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Another strategy used by some classes of bacteria in the oxygen minimum zones is to use nitrate rather than oxygen, thus drawing down the concentrations of this important nutrient. This process is called [[denitrification]]. The oxygen minimum zones thus play an important role in regulating the productivity and ecological community structure of the global ocean.<ref>{{cite journal |doi=10.1038/nature05392 |title=Spatial coupling of nitrogen inputs and losses in the ocean |year=2006 |last1=Deutsch |first1=Curtis |last2=Sarmiento |first2=Jorge L. |last3=Sigman |first3=Daniel M. |last4=Gruber |first4=Nicolas |last5=Dunne |first5=John P. |journal=Nature |volume=445 |issue=7124 |pages=163–7 |pmid=17215838 |bibcode=2007Natur.445..163D|s2cid=10804715 }}</ref> For example, giant bacterial mats floating in the oxygen minimum zone off the west coast of [[South America]] may play a key role in the region's extremely rich fisheries, as bacterial mats the size of [[Uruguay]] have been found there.<ref>{{cite news |first=Stephen |last=Leahy |date=20 April 2010 |agency=Tierramérica |title=Giant Bacteria Colonise the Oceans |url=http://www.ipsnews.net/news.asp?idnews=51117 |publisher=[[Inter Press Service]] |url-status=dead |archive-url=https://web.archive.org/web/20100624092254/http://ipsnews.net/news.asp?idnews=51117 |archive-date=24 June 2010 }}</ref>
Another strategy used by some classes of bacteria in the oxygen minimum zones is to use nitrate rather than oxygen, thus drawing down the concentrations of this important nutrient. This process is called [[denitrification]]. The oxygen minimum zones thus play an important role in regulating the productivity and ecological community structure of the global ocean.<ref>{{cite journal |doi=10.1038/nature05392 |title=Spatial coupling of nitrogen inputs and losses in the ocean |year=2006 |last1=Deutsch |first1=Curtis |last2=Sarmiento |first2=Jorge L. |last3=Sigman |first3=Daniel M. |last4=Gruber |first4=Nicolas |last5=Dunne |first5=John P. |journal=Nature |volume=445 |issue=7124 |pages=163–7 |pmid=17215838 |bibcode=2007Natur.445..163D|s2cid=10804715 }}</ref> For example, giant bacterial mats floating in the oxygen minimum zone off the west coast of [[South America]] may play a key role in the region's extremely rich fisheries, as bacterial mats the size of [[Uruguay]] have been found there.<ref>{{cite news |first=Stephen |last=Leahy |date=20 April 2010 |agency=Tierramérica |title=Giant Bacteria Colonise the Oceans |url=http://www.ipsnews.net/news.asp?idnews=51117 |publisher=[[Inter Press Service]] |url-status=dead |archive-url=https://web.archive.org/web/20100624092254/http://ipsnews.net/news.asp?idnews=51117 |archive-date=24 June 2010 }}</ref>

=== Zooplankton ===
Decreased oxygen availability results in decreases in many zooplankton species’ egg production, food intake, respiration,<ref name="Elliott2013">{{cite journal |last1=Elliott |first1=DT |last2=Pierson |first2=JJ |last3=Roman |first3=MR |date=2013 |title=Elliott, D.T., Pierson, J.J. and Roman, M.R., 2013. Predicting the effects of coastal hypoxia on vital rates of the planktonic copepod Acartia tonsa Dana |journal=PLOS ONE |volume=8 |issue=5 |page=e63987 |doi=10.1371/journal.pone.0063987 |pmc=3656935 |pmid=23691134 |doi-access=free}}</ref> and metabolic rates.<ref name="ES2015">{{cite journal |last1=Elder |first1=LE |last2=Seibel |first2=BA |date=2015 |title=Ecophysiological implications of vertical migration into oxygen minimum zones for the hyperiid amphipod Phronima sedentaria |journal=Journal of Plankton Research |volume=37 |issue=5 |pages=897–911 |doi=10.1093/plankt/fbv066 |doi-access=free}}</ref><ref name="Seibel2011">{{cite journal |last1=Seibel |first1=BA |date=2011 |title=Critical oxygen levels and metabolic suppression in oceanic oxygen minimum zones |journal=Journal of Experimental Biology |volume=214 |issue=2 |pages=326–336 |doi=10.1242/jeb.049171 |pmid=21177952 |s2cid=16469678 |doi-access=free}}</ref><ref name="Kiko2016">{{cite journal |last1=Kiko |first1=R |last2=Hauss |first2=H |last3=Bucholz |first3=F |last4=Melzner |first4=F |date=2016 |title=Ammonium excretion and oxygen respiration of tropical copepods and euphausiids exposed to oxygen minimum zone conditions |journal=Biogeosciences |volume=13 |issue=8 |pages=2241–2255 |bibcode=2016BGeo...13.2241K |doi=10.5194/bg-13-2241-2016 |doi-access=free}}</ref> Temperature and salinity in areas of decreased oxygen concentrations also affect oxygen availability. Higher temperatures and salinity lower oxygen solubility decrease the partial pressure of oxygen. This decreased partial pressure increases organisms’ respiration rates, causing the oxygen demand of the organism to increase.<ref name="Elliott2013" /><ref name="Kiko2016" />

In addition to affecting their vital functions, zooplankton alter their distribution in response to hypoxic or anoxic zones. Many species actively avoid low oxygen zones,<ref name="Elliott2012">{{cite journal |last1=Elliott |first1=DT |last2=Pierson |first2=JJ |last3=Roman |first3=MR |date=2012 |title=Relationship between environmental conditions and zooplankton community structure during summer hypoxia in the northern Gulf of Mexico. |journal=Journal of Plankton Research |volume=34 |issue=7 |pages=602–613 |doi=10.1093/plankt/fbs029 |doi-access=free}}</ref><ref name="Vanderploeg2009a">{{cite journal |last1=Vanderploeg |first1=HA |last2=Ludsin |first2=SA |last3=Cavaletto |first3=JF |last4=Höök |first4=TO |last5=Pothoven |first5=SA |last6=Brandt |first6=SB |last7=Liebig |first7=JR |last8=Lang |first8=GA |date=2009 |title=Hypoxic zones as habitat for zooplankton in Lake Erie: refuges from predation or exclusion zones? |journal=Journal of Experimental Marine Biology and Ecology |volume=381 |pages=S108–S120 |doi=10.1016/j.jembe.2009.07.015}}</ref><ref name="Vanderploeg2009b">{{cite journal |last1=Vanderploeg |first1=HA |last2=Ludsin |first2=SA |last3=Ruberg |first3=SA |last4=Höök |first4=TO |last5=Pothoven |first5=SA |last6=Brandt |first6=SB |last7=Lang |first7=GA |last8=Liebig |first8=JR |last9=Cavaletto |first9=JF |date=2009 |title=Hypoxia affects spatial distributions and overlap of pelagic fish, zooplankton, and phytoplankton in Lake Erie |journal=Journal of Experimental Marine Biology and Ecology |volume=381 |pages=S92–S107 |doi=10.1016/j.jembe.2009.07.027}}</ref> while others take advantage of their predators’ low tolerance for hypoxia and use these areas as a refuge.<ref name="Elliott2012" /><ref name="Vanderploeg2009a" /><ref name="Vanderploeg2009b" /> Zooplankton that exhibit daily vertical migrations to avoid predation and low oxygen conditions also excrete ammonium near the oxycline and contribute to increased anaerobic ammonium oxidation (anammox;,<ref name="Bianchi2014">{{cite journal |last1=Bianchi |first1=D |last2=Babbin |first2=AR |last3=Galbraith |first3=ED |date=2014 |title=Enhancement of anammox by the excretion of diel vertical migrators |journal=Proceedings of the National Academy of Sciences |volume=111 |issue=44 |pages=15653–15658 |bibcode=2014PNAS..11115653B |doi=10.1073/pnas.1410790111 |pmc=4226083 |pmid=25288743 |doi-access=free}}</ref><ref name="Kiko2016" /> which produces N<sub>2</sub> gas. As hypoxic regions expand vertically and horizontally,<ref name="Stramma2012">{{cite journal |last1=Stramma |first1=L |last2=Prince |first2=ED |last3=Schmidtko |first3=S |last4=Luo |first4=J |last5=Hoolihan |first5=JP |last6=Visbeck |first6=M |last7=Wallace |first7=DWR |last8=Brandt |first8=P |last9=Körtzinger |first9=A |date=2012 |title=Expansion of oxygen minimum zones may reduce available habitat for tropical pelagic fishes |url=http://oceanrep.geomar.de/13127/2/Stramma.pdf |journal=Nature Climate Change |volume=2 |issue=1 |pages=33–37 |bibcode=2012NatCC...2...33S |doi=10.1038/nclimate1304 |hdl-access=free |hdl=10961/1538}}</ref><ref name="PG2006">{{cite journal |last1=Prince |first1=ED |last2=Goodyear |first2=CP |date=2006 |title=Hypoxia-based habitat compression of tropical pelagic fishes |journal=Fisheries Oceanography |volume=15 |issue=6 |pages=451–464 |doi=10.1111/j.1365-2419.2005.00393.x}}</ref> the habitable ranges for phytoplankton, zooplankton, and [[nekton]] increasingly overlap, increasing their susceptibility to predation and human exploitation.<ref name="deMutsert2016">{{cite journal |last1=de Mutsert |first1=K |last2=Steenbeek |first2=J |last3=Lewis |first3=K |last4=Buszowski |first4=J |last5=Cowan Jr. |first5=JH |last6=Christensen |first6=V |date=2016 |title=Exploring effects of hypoxia on fish and fisheries in the northern Gulf of Mexico using a dynamic spatially explicit ecosystem model |journal=Ecological Modelling |volume=331 |pages=142–150 |bibcode=2016AGUOSAH43A..07D |doi=10.1016/j.ecolmodel.2015.10.013 |doi-access=free}}</ref><ref name="ES2015" /><ref name="Kraus2015">{{cite journal |last1=Kraus |first1=RT |last2=Secor |first2=DH |last3=Wingate |first3=RL |date=2015 |title=Testing the thermal-niche oxygen-squeeze hypothesis for estuarine striped bass |journal=Environmental Biology of Fishes |volume=98 |issue=10 |pages=2083–2092 |doi=10.1007/s10641-015-0431-3 |s2cid=16052635}}</ref><ref name="Roman2012">{{cite journal |last1=Roman |first1=MR |last2=Pierson |first2=JJ |last3=Kimmel |first3=DG |last4=Boicourt |first4=WC |last5=Zhang |first5=X |date=2012 |title=Impacts of hypoxia on zooplankton spatial distributions in the northern Gulf of Mexico |journal=Estuaries and Coasts |volume=35 |issue=5 |pages=1261–1269 |doi=10.1007/s12237-012-9531-x |s2cid=84592608}}</ref><ref name="Vanderploeg2009a" />


== Changes ==
== Changes ==

Revision as of 08:14, 5 July 2023

The oxygen minimum zone (OMZ), sometimes referred to as the shadow zone, is the zone in which oxygen saturation in seawater in the ocean is at its lowest. This zone occurs at depths of about 200 to 1,500 m (700–4,900 ft), depending on local circumstances. OMZs are found worldwide, typically along the western coast of continents, in areas where an interplay of physical and biological processes concurrently lower the oxygen concentration (biological processes) and restrict the water from mixing with surrounding waters (physical processes), creating a "pool" of water where oxygen concentrations fall from the normal range of 4–6 mg/L to below 2 mg/L.[1]

Physical and biological processes

Surface ocean waters generally have oxygen concentrations close to equilibrium with the Earth's atmosphere. In general, colder waters hold more oxygen than warmer waters. As water moves out of the mixed layer into the thermocline, it is exposed to a rain of organic matter from above. Aerobic bacteria feed on this organic matter; oxygen is used as part of the bacterial metabolic process, lowering its concentration within the water. Therefore, the concentration of oxygen in deep water is dependent on the amount of oxygen it had when it was at the surface, minus depletion by deep sea organisms.

Annual mean dissolved oxygen (upper panel) and apparent oxygen utilisation (lower panel) from the World Ocean Atlas.[2] The data plotted show a section running north–south at the 180th meridian (approximately the centre of the Pacific Ocean). White regions indicate section bathymetry. In the upper panel a minimum in oxygen content is indicated by light blue shading between 0° (equator) and 60°N at an average depth of ca. 1,000 m (3,300 ft).

The downward flux of organic matter decreases sharply with depth, with 80–90% being consumed in the top 1,000 m (3,300 ft). The deep ocean thus has higher oxygen because rates of oxygen consumption are low compared with the supply of cold, oxygen-rich deep waters from polar regions. In the surface layers, oxygen is supplied by photosynthesis of phytoplankton. Depths in between, however, have higher rates of oxygen consumption and lower rates of advective supply of oxygen-rich waters. In much of the ocean, mixing processes enable the resupply of oxygen to these waters (see upwelling).

A distribution of the open-ocean oxygen minimum zones is controlled by the large-scale ocean circulation as well as local physical as well as biological processes. For example, wind blowing parallel to the coast causes Ekman transport that upwells nutrients from deep water. The increased nutrients support phytoplankton blooms, zooplankton grazing, and an overall productive food web at the surface. The byproducts of these blooms and the subsequent grazing sink in the form of particulate and dissolved nutrients (from phytodetritus, dead organisms, fecal pellets, excretions, shed shells, scales, and other parts). This "rain" of organic matter (see the biological pump) feeds the microbial loop and may lead to bacterial blooms in water below the euphotic zone due to the influx of nutrients.[3] Since oxygen is not being produced as a byproduct of photosynthesis below the euphotic zone, these microbes use up what oxygen is in the water as they break down the falling organic matter thus creating the lower oxygen conditions.[1]

Physical processes then constrain the mixing and isolate this low oxygen water from outside water. Vertical mixing is constrained due to the separation from the mixed layer by depth. Horizontal mixing is constrained by bathymetry and boundaries formed by interactions with sub-tropical gyres and other major current systems.[4][5][6] Low oxygen water may spread (by advection) from under areas of high productivity up to these physical boundaries to create a stagnant pool of water with no direct connection to the ocean surface even though (as in the Eastern Tropical North Pacific) there may be relatively little organic matter falling from the surface.

Microbes

In OMZs oxygen concentration drops to levels <10 nM at the base of the oxycline and can remain anoxic for over 700 m depth.[7] This lack of oxygen can be reinforced or increased due to physical processes changing oxygen supply such as eddy-driven advection,[7] sluggish ventilation,[8] increases in ocean stratification, and increases in ocean temperature which reduces oxygen solubility.[9]

At a microscopic scale the processes causing ocean deoxygenation rely on microbial aerobic respiration.[9] Aerobic respiration is a metabolic process that microorganisms like bacteria or archaea use to obtain energy by degrading organic matter, consuming oxygen, producing CO2 and obtaining energy in the form of ATP.[9] In the ocean surface photosynthetic microorganisms called phytoplankton use solar energy and CO2 to build organic molecules (organic matter) releasing oxygen in the process.[10] A large fraction of the organic matter from photosynthesis becomes dissolved organic matter (DOM) that is consumed by bacteria during aerobic respiration in sunlit waters. Another fraction of organic matter sinks to the deep ocean forming aggregates called marine snow.[11] These sinking aggregates are consumed via degradation of organic matter and respiration at depth.[8]

At depths in the ocean where no light can reach, aerobic respiration is the dominant process. When the oxygen in a parcel of water is consumed, the oxygen cannot be replaced without the water reaching the surface ocean. When oxygen concentrations drop to below <10 nM, microbial processes that are normally inhibited by oxygen can take place like denitrification and anammox. Both processes extract elemental nitrogen from nitrogen compounds and that elemental nitrogen which does not stay in solution escapes as a gas, resulting in a net loss of nitrogen from the ocean.[8]

Life in the OMZ

Despite the low oxygen conditions, organisms have evolved to live in and around OMZs. For those organisms, like the vampire squid, special adaptations are needed to either make do with lesser amounts of oxygen or to extract oxygen from the water more efficiently. For example, the giant red mysid (Gnathophausia ingens) continues to live aerobically (using oxygen) in OMZs. They have highly developed gills with large surface area and thin blood-to-water diffusion distance that enables effective removal of oxygen from the water (up to 90% O2 removal from inhaled water) and an efficient circulatory system with high capacity and high blood concentration of a protein (hemocyanin) that readily binds oxygen.[12][13][14]

Another strategy used by some classes of bacteria in the oxygen minimum zones is to use nitrate rather than oxygen, thus drawing down the concentrations of this important nutrient. This process is called denitrification. The oxygen minimum zones thus play an important role in regulating the productivity and ecological community structure of the global ocean.[15] For example, giant bacterial mats floating in the oxygen minimum zone off the west coast of South America may play a key role in the region's extremely rich fisheries, as bacterial mats the size of Uruguay have been found there.[16]

Zooplankton

Decreased oxygen availability results in decreases in many zooplankton species’ egg production, food intake, respiration,[17] and metabolic rates.[18][19][20] Temperature and salinity in areas of decreased oxygen concentrations also affect oxygen availability. Higher temperatures and salinity lower oxygen solubility decrease the partial pressure of oxygen. This decreased partial pressure increases organisms’ respiration rates, causing the oxygen demand of the organism to increase.[17][20]

In addition to affecting their vital functions, zooplankton alter their distribution in response to hypoxic or anoxic zones. Many species actively avoid low oxygen zones,[21][22][23] while others take advantage of their predators’ low tolerance for hypoxia and use these areas as a refuge.[21][22][23] Zooplankton that exhibit daily vertical migrations to avoid predation and low oxygen conditions also excrete ammonium near the oxycline and contribute to increased anaerobic ammonium oxidation (anammox;,[24][20] which produces N2 gas. As hypoxic regions expand vertically and horizontally,[25][26] the habitable ranges for phytoplankton, zooplankton, and nekton increasingly overlap, increasing their susceptibility to predation and human exploitation.[27][18][28][29][22]

Changes

OMZs have changed over time due to effects from numerous global chemical and biological processes.[30] To assess these changes, scientists utilize climate models and sediment samples to understand changes to dissolved oxygen in OMZs.[31] Many recent studies of OMZs have focused on their fluctuations over time and how they may be currently changing as a result of climate change.[31][32]

In geological time scales

Some research has aimed to understand how OMZs have changed over geological time scales.[32] Throughout the history of Earth's oceans, OMZs have fluctuated on long time scales, becoming larger or smaller depending on multiple variables.[33] The factors that change OMZs are the amount of oceanic primary production resulting in increased respiration at greater depths, changes in the oxygen supply due to poor ventilation, and amount of oxygen supplied through thermohaline circulation.[33]

In 19th century

From recent observations, it is evident that the extent of OMZs has expanded in tropical oceans during the past half century.[34][35] Vertical expansion of tropical OMZs has reduced the area between the OMZ and surface where oxygen is used by many organisms.[31] Currently, research aims to better understand how OMZ expansion affects food webs in these areas.[31] Studies on OMZ expansion in the tropical Pacific and Atlantic have observed negative effects on fish populations and commercial fisheries that likely occurred from reduced habitat when OMZs shoal.[34][36]

See also

References

  1. ^ a b Lalli, Carol; Parsons, Timothy (1993). Biological Oceanography: An Introduction. Oxford. ISBN 0-7506-2742-5.
  2. ^ "World Ocean Atlas 2009". National Oceanic and Atmospheric Administration. 2009. Retrieved 5 December 2012.
  3. ^ Mann, K.H.; Lazier, J.R.N. (1991). Dynamics of Marine Ecosystems: Biological-Physical interactions in the oceans. Blackwell Scientific Publications. ISBN 978-1-4051-1118-8.
  4. ^ Gnanadesikan, A.; Bianchi, D.; Pradal, M.A. (2013). "Critical role for mesoscale eddy diffusion in supplying oxygen to hypoxic ocean waters". Geophysical Research Letters. 40 (19): 5194–5198. Bibcode:2013GeoRL..40.5194G. doi:10.1002/grl.50998. S2CID 3426474.
  5. ^ Luyten, J; Pedlosky, J; Stommel, H (1983). "The ventilated thermocline". J Phys Oceanogr. 13 (2): 292–309. Bibcode:1983JPO....13..292L. doi:10.1175/1520-0485(1983)013<0292:tvt>2.0.co;2.
  6. ^ Pedlosky, J. (1990). "The dynamics of the oceanic subtropical gyres". Science. 248 (4953): 316–322. Bibcode:1990Sci...248..316P. doi:10.1126/science.248.4953.316. PMID 17784484. S2CID 37589358.
  7. ^ a b Bertagnolli, AD; Stewart, FJ (2018). "Microbial niches in marine oxygen minimum zones". Nature Reviews Microbiology. 16 (12): 723–729. doi:10.1038/s41579-018-0087-z. PMID 30250271. S2CID 52811177.
  8. ^ a b c Lam, P; Kuypers, MM (2011). "Microbial nitrogen cycling processes in oxygen minimum zones". Annual Review of Marine Science. 3: 317–345. Bibcode:2011ARMS....3..317L. doi:10.1146/annurev-marine-120709-142814. hdl:21.11116/0000-0001-CA25-2. PMID 21329208.
  9. ^ a b c Robinson, C (2019). "Microbial respiration, the engine of ocean deoxygenation". Frontiers in Marine Science. 5: 533. doi:10.3389/fmars.2018.00533. S2CID 58010259.
  10. ^ Sigman, DM; Hain, MP (2012). "The biological productivity of the ocean". Nature Education Knowledge. 3 (6): 1–16.
  11. ^ Azam, F; Malfatti, F (2007). "Microbial structuring of marine ecosystems". Nature Reviews Microbiology. 5 (10): 782–791. doi:10.1038/nrmicro1747. PMID 17853906. S2CID 10055219.
  12. ^ Childress, J.J.; Seibel, B.A. (1998). "Life at stable low oxygen levels: adaptations of animals to oceanic oxygen minimum layers". The Journal of Experimental Biology. 201 (Pt 8): 1223–1232. doi:10.1242/jeb.201.8.1223. PMID 9510533.
  13. ^ Sanders, N.K.; Childress, J.J. (1990). "Adaptations to the Deep-Sea Oxygen Minimum Layer: Oxygen Binding by the Hemocyanin of the Bathypelagic Mysid, Gnathophausia ingens Dohrn". Biological Bulletin. 178 (3): 286–294. doi:10.2307/1541830. JSTOR 1541830. PMID 29314949.
  14. ^ Torres, J.J.; Grigsby, M.D.; Clarke, M.E. (2012). "Aerobic and anaerobic metabolism in oxygen minimum layer fishes: the role of alcohol dehydrogenase". The Journal of Experimental Biology. 215 (11): 1905–1914. doi:10.1242/jeb.060236. PMID 22573769.
  15. ^ Deutsch, Curtis; Sarmiento, Jorge L.; Sigman, Daniel M.; Gruber, Nicolas; Dunne, John P. (2006). "Spatial coupling of nitrogen inputs and losses in the ocean". Nature. 445 (7124): 163–7. Bibcode:2007Natur.445..163D. doi:10.1038/nature05392. PMID 17215838. S2CID 10804715.
  16. ^ Leahy, Stephen (20 April 2010). "Giant Bacteria Colonise the Oceans". Inter Press Service. Tierramérica. Archived from the original on 24 June 2010.
  17. ^ a b Elliott, DT; Pierson, JJ; Roman, MR (2013). "Elliott, D.T., Pierson, J.J. and Roman, M.R., 2013. Predicting the effects of coastal hypoxia on vital rates of the planktonic copepod Acartia tonsa Dana". PLOS ONE. 8 (5): e63987. doi:10.1371/journal.pone.0063987. PMC 3656935. PMID 23691134.
  18. ^ a b Elder, LE; Seibel, BA (2015). "Ecophysiological implications of vertical migration into oxygen minimum zones for the hyperiid amphipod Phronima sedentaria". Journal of Plankton Research. 37 (5): 897–911. doi:10.1093/plankt/fbv066.
  19. ^ Seibel, BA (2011). "Critical oxygen levels and metabolic suppression in oceanic oxygen minimum zones". Journal of Experimental Biology. 214 (2): 326–336. doi:10.1242/jeb.049171. PMID 21177952. S2CID 16469678.
  20. ^ a b c Kiko, R; Hauss, H; Bucholz, F; Melzner, F (2016). "Ammonium excretion and oxygen respiration of tropical copepods and euphausiids exposed to oxygen minimum zone conditions". Biogeosciences. 13 (8): 2241–2255. Bibcode:2016BGeo...13.2241K. doi:10.5194/bg-13-2241-2016.
  21. ^ a b Elliott, DT; Pierson, JJ; Roman, MR (2012). "Relationship between environmental conditions and zooplankton community structure during summer hypoxia in the northern Gulf of Mexico". Journal of Plankton Research. 34 (7): 602–613. doi:10.1093/plankt/fbs029.
  22. ^ a b c Vanderploeg, HA; Ludsin, SA; Cavaletto, JF; Höök, TO; Pothoven, SA; Brandt, SB; Liebig, JR; Lang, GA (2009). "Hypoxic zones as habitat for zooplankton in Lake Erie: refuges from predation or exclusion zones?". Journal of Experimental Marine Biology and Ecology. 381: S108–S120. doi:10.1016/j.jembe.2009.07.015.
  23. ^ a b Vanderploeg, HA; Ludsin, SA; Ruberg, SA; Höök, TO; Pothoven, SA; Brandt, SB; Lang, GA; Liebig, JR; Cavaletto, JF (2009). "Hypoxia affects spatial distributions and overlap of pelagic fish, zooplankton, and phytoplankton in Lake Erie". Journal of Experimental Marine Biology and Ecology. 381: S92–S107. doi:10.1016/j.jembe.2009.07.027.
  24. ^ Bianchi, D; Babbin, AR; Galbraith, ED (2014). "Enhancement of anammox by the excretion of diel vertical migrators". Proceedings of the National Academy of Sciences. 111 (44): 15653–15658. Bibcode:2014PNAS..11115653B. doi:10.1073/pnas.1410790111. PMC 4226083. PMID 25288743.
  25. ^ Stramma, L; Prince, ED; Schmidtko, S; Luo, J; Hoolihan, JP; Visbeck, M; Wallace, DWR; Brandt, P; Körtzinger, A (2012). "Expansion of oxygen minimum zones may reduce available habitat for tropical pelagic fishes" (PDF). Nature Climate Change. 2 (1): 33–37. Bibcode:2012NatCC...2...33S. doi:10.1038/nclimate1304. hdl:10961/1538.
  26. ^ Prince, ED; Goodyear, CP (2006). "Hypoxia-based habitat compression of tropical pelagic fishes". Fisheries Oceanography. 15 (6): 451–464. doi:10.1111/j.1365-2419.2005.00393.x.
  27. ^ de Mutsert, K; Steenbeek, J; Lewis, K; Buszowski, J; Cowan Jr., JH; Christensen, V (2016). "Exploring effects of hypoxia on fish and fisheries in the northern Gulf of Mexico using a dynamic spatially explicit ecosystem model". Ecological Modelling. 331: 142–150. Bibcode:2016AGUOSAH43A..07D. doi:10.1016/j.ecolmodel.2015.10.013.
  28. ^ Kraus, RT; Secor, DH; Wingate, RL (2015). "Testing the thermal-niche oxygen-squeeze hypothesis for estuarine striped bass". Environmental Biology of Fishes. 98 (10): 2083–2092. doi:10.1007/s10641-015-0431-3. S2CID 16052635.
  29. ^ Roman, MR; Pierson, JJ; Kimmel, DG; Boicourt, WC; Zhang, X (2012). "Impacts of hypoxia on zooplankton spatial distributions in the northern Gulf of Mexico". Estuaries and Coasts. 35 (5): 1261–1269. doi:10.1007/s12237-012-9531-x. S2CID 84592608.
  30. ^ US Department of Commerce, National Oceanic and Atmospheric Administration. "What is a dead zone?". oceanservice.noaa.gov. Retrieved 13 November 2019.
  31. ^ a b c d Stramma, Lothar; Schmidtko, Sunke; Levin, Lisa A.; Johnson, Gregory C. (April 2010). "Ocean oxygen minima expansions and their biological impacts". Deep Sea Research Part I: Oceanographic Research Papers. 57 (4): 587–595. Bibcode:2010DSRI...57..587S. doi:10.1016/j.dsr.2010.01.005. ISSN 0967-0637.
  32. ^ a b van Geen, A.; Smethie, W. M.; Horneman, A.; Lee, H. (7 October 2006). "Sensitivity of the North Pacific oxygen minimum zone to changes in ocean circulation: A simple model calibrated by chlorofluorocarbons". Journal of Geophysical Research. 111 (C10): C10004. Bibcode:2006JGRC..11110004V. doi:10.1029/2005jc003192. ISSN 0148-0227.
  33. ^ a b Cartapanis, Olivier; Tachikawa, Kazuyo; Bard, Edouard (29 October 2011). "Northeastern Pacific oxygen minimum zone variability over the past 70 kyr: Impact of biological production and oceanic ventilation". Paleoceanography. 26 (4): PA4208. Bibcode:2011PalOc..26.4208C. doi:10.1029/2011pa002126. ISSN 0883-8305.
  34. ^ a b Stramma, L.; Johnson, G. C.; Sprintall, J.; Mohrholz, V. (2 May 2008). "Expanding Oxygen-Minimum Zones in the Tropical Oceans". Science. 320 (5876): 655–658. Bibcode:2008Sci...320..655S. doi:10.1126/science.1153847. ISSN 0036-8075. PMID 18451300. S2CID 206510856.
  35. ^ Gilly, William F.; Beman, J. Michael; Litvin, Steven Y.; Robison, Bruce H. (3 January 2013). "Oceanographic and Biological Effects of Shoaling of the Oxygen Minimum Zone". Annual Review of Marine Science. 5 (1): 393–420. doi:10.1146/annurev-marine-120710-100849. ISSN 1941-1405. PMID 22809177.
  36. ^ Hallam, Steven J.; Torres-Beltrán, Mónica; Hawley, Alyse K. (31 October 2017). "Monitoring microbial responses to ocean deoxygenation in a model oxygen minimum zone". Scientific Data. 4 (1): 170158. Bibcode:2017NatSD...470158H. doi:10.1038/sdata.2017.158. ISSN 2052-4463. PMC 5663219. PMID 29087370.