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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/939581.rdf" xlink:actuate="onRequest">Data from scallop survival assays conducted as part of a larger concurrent study of fragmentation effects on estuarine faunal communities with Artificial Seagrass Units (ASU) in Back Sound, NC from July to September 2018</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Yarnall, A., Fodrie, F. J. (2024) Data from scallop survival assays conducted as part of a larger concurrent study of fragmentation effects on estuarine faunal communities with Artificial Seagrass Units (ASU) in Back Sound, NC from July to September 2018. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2024-10-04 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.939581.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Methods and Sampling: &amp;lt;p&amp;gt;To parse the influences of fragmentation components on scallop survival, we generated nine unique landscape grids of 15 × 15 cells. Each cell was the size of an ASU, making the landscape area = 234 m&amp;lt;sup&amp;gt;2&amp;lt;/sup&amp;gt; (18-m × 13-m). These landscapes were part of a larger-scale concurrent experiment, during which we examined seagrass fragmentation effects on estuarine faunal communities (Yarnall et al. In Press). Landscapes were designed to be treatments along orthogonal axes of seagrass percent cover of the landscape footprint (10%, 35%, 60%) and fragmentation &amp;lt;em&amp;gt;per se&amp;lt;/em&amp;gt;, indexed by percolation probability (0.1, 0.35, 0.59).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Relative scallop survival was measured using tethered juvenile bay scallops of initial shell height (SH) 3-5 mm, provided by the Castagna Shellfish Research Hatchery at The Virginia Institute of Marine Science, Eastern Shore Laboratory (VIMS ESL) in Wachapreague, VA. The knotted end of 10-cm segment of 12-lbs test monofilament was dotted with cyanoacrylate glue and pressed into a scallop’s ventral shell ridge under a tab of duct tape. Each tether was then anchored to a 30-cm lawn staple and held overnight in aquaria to check attachment integrity. Tethers were then deployed across landscapes the following day.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;To examine whether landscape configuration could mediate density-dependent predation rates on scallops, tethers were deployed in low (1&amp;lt;em&amp;gt;x&amp;lt;/em&amp;gt; = 4 or 5 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt;) and high (6&amp;lt;em&amp;gt;x&amp;lt;/em&amp;gt; = 24 or 30 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt;) density treatments (&amp;lt;em&amp;gt;x&amp;lt;/em&amp;gt; was chosen based on scallop availability). All scallop tethers were placed ≤1-m from the seagrass-sandflat interface on randomly selected edge (interface-bordering) ASUs, to avoid potential edge effects. Five 24-h survival assay trials were conducted from July to September 2018. Because predation rates after 24 h were high during the first trial, when scallops were smallest, tethers were also checked at 2 h and 6 h during subsequent trials. However, preliminary analysis revealed that across trials, predation rates after 2 h and 6 h were too low to provide resolution among landscape treatments; therefore, only results for cumulative survival after 24 h are presented.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;During each survival assay, observers snorkel surveyed tethers and recorded the number of live and dead scallops per treatment. During the first trial, ten tethered dead scallop shells (valves glued shut) were deployed as an additional tether integrity control. However, controls were depredated at similar rates to live scallops, as evinced by crushed shells. For all subsequent trials, control tethers were deployed in cages constructed from cuboid PVC frames covered by mesh VEXAR®. Attachment failure occurred in &amp;amp;lt;3% of all caged-control tethers, therefore no adjustments to scallop recovery rates were necessary.&amp;amp;nbsp;&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Depth note:&amp;amp;nbsp;&amp;amp;nbsp;Depth ranges were similar across all sites as they were located on a single shoal (Oscar Shoal in Back Sound, NC, USA). Depths typically ranged from &amp;amp;lt;0.5 m (at low tide) to 1.5-2 m (at high tide).&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Organism identifiers (common name, scientific name, LSID):&amp;lt;br /&amp;gt;
bay scallop, &amp;lt;em&amp;gt;Argopecten irradians&amp;lt;/em&amp;gt;,&amp;amp;nbsp;urn:lsid:marinespecies.org:taxname:156817&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/714025.rdf" xlink:title="OCE-1635950" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1635950 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1635950</gmx:Anchor>
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http://lod.bco-dmo.org/id/dataset-parameter/939755.rdf
	Name: Date_In
	Units: unitless
	Description: &lt;p&gt;Date of scallop tether deployment  (local time zone EST/EDT)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939756.rdf
	Name: Time_In
	Units: unitless
	Description: &lt;p&gt;Time of scallop tether deployment  (local time zone EST/EDT, 24hr)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939757.rdf
	Name: ISO_DateTime_UTC_In
	Units: unitless
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http://lod.bco-dmo.org/id/dataset-parameter/939758.rdf
	Name: Check_num
	Units: unitless
	Description: &lt;p&gt;Interval of scallop tether check 2 h, 6 h, 24 h&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939759.rdf
	Name: Date_check
	Units: unitless
	Description: &lt;p&gt;Date of scallop tether check  (local time zone EST/EDT)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939760.rdf
	Name: Time_check
	Units: unitless
	Description: &lt;p&gt;Time of scallop tether check  (local time zone EST/EDT, 24hr)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939761.rdf
	Name: H_tide
	Units: unitless
	Description: &lt;p&gt;Time of high tide proximate to scallop tether check (local time zone EST/EDT, 24hr)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939762.rdf
	Name: L_tide
	Units: unitless
	Description: &lt;p&gt;Time of low tide proximate to scallop tether check  (local time zone EST/EDT, 24hr)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939763.rdf
	Name: WaterTemp_C
	Units: degrees C
	Description: &lt;p&gt;Surface water temperature at time of scallop tether check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939764.rdf
	Name: Sal_PSU
	Units: Practical Salinity Units (PSU)
	Description: &lt;p&gt;Surface salinity at time of scallop tether check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939765.rdf
	Name: Cell_coord
	Units: unitless
	Description: &lt;p&gt;ASU landscape &amp;quot;cell coordinate&amp;quot; by C (column; out of 15) and R (row; out of 15) number. See &amp;quot;Methods &amp;amp; Sampling&amp;quot; section for additional details of survey design for grid cells.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939766.rdf
	Name: Treatment
	Units: unitless
	Description: &lt;p&gt;Scallop tether density treatment. CC= &quot;Caged Controls&quot; - dead scallop shell tether controls in a cage; DC= &quot;Dead Controls&quot; - dead scallop shell tether controls  (not caged); H= &quot;High density treatment&quot;; L= &quot;Low density treatment&quot;&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939767.rdf
	Name: Density_initial
	Units: number per meter squared (per m2)
	Description: &lt;p&gt;Number of scallop tethers deployed for high or low density treatment&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939768.rdf
	Name: Live_check
	Units: count
	Description: &lt;p&gt;Number of live tethered scallops at time of check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939769.rdf
	Name: Dead_check
	Units: count
	Description: &lt;p&gt;Number (since last check) of dead/eaten/missing tethered scallops at time of check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939770.rdf
	Name: Dead_total
	Units: count
	Description: &lt;p&gt;Cumulative number (since deployment) of dead/eaten/missing tethered scallops at time of check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939771.rdf
	Name: Shell_gone
	Units: count
	Description: &lt;p&gt;Number of missing tethered scallops whether the complete tether is present in Dead_check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939772.rdf
	Name: Shell_intactdead
	Units: count
	Description: &lt;p&gt;Number of intact dead shells of tethered scallops in Dead_check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939773.rdf
	Name: Shell_intacthalf
	Units: count
	Description: &lt;p&gt;Number of intact half shells (i.e., one valve) of tethered scallops in Dead_check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939774.rdf
	Name: Shell_fragment
	Units: count
	Description: &lt;p&gt;Number of fragmented/chrushed tethered scallops in Dead_check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939775.rdf
	Name: Tether_snipped
	Units: count
	Description: &lt;p&gt;Number of missing tethered scallops where the tether has been snipped in Dead_check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939776.rdf
	Name: Shell_chipped
	Units: count
	Description: &lt;p&gt;Number of chipped shell tethered scallops in Dead_check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939777.rdf
	Name: Shell_drilled
	Units: count
	Description: &lt;p&gt;Number of drilled shell tethered scallops in Dead_check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939778.rdf
	Name: Not_found
	Units: count
	Description: &lt;p&gt;Number of tethers not relocated. This number was substracted from initial density (i.e., removed from the experiment)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939779.rdf
	Name: Notes
	Units: unitless
	Description: &lt;p&gt;Observational notes on tethered scallops&lt;/p&gt; 
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&amp;lt;p&amp;gt;Relative scallop survival was measured using tethered juvenile bay scallops of initial shell height (SH) 3-5 mm, provided by the Castagna Shellfish Research Hatchery at The Virginia Institute of Marine Science, Eastern Shore Laboratory (VIMS ESL) in Wachapreague, VA. The knotted end of 10-cm segment of 12-lbs test monofilament was dotted with cyanoacrylate glue and pressed into a scallop’s ventral shell ridge under a tab of duct tape. Each tether was then anchored to a 30-cm lawn staple and held overnight in aquaria to check attachment integrity. Tethers were then deployed across landscapes the following day.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;To examine whether landscape configuration could mediate density-dependent predation rates on scallops, tethers were deployed in low (1&amp;lt;em&amp;gt;x&amp;lt;/em&amp;gt; = 4 or 5 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt;) and high (6&amp;lt;em&amp;gt;x&amp;lt;/em&amp;gt; = 24 or 30 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt;) density treatments (&amp;lt;em&amp;gt;x&amp;lt;/em&amp;gt; was chosen based on scallop availability). All scallop tethers were placed ≤1-m from the seagrass-sandflat interface on randomly selected edge (interface-bordering) ASUs, to avoid potential edge effects. Five 24-h survival assay trials were conducted from July to September 2018. Because predation rates after 24 h were high during the first trial, when scallops were smallest, tethers were also checked at 2 h and 6 h during subsequent trials. However, preliminary analysis revealed that across trials, predation rates after 2 h and 6 h were too low to provide resolution among landscape treatments; therefore, only results for cumulative survival after 24 h are presented.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;During each survival assay, observers snorkel surveyed tethers and recorded the number of live and dead scallops per treatment. During the first trial, ten tethered dead scallop shells (valves glued shut) were deployed as an additional tether integrity control. However, controls were depredated at similar rates to live scallops, as evinced by crushed shells. For all subsequent trials, control tethers were deployed in cages constructed from cuboid PVC frames covered by mesh VEXAR®. Attachment failure occurred in &amp;amp;lt;3% of all caged-control tethers, therefore no adjustments to scallop recovery rates were necessary.&amp;amp;nbsp;&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Depth note:&amp;amp;nbsp;&amp;amp;nbsp;Depth ranges were similar across all sites as they were located on a single shoal (Oscar Shoal in Back Sound, NC, USA). Depths typically ranged from &amp;amp;lt;0.5 m (at low tide) to 1.5-2 m (at high tide).&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Organism identifiers (common name, scientific name, LSID):&amp;lt;br /&amp;gt;
bay scallop, &amp;lt;em&amp;gt;Argopecten irradians&amp;lt;/em&amp;gt;,&amp;amp;nbsp;urn:lsid:marinespecies.org:taxname:156817&amp;lt;/p&amp;gt;</gco:CharacterString>
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