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3,800
AR6_WGII
447
14
Projections also suggest that warming-related increases in trophic efficiency lead to a 17% increase in the biomass of the deep-scattering layer (zooplankton and fish in the mesopelagic) by 2100
low
0
test
3,801
AR6_WGII
447
15
Observational studies appear to show that mesopelagic fishes adapted to warm water increased in abundance and distribution in the California Current associated with warming and the expansion of OMZ (Koslow et al., 2019), suggesting that some mesopelagic fish stocks might be resilient to a changing climate
medium
1
train
3,802
AR6_WGII
447
19
Moreover, different trophic levels within epipelagic food webs are responding at different rates
very high
3
train
3,803
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4
There is high agreement in model projections that the start of the phytoplankton Table 3.18 | Summary of previous IPCC assessments of phenological shifts and trophic mismatches Observations Projections AR5 WGII (Hoegh-Guldberg et al., 2014; Larsen et al., 2014) ‘Changes to sea temperature have altered the phenology, or timing of key life-history events such as plankton blooms, and migratory patterns, and spawning in fish and invertebrates, over recent decades
medium
1
train
3,804
AR6_WGII
448
5
There is medium to high agreement that these changes pose significant uncertainties and risks to fisheries, aquaculture and other coastal activities.’ The highly productive high-latitude spring bloom systems in the northeast Atlantic are responding to warming (medium evidence, high agreement), with the greatest changes being observed since the late 1970s in the phenology, distribution and abundance of plankton assemblages, and the reorganisation of fish assemblages, with a range of consequences for fisheries
high
2
train
3,805
AR6_WGII
448
8
This impact would be exacerbated if shifts in timing occur rapidly
medium
1
train
3,806
AR6_WGII
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9
SROCC (Bindoff et al., 2019a) ‘Phenology of marine ectotherms in the epipelagic systems related to ocean warming (high confidence) and the timing of biological events has shifted earlier
high
2
train
3,807
AR6_WGII
448
10
WGI AR6 Chapter 2 (Gulev et al., 2021) ‘Phenological metrics for many species of marine organisms have changed in the last half century
high
2
train
3,808
AR6_WGII
448
11
The changes vary with location and with species
high
2
train
3,809
AR6_WGII
448
12
There is a strong dependence of survival in higher trophic-level organisms (fish, exploited invertebrates, birds) on the availability of food at various stages in their life cycle, which in turn depends on the phenologies of both
high
2
train
3,810
AR6_WGII
448
16
Overall, the regional patterns are qualitatively similar under SSP1-2.6 and SSP5-8.5 but with greater magnitude and larger areas under SSP5-8.5
low
0
train
3,811
AR6_WGII
448
18
Furthermore, under RCP8.5, trophic mismatch events exceeding ±30 days (Asch et al., 2019) leading to fish-recruitment failure are expected to increase tenfold for geographic spawners across much of the North Atlantic, North Pacific and Arctic Ocean basins
low
0
train
3,812
AR6_WGII
449
3
Temperatures during the last Interglacial (~125 ka), which were warmer than today, led to poleward range shifts of reef corals
medium
1
train
3,813
AR6_WGII
449
4
Temperature has also driven marine range shifts over multi-million-year time scales
medium
1
train
3,814
AR6_WGII
449
5
Warming climates, even with low ocean- warming rates, inevitably decreased tropical marine biodiversity compared with middle latitudes
high
2
train
3,815
AR6_WGII
449
6
The paleorecord confirms that marine biodiversity has been vulnerable to climate warming both globally and regionally
very high
3
train
3,816
AR6_WGII
449
7
In extreme cases of warming (e.g., >5.2°C), marine mass extinctions occurred in the geological past, and there may be a relationship between warming magnitude and extinction toll
medium
1
train
3,817
AR6_WGII
449
8
A combination of warming and spreading anoxia caused marine extinctions in ancient episodes of rapid climate warming
high
2
train
3,818
AR6_WGII
449
9
The role of ocean acidification in ancient extinctions is yet to be resolved
low
0
train
3,819
AR6_WGII
451
4
At the community level, the magnitude and shape of projected future biodiversity changes differ depending on which groups are considered
medium
1
train
3,820
AR6_WGII
452
5
On longer time scales, alteration of energy flow through marine food webs may lead to ecological tipping points (Wernberg et al., 2016; Harley et al., 2017) after which the food web collapses into shorter, bottom-heavy trophic pyramids
medium
1
train
3,821
AR6_WGII
452
7
Table 3.20 | Summary of previous IPCC assessments of community composition and biodiversity Observations Projections AR5 (Hoegh-Guldberg et al., 2014; Pörtner et al., 2014) The paleoecological record shows that global climate changes comparable in magnitudes to those projected for the 21st century under all scenarios resulted in large-scale biome shifts and changes in community composition, and that for rates projected under RCP6 and 8.5 those changes were associated with species extinctions in some groups
high
2
train
3,822
AR6_WGII
452
8
Loss of corals due to bleaching has a potentially critical influence on the maintenance of marine biodiversity in the tropics (high confidence).Spatial shifts of marine species due to projected warming will cause high-latitude invasions and high local-extinction rates in the tropics and semi-enclosed seas
medium
1
train
3,823
AR6_WGII
452
9
Species richness and fisheries catch potential are projected to increase, on average, at mid and high latitudes (high confidence) and decrease at tropical latitudes
medium
1
train
3,824
AR6_WGII
452
11
Thereby, climate change will reassemble communities and affect biodiversity, with differences over time and between biomes and latitudes
high
2
train
3,825
AR6_WGII
452
12
However, specific quantitative projections by these models remain imprecise (low confidence).’ SROCC (Bindoff et al., 2019a) ‘Ocean warming has contributed to observed changes in biogeography of organisms ranging from phytoplankton to marine mammals (high confidence), consequently changing community composition (high confidence), and in some cases altering interactions between organisms and ecosystem function
medium
1
train
3,826
AR6_WGII
452
14
In addition, geographic barriers, such as land, [bounding the] poleward species range edge in semi-enclosed seas or low-oxygen water in deeper waters are projected to limit range shifts, resulting in a larger relative decrease in species richness (medium confidence).’ ‘The large variation in sensitivity between different zooplankton taxa to future conditions of warming and ocean acidification suggests elevated risk on community structure and inter-specific interactions of zooplankton in the 21st century
medium
1
train
3,827
AR6_WGII
452
15
Under continuing climate change, the projected loss of biodiversity may ultimately threaten marine ecosystem stability (medium confidence) (Albouy et al., 2020; Nagelkerken et al., 2020; Henson et al., 2021), altering both the functioning and structure of marine ecosystems and thus affecting service provisioning
medium
1
train
3,828
AR6_WGII
453
3
Abrupt ecosystem shifts have been observed in both large open-ocean ecosystems and coastal ecosystems (Section 3.4.2), with dramatic social consequences through significant loss of diverse ecosystem services
high
2
train
3,829
AR6_WGII
453
5
Abrupt ecosystem shifts are associated with large-scale patterns of climate variability (Alheit et al., 2019; Beaugrand et al., 2019; Lehodey et al., 2020), some of which are projected to intensify with climate change
medium
1
train
3,830
AR6_WGII
453
6
Over the past 60 years, abrupt ecosystem shifts have generally followed El Niño/ Southern Oscillation events of any strength, but some periods had geographically limited ecological shifts (~0.25% of the global ocean in 1984–1987) and others more extensive shifts (14% of the global ocean in 2012–2015)
medium
1
train
3,831
AR6_WGII
453
7
Typically, interacting drivers, such as eutrophication and overharvest, reduce ecosystem resilience to climate extremes (e.g., MHWs, cyclones) or gradual warming, and hence promote ecosystem shifts
high
2
train
3,832
AR6_WGII
453
8
Shifts in different ecosystems may be connected through common drivers or through cascading effects
medium
1
test
3,833
AR6_WGII
453
9
Recent MHWs (Section 3.2.2.1) have caused major ecosystem shifts and mass mortality in oceanic and coastal ecosystems, including corals, kelp forests and seagrass meadows (Sections 3.4.2.1, 3.4.2.3, 3.4.2.5, 3.4.2.6, 3.4.2.10; Cross-Chapter Box MOVING SPECIES in Chapter 5; Cross-Chapter Box EXTREMES in Chapter 2), with dramatic declines in species foundational for habitat formation or trophic flow, biodiversity declines, and biogeographic shifts in fish stocks
very high
3
train
3,834
AR6_WGII
454
10
Marine birds and mammals are vulnerable to climate-induced loss of breeding and foraging habitats such as sea ice (Section 3.4.2.12), sandy beaches (Section 3.4.2.6), salt marshes (Section 3.4.2.5) and seagrass beds
high
2
train
3,835
AR6_WGII
454
12
Marine mammals dependent on sea ice habitat are particularly vulnerable to warming
medium
1
train
3,836
AR6_WGII
455
1
Nevertheless, even under an intermediate emission scenario RCP4.5, increasing ice-free periods will likely reduce both recruitment and adult survival across most polar bear populations over the next four decades, threatening their existence
medium
1
train
3,837
AR6_WGII
455
2
Climate change is affecting marine food-web dynamics
high
2
train
3,838
AR6_WGII
455
3
Higher-vulnerability species include central-place foragers (confined to, for example, breeding colonies fixed in space), diet and habitat specialists, and species with restricted distributions such as marine mammal populations in SES
medium
1
train
3,839
AR6_WGII
455
4
Surface-feeding and piscivorous marine birds appear to be more vulnerable to food-web changes than diving seabirds and planktivorous seabirds
medium
1
train
3,840
AR6_WGII
455
6
Marine birds are vulnerable to phenological shifts in food-web dynamics, as they have limited phenotypic plasticity of reproductive timing, with potentially little scope for evolutionary adaptation
medium
1
train
3,841
AR6_WGII
456
2
Also, climate-change driven distributional shifts have strengthened interactions with other anthropogenic impacts, through, for example, increasing risks of ship strikes and bycatch (medium confidence) (e.g., Hauser et al., 2018; Krüger et al., 2018; Record et al., 2019; Santora et al., 2020).Box 3.2 (continued) the risk of abrupt ecosystem shifts
high
2
train
3,842
AR6_WGII
456
4
However, where climate change is a dominant driver, ecosystem collapses increasingly cause permanent transitions
high
2
train
3,843
AR6_WGII
456
5
Over the coming decades, MHWs are projected to very likely become more frequent under all emission scenarios (Section 3.2; WGI AR6 Chapter 9; Fox-Kemper et al., 2021), with intensities and rates too high for recovery of degraded foundational species, habitats or biodiversity
medium
1
train
3,844
AR6_WGII
456
9
In contrast, the anthropogenic signal in phytoplankton community structure, which has a lower natural variability, will emerge under RCP8.5 across 63% of the ocean by 2100 when two standard deviations are used (limited evidence) (Dutkiewicz et al., 2019).Table 3.21 | Summary of previous IPCC assessments of observed and projected abrupt ecosystem shifts and extreme events Observations Projections AR5 (Wong et al., 2014) Observations of abrupt ecosystem shifts and extreme events were not assessed in this report.‘Warming and acidification will lead to coral bleaching, mortality, and decreased constructional ability
high
2
train
3,845
AR6_WGII
456
10
Temperate seagrass and kelp ecosystems will decline with the increased frequency of heatwaves and sea temperature extremes as well as through the impact of invasive subtropical species (high confidence).’ SROCC (Collins et al., 2019a) ‘Marine heatwaves (MHWs), periods of extremely high ocean temperatures, have negatively impacted marine organisms and ecosystems in all ocean basins over the last two decades, including critical foundation species such as corals, seagrasses and kelps (very high confidence).’‘Marine heatwaves are projected to further increase in frequency, duration, spatial extent and intensity (maximum temperature)
very high
3
train
3,846
AR6_WGII
456
11
Climate models project increases in the frequency of marine heatwaves by 2081–2100, relative to 1850–1900, by approximately 50 times under RCP8.5 and 20 times under RCP2.6
medium
1
train
3,847
AR6_WGII
456
12
Extreme El Niño events are projected to occur about twice as often under both RCP2.6 and RCP8.5 in the 21st century when compared to the 20th century (medium confidence).’ ‘Limiting global warming would reduce the risk of impacts of MHWs, but critical thresholds for some ecosystems (e.g., kelp forests, coral reefs) will be reached at relatively low levels of future global warming
high
2
train
3,848
AR6_WGII
457
2
Better accounting for multiple interacting factors in ESMs (see Box 3.1) will provide insight into how marine ecosystems will respond to future climate
high
2
train
3,849
AR6_WGII
457
14
Using an ensemble of global-scale marine ecosystem and fisheries models (Fish-MIP) (Tittensor et al., 2018) with the CMIP5 ESM ensemble, SROCC concludes that projected ocean warming and decreased phytoplankton production and biomass will reduce global marine animal biomass during the 21st century
medium
1
train
3,850
AR6_WGII
460
1
These declines result from combined warming and decreased primary production (with low confidence in future changes in primary production; Section 3.4.3.5) and are amplified at each trophic level within all ESM and marine ecosystem model projections across all scenarios
medium
1
train
3,851
AR6_WGII
461
3
Owing to contradictory observations there is currently uncertainty about the future trends of major upwelling systems and how their drivers (enhanced productivity, acidification and hypoxia) will shape ecosystem characteristics
low
0
test
3,852
AR6_WGII
461
4
Animal biomass Observed changes in animal biomass were not assessed in this report.‘The climate-change-induced intensification of ocean upwelling in some eastern boundary systems, as observed in the last decades, may lead to regional cooling, rather than warming, of surface waters and cause enhanced productivity
medium
1
train
3,853
AR6_WGII
461
8
The strong dependence of the projected declines on phytoplankton production
low
0
train
3,854
AR6_WGII
461
11
Some increases are projected in the polar regions, due to enhanced stratification in the surface ocean, reduced primary production and shifts towards small phytoplankton
medium
1
train
3,855
AR6_WGII
462
4
Overall, ocean warming and decreased phytoplankton production and biomass will drive a global decline in biomass for zooplankton (low confidence), marine animals (medium confidence) and seafloor benthos (low confidence), with regional differences in the direction and magnitude of changes
high
2
train
3,856
AR6_WGII
462
5
There is increasing evidence that responses will amplify throughout the food web and at ocean depths, with relatively modest changes in surface primary producers translating into substantial changes at higher trophic levels and for deep-water benthic communities
medium
1
train
3,857
AR6_WGII
462
9
This is consistent with previous assessments that identified ocean warming and increased stratification as the main drivers
high
2
train
3,858
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462
16
Furthermore, accurate simulation of many of the biogeochemical tracers upon which NPP depends (e.g., the distribution of iron; Tagliabue et al., 2016; Bindoff et al., 2019a) remains a significant and ongoing challenge to ESMs
high
2
train
3,859
AR6_WGII
464
1
Increasing model complexity with more widespread representation of ocean biogeochemical processes between CMIP5 and CMIP6, and inclusion of more than one or two classes of phyto- and zooplankton, will provide opportunities to improve assessments of how climate-induced drivers affect different components of biological carbon pump in the epipelagic ocean, as well as changes in the efficiency and magnitude of carbon export in the deep ocean
high
2
train
3,860
AR6_WGII
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5
Model results indicate that sea surface temperatures (high confidence), Arctic sea ice (high confidence), surface ocean acidification (very high confidence) and surface ocean deoxygenation
very high
3
train
3,861
AR6_WGII
464
7
In an overshoot scenario in which CO 2 returns to 2040 levels by 2100 (SSP5-3.4-OS; O’Neill et al., 2016), SST and Arctic sea ice do not fully return by 2100 to levels prior to the CO 2 peak
medium
1
train
3,862
AR6_WGII
464
8
Models also indicate that global sea level rise, as well as warming, ocean acidification and deoxygenation at depth, are irreversible for centuries or longer
very high
3
train
3,863
AR6_WGII
464
11
A small decrease in productivity is evident globally for the period 1998–2015, but regional changes are larger and of opposing signs
low
0
train
3,864
AR6_WGII
465
1
The deep sea covers >63% of Earth’s surface (Costello and Cheung, 2010) and is exposed to climate-driven changes in abyssal, intermediate and surface waters that influence sinking fluxes of particulate organic matter
high
2
train
3,865
AR6_WGII
465
7
Acute mortality of some reef-forming cold-water corals to laboratory-simulated warming (Lunden et al., 2014) suggests that both long-term warming and the increase of MHWs in intermediate and deep waters (Elzahaby and Schaeffer, 2019) could pose significant risk to associated ecosystems
high
2
test
3,866
AR6_WGII
465
9
The extension and intensification of deep-water acidification (Section 3.2.3.1) has been identified as a further key risk to deep-water coral ecosystems
medium
1
train
3,867
AR6_WGII
465
12
Desmophyllum pertusum7and Madrepora oculata maintain calcification in moderately low pH (7.75) and near-saturation of aragonite (Hennige et al., 2014; Maier et al., 2016; Büscher et al., 2017), but lower pH (7.6) and corrosive conditions lead to net dissolution of D. pertusum skeletons
high
2
train
3,868
AR6_WGII
465
15
In OMZ regions (Section 3.2.3.2), benthic species distributions (Sperling et al., 2016; Levin, 2018; Gallo et al., 2020), abundance and composition of demersal fishes in canyons (De Leo et al., 2012) and deep-pelagic zooplankton (Wishner et al., 2018) follow oxygen gradients, indicating that deep-sea biodiversity and ecosystem structure will be impacted by extension of hypoxic areas
medium
1
train
3,869
AR6_WGII
465
18
Despite mortality and functional impacts from low oxygen concentrations observed in aquaria (Lunden et al., 2014), recent observations of the deep-water coral D. pertusum suggest adaptive capacity to hypoxia among specimens from OMZ regions that are highly productive
low
0
train
3,870
AR6_WGII
466
3
Climate-driven impacts further limit the resilience of deep-sea ecosystems to impacts from human activities
high
2
train
3,871
AR6_WGII
466
6
The spatial resolution of CMIP5 models is too coarse to robustly project changes in mesoscale circulation at the seafloor (Sulpis et al., 2019), on which deep-sea ecosystems depend for organic material supplies and dispersal of planktonic and planktotrophic larvae
high
2
train
3,872
AR6_WGII
467
5
Biodiversity has changed in association with ocean warming and loss of sea ice, sea level rise, coral bleaching, marine heat waves and upwelling changes
high
2
test
3,873
AR6_WGII
467
6
Overlapping non-climate drivers (Section 3.1) also decrease ocean and coastal ecosystem biodiversity
very high
3
train
3,874
AR6_WGII
467
9
Projected changes in biodiversity due to climate change (Section 3.4.3.3.3) are expected to alter the flow and array of ocean and coastal ecosystem services
high
2
train
3,875
AR6_WGII
467
10
Non-indigenous marine species are major agents of ocean and coastal biodiversity change, and climate and non-climate drivers interact to support their movement and success
high
2
train
3,876
AR6_WGII
467
11
At times, non-indigenous species act invasively and outcompete indigenous species, causing regional biodiversity shifts and altering ecosystem function, as seen in the Mediterranean region
high
2
train
3,877
AR6_WGII
467
14
Non-climate drivers, especially marine shipping in newly ice-free locations (Chan et al., 2019), fishing pressure (Last et al., 2011), aquaculture of non-indigenous species (Mach et al., 2017; Ruby and Ahilan, 2018) and marine pollution and debris (Gall and Thompson, 2015; Carlton et al., 2018; Carlton and Fowler, 2018; Lasut et al., 2018; Miralles et al., 2018; Rech et al., 2018; Therriault et al., 2018), promote range shifts and movement of non-indigenous species
high
2
train
3,878
AR6_WGII
467
16
Invasive marine species can alter species behaviour, reduce indigenous species abundance, reduce water clarity, bioaccumulate more heavy metals than indigenous species and inhibit ecosystem resilience in the face of extreme events
medium
1
train
3,879
AR6_WGII
468
23
Catch composition is changing in many locations fished by smaller-scale, less-mobile commercial, artisanal and recreational fisheries
high
2
train
3,880
AR6_WGII
468
25
Where possible, fishers are maintaining harvests by broadening catch diversity, traveling poleward and changing gear and strategies
high
2
train
3,881
AR6_WGII
469
1
Both positive and negative impacts result for food security through fisheries (medium confidence), local cultures and livelihoods (medium confidence), and tourism and recreation
medium
1
train
3,882
AR6_WGII
469
2
The impacts on ecosystem services have negative consequences for health and well-being (medium confidence), and for Indigenous Peoples and local communities dependent on fisheries (high confidence) (1.1, 1.5, 3.2.1, 5.4.1, 5.4.2, Figure SPM.2)’ (SROCC SPM A.8; IPCC, 2019c).‘Long-term loss and degradation of marine ecosystems compromises the ocean’s role in cultural, recreational, and intrinsic values important for human identity and well-being
medium
1
train
3,883
AR6_WGII
469
3
Biodiversity (Section 3.5.2)‘[Climate] Impacts are already observed on [coastal ecosystem] habitat area and biodiversity, as well as ecosystem functioning and services
high
2
train
3,884
AR6_WGII
469
4
Food provision (Section 3.5.3)‘Warming-induced changes in the spatial distribution and abundance of some fish and shellfish stocks have had positive and negative impacts on catches, economic benefits, livelihoods, and local culture
high
2
train
3,885
AR6_WGII
469
5
There are negative consequences for Indigenous Peoples and local communities that are dependent on fisheries
high
2
train
3,886
AR6_WGII
469
6
Shifts in species distributions and abundance has challenged international and national ocean and fisheries governance, including in the Arctic, North Atlantic and Pacific, in terms of regulating fishing to secure ecosystem integrity and sharing of resources between fishing entities (high confidence) (3.2.4, 3.5.3, 5.4.2, 5.5.2, Figure SPM.2)’ (SROCC SPM A.8.1; IPCC, 2019c).‘Future shifts in fish distribution and decreases in their abundance and fisheries catch potential due to climate change are projected to affect income, livelihoods, and food security of marine resource-dependent communities
medium
1
train
3,887
AR6_WGII
469
7
Long-term loss and degradation of marine ecosystems compromises the ocean’s role in cultural, recreational, and intrinsic values important for human identity and well-being
medium
1
test
3,888
AR6_WGII
469
9
The emerging demand for alternative energy sources is expected to generate economic opportunities for the ocean renewable energy sector (high confidence), although their potential may also be affected by climate change
low
0
train
3,889
AR6_WGII
469
10
Habitat creation and maintenance (Section 3.5.5.1)‘[Climate] Impacts are already observed on [coastal ecosystem] habitat area and biodiversity, as well as ecosystem functioning and services
high
2
train
3,890
AR6_WGII
469
13
Climate regulation and air quality (Section 3.5.5.2)‘Global ocean heat content continued to increase throughout [the 1951 to present] period, indicating continuous warming of the entire climate system
very high
3
train
3,891
AR6_WGII
469
15
This is projected to result in a higher proportion of emitted CO 2 remaining in the atmosphere
high
2
train
3,892
AR6_WGII
470
2
Technology-based adaptations (Section 3.6.3) have minimised aquaculture losses from ocean acidification, including early-warning systems to guide hatchery operations and culturing resilient shellfish Ecosystem service and chapter subsectionObserved impacts Projected impacts Observed impacts on marine organisms’ contribution to climate regulation not previously assessed.‘The effect of climate change on marine biota will alter their contribution to climate regulation, that is, the maintenance of the chemical composition and physical processes in the atmosphere and oceans
high
2
train
3,893
AR6_WGII
470
3
Provision of freshwater, maintenance of water quality, regulation of pathogens (Section 3.5.5.3)Observed climate impacts on salinisation of coastal soil and groundwater not previously assessed.‘In the absence of more ambitious adaptation efforts compared to today, and under current trends of increasing exposure and vulnerability of coastal communities, risks, such as erosion and land loss, flooding, salinisation, and cascading impacts due to mean sea level rise and extreme events are projected to significantly increase throughout this century under all greenhouse gas emissions scenarios
very high
3
train
3,894
AR6_WGII
470
8
Regulation of physical hazards (Section 3.5.5.4)‘Coastal ecosystems are already impacted by the combination of sea level rise, other climate-related ocean changes, and adverse effects from human activities on ocean and land (high confidence)... Coastal and near-shore ecosystems including saltmarshes, mangroves, and vegetated dunes in sandy beaches,...provide important services including coastal protection...(high confidence)’ (SROCC Chapter 4 Executive Summary; Oppenheimer et al., 2019).‘The decline in warm water coral reefs is projected to greatly compromise the services they provide to society, such as...coastal protection
high
2
train
3,895
AR6_WGII
470
10
However, the effect of these changes is not yet reflected in a weakening trend of the contemporary (1960–2019) ocean sink
high
2
train
3,896
AR6_WGII
470
14
Cultural services (Section 3.5.6)‘Climate change impacts on marine ecosystems and their services put key cultural dimensions of lives and livelihoods at risk
medium
1
train
3,897
AR6_WGII
470
15
This includes potentially rapid and irreversible loss of culture and local knowledge and Indigenous knowledge, and negative impacts on traditional diets and food security, aesthetic aspects, and marine recreational activities (medium confidence)’ (SROCC SPM B.8.4; IPCC, 2019c).‘Future shifts in fish distribution and decreases in their abundance and fisheries catch potential due to climate change are projected to affect income, livelihoods, and food security of marine resource-dependent communities
medium
1
train
3,898
AR6_WGII
470
16
Long-term loss and degradation of marine ecosystems compromises the ocean’s role in cultural, recreational, and intrinsic values important for human identity and well-being
medium
1
train
3,899
AR6_WGII
471
1
Laboratory studies show that ocean acidification decreases the fitness, growth or survival of many economically and culturally important larval or juvenile shelled mollusks
high
2
train