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            <gco:CharacterString>Cite this dataset as: Clements, C. (2024) Coral tissue mortality as a function of the presence or absence of sea cucumbers and coral outplant type in cage experiments in lagoonal habitat of Mo’orea, French Polynesia in April and May of 2020. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2024-02-12 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.920209.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Methods and Sampling: &amp;lt;div id=&amp;quot;form_methodology&amp;quot;&amp;gt;
&amp;lt;p&amp;gt;In Mo’orea, to assess the impact of sea cucumber removal on sediment- and coral-associated microbiomes, as well as how farmerfish turf on the base of corals might affect disease prevalence, we erected thirty-six 50 cm x 50 cm x 12 cm tall cages using 1 cm&amp;lt;sup&amp;gt;2&amp;lt;/sup&amp;gt;&amp;amp;nbsp;grid metal screening to contain or exclude sea cucumbers and prevent access by coral consumers. Cages were situated in an ~85 m&amp;lt;sup&amp;gt;2&amp;amp;nbsp;&amp;lt;/sup&amp;gt;sand patch within the fringing reef area utilized in our initial experiment described above and were separated from adjacent cages by ≥60 cm, creating a 6 x 6 grid of enclosures. Each cage was stocked with either zero, one, or two&amp;amp;nbsp;&amp;lt;em&amp;gt;H. atra&amp;amp;nbsp;&amp;lt;/em&amp;gt;(12 cages treatment&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;) that were approximately 9-14 cm in length, as is typical for individuals at our site. Density treatments were assigned at random. Cages were inspected daily to ensure that density treatments were maintained (they were), and sea cucumbers outside of cages were removed daily from within about 10 m of the 2 m deep area where cages were situated. All cages were brushed every other day to prevent fouling.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Seven days after applying sea cucumber treatments, sediment samples were taken for microbiome analyses by scraping 30-40 mL of surficial sediment from the top ~5 mm of each caged area into a small Whirl-Pak. Samples were immediately placed on ice and stored in a -80°C freezer upon return to shore. Following sediment sampling, three&amp;amp;nbsp;&amp;lt;em&amp;gt;A. pulchra&amp;lt;/em&amp;gt;&amp;amp;nbsp;outplants were embedded into the sediment of each cage&amp;amp;nbsp;(108 outplants total) to test the potential effects of (i) sea cucumber density, and (ii) protective effects of farmerfish-cultivated turf algae on coral health and microbiomes (see below). Corals used were approximately 8-10 cm in length and were initially fragmented from numerous&amp;amp;nbsp;&amp;lt;em&amp;gt;A. pulchra&amp;lt;/em&amp;gt;&amp;amp;nbsp;thickets adjacent to our study area and outplanted using the methods described above.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Of the three outplants included in each cage, two were fragmented from colonies in the field in such a way as to include farmerfish-generated turf algae at their base, while the third was fragmented so that it lacked turf at its base. These three outplants were embedded into the sediment as follows: (i) coral lacking turf planted in direct contact with benthic sediment (hereafter “no turf”), (ii) coral separated from direct contact with sediment by turf algae growing at its base (hereafter “turf”), or (iii) coral with turf on its base, but embedded more deeply into the sediment so that the living coral tissue was in direct contact with the sediment (hereafter “embedded turf”). Percent coral tissue mortality among outplants was visually estimated daily for 36 days. The microbiomes of all corals and the sediment within a cage were sampled when one or more outplants within that cage exhibited ≥50% tissue mortality or when the experiment was terminated on day 36.&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Organism identifiers:&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Coral: Acropora pulchra, LSID (urn:lsid:marinespecies.org:taxname:207015)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Cucumber: Holothuria atra, LSID (urn:lsid:marinespecies.org:taxname:1672768)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;farmerfish: Stegastes spp, LSID (urn:lsid:marinespecies.org:taxname:203822)&amp;lt;/p&amp;gt;
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/837801.rdf" xlink:title="OCE-1947522" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1947522 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1947522</gmx:Anchor>
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&lt;p&gt;Ecologists have excelled at demonstrating the importance of direct (often negative) interactions among species pairs. However, when these interactions occur in a complex context among thousands of other species in the field, the sum of the many, poorly-known, indirect interactions can counterbalance, or even reverse, the better-known direct interactions, generating diffuse mutualisms instead of agonistic outcomes. In a proof-of-concept initial experiment, coral growth and survivorship were greater in coral polycultures than monocultures, especially during early stages of community development. Processes generating this outcome are unclear but understanding these is of critical importance as diversity and function of reefs decline and as humans need to predict and adapt to changing environments. This interdisciplinary investigation merges expertise in experimental field ecology, chemical ecology, and the ecology of microbiomes to investigate the functional role of biodiversity in coral reef ecosystems. Experiments use a novel coral transplantation method and field manipulations to assess: 1) whether greater coral species diversity enhances coral community performance, as well as growth and survivorship of individual corals, 2) whether greater genotypic diversity enhances coral performance within a species, 3) whether greater diversity of seaweed competitors further suppresses corals and enhances seaweed performance, and 4) the processes driving the patterns documented above, including the roles of disease, intraspecific versus interspecific competition, predators, mutualists, and differential access to, or use of, resources. The research investigates the relationship between biodiversity and ecosystem function across dimensions of coral taxonomic diversity, from species to genotypes, and creates a series of experiments elucidating general principles underlying ecosystem dynamics. Filling these knowledge gaps advances our fundamental understanding of how biodiversity influences ecosystem function at multiple scales and provides insight into the processes promoting coral coexistence in these species-rich ecosystems. Findings will have practical implications for coral management and restoration and may improve predictions regarding coral reef resilience and recovery in the face of changing climate.&lt;/p&gt;</gco:CharacterString>
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&amp;lt;p&amp;gt;In Mo’orea, to assess the impact of sea cucumber removal on sediment- and coral-associated microbiomes, as well as how farmerfish turf on the base of corals might affect disease prevalence, we erected thirty-six 50 cm x 50 cm x 12 cm tall cages using 1 cm&amp;lt;sup&amp;gt;2&amp;lt;/sup&amp;gt;&amp;amp;nbsp;grid metal screening to contain or exclude sea cucumbers and prevent access by coral consumers. Cages were situated in an ~85 m&amp;lt;sup&amp;gt;2&amp;amp;nbsp;&amp;lt;/sup&amp;gt;sand patch within the fringing reef area utilized in our initial experiment described above and were separated from adjacent cages by ≥60 cm, creating a 6 x 6 grid of enclosures. Each cage was stocked with either zero, one, or two&amp;amp;nbsp;&amp;lt;em&amp;gt;H. atra&amp;amp;nbsp;&amp;lt;/em&amp;gt;(12 cages treatment&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;) that were approximately 9-14 cm in length, as is typical for individuals at our site. Density treatments were assigned at random. Cages were inspected daily to ensure that density treatments were maintained (they were), and sea cucumbers outside of cages were removed daily from within about 10 m of the 2 m deep area where cages were situated. All cages were brushed every other day to prevent fouling.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Seven days after applying sea cucumber treatments, sediment samples were taken for microbiome analyses by scraping 30-40 mL of surficial sediment from the top ~5 mm of each caged area into a small Whirl-Pak. Samples were immediately placed on ice and stored in a -80°C freezer upon return to shore. Following sediment sampling, three&amp;amp;nbsp;&amp;lt;em&amp;gt;A. pulchra&amp;lt;/em&amp;gt;&amp;amp;nbsp;outplants were embedded into the sediment of each cage&amp;amp;nbsp;(108 outplants total) to test the potential effects of (i) sea cucumber density, and (ii) protective effects of farmerfish-cultivated turf algae on coral health and microbiomes (see below). Corals used were approximately 8-10 cm in length and were initially fragmented from numerous&amp;amp;nbsp;&amp;lt;em&amp;gt;A. pulchra&amp;lt;/em&amp;gt;&amp;amp;nbsp;thickets adjacent to our study area and outplanted using the methods described above.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Of the three outplants included in each cage, two were fragmented from colonies in the field in such a way as to include farmerfish-generated turf algae at their base, while the third was fragmented so that it lacked turf at its base. These three outplants were embedded into the sediment as follows: (i) coral lacking turf planted in direct contact with benthic sediment (hereafter “no turf”), (ii) coral separated from direct contact with sediment by turf algae growing at its base (hereafter “turf”), or (iii) coral with turf on its base, but embedded more deeply into the sediment so that the living coral tissue was in direct contact with the sediment (hereafter “embedded turf”). Percent coral tissue mortality among outplants was visually estimated daily for 36 days. The microbiomes of all corals and the sediment within a cage were sampled when one or more outplants within that cage exhibited ≥50% tissue mortality or when the experiment was terminated on day 36.&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Organism identifiers:&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Coral: Acropora pulchra, LSID (urn:lsid:marinespecies.org:taxname:207015)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Cucumber: Holothuria atra, LSID (urn:lsid:marinespecies.org:taxname:1672768)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;farmerfish: Stegastes spp, LSID (urn:lsid:marinespecies.org:taxname:203822)&amp;lt;/p&amp;gt;
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