the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.

Seafloor marine heatwaves outpace surface events in the future on the northwestern European shelf
Yuri Artioli
Giovanni Galli
James Harle
Jason Holt
Ana M. Queirós
Sarah Wakelin
Marine heatwaves are becoming increasingly frequent across the world's oceans. As a result, there are growing impacts on marine ecosystems due to temperatures exceeding the thermal niche and historical exposure of many species. Anticipating the future frequency and severity of marine heatwaves is necessary. Here, we provide the first projections of future marine heatwaves for the sea surface and seafloor across the northwestern European shelf, which is a critically important marine ecosystem. We use an ensemble of five dynamically downscaled hydrodynamic models under the high-emission scenario Representative Concentration Pathway 8.5 (RCP 8.5). Heatwaves were defined as events lasting at least 5 d where temperatures exceed the 90th percentile of a historical baseline period. The frequency of marine heatwaves at the surface and seafloor is projected to increase significantly during the 21st century under RCP 8.5, with most of the year being projected to be under heatwave conditions by the end of the century. Critically, we find that marine heatwaves are projected to increase in frequency to a greater extent at the seafloor compared to at the sea surface due to their lower levels of natural temperature variation. Similarly, we find that the severity of summer heatwaves at the surface is projected to be lower than that of heatwaves during the rest of the year due to lower climatological variations in temperature outside the summer. The impacts of marine heatwaves in shelf seas are therefore likely to be much more complex than previously thought.
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Marine heatwaves are defined as prolonged periods where the sea is anomalously warm (Oliver et al., 2021). Since Pearce et al. (2011) first used the term, there has been a rapid growth in our understanding of their causes and how they impact ecosystems. In recent decades, rising temperatures have caused marine heatwaves to become more and more frequent around the world (Oliver et al., 2019, 2018a, b; Marin et al., 2021; Scannell et al., 2016; Darmaraki et al., 2019; Yao et al., 2023). They have multiple causes, ranging from the occurrence of atmospheric heatwaves to changes in wind speeds and variations in ocean mixing (sen Gupta et al., 2020; Amaya et al., 2020).
Marine heatwaves have largely negative impacts on marine ecosystems (Smith et al., 2023). Negative impacts on seaweeds (Thomsen et al., 2019; Gurgel et al., 2020; Arafeh-Dalmau et al., 2019; Filbee-Dexter et al., 2020), seagrasses (Arias-Ortiz et al., 2018; Strydom et al., 2020), seabirds (Jones et al., 2018; Piatt et al., 2020), coral reefs (Leggat et al., 2019; Le Nohaïc et al., 2017), crustaceans (Chandrapavan et al., 2019), fish (Wild et al., 2019; Roberts et al., 2019), and plankton (Brodeur et al., 2019; Nielsen et al., 2021), among others, have been recorded. However, the impacts of marine heatwaves are complex and vary across ecosystems (Smale et al., 2017), and it remains unclear to what extent ecosystems can adapt to the continued rise in their frequency (Pershing et al., 2018).
The impacts of marine heatwaves on the sea surface and seafloor are likely to be distinct. Pelagic species and communities are typically advected or can swim across large regions and can therefore acclimate or reorganize in response to climate change relatively quickly. In contrast, benthic and demersal species tend to have limited mobility, such that tracking optimal thermal habitats, e.g. though the deepening of assemblages, is seen to be more challenging. It is thus more likely that negative impacts will be observed (e.g. Queirós et al., 2021, 2023), especially in species with slow growth rates, which slow the ability to respond to disturbances (Ceccherelli et al., 2007). Effective management of these species and habitats thus necessitates that projections of future marine heatwaves at both the ocean surface and the seafloor are considered. While most of the marine-heatwave assessments to date have looked at sea surface temperature data, recent studies suggest that sub-surface heatwaves can be equally relevant (He et al., 2024; Sun et al., 2023a).
A large body of work has used global climate models to project how future marine heatwaves are expected to increase this century (Azarian et al., 2023; Cheng et al., 2023; Oliver et al., 2019; Plech and Soares, 2019; Qiu et al., 2021; Rosselló et al., 2023; Sun et al., 2023b; Xue et al., 2023). However, global models are substantially limited in their ability to project marine heatwaves at both the sea surface and seafloor in shelf seas. Global models typically have a coarse spatial resolution, which can result in poor representation of ocean shelf processes, and the representation of critical processes, such as riverine inputs which affect key processes in shelf environments, is poor (Holt et al., 2017; Kay et al., 2023). In combination, this results in poor representation of processes such as seasonal thermal stratification of the water column, resulting in modelling projections which do not provide sufficiently credible representation of coastal processes. Finally, marine-heatwave calculations require daily temperature data (Hobday et al., 2016). These are available for the sea surface for many global climate models (Wilson et al., 2024); however, daily near-bottom temperatures are not available in those models, including the models used in the global climate change modelling standard, the Coupled Model Intercomparison Project Phases 5 and 6 (CMIP5 and 6). This leads to an unavailability of reliable ocean modelling projections from which to derive marine-heatwave estimations to inform marine science, policy, and industry development operating at the international, national, and sub-national levels.
The limitations of global climate models on continental shelves can largely be resolved using dynamical downscaling (e.g. Drenkard et al., 2021), whereby a regional model with a higher horizontal and vertical resolution is used to project future changes in ocean physics and biogeochemistry (e.g. Butenschön et al., 2016). Through this approach, a regional model is forced at the boundaries, i.e. at the air–surface boundary and the geographic limits of the regional model domain, by the outputs of a global model, offering a higher resolution of processes within the region of interest whilst being consistent with the broader processes simulated in the global model. Here, we apply this approach to understand future marine heatwaves on the northwestern European shelf.
The northwestern European shelf is an important marine ecosystem that provides ecological, cultural, and economic services to many countries (Culhane et al., 2020). It is one of the world's most heavily fished regions (Halpern et al., 2008) and has the world's largest and fastest-growing offshore wind industry. Understanding how climate change will impact the region is thus critical to enable effective spatial and fishery management into the future (Queirós et al., 2021). Due to its shallow bathymetry and the complex circulation system (Holt et al., 2010), the drivers of marine heatwaves in this region are likely to differ significantly from those in more studied oceanic systems (Jacobs et al., 2024). Importantly, marine heatwaves are likely to be due to the combined impacts of atmospheric (Berthou et al., 2024) and regional changes (Mohamed et al., 2023), necessitating the use of high-resolution regional modelling to understand their present-day drivers and future evolution.
In the northwestern European shelf, a suite of dynamically downscaled projections exist and have been used to consider the impacts of climate change on sea level rise (Hermans et al., 2020), changes in oxygen concentration (Wakelin et al., 2020; Galli et al., 2024), changes in circulation patterns (Holt et al., 2018), and the impacts of climate change on primary production (Holt et al., 2016). These have been used further to consider the impacts on higher trophic levels and the human uses of the marine environment, such as fisheries, aquaculture, and conservation, as well as on the full marine ecosystem (Palmer et al., 2021; Queirós et al., 2021, 2023; du Pontavice et al., 2023; Townhill et al., 2023).
The key aim of this study is to understand how future marine heatwaves will change in northwestern Europe under a high-emission greenhouse gas scenario. We separately assess the future evolution of marine heatwaves at the surface and the seafloor and, furthermore, disaggregate changes seasonally. This assessment will provide a more nuanced and complete understanding of future marine heatwaves in shelf seas.
2.1 Physical models and climate change scenario
Future marine heatwaves on the northwestern European shelf were projected using the high-emission climate change scenario Representative Concentration Pathway 8.5 (RCP 8.5) (van Vuuren et al., 2010) using an existing ensemble of dynamically downscaled global climate models. This is a higher-emission scenario that is likely given developments in global climate policies and industrial development (Hausfather and Peters, 2020). However, the core aim of this paper is to understand the comparative effects of future climate change on seafloor and sea surface heatwaves. The use of an individual scenario is sufficient to indicate how their trajectories will differ and by what magnitude. The choice of restricting the analysis to RCP 8.5 also allowed for the investigation of changes in heatwave frequency across a small ensemble and, therefore, an assessment of the robustness of the changes with respect to the uncertainty of the climate projection.
Each global climate model used for the downscaling (Holt et al., 2022a) is from the CMIP5 project (Taylor et al., 2012) and was downscaled using the Atlantic Margin Model at 7 km resolution based on the Nucleus of a European Model of the Ocean (NEMO). A detailed explanation of this model can be found in O'Dea et al. (2017). The model employs an equal-angle quadrilateral C-grid mesh with a spatial resolution of ° latitude (7.4 km) and ° longitude (ranging from 5.2 to 9.4 km), and it features 51 terrain-following vertical levels. The model's geographic domain covers 40 to 65° N and 20° W to 13° E. For the purposes of heatwave calculations, we defined the northwestern European shelf as the region shallower than 200 m, and we also considered the Norwegian Trench.
In the downscaling approach described by Holt et al. (2022a), the surface and lateral boundary conditions, such as air temperature, and the initial conditions are taken from the global climate model without bias correction. Due to the poor representation of the boundary connecting the North and the Baltic seas, a present-day climatology (Gräwe et al., 2015) was used to define the boundary connecting them. This downscaling approach enables the large-scale atmospheric changes projected by the global climate model to be transferred to the fine-scale changes projected by the regional model. The ensemble of dynamically downscaled projections is fully described in Holt et al. (2022a), who produced a seven-member ensemble of future projections that reasonably represent seasonal stratification and present-day temperature. This was then reduced to a five-member ensemble by only using one model simulation from each of the two instances where downscalings were produced from closely related global models, to ensure ensemble independence. The global climate models included in the downscaling were as follows: CanESM2 (Swart et al., 2019), CNRM-CM5 (Voldoire et al., 2013), GFDL-ESM2M (Dunne et al., 2020), IPSL-CM5A-MR (Boucher et al., 2020), and MIROC-ESM (Watanabe et al., 2011). In each case, the downscaled projections were run from 1980 to 2099.
2.2 Calculation of marine heatwaves
The aim of this study is to provide ecologically relevant projections of future marine heatwaves. Critically, we aim to understand the comparative impacts of climate change on heatwaves on the sea surface and seafloor and therefore must choose a heatwave definition which is comparable. We therefore projected marine heatwaves using a fixed historical baseline (Hobday et al., 2016) instead of a shifting baseline (Giménez et al., 2024) to define marine-heatwave conditions. This was for multiple reasons. The ability of ecosystems to adapt to warming is thought to be slower than the current and projected future rates of warming (Oliver et al., 2021), and, importantly, benthic species are understood to track temperature shifts slowly (Hiddink et al., 2015), unlike the more mobile pelagic species. This implies that any shifting baseline for marine heatwaves should be defined differently for sea surface and seafloor ecosystems. Given the lack of existing approaches to defining shifting baselines differently, we therefore chose a fixed-baseline approach.
Marine heatwaves were defined and classified based on the methodology of Hobday et al. (2016). Heatwaves were defined as periods where temperatures are above historically high levels for a prolonged period of at least 5 d. Historically “high” temperatures were defined as the 90th percentile of temperature within an 11 d window centred on each day of the year for a pre-defined baseline period. For this study, we defined the baseline period to be the years of 1990–2009, which is typically viewed as a large enough climatological period for assessing projected changes (Kajtar et al., 2022). The baseline period includes a period of historical forcing (1990–2004) and 5 years of scenario forcing, i.e. assumed and not actual atmospheric CO2 emissions. However, the scenario assumptions are identical in each model run, making the model runs directly comparable.
Furthermore, we classified heatwaves as moderate, strong, severe, or extreme using the approach of Hobday et al. (2018). In this approach, heatwaves are classified based on multiples of the differences between the 90th percentile and the climatological average temperature on each day of the year. A heatwave of maximum temperature which represents the equivalent of a multiple of 1–2 times this difference is classified as moderate, strong is 2–3 times this difference, severe is 3–4 times this difference, and extreme is > 4 times this difference. So, for example, if the 90th percentile historically represented a temperature anomaly of 1 °C, a heatwave with a maximum anomaly of 1.5 °C would be classified as moderate, whereas a heatwave of a maximum anomaly of 3.5 °C would be classified as severe. As with the historical percentiles, we calculated the historical average temperature using an 11 d window for the baseline period.

Figure 1Projected change in average sea surface and seafloor temperature between a historical baseline period of 1990–2009 and mid-century (2040–2059) and end-century (2080–2099) periods from five dynamically downscaled climate models under the climate change scenario RCP 8.5. The column names list the global climate model used in the downscaling.
The ability of the models to reproduce historical (1990–2009) variations in surface temperature during summer was assessed by comparing the anomaly of the historical heatwave temperature threshold in the model with observations. The anomaly is defined as the daily threshold – the average temperature on each day. Historical daily sea surface temperature (at a spatial resolution of 0.05° × 0.05°) was acquired from the Operational Sea Surface Temperature and Sea Ice Analysis system (OSTIA) (Good et al., 2020) provided by the United Kingdom Met Office. This was downloaded from the Copernicus Marine Environment Monitoring Service (CMEMS: https://marine.copernicus.eu, last access: 2 February 2024; https://doi.org/10.48670/moi-00168). The ability of the models to reproduce regional stratification patterns was assessed by Holt et al. (2022a), and an assessment of the ability of the AMM7 model configuration to reproduce regional temperature has been made by Tonani et al. (2019). Due to the lack of robust and unbiased large-scale seafloor temperature data covering the model domain, we did not assess temperature variations at the seafloor. However, the stratification assessment of Holt et al. (2022a) indicates that the ability of the models to reproduce seafloor temperature variations should be similar to that at the sea surface.

Figure 2Projected annual heatwave occurrence rate in the mid-century (2040–2059) and at the end of the century (2080–2099), as derived from five dynamically downscaled climate models under RCP 8.5. Heatwaves were defined as periods lasting at least 5 d where the daily temperature is greater than the 90th percentile of temperature in the baseline climatological period of 1990–2009.
While the impact of winter heatwaves has been observed in the region in a small number of instances (e.g. Atkinson et al., 2020), negative impacts of marine heatwaves have almost exclusively been assessed during the warm seasons during the months of spring and summer (e.g. Bass et al., 2023). Marine-heatwave projections should therefore be disaggregated seasonally (Li and Donner, 2023; Song et al., 2023) to separate warm-season (e.g. summer) heatwaves, which have well-established negative consequences, from the those occurring during the rest of the year, when they have poorly understood consequences. We therefore separated heatwaves by season.
In line with expectations, all models project an increase in sea temperatures across the northwestern European shelf by the end of the 21st century (Fig. 1). Reflecting the fact that climate models have broad climate sensitivities (Scafetta, 2022), projected temperature increases vary across the ensemble. The lowest projected increase in annual average surface temperature on the shelf between 1990–2009 and 2080–2099 is 1.34 °C in GFDL-ESM2M, and the highest is 4.14 °C in the MIROC-ESM model, with an average of 2.55 °C across the five-member ensemble. Notably, across all models, there is a higher level of warming in the seasonally stratified surface waters, which is notable in the northern North Sea (Fig. 1), compared with the seafloor. This reflects how increased thermal stratification (Holt et al., 2022a) will result in less warming translating to deeper waters in the future compared with today. Across the ensemble, surface warming during summer is projected to be 0.88 °C higher than at the seafloor, while differences in warming in winter are negligible (Fig. S1 in the Supplement).

Figure 4Projected average rate of heatwave occurrence at the sea surface for each season in 2080–2099 using five dynamically downscaled climate models and climate change scenario RCP 8.5. Each column shows the projection from one model.
Table 1Projected percentage of the time at which marine heatwaves occur in the future on the northwestern European shelf annually and across each season for the middle and end of the 21st century.

This large level of ocean warming translates to a large and sometimes rapid increase in annual marine-heatwave frequency across the northwestern European shelf across model runs (Figs. 2–4, Table 1). In line with warming levels, the MIROC-ESM run projects the highest levels of heatwave frequency, with these occurring almost year-round by the end of the 21st century across much of the shelf at the sea surface. Similarly, the GFDL-ESM2M model projection shows the lowest future frequency of marine heatwaves, but it still projects that surface heatwaves will occur for approximately 63 % of the year at the end of the 21st century on average across the shelf. The shelf average annual frequency of marine heatwaves at the surface in the mid-century ranges from 29.5 % to 90.5 %, and that at the end of the century ranges from 63.3 % to 99.0 %. Similarly, the annual frequency of marine heatwaves at the seafloor in the mid-century ranges from 39.7 % to 96.4 %, and that at the end of the century ranges from 77.2 % to 99.7 %.

Figure 5Marine heatwaves at the sea surface and seafloor in the first 20-year period when, on average, across the shelf, heatwaves occur for more than 50 % of the summer at the surface. The 20-year period shown in the top left of each panel indicates when the 50 % threshold is first exceeded. In the bottom right of each plot, the average fraction of time during which the shelf is under heatwave conditions at the surface or seafloor is shown. For example, CanESM2 projects that, in 2045–2064, surface heatwaves will occur for, on average, 50.2 % of the summer, but seafloor heatwaves will occur for 73.8 % of the summer.
While the pattern of increased heatwave occurrences is evident at both the sea surface and seafloor, the projections show that the increase is expected to be larger at the seafloor. This is reflected by mapped changes (Fig. 2) and time series of average changes in heatwaves (Fig. 3). Overall, the model projections show a clear pattern where there are minimal differences in terms of projected heatwaves at the sea surface and seafloor during winter when stratification is negligible, while there are pronounced differences in summer when waters are stratified (Figs. 3 and 4). We illustrated these differences by identifying the first 20-year period when, on average, surface waters are under heatwave conditions for at least 50 % of the summer. This highlights the magnitude of differences when temperatures will exceed upper thermal thresholds for species. Figure 5 shows that, during these 20-year periods, summer heatwaves in deep waters are much more frequent than at the surface. The most extreme difference is the projection from IPSL-CM5A-MR, which shows that, in 2060–2080, on average, the sea surface will be under heatwave conditions for 50.4 % of the summer, but the seafloor will be under heatwave conditions for 89.9 % of the summer. Furthermore, these differences are most pronounced in seasonally stratified waters, while permanently mixed waters, such as the southern North Sea, see smaller differences between the surface and seafloor.

Figure 6Average anomaly of the climatological heatwave temperature threshold during summer, as derived from five dynamically downscaled climate models. The threshold is defined as the 90th percentile of climatological temperature on each day in the baseline period of 1990–2009 using an 11 d window centred on each day. The anomaly is defined as the difference between the threshold and the average temperature on each day. The surface layer represents the sea surface cell in the model output, while the bottom layer represents the model cell closest to the seafloor. Column labels name the downscaled global climate model used, with OSTIA representing the thresholds derived from satellite sea surface temperature. Bias represents the difference between the model and satellite threshold; i.e. a negative bias implies that the model's temperature variability during summer is too low.
This difference between heatwaves at the surface and seafloor runs counter to the fact that warming is projected to be higher at the surface than at the seafloor. Instead, it should be viewed as consequence of the lower natural inter-annual variability of temperature at the seafloor. This is shown in Fig. 6, which shows how much warmer, on average, heatwave temperature thresholds are than the average temperature in the models and observational data. In seasonally stratified waters, the 90th-percentile threshold is much lower relative to average conditions at the seafloor than at the surface. Consequently, it takes lower warming levels to translate into more frequent heatwaves. Critically, we also find that the ability of the models to represent inter-annual variability in surface temperature varies, as measured by comparing the temperature anomaly of the 90th-percentile threshold with an observational figure (Fig. 6). Specific geographic features of individual projections may therefore be partly due to biases in the representation of inter-annual variability. For example, in the northern North Sea, the GFDL-ESM2M has lower inter-annual variability in summer than what is observed, which partly translates into higher future surface heatwaves than would otherwise be expected. These differences highlight the importance of an ensemble approach to projecting heatwaves.

Figure 7Projected average rate of marine-heatwave occurrence by category at the sea surface, averaged across the northwestern European shelf, using five dynamically downscaled climate models under RCP 8.5. Heatwaves are stacked by colour; i.e. the total frequency of heatwaves is shown in the top line. The left column shows the average frequency of heatwaves each year, and the right column shows the frequency during summer. A 20-year rolling average is shown, with the output being aligned to the final year in each 20-year period.
These differences in inter-annual variability have further consequences. Summer temperatures vary more than during the rest of the year (Fig. S2). As a consequence, we find that heatwaves increase in frequency more slowly during summer than during the rest of the year (Figs. 3 and 4, Table 1). This is most pronounced at the surface, where, across the ensemble, sea surface heatwaves occur, on average, 40.2 % of the time during summer and 52.8 % of the time annually in 2040–2059 and 73.1 % of the time during summer and 85.6 % of the time annually in 2080–2098. The impact of these differences is even more pronounced when the severity of heatwaves is considered (Fig. 7), where extreme sea surface heatwaves are much less likely in summer than they are on average. Notably, in four of the model projections, extreme surface heatwaves are less than 50 % as frequent in summer than during the rest of the year at the end of the century. This indicates that marine heatwaves need to be categorized at a seasonal level to accurately assess their impact.
Up until now, most research projecting future marine heatwaves in the world's oceans has focused on the sea surface, and changes are typically not disaggregated seasonally. We have shown that this may lead to an incomplete picture in shelf seas. On the northwestern European shelf, future seafloor heatwaves are expected to grow at a significantly faster rate than at the sea surface, while summer heatwaves are expected to be less frequent than during the rest of the year. This has nuanced implications for marine ecosystems.
Our study highlights the complex relationship between rising temperatures and marine heatwaves and how focusing on temperature change alone may mask many nuances. We find that, across the northwestern European shelf, seafloor temperatures are projected to rise at a lower rate than at the surface due to increasing thermal stratification (Holt et al., 2022a). However, a lower level of warming on the seafloor may not translate to lower levels of future marine heatwaves. In fact, due to the lower variability of seafloor temperatures, we find that lower levels of warming are required to shift them to heatwave conditions compared to in surface waters and, therefore, that it is more likely that seafloor habitats will experience more frequent heatwave events than the surface ocean in the region. This indicates that assessing future heatwaves purely based on surface waters is likely to significantly underestimate future heatwave impacts on many benthic communities in shelf waters. This finding has important implications for seafloor communities and processes in the region, especially for species where population dynamics and lower genetic plasticity resulting from millions of years of more stable thermal conditions may limit the ability of communities to adapt (Somero, 2010; Hiddink et al., 2014).
A critical finding in this study is that summer heatwaves in northwestern Europe are projected to be relatively less frequent and potentially significantly less severe than during the rest of the year. This is not because summer warming is expected to be less severe per se but rather because of how heatwave calculations are affected by present-day temperature variability. This indicates that assessing the impacts of marine heatwaves purely based on annual changes may overestimate their impacts based on the assumption that marine heatwaves primarily have a significant negative impact in summer. To date, assessments of the ecological impacts of marine heatwaves have largely focused on warm summer months (Smith et al., 2023) when temperatures reach their highest; the data regarding the potential ecological heatwaves in cooler months are still much sparser (e.g. Shanks et al., 2020). It is therefore critical that research establish whether heatwave impacts largely reside in summer months when temperatures are highest.
Increasing attention has been placed on defining marine heatwaves in ways meaningful to ecosystem management, with some arguing that a shifting baseline should supplement the fixed-baseline approach (Amaya et al., 2023a, b), with the latter being carried out here. A shifting-baseline approach is likely to be of significant value for pelagic ecosystems, which, as suggested by marine ecosystem models, can reorganize very rapidly in response to climate change. Pelagic ecosystems are likely to be adapted to a climate resembling a shifting baseline. However, it is unclear if the shifting-baseline approach is sensible for all ecological systems and, in particular, benthic systems. Seabed benthic species may have a poor ability to track more suitable habitats in response to extreme weather events due to organisms having low dispersal potential or being adapted to historically stabler, deeper water environments (Somero, 2010). This may partially explain why seabed invertebrates in the North Sea have been found to have a poor ability to shift range distributions in response to seabed temperature changes (Hiddink et al., 2014).
Identifying regions that are more resilient to climate change is an important task in providing scientific projections of relevance to marine management (Queirós et al., 2021). Notably, our multi-model ensemble shows that some seafloor regions, such as that of northwestern Ireland and the area west of the Norwegian Trench in the North Sea, are less impacted by future marine heatwaves than most of the northwestern European shelf. This finding indicates that some regions could be reasonably resilient to future heatwaves.
Our study highlights the importance of looking at heatwave impacts on waters deeper than the sea surface. The general conclusion of the study that seafloor heatwaves are likely to be greater in future than at the surface is likely to be transferable to most shelf seas due to the common existence of seasonal stratification. However, future research should consider the magnitude of the difference in other regions. Furthermore, our conclusion sits within the context of a growing body of research indicating that the sub-surface heatwaves have grown more rapidly than those at the surface (Sun et al., 2023a; He et al., 2024).
This study provides the most comprehensive assessment to date of future heatwaves on the northwestern European shelf. However, a number of aspects require future attention. For ecosystems and species that can reorganize quickly in response to climate change, projections using a shifting baseline (Giménez et al., 2024) may be more informative. Secondly, many species have critical temperatures, which can either trigger key life cycle events (Wilson et al., 2024) or represent thermal limits above which there is rapid mortality or tissue damage (Savva et al., 2018). Projecting future heatwaves based on known thermal thresholds for key species is therefore the next step in understanding how marine ecosystems will change in the future.
The projections for sea surface and seafloor temperatures are openly available: https://gws-access.jasmin.ac.uk/public/recicle/ (Holt et al., 2022b).
The supplement related to this article is available online at https://doi.org/10.5194/os-21-1255-2025-supplement.
RJW, AMQ, and YA conceived the research. RJW wrote the paper, with input and revisions from all of the authors.
The contact author has declared that none of the authors has any competing interests.
Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims made in the text, published maps, institutional affiliations, or any other geographical representation in this paper. While Copernicus Publications makes every effort to include appropriate place names, the final responsibility lies with the authors.
This article is part of the special issue “Special issue on ocean extremes (55th International Liège Colloquium)”. It is not associated with a conference.
We acknowledge the World Climate Research Programme, which, through its Working Group on Coupled Modelling, coordinated and promoted CMIP5. We thank the climate modeling groups for producing and making available their model output, the Earth System Grid Federation (ESGF) for archiving the data and providing access, and the multiple funding agencies who support CMIP6 and ESGF.
This research has been supported by the Natural Environment Research Council (grant nos. NE/M004120/1, NE/M003477/2, NE/X006271/1, NE/R015953/1, and NE/V016725/1) and the European Union's Horizon 2020 (grant no. 820989).
This paper was edited by Aida Alvera-Azcárate and reviewed by Claudia Hinrichs and one anonymous referee.
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