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            <gco:CharacterString>Cite this dataset as: Geange, S. (2021) The influence of structural refuge, competition and their interaction on the early post-settlement survival of transplanted Thalassoma hardwicke (the sixbar wrasse) in Moorea, French Polynesia from 2005-2007 (CDD_in_Reef_Fish project). Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2017-10-05 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.726353.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>This dataset specially refers to the field experiment used to test how competition with larger residents and structural refuge interact to influence survival of transplanted T. hardwicke. Dataset Description: &amp;lt;p&amp;gt;This dataset is from a study examining the influence of structural refuge, competition and their interaction on the early post-settlement survival of transplanted &amp;lt;em&amp;gt;Thalassoma hardwicke &amp;lt;/em&amp;gt;(the sixbar wrasse).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;This dataset specifically&amp;amp;nbsp;refers to the field experiment used to test how competition with larger residents and structural refuge interact to influence survival of transplanted &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt;. Please see Related Datasets below for additional data associated with this project.&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;Results from the field assay identified larger &amp;lt;em&amp;gt;Thalassoma quinquevittatum&amp;lt;/em&amp;gt; as strongly competing with focal &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt;. A factorial experiment was used to evaluate the effect of competition with larger &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt; and the provisioning of structural refuge on the survival of transplanted &amp;lt;em&amp;gt;T.&amp;lt;/em&amp;gt; &amp;lt;em&amp;gt;hardwicke&amp;lt;/em&amp;gt;. Structural refuge was increased by adding &amp;lt;em&amp;gt;Turbinaria ornata&amp;lt;/em&amp;gt; (a structurally complex, locally common, macroalga) to reefs. Twenty reefs were haphazardly selected, with an average surface area of 5.46 m2 (SE = 0.36), a mean height of 0.79 m (SE = 0.03) and isolated from their nearest neighbour by 3.02 m (SE = 0.19). All reefs initially had three to five (mean = 3.38; SE = 0.16) resident &amp;lt;em&amp;gt;Thalassoma quinquevittatum&amp;lt;/em&amp;gt; (22.1 mm SL, SE = 0.56) and lacked &amp;lt;em&amp;gt;Turbinaria ornata&amp;lt;/em&amp;gt;. The presence/absence of &amp;lt;em&amp;gt;T. ornata&amp;lt;/em&amp;gt; was cross-factored with the presence/absence of &amp;lt;em&amp;gt;T&amp;lt;/em&amp;gt;. &amp;lt;em&amp;gt;quinquevittatum&amp;lt;/em&amp;gt; and treatments were randomly assigned to reefs. On reefs assigned to the presence of &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt;, selective removals were conducted so that each reef had three, similarly sized, T. quinquevittatum individuals that were larger than focal &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; individuals. For &amp;lt;em&amp;gt;T. ornata &amp;lt;/em&amp;gt;present treatments, whole &amp;lt;em&amp;gt;T. ornata&amp;lt;/em&amp;gt; plants were attached to recipient reefs with cable ties, so that ~15% of habitat cover was &amp;lt;em&amp;gt;T. ornata&amp;lt;/em&amp;gt;. Before the experiment, all resident T. hardwicke were removed from the reefs. Three &amp;lt;em&amp;gt;Thalassoma hardwicke&amp;lt;/em&amp;gt; individuals (13.69 mm SL, SE = 0.51: collected and tagged as per the field assay) were transplanted onto each reef and their survival surveyed daily (~ 9 a.m.) for five days. Each morning, immigrant &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt; (three immigrants were observed) and new &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; that had settled the previous night (a total of eight settlers) were removed. Neighboring non-experimental reefs were also searched for tagged &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; immigrants. No tagged immigrants were found; therefore, the disappearance of a tagged fish was assumed due to mortality rather than migration (as for the field assay). Using the same reefs, the experiment was run in two temporal blocks (beginning12 June 2005 and 12 May 2007), yielding ten replicates (five in each temporal block) for each of the four treatments. The mean proportion of &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; remaining in each treatment on the last day of the experiment was used as the response variable because by the end of each experimental run survival trajectories had stabilized.&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/540422.rdf" xlink:title="OCE-0242312" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-0242312 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=0242312</gmx:Anchor>
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Ecologists have long been interested in the factors that drive spatial and temporal variability in population density and structure. In marine reef systems, attention has focused on the role of settlement-the transition of pelagic larvae to a benthic stage-and on density-dependent processes affecting recently settled juveniles. Recent data suggest that co-variance in settlement and subsequent density-dependent survival can obscure the patterns of density dependence at larger scales, a phenomenon called cryptic density dependence. This research will explore the mechanisms that underlie the spatial covariance of settlement and site quality - a process that has received little attention in the standard paradigm. These mechanistic studies of cryptic density dependence will facilitate the development of new frameworks for fish population dynamics that incorporate larval ecology, habitat quality, density dependence, life history, and the patterns and implications of spatial covariance among these factors. More generally, the work provides a specific empirical context, and a general theoretical treatment, of cryptic heterogeneity (hidden individual variation in demographic rates).&lt;/p&gt;
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                <gco:CharacterString>&amp;lt;p&amp;gt;Results from the field assay identified larger &amp;lt;em&amp;gt;Thalassoma quinquevittatum&amp;lt;/em&amp;gt; as strongly competing with focal &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt;. A factorial experiment was used to evaluate the effect of competition with larger &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt; and the provisioning of structural refuge on the survival of transplanted &amp;lt;em&amp;gt;T.&amp;lt;/em&amp;gt; &amp;lt;em&amp;gt;hardwicke&amp;lt;/em&amp;gt;. Structural refuge was increased by adding &amp;lt;em&amp;gt;Turbinaria ornata&amp;lt;/em&amp;gt; (a structurally complex, locally common, macroalga) to reefs. Twenty reefs were haphazardly selected, with an average surface area of 5.46 m2 (SE = 0.36), a mean height of 0.79 m (SE = 0.03) and isolated from their nearest neighbour by 3.02 m (SE = 0.19). All reefs initially had three to five (mean = 3.38; SE = 0.16) resident &amp;lt;em&amp;gt;Thalassoma quinquevittatum&amp;lt;/em&amp;gt; (22.1 mm SL, SE = 0.56) and lacked &amp;lt;em&amp;gt;Turbinaria ornata&amp;lt;/em&amp;gt;. The presence/absence of &amp;lt;em&amp;gt;T. ornata&amp;lt;/em&amp;gt; was cross-factored with the presence/absence of &amp;lt;em&amp;gt;T&amp;lt;/em&amp;gt;. &amp;lt;em&amp;gt;quinquevittatum&amp;lt;/em&amp;gt; and treatments were randomly assigned to reefs. On reefs assigned to the presence of &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt;, selective removals were conducted so that each reef had three, similarly sized, T. quinquevittatum individuals that were larger than focal &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; individuals. For &amp;lt;em&amp;gt;T. ornata &amp;lt;/em&amp;gt;present treatments, whole &amp;lt;em&amp;gt;T. ornata&amp;lt;/em&amp;gt; plants were attached to recipient reefs with cable ties, so that ~15% of habitat cover was &amp;lt;em&amp;gt;T. ornata&amp;lt;/em&amp;gt;. Before the experiment, all resident T. hardwicke were removed from the reefs. Three &amp;lt;em&amp;gt;Thalassoma hardwicke&amp;lt;/em&amp;gt; individuals (13.69 mm SL, SE = 0.51: collected and tagged as per the field assay) were transplanted onto each reef and their survival surveyed daily (~ 9 a.m.) for five days. Each morning, immigrant &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt; (three immigrants were observed) and new &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; that had settled the previous night (a total of eight settlers) were removed. Neighboring non-experimental reefs were also searched for tagged &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; immigrants. No tagged immigrants were found; therefore, the disappearance of a tagged fish was assumed due to mortality rather than migration (as for the field assay). Using the same reefs, the experiment was run in two temporal blocks (beginning12 June 2005 and 12 May 2007), yielding ten replicates (five in each temporal block) for each of the four treatments. The mean proportion of &amp;lt;em&amp;gt;T. hardwicke&amp;lt;/em&amp;gt; remaining in each treatment on the last day of the experiment was used as the response variable because by the end of each experimental run survival trajectories had stabilized.&amp;lt;/p&amp;gt;</gco:CharacterString>
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Processing notes from the researcher:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

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&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;BCO-DMO Processing:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;ul&amp;gt;
&amp;lt;li&amp;gt;added conventional header with dataset name, PI name, version date&amp;lt;/li&amp;gt;
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</gmi:platform>
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