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            <gco:CharacterString>Cite this dataset as: Tarling, G., Bakker, D., Fielding, S. (2014) Pteropod shell dissolution in natural and high-CO2 environments from samples collected on RRS James Clark Ross cruise JR177 in the Scotia Sea, Southern Ocean from 2007-2008. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2014-02-03 [if applicable, indicate subset used]. doi:10.1575/1912/bco-dmo.489471.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Pteropod shell dissolution in natural and high-CO2 environments. Dataset Description: &amp;lt;p&amp;gt;This dataset contains data from a study of pteropod shell dissolution on individuals exposed to CO2-enriched seawater. The data include the amount of dissolution as well as the physical and chemical parameters on which carbonate chemistry parameters were calculated.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;For more information on the experimental methods and results, see&amp;amp;nbsp;Bednarsek et al., 2012.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;This dataset has also been deposited to PANGAEA where additional carbonate system variables were calculated as described by Nisumaa et al., 2010.&amp;amp;nbsp;See: &amp;lt;a href=&amp;quot;http://doi.pangaea.de/10.1594/PANGAEA.779926&amp;quot; target=&amp;quot;_blank&amp;quot;&amp;gt;http://doi.pangaea.de/10.1594/PANGAEA.779926&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;&amp;lt;em&amp;gt;Sample collection:&amp;lt;/em&amp;gt;&amp;lt;br /&amp;gt;
Pteropods were collected from upper ocean water down to a maximum depth of 200 m from various locations across the Scotia Sea using a combination of vertically and obliquely towed Bongo nets and MOCNESS nets during the JR177 research cruise. Oblique tows were carried out at speeds of less than 1 knot.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;em&amp;gt;Experimental conditions:&amp;lt;/em&amp;gt;&amp;lt;br /&amp;gt;
A fraction of the captured specimens was preserved immediately in 70% ethanol to act as controls for comparison with those exposed to raised pCO2 conditions. A further fraction of specimens was incubated at various levels of pCO2 to test the effect on shell dissolution. Two liter bottles containing filtered sea water (0.7 um filters) were bubbled with air/CO2 mixtures of 500 ppm, 750 ppm, and 1200 ppm, until the required xCO2 was reached. An average of 30 live pteropod of &amp;lt;em&amp;gt;Limacina helicina ant. &amp;lt;/em&amp;gt;were incubated in each experimental container and maintained for 4, 8, and 14 days before extraction and immediate preservation in 70% ethanol. The majority of specimens were juvenile stages of &amp;lt;em&amp;gt;Limacina helicina ant&amp;lt;/em&amp;gt;., but the incubations were also carried out on adult stages of both &amp;lt;em&amp;gt;Limacina helicina ant&amp;lt;/em&amp;gt;. and &amp;lt;em&amp;gt;Clio pyramidata &amp;lt;/em&amp;gt;f&amp;lt;em&amp;gt;. ant. &amp;lt;/em&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Omega was assessed from measurements of DIC (dissolved inorganic carbon) and total alkalinity (TA) at the start and end of each incubation experiment. DIC and TA were measured using VINDTA instrument (Versatile INstrument for the Determination of Titration Alkalinity, Marianda, Kiel, Germany) following the Standard Operating Procedures for oceanic CO&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; measurements (Dickson et al. 2007) with a Certified Reference Material (CRM) analysed in duplicate at the beginning and end of each sample analysis day. Other carbonate chemistry parameters (total pH and Omega-aragonite) were calculated from all discrete samples using&amp;amp;nbsp; DIC, TA, temperature, salinity, pressure and macronutrient concentrations using the CO2SYS programme (Lewis and Wallace 1998) with thermodynamic dissociation constants for K1 and K2 by Mehrbach et al. (1973) refitted by Dickson &amp;amp;amp; Millero (1987).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;em&amp;gt;Shell dehydration:&amp;lt;/em&amp;gt;&amp;lt;br /&amp;gt;
Dehydration was undertaken using 2,2-Dimethoxypropane (DMP; chemical formula: (CH3)2C(OCH3)2), and 1,1,1,3,3,3-hexamethyldisilazane (HMDS; chemical formula: (CH3)3SiNHSi(CH3)3). Before starting dehydration with DMP, the shells were transferred to 50% methanol for two 5 min washes then transferred to 85% methanol (10 min). Complete tissue dehydration was accomplished by immersion in DMP: two changes at 15-20 min each. It was important not to let the shells air dry at this stage, so they were transferred to a 1:1 mixture of DMP and HMDS for about 10 min, followed by 100% HMDS for 20–25 min twice. The HMDS was subsequently allowed to evaporate allowing the shells to dry completely (Figure 2 of Bednarsek et al., 2012). The moderate vapor pressure and very low surface tension of HMDS allowed the shells to dry without distortion or loss of shell integrity.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;em&amp;gt;SEM:&amp;lt;/em&amp;gt;&amp;lt;br /&amp;gt;
Scanning Electron Microscopy (SEM) was done using a JEOL JSM 5900LV fitted with a tungsten filament at an acceleration voltage of 15 kV and a working distance of about 10 mm. Analysis of SEM photos enabled observation of the shell surface and identification of shell dissolution. Refer to Bednarsek et al. (2012) for more information on dissolution types.&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/489479.rdf" xlink:title="NE/H017267/1" xlink:actuate="onRequest">Funding provided by United Kingdom Natural Environmental Research Council (NERC) Award Number: NE/H017267/1 Award URL: http://gtr.rcuk.ac.uk/project/098910A1-90B5-48DD-8EDA-E546F7FD36EC</gmx:Anchor>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/489482.rdf" xlink:title="MEST-CT-2004-514159" xlink:actuate="onRequest">Funding provided by European Commission Marie Curie Actions Program (EC - Marie Curie Actions) Award Number: MEST-CT-2004-514159</gmx:Anchor>
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                            <gco:CharacterString>NSF Climate Research Investment (CRI) activities that were initiated in 2010 are now included under Science, Engineering and Education for Sustainability NSF-Wide Investment (SEES). SEES is a portfolio of activities that highlights NSF's unique role in helping society address the challenge(s) of achieving sustainability. Detailed information about the SEES program is available from NSF (https://www.nsf.gov/funding/pgm_summ.jsp?pims_id=504707).
In recognition of the need for basic research concerning the nature, extent and impact of ocean acidification on oceanic environments in the past, present and future, the goal of the SEES: OA program is to understand (a) the chemistry and physical chemistry of ocean acidification; (b) how ocean acidification interacts with processes at the organismal level; and (c) how the earth system history informs our understanding of the effects of ocean acidification on the present day and future ocean.
Solicitations issued under this program:
NSF 10-530, FY 2010-FY2011
NSF 12-500, FY 2012
NSF 12-600, FY 2013
NSF 13-586, FY 2014
NSF 13-586 was the final solicitation that will be released for this program.
PI Meetings:
1st U.S. Ocean Acidification PI Meeting(March 22-24, 2011, Woods Hole, MA)
2nd U.S. Ocean Acidification PI Meeting(Sept. 18-20, 2013, Washington, DC)
3rd U.S. Ocean Acidification PI Meeting (June 9-11, 2015, Woods Hole, MA – Tentative)
NSF media releases for the Ocean Acidification Program:
Press Release 10-186 NSF Awards Grants to Study Effects of Ocean Acidification
Discovery Blue Mussels &quot;Hang On&quot; Along Rocky Shores: For How Long?
Discovery nsf.gov - National Science Foundation (NSF) Discoveries - Trouble in Paradise: Ocean Acidification This Way Comes - US National Science Foundation (NSF)
Press Release 12-179 nsf.gov - National Science Foundation (NSF) News - Ocean Acidification: Finding New Answers Through National Science Foundation Research Grants - US National Science Foundation (NSF)
Press Release 13-102 World Oceans Month Brings Mixed News for Oysters
Press Release 13-108 nsf.gov - National Science Foundation (NSF) News - Natural Underwater Springs Show How Coral Reefs Respond to Ocean Acidification - US National Science Foundation (NSF)
Press Release 13-148 Ocean acidification: Making new discoveries through National Science Foundation research grants
Press Release 13-148 - Video nsf.gov - News - Video - NSF Ocean Sciences Division Director David Conover answers questions about ocean acidification. - US National Science Foundation (NSF)
Press Release 14-010 nsf.gov - National Science Foundation (NSF) News - Palau's coral reefs surprisingly resistant to ocean acidification - US National Science Foundation (NSF)
Press Release 14-116 nsf.gov - National Science Foundation (NSF) News - Ocean Acidification: NSF awards $11.4 million in new grants to study effects on marine ecosystems - US National Science Foundation (NSF)</gco:CharacterString>
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                            <gco:CharacterString>The Ocean Carbon and Biogeochemistry (OCB) program focuses on the ocean's role as a component of the global Earth system, bringing together research in geochemistry, ocean physics, and ecology that inform on and advance our understanding of ocean biogeochemistry. The overall program goals are to promote, plan, and coordinate collaborative, multidisciplinary research opportunities within the U.S. research community and with international partners. Important OCB-related activities currently include: the Ocean Carbon and Climate Change (OCCC) and the North American Carbon Program (NACP); U.S. contributions to IMBER, SOLAS, CARBOOCEAN; and numerous U.S. single-investigator and medium-size research projects funded by U.S. federal agencies including NASA, NOAA, and NSF.
The scientific mission of OCB is to study the evolving role of the ocean in the global carbon cycle, in the face of environmental variability and change through studies of marine biogeochemical cycles and associated ecosystems.
The overarching OCB science themes include improved understanding and prediction of: 1) oceanic uptake and release of atmospheric CO2 and other greenhouse gases and 2) environmental sensitivities of biogeochemical cycles, marine ecosystems, and interactions between the two.
The OCB Research Priorities (updated January 2012) include: ocean acidification; terrestrial/coastal carbon fluxes and exchanges; climate sensitivities of and change in ecosystem structure and associated impacts on biogeochemical cycles; mesopelagic ecological and biogeochemical interactions; benthic-pelagic feedbacks on biogeochemical cycles; ocean carbon uptake and storage; and expanding low-oxygen conditions in the coastal and open oceans.</gco:CharacterString>
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                  <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/project/2183.rdf" xlink:title="Project" xlink:actuate="onRequest">An Investigation of the Role of Nutrition in the Coral Calcification Response to Ocean Acidification</gmx:Anchor>
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                            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/project/2183.rdf" xlink:title="Project Name" xlink:actuate="onRequest">An Investigation of the Role of Nutrition in the Coral Calcification Response to Ocean Acidification</gmx:Anchor>
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                            <gco:CharacterString>&lt;p&gt;&lt;i&gt;The project description is a modification of the original NSF award abstract.&lt;/i&gt;&lt;/p&gt;
&lt;p&gt;This research project is part of the larger NSF funded CRI-OA collaborative research initiative and was funded as an Ocean Acidification-Category 1, 2010 award. Over the course of this century, all tropical coral reef ecosystems, whether fringing heavily populated coastlines or lining remote islands and atolls, face unprecedented threat from ocean acidification caused by rising levels of atmospheric CO2. In many laboratory experiments conducted to date, calcium carbonate production (calcification) by scleractinian (stony) corals showed an inverse correlation to seawater saturation state OMEGAar), whether OMEGAar was manipulated by acid or CO2 addition. Based on these data, it is predicted that coral calcification rates could decline by up to 80% of modern values by the end of this century. A growing body of new experimental data however, suggests that the coral calcification response to ocean acidification may be less straightforward and a lot more variable than previously recognized. In at least 10 recent experiments including our own, 8 different tropical and temperate species reared under nutritionally-replete but significantly elevated CO2 conditions (780-1200 ppm, OMEAGar ~1.5-2), continued to calcify at rates comparable to conspecifics reared under ambient CO2. These experimental results are consistent with initial field data collected on reefs in the eastern Pacific and southern Oman, where corals today live and accrete their skeletons under conditions equivalent to 2X and 3X pre-industrial CO2. On these high CO2, high nutrient reefs (where nitrate concentrations typically exceed 2.5 micro-molar), coral growth rates rival, and sometimes even exceed, those of conspecifics in low CO2, oligotrophic reef environments.&lt;/p&gt;
&lt;p&gt;The investigators propose that a coral's energetic status, tightly coupled to the availability of inorganic nutrients and/or food, is a key factor in the calcification response to CO2-induced ocean acidification. Their hypothesis, if confirmed by the proposed laboratory investigations, implies that predicted changes in coastal and open ocean nutrient concentrations over the course of this century, driven by both climate impacts on ocean stratification and by increased human activity in coastal regions, could play a critical role in exacerbating and in some areas, modulating the coral reef response to ocean acidification. This research program builds on the investigators initial results and observations. The planned laboratory experiments will test the hypothesis that: (1) The coral calcification response to ocean acidification is linked to the energetic status of the coral host. The relative contribution of symbiont photosynthesis and heterotrophic feeding to a coral's energetic status varies amongst species. Enhancing the energetic status of corals reared under high CO2, either by stimulating photosynthesis with inorganic nutrients or by direct heterotrophic feeding of the host lowers the sensitivity of calcification to decreased seawater OMEGAar; (2) A species-specific threshold CO2 level exists over which enhanced energetic status can no longer compensate for decreased OMEGAar of the external seawater. Similarly, we will test the hypothesis that a nutrient threshold exists over which nutrients become detrimental for calcification even under high CO2 conditions; and (3) Temperature-induced reduction of algal symbionts is one stressor that can reduce the energetic reserve of the coral host and exacerbate the calcification response to ocean acidification.&lt;/p&gt;
&lt;p&gt;The investigator's initial findings highlight the critical importance of energetic status in the coral calcification response to ocean acidification. Verification of these findings in the laboratory, and identification of nutrient and CO2 thresholds for a range of species will have immediate, direct impact on predictions of reef resilience in a high CO2 world. The research project brings together a diverse group of expertise in coral biogeochemistry, chemical oceanography, molecular biology and coral reproductive ecology to focus on a problem that has enormous societal, economic and conservation relevance.&lt;/p&gt;</gco:CharacterString>
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        <gco:CharacterString>eng; USA</gco:CharacterString>
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            <gco:CharacterString>BCO-DMO catalogue of parameters from Pteropod shell dissolution in natural and high-CO2 environments from samples collected on RRS James Clark Ross cruise JR177 in the Scotia Sea, Southern Ocean from 2007-2008</gco:CharacterString>
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            http://lod.bco-dmo.org/id/dataset-parameter/489499.rdf
	Name: treatment
	Units: dimensionless
	Description: &lt;p&gt;Type of experimental treatment.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489500.rdf
	Name: incubation_time
	Units: days
	Description: &lt;p&gt;Number of days incubated.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489501.rdf
	Name: N
	Units: dimensionless
	Description: &lt;p&gt;Number of samples in the treatment.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489502.rdf
	Name: species
	Units: dimensionless
	Description: &lt;p&gt;Name of the species of study.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489503.rdf
	Name: sal
	Units: dimensionless
	Description: &lt;p&gt;Salinity.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489504.rdf
	Name: temp
	Units: degrees Celsius
	Description: &lt;p&gt;Water temperature.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489505.rdf
	Name: phosphate
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Phosphate concentration.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489506.rdf
	Name: silicate
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Silicate concentration.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489507.rdf
	Name: alk_tot
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Total alkalinity.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489508.rdf
	Name: alk_tot_stdev
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Standard deviation of alk_tot.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489509.rdf
	Name: DIC
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Total dissolved inorganic carbon.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489510.rdf
	Name: DIC_stdev
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Standard deviation of C_tot.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489511.rdf
	Name: pH
	Units: dimensionless
	Description: &lt;p&gt;pH of the water.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489512.rdf
	Name: pH_stdev
	Units: dimensionless
	Description: &lt;p&gt;Standard deviation of pH.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489513.rdf
	Name: pCO2
	Units: microatmospheres (uatm)
	Description: &lt;p&gt;Partial pressure of carbon dioxide at sea surface temperature.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489514.rdf
	Name: pCO2_stdev
	Units: microatmospheres (uatm)
	Description: &lt;p&gt;Standard deviation of pCO2.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489515.rdf
	Name: bicarbonate
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Concentration of bicarbonate ion [HCO3]-.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489516.rdf
	Name: bicarbonate_stdev
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Standard deviation of bicarbonate concentration.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489517.rdf
	Name: carbonate
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Concentration of carbonate ion [CO3]2-.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489518.rdf
	Name: carbonate_stdev
	Units: micromoles per kilogram (umol/kg)
	Description: &lt;p&gt;Standard deviation of carbonate concentration.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489519.rdf
	Name: omega_Arg
	Units: dimensionless
	Description: &lt;p&gt;Aragonite saturation state.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489520.rdf
	Name: omega_Arg_stdev
	Units: dimensionless
	Description: &lt;p&gt;Standard deviation of omega_Arg.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489521.rdf
	Name: non_diss
	Units: percentage (%)
	Description: &lt;p&gt;Percentage of non-dissolving individuals as determined by SEM.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489522.rdf
	Name: non_diss_stdev
	Units: percentage (%)
	Description: &lt;p&gt;Standard deviation of non_diss.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489523.rdf
	Name: diss_rate1
	Units: percentage (%)
	Description: &lt;p&gt;Type I dissolution rate as determined by SEM. Bednarsek et al. (2012) describe Type I dissolution as &quot;First indices of slightly increased porosity. Aragonite crystals within the upper-prismatic layer affected by dissolution - ‘cauliflower heads’ present.&quot;&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489524.rdf
	Name: diss_rate1_stdev
	Units: percentage (%)
	Description: &lt;p&gt;Standard deviation of diss_rate1.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489525.rdf
	Name: diss_rate2
	Units: percentage (%)
	Description: &lt;p&gt;Type II dissolution rate as determined by SEM. Bednarsek et al. (2012) describe Type II dissolution as &quot;Increased porosity. Dissolved patches more extensive and numerous. Prismatic layer partially or completely dissolved, crossed-lamellar layer exposed.&quot;&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489526.rdf
	Name: diss_rate2_stdev
	Units: percentage (%)
	Description: &lt;p&gt;Standard deviation of diss_rate2.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/489527.rdf
	Name: diss_rate3
	Units: percentage (%)
	Description: &lt;p&gt;Type III dissolution rate as determined by SEM. Bednarsek et al. (2012) describe Type III dissolution as &quot;Less compact crystal structure with compromised shell integrity and extreme frailness. Dissolution within crossed-lamellar layer with crystals thicker and chunkier.&quot;&lt;/p&gt; 
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&amp;lt;p&amp;gt;&amp;lt;em&amp;gt;Experimental conditions:&amp;lt;/em&amp;gt;&amp;lt;br /&amp;gt;
A fraction of the captured specimens was preserved immediately in 70% ethanol to act as controls for comparison with those exposed to raised pCO2 conditions. A further fraction of specimens was incubated at various levels of pCO2 to test the effect on shell dissolution. Two liter bottles containing filtered sea water (0.7 um filters) were bubbled with air/CO2 mixtures of 500 ppm, 750 ppm, and 1200 ppm, until the required xCO2 was reached. An average of 30 live pteropod of &amp;lt;em&amp;gt;Limacina helicina ant. &amp;lt;/em&amp;gt;were incubated in each experimental container and maintained for 4, 8, and 14 days before extraction and immediate preservation in 70% ethanol. The majority of specimens were juvenile stages of &amp;lt;em&amp;gt;Limacina helicina ant&amp;lt;/em&amp;gt;., but the incubations were also carried out on adult stages of both &amp;lt;em&amp;gt;Limacina helicina ant&amp;lt;/em&amp;gt;. and &amp;lt;em&amp;gt;Clio pyramidata &amp;lt;/em&amp;gt;f&amp;lt;em&amp;gt;. ant. &amp;lt;/em&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Omega was assessed from measurements of DIC (dissolved inorganic carbon) and total alkalinity (TA) at the start and end of each incubation experiment. DIC and TA were measured using VINDTA instrument (Versatile INstrument for the Determination of Titration Alkalinity, Marianda, Kiel, Germany) following the Standard Operating Procedures for oceanic CO&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; measurements (Dickson et al. 2007) with a Certified Reference Material (CRM) analysed in duplicate at the beginning and end of each sample analysis day. Other carbonate chemistry parameters (total pH and Omega-aragonite) were calculated from all discrete samples using&amp;amp;nbsp; DIC, TA, temperature, salinity, pressure and macronutrient concentrations using the CO2SYS programme (Lewis and Wallace 1998) with thermodynamic dissociation constants for K1 and K2 by Mehrbach et al. (1973) refitted by Dickson &amp;amp;amp; Millero (1987).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;em&amp;gt;Shell dehydration:&amp;lt;/em&amp;gt;&amp;lt;br /&amp;gt;
Dehydration was undertaken using 2,2-Dimethoxypropane (DMP; chemical formula: (CH3)2C(OCH3)2), and 1,1,1,3,3,3-hexamethyldisilazane (HMDS; chemical formula: (CH3)3SiNHSi(CH3)3). Before starting dehydration with DMP, the shells were transferred to 50% methanol for two 5 min washes then transferred to 85% methanol (10 min). Complete tissue dehydration was accomplished by immersion in DMP: two changes at 15-20 min each. It was important not to let the shells air dry at this stage, so they were transferred to a 1:1 mixture of DMP and HMDS for about 10 min, followed by 100% HMDS for 20–25 min twice. The HMDS was subsequently allowed to evaporate allowing the shells to dry completely (Figure 2 of Bednarsek et al., 2012). The moderate vapor pressure and very low surface tension of HMDS allowed the shells to dry without distortion or loss of shell integrity.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;em&amp;gt;SEM:&amp;lt;/em&amp;gt;&amp;lt;br /&amp;gt;
Scanning Electron Microscopy (SEM) was done using a JEOL JSM 5900LV fitted with a tungsten filament at an acceleration voltage of 15 kV and a working distance of about 10 mm. Analysis of SEM photos enabled observation of the shell surface and identification of shell dissolution. Refer to Bednarsek et al. (2012) for more information on dissolution types.&amp;lt;/p&amp;gt;</gco:CharacterString>
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