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Glob Chang Biol
2020 Nov 01;2611:6424-6444. doi: 10.1111/gcb.15307.
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Rapid deep ocean deoxygenation and acidification threaten life on Northeast Pacific seamounts.
Ross T
,
Du Preez C
,
Ianson D
.
Abstract
Anthropogenic climate change is causing our oceans to lose oxygen and become more acidic at an unprecedented rate, threatening marine ecosystems and their associated animals. In deep-sea environments, where conditions have typically changed over geological timescales, the associated animals, adapted to these stable conditions, are expected to be highly vulnerable to any change or direct human impact. Our study coalesces one of the longest deep-sea observational oceanographic time series, reaching back to the 1960s, with a modern visual survey that characterizes almost two vertical kilometers of benthic seamount ecosystems. Based on our new and rigorous analysis of the Line P oceanographic monitoring data, the upper 3,000 m of the Northeast Pacific (NEP) has lost 15% of its oxygen in the last 60 years. Over that time, the oxygen minimum zone (OMZ), ranging between approximately 480 and 1,700 m, has expanded at a rate of 3.0 ± 0.7 m/year (due to deepening at the bottom). Additionally, carbonate saturation horizons above the OMZ have been shoaling at a rate of 1-2 m/year since the 1980s. Based on our visual surveys of four NEP seamounts, these deep-sea features support ecologically important taxa typified by long life spans, slow growth rates, and limited mobility, including habitat-forming cold water corals and sponges, echinoderms, and fish. By examining the changing conditions within the narrow realized bathymetric niches for a subset of vulnerable populations, we resolve chemical trends that are rapid in comparison to the life span of the taxa and detrimental to their survival. If these trends continue as they have over the last three to six decades, they threaten to diminish regional seamount ecosystem diversity and cause local extinctions. This study highlights the importance of mitigating direct human impacts as species continue to suffer environmental changes beyond our immediate control.
FIGURE 1. Map of our Northeast Pacific seamounts study region. Line P oceanographic monitoring stations are indicated by red squares; major stations (P12, P16, and P26) are highlighted in yellow (main map) and black (inset). The triangle symbols indicate seamount summits in our study region (DFO, 2019), the four in black were surveyed during the 2017 benthic imaging survey cruise (Table 1). The proposed Offshore Pacific marine protected area is outlined in blue. Bathymetry is from GEBCO 2014 Grid, version 20141103, http://www.gebco.net
FIGURE 2. False color plots of dissolved oxygen (a) and aragonite saturation state (ΩAr, b) over the Line P time series, averaged over our NEP seamounts study region (Figure 1). Overlaid on (a) are the calcite saturation depth (yellow), and the upper (red) and lower (blue) boundaries of the oxygen minimum zone. The legend indicates the trends associated with each of these boundaries. In (b), the ΩAr = 0.7 (red) horizon is shown. Also overlaid are the isopycnal depths for the 26.83 (thick gray dotted line), 27.04 (thick gray dash‐dotted line), 27.4 (thick gray dashed line), and 27.62 kg/m3 (thick gray line) sigma levels. Depths of the bottle samples that were interpolated to create the contour plot of ΩAr are shown (black dots)
FIGURE 3. Time series of dissolved oxygen at fixed depth (475 m, a; 1,000 m, b; 1,700 m, c; thick black lines), at fixed potential density (1,027.04 kg/m3, a; 1,027.4 kg/m3, b; 1,027.62 kg/m3, c; blue lines/dots), and the estimated oxygen change due to movement of these constant potential density surfaces (mean oxygen has been added to put it on the same axis; red lines/squares). The gray patch behind the black lines represents the intra‐annual natural variability in the data at that depth (it is the inter‐month standard deviation from station P12 in 2013 [N = 4])
FIGURE 4. Images of the indicator taxa: (a) rougheye rockfish (Sebastes aleutianus) were observed as solitary individuals and in schools; (a–c) brittle stars (Ophiacantha diplasia and Ophiopholis spp.) could form dense living mats covering the seafloor often collocated with (also b, indicated with arrow) the bubblegum coral (Paragorgia cf. jamesi), which was small but dense while (c) the bamboo coral (Isidella tentaculum) was slightly less dense but could grow over 2 m high; (d, indicated with arrows) the black coral (Chrysopathes speciosa) formed extensive gardens; (e) the tall vase‐shape bugle sponge (Pinulasma n. sp.); (f, indicated with arrows) the cup coral (Flabellidae) is solitary coral; (g, indicated with arrows) the undulated glass sponges (cf Tretodictyum n. sp.) increased seafloor structural complexity with its body morphology; and (h) the sea lily was observed as solitary individuals and as dense fields (Florometra serratissima). The white scale bars in the corner of each panel are 10 cm long
FIGURE 5. Plot of the observed depth distributions of the nine indicator taxa identified based on the benthic visual surveys along with simultaneously collected depth profiles of Union, Dellwood, Unnamed (UN) 16 and 18 seamounts (Figure 1). The red background shows the mean oxygen concentration over the full time series, highlighting the OMZ (i.e., white is outside the OMZ). The dashed white lines delineate the region between 800 and 1,200 m which corresponds to oxygen <0.5 ml/L and dotted blue line indicates the mean depth of the calcite saturation horizon. A range of metrics on the species’ depth ranges are plotted (mean, horizontal black lines; ±1 standard deviation, dark gray boxes; maximum and minimum depth observed, thin dark gray lines). *The sea lily has a bimodal depth distribution (gap between 1,150 and 700 m); the black coral also has a bimodal distribution (dip between 900 and 850 m); the rest have roughly bell‐shaped unimodal distributions (except for the rockfish, which is truncated at the top) (S5). All taxa were found on all seamounts with habitat (seafloor) in their depth range (mean ± 1 standard deviation) with the exception of the bugle sponge which was not observed on UN 16 (S5)
Addamo,
Merging scleractinian genera: the overwhelming genetic similarity between solitary Desmophyllum and colonial Lophelia.
2016, Pubmed
Addamo,
Merging scleractinian genera: the overwhelming genetic similarity between solitary Desmophyllum and colonial Lophelia.
2016,
Pubmed
Baco,
Defying Dissolution: Discovery of Deep-Sea Scleractinian Coral Reefs in the North Pacific.
2017,
Pubmed
Breitburg,
Declining oxygen in the global ocean and coastal waters.
2018,
Pubmed
Caldeira,
Oceanography: anthropogenic carbon and ocean pH.
2003,
Pubmed
Claiborne,
Acid-base regulation in fishes: cellular and molecular mechanisms.
2002,
Pubmed
Clark,
The ecology of seamounts: structure, function, and human impacts.
2010,
Pubmed
Cripps,
Have we been underestimating the effects of ocean acidification in zooplankton?
2014,
Pubmed
Danovaro,
The deep-sea under global change.
2017,
Pubmed
Davis,
The role of Mg2+ as an impurity in calcite growth.
2000,
Pubmed
Du Preez,
The Structure and Distribution of Benthic Communities on a Shallow Seamount (Cobb Seamount, Northeast Pacific Ocean).
2016,
Pubmed
Dupont,
Impact of near-future ocean acidification on echinoderms.
2010,
Pubmed
,
Echinobase
Eberlein,
Effects of ocean acidification on primary production in a coastal North Sea phytoplankton community.
2017,
Pubmed
Feely,
Impact of anthropogenic CO2 on the CaCO3 system in the oceans.
2004,
Pubmed
Gabay,
Octocoral tissue provides protection from declining oceanic pH.
2014,
Pubmed
Gallagher,
Evolutionary theory as a tool for predicting extinction risk.
2015,
Pubmed
Grantham,
Upwelling-driven nearshore hypoxia signals ecosystem and oceanographic changes in the northeast Pacific.
2004,
Pubmed
Gruber,
Warming up, turning sour, losing breath: ocean biogeochemistry under global change.
2011,
Pubmed
Gruber,
The oceanic sink for anthropogenic CO2 from 1994 to 2007.
2019,
Pubmed
Guinotte,
Ocean acidification and its potential effects on marine ecosystems.
2008,
Pubmed
Gómez,
Growth and feeding of deep-sea coral Lophelia pertusa from the California margin under simulated ocean acidification conditions.
2018,
Pubmed
Haigh,
Effects of ocean acidification on temperate coastal marine ecosystems and fisheries in the northeast Pacific.
2015,
Pubmed
Hamilton,
Species-Specific Responses of Juvenile Rockfish to Elevated pCO2: From Behavior to Genomics.
2017,
Pubmed
Hamilton,
CO2-induced ocean acidification increases anxiety in rockfish via alteration of GABAA receptor functioning.
2014,
Pubmed
Hoegh-Guldberg,
The impact of climate change on the world's marine ecosystems.
2010,
Pubmed
Hurst,
Elevated CO2 alters behavior, growth, and lipid composition of Pacific cod larvae.
2019,
Pubmed
Iglikowska,
Variability in magnesium content in Arctic echinoderm skeletons.
2017,
Pubmed
Kleypas,
Geochemical consequences of increased atmospheric carbon dioxide on coral reefs.
1999,
Pubmed
Kroeker,
Impacts of ocean acidification on marine organisms: quantifying sensitivities and interaction with warming.
2013,
Pubmed
Le Goff,
In vivo pH measurement at the site of calcification in an octocoral.
2017,
Pubmed
Leys,
Oxygen and the Energetic Requirements of the First Multicellular Animals.
2018,
Pubmed
Leys,
The biology of glass sponges.
2007,
Pubmed
Leys,
The sponge pump: the role of current induced flow in the design of the sponge body plan.
2011,
Pubmed
Masuda,
Simulated rapid warming of abyssal North Pacific waters.
2010,
Pubmed
Matabos,
A year in hypoxia: epibenthic community responses to severe oxygen deficit at a subsea observatory in a coastal inlet.
2012,
Pubmed
Morato,
Climate-induced changes in the suitable habitat of cold-water corals and commercially important deep-sea fishes in the North Atlantic.
2020,
Pubmed
Parker,
Dispersal Strategies of the Biota on an Oceanic Seamount: Implications for Ecology and Biogeography.
1994,
Pubmed
Pinsky,
Marine taxa track local climate velocities.
2013,
Pubmed
Riebesell,
Enhanced biological carbon consumption in a high CO2 ocean.
2007,
Pubmed
Rossoll,
Ocean acidification-induced food quality deterioration constrains trophic transfer.
2012,
Pubmed
Sabine,
The oceanic sink for anthropogenic CO2.
2004,
Pubmed
Schmidtko,
Decline in global oceanic oxygen content during the past five decades.
2017,
Pubmed
Steckbauer,
Additive impacts of deoxygenation and acidification threaten marine biota.
2020,
Pubmed
Talley,
Changes in Ocean Heat, Carbon Content, and Ventilation: A Review of the First Decade of GO-SHIP Global Repeat Hydrography.
2016,
Pubmed
Victorero,
Species replacement dominates megabenthos beta diversity in a remote seamount setting.
2018,
Pubmed
Wood,
Ocean acidification may increase calcification rates, but at a cost.
2008,
Pubmed
,
Echinobase
Yesson,
Improved bathymetry leads to >4000 new seamount predictions in the global ocean - but beware of phantom seamounts!
2021,
Pubmed
Zeng,
Species-specific genetic variation in response to deep-sea environmental variation amongst Vulnerable Marine Ecosystem indicator taxa.
2020,
Pubmed