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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/750579.rdf" xlink:actuate="onRequest">Effect of flow environment on mud crab perceptive range based on field experiments in intertidal mudflats on Skidaway Island, GA, 2014-2016</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Pruett, J. P. (2018) Effect of flow environment on mud crab perceptive range based on field experiments in intertidal mudflats on Skidaway Island, GA, 2014-2016. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2018-12-03 [if applicable, indicate subset used]. http://lod.bco-dmo.org/id/dataset/750579 [access date]</gco:CharacterString>
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        <gco:CharacterString>Mud crab predation on oyster spat near blue crabs Dataset Description: &amp;lt;p&amp;gt;Mud crab predation on oyster spat in the presence of caged blue crab predators placed various distances away from mud crab refuge. Field experiments were conducted at two different sites on Skidaway Island, GA during two different tidal types to determine the effect of current speed and turbulence on mud crab perceptive range.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;These data were published in Pruett and Weissburg, 2018.&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;Mud crab perceptive range trials were performed in enclosures (2.2 m by 0.75 m by 0.3 m) that contained an oyster reef as a refuge for mud crabs at one end. Oyster shells were glued together to create artificial oyster clusters that were used to manipulate the placement of oyster spat within the enclosure. Four oyster spat (10-16 mm) were epoxied to the artificial oyster clusters and 4 clusters were placed within the constructed oyster reef and 4 clusters outside the reef. Fifteen mud crabs (8 crabs 15-20 mm CW, 4 mud crabs 20-25 mm CW, and 3 mud crabs 25-30 mm CW) were added to the oyster reef in the enclosure. Caged blue crabs (12-16 cm CW) were placed either 0.25, 0.5, 1.0, 1.5, or 2.0 m away from the center of the oyster reef. A caged blue crab was placed on both sides of the oyster reef in the direction of tidal flow with one caged blue crab in the enclosure and the other outside the enclosure. Empty blue crab cages were used for the control treatment.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Enclosures were deployed on intertidal mudflats at either Priest Landing or Skidaway Narrows during either mean tide or spring tide. Flow parameters differed between sites and tidal types based on previous work (Wilson et al. 2013). The number of oyster spat eaten by mud crabs inside and outside the refuge was counted after 24 hours. See Pruett and Weissburg, 2018 for full methods.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Data were statistically analyzed using R version 3.3.1.&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/565702.rdf" xlink:title="OCE-1234449" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1234449 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1234449</gmx:Anchor>
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&amp;lt;p&amp;gt;Enclosures were deployed on intertidal mudflats at either Priest Landing or Skidaway Narrows during either mean tide or spring tide. Flow parameters differed between sites and tidal types based on previous work (Wilson et al. 2013). The number of oyster spat eaten by mud crabs inside and outside the refuge was counted after 24 hours. See Pruett and Weissburg, 2018 for full methods.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

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