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            <gco:CharacterString>Cite this dataset as: Geange, S., Shima, J., Stier, A. (2021) Size distribution of Thalassoma quinquevittatum standard length in the experiment at Moorea, French Polynesia from April to May 2008 (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.727007.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>This dataset is from a manipulative experiment investigating the independent and combined effects of priority effects and habitat complexity on the strength of intraspecific competitive interactions among recently settled individuals of a coral reef fish. Dataset Description: &amp;lt;p&amp;gt;This dataset is from a manipulative experiment investigating the independent and combined effects of priority effects and habitat complexity on the strength of intraspecific competitive interactions among recently settled individuals of a coral reef fish (Thalassoma quinquevittatum: Labridae).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;This file is dataset 3 of a 4 and describes the size distribution of Thalassoma quinquevittatum standard length used in the experiment. For additional data, please see Related Datasets.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Related Datase&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;ul&amp;gt;
&amp;lt;li&amp;gt;Geange_and_Stier_2010 Priority Effects:&amp;amp;nbsp;https://www.bco-dmo.org/dataset/726890&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;Geange_and_Stier_2010 Priority Effects Area:&amp;amp;nbsp;https://www.bco-dmo.org/dataset/726929&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;Geange_and_Stier_2010 Priority Effects Length:&amp;amp;nbsp;https://www.bco-dmo.org/dataset/727007 (current page)&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;Geange_and_Stier_2010 Priority Effects Background Community:&amp;amp;nbsp;https://www.bco-dmo.org/dataset/726945&amp;lt;/li&amp;gt;
&amp;lt;/ul&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;This dataset describes the size distribution of &amp;lt;em&amp;gt;Thalassoma quinquevittatum&amp;lt;/em&amp;gt; stand length used in the experiment.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;We examined the effects of habitat complexity and timing of arrival in the context of the survival of focal &amp;lt;em&amp;gt;Thalassoma quinquevittatum&amp;lt;/em&amp;gt; settlers. We used an array of 30 isolated live-coral patch reefs separated by *10 m in water 2–4 m deep. Reefs were located within a sand-flat, separated from each other, and from nearby natural reefs, by a minimum of 15 m. We constructed reefs to minimize habitat variation by standardizing size, rugosity, and water depth. Each reef consisted of a base of live Porites lobata coral with an average area of 2.23 m2 (SD = 0.56), and a mean height of 0.59 m (SD = 0.10). We controlled habitat complexity by manipulating the availability of the branching coral Pocillopora verrucosa. This was achieved by drilling holes into the upper surface of patch reefs. Into these holes, we inserted stainless steel pins attached to P. verrucosa colonies with Z-Spar Splash Zone Compound (Kopcoat, Pittsburgh, PA, USA). Mean colony surface area was 0.2 m2 (SD = 0.07). We crossed the availability of P. verrucosa (two levels: two, or four colonies) with the presence of three tagged &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt; competitors (three levels: absent, introduced simultaneously with (0 days), or 5 days earlier than the focal individuals). To each reef, we simulated settlement by introducing three tagged &amp;lt;em&amp;gt;T. quinquevittatum &amp;lt;/em&amp;gt;focal individuals. Thus, our design had six treatments: (1) focal individuals without competitors, with two &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; (2) focal individuals and competitors introduced simultaneously, with two P. verrucosa colonies; (3) focal individuals with competitors introduced 5 days previously, with two &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; (4) focal individuals without competitors, with four &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; (5) focal individuals and competitors introduced simultaneously, with four &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; and (6) focal individuals with competitors introduced 5 days previously, with four &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies. We ran the experiment in two temporal blocks (17–23 April and 1–7 May 2008), yielding ten replicates (five in each temporal block) for each of the six treatments. We surveyed reefs twice daily (approximately 0800 and 1600 hours) for 5 days after the introduction of focal individuals.&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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&amp;lt;p&amp;gt;We examined the effects of habitat complexity and timing of arrival in the context of the survival of focal &amp;lt;em&amp;gt;Thalassoma quinquevittatum&amp;lt;/em&amp;gt; settlers. We used an array of 30 isolated live-coral patch reefs separated by *10 m in water 2–4 m deep. Reefs were located within a sand-flat, separated from each other, and from nearby natural reefs, by a minimum of 15 m. We constructed reefs to minimize habitat variation by standardizing size, rugosity, and water depth. Each reef consisted of a base of live Porites lobata coral with an average area of 2.23 m2 (SD = 0.56), and a mean height of 0.59 m (SD = 0.10). We controlled habitat complexity by manipulating the availability of the branching coral Pocillopora verrucosa. This was achieved by drilling holes into the upper surface of patch reefs. Into these holes, we inserted stainless steel pins attached to P. verrucosa colonies with Z-Spar Splash Zone Compound (Kopcoat, Pittsburgh, PA, USA). Mean colony surface area was 0.2 m2 (SD = 0.07). We crossed the availability of P. verrucosa (two levels: two, or four colonies) with the presence of three tagged &amp;lt;em&amp;gt;T. quinquevittatum&amp;lt;/em&amp;gt; competitors (three levels: absent, introduced simultaneously with (0 days), or 5 days earlier than the focal individuals). To each reef, we simulated settlement by introducing three tagged &amp;lt;em&amp;gt;T. quinquevittatum &amp;lt;/em&amp;gt;focal individuals. Thus, our design had six treatments: (1) focal individuals without competitors, with two &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; (2) focal individuals and competitors introduced simultaneously, with two P. verrucosa colonies; (3) focal individuals with competitors introduced 5 days previously, with two &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; (4) focal individuals without competitors, with four &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; (5) focal individuals and competitors introduced simultaneously, with four &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies; and (6) focal individuals with competitors introduced 5 days previously, with four &amp;lt;em&amp;gt;P. verrucosa&amp;lt;/em&amp;gt; colonies. We ran the experiment in two temporal blocks (17–23 April and 1–7 May 2008), yielding ten replicates (five in each temporal block) for each of the six treatments. We surveyed reefs twice daily (approximately 0800 and 1600 hours) for 5 days after the introduction of focal individuals.&amp;lt;/p&amp;gt;</gco:CharacterString>
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&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;
&amp;lt;li&amp;gt;modified parameter names to conform with BCO-DMO naming conventions&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;date fromat was converted from dd-mon-yy (eg.&amp;amp;nbsp;17-Apr-08) to yyyymmdd (20080417).&amp;lt;/li&amp;gt;
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