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  • Review Article
  • Published:

ENSO impacts on marine ecosystems and fisheries in the tropical and South Atlantic

Abstract

Tropical and South Atlantic marine ecosystems support fisheries that have vital environmental and socioeconomic importance. In this Review, we outline how the El Niño–Southern Oscillation — a Pacific mode of sea surface temperature variability — influences Atlantic fisheries via teleconnections and cascading linkages between physical, biogeochemical and ecological systems. Connections are driven by tropical pathways (involving changes in atmospheric stability associated with the Walker circulation and tropospheric warming) and extratropical pathways (involving the Pacific–South American and Pacific–North American teleconnection patterns). Depending on the location, these pathways modify rainfall and river discharge, winds and upwelling, or a combination of both, impacting salinity, nutrient availability, primary production and, thus, fish recruitment, biomass and catch. Fishery responses are strongly species dependent, reflecting variations in behaviour between species to environmental factors (such as temperature, oxygen, salinity, habitat and food availability). This regional variability and species dependency, coupled with strong non-stationarity, highlights the complexity of El Niño–Southern Oscillation impacts on Atlantic marine ecosystems. This historical signal is projected to weaken in the future. Enhanced observational systems and refined ecosystem models are urgently needed to enhance predictive capabilities, reduce societal impacts and improve sustainable management in these regions.

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Fig. 1: El Niño–Southern Oscillation teleconnection mechanism affecting the tropical and South Atlantic.
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Fig. 2: Non-stationarity of ENSO teleconnection impacts.
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Fig. 3: El Niño–Southern Oscillation impacts on marine ecosystems from physics to fish.
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Fig. 4: ENSO fishery impacts.
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Fig. 5: ENSO impacts on fisheries via physical drivers.
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Fig. 6: An overview of ENSO relationships with tropical and South Atlantic fisheries.
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Acknowledgements

The authors are grateful for support from the EU H2020 Project TRIATLAS under grant agreement no. 817578, the Spanish national projects PID2021-125806NB-I00 and TED2021-130106B-I00, the EU Horizon 2020 nextGEMS project (EU Horizon 2020 no. 101003470) and the UCM FEI-EU-25-02. M.M.R. is grateful for support from the Ramón y Cajal grant (RYC2022-038454-I, funded by MCIN/AEI/10.13039/ 501100011033 and co-funded by the FSE + European Union). R.A thanks CNPq–Brazil (302836/2025-0) for support. M.C., F.R. and J.S. thank Spanish projects PID2020-118097RB-I00 and PID2021-124831OA-I00 for support, with additional support from CEX2024-001494-S (AEI, 10.13039/501100011033) and 2021 SGR 00435. I.G. is grateful for support from the CONSCIENCE project (PID2023-146344OB-I00), funded by the Spanish Ministry of Science, Innovation and Universities (MICIU/AEI/10.13039/501100011033) and by FEDER-EU. H.C.N thanks Deutsche Forschungsgemeinschaft (DFG) grant 456490637 for support. J.L.-P. and J.C.S.-G. acknowledge funding from Spanish projects CARMEN (PCI2021-122061-2B) and CARDUMEN (CNS2023-144704). L.G.’s work was supported in part by the National Research Foundation of South Africa (grant number 136481). M.M. thanks NOAA for support PMEL contribution no. 5562. This work is a contribution to the IJL TAPIOCA.

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B.R.F. and R.R conceived the article. B.R.F. led writing with contributions from all authors. B.R.F., E.C.M. and L.M.C. created the figures and conducted all data analysis. I.P., M.M.R., T.L., J.L.P., I.G., L.S., D.R., E.E., F.F., F.R. and N.K. coordinated the presentation, writing and discussion for various sections. E.E., E.S. and D.R. conducted the model analysis. A.B., R.R., W.C. and M.M. revised the text.

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Rodríguez-Fonseca, B., Calvo-Miguélez, E., Montoya-Carramolino, L. et al. ENSO impacts on marine ecosystems and fisheries in the tropical and South Atlantic. Nat Rev Earth Environ 7, 43–59 (2026). https://doi.org/10.1038/s43017-025-00742-2

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