in our model, this could potentially slow the reduction of harvest under OA and raise global MSY. At the same time, our model is generally optimistic, in that it does not resolve habitat destruction by intensive trawling38, the takeover of ecosystems by non-commercial species39, trophic cascades40, alternative stable states41, ocean acidification and deoxygenation, or the development of overcapacity due to subsidies6, all of which would benefit from further study. The urgent need for improved fisheries management at the global scale is widely recognized, given the existing level of fishing effort19 and growing pressure from climate change42,43. Our results amplify these concerns by showing that, whereas progress in fishing technology contributed to massive gains in fish harvest during the 20th century at the global scale, its influence on catchability would be expected to only reduce harvest in the 21st century unless met with a global expansion of effective fisheries management.
The model presented here takes a highly simplified approach to the wild capture fishery, as required to remain tractable at the global scale and over long timescales. But despite its simplicity, the comprehensive treatment of critical elements, including spatially and temporally resolved interactions of humans with the ecosystem, allow it to identify the relative importance of general mechanisms that are difficult to discern among the multiplicity of factors typically considered on shorter timescales. Similar approaches may help to better understand the long-term dynamics of other coupled human-Earth systems.
At the foundation of the model is energy production by phytoplankton, which is transferred to multiple fish size-spectra according to an efficiency that depends on gross ecosystem metabolic rates16,44,45. The fish spectra are defined as representing the entire range of finfish and invertebrates with individual mass greater than 10 g, commercially harvested before 2006. The spectra resolve basic life-history characteristics, including temperature-dependent growth, mortality and density-dependent recruitment. By including all commercial species within the spectra, we implicitly account for species range shifts46,47, evolution48, and changes in targeted species, all of which have been significant historically and could play important roles in the future.
An economic model, coupled directly to the fish spectra at the grid scale, predicts fishing effort as a function of local profit, assuming open access to the available fish, following the classic work of ref. 49. Fishing effort in each grid cell changes over time according to the difference between local revenues and costs, at a rate determined by the fleet adjustment timescale. The effectiveness of fishing effort at catching the locally available biomass is determined by a catchability parameter that encapsulates both embodied and disembodied technology. Although fisheries are not strictly open access, and approximately one third of fisheries currently has some form of reasonably effective management19, the absence of effective management from most of the world’s fisheries throughout the 20th century makes it a good approximation at the global scale during the historical period21,22 as well as an illustrative example to consider the importance of management in future. The approximate global Maximum Sustainable Yield (MSY) is calculated by conducting transient simulations in which catchability is increased slowly, and summing the maximum harvest obtained in each grid cell. A more complete description of the model is given in ‘Model description’ in Supplementary Methods.
We calibrate the most important 13 model parameters through a Monte Carlo method and comparison with observationally estimated fish catches and stock assessments at the LME scale (‘Parameter optimization’ in Supplementary Methods). Because the LMEs span a very broad range of temperature and primary production, this strategy ensures a robust calibration to both these important variables. For the simulations shown here, we use an ensemble of five optimized models that span the uncertain parameter space as widely as possible, while producing a reasonably accurate simulation.
Model forcing and simulations
The model is forced with ocean temperature and net primary production, either from satellite-based observational estimates, or from the Institut Pierre Simon Laplace (IPSL) global climate model50, using the historical hindcast followed by the Representative Concentration Pathway (RCP) 8.5 scenario. The factors at play during the historical transient, according to the model framework, include the increase of catchability due to technology24,26, and an observational estimate of the global average ex-vessel fish price51, which has varied remarkably little (‘Ex-vessel Price variations’ in the Supplementary Methods). Given that there is no currently available estimate of historical variations in cost per unit effort, we roughly approximate its potential role using its relationship with observed price, effort and harvest under open-access, and making a steady-state assumption (‘Historical global average cost per unit effort’ in Supplementary Methods).
For the future projections, the OA model is integrated under four idealized scenarios, two of which assume a continuation of the same 5% per year exponential increase in fishing technology, while the other two simulate a gradual decrease in the rate of progress after 2006, reaching stabilized-technology after 2036. Given that technological progress is clearly continuing through advances such as improved fish tracking, the deployment of fish aggregating devices, and the increasing mechanization of fleets in developing nations, the technology-stabilization scenarios are included as baselines from which to estimate the long-term importance of future technological progress, rather than representing realistic future outcomes. For each of the technological scenarios, we address uncertainty in future market conditions by changing the ex-vessel price. Because the price of fish depends on the demand for fish products, which is difficult to predict given its dependence on societal preferences, available substitutes, and distribution networks52, we apply two end-member scenarios for ex-vessel price: linearly increasing, and constant. These represent the outcomes that might come from a larger population and/or a greater preference for seafood (increasing price), or a ready availability of substitutes from terrestrial food production (constant price), and bracket a wide range of intermediate possibilities.
The model code was written in MATLAB version R2012a. The zero-dimensional version of the model (that is, for a single patch of ocean), which includes the model run script, required functions, and forcing data, is available for download at http://dx.doi.org/10.5281/zenodo.27700 (ref. 53).
The model output and observational data are available from the authors on request.
How to cite this article: Galbraith, E. D. et al. A coupled human-Earth model perspective on long-term trends in the global marine fishery. Nat. Commun. 8, 14884 doi: 10.1038/ncomms14884 (2017).
Publisher’s note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Pauly, D. & Zeller, D. Catch reconstructions reveal that global marine fisheries catches are higher than reported and declining. Nat. Commun. 7, 10244 (2016).
Watson, R. A. et al. Global marine yield halved as fishing intensity redoubles. Fish Fish. 14, 493–503 (2013).
Hilborn, R. et al. State of the world's fisheries. Ann. Rev. Environ. Resources 28, 359–399 (2003).
Worm, B. & Branch, T. A. The future of fish. Trends Ecol. Evol. 27, 594–599 (2012).
Willman, R., Kelleher, K., Arnason, R. & Franz, N. The Sunken Billions: the Economic Justification for Fisheries Reform IBRD/FAO (2009).
Sumaila, U. R. et al. A bottom-up re-estimation of global fisheries subsidies. J. Bioecon. 12, 201–225 (2010).
Squires, D. & Vestergaard, N. Technical change in fisheries. Mar. Policy 42, 286–292 (2013).
Brander, K. M. Global fish production and climate change. Proc. Natl Acad. Sci. 104, 19709–19714 (2007).
Cheung, W. W. et al. Large-scale redistribution of maximum fisheries catch potential in the global ocean under climate change. Glob. Change Biol. 16, 24–35 (2010).
Quaas, M. F., Reusch, T. B., Schmidt, J. O., Tahvonen, O. & Voss, R. It is the economy, stupid! Projecting the fate of fish populations using ecological-economic modeling. Glob. Change Biol. 22, 264–270 (2016).
Carozza, D. A., Bianchi, D. & Galbraith, E. D. The ecological module of BOATS-1.0: a bioenergetically constrained model of marine upper trophic levels suitable for studies of fisheries and ocean biogeochemistry. Geosci. Model Dev. 9, 1545–1565 (2016).
Carozza, D. A., Bianchi, D. & Galbraith, E. D. Formulation, general features and global calibration of a bioenergetically-constrained fishery model. PLoS ONE 12, e0169763 (2017).
Fulton, E. A. Approaches to end-to-end ecosystem models. J. Mar. Syst. 81, 171–183 (2010).
Barange, M. et al. Impacts of climate change on marine ecosystem production in societies dependent on fisheries. Nat. Clim. Change 4, 211–216 (2014).
Christensen, V. et al. The global ocean is an ecosystem: simulating marine life and fisheries. Glob. Ecol. Biogeogr. 24, 507–517 (2015).
Jennings, S. et al. Global-scale predictions of community and ecosystem properties from simple ecological theory. Proc. R. Soc. B 275, 1375–1383 (2008).
Andersen, K. H., Jacobsen, N. S. & Farnsworth, K. D. The theoretical foundations for size spectrum models of fish communities. Can. J. Fish Aquat. Sci. 73, 575–588 (2016).
Branch, T. A. et al. Fleet dynamics and fishermen behavior: lessons for fisheries managers. Can. J. Fish Aquat. Sci. 63, 1647–1668 (2006).
Costello, C. et al. Global fishery prospects under contrasting management regimes. Proc. Natl Acad. Sci. 113, 5125–5129 (2016).
Larkin, P. A. An epitaph for the concept of maximum sustained yield. Trans. Am. Fish. Soc. 106, 1–11 (1977).
Mora, C. et al. Management effectiveness of the world's marine fisheries. PLoS Biol. 7, e1000131 (2009).
Costello, C., Lynham, J., Lester, S. E. & Gaines, S. D. Economic incentives and global fisheries sustainability. Ann. Rev. Resource Econ. 2, 299–318 (2010).
Stott, P. A. et al. External control of 20th century temperature by natural and anthropogenic forcings. Science 290, 2133–2137 (2000).
Squires, D. & Vestergaard, N. Technical change and the commons. Rev. Econ. Stat. 95, 1769–1787 (2013).
Wilberg, M. J., Thorson, J. T., Linton, B. C. & Berkson, J. Incorporating time-varying catchability into population dynamic stock assessment models. Rev. Fish. Sci. 18, 7–24 (2009).
Pauly, D. & Palomares, M. An empirical equation to predict annual increases in fishing efficiency. Working Paper Series, Working Paper #2010-07 (Fisheries Centre, The University of British Columbia, 2010).
Tidd, A. N., Reid, C., Pilling, G. M. & Harley, S. J. Estimating productivity, technical and efficiency changes in the Western Pacific purse-seine fleets. ICES J. Mar. Sci.: J. Conseil. 73, 1226–1234 (2016).
Mullon, C., Fréon, P. & Cury, P. The dynamics of collapse in world fisheries. Fish Fish. 6, 111–120 (2005).
Branch, T. A., Jensen, O. P., Ricard, D., Ye, Y. & Hilborn, R. Contrasting global trends in marine fishery status obtained from catches and from stock assessments. Conserv. Biol. 25, 777–786 (2011).
Villasante, S. & Sumaila, U. R. Estimating the effects of technological efficiency on the European fishing fleet. Mar. Policy 34, 720–722 (2010).
Jackson, J. B. et al. Historical overfishing and the recent collapse of coastal ecosystems. Science 293, 629–637 (2001).
Swartz, W., Sala, E., Tracey, S., Watson, R. & Pauly, D. The spatial expansion and ecological footprint of fisheries (1950 to Present). PLoS ONE 5, e15143 (2010).
Watson, R. A. & Morato, T. Fishing down the deep: accounting for within-species changes in depth of fishing. Fish. Res. 140, 63–65 (2013).
Cheung, W. W. et al. Building confidence in projections of the responses of living marine resources to climate change. ICES J. Mar. Sci.: J. Conseil. 73, 1283–1296 (2016).
Cushing, D. Dependence of recruitment on parent stock. J. Fish. Board Can. 30, 1965–1976 (1973).
Myers, R. A. Stock and recruitment: generalizations about maximum reproductive rate, density dependence, and variability using meta-analytic approaches. ICES J. Mar. Sci.: J. Conseil. 58, 937–951 (2001).
Eigaard, O. R., Thomsen, B., Hovgaard, H., Nielsen, A. & Rijnsdorp, A. D. Fishing power increases from technological development in the Faroe Islands longline fishery. Can. J. Fish. Aquat. Sci. 68, 1970–1982 (2011).
Pusceddu, A. et al. Chronic and intensive bottom trawling impairs deep-sea biodiversity and ecosystem functioning. Proc. Natl Acad. Sci. 111, 8861–8866 (2014).
Robinson, K. L. et al. Jellyfish, forage fish, and the world's major fisheries. Oceanography 27, 104–115 (2014).
Andersen, K. H. & Pedersen, M. Damped trophic cascades driven by fishing in model marine ecosystems. Proc. R. Soc. B 277, 795–802 (2009).
De Roos, A. M., Boukal, D. S. & Persson, L. Evolutionary regime shifts in age and size at maturation of exploited fish stocks. Proc. R. Soc. B 273, 1873–1880 (2006).
Beddington, J. R., Agnew, D. J. & Clark, C. W. Current problems in the management of marine fisheries. Science 316, 1713–1716 (2007).
Worm, B. et al. Rebuilding global fisheries. Science 325, 578–585 (2009).
Brown, J. H., Gillooly, J. F., Allen, A. P., Savage, V. M. & West, G. B. Toward a metabolic theory of ecology. Ecology 85, 1771–1789 (2004).
Kooijman, S. A. L. M. Dynamic Energy Budget Theory for Metabolic Organisation Cambridge University Press (2009).
Perry, A. L., Low, P. J., Ellis, J. R. & Reynolds, J. D. Climate change and distribution shifts in marine fishes. Science 308, 1912–1915 (2005).
Pinsky, M. L., Worm, B., Fogarty, M. J., Sarmiento, J. L. & Levin, S. A. Marine taxa track local climate velocities. Science 341, 1239–1242 (2013).
Kuparinen, A. & Merilä, J. Detecting and managing fisheries-induced evolution. Trends Ecol. Evol. 22, 652–659 (2007).
Gordon, H. S. The economic theory of a common-property resource: the fishery. J. Polit. Econ. 62, 124–142 (1954).
Dufresne, J.-L. et al. Climate change projections using the IPSL-CM5 Earth system model: from CMIP3 to CMIP5. Clim. Dyn. 40, 2123–2165 (2013).
Sumaila, U. R., Marsden, A. D., Watson, R. & Pauly, D. A global ex-vessel fish price database: construction and applications. J. Bioecon. 9, 39–51 (2007).
Mullon, C. et al. Exploring future scenarios for the global supply chain of tuna. Deep Sea Research Part II: Topical Studies in Oceanography (in the press).
Carozza, D. A., Bianchi, D. & Galbraith, E. 0-D BiOeconomic mArine Trophic Size-spectrum (BOATS) model (review version). doi:10.5281/zenodo.27700 (2015).
We thank the Canadian Foundation for Innovation (CFI) for providing computing infrastructure, and the Marine Environmental Prediction and Response (MEOPAR) Network Centre of Excellence and Canadian Foundation for Advanced Research (CIFAR) for funding support. EDG acknowledges financial support from the Spanish Ministry of Economy and Competitiveness, through the María de Maeztu Programme for Centres/Units of Excellence in R&D (MDM-2015-0552). This project has received funding from the European Research Council (ERC) under the European Union’s Horizon 2020 research and innovation programme (grant agreement No 682602, BIGSEA). D.B. acknowledges financial support from a Faculty Research Grant from University of California Los Angeles.
The authors declare no competing financial interests.
About this article
Cite this article
Galbraith, E., Carozza, D. & Bianchi, D. A coupled human-Earth model perspective on long-term trends in the global marine fishery. Nat Commun 8, 14884 (2017). https://doi.org/10.1038/ncomms14884
Nature Communications (2020)