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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/516969.rdf" xlink:actuate="onRequest">Coral physiology, algal density and type collected from the Reef Field Sites from the Puerto Morelos, Mexico &amp; Kaneohe Bay, Hawaii in 2009 (repeat coral bleaching project)</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Grottoli, A. G. (2015) Coral physiology, algal density and type collected from the Reef Field Sites from the Puerto Morelos, Mexico &amp; Kaneohe Bay, Hawaii in 2009 (repeat coral bleaching project). Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 2015-02-13) Version Date 2015-02-13 [if applicable, indicate subset used]. http://lod.bco-dmo.org/id/dataset/516969 [access date]</gco:CharacterString>
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        <gco:CharacterString>Coral metabolism, energy reserves, calcification, algal density and type Dataset Description: &amp;lt;p&amp;gt;Coral metabolism, energy reserves, calcification, algal density and type.&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;Full details of the experimental design are in:&amp;lt;br /&amp;gt;
Grottoli AG, Warner ME, Levas SJ, Aschaffenburg MD, Schopef B, McGinley M, Baumann J, Matsui Y. 2014. Cumulative impact of annual coral bleaching can turn some coral species winners into losers. &amp;lt;em&amp;gt;Global Change Biology&amp;lt;/em&amp;gt;.&amp;amp;nbsp; doi:&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1111/gcb.12658&amp;quot; target=&amp;quot;_blank&amp;quot;&amp;gt;10.1111/gcb.12658&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;A brief description of the analytical methods follows.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;&amp;lt;em&amp;gt;Calcification, endosymbiotic algae concentration, total energy reserves, and Symbiodinium identification&amp;lt;/em&amp;gt;&amp;lt;/strong&amp;gt;.&amp;amp;nbsp; Calcification rates were calculated from the buoyant weight data (Jokiel&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 1978) and standardized to surface area.&amp;amp;nbsp; Endosymbiont cell concentration (Warner&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006), and total soluble lipid, soluble animal protein, and soluble animal carbohydrates (Levas&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2013, Rodrigues &amp;amp;amp;&amp;amp;nbsp; Grottoli, 2007) were measured on all frozen fragments. Total energy reserves were calculated as the sum of total lipids, protein, and carbohydrates and reported in Joules (Gnaiger &amp;amp;amp;&amp;amp;nbsp; Bitterlich, 1984) per gram ash free dry weight of coral tissue. Since polyp structure and the coral tissue thickness of each species are different, this normalization facilitates inter-species comparisons (Edmunds &amp;amp;amp;&amp;amp;nbsp; Gates, 2002). Genetic characterizations of &amp;lt;em&amp;gt;Symbiodinium&amp;lt;/em&amp;gt; were determined by amplification of the internal-transcribed spacer 2 region (ITS2), followed by denaturing gradient gel electrophoresis and cycle-sequencing (Warner&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006). This method reliably identifies the dominant symbiont type in healthy and bleached corals (LaJeunesse&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2004, LaJeunesse&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2009, Warner&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006) and provides qualitative identification of other background &amp;lt;em&amp;gt;Symbiodinium&amp;lt;/em&amp;gt;, either within different clades (e.g., endosymbionts A3 vs B1) or at the intra-cladal scale (e.g., endosymbionts A3 and A13) within the same coral fragment.&amp;amp;nbsp; The dominant ITS2-types (intra-cladal designations) are listed for each coral species in the text, while for statistical analyses (described below), the dominant symbiont for each coral fragment treatment&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt; was grouped by clade. Specific quantitative PCR for all clades confirmed the accuracy of scoring dominant bands by DGGE analysis (data not shown, McGinley, 2012).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;&amp;lt;em&amp;gt;Photosynthesis, respiration, and feeding&amp;lt;/em&amp;gt;.&amp;lt;/strong&amp;gt;&amp;amp;nbsp; Maximal photosynthesis and respiration rates were measured via changes in dissolved oxygen on each individual coral fragment immediately following their respective thermal stress then standardized to ash free dry weight (Rodrigues &amp;amp;amp;&amp;amp;nbsp; Grottoli, 2007). All fragments were placed back on the reef and then feeding rates of each coral fragment were determined using methods in Palardy et al. (2008). Photosynthesis and respiration were used to calculate the percent Contribution of Zooxanthellae (&amp;lt;em&amp;gt;Symbiodinium &amp;lt;/em&amp;gt;spp.) to Animal Respiration (CZAR) (Muscatine&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 1981), while respiration and feeding rates were used to calculate the percent Contribution of Heterotrophy to Animal Respiration CHAR (Grottoli&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006, Palardy &amp;lt;em&amp;gt;et al.&amp;lt;/em&amp;gt;, 2008). The Contribution of the Total acquired fixed carbon relative to Animal Respiration (CTAR) was calculated as the sum of CZAR and CHAR.&amp;lt;/p&amp;gt;</gco:CharacterString>
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&lt;p&gt;The overall stability and health of coral reefs is declining world-wide at an unprecedented rate. Mass coral bleaching, wherein exposure to elevated temperature leads to the loss of significant numbers of endosymbiotic dinoflagellates (Symbiodinium spp., commonly called zooxanthellae) and/or photosynthetic pigments, serves as a primary global example of how fragile this symbiosis is. While we have begun to understand the ecological and physiological impacts of bleaching, there remain key fundamental gaps in knowledge. In particular, it is becoming increasingly clear that a) not all corals either respond to, or recover from, bleaching events the same way, and that b) the impact of annual or repeated bleaching events on corals has not been examined in sufficient detail. Several non-mutually exclusive ecological and physiological pathways could impact how a particular coral species succumbs to or recovers from bleaching. Recent evidence suggests that the following features may play key roles for coral survival in the face of future seawater warming and mass bleaching events: 1) shifts in trophic partitioning (e.g., proportional reliance on autotrophy and heterotrophy) and energy reserve utilization, 2) enhanced thermal tolerance through host and algal-mediated physiological responses, and 3) harboring of different Symbiodinium phylotypes. However, these mechanisms have yet to be investigated in a unified approach that covers the entire coral holobiont system (algae, host tissue, and skeleton), or under scenarios of repeated bleaching.&lt;/p&gt;
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	Name: lat
	Units: decimal degrees
	Description: &lt;p&gt;Latitude component of geographic position where experiments were conducted.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517271.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/517274.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/517285.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/517286.rdf
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	Description: &lt;p&gt;Status represents treatment conditions applied to coral samples during experiment, where 1=control and 2=treatment conditions.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517287.rdf
	Name: treatment_recovery_time
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	Description: &lt;p&gt;Number of years of applied treatment conditions and observation of recovery time on the reef, where:&lt;br /&gt;
0 = Year 1, 0 month on the reef&lt;br /&gt;
1.5 = Year 1, 6 weeks on the reef&lt;br /&gt;
13 = Year 2, 0 months on the reef&lt;br /&gt;
14.5 = Year 2, 6 weeks on the reef&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517288.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/517289.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/517330.rdf
	Name: CHAR
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	Description: &lt;p&gt;Contribution of Heterotrophy to Animal Respiration sensu Grottoli et al., (2006) and Palardy et al., (2008).&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517331.rdf
	Name: CTAR
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	Description: &lt;p&gt;Contribution of the Total acquired fixed carbon relative to Animal Respiration (CZAR + CHAR).&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517397.rdf
	Name: energy_rsrv_total
	Units: joules per gram dry weight
	Description: &lt;p&gt;The total coral soluble lipids + animal soluble protein + animal soluble carbohydrates.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517398.rdf
	Name: calcification
	Units: milligrams per cm^2 per day
	Description: &lt;p&gt;Calification rate.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517399.rdf
	Name: count_endosymbiont
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http://lod.bco-dmo.org/id/dataset-parameter/517400.rdf
	Name: symbiodinium_primary_type
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	Description: &lt;p&gt;Dominant endosymbiont type.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517401.rdf
	Name: symbiodinium_secondary_type
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	Description: &lt;p&gt;Secondary endosymbiont type.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/517402.rdf
	Name: symbiodinium_tertiary_type
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              <gmd:description>
                <gco:CharacterString>&amp;lt;p&amp;gt;Full details of the experimental design are in:&amp;lt;br /&amp;gt;
Grottoli AG, Warner ME, Levas SJ, Aschaffenburg MD, Schopef B, McGinley M, Baumann J, Matsui Y. 2014. Cumulative impact of annual coral bleaching can turn some coral species winners into losers. &amp;lt;em&amp;gt;Global Change Biology&amp;lt;/em&amp;gt;.&amp;amp;nbsp; doi:&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1111/gcb.12658&amp;quot; target=&amp;quot;_blank&amp;quot;&amp;gt;10.1111/gcb.12658&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;A brief description of the analytical methods follows.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;&amp;lt;em&amp;gt;Calcification, endosymbiotic algae concentration, total energy reserves, and Symbiodinium identification&amp;lt;/em&amp;gt;&amp;lt;/strong&amp;gt;.&amp;amp;nbsp; Calcification rates were calculated from the buoyant weight data (Jokiel&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 1978) and standardized to surface area.&amp;amp;nbsp; Endosymbiont cell concentration (Warner&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006), and total soluble lipid, soluble animal protein, and soluble animal carbohydrates (Levas&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2013, Rodrigues &amp;amp;amp;&amp;amp;nbsp; Grottoli, 2007) were measured on all frozen fragments. Total energy reserves were calculated as the sum of total lipids, protein, and carbohydrates and reported in Joules (Gnaiger &amp;amp;amp;&amp;amp;nbsp; Bitterlich, 1984) per gram ash free dry weight of coral tissue. Since polyp structure and the coral tissue thickness of each species are different, this normalization facilitates inter-species comparisons (Edmunds &amp;amp;amp;&amp;amp;nbsp; Gates, 2002). Genetic characterizations of &amp;lt;em&amp;gt;Symbiodinium&amp;lt;/em&amp;gt; were determined by amplification of the internal-transcribed spacer 2 region (ITS2), followed by denaturing gradient gel electrophoresis and cycle-sequencing (Warner&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006). This method reliably identifies the dominant symbiont type in healthy and bleached corals (LaJeunesse&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2004, LaJeunesse&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2009, Warner&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006) and provides qualitative identification of other background &amp;lt;em&amp;gt;Symbiodinium&amp;lt;/em&amp;gt;, either within different clades (e.g., endosymbionts A3 vs B1) or at the intra-cladal scale (e.g., endosymbionts A3 and A13) within the same coral fragment.&amp;amp;nbsp; The dominant ITS2-types (intra-cladal designations) are listed for each coral species in the text, while for statistical analyses (described below), the dominant symbiont for each coral fragment treatment&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt; was grouped by clade. Specific quantitative PCR for all clades confirmed the accuracy of scoring dominant bands by DGGE analysis (data not shown, McGinley, 2012).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;&amp;lt;em&amp;gt;Photosynthesis, respiration, and feeding&amp;lt;/em&amp;gt;.&amp;lt;/strong&amp;gt;&amp;amp;nbsp; Maximal photosynthesis and respiration rates were measured via changes in dissolved oxygen on each individual coral fragment immediately following their respective thermal stress then standardized to ash free dry weight (Rodrigues &amp;amp;amp;&amp;amp;nbsp; Grottoli, 2007). All fragments were placed back on the reef and then feeding rates of each coral fragment were determined using methods in Palardy et al. (2008). Photosynthesis and respiration were used to calculate the percent Contribution of Zooxanthellae (&amp;lt;em&amp;gt;Symbiodinium &amp;lt;/em&amp;gt;spp.) to Animal Respiration (CZAR) (Muscatine&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 1981), while respiration and feeding rates were used to calculate the percent Contribution of Heterotrophy to Animal Respiration CHAR (Grottoli&amp;lt;em&amp;gt; et al.&amp;lt;/em&amp;gt;, 2006, Palardy &amp;lt;em&amp;gt;et al.&amp;lt;/em&amp;gt;, 2008). The Contribution of the Total acquired fixed carbon relative to Animal Respiration (CTAR) was calculated as the sum of CZAR and CHAR.&amp;lt;/p&amp;gt;</gco:CharacterString>
              </gmd:description>
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                <gmd:LI_Source>
                  <gmd:sourceCitation>
                    <gmd:CI_Citation>
                      <gmd:title>
                        <gco:CharacterString>Specified by the Principal Investigator(s)</gco:CharacterString>
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                      <gmd:date gco:nilReason="unknown"/>
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            </gmd:LI_ProcessStep>
          </gmd:processStep>
          <gmd:processStep xlink:title="Data Processing Description">
            <gmd:LI_ProcessStep>
              <gmd:description>
                <gco:CharacterString>&amp;lt;p&amp;gt;Three statistical outliers were removed in order to meet assumptions of normality and homogeneity prior to ANOVA analyses.&amp;amp;nbsp; These data are flagged in the excel file and the removed value is included as a comment.&amp;amp;nbsp; Details of the statistical analysis methods are in Grottoli&amp;lt;em&amp;gt; et al.&amp;amp;nbsp;&amp;lt;/em&amp;gt;(in press).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;BCO-DMO Data Processing:&amp;lt;br /&amp;gt;
- Added BCO-DMO header info to include brf dscrptn, PI and version&amp;lt;br /&amp;gt;
- Edited parameter headers to comply with BCO-DMO convention:&amp;lt;/p&amp;gt;

&amp;lt;ul&amp;gt;
&amp;lt;li&amp;gt;Total EnRes&amp;amp;nbsp;--&amp;amp;gt;&amp;amp;nbsp;energy_rsrv_total&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;'number endosymbiont cells/cm2' --&amp;amp;gt; count_endosymbiont&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;1&amp;lt;sup&amp;gt;o&amp;lt;/sup&amp;gt; Symbiodinium type --&amp;amp;gt; symbiodinium_primary_type&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;2&amp;lt;sup&amp;gt;o&amp;lt;/sup&amp;gt; Symbiodinium type --&amp;amp;gt; symbiodinium_secondary_type&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;3&amp;lt;sup&amp;gt;o&amp;lt;/sup&amp;gt; Symbiodinium type --&amp;amp;gt; symbiodinium_tertiary_type&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;year&amp;amp;nbsp;--&amp;amp;gt;&amp;amp;nbsp;treatment_year&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;time --&amp;amp;gt; treatment_recovery_time&amp;lt;/li&amp;gt;
&amp;lt;/ul&amp;gt;

&amp;lt;p&amp;gt;- Species was decoded and genus species names were included in data, replacing&amp;amp;nbsp;codes of 1,2,3&amp;lt;br /&amp;gt;
- Replaced all &amp;quot;.&amp;quot; with &amp;quot;nd&amp;quot;&amp;lt;br /&amp;gt;
- Added lat/lon of the collection site of coral fragments (Puerto Morelos 20.8333, 86.8666)&amp;lt;br /&amp;gt;
- All precisions were edited to two decimals after consultation with PI.&amp;lt;br /&amp;gt;
- Corrected longitude values to negative degrees. (were positive); 13 Feb 2015.&amp;lt;/p&amp;gt;</gco:CharacterString>
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    <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/affiliation/191.rdf" xlink:actuate="onRequest">Biological and Chemical Oceanography Data Management Office (BCO-DMO)</gmx:Anchor>
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				    <gco:CharacterString>Woods Hole</gco:CharacterString>
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      <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/platform/517692.rdf" xlink:title="Reef Field Sites" xlink:actuate="onRequest">laboratory</gmx:Anchor>
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