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Similarities and differences between cold-water and warm-water coral reefs 

Similarities and differences between cold-water and warm-water coral reefs 

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Over the last few decades the exploration of deep-water environments using new technologies has revealed insights into parts of our planet that challenge conventional wisdom. Coral reefs, once thought to be restricted to warm shallow waters in tropical and subtropical regions, have been found found in dark, cold, nutrient-rich waters off the coasts...

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... For example, these species are often referred to as non-constructional (previously ahermatypic), not habitat forming, found only in deep or cold-water habitats, and solitary living 17 . However, while many species within these groups align with these descriptions, some have the capacity to form constructional (previously hermatypic) colonial reef systems 14,[17][18][19] and maintain similar calcification rates to photoendosymbiotic species 20 . The absence of photoendosymbiotic dinoflagellates within these coral species removes light constraints on growth, enabling these species to exploit broad geographical and bathymetric ranges. ...
... As such, coral species living without reliance on photoendosymbioses are found across polar, temperate, sub-tropical and tropical regions, exhibiting immense depth variation, from the intertidal zone to abyssal depths greater than 6000 m 17,21 . In deep and/or cold-water habitats, coral reefs can play host to highly diverse biological assemblages similar to those of tropical coral reefs 9,18 but these ecosystems are largely understudied due to the complexities and cost associated with deep-water research, a perceived lack of environmental significance and little information on potential environmental threats 19 . However, these ecosystems cover vast areas, are environmentally important including facilitating speciation within the deep sea 18 and have significant socio-economic roles, such as hosting breeding grounds for fished species 22 . ...
... Approximately 20 of the deep sea Scleractinia form structural reef systems 22 , including species such as; Desmophyllum pertusum, Madrepora oculata, Oculina varicosa, Solenosmilia variabilis, Enallopsammia profunda, Goniocorella dumosa and Bathelia candida, whilst the majority of species records in the deep sea are for solitary species. Desmophyllum pertusum (Linneaus 1758) is the most commonly occurring reef-building coral at depth 19 , significantly contributing to reef structures that have been found to span several kilometres 76 . Desmophyllum pertusum has a broad geographical range, extending throughout the North Atlantic Ocean 77 and the Pacific Ocean 78,79 and can be found anywhere from 50 to 3000 m depth 77 . ...
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... and OBIS (2022). From the NOAA database we selected all records of the main CWC reef-building species Desmophyllum pertusum (previously Lophelia pertusa), Enallopsammia profunda, E. pusilla, E. rostrata, Goniocorella dumosa, Madrepora carolina, M. oculata, and Solenosmilia variabilis (Freiwald et al., 2004;Maier et al., 2023), below 100 m depth, recorded from 1900 or later, with a horizontal location accuracy of 1000 m or less, and between the critical latitudes for the M2 tide of 70°N and S (15 629 records). ...
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... Their colony morphology varies from branched, bush-like, and feather-like to whip types (Wagner et al. 2012). The dense canopies they form can change local physical conditions and generate a three-dimensional habitat, which provide shelter to associated species and, ultimately, increase biodiversity (Freiwald et al. 2004;Buhl-Mortensen et al. 2010;De Clippele et al. 2019). One of the main components of the visible black coral forests-associated biodiversity is accounted by epifauna (i.e., crustaceans, polychaetes and molluscs, Lavelle 2012; Wagner et al. 2012), which can find habitat (Herler 2007), food (Angel 1990;Bo et al. 2012), and protection against predators (Lavelle 2012). ...
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... 18 The next depth zone found at between 70-140 m include similar assemblages to the upper-mid assemblages of anemones, so corals, hydroids, tube worms and barnacles, as well as the hard bodies deep water cold coral, L. pertusa. At greater depths assemblages can become sparser, but this isn't necessarily the case, L. pertusa for example has been found at depths greater than 1000 m. 46 Birds including gules, garnets and kittiwakes 47 colonise the topsides (structures above sea level) as structures such as drilling derricks provide many places to build nests and raise chicks and deposit guano. Fig. 5 illustrates the evolution of the species assemblages over time from emplacement to the point at which the OGI MMS are ready for decommissioning. ...
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... Scleractinian corals D. pertusum, M. oculata, E. rostrata, G. dumosa, O. varicosa, and S. variabilis are all reef-framework forming species with cosmopolitan distributions (Davies and Guinotte, 2011). Desmophyllum pertusum often occurs as the dominant framework-forming Scleractinian or as isolated thickets mainly in the North Atlantic (Freiwald et al., 2004;Tong et al., 2016), while M. oculata has mainly been found as a secondary framework-forming species within D. pertusum or G. dumosa reefs (Freiwald et al., 2004;Roberts et al., 2006). Goniocorella dumosa has been observed as the dominant reef-builder in New Zealand waters (Tracey et al., 2011). ...
... Scleractinian corals D. pertusum, M. oculata, E. rostrata, G. dumosa, O. varicosa, and S. variabilis are all reef-framework forming species with cosmopolitan distributions (Davies and Guinotte, 2011). Desmophyllum pertusum often occurs as the dominant framework-forming Scleractinian or as isolated thickets mainly in the North Atlantic (Freiwald et al., 2004;Tong et al., 2016), while M. oculata has mainly been found as a secondary framework-forming species within D. pertusum or G. dumosa reefs (Freiwald et al., 2004;Roberts et al., 2006). Goniocorella dumosa has been observed as the dominant reef-builder in New Zealand waters (Tracey et al., 2011). ...
... Goniocorella dumosa has been observed as the dominant reef-builder in New Zealand waters (Tracey et al., 2011). Enallopsammia rostrata is also observed associated with D. pertusum, M. oculata, and S. variabilis (Freiwald et al., 2004). Oculina varicosa can inhabit both shallow and deep waters (Reed, 2002). ...
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... Model outputs have indicated that continental slopes are one of the main suitable coral sites worldwide 8 . The bathyal (~200-3000 m depth) region 12 has large protruding topographical features, interfering with bottom current flow and creating colonizable hard substrates at multiple depths; this enhances seabed erosion and resuspends particulates, which provides an elevated supply of suspended food particles for corals 13 . Along the Brazilian margin, five main water masses with distinct intensity and transport directions influence the continental slope 14 , which may contribute to regional species diversity pools. ...
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Data were obtained from the literature to identify past changes in and the present status of the coastal carbon cycle. They indicate that marine coastal ecosystems driving the coastal carbon cycle cover, on average, 5.8% of the Earth’s surface and contributed 55.2% to carbon transport from the climate-active carbon cycle to the geological carbon cycle. The data suggest that humans not only increase the CO 2 concentration in the atmosphere but also mitigate (and before 1860 even balanced) their CO 2 emissions by increasing CO 2 storage within marine coastal ecosystems. Soil degradation in response to the expansion and intensification of agriculture is assumed to be a key process driving the enhanced CO 2 storage in marine coastal ecosystems because it increases the supply of lithogenic matter that is known to favour the burial of organic matter in sediments. After 1860, rising CO 2 concentrations in the atmosphere indicate that enhanced CO 2 emissions caused by land-use changes and the burning of fossil fuel disturbed what was a quasi-steady state before. Ecosystem restoration and the potential expansion of forest cover could mitigate the increase of atmospheric CO 2 concentrations, but this carbon sink to the atmosphere is much too weak to represent an alternative to the reduction of CO 2 emission in order to keep global warming below 1.5–2.°C. Although the contribution of benthic marine coastal ecosystems to the global CO 2 uptake potential of ecosystem restoration is only around 6%, this could be significant given national carbon budgets. However, the impact on climate is still difficult to quantify because the associated effects on CH 4 and N 2 O emissions have not been established. Addressing these uncertainties is one of the challenges faced by future research, as are related issues concerning estimates of carbon fluxes between the climate-active and the geological carbon cycle and the development of suitable methods to quantify changes in the CO 2 uptake of pelagic ecosystems in the ocean.
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Seabed-contact activities operating in the deep sea can generate sediment plumes that pose varying levels of threat to benthic fauna. Corals are important components of deep-sea ecosystems and can be particularly sensitive to elevated suspended sediment concentrations. In this study, we exposed colony fragments of the New Zealand deep-sea scleractinian Goniocorella dumosa to four-day pulses of four target sediment concentrations: 0 mg l−1 (representing control conditions) and 45, 102 and 435 mg l−1 (targeting concentrations expected from mining and trawling disturbance). All coral fragments survived. Oxygen consumption rates were not affected by treatments and time. No visible detrimental effects on coral health were noted after the first pulse of sediment exposure. However, both a loss of coenosarc and instances of polyp mortality were observed on fragments exposed to suspended sediments during the following sediment pulses. This observed decline in coral health over time indicates that G. dumosa could cope with sediment disturbance from human activities that disturb the seafloor for periods of up to four days, but that repeated, or prolonged sediment exposure could cause a deterioration in the health condition of this species. This hypothesis should be further investigated in following studies.
... Cold-water coral (CWC) reefs are biodiversity-rich ecosystems found in a vast range of water depths and habitats, down to over 1000 m of depth on seamounts and continental slopes (Freiwald et al. 2004), and up to 39 m in Norwegian fjords (Fosså et al. 2002). These ecosystems rely on the three-dimensional (3D) skeletal frameworks formed by a few species of azooxanthellate scleractinians such as the widely distributed Desmophyllum pertusum (previously known as Lophelia pertusa), the primary framework builder in the North Atlantic Ocean (Freiwald et al. 2004). ...
... Cold-water coral (CWC) reefs are biodiversity-rich ecosystems found in a vast range of water depths and habitats, down to over 1000 m of depth on seamounts and continental slopes (Freiwald et al. 2004), and up to 39 m in Norwegian fjords (Fosså et al. 2002). These ecosystems rely on the three-dimensional (3D) skeletal frameworks formed by a few species of azooxanthellate scleractinians such as the widely distributed Desmophyllum pertusum (previously known as Lophelia pertusa), the primary framework builder in the North Atlantic Ocean (Freiwald et al. 2004). The majority of the CWC reef framework consists of dead coral skeleton (devoid of living tissue) (Vad et al. 2017), which supports key ecological functions modulated by its physical branching structure, including habitat provision for most of the numerous reef-associated species (Mortensen et al. 1995) and baffling and retention of suspended sediment and particulate organic matter (Wheeler et al. 2005;Maier et al. 2021;Wang et al. 2021). ...
... The marked architectural diversity of D. pertusum at local scales has important implications for CWC reef ecosystems, suggesting partitioning of the coral's ecological functions not solely among different reef zones (living coral, dead framework and coral rubble; Freiwald et al. 2004), but also between different portions of the dead framework. In terms of habitat provision, this architectural variability may induce locally heterogeneous distribution patterns of reef-dwelling organisms that thrive in different framework configurations, contributing to complex local structuring of CWC reef communities (Henry et al. 2013). ...
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The three-dimensional (3D) structure of habitat-forming corals has profound impacts on reef ecosystem processes. Elucidating coral structural responses to the environment is therefore crucial to understand changes in these ecosystems. However, little is known of how environmental factors shape coral structure in deep and dark waters, where cold-water coral (CWC) reefs thrive. Here, we attempt to infer the influence of current flow on CWC framework architecture, using 3D scanning to quantify colony shape traits (volume compactness and surface complexity) in the reef-building CWC Desmophyllum pertusum from adjacent fjord and offshore habitats with contrasting flow regimes. We find substantial architectural variability both between and within habitats. We show that corals are generally more compact in the fjord habitat, reflecting the prevailing higher current speeds, although differences in volume compactness between fjord and offshore corals are more subtle when comparing the fjord with the more exposed side of the offshore setting, probably due to locally intensified currents. Conversely, we observe no clear disparity in coral surface complexity between habitats (despite its positive correlation with volume compactness), suggesting it is not affected by current speed. Unlike volume compactness, surface complexity is similarly variable within a single colony as it is between colonies within the same habitat or between habitats and is therefore perhaps more dependent than volume compactness on microenvironmental conditions. These findings suggest a highly plastic, trait-specific and functionally relevant structural response of CWCs to current flow and underscore the importance of multiple concurrent sources of hydrodynamic forcing on CWC growth.
... Humans often exploit these ecosystem services without a good understanding of the impacts on the processes that sustain them (Levin et al., 2020;Mejjad and Rovere, 2021). For example, fisheries bottom trawls remove coral colonies, which can be hundreds to thousands of years old (Watling and Norse, 1998;Roberts et al., 2005) and provide nursery and breeding grounds for the same species that are targeted by the fisheries (Freiwald et al., 2004;Clark et al., 2016). In another example, the Deepwater Horizon (DWH) oil spill caused significant damage to coral colonies that were hundreds of years old (Prouty et al., 2016), and complete recovery of the ecosystem and its services may require time scales on the same order-of-magnitude (Girard & Fisher, 2018). ...
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