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            <gco:CharacterString>Cite this dataset as: Williamson, O., Baker, A. (2024) Proportions of healthy, pale, bleached, and dead Orbicella faveolata recruits over time during a heat stress laboratory experiment conducted in 2018 and 2019, corresponding to proportions of different symbiont genera hosted. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2024-03-04 [if applicable, indicate subset used]. http://lod.bco-dmo.org/id/dataset/920837 [access date]</gco:CharacterString>
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        <gco:CharacterString>Methods and Sampling: &amp;lt;p&amp;gt;This section includes methodology for several related treatments and experiments conducted in the course of research&amp;amp;nbsp;presented in Williamson et al. (2021).&amp;amp;nbsp; &amp;amp;nbsp;Each BCO-DMO page provides access to one of these datasets, see the &amp;quot;Related Datasets&amp;quot; section for access to all related datasets.&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Parents of recruits used in this study were located on Horseshoe Reef in Key Largo, FL at 5 - 8 meters depth.&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
&amp;lt;strong&amp;gt;Symbiont uptake experiment&amp;lt;/strong&amp;gt;&amp;amp;nbsp;&amp;amp;nbsp;(see related dataset&amp;amp;nbsp;&amp;quot;Recruit survivorship and symbiont acquisition&amp;quot; https://www.bco-dmo.org/dataset/920853)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Throughout symbiont uptake period, a dissecting microscope was used to count the number of: (1) surviving recruits and (2) recruits visibly infected with symbionts. When infection was first observed in all aquaria (day 21) and again after 60&amp;amp;nbsp;days in their treatments, three to five recruits from each aquarium were sacrificed using a razor blade. To standardize sampling, only solitary polyps not clumped with others were sacrificed. Sacrificed recruits were placed in individual 1.5-mL microcentrifuge tubes with 200&amp;amp;nbsp;μL of 1% SDS + DNAB and incubated at 65&amp;amp;nbsp;°C for one hour. Genomic DNA was extracted from SDS archives following modified organic extraction methods (Rowan and Powers&amp;amp;nbsp;1991; Baker and Cunning&amp;amp;nbsp;2016).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Growth and symbiont density&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(see related dataset &amp;quot;Recruit area measurements&amp;quot; https://www.bco-dmo.org/dataset/920846)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Five months (150&amp;amp;nbsp;days) after settlement, a random sample of recruits from each of the four original treatments was photographed under a dissecting microscope with QCapture Suite Plus. Only solitary polyps were photographed to maximize accuracy of area measurements. ImageJ was used to calculate recruit skeletal area in mm2. A subset of the photographed recruits was then sacrificed to measure symbiont identity and density at the time of growth measurements.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Heat stress experiment&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(data included in this dataset)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;A subset of plugs with each symbiont type were placed into new aquaria, where temperature was increased from 22 to 28&amp;amp;nbsp;°C over six days, and then to 32&amp;amp;nbsp;°C over 48&amp;amp;nbsp;h. At this point, all recruits (n = 66) were infected with symbionts. About half the recruits (n = 32) were pre-exposed to mild heat stress (reared at 31&amp;amp;nbsp;°C during Experiment 1), while the other half (n = 34) were naïve to heat stress (reared at 29&amp;amp;nbsp;°C). Temperature was maintained at 32&amp;amp;nbsp;°C for ten days, then raised to 33&amp;amp;nbsp;°C for ten days, then raised to 34&amp;amp;nbsp;°C for 40&amp;amp;nbsp;days. Every two to five days, recruits were scored as “healthy,” “pale,” “bleached,” or “dead” using a fluorescence microscope. After 60&amp;amp;nbsp;days, all remaining living recruits were sacrificed for symbiont community analysis.&amp;amp;nbsp;&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
&amp;lt;strong&amp;gt;Recruit PCR (qPCR) data&amp;amp;nbsp;&amp;lt;/strong&amp;gt;&amp;amp;nbsp;(see &amp;quot;Recruit qPCR data&amp;quot; https://www.bco-dmo.org/dataset/920860)&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Quantitative PCR (qPCR) assays were used to identify Symbiodiniaceae to genus level and quantify symbiont-to-host (S:H) cell ratios for each recruit sampled. Since O. faveolata commonly hosts members of Symbiodinium, Breviolum, Cladocopium, and Durusdinium (Kemp et al. 2015), assays targeting specific actin loci for each genus were performed using a QuantStudio 3 Real-Time PCR Instrument (Applied Biosystems, USA). Assays for O. faveolata, Symbiodinium, and Breviolum followed reactions described in Cunning and Baker (2013), whereas Cladocopium and Durusdinium assays were multiplexed as described in Cunning et al. (2015).&amp;amp;nbsp;&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/817972.rdf" xlink:title="OCE-1851392" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1851392 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1851392</gmx:Anchor>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/817977.rdf" xlink:title="OCE-1851305" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1851305 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1851305</gmx:Anchor>
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Climate change represents an existential threat to coral reef ecosystems worldwide, with coral bleaching driven by continued ocean warming presenting the most pressing challenge to the persistence of these ecosystems over the next few decades. Given the severity and urgency of this threat it is critical to investigate mechanisms by which some corals might survive warming, assess the degree to which this is happening on reefs, and apply these discoveries to inform conservation interventions that might improve survival trajectories wherever possible. This project aims to fulfill these objectives by testing whether reef corals in the Caribbean are undergoing shifts in their algal symbionts in favor of more heat-tolerant types, what the consequences of these shifts might be for coral reef ecosystems, and the way in which we might use this information to help conserve them. Scientific objectives will be leveraged to improve the effectiveness of reef restoration efforts in the Caribbean by applying findings to ongoing intervention trials which aim to seed outplanted corals (both adult fragments raised in nurseries, and sexually derived coral recruits) with heat tolerant algae that are climate-resistant. It also takes advantage of emerging opportunities at two major public aquariums to highlight the plight of coral reefs to engaged public audiences primed to receive this message and learn about the role of science in both understanding and mitigating the problem. Finally, numerous high school, undergraduate, and graduate students will receive mentorship during this project, helping to train the next generation of marine scientists.&lt;/p&gt;
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                <gco:CharacterString>&amp;lt;p&amp;gt;This section includes methodology for several related treatments and experiments conducted in the course of research&amp;amp;nbsp;presented in Williamson et al. (2021).&amp;amp;nbsp; &amp;amp;nbsp;Each BCO-DMO page provides access to one of these datasets, see the &amp;quot;Related Datasets&amp;quot; section for access to all related datasets.&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Parents of recruits used in this study were located on Horseshoe Reef in Key Largo, FL at 5 - 8 meters depth.&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
&amp;lt;strong&amp;gt;Symbiont uptake experiment&amp;lt;/strong&amp;gt;&amp;amp;nbsp;&amp;amp;nbsp;(see related dataset&amp;amp;nbsp;&amp;quot;Recruit survivorship and symbiont acquisition&amp;quot; https://www.bco-dmo.org/dataset/920853)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Throughout symbiont uptake period, a dissecting microscope was used to count the number of: (1) surviving recruits and (2) recruits visibly infected with symbionts. When infection was first observed in all aquaria (day 21) and again after 60&amp;amp;nbsp;days in their treatments, three to five recruits from each aquarium were sacrificed using a razor blade. To standardize sampling, only solitary polyps not clumped with others were sacrificed. Sacrificed recruits were placed in individual 1.5-mL microcentrifuge tubes with 200&amp;amp;nbsp;μL of 1% SDS + DNAB and incubated at 65&amp;amp;nbsp;°C for one hour. Genomic DNA was extracted from SDS archives following modified organic extraction methods (Rowan and Powers&amp;amp;nbsp;1991; Baker and Cunning&amp;amp;nbsp;2016).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Growth and symbiont density&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(see related dataset &amp;quot;Recruit area measurements&amp;quot; https://www.bco-dmo.org/dataset/920846)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Five months (150&amp;amp;nbsp;days) after settlement, a random sample of recruits from each of the four original treatments was photographed under a dissecting microscope with QCapture Suite Plus. Only solitary polyps were photographed to maximize accuracy of area measurements. ImageJ was used to calculate recruit skeletal area in mm2. A subset of the photographed recruits was then sacrificed to measure symbiont identity and density at the time of growth measurements.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Heat stress experiment&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(data included in this dataset)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;A subset of plugs with each symbiont type were placed into new aquaria, where temperature was increased from 22 to 28&amp;amp;nbsp;°C over six days, and then to 32&amp;amp;nbsp;°C over 48&amp;amp;nbsp;h. At this point, all recruits (n = 66) were infected with symbionts. About half the recruits (n = 32) were pre-exposed to mild heat stress (reared at 31&amp;amp;nbsp;°C during Experiment 1), while the other half (n = 34) were naïve to heat stress (reared at 29&amp;amp;nbsp;°C). Temperature was maintained at 32&amp;amp;nbsp;°C for ten days, then raised to 33&amp;amp;nbsp;°C for ten days, then raised to 34&amp;amp;nbsp;°C for 40&amp;amp;nbsp;days. Every two to five days, recruits were scored as “healthy,” “pale,” “bleached,” or “dead” using a fluorescence microscope. After 60&amp;amp;nbsp;days, all remaining living recruits were sacrificed for symbiont community analysis.&amp;amp;nbsp;&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
&amp;lt;strong&amp;gt;Recruit PCR (qPCR) data&amp;amp;nbsp;&amp;lt;/strong&amp;gt;&amp;amp;nbsp;(see &amp;quot;Recruit qPCR data&amp;quot; https://www.bco-dmo.org/dataset/920860)&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Quantitative PCR (qPCR) assays were used to identify Symbiodiniaceae to genus level and quantify symbiont-to-host (S:H) cell ratios for each recruit sampled. Since O. faveolata commonly hosts members of Symbiodinium, Breviolum, Cladocopium, and Durusdinium (Kemp et al. 2015), assays targeting specific actin loci for each genus were performed using a QuantStudio 3 Real-Time PCR Instrument (Applied Biosystems, USA). Assays for O. faveolata, Symbiodinium, and Breviolum followed reactions described in Cunning and Baker (2013), whereas Cladocopium and Durusdinium assays were multiplexed as described in Cunning et al. (2015).&amp;amp;nbsp;&amp;lt;/p&amp;gt;</gco:CharacterString>
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                  <gco:CharacterString>* Submitted file &amp;quot;heat_stress_data.csv&amp;quot; was imported into the BCO-DMO data system for this dataset. &amp;quot;heat_bar_data.csv&amp;quot; was added as a supplemental file.
** Missing data values are displayed differently based on the file format you download.  They are blank in csv files, &amp;quot;NaN&amp;quot; in MatLab files, etc.

* Column names adjusted to conform to BCO-DMO naming conventions designed to support broad re-use by a variety of research tools and scripting languages. [Only numbers, letters, and underscores.  Can not start with a number]

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