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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/939617.rdf" xlink:actuate="onRequest">Scallop density survey data across landscape fragmentation per se treatments in June, July, and August 2019 in Back Sound, NC</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Yarnall, A., Fodrie, F. J. (2024) Scallop density survey data across landscape fragmentation per se treatments in June, July, and August 2019 in Back Sound, NC. 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.939617.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Dataset Description: &amp;lt;p&amp;gt;ASU = artificial seagrass unit&amp;lt;br /&amp;gt;
VIMS ESL = Eastern Shore Laboratory | Virginia Institute of Marine Science&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;To explore the independent influence of fragmentation &amp;lt;em&amp;gt;per se&amp;lt;/em&amp;gt; (patchiness) on mobile juvenile bay scallop (&amp;lt;em&amp;gt;Argopecten irradians&amp;lt;/em&amp;gt;) density, we constructed 16 artificial seagrass unit (ASU) landscapes (12-m x 10-m), consisting of four replicates each of four treatments. Fragmentation &amp;lt;em&amp;gt;per se&amp;lt;/em&amp;gt; treatments consisted of three levels of patchiness (i.e., 1 patch, 12 patches, 24 patches) while maintaining consistent total ASU area (48 ASUs, 50 m&amp;lt;sup&amp;gt;2&amp;lt;/sup&amp;gt; artificial seagrass). Between treatments of 12 and 24 patches, differences in configuration could be achieved by either varying interpatch distances or total footprint area. Therefore, we used two 12-patch treatments to consider these covariates separately, as indicated by footprint sizes (i.e., 12 patches-small versus 12 patches-large). We also examined the effect of patch-scale position on scallop densities. Relative 'inner' and 'outer' positions were operationally defined for 1-patch and multi-patch landscapes, separately. Within 1-patch landscapes, ASUs that bordered sandflat were considered 'outer' positions, while 'inner' positions were defined by ASUs that only bordered other ASUs. Within multi-patch landscapes, 'outer' positions were patches that had no additional patches between them and the landscape footprint border. 'Inner' position patches were centrally located patches in the landscape.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Freely mobile (non-tethered) juvenile scallops of SH 43.1 ± 6.8 mm [mean ± SD] were placed at a consistent density (indiv. m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt;) across landscapes for three density survey trials, one each during June, July, and August 2019. Prior to each trial, landscapes were snorkeled to confirm that no scallops were present. Due to the isolation of these ASU landscapes and the general rarity of scallops on Oscar shoal, we were reasonably certain all scallops in these landscapes were purposefully placed there, meaning there was no immigration from other ASU landscapes or natural seagrass. For June and July trials, all scallops were collected from a natural seagrass meadow located across a deep boating channel from the experimental landscapes. During August, a mixture of scallops from two sources was used: from the nearby meadow, and NC-descendant scallops of similar size provided by VIMS ESL. Before scallop placement in landscapes, all scallops were stored in outdoor estuary-fed flow-through aquaria for up to two weeks. During June and July trials, scallops were placed in all 16 landscapes at an initial density of 1 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; (i.e., one per ASU), allowing for resolution in landscape treatment effects while maintaining relative comparability to natural conditions in our system (i.e., 0.6 scallops m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; in the nearby scallop-source meadow). By the conclusion of the July trial, landscapes along one shoal margin were becoming substantially buried under sediment due to wave/current action. Therefore, for the August trial the number of landscape treatment replicates was reduced to three to exclude the buried replicates, and a 1-patch landscape replicate was rebuilt in a calmer area of the shoal. In addition, during the August trial, the initial scallop density was increased to 2 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; (i.e., two per ASU) to increase resolution among habitat treatments. Observers snorkel surveyed each landscape at 24 h, 48 h, and 72 h during each trail, except for the 48-h survey in June, which was canceled due to inclement weather. During each survey, observers recorded the number of scallops per ASU. On rare occasions when scallops were found on sand &amp;amp;lt;1 m from an ASU, their count was assigned to that nearest ASU, as they were likely still using the artificial seagrass mosaic as habitat.&amp;amp;nbsp;&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Depth note:&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;/p&amp;gt;

&amp;lt;p&amp;gt;Organism identifiers&amp;amp;nbsp;(common name, scientific name, LSID):&amp;lt;br /&amp;gt;
bay scallop, &amp;lt;em&amp;gt;Argopecten irradians&amp;lt;/em&amp;gt;, urn:lsid:marinespecies.org:taxname:156817&amp;lt;br /&amp;gt;
Tulip whelk,&amp;lt;em&amp;gt;Fasciolaria&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:138001&amp;lt;br /&amp;gt;
Knobbed whelk,&amp;lt;em&amp;gt;Busycon carica&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:160185&amp;lt;br /&amp;gt;
Horse conch,&amp;lt;em&amp;gt;Triplofusus papillosus auct.&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:448509&amp;lt;br /&amp;gt;
Moon snail,&amp;lt;em&amp;gt;Neverita duplicata&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:160407&amp;lt;br /&amp;gt;
Lightning whelk,&amp;lt;em&amp;gt;Sinistrofulgur sinistrum&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:862934&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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            <gmx:Anchor xlink:href="https://ror.org/0130frc33" xlink:title="ROR ID" xlink:actuate="onRequest">University of North Carolina at Chapel Hill</gmx:Anchor>
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http://lod.bco-dmo.org/id/dataset-parameter/939926.rdf
	Name: Check_num
	Units: unitless
	Description: &lt;p&gt;Interval of scallop tether check 24 h, 48 h, 72 h&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939927.rdf
	Name: Time_check
	Units: unitless
	Description: &lt;p&gt;Time of scallop density check (local time zone EST/EDT, 24h)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939928.rdf
	Name: ISO_DateTime_UTC_check
	Units: unitless
	Description: &lt;p&gt;DateTime with timezone of scallop density check (ISO 8601 format in timezone UTC)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939929.rdf
	Name: H_tide
	Units: unitless
	Description: &lt;p&gt;Time of high tide proximate to scallop tether check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939930.rdf
	Name: L_tide
	Units: unitless
	Description: &lt;p&gt;Time of low tide proximate to scallop tether check&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939931.rdf
	Name: Position
	Units: unitless
	Description: &lt;p&gt;Patch-scale position (Inner, Outer)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939932.rdf
	Name: Patch_type
	Units: unitless
	Description: &lt;p&gt;Relative location of patch within landscape configuration (Inner, Outer, NA)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939933.rdf
	Name: Edge_Interior
	Units: unitless
	Description: &lt;p&gt;Edge or interior ASU&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939934.rdf
	Name: Cell_coord
	Units: unitless
	Description: &lt;p&gt;ASU &amp;quot;cell coordinate&amp;quot; by C (column; out of 6) and R (row; out of 8) number&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939935.rdf
	Name: Scallop_density
	Units: number per square meter (#/m2)
	Description: &lt;p&gt;Number of scallops on ASU Cell_coord&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939936.rdf
	Name: Sand_density
	Units: number per square meter (#/m2)
	Description: &lt;p&gt;Number of scallops on sand &amp;lt;1-m from ASU Cell_coord&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939937.rdf
	Name: Tulip_whelk
	Units: number per square meter (#/m2)
	Description: &lt;p&gt;Number of Tulip whelk (Fasciolaria). Life Science Identifier (LSID)=urn:lsid:marinespecies.org:taxname:138001&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939938.rdf
	Name: Knobbed_whelk
	Units: number per square meter (#/m2)
	Description: &lt;p&gt;Number of Knobbed whelk (Busycon carica). Life Science Identifier (LSID)=urn:lsid:marinespecies.org:taxname:160185&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939939.rdf
	Name: Horse_conch
	Units: number per square meter (#/m2)
	Description: &lt;p&gt;Number of Horse conch (Triplofusus papillosus auct.). Life Science Identifier (LSID)=urn:lsid:marinespecies.org:taxname:448509&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939940.rdf
	Name: Moon_snail
	Units: number per square meter (#/m2)
	Description: &lt;p&gt;Number of Moon snail (Neverita duplicata). Life Science Identifier (LSID)=urn:lsid:marinespecies.org:taxname:160407&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/939941.rdf
	Name: Lightning_whelk
	Units: number per square meter (#/m2)
	Description: &lt;p&gt;Number of Lightning whelk (Sinistrofulgur sinistrum). Life Science Identifier (LSID)=urn:lsid:marinespecies.org:taxname:862934&lt;/p&gt; 
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                <gco:CharacterString>&amp;lt;p&amp;gt;To explore the independent influence of fragmentation &amp;lt;em&amp;gt;per se&amp;lt;/em&amp;gt; (patchiness) on mobile juvenile bay scallop (&amp;lt;em&amp;gt;Argopecten irradians&amp;lt;/em&amp;gt;) density, we constructed 16 artificial seagrass unit (ASU) landscapes (12-m x 10-m), consisting of four replicates each of four treatments. Fragmentation &amp;lt;em&amp;gt;per se&amp;lt;/em&amp;gt; treatments consisted of three levels of patchiness (i.e., 1 patch, 12 patches, 24 patches) while maintaining consistent total ASU area (48 ASUs, 50 m&amp;lt;sup&amp;gt;2&amp;lt;/sup&amp;gt; artificial seagrass). Between treatments of 12 and 24 patches, differences in configuration could be achieved by either varying interpatch distances or total footprint area. Therefore, we used two 12-patch treatments to consider these covariates separately, as indicated by footprint sizes (i.e., 12 patches-small versus 12 patches-large). We also examined the effect of patch-scale position on scallop densities. Relative 'inner' and 'outer' positions were operationally defined for 1-patch and multi-patch landscapes, separately. Within 1-patch landscapes, ASUs that bordered sandflat were considered 'outer' positions, while 'inner' positions were defined by ASUs that only bordered other ASUs. Within multi-patch landscapes, 'outer' positions were patches that had no additional patches between them and the landscape footprint border. 'Inner' position patches were centrally located patches in the landscape.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Freely mobile (non-tethered) juvenile scallops of SH 43.1 ± 6.8 mm [mean ± SD] were placed at a consistent density (indiv. m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt;) across landscapes for three density survey trials, one each during June, July, and August 2019. Prior to each trial, landscapes were snorkeled to confirm that no scallops were present. Due to the isolation of these ASU landscapes and the general rarity of scallops on Oscar shoal, we were reasonably certain all scallops in these landscapes were purposefully placed there, meaning there was no immigration from other ASU landscapes or natural seagrass. For June and July trials, all scallops were collected from a natural seagrass meadow located across a deep boating channel from the experimental landscapes. During August, a mixture of scallops from two sources was used: from the nearby meadow, and NC-descendant scallops of similar size provided by VIMS ESL. Before scallop placement in landscapes, all scallops were stored in outdoor estuary-fed flow-through aquaria for up to two weeks. During June and July trials, scallops were placed in all 16 landscapes at an initial density of 1 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; (i.e., one per ASU), allowing for resolution in landscape treatment effects while maintaining relative comparability to natural conditions in our system (i.e., 0.6 scallops m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; in the nearby scallop-source meadow). By the conclusion of the July trial, landscapes along one shoal margin were becoming substantially buried under sediment due to wave/current action. Therefore, for the August trial the number of landscape treatment replicates was reduced to three to exclude the buried replicates, and a 1-patch landscape replicate was rebuilt in a calmer area of the shoal. In addition, during the August trial, the initial scallop density was increased to 2 m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; (i.e., two per ASU) to increase resolution among habitat treatments. Observers snorkel surveyed each landscape at 24 h, 48 h, and 72 h during each trail, except for the 48-h survey in June, which was canceled due to inclement weather. During each survey, observers recorded the number of scallops per ASU. On rare occasions when scallops were found on sand &amp;amp;lt;1 m from an ASU, their count was assigned to that nearest ASU, as they were likely still using the artificial seagrass mosaic as habitat.&amp;amp;nbsp;&amp;lt;br /&amp;gt;
&amp;lt;br /&amp;gt;
Depth note:&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;/p&amp;gt;

&amp;lt;p&amp;gt;Organism identifiers&amp;amp;nbsp;(common name, scientific name, LSID):&amp;lt;br /&amp;gt;
bay scallop, &amp;lt;em&amp;gt;Argopecten irradians&amp;lt;/em&amp;gt;, urn:lsid:marinespecies.org:taxname:156817&amp;lt;br /&amp;gt;
Tulip whelk,&amp;lt;em&amp;gt;Fasciolaria&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:138001&amp;lt;br /&amp;gt;
Knobbed whelk,&amp;lt;em&amp;gt;Busycon carica&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:160185&amp;lt;br /&amp;gt;
Horse conch,&amp;lt;em&amp;gt;Triplofusus papillosus auct.&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:448509&amp;lt;br /&amp;gt;
Moon snail,&amp;lt;em&amp;gt;Neverita duplicata&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:160407&amp;lt;br /&amp;gt;
Lightning whelk,&amp;lt;em&amp;gt;Sinistrofulgur sinistrum&amp;lt;/em&amp;gt;,urn:lsid:marinespecies.org:taxname:862934&amp;lt;/p&amp;gt;</gco:CharacterString>
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                  <gco:CharacterString>* Sheet &amp;quot;Data&amp;quot; of submitted file &amp;quot;Scallop_Density_2019.xlsx&amp;quot; were imported into the BCO-DMO data system for this dataset. Values &amp;quot;NA&amp;quot; imported as missing data values.
** In the BCO-DMO data system missing data identifiers are displayed according to the format of data you access. For example, in csv files it will be blank (null) values. In Matlab .mat files it will be NaN values. When viewing data online at BCO-DMO, the missing value will be shown as blank (null) values.

* Column names adjusted to conform to BCO-DMO naming conventions designed to support broad re-use by a variety of research tools and scripting languages. [Only numbers, letters, and underscores. Can not start with a number]

* DateTime with time zone column added &amp;quot;ISO_DateTime_UTC_In.&amp;quot; Converted from Date_In and Time_In (from local EST/EDT to UTC) converted to ISO 8601 format.

* Species names provided in email correspondence were added to the metadata for this dataset.  LSIDs added from World Register of Marine Species (WoRMS) matches on 2024-10-10.   &amp;quot;Triplofusus papillosus&amp;quot;  matched to &amp;quot;Triplofusus papillosus auct.&amp;quot;,urn:lsid:marinespecies.org:taxname:448509</gco:CharacterString>
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