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Ocean Acidification - Science topic

Ocean acidification is the name given to the ongoing decrease in the pH of the Earth's oceans, caused by the uptake of anthropogenic carbon dioxide (CO2) from the atmosphere. About a quarter of the carbon dioxide in the atmosphere goes into the oceans, where it forms carbonic acid.
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Earth’s ‘Big Five’ Mass Extinctions
Global Warming: Is it something NEW to our planet?
Extinctions are a normal part of evolution: they occur naturally and periodically over time.
Evolution occurs through the balance of extinction – the end of species – and speciation – the creation of new ones.
In a mass extinction, at least 75% of species go extinct within a relatively (by geological standard) short period of time, typically less than two million years.
The first known mass extinction – End Ordovician (444 million years ago) – with intense glacial and interglacial periods - resulted in 86% of species lost - with significant changes in Ocean Chemistry. Resulted in Climate Change.
The 2nd known mass extinction – Late Devonian (366 million years ago) resulted in 75% of species lost. Resulted in severe Global Cooling.
The 3rd known mass extinction – End Permian (250 million years ago) resulted in 96% of species lost - with elevated CO2 and Sulfur levels from volcanoes caused ocean-acidification/acid-rain. Resulted in Global Warming.
The 4th known mass extinction – End Triassic (200 million years ago) resulted in 80% of species lost - with drastic changes in the chemical composition of Oceans. Resulted in Global Warming.
The 5th known mass extinction – End Cretaceous (65 million years ago) resulted in 76% of species lost - with an asteroid impact in Yucatan, Mexico. Resulted in rapid Global Cooling.
Are we already going through 'Sixth Mass Extinction'? If so, 'Anthropocene' to be blamed?
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There is growing evidence to suggest that the Earth is currently experiencing a "Sixth Mass Extinction" event, characterized by a rapid and widespread loss of biodiversity. While mass extinctions have occurred in the Earth's history before, the current rate of species loss far exceeds the natural background extinction rate. Human activities, particularly those associated with the Anthropocene era, are widely implicated in driving this biodiversity crisis.
The Anthropocene, often referred to as the "Age of Humans," is marked by significant human impacts on the Earth's geology and ecosystems. Human activities such as deforestation, habitat destruction, pollution, overexploitation of natural resources, climate change, and the introduction of invasive species have all contributed to the current biodiversity crisis. These factors disrupt ecosystems, degrade habitats, and directly threaten species survival, leading to population declines and extinctions.
While natural factors such as volcanic eruptions, asteroid impacts, and climate fluctuations have historically driven mass extinctions, the primary drivers of the current biodiversity crisis are anthropogenic. The profound changes brought about by human activities highlight the need for urgent and concerted action to mitigate further biodiversity loss and preserve ecosystems for future generations. Efforts to address climate change, conserve habitats, protect endangered species, and promote sustainable practices are essential in combating the Sixth Mass Extinction and safeguarding the planet's biodiversity.
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Climate change leading to a 'Super-Dynamic' Coastal System?
1. Regarding the accelerated sea-level rise predictions associated with the melting of glaciers and ice sheets and from thermal expansion of water, where do we stand now, with reference to the levels of 2000, 2010 & 2020?
Where do we stand now, from '2 mm per annum' during 20th century?
2. If mean sea levels have already risen to the anticipated levels, then, at how many places across the globe, the coastal shorelines have got retreated?
And, how many low-lying areas have been inundated across the globe?
3. Have we captured any significant change in the run-off to the coast, resulting from (a) extreme rainfall events; and (b) enhancement in mean global temperature?
4. Whether the sustainability of existing coastal communities and natural resources have become a challenging task – associated with the climate change?
5. How easy would it remain for coastal economies in order to adapt to the changing climate?
How complex would remain to be the role of coastal land-forms and estuaries?
6. Do we have a control over the impacts and the timing of the impacts of the extreme events associated with coastal regions – resulting from climate change?
7. What exactly have we learnt from an enhanced erosion of beaches; and frequent flooding from rivers and tidal surge?
8. To what extent, coral reefs and shellfish have been affected by ocean acidification resulting from an enhanced uptake of atmospheric CO2 by the oceans?
9. How exactly waves, winds and currents have been altered resulting from sea-level rise and increase in sea surface temperature?
Have we observed any fundamental changes in physical forces associated with ocean circulation and sediment budgets?
10. Whether climate change has resulted in a significant variation in ocean circulation pattern?
Feasible to capture the effects of sea level rise given the wide range of variations in both spatial as well as temporal scales?
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The answers to your questions are in my monograph "Modern changes in the level of the Black Sea as the basis for the strategy of construction development of the coasts". Look at several of the drawings analyzed in my book.
The first figure is the rise and fall of the coast relative to the shape of the geoid. It's about geodynamics. These are answers to requests about land flooding.
The following figure shows the dependence of sea level changes on increasing carbon dioxide emissions into the atmosphere. On this issue, see my discussion "Increasing carbon dioxide contribute to lowering sea levels? Is it possible?".
The other two figures provide information about the stabilization of sea level changes.
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Decreased carbonate ions with increased bicarbonate ions reduce pH. But while measuring water quality, we estimate carbonate and bicarbonate ions as one of the parameters and a higher concentration of these ions indicates alkalinity. But how ocean acidification happens when bicarbonate concentration increases.
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I'd say it's just the opposite. The activity ratios of CO3-2, HCO3- and H2CO3* are controlled by the pH value and also by the partial pressure of CO2. It is carbonate equilibria.
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I want to know which is the best part to look at to compare if coral calcification is affected by in situ low pH environment. I've been reading papers but I can't pinpoint which part they are looking at under SEM. My fragments are from the genus Porites, Goniopora, and Platygyra.
#corals #calcification #microstructures #skeleton
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Hi Joana,
I am not 100% sure what questions you are asking but if you are interested to compare the effects of ocean acidification (i.e., lower pH) on coral skeletons you have some options. Looking and comparing basic skeletal corallite structures at macro-morphological (e.g., corallite diameter and wall thickness; septal and costoseptal thickness and high) and micro-morphological levels (e.g., septal teeth height) would be relatively easy. You can look at the thickness and porosity of the skeletal material in general. Recently new studies have been done on pH effects on crystallographic features of coral skeletons (see attached paper). I hope the attached papers will assist you in getting your answer, the reference sections are full of good papers.
Cheers,
Tom
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Since 1850 59% of atmospheric CO2 emissions have been taken up by terrestrial and marine sinks according to AR6 (see attached image). This amounts to 1430 Gt of CO2. Unlike the terrestrial sink, which is largely permanent (soil organic matter and living biomass), some of the marine sink is transitory. For example, a portion of dissolved CO2 (and the carbonate and bicarbonate is equilibrates with) will offgas when atmospheric partial pressure of CO2 drops, after accounting for the time lags in oceanic circulation.
Do any of you have references to studies that estimate what portion of the marine sink is permanent? This is important when calculating how much excess CO2 (atmospheric plus transitory marine) we need to draw down to solve climate change and ocean acidification. Thank you!
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Are there studies showing that shells from living or dead oysters prevent ocean acidification and ultimately promote the absorption of carbon dioxide from the atmosphere?
It would be better if there were quantitative calculations as well.
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I hope the attached paper helps. It is an interesting topic.
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i have to give an university exam on february 11 and i can't find enough information about it. i have to present the whole exam on the phenomenon of bioluminescence: how has the phenomenon changed over the years and i need the relationship between it and ocean acidification. if any of you have anything useful i would be grateful. thank you very much.
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There are a couple of articles, and the result of a discussion at the SICB annual meeting.
Waters & Lloyd's 1985 "Salt, pH and Temperature Dependencies of Growth and Bioluminescence of Three Species of Luminous Bacteria Analysed on Gradient Plates"
Mangwani's 2015 "Ocean acidification and marine microorganisms: responses and consequences"
And the "Turning up the lights: Ocean acidification may increase light intensity of secretory bioluminescent signaling" discussion :
Hope this helps!
Greg
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The current rate of acidification could be unprecedented in Earth's history: it is estimated to be 10 to 100 times faster than the acidification events of the last 50 million years. How do you see the biological impacts of ocean acidification in this changing climate? 55 million years ago, the thermal optimum of the Paleocene-Eocene led to the extinction of several species, particularly shellfish invertebrates.
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Dear Guillermo Auad,
Thank you very much for your valuable contribution and for the articles you share with me. The information provided by these articles will certainly be very useful to me.
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Schiermeler (2010) projections show a range of environmental impacts related to ocean acidification. Given the importance of temperature and pH conditions in the maintenance of life, should we expect, in the absence of remedial actions, to major changes in the marine food chain or to the extinction of marine invertebrates and vertebrates.
I invite you to share your opinions.
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Dear Evens. Climate change is science and technology, but it's also mostly about politics.
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For a class I am looking at the effects of ocean acidification, and within this although I am finding that there are species that are both negatively (coral, oysters, etc.) affected and positively affected (blue crabs, shrimp) by ocean acidification; I want to know if there are a species that do not seem to be affected by acidification and can convert carbonic acid into bicarbonate, therefore limiting the effects and maintaining a controlled pH level.
If not, is there anything that could be created to do so, and is there any research on that?
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Golonka Jan but can they convert when its already in the form of carbonic acid? that is the part I am unsure of
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A lot of studies on climate change / ocean acidification focus on testing biological responses of organisms to future projected ocean pH etc, often through artificially-controlled mesocosms (eg naturalistic aquaria) and this means that we overlook the capacity of organisms to adapt to that change over time.
Is there any research institute that is developing a controllable aquatic mesocosm where CO2 and other factors can be maniuplated so that studies of pre-industrial CO2 levels etc could be conducted?
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Dear researchers,
I would much appreciate if you could explain or suggest good research papers regarding the effects of ocean acidification on the chemical composition of the valves of mainly Mytilidae and Pectinidae species and damage, growth, development or biomarker assessment.
Thanks in advance
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You can also get help searching engine of the below doctoral thesis by Alexander Ventura :
Bivalves in the face of ocean acidification
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As the aragonite becomes undersaturated in deep water, will exposed coral skeleton completely dissolve, or is it only a part of the structure (the aragonitic elements) that will dissolve? I am trying to work out how ocean acidification may affect structural complexity on deep water coral reefs, and coral rubble habitats
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Get in touch with me and I can suggest some publications and direct researcher contacts to get numerical answers.
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Blue forests (seagrasses, mangroves and salt marshes) are included in the so called "Blue carbon" ecosystems due to the capacity of those plants to sink Carbon in marine sediments, from dissolved CO2. Nevertheless, many species of corals, algae, mollusks, etc., incorporate Carbon as carbonate from aquatic media and remains for long time forming rocks or marine sediments. Could coral reefs be considered also as Blue forests?
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I want to collaborate with an American partner working on ocean acidification and he should be aware of the monitoring techniques of carbon dioxide and other climatic change parameters.
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Deep thanks
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When writing about climate change, when should we still cite a source and when is it assumed knowledge?
Example:
Coastal areas are affected by sea level rise (CITE????)
Oceans are affected by ocean acidification (CITE???)
Temperature in the ocean is increasing (CITE???)
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I think that we should cite all that is particular and not necessarily general knowledge. To explain the greenhouse effect could be seen as established knowledge. Whether CC leads to more tropical cyclones, or increase the intensity of cyclones, is specialized knowledge. It is also that this issue is contested, so to cite is also showing who claims what particular knowledge/insight/claim.
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Serious question. I read about ocean acidification all the time and I believe pH is currently 8.1. At what point does ocean water become "acidic" I would imagine the same as regular water at a pH below 7. Is saying ocean "acidification" a misnomer?
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But carbonic acid in the ocean is unstable and dissociates into bicarbonate ions then further dissociates into carbonate ions. Carbonic acid does not remain. The marine organisms combine calcium with the carboate ions to calcify and create that skeleton. I guess my question should be, how much CO2 is too much? Perhaps increasing the amount of Forams and cocolithophores in the ocean can help :-). Thank you all for considering my question and for helping me learn about this topic.
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Is there a way to reduce pH of seawater to assess the dissolution of exoskeletons of marine invertebrates of dead organisms(e.g. shell of mussels). In other words can I for instance use HCl to reduce pH to observe structural difference simulating the pH of ocean acidification models?
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Very good question,
interested to follow
Why you prefer to HCL to reduce pH, in same case it's the case?
Any paper in this direction will be useful
Success
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Our research is about the effects of ocean acidification on coral health in Puerto Princesa Bay, Palawan and examining appropriate coral restoration methods.
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hi there Michelle Marijt , i am also working on coral transplanting mainly by transplanting coral fragments onto a cement plate. When they have grown mature in the nursery, we would attach the cement plate to a bigger structure. May i know what species you worked on that could grow within 3 months? and the condition of the nursery or so.. Thank you in advance.
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Dear everyone,
This is not, properly, a question, but an invitation to contribute to an open-access article collection on Physiological Responses in Aquatic Organisms Adapted to Extreme or Changing Environments" to be published by the journal Frontiers in Physiology.
The aim of this topic is to provide up-to-date information on the physiological responses in aquatic organisms, vertebrates and invertebrates, adapted to extreme or changing environments as well as their interactions with endocrine, biochemical and molecular mechanisms. Studies with an approach related to conservation biology are also invited to contribute.
Best Regards,
Alexssandro Geferson Becker
Ignacio Ruiz-Jarabo
Eduardo Luís Cupertino Ballester
Editors
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Thanks for your explaning
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Ocean acidification is the lowering of ocean pH due to increasing levels of CO2 in the atmosphere (from fossil fuel burning, deforestation etc.). The absorption of CO2 has already acidified the surface layers of the ocean causing an overall decrease of 0.1 pH units since the pre-industrial period, which is equivalent to a 30% increase in acidity and a 16% decrease in carbonate ion concentrations. The surface ocean pH is projected to decrease by 0.3-0.4 pH units by 2100 (predicted to decline from approximately 8.2 in pre-industrial times to 7.8 by the end of this century). The changes in basic ocean chemistry due to ocean acidification are likely to have impacts on organisms that require calcium carbonate to build their shells or skeletons such as corals, and molluscs (oysters, mussels, pteropods, and abalone). There are three naturally occurring forms of calcium carbonate used by marine organisms to build shells, plates or skeletons: calcite (e.g. marine plankton coccolithophores), aragonite (e.g. corals, pteropods) and high magnesium calcite (e.g. starfish, sea urchins, brittle stars). The solubility & sensitivity to ocean acidification is higher with magnesium calcite and the least with calcite in the following order: magnesium calcite>aragonite> calcite.
Increasing ocean acidification can significantly reduce the ability of reef-building corals to produce their skeletons via reduced calcification. Successful fertilisation, larval settlement, recruitment, growth and survivorship of corals can be affected due to ocean acidification. A recent research shows that corals, echinoderms and molluscs are very sensitive to a decline in the pH value compared to crustaceans (Wittmann and Pörtner 2013). Many marine fish (about 25% of known marine fish) use coral reef as a habitat, shelter (refuge) and food. Coral reefs provide food and livelihood security for some 500 million people worldwide including 90% protein need of inhabitants of Pacific Island Developing Nations. Coral reefs are the primary economic driver in many tourist destinations and protect fragile coastlines from threats such as tsunamis and erosions.
Some experimental results showed that calcification is generally reduced in mussels under near-future CO2 levels. Projected future CO2 level (rise of ocean acidification) can impact on shell formation, larval development, and survival rate in abalone. A study on the early development of the oyster (Crassostrea gigas) found that shell calcification is reduced in juveniles and their body shape and size are also altered. Many mollusc species at the adult and juvenile stages have shown reduced growth and/or health under projected ocean acidification scenarios. Molluscs are food for commercial fish such as haddock, halibut, herring, flounder and cod. Clams, scallops, mussels, oysters, abalone and conchs provide direct protein sources for various island and coastal communities and are valuable commercial fisheries. Molluscs account for 8% of the global marine catch.
Though the effects of increased acidity on adult finfish seems to be minimal or supposed to be largely unaffected (since fish are able to control their acid-base balance by bicarbonate buffering, mainly across the gills and via the kidney), however, some recent experiments with tropical coral reef fish suggest that the sensory systems of fish can be affected by ocean acidification. For example, when clownfish (Amphiprion percula) were exposed to higher CO2 levels, they could not distinguish predator from non-predator and were found swimming toward predators, instead of away from them (Dixson et al. 2010). The loss of the senses of sight/smell/touch due to ocean acidification would thus reduce survival in commercially important fish species. Another experiment (Frommell et al. 2012) showed detrimental effects of ocean acidification on the developmental stages of Atlantic cod larvae (Gadus morhua). Exposure to elevated CO2 levels resulted in severe to lethal tissue damage in many internal organs in larval cod, with the degree of damage increasing with CO2 concentrations. As larval survival is the bottleneck to recruitment, ocean acidification has the potential to act as an additional source of natural mortality, which may affect populations of already exploited fish stocks. A small change in early life survival can generate large fluctuations in adult-fish abundance in the wild.
Antarctic krill (Euphausia spp.) is a key pelagic species in the southern region and represents the largest fishery resource. Many animals like whales, seals, penguins and fish are dependent on krill fishery. Marine ecosystems in particular krill populations could be vulnerable to ocean acidification. For example, when krill eggs were exposed to elevated seawater CO2 levels, hatch rates were found significantly lower, it also delayed embryonic development (Kawaguchi et al. 2013). The pteropod, or “sea butterfly” (with aragonite shells) are an important food source (for fish such as juvenile salmon, birds, tiny krill, and giant whales). They (pteropods) are also a good indicator of ecosystem health and play an important role in the oceanic carbon cycle. The shells of pteropods, Limacina helicina antarctica – living in the seas around Antarctica are being severely dissolved by ocean acidification according to a new study (Bednaršek et al. 2012). The main consequence of loss of shell due to ocean acidification will be increasing vulnerability of pteropods to predation and infection, which will in turn impact other parts of the food web.
Ocean acidification may cause an increase in jellyfish (Attrill et al. 2008). Jellyfish are key predators and can affect the abundance of zooplankton, fish larvae and eggs, which affects survival to the adult stage (or recruitment) of fish populations. As jellyfish are rarely the preferred food for other marine animals, any significant increase in their numbers could have major consequences for pelagic ecosystems and fisheries.
Nevertheless, rising CO2 may enhance productivity of non calcifying seagrasses, seaweeds as they require CO2 for photosynthesis and living, for example, photosynthetic organisms such as seagrasses showed higher growth rates, as much as five-fold or higher with acidification (Hendriks et al.2010 )
Question: Will ocean acidification be a threat to seafood security, commercial fishing and livelihoods? If so, how?
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The daily activities of human beings result in the emission of huge amounts of harmful gases, such as carbon dioxide, sulfur oxides and nitrogen. The most important of these activities are the various industries based on burning fuel, power plants, heavy fuel, transport,
 These gases are released into the atmosphere, many of which dissolve in rainwater and sea and ocean waters. Carbon dioxide is dissolved in water and carbonic acid is formed, which causes the acidity of the water to rise.
Many marine organisms are affected by the acidification of the oceans. Many marine systems have deteriorated in many regions of the world after the concentration of carbon dioxide in the atmosphere has increased significantly,
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What are the effects of ocean acidification on the enzyme carbonic anhydrase with a focus on the role of the enzyme both in the calcification. I found several works in which the external, internal enzyme is down-regulated in the presence of high concentrations of CO2. In Corallina officinalis the external carbonic anhydrase increases its activity as it produces carbonate ions from bicarbonate ions. There are some papers that support me that in the presence of high concentrations of CO2, instead of hydration, the conversion of HCO3- into CO32- is favored? Could you please give me a suggestion? Thank you so much.
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Hello Anna, I think this article will solve your problem.
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Does anyone know of a site where I can find the pH of ocean waters in various oceans and at various depths?
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Dear Alistair,
yes, the reason is not too difficult, but it has two parts.
The first part is pure carbonate chemistry: the pH really is mainly a function of two quantities, dissolved inorganic carbon (DIC) and Alkalinity (Alk). With rising DIC, at constant Alk, pH decreases, and with rising Alk at constant DIC, pH increases. The deep Pacific has a higher DIC, compared to the deep North Atlantic, hence its pH is lower; the tendency is somewhat moderated by the fact that Alk is also higher in the North Pacific, compared to the Atlantic, but not as much as DIC.
The second part is: Why is DIC higher in the deep Pacific than in the deep Atlantic? This has to do with the pattern of the deep ocean circulation, the overturning: Deep water is mainly formed (i.e. it had its last surface contact with the atmosphere) in the North Atlantic (North Atlantic Deep Water, NADW) and around Antarctica (Antarctic Bottom Water, AABW). From there it spreads slowly through the worlds oceans in a somewhat complicated patter, which is best described in a paper by Lynne Talley in Oceanography Magazine in 2013. The upshot is that water in the deep North Pacific is the 'oldest' water in the sense that is has been away form the surface longest.
And on its long travel towards the North Pacific, there has been a constant rain of organic particles into that water, which has been remineralised by bacteria and animals, releasing CO2, i.e increasing DIC (and also nitrate, phosphate and silicate), and reducing O2. In the Atlantic, the water simply hasn't had enough time to accumulate the breakdown products of the constant rain of organic particles.
There is of course more that can be said on that, but to first order that is the explanation, I think.
Cheers, Christoph
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It is true that CO2 is soluble in water. As soon it come in contact with water molecules, it produce carbonic acid.
CO2 + H2O = H2CO3
Carbonic acid work on slightly or non soluble calcium and magnesium salt and make it soluble.
CaCO3 + HCO3 = Ca(HCO3)3
This is how alkalinity/pH is increased.
But how it increase ocean acidity. Or, this ocean acidity is a temporary phenomena?
To me, increase and decrease in oven pH is part of ocean ecology. Why it is presented is a problem?
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There is a full description, by top scientists from Wood Holes Oceanographic Institution, of the problem of ocean acidification here: http://www.whoi.edu/website/OCB-OA/faqs/oa-primer
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Polychaete are one of the most abundant group in marine environment, it contain both sensitive and tolerant species. The increase of Ocean Acidification how to affect the Polychaete?
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Thank you so much
Matthew A.Birk
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Kindly provide advice
Thank you
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I would recommend that you contact the Ocean Acidification International Coordination Center (l.hansson@iaea.org). They are developing and distributing ocean-acidification science kits, with quite an arsenal of instruments and tools to study ocean acidification. Being from Nigeria and at an oceanographic research institute, I think you would qualify to receive this kit free of any charge.
I would also recommend that you contact OA-Africa at https://www.oa-africa.net That is an African network that aims to promote and coordinate ocean-acidification research.
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The ocean is the most resistant ecosystem but due to human activities, ocean acidification is starting to occur, which has resulted to drastic changes in marine communities. Are there any current, feasible solutions to this problem? 
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 scientists have said that It will take more than 700 years to reverse ocean acidification to the point of pre-industrial conditions, even with the most aggressive carbon dioxide removal techniques. You may find the following links interesting. Scientists from the Potsdam Institute for Climate Impact Research in Germany say that if we were to remove CO2 from the atmosphere at a rate of 2.5 times that of the current annual emissions, oceans would not recover to a low-emission state by 2700.
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 In what capacity will marine biological systems and species adjust and react to the individual and intelligent impacts of warming, anoxia, and ocean acidification, and to what degree is mitigation conceivable?
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The general response of species is tolerance and resistance to the environmental variables - the zone of tolerance will be the zone within the limits of which the species can live indefinitely amd the zone of resistance is the zone in which the species can live for a finite time, both defined by temporal limits/rigours of the exposed environmental facor such as temperature, dissilved oxygen or pH - influencing the organism individuaaly and in concert.  The responses will  change with species and other specific conditions. This is a general view based on the   environmental effects on organisms.
See:
Fry, F.E.J. (1971) The effect of environmental factors on the physiology of fish. In: Hoar, W.S. and Randall (Eds.), Fish Physiology, Vol. VI, Academic Press, London, pp. 1-98.
Kutty, M. N. (2002)  ECO-PHYSIOLOGY OF FISHES WITH SPECIAL REFERENCE TO THEIR THERMAL REQUIREMENTS. Proceedings of DAE-BNRS National Symposium on Thermal Ecology at M.S. University, Tirunelveli, TN, India. February, 1-2, 2002, pp 1-14.
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Dinosaurs and several other prehistoric animals grew to be gigantic in their time. Ultimately, most animals in the past are significantly larger than the animals now. One largely recognized theory is that the level of oxygen is a major factor for this contrast in sizes. Taking this theory into consideration, is it possible for animals (and plants) to gradually evolve into larger sizes when the oxygen level is increased? Take for example a theoretical experiment inside a large  dome or a controlled environment where oxygen levels are maintained at a high level. Does the abundance of oxygen entail a gradual growth in the size of the organisms (over generations) assuming that this abundance does not affect them fatally? 
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Jehron:
In order to address your question you need to understand what Galileo Galilei had stated long ago: "Nothing is big or Small except by comparison". This implies that one needs to apply "Relative Magnitude" concept to understand Size. If we apply this concept you would find the Life invisible to unaided human eye could have Giant entities like giant Viruses, Bacteria etc. Although elevated levels of Oxygen in the geologic record has been linked to major turnover of life, but the evidence is not so straightforward (see link). Increased levels of Oxygen would have no impact on the size of the Life on planet earth.:
Best
Syed
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The area might possible experience a number of typhoons over the year, stable is understood as most resistant to those factors mainly minimizing the loss of coral transplants.
Least invasive for further definition is the impact the method would have in terms of length of implementation and use of tools that would bore into the ocean floor for example.
Examples of the methods can be found in the provided links.
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Thank you for the article, it should help with the formulation of my theoretical methodology.
The area of the study is Apo Island Marine reserve, apart from having experienced two typhoons, locally named Sendong and Pablo that have destroyed portions of the coral reef, it has also experienced destruction through destructive fishing methods via blast fishing and use of cyanide. To my knowledge, or my research thus far it has not experienced a large bleaching event due to rising ocean temperatures. I do understand the significance of that factor, in the theoretical study this is for the coral species that is to be transplanted will also be tested on their resistance to changes in the environment measured through their survival rates, among those factors would be how resistant they are to changes in temperature.
The question is to aid in formulation of my methodology for a mock research proposal for my undergrad ecology class so the budget is more of to be determined based what I am able to formulate through the methodology, so I wont be able to answer a project 'How much'
While i do understand that global warming is the main problem to prevent further loss of total coral cover, the theoretical objective of the experiment is to propagate and hopefully better protect the damaged portions of the Apo Island Reef system.
If it would interest you I can send you the current draft of my introduction and review of related literature. Thank you for your time and interest.
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I would like to obtain information to model development times at different temperatures of larvae of blue mussels belonging to the Mytilus edulis complex, especially those found in the northwest Atlantic: M. edulis sensu stricto, M. trossulus, and/or their hybrids.
I have found a number of old studies reporting growth (size increase, not development) and survival at different temperatures, and newer studies quantifying growth and development at a few temperatures plus further manipulations (e.g., different pH in ocean acidification studies), but haven't had much luck finding basic temperature-dependent development studies. I.E., a study rearing mussel larvae at multiple controlled temperatures and reporting times or rates of development (total and/or through specific stages). But, surely such information must be out there. Can someone please direct me to some useful sources?
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Does salinity fluctuation have a major effect on survival and growth of Vibrio alginolyticus and V. proteolyticus?
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I hope this gonna help you
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I need studies conducted in the southern hemisphere for my dissertation - preferably in the Indian Ocean and South Pacific Ocean. 
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Few and far between I'm afraid. There have been a number of studies in South America - look for Morandini, Schiariti, Mianzan. In Australasia look for Pitt, Lindsay, Seymour.
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No instruments that are currently used and the amount of data that exists along the Pacific Ocean and Atlantic.
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Hi Jair,
There are many methods that could help you to estimate the acidification variation in the seawater column. For instance, I recommend this article for you: https://www.researchgate.net/publication/275719192_Acidification_of_the_Mediterranean_Sea_from_anthropogenic_carbon_penetration?ev=prf_pub .
If you need further information or clarifications, do not hesitate to send me a direct message.
Regards,
Abed
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Warm Greetings, Fellow Researchers!
I am currently doing research on ocean acidification and its effects on corals in the Philippines. I would like to determine coral colonies resilient to ocean acidification for the purpose of developing appropriate and efficient restoration techniques. I am currently looking into molecular markers that may serve as basis for stress response and in turn resilience, of the coral colonies. I am currently thinking of microsatellite genotyping. Would this be the best approach? Thank you!
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Mr. John,
Thank you for your answer. I will look into heat shock proteins right away. Ideally we might be able to study the entire genome so I will look into that as well!
Many thanks,
Allan Copuyoc
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Our research is about the effects of ocean acidification on coral health in Puerto Princesa Bay, Palawan and examining appropriate coral restoration methods.
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KMT:
The link cited by me was a review article on Corals to provide some clues rather than actual transplantation issues. The article is indeed scary and sounds alarming and with rather unrealistic predictions.
We cannot be sure whether Jv down voted your answer or someone else.
Best
Syed
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1) Is there any risk that salinity measurements,as translated from conductivity, would carry error in experiments modifying the ionic environment of seawater through ocean acidification (or other)?
2) Is the natural ratio between different salts present in natural seawater modified by ocean acidification?
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1) In a theoretical sense, yes. Since conductivity is a measure of the flow of an electrical current, changing the concentration of ions (such as H+) will change the conductivity.
In a practical sense, no. The change in conductivity due to ocean acidification and increasing H+ concentrations would be insignificant compared to the conductivity of seawater due to all the dissolved salts that are already in the ocean...and therefore there is no need to worry that oceanic salinity measurements would start to be wrong.
Here's my rationale: The concentration of H+ in the oceans is 6.3 x 10-9 mol/L at a pH of 8.2. If there were catastrophic acidification and the pH decreased to 7.0, the concentration of H+ would be 1 x 10-7 mol/L. [Note that I am not suggesting that the ocean's pH would get that low anytime soon, just using it as an example.] Even though that is a ~15x increase in the concentration of H+, the concentration of H+ is still minuscule compared to other ions in seawater. For example, the most abundant cation in the ocean is Na+, which has a concentration of roughly 4.7 x 10-4 mol/L. Note that this is more than 3 orders of magnitude greater than the concentration of H+ in a super-acidified ocean (and doesn't even consider the contributions to conductivity of all the other ions in seawater).
2) I suppose that ocean acidification could, theoretically, change the solubility for certain salts or might increase the chemical weathering/dissolution of certain rock types that would then change the ratio of salts in seawater. As a first guess (literally, a guess), I wouldn't expect either of the things I mentioned to change the ratio of different salts by significant amount given the predicted levels of acidification and the huge volume of the ocean. Maybe a marine geochemist will show up to provide a better answer.
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 I'm trying to evaluate CO2 content of seawater in the surface and at depth of the Damariscotta River (ME). So far I've looked at Turner's C-sense ($9K) and Sunburst's SAMI-CO2 ($18K)and I'm looking for a 3rd sensor for comparison as well as advice. Thanks!
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it is not my field of experience
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what are the major possible impacts of ocean acidification on pteropod ecology and distribution? 
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Shells will be thinner as well as shell dimensions will change. Finally they may not survive anymore after few years. 
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How does ocean acidification relate to fisheries and sustainability of aquatic resources?
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Marine aquatic biota are highly sensitive to pH of water. It is difficult to generalize the impact of ocean acidification as different species have their own range. Apart from reduction in population of native species, introduction of some new species is also possible. In India such a situation was observed in Chilka lake which is fed by sea water.. Change in pH resulted in disappearance of several species.
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Ocean acidification due to CO2 increase affect bio calcification.  We can suppose that the same effect can be found in fresh water. However I did not found any research about the effect of CO2 on pound and lac. This is probably because it is negligible in such a limited amount of water. Do you have any knowledges about the atmospheric/pound physiochemical exchanges and the effect of CO2 increase?
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See: Maberly, S. C. (1996). Diel, episodic and seasonal changes in pH and concentrations of inorganic carbon in a productive lake. Freshwater Biology, 35(3), 579-598.
CO2 dissolution will acidify not just seawater but also freshwater, the same way soda water is produced. But lakewater pH is also under the (stronger) influence of land and sediment such that atmospheric CO2 plays a relatively minor role. Also, we need to consider that marine organisms have adapted to a stable pH for centuries; it becomes a challenge for them to cope with the recent rapid (relatively speaking) acidification of the ocean.
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This may help to compare  ocean acidification studies.
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For ocean CO2 data, there are a few major databases, many of which have inconsistent inclusion of other data (e.g. pH, O2), but all of which should have S and T at least.  These include:
http://cdiac.ornl.gov/oceans/ (lots of moored and underway surface ocean CO2 data)
The next version of SOCAT will have more parameters such as pH, but will still only be ocean surface data.
For water column data, you can check out GLODAP (likely to have many data sets with multiple parameters for ocean acidification work): http://cdiac.ornl.gov/oceans/glodap/GlopDV.html
The US National Centers for Environmental Information databases (likely to have many data sets with multiple parameters for ocean acidification work): https://www.nodc.noaa.gov/access/
Good luck.
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Just need to know how ocean acidity will affect shell strength over the course of 60 days. 
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The IPCC has a nice overview on this subject that uses the current literature to make projections on effects on a variety of marine animals. http://www.ipcc.ch/  I cannot remember which one you want, but search on acidity and mollusc or coral and you'll pick it up.
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Greetings! I am currently working on a study involving Crassostreia iredalei and Scylla serrata, two species of shellfish located in the Philippines. I was looking into the possible effects of the lowering of oceanic pH and whether it can have implications on the economical trade (oysters and crabs being a delicacy). While there is already some literature referring to this topic, I wondered other fellow researchers. 
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Hi Andre
See the 2 links below.
ACECRC in Tasmainia has done a lot of work inthis area and should be a good staring point for you.
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Is it possible that the ocean acidification may not appear so simple with the continuous drop in pH after doing a continuous measurement? How do you deal with the simplification of this issue?
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80 years of ocean pH records, consisting of over 2 million records have been hidden from you and the rest of the world, and replaced with a single model hindcast.  It's a terrible thing and all who continue to act like that never happened should reconsider their positions.  My own research in progress has included an exploration of this missing data at www.abeqas.com .  You will see that the actual data show an oscillatory and diffuse behavior as one should expect given other oscillatory ocean parameters such as the Pacific Decadal Oscillation.
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I am searching for an organism that is also easy to breed in the aquarium and reproduces relatively quickly (say up to 2 or 3 months is ok). I am open to both salt- and freshwater organisms!
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I agree with Ana and Kantha. I would also suggest larval stages (pelagic stages) of species such as lobsters, carbs and bivalves which are really sensitive to acidification (decalcification etc..) Cheers,
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Maybe you have already seen this paper of Morabito et al. 2013, they found that ocean acidification affected the osmotic swelling etc of nematocysts. That would hamper their capacity for food capture. This is a really interesting, and devastating, effect that has received very little attention.
Morabito et al. 2013. Sea Water Acidification Affects Osmotic Swelling, Regulatory Volume Decrease and Discharge in Nematocytes of the Jellyfish. Cellular Physiology and Biochemistry 32(suppl 1): 77-85.
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It’s an incredibly interesting question, Susanna. We’ve known for many decades and across a fairly wide body of literature that pH affects the discharge of nematocysts: in some cases, this is inhibitory, while in other cases this is stimulatory. Most of this work has been done in the context of first aid for things that sting us, rather than on the subtler shifts that could alter an organism’s ability to survive. But given everything we know about nematocysts, it seems completely plausible to me that yes, OA could conceivably alter the discharge of nematocysts. In fact, I would go so far as to say it would be surprising if it didn’t. It’s just an educated guess – certainly the research needs to be performed! Man, this is exciting!
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Oceans are becoming more acidic. How will it affect the marine life?
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"Effects of Ocean Acidification on Marine organisms"  is a heavy weight phrase in modern marine research. Marine organisms are numerous and there is not a single effect on them. hence this is not a valid question in fact. Neither oceans are becoming  only acidic, but warmer and oligotrophic, means multi-stressors and effects are also combined  The main reason is the changing carbonate chemistry for dissolving more CO2 in the surface seawater resulting in: increasing CO2, hydrogen ion and bicarbonate ion concentrations  and decreasing pH and carbonate ion concentrations. There are huge literature on each component of marine ecosystems and their responses to ocean acidification, starting from bacteria, phytoplankton, calcifying, non-calcifying phytoplankton, macroalgae, corals, microzooplankton, mesozooplankton, fish, fish larvae and so on . Each component expressed unique responses to changing carbon chemistry parameters. the effects on ecosystem levels would be a combined one and not really an easy job for the marine ecologists.
There were three international symposiums only on "Ocean in a high CO2 world", a special issue was published in Biogeosciences and several publications in Nature Climate change and Nature Geo Science. some are given bellow"
1. Lessons learned from ocean acidification research, Ulf Riebesell  & Jean-Pierre Gattuso, Nature Climate Change, 5,12–14(2015) doi:10.1038/nclimate2456
2.Scott C. Doney, Victoria J. Fabry, Richard A. Feely, and Joan A. Kleypas, Ocean Acidification: The Other CO2 Problem Annual Review of Marine Science
Vol. 1: 169-192 (Volume publication date January 2009) 
3. Broadgate, W. et al. Ocean Acidification Summary for Policymakers: Third Symposium on the Ocean in a High-CO2 World (International Geosphere-Biosphere Programme, 2013). 
4. Schlüter, L., Lohbeck, K. T., Gutowska, M. A., Gröger, J. P., Riebesell, U. and Reusch, T. B. H. (2014) Adaptation of a globally important coccolithophore to ocean warming and acidification Nature Climate Change, 4 (11). pp. 1024-1030. DOI 10.1038/NCLIMATE2379. 
5.Lohbeck, K. T., Riebesell, U. and Reusch, T. B. H. (2012) Adaptive evolution of a key phytoplankton species to ocean acidification Nature Geoscience, 5 . pp. 346-351. DOI 10.1038/ngeo1441. 
6.Turley, C., Eby, M., Ridgwell, A. J., Schmidt, D. N., Findlay, H. S., Brownlee, C., Riebesell, U., Fabry, V. J., Feely, R. A. and Gattuso, J. P. (2010) The societal challenge of ocean acidification,  Marine Pollution Bulletin, 60 (6). pp. 787-792. DOI 10.1016/j.marpolbul.2010.05.006. 
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Acidification of the Hooghly estuarine system...
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Corals are very sensitive organisms, the bleaching problems may be due to combine effects of many adverse environmental factors like Temperature combined with other pollutants.
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Acidification of ocean water of the Hooghly estuarine system
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Also see the attached file
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I read some interesting articles about ocean acidification and chemical reaction in the Ocean. Ocean acidification occurs when pH-levels of the ocean decrease due to rapid increase of CO2 production in the atmosphere by human activity. However, how can the ocean be acidic whereas it has an extremely effective buffering effect (carbon dioxide-carbonate-bicarbonate equilibrium). And also, what are the roles of cyanobacteria and algae to convert CO2 for photosynthesis? I hope I can get some actual explanation to help make me understand the process. Thank you.
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You can look at it as a perturbation of the carbonate buffering system. Basically by increasing the concentration of CO2 you are shifting the equilibrium of the carbonate system in such a way that, in the end, the concentration of HCO3(-) and H(+) ions increase while the CO3(2-) concentration goes down. The increase in H+ ions is what causes the pH to drop, i.e. acidification, although the seawater will still have a pH above 7 so will not technically be “acid”. The decrease in CO3(2-) is what leads to the decrease in Aragonite and Calcite saturation and this is the problem for organisms that use these minerals for calcification (eg corals, pteropods, molluscs, forams, etc).
In simple chemical terms (taken from Andrew Dickson) it plays out as follows:
When CO2 dissolves in seawater it combines with water to form hydrogen (H+) and bicarbonate (HCO3-) ions:
CO2 + H2O -> H(+) + HCO3(-)
Some of the hydrogen ions combine with carbonate (CO3(2-)) ions to form additional bicarbonate ions resulting in a decrease in the former and an increase in the latter:
H(+) + CO3(2-) -> HCO3(-)
Thus, the net effect when is added to seawater is for the concentrations of H+, CO2, and HCO3- to increase, and the concentration of CO32- to decrease. —A. Dickson
As to why this will not be buffered or absorbed by photosynthesis and an increase in photosynthetic organisms – a certain amount of it will be but the vast majority will not. CO2 is not the rate limiting chemical for most photosynthetic organisms – eg phytoplankton is primarily limited by iron availability, plus during the dark phase of photosynthesis there is nett CO2 production. There is some evidence that green macro-algae (eg sea grass) might benefit from the CO2 increase but that might be another stress on corals and shift the competitive balance on many reefs (particularly those that are under stress from other sources such as increased nutrients from run-off).
A very good resource is:
which is a clearing house for information and has a lot of resources available for both lay and scientific audiences.
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Acidification has been referred to be already affecting corals  by inducing coral bleaching and diminishing calcification rate.  At least there are evidences that bleaching is frequently currently killing corals by starving or by predisposing them to disease. What about the expected time scale for killing them through other ways, e.g. physiological stress induced by low pH?
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There is no simple answer to this question.
The first concerns for corals regarding low pH were to do with the dissolution of their skeleton or impediments to forming the skeleton rather than physiological effects per se.  There is an abundance of literature showing a variety of responses by corals, some species can cope with low pH, others not so much.  This website has a newsfeed for ocean acidification news and you will find many links to papers looking at the impacts of pH on corals including specific physiological impacts.
The time scale for negative impacts will depend on the rate of pH decline.  it could be decades or centuries- depending on the rate of increase of atmospheric CO2 and consequent decline of seawater pH. If emissions slow down then the time of impact will be pushed back.
Surveys of corals around natural CO2 vents at Papua New Guinea show that corals still grow at pH 7.8 but the diversity is much reduced.  Some species such as porites are able to grow, but the complex branching corals necessary for reef building are less abundant.
Also, be aware that while individual corals may still be able to grow at low pH as 7.8, a coral reef may not form.  A coral reef is a build up of dead carbonate skeletons of corals and other reef calcifiers.  If the coral fields at the PNG vents are a window into the future, then there will be no preservation of skeletal material at this pH even if corals keep growing.  This means that coral reefs may not longer form even though individual corals can grow.  Thus the answer is different for a coral versus a coral reef.  
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Hello All. I am working on Ocean Acidification and fish physiology , could any one please help me in by calculating the relevant pH value for 10 ppt and 2.5 ppt  salt water with pCO2 values of 380, 1000 and 1900 respectively or by suggesting any relevant formulae or tool for it . Thank you in advance .
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Hi Nitin, in addition to the pCO2, you are going to need either the total alkalinity or the total CO2 (the dissolved inorganic carbon). 
Assuming you have either of those, you can download the Excel-based CO2sys ocean carbonate calculator, available at http://cdiac.esd.ornl.gov/oceans/co2rprt.html
If you are familiar with the r-project, there is a very nice library called seacarb (http://www.obs-vlfr.fr/~gattuso/seacarb.php).  
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There is growing interest in understanding the economics of climate change. There are few studies which are looking at the economics of ocean acidification. I would like to know what approaches are currently being undertaken.
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Yes they are. I recommend you contact Dr Caroline Hattam at Plymouth Marine Laboratory. Her email is caro4@pml.ac.uk 
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Nowadays I´m studying a Master of Coastal oceanography at Baja California University (UABC), and my research  focuses on the effect of ocean acidification to the interaction between sea urchins and fishes and algal communites in tropical coral reef ecosystems and the synergic effects of anthropogenic impacts. I´m wondering if anyone knows about some information about the effects on behaviour with field observations?
Best regards.
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Check works by Munday, McCormick and collaborators for OA effects on fish behaviour - they've done a lot. See also works by Jutfelt, and paper by Forsgren, myself & al. You should find all this easily in any scientific index including ISI.
Cheers, Trond
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This is something I have been wondering for a while, but haven't had the time to figure out myself, so I pose this question here on ResearchGate.
Nowadays you hear a lot about the acidification of the oceans and the damage that it causes in reef systems. It has also been found that marine organisms with a calcareous exoskeleton have ever thinner shells, skeletons and etc. Now I wonder how can these organisms have survived in a greenhouse world where CO2 reached levels of 1000 to 2000 ppm. Is it solely the effect of decreasing solubility of CO2 in sea water with rising temperatures, or are there also other factors playing a role?
I am posing this question purely out of interest and curiosity, not for my research project.
Greetings,
Wim
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Dear Wim,
You seem to refer to high CO2 events in past gelogical time, hundreds of millions of years ago. There were certainly such periods. Yet the very high CO2 periods were often coincident with mass extinction events. Many but not all of the corals died off.  And following such events, it usually took 10 million years or so for corals to be reestablished. But the corals that did eventually come back were transformed. The skeletal material and the corals themselves were very different 600 million years ago than they are today.
Unfortunately though, it is not possible to infer ancient surface ocean pH only from ancient atmospheric CO2 levels. For seawater, we need 2 variables to estimate pH (and the corresponding saturation state, which corals are sensitive to); we cannot do it with just 1 variable (CO2). Along with the atmospheric CO2 concentration, we would also need to know the ocean's alkalinity.  "Alkalinity" refers to the capacity of seawater to neutralize an acid; it should not be confused with "alkaline" (which means pH > 7). Today's surface ocean alkalinity is relatively constant and remains unaffected by the rapid ongoing increase in atmospheric CO2. Alkalinity will eventually start to increase from the fossil CO2 that is now going into the ocean by dissolving marine sediments that contain calcium carbonate. But most of the extra CO2 still remains near the surface and will require a thousand years to penetrate throughout the deep ocean; it will require many millenia more before those CO2 enriched waters could dissolve sufficient carbonate sediments on the sea floor to have much effect on alkalinity.
Although these processes are slow relative to the current rapid increase in CO2, they were not limiting in ancient times when the increase in atmospheric CO2 was much slower. That is, ancient ocean alkalinity was surely much higher than today when ancient atmospheric CO2 was elevated. Hence ancient ocean pH was relatively stable, and probably not so different from natural values during the last million years. Further enhancing this stability of ancient ocean pH is the increased weathering of rocks at higher CO2 levels, which also leads to enhanced ocean alkalinity but acts on much longer time scales (tens of thousands of years and longer).
Hope this helps,
James
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We're looking for a less toxic method to preserve seawater samples for later analysis for carbonate chemistry (DIC, pH, alkalinity). We currently use mercuric chloride. Is zinc chloride a useful alternative?
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We're at sea right now, and we're taking some replicate samples for DIC, alkalinity, d13C of DIC, and D14C of DIC with both ZnCl2 and HgCl2.  Hopefully we will have enough replication to publish a small comparison paper in the near future, but we are only comparing inorganic carbon between the two poisons.
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As dolomite in algae bind reefs together, they make it stronger and less vulnerable to acidification in the ocean, forming "super corals".
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A clarification Bea, it is the algae that have the dolomite, not the coral. The algae with dolomite grow over the coral skeletons and form thick resistant crusts.
Merinda
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The best estimates are that pH will decrease by 0.2 or 0.3 pH units in less than 100 years. Previous pH changes of this magnitude have probably occurred over thousands or even tens of thousands of years. However, when change occurs over short time scales (and 100 years is a short time scale in terms of the history of the Earth), there are increased risks of species extinctions.
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There is an article specifically discussing these scenarios and the foreseen behavior in the case of microbial derived productivity alone, would not be under strong alterations. Many other organisms, for sure! i.e. Corals and decalcification, or many other organisms not adapting quickly to lower O2 minimum concentrations.
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Which satellite is the best one for detecting and monitoring the oil spit? Also which one is the most appropriate one for detecting the oil pollution in a marine ecosystem? And which method should be applied?
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Dear Fatemah.
all of the responses above have value. Especially Angela's. However, you need to define the purposemore fully. Is your need ccompliance surveillance for illegal discharged across a large iceanic area or yo support spill response? Where is the area relative to satellite tracking as many are polar orbiting and so cluster near the poles for regular and frequent coverage? Do you have access to ground stations, image analysis or response systems (compliance or clean-up)?
We have recently gone through a full review and needs analysis of satellite oil spill detection and found it very enlightening. Happy to have a conversstion off line. Contact me through my work at Australian Maritime Safety Authority if need be or email paul.irving@amsa.gov.au
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There seem to be two different definitions of phosphate alkalinity (PA) in seawater. Which one is correct? And why?
PA = [H2PO4-] + 2[HPO4=] + 3[PO4-3]
2. According to Dickson and Sabine's Guide to best practices for ocean
CO2 measurements:
PA = [HPO4=] + 2[PO4-3] - [H3PO4]
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Definition (2) is correct. Alkalinity is defined relative to the "CO2 equivalence point" ([HCO3] = [H+]; e.g. pure solution of CO2 without any strong acid or base). The equivalence point is the endpoint of the Gran titration to determine alkalinity. At the pH of the equivalence point [H2PO4-] is the dominant species, and thus when measuring alkalinity "all" phosphate is titrated to [H2PO4-], not to [H3PO4].
See: Morel and Hering (1993) Principles and Applications of Aquatic Chemistry, chapter 2, section 2 "Alkalinity and related concepts"
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What is the status of blue carbon research? What is the potential for CO2 sequestration via blue carbon?
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Some interesting blue carbon research being conducted in North America looking at carbon capture/storage/sequestration in salt marshes by scientists from McGill University in Canada and the United States Geological Survey.
Some papers below:
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What difference does it make to have too much excess acid?
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Your goal is to get a sensitive measure of the change in hydrogen ion concentration as you add acid. If you are close to the equivalence point in a single point titration, then you can better achieve this. An uncertainty of 0.001 in measuring the final pH is equivalent to an uncertainty of about 0.23% in the hydrogen ion concentration. If the pH is 4.0, this is a significantly smaller absolute number than if it is 3.5.
However, sensitivity is not your only problem! You also need to minimize bias. The largest contribution to bias is in your pH measuring system's calibration, which needs to be done ahead of time for a one-point method.
The next largest contributor to bias is bicarbonate ion that has not reacted. There are a variety of ways to deal with this. The best is to bubble the acidified solution with air for a few minutes so as to remove CO2, thus reducing total carbon, and hence the absolute amount of bicarbonate ion present at any particular pH. A slightly lower pH also reduces the proportion of the total carbon remaining that is present as bicarbonate.
Also, in a one-point method the amount of acid you add needs to ensure you get an OK alkalinity for all the samples you intend to measure. Unless you adjust it with some a priori knowledge as to the true alkalinity, you are bound to have compromises.
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Climate Change and subsequent rise of DIC
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Change in DIC due to possible oceanic acidification is widely observed. The metal speciation is quite likely to affect. I cant comment in absolute terms but we have notices this hapenning in teh persian gulf waters.
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Thanks Everyone for very useful input
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Most of the OA studies have looked at CO2 Sequestration as possible cause. How big is the NOx and SOx contribution in OA?
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I am interested in getting various methods of CO2 measurement in seawater.
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You can use pH and TAlk (Total Alkalinity) to computed DIC (Dissolved inorganic carbon) and then pCO2 (partial pressure of CO2). This indirect method can be easily used in any field sampling condition and it is far less expensive and more easy to set up than the direct one (using the IR analysers). TAlk is measured by Gran electrotitration. pH is measured with a combined electrode. In seawater, the electrode is calibrated on the Total Hydrogen Ion Concentration Scale using the buffers prepared according to Dickson (1993). In contrast, in estuaries and freshwater environments, the electrode is calibrated on the National Bureau of Standards (NBS) (Frankignoulle and Borges, 2001). I particularly use this method to get CO2 data in coastal environments (e.g. lagoons, mangroves, ...) and in rivers.
Note that in practice, the pH of samples is computed using the Nernst equation.
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The rate of acidification is higher in the Persian Gulf. I will appreciate getting guidance on best methods to determine argonite unsaturation.
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Thanks Jeff I have pH and total alkalinity, temperature, salinity data. I will download CO2SYS and try using it. Will update you guys on outcome.
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In Arabian gulf the increased salinity due to desalination appears to counter balance the pH drop.
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Think of how we calculate carbonate saturation. The formula is:
CSS= [Ca][CO3]/Ksp
Ksp is a function of the carbonate mineral phase, pressure, temperature, and salinity.
This, in turn, means that both temperature and salinity have a direct influence on carbonate chemistry.
If you want to look at how salinity alone would drive CSS (i.e., all other parameters kept constant), you'll see that an increase in salinity will drive the saturation state up. However, as Paul suggested, it is all going to depend on how salinity interplays with other factors that contribute to carbonate saturation.
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Here are some measurements that we did, the data looks intresting, your comments are welcomed.
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Hi Saif,
Your work here is very interesting and I'd certainly like to learn more about it! I would say the chlorophyll-a (i.e., increased productivity) in the summers and the abundance of macroalgae and seaweed in winter are certainly influencing your trends. In comparison to my above comment regarding the increase in plankton during the summer driving CO2 levels up and decreasing the pH, we know that seaweeds and macro-algae actually take up CO2, and would therefore contribute to a decrease in CO2 and an increase in pH during the winter. This is consistent with your data and, again, coincides with trends seen elsewhere. However, it is important to recognize that marine carbonate chemistry is not so cut and dry, but is very complex. It would not simply be the plankton and seaweeds driving your trends, but other factors are certainly at play as well. With that said, your data makes sense to me and is quite interesting, with pH changes seemingly driven by algal dynamics, and an overall decrease over time!
I'm still interested in the sharp decline in pH during Nov-Dec 09. Have you looked into this? I think it is certainly something worth exploring. An unexpected algal bloom? Seaweed harvesting?
I have a couple of other questions for you as well:
1. How did you measure pH? Were you simply dropping a probe off the side of a boat at different times of the year, or did you have a sensor deployed for given periods of time?
2. If you've started taking measurements of DIC and/or total alkalinity, you can easily derive estimates of the carbonate saturation state (usually with respect to aragonite) using those parameters coupled with temperature and salinity (and chl-a if you have those measurements as well, but these are not critical). Have you looked into this?
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Henk I am trying to see this in Persian Gulf corals, if you finalize a method please share so that we can compare our data later.
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Is there a relationship between increased oceanic sequestration of CO2 and increased phytoplankton concentration, which will eventually increase the organic detritus?
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Thanks very convincing explanation. I am grateful to you Kenneth.
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In most instances CO2 is considered responsible for OA. However in oil producing countries the level of NOx and SOX emission is reasonably high and ultimately gets into the ocean. Cant this be a cause of accelerated OA?
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Thanks Koji looks interesting could you please share the full text I am able to get only the Abstract.
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Carbon di-oxide is the main cause of ocean acidification.
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The microbial fauna like rodolites, and others which need calcium carbonate to build they structure may be afeccted, and the population could be eliminated
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I'm assessing sedimentary carbonate saturation states with respect to aragonite and was wondering if it may be worthwhile to spend some money on DIC analysis rather than measuring pH for predicting aragonite saturation states? Given that DIC is quite expensive, I was wondering if there is any available literature outlining degrees of precision of the two predictors on which to base a decision?
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There is a nice discussion of uncertainty of using various combinations of parameters to describe the CO2 system in seawater in Jason Waters' recent dissertation from the University of Miami:
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The ocean is like a carbon dioxide basin because this is where CO2 present in the atmosphere is absorbed. This is causing this body of water to become acidic greatly threatening marine life, which may eventually kill them.
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As is generally the case with anthropogenic disturbances to ecosystems, ocean acidification will have winners and losers: some populations of marine organisms will adapt, while others will go extinct. A recent study by Parker et al. (2012) provides relevant evidence in this respect. They found that exposing adult oysters to elevated CO2 during reproductive conditioning had positive carry-over effects. Larvae spawned from adults exposed to elevated CO2 were larger and developed faster, but displayed similar survival compared with larvae spawned from adults exposed to ambient CO2. Importantly, this happened just across one generation, which is not enough for natural selection.
Parker LM, Ross PM, O’Connor WA, Borysko L, Raftos DA, Pörtner H (2012) Adult exposure influences offspring response to ocean acidification in oysters. Global Change Biology 18:82–92. DOI: 10.1111/j.1365-2486.2011.02520.x
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The study of increased dissolved CO2 on calcification of organisms suggests that decapods, including crabs and lobsters studied, would not be adversely affected by increases on dissolved CO2 compared to more sensitive corals (for instance) (Ries, 2009, Geological Soc. America 37(12): 1131-1134). Are there other effects of the increased CO2 that may be deleterious to the decapods?
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Dear Joseph
1. Investigations on decapods raised in acidified seawater demonstrated a significantly shorter carapace length than those in control seawater after every molt.
2. Larvae raised in acidified seawater take significantly longer time to reach each molt than under control. In the wild, this may result in spending extended time in the water column, i.e., increased vulnerability to pelagic predators and in turn, reduction in benthic recruitment.
3. Indications of reduced survival when reaching the last developmental stage under acidified conditions were also reported.
4. Decapods have limited capabilities to make up for acid–base imbalances (poor iono- and osmoregulators). The issues are even complex in sluggish, relatively inactive species as those have low circulating protein levels and low buffering capacities.
5. Species existing in low-energy environments (e.g deep-sea and polar habitats) are particularly vulnerable, as they are metabolically limited with respect to environmental change.
6. Elevated pCO2 levels in seawater, such as those predicted for the year 2300, are predicted to have varied impacts on calcification rate, egg production and, growth rate and moulting frequency in marine decapods. Reports illustrate that at these levels, embryonic development is negatively impacted.
7. Further, if the changes in pCO2 come with a rising surface seawater temperature, the impacts may get compounded as the molting process in pelagic larvae of decapoda show an inverse relationship to temperature. This may affect the schedule (seasonal) of emergence of decapod larvae in the plankton, consequently influening the biomass and production of the larvae in the plankton.
Overall, marine crustaceans are generally tolerant to the seawater pCO2 levels projected by 2100 and 2300, but only for a short-term period (few weeks) and only in the more adaptable species, as investigated in the laboratories and anticipated by the researchers. Studies are to be undertaken to evaluate their vulnerability over a long-term exposure to the relevant pCO2 levels, in combination with changes in other environmental factors.
Best
Dola
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If so, why is it not as well known among administrations and citizens? Both threats have the same origin, emission of CO2 into the atmosphere by humans and both will have a major impact on biodiversity. However, acidification of the oceans is much less known. Why? Is acidification of the oceans considered to be less severe for biodiversity?
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Ocean acidification (OA) is an important issue - no doubt - in view of the vast amounts of carbon emissions to the atmosphere and the fact that the world ocean is the largest sink of anthhropogenic CO2. This process is very well documented. But in terms of hard scientific evidence, what concerns the magnitude of OA impact on the marine biota and future trends remains highly speculative, as we are deficient in time series and in relevant experimental data. A fair amount of research is now going (understandably) to the response of calcified organisms (coral assemblages, mollusks, crustaceans, etc) to decreasing pH, where there appears that not one answer wil fit all. In fact it appears that the impact is often species-specific, even within same taxonomic group. While bivalve mollusks and coralline algae do not do well in general under such stress, the response of sea stars and coccolitophores ( a large group of calcareous phytoplankton) will vary from species to species. More importantly, insufficient attention has been paid to potential OA impact on the larval stages of many marine animals, notably fish.
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