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1

Schnoor, Jerald L. "Ocean Acidification." Environmental Science & Technology 47, no. 21 (November 5, 2013): 11919. http://dx.doi.org/10.1021/es404263h.

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2

Fenchel, Tom. "Ocean Acidification." Marine Biology Research 7, no. 4 (May 2011): 418–19. http://dx.doi.org/10.1080/17451000.2010.550051.

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Huo, Chuan Lin, Cheng Huo, and Dao Ming Guan. "Advances in Studies of Ocean Acidification." Applied Mechanics and Materials 295-298 (February 2013): 2191–94. http://dx.doi.org/10.4028/www.scientific.net/amm.295-298.2191.

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During the past 200 years, approximately one-half of the carbon dioxide from human activities is being taken up by the oceans. The uptake of carbon dioxide has led to a reduction of the pH value of surface seawater of 0.1 units, equivalent to a 30% increase in the concentration of hydrogen ions. If global emission of carbon dioxide from human activities continues to rise at the current rates, the average pH value of the oceans could fall by 0.5 units by the year 2100. This was equivalent to a three fold increase in the concentration of hydrogen ions. Global ocean acidification has become one of the most threatening disasters to the ocean ecosystem and has been attached great importance by the countries adjacent to oceans and the related international organizations in the world. In this paper the current situation and development of ocean acidification and the impacts of ocean acidification are described. It also summarizes the latest research achievements of ocean acidification and the ocean acidification studies in such countries as US, Europe, Japan, Australia, the Republic of Korea, and China, etc.
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Falkenberg, Laura J., Richard G. J. Bellerby, Sean D. Connell, Lora E. Fleming, Bruce Maycock, Bayden D. Russell, Francis J. Sullivan, and Sam Dupont. "Ocean Acidification and Human Health." International Journal of Environmental Research and Public Health 17, no. 12 (June 24, 2020): 4563. http://dx.doi.org/10.3390/ijerph17124563.

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The ocean provides resources key to human health and well-being, including food, oxygen, livelihoods, blue spaces, and medicines. The global threat to these resources posed by accelerating ocean acidification is becoming increasingly evident as the world’s oceans absorb carbon dioxide emissions. While ocean acidification was initially perceived as a threat only to the marine realm, here we argue that it is also an emerging human health issue. Specifically, we explore how ocean acidification affects the quantity and quality of resources key to human health and well-being in the context of: (1) malnutrition and poisoning, (2) respiratory issues, (3) mental health impacts, and (4) development of medical resources. We explore mitigation and adaptation management strategies that can be implemented to strengthen the capacity of acidifying oceans to continue providing human health benefits. Importantly, we emphasize that the cost of such actions will be dependent upon the socioeconomic context; specifically, costs will likely be greater for socioeconomically disadvantaged populations, exacerbating the current inequitable distribution of environmental and human health challenges. Given the scale of ocean acidification impacts on human health and well-being, recognizing and researching these complexities may allow the adaptation of management such that not only are the harms to human health reduced but the benefits enhanced.
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Boyd, Philip W. "Beyond ocean acidification." Nature Geoscience 4, no. 5 (April 29, 2011): 273–74. http://dx.doi.org/10.1038/ngeo1150.

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6

Contestabile, Monica. "Ocean acidification costs." Nature Climate Change 2, no. 3 (February 24, 2012): 146–47. http://dx.doi.org/10.1038/nclimate1439.

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7

Pope, Aaron, and Elizabeth Selna. "Communicating Ocean Acidification." Journal of Museum Education 38, no. 3 (October 2013): 279–85. http://dx.doi.org/10.1080/10598650.2013.11510780.

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8

Ridgwell, Andrew, and D. Schmidt. "Dangerous ocean acidification." IOP Conference Series: Earth and Environmental Science 6, no. 7 (February 1, 2009): 072005. http://dx.doi.org/10.1088/1755-1307/6/7/072005.

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9

Lan, Yilin. "The review of how ocean acidification affect organisms and ecological environment." Applied and Computational Engineering 58, no. 1 (April 30, 2024): 43–47. http://dx.doi.org/10.54254/2755-2721/58/20240689.

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The pH of our sea water is decreasing nowadays. Therefore, ocean acidification has gradually become a problem that people have to face. Human activities since Industrial Revolution are making sea water more and more acidic. Human activity has done some damage to the environment that will directly or indirectly increases the amount of hydrogen ions in seawater, which will finally make the seawater more acidic. One of the result of this changes is ocean acidification. People should start playing attention on this problem. If people do not intervene in advance to acidify the oceans, this issue can cause some consequences that will hurt our environment. The following is the main content of this paper. The reason why carbon dioxide can cause ocean acidification, effects of ocean acidification on Marine ecological environment, the shape of Balanophyllias bones changes in different PH environment and Changes in metabolic pathways of phytoplankton under ocean acidification.
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10

Ollier, Clifford. "The hoax of ocean acidification." Quaestiones Geographicae 38, no. 3 (September 10, 2019): 59–66. http://dx.doi.org/10.2478/quageo-2019-0029.

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Abstract A widespread alarm is sweeping the world at present about the ill effects of man-made increases in carbon dioxide (CO2) production. One aspect is that it may cause the ocean to become acid, and dissolve the carbonate skeletons of many living things including shellfish and corals. However, the oceans are not acid, never have been in geological history, and cannot become acid in the future. Changes in atmospheric CO2 cannot produce an acid ocean. Marine life depends on CO2, and some plants and animals fix it as limestone. Over geological time enormous amounts of CO2 have been sequestered by living things, and today there is far more CO2 in limestones than in the atmosphere or ocean. Carbon dioxide in seawater does not dissolve coral reefs, but is essential to their survival.
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11

Gattuso, Jean-Pierre. "Ocean Acidification - How will ongoing ocean acidification affect marine life? [Present]." PAGES news 20, no. 1 (February 2012): 36. http://dx.doi.org/10.22498/pages.20.1.36.

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Thomas, Ellen. "Ocean Acidification - How will ongoing ocean acidification affect marine life? [Past]." PAGES news 20, no. 1 (February 2012): 37. http://dx.doi.org/10.22498/pages.20.1.37.

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13

Hall-Spencer, Jason M., and Ben P. Harvey. "Ocean acidification impacts on coastal ecosystem services due to habitat degradation." Emerging Topics in Life Sciences 3, no. 2 (April 26, 2019): 197–206. http://dx.doi.org/10.1042/etls20180117.

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Abstract The oceanic uptake of anthropogenic carbon dioxide emissions is changing seawater chemistry in a process known as ocean acidification. The chemistry of this rapid change in surface waters is well understood and readily detectable in oceanic observations, yet there is uncertainty about the effects of ocean acidification on society since it is difficult to scale-up from laboratory and mesocosm tests. Here, we provide a synthesis of the likely effects of ocean acidification on ecosystem properties, functions and services based on observations along natural gradients in pCO2. Studies at CO2 seeps worldwide show that biogenic habitats are particularly sensitive to ocean acidification and that their degradation results in less coastal protection and less habitat provisioning for fisheries. The risks to marine goods and services amplify with increasing acidification causing shifts to macroalgal dominance, habitat degradation and a loss of biodiversity at seep sites in the tropics, the sub-tropics and on temperate coasts. Based on this empirical evidence, we expect ocean acidification to have serious consequences for the millions of people who are dependent on coastal protection, fisheries and aquaculture. If humanity is able to make cuts in fossil fuel emissions, this will reduce costs to society and avoid the changes in coastal ecosystems seen in areas with projected pCO2 levels. A binding international agreement for the oceans should build on the United Nations Sustainable Development Goal to ‘minimise and address the impacts of ocean acidification’.
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14

Doney, Scott. "BOOK REVIEW | Ocean Acidification." Oceanography 25, no. 1 (March 1, 2012): 301–3. http://dx.doi.org/10.5670/oceanog.2012.33.

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15

Stead, N. "COPING WITH OCEAN ACIDIFICATION." Journal of Experimental Biology 216, no. 8 (March 27, 2013): i—ii. http://dx.doi.org/10.1242/jeb.086728.

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16

Zielinski, Sarah. "Buoy monitors ocean acidification." Eos, Transactions American Geophysical Union 88, no. 26 (June 26, 2007): 270. http://dx.doi.org/10.1029/2007eo260002.

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17

Bellerby, Richard G. J. "Ocean acidification without borders." Nature Climate Change 7, no. 4 (February 27, 2017): 241–42. http://dx.doi.org/10.1038/nclimate3247.

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18

Kerr, R. A. "Ocean Acidification Unprecedented, Unsettling." Science 328, no. 5985 (June 17, 2010): 1500–1501. http://dx.doi.org/10.1126/science.328.5985.1500.

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19

Sun, Yuan. "Effects of Ocean Acidification on the Marine Organisms." Highlights in Science, Engineering and Technology 69 (November 6, 2023): 342–48. http://dx.doi.org/10.54097/hset.v69i.12130.

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Climate change is a severe environmental issue which can mainly be caused by anthropogenic activities like deforestation. It can cause another severe environmental issue called ocean acidification. It is worth seeking how ocean acidification occurs and how ocean acidification affects marine organisms including marine animals, marine plants and marine microorganisms. The increase of atmospheric carbon dioxide can be a dominant driver of ocean acidification. Ocean acidification can adversely influence marine animals like oysters. It can also either cause positive or negative impacts on marine plants. Marine microorganisms and marine biodiversity can also be sensitive to ocean acidification. Multiple strategies can be implemented to mitigate ocean acidification such as atmospheric carbon dioxide removal, growing of coastal seagrass, educational activities, and cultivation of marine submerged aquatic vegetation. However, the effectiveness and efficiency of mitigation strategies still need to be tracked in the long term. The quality of data collection for implementing the mitigation strategies is essential to determine and predict the response of the ocean towards to mitigation of ocean acidification.
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20

Sponberg, Adrienne Froelich. "Ocean Acidification: The Biggest Threat to Our Oceans?" BioScience 57, no. 10 (November 1, 2007): 822. http://dx.doi.org/10.1641/b571004.

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21

Beman, J. Michael, Cheryl-Emiliane Chow, Andrew L. King, Yuanyuan Feng, Jed A. Fuhrman, Andreas Andersson, Nicholas R. Bates, Brian N. Popp, and David A. Hutchins. "Global declines in oceanic nitrification rates as a consequence of ocean acidification." Proceedings of the National Academy of Sciences 108, no. 1 (December 20, 2010): 208–13. http://dx.doi.org/10.1073/pnas.1011053108.

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Ocean acidification produced by dissolution of anthropogenic carbon dioxide (CO2) emissions in seawater has profound consequences for marine ecology and biogeochemistry. The oceans have absorbed one-third of CO2emissions over the past two centuries, altering ocean chemistry, reducing seawater pH, and affecting marine animals and phytoplankton in multiple ways. Microbially mediated ocean biogeochemical processes will be pivotal in determining how the earth system responds to global environmental change; however, how they may be altered by ocean acidification is largely unknown. We show here that microbial nitrification rates decreased in every instance when pH was experimentally reduced (by 0.05–0.14) at multiple locations in the Atlantic and Pacific Oceans. Nitrification is a central process in the nitrogen cycle that produces both the greenhouse gas nitrous oxide and oxidized forms of nitrogen used by phytoplankton and other microorganisms in the sea; at the Bermuda Atlantic Time Series and Hawaii Ocean Time-series sites, experimental acidification decreased ammonia oxidation rates by 38% and 36%. Ammonia oxidation rates were also strongly and inversely correlated with pH along a gradient produced in the oligotrophic Sargasso Sea (r2= 0.87,P< 0.05). Across all experiments, rates declined by 8–38% in low pH treatments, and the greatest absolute decrease occurred where rates were highest off the California coast. Collectively our results suggest that ocean acidification could reduce nitrification rates by 3–44% within the next few decades, affecting oceanic nitrous oxide production, reducing supplies of oxidized nitrogen in the upper layers of the ocean, and fundamentally altering nitrogen cycling in the sea.
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22

Guo, Ziyi. "Biosensors for ocean acidification detection." Applied and Computational Engineering 32, no. 1 (January 22, 2024): 124–28. http://dx.doi.org/10.54254/2755-2721/32/20230196.

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Ocean acidification is a global environmental problem that significantly impacts Marine ecosystems and biodiversity. The traditional chemical analysis method has the problems of complex equipment and high cost in ocean acidification monitoring. In recent years, fluorescent protein biosensor technology, as an innovative monitoring method, has provided a new solution for the real-time detection of ocean acidification. Compared with traditional chemical analysis methods, fluorescent protein biosensors have the advantages of simple operation, high sensitivity and low cost. Current studies have demonstrated the potential of fluorescent protein biosensors for ocean acidification monitoring. The researchers designed a variety of fluorescent protein biosensors and conducted indoor and outdoor experimental validation. These results show that fluorescent protein biosensors can detect ocean acidification quickly and accurately and maintain stable performance under different environmental conditions. Further studies are needed to verify the consistency and reliability of fluorescent protein biosensors and traditional chemical analysis methods for ocean acidification monitoring. Future research directions include further improving the performance of the fluorescent protein biosensor, increasing its sensitivity and stability, and verifying its application in real Marine environments. This will help establish a better monitoring network for ocean acidification and provide a reliable scientific basis for Marine environmental protection and management decisions. The development and application of fluorescent protein biosensor technology will provide important support and guidance for us to better understand the impact of ocean acidification.
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23

Howard, William, D. Roberts, A. Moy, J. Roberts, T. Trull, S. Bray, and R. Hopcroft. "Ocean acidification impacts on southern ocean calcifiers." IOP Conference Series: Earth and Environmental Science 6, no. 46 (February 1, 2009): 462001. http://dx.doi.org/10.1088/1755-1307/6/46/462001.

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24

Cao, Long, and Ken Caldeira. "Can ocean iron fertilization mitigate ocean acidification?" Climatic Change 99, no. 1-2 (January 20, 2010): 303–11. http://dx.doi.org/10.1007/s10584-010-9799-4.

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25

Leung, Jonathan Y. S., Zoë A. Doubleday, Ivan Nagelkerken, Yujie Chen, Zonghan Xie, and Sean D. Connell. "How calorie-rich food could help marine calcifiers in a CO 2 -rich future." Proceedings of the Royal Society B: Biological Sciences 286, no. 1906 (July 10, 2019): 20190757. http://dx.doi.org/10.1098/rspb.2019.0757.

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Increasing carbon emissions not only enrich oceans with CO 2 but also make them more acidic. This acidifying process has caused considerable concern because laboratory studies show that ocean acidification impairs calcification (or shell building) and survival of calcifiers by the end of this century. Whether this impairment in shell building also occurs in natural communities remains largely unexplored, but requires re-examination because of the recent counterintuitive finding that populations of calcifiers can be boosted by CO 2 enrichment. Using natural CO 2 vents, we found that ocean acidification resulted in the production of thicker, more crystalline and more mechanically resilient shells of a herbivorous gastropod, which was associated with the consumption of energy-enriched food (i.e. algae). This discovery suggests that boosted energy transfer may not only compensate for the energetic burden of ocean acidification but also enable calcifiers to build energetically costly shells that are robust to acidified conditions. We unlock a possible mechanism underlying the persistence of calcifiers in acidifying oceans.
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Babila, Tali L., Donald E. Penman, Bärbel Hönisch, D. Clay Kelly, Timothy J. Bralower, Yair Rosenthal, and James C. Zachos. "Capturing the global signature of surface ocean acidification during the Palaeocene–Eocene Thermal Maximum." Philosophical Transactions of the Royal Society A: Mathematical, Physical and Engineering Sciences 376, no. 2130 (September 3, 2018): 20170072. http://dx.doi.org/10.1098/rsta.2017.0072.

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Geologically abrupt carbon perturbations such as the Palaeocene–Eocene Thermal Maximum (PETM, approx. 56 Ma) are the closest geological points of comparison to current anthropogenic carbon emissions. Associated with the rapid carbon release during this event are profound environmental changes in the oceans including warming, deoxygenation and acidification. To evaluate the global extent of surface ocean acidification during the PETM, we present a compilation of new and published surface ocean carbonate chemistry and pH reconstructions from various palaeoceanographic settings. We use boron to calcium ratios (B/Ca) and boron isotopes (δ 11 B) in surface- and thermocline-dwelling planktonic foraminifera to reconstruct ocean carbonate chemistry and pH. Our records exhibit a B/Ca reduction of 30–40% and a δ 11 B decline of 1.0–1.2‰ coeval with the carbon isotope excursion. The tight coupling between boron proxies and carbon isotope records is consistent with the interpretation that oceanic absorption of the carbon released at the onset of the PETM resulted in widespread surface ocean acidification. The remarkable similarity among records from different ocean regions suggests that the degree of ocean carbonate change was globally near uniform. We attribute the global extent of surface ocean acidification to elevated atmospheric carbon dioxide levels during the main phase of the PETM. This article is part of a discussion meeting issue ‘Hyperthermals: rapid and extreme global warming in our geological past’.
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Hartin, Corinne A., Benjamin Bond-Lamberty, Pralit Patel, and Anupriya Mundra. "Ocean acidification over the next three centuries using a simple global climate carbon-cycle model: projections and sensitivities." Biogeosciences 13, no. 15 (August 1, 2016): 4329–42. http://dx.doi.org/10.5194/bg-13-4329-2016.

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Abstract. Continued oceanic uptake of anthropogenic CO2 is projected to significantly alter the chemistry of the upper oceans over the next three centuries, with potentially serious consequences for marine ecosystems. Relatively few models have the capability to make projections of ocean acidification, limiting our ability to assess the impacts and probabilities of ocean changes. In this study we examine the ability of Hector v1.1, a reduced-form global model, to project changes in the upper ocean carbonate system over the next three centuries, and quantify the model's sensitivity to parametric inputs. Hector is run under prescribed emission pathways from the Representative Concentration Pathways (RCPs) and compared to both observations and a suite of Coupled Model Intercomparison (CMIP5) model outputs. Current observations confirm that ocean acidification is already taking place, and CMIP5 models project significant changes occurring to 2300. Hector is consistent with the observational record within both the high- (> 55°) and low-latitude oceans (< 55°). The model projects low-latitude surface ocean pH to decrease from preindustrial levels of 8.17 to 7.77 in 2100, and to 7.50 in 2300; aragonite saturation levels (ΩAr) decrease from 4.1 units to 2.2 in 2100 and 1.4 in 2300 under RCP 8.5. These magnitudes and trends of ocean acidification within Hector are largely consistent with the CMIP5 model outputs, although we identify some small biases within Hector's carbonate system. Of the parameters tested, changes in [H+] are most sensitive to parameters that directly affect atmospheric CO2 concentrations – Q10 (terrestrial respiration temperature response) as well as changes in ocean circulation, while changes in ΩAr saturation levels are sensitive to changes in ocean salinity and Q10. We conclude that Hector is a robust tool well suited for rapid ocean acidification projections and sensitivity analyses, and it is capable of emulating both current observations and large-scale climate models under multiple emission pathways.
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28

Kelley, Amanda L., Paul R. Hanson, and Stephanie A. Kelley. "Demonstrating the Effects of Ocean Acidification on Marine Organisms to Support Climate Change Understanding." American Biology Teacher 77, no. 4 (April 1, 2015): 258–63. http://dx.doi.org/10.1525/abt.2015.77.4.5.

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Ocean acidification, a product of CO2 absorption by the world’s oceans, is largely driven by the anthropogenic combustion of fossil fuels and has already lowered the pH of marine ecosystems. Organisms with calcium carbonate shells and skeletons are especially susceptible to increasing environmental acidity due to reduction in the saturation state of CaCO3 that accompanies ocean acidification. Creating a connection between human-mediated changes to our environment and the effect it will have on biota is crucial to establishing an understanding of the potential effects of global climate change. We outline two low-cost laboratory experiments that eloquently mimic the biochemical process of ocean acidification on two timescales, providing educators with hands-on, hypothesis-driven experiments that can easily be conducted in middle and high school biology or environmental science courses.
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29

Matear, Richard J., and Andrew Lenton. "Carbon–climate feedbacks accelerate ocean acidification." Biogeosciences 15, no. 6 (March 22, 2018): 1721–32. http://dx.doi.org/10.5194/bg-15-1721-2018.

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Abstract. Carbon–climate feedbacks have the potential to significantly impact the future climate by altering atmospheric CO2 concentrations (Zaehle et al., 2010). By modifying the future atmospheric CO2 concentrations, the carbon–climate feedbacks will also influence the future ocean acidification trajectory. Here, we use the CO2 emissions scenarios from four representative concentration pathways (RCPs) with an Earth system model to project the future trajectories of ocean acidification with the inclusion of carbon–climate feedbacks. We show that simulated carbon–climate feedbacks can significantly impact the onset of undersaturated aragonite conditions in the Southern and Arctic oceans, the suitable habitat for tropical coral and the deepwater saturation states. Under the high-emissions scenarios (RCP8.5 and RCP6), the carbon–climate feedbacks advance the onset of surface water under saturation and the decline in suitable coral reef habitat by a decade or more. The impacts of the carbon–climate feedbacks are most significant for the medium- (RCP4.5) and low-emissions (RCP2.6) scenarios. For the RCP4.5 scenario, by 2100 the carbon–climate feedbacks nearly double the area of surface water undersaturated with respect to aragonite and reduce by 50 % the surface water suitable for coral reefs. For the RCP2.6 scenario, by 2100 the carbon–climate feedbacks reduce the area suitable for coral reefs by 40 % and increase the area of undersaturated surface water by 20 %. The sensitivity of ocean acidification to the carbon–climate feedbacks in the low to medium emission scenarios is important because recent CO2 emission reduction commitments are trying to transition emissions to such a scenario. Our study highlights the need to better characterise the carbon–climate feedbacks and ensure we do not underestimate the projected ocean acidification.
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30

Dodd, Luke F., Jonathan H. Grabowski, Michael F. Piehler, Isaac Westfield, and Justin B. Ries. "Ocean acidification impairs crab foraging behaviour." Proceedings of the Royal Society B: Biological Sciences 282, no. 1810 (July 7, 2015): 20150333. http://dx.doi.org/10.1098/rspb.2015.0333.

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Anthropogenic elevation of atmospheric CO 2 is driving global-scale ocean acidification, which consequently influences calcification rates of many marine invertebrates and potentially alters their susceptibility to predation. Ocean acidification may also impair an organism's ability to process environmental and biological cues. These counteracting impacts make it challenging to predict how acidification will alter species interactions and community structure. To examine effects of acidification on consumptive and behavioural interactions between mud crabs ( Panopeus herbstii ) and oysters ( Crassostrea virginica ), oysters were reared with and without caged crabs for 71 days at three p CO 2 levels. During subsequent predation trials, acidification reduced prey consumption, handling time and duration of unsuccessful predation attempt. These negative effects of ocean acidification on crab foraging behaviour more than offset any benefit to crabs resulting from a reduction in the net rate of oyster calcification. These findings reveal that efforts to evaluate how acidification will alter marine food webs should include quantifying impacts on both calcification rates and animal behaviour.
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31

Danielson, Kathryn I., and Kimberly D. Tanner. "Investigating Undergraduate Science Students’ Conceptions and Misconceptions of Ocean Acidification." CBE—Life Sciences Education 14, no. 3 (September 2015): ar29. http://dx.doi.org/10.1187/cbe.14-11-0209.

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Scientific research exploring ocean acidification has grown significantly in past decades. However, little science education research has investigated the extent to which undergraduate science students understand this topic. Of all undergraduate students, one might predict science students to be best able to understand ocean acidification. What conceptions and misconceptions of ocean acidification do these students hold? How does their awareness and knowledge compare across disciplines? Undergraduate biology, chemistry/biochemistry, and environmental studies students, and science faculty for comparison, were assessed on their awareness and understanding. Results revealed low awareness and understanding of ocean acidification among students compared with faculty. Compared with biology or chemistry/biochemistry students, more environmental studies students demonstrated awareness of ocean acidification and identified the key role of carbon dioxide. Novel misconceptions were also identified. These findings raise the question of whether undergraduate science students are prepared to navigate socioenvironmental issues such as ocean acidification.
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32

Patterson, Joshua, Lisa Krimsky, and Joseph Henry. "Ocean Acidification: Fish Physiology and Behavior." EDIS 2020, no. 2 (March 20, 2020): 5. http://dx.doi.org/10.32473/edis-fa219-2020.

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Increased atmospheric carbon dioxide has led to increased levels of dissolved carbon dioxide in the oceans and acidified ocean water, which could have direct effects on the physiology and behavior of fishes. This 5-page fact sheet written by Joshua Patterson, Lisa Krimsky, and Joseph Henry and published by the UF/IFAS School of Forest Resources and Conservation, Program in Fisheries and Aquatic Sciences will summarize the current state of our understanding on the topic, with special emphasis on Florida fishes. It will also address current challenges in understanding the real-world effects of a complex global process using data largely collected on isolated fish in laboratory experiments. https://edis.ifas.ufl.edu/fa219
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33

Taylor-Burns, Rae, Courtney Cochran, Kelly Ferron, Madison Harris, Courtney Thomas, Alexa Fredston, and Bruce E. Kendall. "Locating gaps in the California Current System ocean acidification monitoring network." Science Progress 103, no. 3 (July 2020): 003685042093620. http://dx.doi.org/10.1177/0036850420936204.

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Ocean acidification is a global issue with particular regional significance in the California Current System, where social, economic, and ecological impacts are already occurring. Although ocean acidification is a concern that unifies the entire West Coast region, managing for this phenomenon at a regional scale is complex and further complicated by the large scale and dynamic nature of the region. Currently, data collection relevant to ocean acidification on the West Coast is piecemeal, and cannot capture the primary sources of variability in ocean acidification through time and across the region, hindering collaboration among regional managers. We developed a tool to analyze gaps in the West Coast ocean acidification monitoring network. We describe this tool and discuss how it can enable scientists and marine managers in the California Current System to fill information gaps and better understand and thus respond to ocean acidification through the implementation of management solutions at the local level.
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34

Bates, N. R., M. H. P. Best, K. Neely, R. Garley, A. G. Dickson, and R. J. Johnson. "Detecting anthropogenic carbon dioxide uptake and ocean acidification in the North Atlantic Ocean." Biogeosciences Discussions 9, no. 1 (January 23, 2012): 989–1019. http://dx.doi.org/10.5194/bgd-9-989-2012.

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Abstract. Fossil fuel use, cement manufacture and land-use changes are the primary sources of anthropogenic carbon dioxide (CO2) to the atmosphere, with the ocean absorbing 30 %. Ocean uptake and chemical equilibration of anthropogenic CO2with seawater results in a gradual reduction in seawater pH and saturation states (Ω) for calcium carbonate (CaCO3) minerals in a process termed ocean acidification. Assessing the present and future impact of ocean acidification on marine ecosystems requires detection of the multi-decadal rate of change across ocean basins and at ocean time-series sites. Here, we show the longest continuous record of ocean CO2 changes and ocean acidification in the North Atlantic subtropical gyre near Bermuda from 1983–2011. Dissolved inorganic carbon (DIC) and partial pressure of CO2 (pCO2) increased in surface seawater by ~40 μmol kg−1 and ~50 μatm (~20 %), respectively. Increasing Revelle factor (β) values imply that the capacity of North Atlantic surface waters to absorb CO2 has also diminished. As indicators of ocean acidification, seawater pH decreased by ~0.05 (0.0017 yr−1) and Ω values by ~7–8 %. Such data provide critically needed multi-decadal information for assessing the North Atlantic Ocean CO2sink and the pH changes that determine marine ecosystem responses to ocean acidification.
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Bates, N. R., M. H. P. Best, K. Neely, R. Garley, A. G. Dickson, and R. J. Johnson. "Detecting anthropogenic carbon dioxide uptake and ocean acidification in the North Atlantic Ocean." Biogeosciences 9, no. 7 (July 11, 2012): 2509–22. http://dx.doi.org/10.5194/bg-9-2509-2012.

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Abstract. Fossil fuel use, cement manufacture and land-use changes are the primary sources of anthropogenic carbon dioxide (CO2) to the atmosphere, with the ocean absorbing approximately 30% (Sabine et al., 2004). Ocean uptake and chemical equilibration of anthropogenic CO2 with seawater results in a gradual reduction in seawater pH and saturation states (Ω) for calcium carbonate (CaCO3) minerals in a process termed ocean acidification. Assessing the present and future impact of ocean acidification on marine ecosystems requires detection of the multi-decadal rate of change across ocean basins and at ocean time-series sites. Here, we show the longest continuous record of ocean CO2 changes and ocean acidification in the North Atlantic subtropical gyre near Bermuda from 1983–2011. Dissolved inorganic carbon (DIC) and partial pressure of CO2 (pCO2) increased in surface seawater by ~40 μmol kg−1 and ~50 μatm (~20%), respectively. Increasing Revelle factor (β) values imply that the capacity of North Atlantic surface waters to absorb CO2 has also diminished. As indicators of ocean acidification, seawater pH decreased by ~0.05 (0.0017 yr−1) and ω values by ~7–8%. Such data provide critically needed multi-decadal information for assessing the North Atlantic Ocean CO2 sink and the pH changes that determine marine ecosystem responses to ocean acidification.
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36

Cui, Zhehao, Siqi Huang, Jiarui Liu, and Junde Zhu. "Impact and Potential Solutions toward Ocean Acidification." E3S Web of Conferences 308 (2021): 02002. http://dx.doi.org/10.1051/e3sconf/202130802002.

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Ocean acidification is a new problem for humans that rose recently. It has been drawing attention from people. It is getting more serious and important with the continuous carbon emission to the atmosphere. The threatens from ocean acidification are affecting multiple characters, especially organisms like marine animals and marine plants. Researches show the change in the pH will affect the lifespan and the reproduction process of marine organisms. Besides the impact on organisms, ocean acidification is also likely to impact the global climate. For places located around the tropical area, ocean acidification will bring more frequent storms and hurricanes. Focused on the problem, we want to seek solutions. However, currently, there are no direct ways to address the problem of ocean acidification. Some hypotheses have been made, such as managing the seaweed and the precipitation method, but these approaches are immature and currently inapplicable. The most practical method to slow down ocean acidification is to make agreements and regulations to directly control carbon emission. Future agreements should increase the collaboration internationally and apply the most suitable measures locally. This research aims to provide background knowledge for future studies about the ocean.
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37

Stallinga, Peter. "Carbon Dioxide and Ocean Acidification." European Scientific Journal, ESJ 14, no. 18 (June 30, 2018): 476. http://dx.doi.org/10.19044/esj.2018.v14n18p476.

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One of the results of Anthropogenic Global Warming is the acidification of the oceans which threatens wildlife on this planet. In this work it will be shown what will be the effect of carbon dioxide injected into the atmosphere, doubling the total amount from 350 ppm to 700 ppm. Principally the effect on carbonate ions CO32-. It is based on textbook chemical principles worked out by numerically solving the resulting non-linear equations by the bisection method. The results are the following: In a pure-water environment the effect is that carbonate ion concentration remains unaltered (i.e., no harm to coral reefs). In a constant-pH environment the carbonate ion concentration grows linearly with CO2 in the atmosphere (i.e., good for coral reefs). When lowering the pH by other means than CO2, the carbonate ion concentration drops linearly (i.e., bad for coral reefs). In some specific cases can raising the CO2 in the atmosphere slightly reduce carbonate ions in the oceans.
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38

Dupont, Sam, Jean-Pierre Gattuso, Hans-Otto Pörtner, and Steve Widdicombe. "Ocean acidification science stands strong." Science 372, no. 6547 (June 10, 2021): 1160.2–1161. http://dx.doi.org/10.1126/science.abj4129.

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39

Wisshak, Max, Christine H. L. Schönberg, Armin Form, and André Freiwald. "Ocean Acidification Accelerates Reef Bioerosion." PLoS ONE 7, no. 9 (September 18, 2012): e45124. http://dx.doi.org/10.1371/journal.pone.0045124.

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40

Kump, Lee, Timothy Bralower, and Andy Ridgwell. "Ocean Acidification in Deep Time." Oceanography 22, no. 4 (December 1, 2009): 94–107. http://dx.doi.org/10.5670/oceanog.2009.100.

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41

Kleypas, Joan, and Kimberly Yates. "Coral Reefs and Ocean Acidification." Oceanography 22, no. 4 (December 1, 2009): 108–17. http://dx.doi.org/10.5670/oceanog.2009.101.

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42

Gledhill, Dwight, Rik Wanninkhof, and C. Mark Eakin. "Observing Ocean Acidification from Space." Oceanography 22, no. 4 (December 1, 2009): 48–59. http://dx.doi.org/10.5670/oceanog.2009.96.

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43

Doney, Scott C., Victoria J. Fabry, Richard A. Feely, and Joan A. Kleypas. "Ocean Acidification: The Other CO2Problem." Annual Review of Marine Science 1, no. 1 (January 2009): 169–92. http://dx.doi.org/10.1146/annurev.marine.010908.163834.

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44

Doney, Scott C. "The Dangers of Ocean Acidification." Scientific American 294, no. 3 (March 2006): 58–65. http://dx.doi.org/10.1038/scientificamerican0306-58.

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45

Benka, Stephen G. "Ocean acidification and coral reefs." Physics Today 65, no. 2 (February 2012): 20. http://dx.doi.org/10.1063/pt.3.1430.

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46

Stanley Jr.;, G. D., M. Fine, and D. Tchernov. "Ocean Acidification and Scleractinian Corals." Science 317, no. 5841 (August 24, 2007): 1032c—1033c. http://dx.doi.org/10.1126/science.317.5841.1032c.

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47

Stillman, J. H., and A. W. Paganini. "Biochemical adaptation to ocean acidification." Journal of Experimental Biology 218, no. 12 (June 1, 2015): 1946–55. http://dx.doi.org/10.1242/jeb.115584.

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48

Wyatt, T. D., J. D. Hardege, and J. Terschak. "Ocean acidification foils chemical signals." Science 346, no. 6206 (October 9, 2014): 176. http://dx.doi.org/10.1126/science.346.6206.176-a.

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49

Schmidt, Daniela N., and Andy Ridgwell. "Ocean acidification in the freezer." Antarctic Science 23, no. 5 (October 2011): 417. http://dx.doi.org/10.1017/s0954102011000691.

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Dery, Aurélie, Phuong Dat Tran, Philippe Compère, and Philippe Dubois. "Cidaroids spines facing ocean acidification." Marine Environmental Research 138 (July 2018): 9–18. http://dx.doi.org/10.1016/j.marenvres.2018.03.012.

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