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3,600
AR6_WGII
424
6
The increased water depth due to coral loss and reef erosion, as well as reduced structural complexity, will limit wave attenuation and exacerbate the risk of flooding from SLR on reef- Table 3.3 | Summary of previous IPCC assessments of coral reefs Observations Projections AR5 (Hoegh-Guldberg et al., 2014; Wong et al., 2014) Coral reefs are one of the most vulnerable marine ecosystems
high
2
train
3,601
AR6_WGII
424
7
Mass coral bleaching and mortality, triggered by positive temperature anomalies
high
2
train
3,602
AR6_WGII
424
8
Ocean acidification reduces biodiversity and the calcification rate of corals (high confidence) while at the same time increasing the rate of dissolution of the reef framework
medium
1
train
3,603
AR6_WGII
424
12
SROCC (Bindoff et al., 2019a) ‘New evidence since AR5 and SR15 confirms the impacts of ocean warming and acidification on coral reefs (high confidence), enhancing reef dissolution and bioerosion (high confidence), affecting coral species distribution and leading to community changes
high
2
train
3,604
AR6_WGII
424
13
The rate of SLR (primarily noticed in small reef islands) may outpace the growth of reefs to keep up, although there is low agreement in the literature (low confidence).’ ‘Reefs are further exposed to other increased impacts, such as enhanced storm intensity, turbidity and increased runoff from the land
high
2
train
3,605
AR6_WGII
424
14
Recovery of coral reefs resulting from repeated disturbance events is slow
high
2
train
3,606
AR6_WGII
424
15
Only few coral reef areas show some resilience to global change drivers (low confidence).’‘Coral reefs will face very high risk at temperatures 1.5°C of global sea surface warming (very high confidence).’ ‘Almost all coral reefs will degrade from their current state, even if global warming remains below 2°C (very high confidence), and the remaining shallow coral reef communities will differ in species composition and diversity from present reefs
very high
3
train
3,607
AR6_WGII
424
16
This will greatly diminish the services they provide to society, such as food provision (high confidence), coastal protection (high confidence) and tourism (medium confidence).’ ‘The very high vulnerability of coral reefs to warming, ocean acidification, increasing storm intensity and SLR under climate change, including enhanced bioerosion
high
2
train
3,608
AR6_WGII
425
1
Local coral reef fish species richness is projected to decline due to the impacts of warming on coral cover and diversity
high
2
train
3,609
AR6_WGII
425
3
Major reef crises in the past 300 million years were governed by hyperthermal events (medium confidence) (Section 3.2.4.4; Cross-Chapter Box PALEO in Chapter 1) longer in time scale than anthropogenic climate change, during which net coral reef accretion was more strongly affected than biodiversity
medium
1
test
3,610
AR6_WGII
425
10
Recovery and restoration efforts that target heat- resistant coral populations and culture heat-tolerant algal symbionts have the greatest potential of effectiveness under future warming
high
2
train
3,611
AR6_WGII
425
12
In summary, additional evidence since SROCC and SR15 (Table 3.3) finds that living coral and reef growth are declining due to warming and MHWs
very high
3
train
3,612
AR6_WGII
425
13
Coral reefs are under threat of transitioning to net erosion with >1.5°C of global warming
high
2
train
3,613
AR6_WGII
425
14
The effectiveness of conservation efforts to sustain living coral area, coral diversity and reef growth is limited for the majority of the world’s reefs with >1.5°C of global warming
high
2
train
3,614
AR6_WGII
425
20
For example, the collapse of sea star populations in the Northeast Pacific due to a MHW-related disease outbreak (Hewson et al., 2014; Menge et al., 2016; Miner et al., 2018; Schiebelhut et al., 2018), including 80–100% loss of the common predatory sunflower star, Pycnopodia helianthoides
very high
3
train
3,615
AR6_WGII
425
21
Multiple lines of evidence find that foundational calcifying organisms such as mussels are at high risk of decline due to both the individual and synergistic effects of warming, acidification and hypoxia
high
2
train
3,616
AR6_WGII
425
23
Experiments show that ocean acidification negatively impacts mussel physiology
very high
3
train
3,617
AR6_WGII
425
24
Net calcification and abundance of mussels and other foundational species, including oysters, are expected to decline due to ocean acidification (very high confidence) (Kwiatkowski et al., 2016; Sunday et al., 2016; McCoy et al., 2018; Meng et al., 2018), causing the reorganisation of communities
high
2
train
3,618
AR6_WGII
426
10
Experiments indicate that warming reduces calcification by coralline algae
high
2
train
3,619
AR6_WGII
429
1
The upper vertical limits of some species will also be constrained by climate change
high
2
train
3,620
AR6_WGII
429
2
Experimental evidence since previous assessments further indicates that acidification decreases abundance and richness of calcifying species
high
2
train
3,621
AR6_WGII
429
3
Synergistic effects of warming and acidification will promote shifts towards macroalgal dominance in some ecosystems (medium confidence) and lead to reorganisation of communities
medium
1
train
3,622
AR6_WGII
429
8
Recent research (Straub et al., 2019; Butler et al., 2020; Filbee-Dexter et al., 2020b; Tait et al., 2021) supports the findings of previous assessments (Table 3.5) that kelp and other seaweeds in most regions are undergoing mass mortalities from high temperature extremes and range shifts from warming
very high
3
train
3,623
AR6_WGII
429
12
The most prominent effects are range shifts of species in response to ocean warming (high confidence) and changes in species distribution and abundance (high confidence) mostly in relation to ocean warming and acidification.’ ‘The dramatic decline of biodiversity in mussel beds of the Californian coast has been attributed to large-scale processes associated with climate-related drivers [...] (high confidence).’‘The abundance and distribution of rocky shore species will continue to change in a warming world
high
2
train
3,624
AR6_WGII
429
13
For example, the long-term consequences of ocean warming on mussel beds of the northeast Pacific are both positive (increased growth) and negative (increased susceptibility to stress and of exposure to predation) (medium confidence).’ ‘Observations performed near natural CO 2 vents in the Mediterranean Sea show that diversity, biomass and trophic complexity of rocky shore communities will decrease at future pH levels (high confidence).’ SR15 (Hoegh-Guldberg et al., 2018a) ‘Changes in ocean circulation can have profound impacts on [temperate] marine ecosystems by connecting regions and facilitating the entry and establishment of species in areas where they were unknown before (‘tropicalization’ ...) as well as the arrival of novel disease agents (medium agreement, limited evidence).’‘In the transition to 1.5°C, changes to water temperatures are expected to drive some species (e.g., plankton, fish) to relocate to higher latitudes and cause novel ecosystems to assemble
high
2
train
3,625
AR6_WGII
429
14
Other ecosystems (e.g., kelp forests, coral reefs) are relatively less able to move, however, and are projected to experience high rates of mortality and loss
very high
3
train
3,626
AR6_WGII
429
15
SROCC (Bindoff et al., 2019a) Intertidal rocky shores ecosystems are highly sensitive to ocean warming, acidification and extreme heat exposure during low tide emersion
high
2
train
3,627
AR6_WGII
429
17
These ecosystems have low to moderate adaptive capacity, as they are highly sensitive to ocean temperatures and acidification.’ ‘Benthic species will continue to relocate in the intertidal zones and experience mass mortality events due to warming
high
2
train
3,628
AR6_WGII
429
18
Interactive effects between acidification and warming will exacerbate the negative impacts on rocky shore communities, causing a shift towards a less diverse ecosystem in terms of species richness and complexity, increasingly dominated by macroalgae
high
2
train
3,629
AR6_WGII
430
1
Warming is driving range contraction and extirpation at the warm edge of species’ ranges and expansions at the cold range edge
very high
3
train
3,630
AR6_WGII
430
2
Local declines in populations of kelp and other canopy-forming seaweeds driven by MHWs and other stressors have caused irreversible shifts to turf- or urchin-dominated ecosystems, with lower productivity and biodiversity (high confidence) (Filbee-Dexter and Scheibling, 2014; Filbee-Dexter and Wernberg, 2018; Rogers-Bennett and Catton, 2019; Beas-Luna et al., 2020; Stuart-Smith et al., 2021), ecosystems dominated by warm- affinity seaweeds or coral
high
2
train
3,631
AR6_WGII
430
9
While reducing non-climate drivers can help prevent kelp loss from warming and MHWs, there is limited potential for restoration of kelp ecosystems after transition to urchin-dominant ecosystems
high
2
train
3,632
AR6_WGII
430
12
Active reseeding of wild kelp populations through transplantation and propagation of warm-tolerant genotypes (Coleman et al., 2020b; Alsuwaiyan et al., 2021) can overcome low dispersal rates of many kelp species and facilitate effective restoration
medium
1
train
3,633
AR6_WGII
430
13
Building on the conclusions of SROCC, this assessment finds that kelp ecosystems are expected to decline and undergo changes in community structure in the future due to warming and increasing frequency and intensity of MHWs
high
2
train
3,634
AR6_WGII
430
14
Risk of loss of kelp ecosystems Table 3.5 | Summary of previous IPCC assessments of kelp ecosystems Observations Projections AR5 (Wong et al., 2014) ‘Kelp forests have been reported to decline in temperate areas in both hemispheres, a loss involving climate change
high
2
train
3,635
AR6_WGII
430
15
Decline in kelp populations attributed to ocean warming has been reported in southern Australia and the north coast of Spain.’‘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).’ ‘Climate change will contribute to the continued decline in the extent of [...] kelps in the temperate zone (medium confidence) and the range of [...] kelps in the Northern Hemisphere will expand poleward (high confidence).’ SR15 (Hoegh-Guldberg et al., 2018a) Observed movement of kelp ecosystems not assessed.‘In the transition to 1.5°C of warming, changes to water temperatures will drive some species (e.g., plankton, fish) to relocate to higher latitudes and cause novel ecosystems to assemble
high
2
train
3,636
AR6_WGII
430
16
Other ecosystems (e.g., kelp forests, coral reefs) are relatively less able to move, however, and are projected to experience high rates of mortality and loss (very high confidence).’ SROCC (Bindoff et al., 2019a) ‘Kelp forests have experienced large-scale habitat loss and degradation of ecosystem structure and functioning over the past half century, implying a moderate to high level of risk at present conditions of global warming (high confidence).’ ‘The abundance of kelp forests has decreased at a rate of ~2% per year over the past half century, mainly due to ocean warming and marine heat waves [...], as well as from other human stressors (high confidence).’ ‘Changes in ocean currents have facilitated the entry of tropical herbivorous fish into temperate kelp forests decreasing their distribution and abundance (medium confidence).’ ‘The loss of kelp forests is followed by the colonisation of turfs, which contributes to the reduction in habitat complexity, carbon storage and diversity (high confidence).’Kelp forests will face moderate to high risk at temperatures above 1.5°C global sea surface warming
high
2
train
3,637
AR6_WGII
431
2
Although these coastal ecosystems have historically been sensitive to erosion-accretion cycles driven by sea level, drought and storms (high confidence) (Peteet et al., 2018; Wang et al., 2018c; Jones et al., 2019b; Urrego et al., 2019; Hapsari et al., 2020; Zhao et al., 2020b), they were impacted for much of the 20th century primarily by non-climate drivers
very high
3
train
3,638
AR6_WGII
431
3
Nevertheless, the influence of climate-induced drivers has become more apparent over recent decades
medium
1
train
3,639
AR6_WGII
431
4
Estuarine biota are sensitive to warming
high
2
train
3,640
AR6_WGII
431
5
MHWs can be more severe in estuaries than in adjacent coastal seas (Lonhart et al., 2019), causing conspicuous impacts
very high
3
train
3,641
AR6_WGII
431
6
Relative SLR extends the upstream limit of saline waters (high confidence) (Harvey et al., 2020; Jiang et al., 2020) and alters tidal ranges
high
2
train
3,642
AR6_WGII
431
7
Elevated water levels also alter submergence patterns for intertidal habitat (high confidence) (Andres et al., 2019), moving high-water levels inland (high confidence) (Peteet et al., 2018; Appeaning Addo et al., 2020; Liu et al., 2020e) and increasing the salinity of coastal water tables and soils
high
2
train
3,643
AR6_WGII
431
8
These processes favour inland and/or upstream migration of intertidal habitat, where it is unconstrained by infrastructure, topography or other environmental features
high
2
train
3,644
AR6_WGII
431
11
Overall, changing salinity and submergence patterns decrease the ability of shoreline vegetation to trap sediment (Xue et al., 2018), reducing accretion rates and increasing the vulnerability of estuarine shorelines to submergence by SLR and erosion by wave action
medium
1
train
3,645
AR6_WGII
431
14
The same phenomena alter salinity gradients, which are the primary drivers of estuarine species distributions
high
2
train
3,646
AR6_WGII
431
16
Acidification of estuarine water is a growing hazard (medium confidence) (Doney et al., 2020; Scanes et al., 2020a; Cai et al., 2021), and resident organisms display sensitivity to altered pH in laboratory settings
medium
1
train
3,647
AR6_WGII
431
20
Warming (including MHWs) and eutrophication interact to decrease estuarine oxygen content and pH, increasing the vulnerability of animals to MHWs (Brauko et al., 2020) and exacerbating the incidence and impact of dead zones
medium
1
train
3,648
AR6_WGII
431
22
All these impacts are projected to escalate under future climate change, but their magnitude depends on the amount of warming, the socioeconomic development pathway and implementation of adaptation strategies
medium
1
train
3,649
AR6_WGII
431
23
Modelling studies (Lopes et al., 2019; Rodrigues et al., 2019; White et al., 2019; Zhang and Li, 2019; Hong et al., 2020; Krvavica and Ružić, 2020; Liu et al., 2020e; Shalby et al., 2020) suggest that responses of estuaries to SLR will be complex and context dependent (Khojasteh et al., 2021), but project that salinity, tidal range, storm-surge amplitude, depth and stratification will increase with SLR (medium confidence), and that marine-dominated waters will penetrate farther upstream
high
2
train
3,650
AR6_WGII
431
24
Without careful management of freshwater inputs, sediment augmentation and/or the restoration of shorelines to more natural states, transformation and loss of intertidal areas and wetland vegetation will increase with SLR (high confidence) (Doughty et al., 2019; Leuven et al., 2019; Yu et al., 2019; Raw et al., 2020; Shih, 2020; Stein et al., 2020), with small, shallow microtidal estuaries being more vulnerable to impacts than deeper estuaries with well-developed sediments
medium
1
train
3,651
AR6_WGII
431
25
Warming and MHWs will enhance stratification and deoxygenation in shallow lagoons
medium
1
train
3,652
AR6_WGII
432
3
Since AR5 and SROCC, syntheses have emphasised that the vulnerability of rooted wetland ecosystems to climate-induced drivers is exacerbated by non-climate drivers (high confidence) (Elliott et al., 2019; Ostrowski et al., 2021; Williamson and Guinder, 2021) and climate Table 3.6 | Summary of previous IPCC assessments of estuaries, deltas and coastal lagoons Observations Projections AR5 (Wong et al., 2014) Humans have impacted lagoons, estuaries and deltas (high to very high confidence), but non-climate drivers have been the primary agents of change
very high
3
train
3,653
AR6_WGII
432
4
In estuaries and lagoons, nutrient inputs have driven eutrophication, which has modified food-web structures (high confidence) and caused more-intense and longer-lasting hypoxia, more-frequent occurrence of harmful algal blooms and enhanced emissions of nitrous oxide
high
2
train
3,654
AR6_WGII
432
5
In deltas, land-use changes and associated disruption of sediment dynamics and land subsidence have driven changes that have been exacerbated by relative SLR and episodic events, including river floods and oceanic storm surges
very high
3
train
3,655
AR6_WGII
432
6
Increased coastal flooding, erosion and saltwater intrusions have led to degradation of ecosystems (very high confidence).Future changes in climate impact-drivers such as warming, acidification, waves, storms, sea level rise (SLR) and runoff will have consequences for ecosystem function and services in lagoons and estuaries
high
2
train
3,656
AR6_WGII
432
7
Warming, changes in precipitation and changes in wind strength can interact to alter water-column salinity and stratification (medium confidence), which could impact water column oxygen content
medium
1
train
3,657
AR6_WGII
432
8
Land-use change, SLR and intensifying storms will alter deposition-erosion dynamics, impacting shoreline vegetation and altering turbidity
medium
1
train
3,658
AR6_WGII
432
10
The projected impacts of climate change on deltas are associated mainly with pluvial floods and SLR, which will amplify observed impacts of interacting climate and non-climate drivers
high
2
train
3,659
AR6_WGII
432
11
Estuaries, deltas and lagoons were not assessed in this report.Under both a 1.5°C and 2°C of warming, relative to the pre-industrial era, deltas are expected to be highly threatened by SLR and localised subsidence
high
2
test
3,660
AR6_WGII
432
12
The slower rate of SLR associated with 1.5°C of warming poses smaller risks of flooding and salinisation (high confidence), and facilitates greater opportunities for adaptation, including managing and restoring natural coastal ecosystems and infrastructure reinforcement
medium
1
train
3,661
AR6_WGII
432
14
Other feedbacks, such as landward migration of wetlands and the adaptation of infrastructure, remain important (medium confidence).’ SROCC (Bindoff et al., 2019a) Increased seawater intrusion caused by SLR has driven upstream redistribution of marine biotic communities in estuaries (medium confidence) where physical barriers, such as the availability of benthic substrates, do not limit availability of suitable habitats
medium
1
train
3,662
AR6_WGII
432
15
Warming has driven poleward range shifts in species’ distributions among estuaries
medium
1
train
3,663
AR6_WGII
432
16
Interactions between warming, eutrophication and hypoxia have increased the incidence of harmful algal blooms (high confidence), pathogenic bacteria, such as Vibrio species, (low confidence) and mortalities of invertebrates and fish communities (medium confidence).‘Salinisation and expansion of hypoxic conditions will intensify in eutrophic estuaries, especially in mid and high latitudes with microtidal regimes (high confidence).’ ‘The effects of warming will be more pronounced in high-latitude and temperate shallow estuaries with limited exchange with the open ocean [...] and seasonality that already leads to dead zone development [...] (medium confidence).’ Interaction between SLR and changes in precipitation will have greater impacts on shallow than deep estuaries
medium
1
train
3,664
AR6_WGII
432
17
Estuaries characterised by large tidal exchanges and associated well-developed sediments will be more resilient to projected SLR and changes in river flow
medium
1
train
3,665
AR6_WGII
432
18
Human activities that inhibit sediment dynamics in coastal deltas increase their vulnerability to SLR
medium
1
train
3,666
AR6_WGII
433
1
Global rates of mangrove loss have been extensive but are slowing
high
2
train
3,667
AR6_WGII
433
2
From 2000 to 2010 mangrove loss averaged 0.16% yr–1, globally, but with greatest loss in Southeast Asia
high
2
train
3,668
AR6_WGII
433
3
Salt-marsh ecosystems have also suffered extensive losses (up to 60% in places since the 1980s), especially in developed and rapidly developing countries
medium
1
train
3,669
AR6_WGII
433
4
Similarly, 29% of seagrass meadows were lost from 1879–to 2006 due primarily to coastal development and degradation of water quality, with climate-change impacts escalating since 1990
medium
1
train
3,670
AR6_WGII
433
5
Local examples of habitat stability or growth (e.g., de los Santos et al., 2019; Laengner et al., 2019; Sousa et al., 2019; Suyadi et al., 2019; Derolez et al., 2020; Goldberg et al., 2020; McKenzie and Yoshida, 2020) indicate some resilience to climate change in the absence of non-climate drivers
high
2
train
3,671
AR6_WGII
433
6
Nevertheless, previous declines have left wetland ecosystems more vulnerable to impacts from climate-induced drivers and non-climate drivers
high
2
train
3,672
AR6_WGII
433
8
Warming is allowing some, but not all (Rogers and Krauss, 2018; Saintilan et al., 2018), mangrove Table 3.7 | Summary of previous IPCC assessments of mangroves, salt marshes and seagrass beds Observations Projections AR5 (Wong et al., 2014) Seagrasses occurring close to their upper thermal limits are already stressed by climate change
high
2
train
3,673
AR6_WGII
433
11
As a result, interactions between climate change and non-climate drivers will continue to cause declines in estuarine vegetated systems
very high
3
train
3,674
AR6_WGII
433
12
SR15 (Hoegh-Guldberg et al., 2018a) Vegetated blue carbon systems were not assessed in this report.Intact wetland ecosystems can reduce the adverse impacts of rising sea levels and intensifying storms by protecting shorelines
medium
1
train
3,675
AR6_WGII
433
13
Under 1.5°C of warming, natural sedimentation rates are projected to outpace SLR (medium confidence), but ‘other feedbacks, such as landward migration of wetlands and the adaptation of infrastructure, remain important (medium confidence).’ SROCC (Bindoff et al., 2019a; Oppenheimer et al., 2019) Coastal ecosystems, including salt marshes, mangroves, vegetated dunes and sandy beaches, can build vertically and expand laterally in response to SLR, though this capacity varies across sites
high
2
train
3,676
AR6_WGII
433
15
However, as a consequence of human actions that fragment wetland habitats and restrict landward migration, coastal ecosystems progressively lose their ability to adapt to climate-induced changes and provide ecosystem services, including acting as protective barriers
high
2
train
3,677
AR6_WGII
433
16
Examples include mangrove encroachment into subtropical salt marshes (high confidence) and contraction in extent of low-latitude seagrass meadows
high
2
train
3,678
AR6_WGII
433
17
Plants with low tolerance to flooding and extreme temperatures are particularly vulnerable, increasing the risk of extirpation
medium
1
train
3,679
AR6_WGII
433
18
Extreme-weather events, including heatwaves, droughts and storms, are causing mass mortalities and changes in community composition in coastal wetlands
high
2
train
3,680
AR6_WGII
433
19
Severe disturbance of wetlands or transitions among wetland community types can favour invasive species
medium
1
train
3,681
AR6_WGII
433
20
The degradation or loss of vegetated coastal ecosystems reduces carbon storage, with positive feedbacks to the climate system (high confidence).‘Seagrass meadows (high confidence) [...] will face moderate to high risk at temperature above 1.5°C global sea surface warming.’ ‘The transition from undetectable to moderate risk in salt marshes [...] takes place between 0.7°C–1.2°C of global sea surface warming (medium/high confidence), and between 0.9°C–1.8°C (medium confidence) in sandy beaches, estuaries and mangrove forests.’ ‘The ecosystems at moderate to high risk under future emission scenarios are mangrove forests (transition from moderate to high risk at 2.5°C–2.7°C of global sea surface warming), estuaries and sandy beaches (2.3°C–3.0°C) and salt marshes (transition from moderate to high risk at 1.8°C–2.7°C and from high to very high risk at 3.0°C–3.4°C) (medium confidence).’ ‘Global coastal wetlands will lose between 20–90% of their area depending on emissions scenario with impacts on their contributions to carbon sequestration and coastal protection
high
2
train
3,682
AR6_WGII
433
21
But SLR and warming are projected to drive global loss of up to 90% of vegetated wetlands by the end of the century under the RCP8.5 (medium confidence), especially if landward migration and sediment supply are limited by human modification of shorelines and river flows
medium
1
train
3,683
AR6_WGII
434
1
This expansion can affect species interactions (Guo et al., 2017; Friess et al., 2019), and enhance sediment accretion and carbon storage rates in some instances
medium
1
train
3,684
AR6_WGII
434
2
Drought, low sea levels and MHWs can cause significant die-offs among mangroves
medium
1
train
3,685
AR6_WGII
434
3
Seagrasses are similarly vulnerable to warming (high confidence) (Repolho et al., 2017; Duarte et al., 2018; Jayathilake and Costello, 2018; Savva et al., 2018), which has been attributed as one cause of observed changes in distribution and community structure
medium
1
train
3,686
AR6_WGII
434
4
MHWs, together with storm-driven turbidity and structural damage, can cause seagrass die-offs (high confidence) (Arias-Ortiz et al., 2018; Kendrick et al., 2019; Smale et al., 2019; Strydom et al., 2020), shifts to small, fast-growing species
high
2
train
3,687
AR6_WGII
434
5
The sensitivity of salt marshes and mangroves to RSLR depends on whether they accrete inorganic sediment and/or organic material at rates equivalent to rising water levels
very high
3
train
3,688
AR6_WGII
434
6
Otherwise, wetland ecosystems must migrate either inland or upstream, or face gradual submergence in deeper, increasingly saline water
very high
3
train
3,689
AR6_WGII
434
8
Submergence drives changes in community structure (high confidence) (Jones et al., 2019b; Yu et al., 2019; Douglass et al., 2020; Langston et al., 2020) and functioning (high confidence) (Charles et al., 2019; Buffington et al., 2020; Stein et al., 2020), and will eventually lead to extirpation of the most sensitive vegetation (medium confidence) (Schepers et al., 2017; Scalpone et al., 2020) and associated animals
low
0
train
3,690
AR6_WGII
434
11
On the basis of paleorecords (Table 3.8), we assess that mangroves and salt marshes are likely at high risk from future SLR, even under SSP1-1.9, with impacts manifesting in the mid- term
medium
1
train
3,691
AR6_WGII
434
12
Under SSP5-8.5, wetlands are very likely at high risk from SLR, with larger impacts manifesting before 2040
medium
1
train
3,692
AR6_WGII
434
13
By 2100, these ecosystems are at high risk of impacts under all scenarios except SSP1-1.9 (high confidence), with impacts most severe along coastlines with gently sloping shorelines, limited sediment inputs, small tidal ranges and limited space for inland migration
very high
3
train
3,693
AR6_WGII
434
16
Other species, such as Posidonia oceanica in the Mediterranean, might lose as much as 75% of their habitat by 2050 under RCP8.5 and become functionally extinct
low
0
test
3,694
AR6_WGII
434
17
Observed impacts of MHWs (Kendrick et al., 2019; Strydom et al., 2020; Serrano et al., 2021) indicate that increasing intensity and frequency of MHWs (Section 3.2.2.1) will have escalating impacts on seagrass ecosystems
high
2
train
3,695
AR6_WGII
434
18
Habitat suitability can also be reduced by moderate RSLR, due to its impact on light attenuation
medium
1
train
3,696
AR6_WGII
434
19
Overall, warming will drive range shifts in wetland species (medium to high confidence), but SLR poses the greatest risk for mangroves and salt marshes, with significant losses projected under all future scenarios by mid-century
medium
1
train
3,697
AR6_WGII
435
1
Observations Projections AR5 (Wong et al., 2014) ‘Globally, beaches and dunes have in general undergone net erosion over the past century or longer.’ ‘Attributing shoreline changes to climate change is still difficult owing to the multiple natural and anthropogenic drivers contributing to coastal erosion.’‘In the absence of adaptation, beaches, sand dunes and cliffs currently eroding will continue to do so under increasing sea level
high
2
train
3,698
AR6_WGII
435
2
In many locations, finding sufficient sand to rebuild beaches and dunes artificially will become increasingly difficult and expensive as present supplies near project sites are depleted (high confidence).’ ‘In the absence of adaptation measures, beaches and sand dunes currently affected by erosion will continue to be affected under increasing sea levels (high confidence).’ SROCC (Bindoff et al., 2019a) Coastal ecosystems are already impacted by the combination of SLR, other climate-related ocean changes and adverse effects from human activities on ocean and land
high
2
train
3,699
AR6_WGII
435
3
Attributing such impacts to SLR, however, remains challenging due to the influence of other climate-related and non-climate drivers such as infrastructure development and human-induced habitat degradation
high
2
train