Click
here to close Hello! We notice that
you are using Internet Explorer, which is not supported by Echinobase
and may cause the site to display incorrectly. We suggest using a
current version of Chrome,
FireFox,
or Safari.
Proc Biol Sci
2023 Jan 25;2901991:20222262. doi: 10.1098/rspb.2022.2262.
Show Gene links
Show Anatomy links
Marine heatwaves and upwelling shape stress responses in a keystone predator.
Rühmkorff S
,
Wolf F
,
Vajedsamiei J
,
Barboza FR
,
Hiebenthal C
,
Pansch C
.
???displayArticle.abstract???
Climate change increases the frequency and intensifies the magnitude and duration of extreme events in the sea, particularly so in coastal habitats. However, the interplay of multiple extremes and the consequences for species and ecosystems remain unknown. We experimentally tested the impacts of summer heatwaves of differing intensities and durations, and a subsequent upwelling event on a temperate keystone predator, the starfish Asterias rubens. We recorded mussel consumption throughout the experiment and assessed activity and growth at strategically chosen time points. The upwelling event overall impaired starfish feeding and activity, likely driven by the acidification and low oxygen concentrations in the upwelled seawater. Prior exposure to a present-day heatwave (+5°C above climatology) alleviated upwelling-induced stress, indicating cross-stress tolerance. Heatwaves of present-day intensity decreased starfish feeding and growth. While the imposed heatwaves of limited duration (9 days) caused slight impacts but allowed for recovery, the prolonged (13 days) heatwave impaired overall growth. Projected future heatwaves (+8°C above climatology) caused 100% mortality of starfish. Our findings indicate a positive ecological memory imposed by successive stress events. Yet, starfish populations may still suffer extensive mortality during intensified end-of-century heatwave conditions.
Figure 1. . Schematic representation of the treatments experienced by individuals of Asterias rubens throughout the duration of the experiment. No heatwave: followed a smoothed natural mean seasonal temperature profile (blue line in (a); see methods for further information). Present-day: experienced a short heatwave with the intensity and duration of present-day events (9 days above the seasonal profile depicted in (a) with a maximum +5°C, green polygon in (b)). Extended: a heatwave of extended duration in comparison to Present-day (13 days above seasonal profile with a maximum +5°C, yellow polygon in (c)). Amplified: a heatwave of increased intensity in comparison to Present-day (9 days above seasonal profile with a maximum +8°C, pink polygon in (d)). Future: a heatwave with the combined characteristics of those described in (c) and (d) (13 days above seasonal profile with a maximum +8°C, red polygon in (e)). All treatments received an upwelling event (blue polygon) towards the end of the experiment, which was characterized by a drop in temperature (−4.4°C), oxygen concentration (−6.3 mg l−1) and pHNBS (−0.5 units) as well as an increase in salinity (+2.2 units; details in electronic supplementary material, figure S1). Black dots represent measuring events of wet weight, while grey triangles represent assessments of righting responses of A. rubens.
Figure 2. . Feeding rate (milligrams of mussel dry weight per day, (a)), wet weight (g, (b)) and righting time (minutes, (c)) of Asterias rubens throughout 63 days of our experiment, under No (blue), Present-day (green) and Extended (yellow) heatwave treatments (see figure 1 for treatment descriptions). All treatments received an upwelling event towards the end of the experiment. The red dashed lines represent the periods of heatwaves (Present-day and Extended) and the blue dashed lines the period of upwelling. Data are represented as means (dots) of n = 12 experimental units. Trends in (a) and (b) were modelled using GAMM (explained deviance = 37.6% and 40.5%, respectively). Solid lines show the mean fitted trends and the shaded areas the associated 95% confidence intervals (a,b). Whiskers in (c) represent 95% confidence intervals. Differences between No and Present-day, between No and Extended and between Present-day and Extended are represented by solid, dashed and dotted black lines placed at the bottom of the plots, respectively (see electronic supplementary material S3: figure S8 for further details). See also electronic supplementary material S3: figures S9, S10, and S11 for related bar plots and 95% confidence intervals. Detailed statistical outcomes are presented in the electronic supplementary material S3: tables S2–S4. All starfish died after 24 days in the Amplified treatments and were therefore excluded from the plots.
Figure 3. . Mean feeding rate (milligrams of mussel dry weight per day, (a)) and wet weight (g, (b)) of Asterias rubens during 63 days of incubation, under No (blue), Present-day (green) and Extended (yellow) heatwave treatments (see figure 1 for treatment descriptions). All treatments received an upwelling event towards the end of the experiment. Data are presented as means and 95% confidence intervals (n = 12). Lower case letters represent significant differences between treatments based on LMM (see electronic supplementary material S3: tables S2 and S3). All starfish died after 24 days in the Amplified treatments and were therefore excluded from the plots.
Banti,
Heat acclimation and cross-tolerance against anoxia in Arabidopsis.
2008, Pubmed
Banti,
Heat acclimation and cross-tolerance against anoxia in Arabidopsis.
2008,
Pubmed
Ceylan,
Potential habitats of an alien species (Asterias rubens Linnaeus, 1758) in the Black Sea: its current and future distribution patterns.
2022,
Pubmed
,
Echinobase
Diaz,
Spreading dead zones and consequences for marine ecosystems.
2008,
Pubmed
Diaz,
Overview of hypoxia around the world.
2001,
Pubmed
Dobashi,
Decomposing the effects of ocean environments on predator-prey body-size relationships in food webs.
2018,
Pubmed
Ely,
Heat acclimation and cross tolerance to hypoxia: Bridging the gap between cellular and systemic responses.
2014,
Pubmed
Fennel,
Biogeochemical Controls on Coastal Hypoxia.
2019,
Pubmed
Grantham,
Upwelling-driven nearshore hypoxia signals ecosystem and oceanographic changes in the northeast Pacific.
2004,
Pubmed
Gunderson,
Multiple Stressors in a Changing World: The Need for an Improved Perspective on Physiological Responses to the Dynamic Marine Environment.
2016,
Pubmed
Hofmann,
Molecular chaperones in ectothermic marine animals: biochemical function and gene expression.
2002,
Pubmed
Hu,
Trans-life cycle acclimation to experimental ocean acidification affects gastric pH homeostasis and larval recruitment in the sea star Asterias rubens.
2018,
Pubmed
,
Echinobase
Hue,
Temperature affects the reproductive outputs of coral-eating starfish Acanthaster spp. after adult exposure to near-future ocean warming and acidification.
2020,
Pubmed
,
Echinobase
Huo,
Impact of hypoxia stress on the physiological responses of sea cucumber Apostichopus japonicus: respiration, digestion, immunity and oxidative damage.
2018,
Pubmed
,
Echinobase
Jackson,
The Temporal Dynamics of Multiple Stressor Effects: From Individuals to Ecosystems.
2021,
Pubmed
Lämke,
A hit-and-run heat shock factor governs sustained histone methylation and transcriptional stress memory.
2016,
Pubmed
Lefevre,
Are global warming and ocean acidification conspiring against marine ectotherms? A meta-analysis of the respiratory effects of elevated temperature, high CO2 and their interaction.
2016,
Pubmed
Leung,
Heatwaves diminish the survival of a subtidal gastropod through reduction in energy budget and depletion of energy reserves.
2017,
Pubmed
McBryan,
Warm acclimation improves hypoxia tolerance in Fundulus heteroclitus.
2016,
Pubmed
Melzner,
Ocean winter warming induced starvation of predator and prey.
2020,
Pubmed
,
Echinobase
Morón Lugo,
Warming and temperature variability determine the performance of two invertebrate predators.
2020,
Pubmed
,
Echinobase
Oliver,
Longer and more frequent marine heatwaves over the past century.
2018,
Pubmed
Pansch,
Heat waves and their significance for a temperate benthic community: A near-natural experimental approach.
2018,
Pubmed
Pörtner,
Climate change and temperature-dependent biogeography: oxygen limitation of thermal tolerance in animals.
2001,
Pubmed
Przeslawski,
A review and meta-analysis of the effects of multiple abiotic stressors on marine embryos and larvae.
2015,
Pubmed
Rakocinski,
Seasonal hypoxia regulates macrobenthic function and structure in the Mississippi Bight.
2016,
Pubmed
Rall,
Universal temperature and body-mass scaling of feeding rates.
2012,
Pubmed
Randall,
Upwelling buffers climate change impacts on coral reefs of the eastern tropical Pacific.
2020,
Pubmed
Roegner,
Coastal upwelling supplies oxygen-depleted water to the Columbia River estuary.
2011,
Pubmed
Rühmkorff,
Marine heatwaves and upwelling shape stress responses in a keystone predator.
2023,
Pubmed
,
Echinobase
Sanford,
Water temperature, predation, and the neglected role of physiological rate effects in rocky intertidal communities.
2002,
Pubmed
,
Echinobase
Sanford,
Regulation of keystone predation by small changes in ocean temperature.
1999,
Pubmed
,
Echinobase
Seibel,
Critical oxygen levels and metabolic suppression in oceanic oxygen minimum zones.
2011,
Pubmed
Sokolova,
Energy-limited tolerance to stress as a conceptual framework to integrate the effects of multiple stressors.
2013,
Pubmed
Todgham,
Cross-tolerance in the tidepool sculpin: the role of heat shock proteins.
2005,
Pubmed
Vahl,
The relationship between specific dynamic action (SDA) and growth in the common starfish, Asterias rubens L.
1984,
Pubmed
,
Echinobase
Vaquer-Sunyer,
Thresholds of hypoxia for marine biodiversity.
2008,
Pubmed