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            <gco:CharacterString>Cite this dataset as: Hughes, A. R., Truskey, S. (2026) Oyster genetic assignment data from an experimental oyster reef restoration in Ninigret Pond, Rhode Island (USA) in 2017-2020. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2026-08-07 [if applicable, indicate subset used]. http://lod.bco-dmo.org/id/dataset/1004242 [access date]</gco:CharacterString>
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        <gco:CharacterString>Individual genetic assignments from hatchery samples and restored reefs Dataset Description:  Methods and Sampling: &amp;lt;p&amp;gt;These data were published in Truskey et al. 2025 (Evolutionary Applications). All figure numbers and supplementary materials mentioned refer to Truskey et al. 2025 (Evolutionary Applications).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Restoration experiment and sample collection&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;In April 2017, we collaborated with local oyster farmers to source oyster eyed-larvae from four commercial hatcheries for the construction of new experimental oyster reefs in Ninigret Pond (Charlestown, Rhode Island, USA). Hatchery sources were selected across a broad geographic sampling range to maximize diversity (Figure&amp;amp;nbsp;1a of Truskey et al. 2025). They included two regional hatcheries, one from Massachusetts (MA) and one from New York (NY), and two more distant hatcheries, one from Maine (ME) and one from Virginia (VA). A local Rhode Island hatchery facility received oyster eyed-larvae from each source hatchery, set the eyed-larvae on dead oyster and/or clam shell (hereafter referred to as spat-on-shell oysters), and distributed the spat-on-shell oysters to three local oyster growers (Grower 1: MA; Grower 2: ME, NY, VA; Grower 3: NY, VA) who maintained these juvenile oysters on separate leased oyster farm plots prior to reef construction. Immediately prior to reef construction, we collected 20 juvenile spat-on-shell oysters from each grower-hatchery source combination for genetic analysis (&amp;lt;em&amp;gt;n&amp;lt;/em&amp;gt; = 6 combinations; Grower 1-MA; Grower 2-ME; Grower 2-NY; Grower 2-VA; Grower 3-NY; Grower 3-VA).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;In October and November 2017, we constructed 16 subtidal reefs within a no-harvest Shellfish Management Area in Ninigret Pond. Reefs were created across four 0.025-acre experimental blocks, with four reefs per block (Figure&amp;amp;nbsp;2 of Truskey et al. 2025). Each reef consisted of a base layer of 0.25 cubic yards of dead oyster or clam shell deployed in October and topped with 1.25 cubic yards of spat-on-shell oysters in early November from the stock grown out by the local oyster growers. Our experiment was originally designed to seed three reefs per block with a different single hatchery source from the four available hatchery sources and to seed the fourth reef per block with a mixed combination of the three sources (e.g., Reef 1: ME, Reef 2: MA, Reef 3: NY, Reef 4: ME+MA+NY). However, analysis of the hatchery samples from oyster growers collected prior to reef construction revealed an early, unintended mixing of some of the sources (Appendix&amp;amp;nbsp;S1 of Truskey et al. 2025; Figure&amp;amp;nbsp;S1 of Truskey et al. 2025), resulting in mixtures of multiple sources on 12 out of the 16 constructed reefs. Thus, we focused our analyses on the actual genetic composition of each reef as determined by genetic sampling at two time points (fall 2018, fall 2020).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;In fall 2018, we haphazardly sampled live oysters from each reef on scuba or snorkel (&amp;lt;em&amp;gt;N&amp;lt;/em&amp;gt; = 512 individuals total, 32 per reef). Oysters were put on ice and transported to the Northeastern University Marine Science Center where they were held at −80°C until DNA extraction. By the fall of 2020, live oyster densities on all experimental reefs had declined, reflecting mortality of the original planted oysters and a lack of recruitment, consistent with other data from this system (Barrett et&amp;amp;nbsp;al.&amp;amp;nbsp;2024). To assess whether this mortality was associated with a consistent change in the genetic composition of surviving oysters on reefs, we repeated our sampling in fall 2020 and compared the resulting reef genetic profiles to those from fall 2018. Reef sample sizes varied at this time point due to low live abundances (&amp;lt;em&amp;gt;N&amp;lt;/em&amp;gt; = 249 individuals total, ranging from 8 to 32 per reef).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;DNA extraction, RADseq library preparation, and bioinformatics&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Genomic DNA was extracted using the E-Z 96 Tissue DNA Kit (Omega-Biotek, Norcross, GA) following the animal tissue protocol with tissue centrifugation. Double-digest restriction-site-associated DNA (ddRAD) libraries with individually barcoded samples were prepared in three batches following Parchman et al. (2012): (1) initial hatchery samples (n = 120), (2) fall 2018 reef samples (n = 480; 30 oysters per reef across 16 reefs), and (3) fall 2020 reef samples (n = 248). For additional details on ddRAD library preparation, see Appendix S2 of Truskey et al. 2025. All libraries were sequenced with 100-bp single-end reads on an Illumina platform. The initial and fall 2020 batches were sequenced on a single lane of the Illumina HiSeq 2500 at Tufts University Core Facility Genomics; the fall 2018 batch was sequenced on two lanes of the Illumina NovaSeq 6000 at the University of Texas at Austin Genomic Sequencing and Analysis Facility.&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/709941.rdf" xlink:title="OCE-1652320" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1652320 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1652320</gmx:Anchor>
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	Name: ind_id
	Units: unitless
	Description: &lt;p&gt;Unique identifier for each individual oyster. This identifier corresponds to the associated FASTQ sequence file name&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004407.rdf
	Name: sampling_group
	Units: unitless
	Description: &lt;p&gt;Indicator for whether an individual was sampled from either an experimental reef or pre-reef construction from an initial hatchery group&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004408.rdf
	Name: yearcoll
	Units: unitless
	Description: &lt;p&gt;Year and season of sample collection (e.g., F2018 = Fall 2018, F2020 = Fall 2020, Init = hatchery-sourced samples taken before reef deployment)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004409.rdf
	Name: reef
	Units: unitless
	Description: &lt;p&gt;For reef samples only. Restored reef from which an individual was collected. Letter refers to experimental block and number refers to the reef number within a block (e.g., D3)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004410.rdf
	Name: block
	Units: unitless
	Description: &lt;p&gt;Experimental block in which a restored reef was situated (A - D)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004411.rdf
	Name: grower
	Units: unitless
	Description: &lt;p&gt;For initial hatchery samples only. Oyster grower that provided the grown-out hatchery-source sample (e.g., Grower1, Grower3)&lt;/p&gt; 
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	Description: &lt;p&gt;For initial hatchery samples only. Original source hatchery ID as provided by oyster grower labels, corresponding to the state of origin of the respective hatcheries (e.g., NY, MA, VA, ME). *asterisk denotes a source that is likely mislabelled; see Problems/Issues section for details on the unintended mixing of hatchery-sourced samples prior to reef construction&lt;/p&gt; 
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	Units: unitless
	Description: &lt;p&gt;For initial hatchery samples only. Combined identifier for oyster grower and original source hatchery label (e.g., Grower1_MA). *asterisk denotes a source that is likely mislabelled; see Problems/Issues section for details on the unintended mixing of hatchery-sourced samples prior to reef construction.&lt;/p&gt; 
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	Name: library
	Units: unitless
	Description: &lt;p&gt;RADseq library batch in which an individual was processed and sequenced&lt;/p&gt; 
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	Description: &lt;p&gt;Assigned genetic cluster for an individual using the primary genetic assignment set applied to all main text analyses (DAPC approach, SNP set filtered for MAF &amp;gt; 0.01, LD pruning, and Fall 2020 missing data). Label names correspond to the state of origin of the hatchery source associated with a given genetic cluster (gME, gMA, gNY, gVA)&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.01 and pruned for LD&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.01 and pruned for Fall 2020 missing data&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.01&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004419.rdf
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	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.025, pruned for LD and Fall 2020 missing data&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004420.rdf
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	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.025 and pruned for LD&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004421.rdf
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	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.025 and pruned for Fall 2020 missing data&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004422.rdf
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	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.025&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004423.rdf
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	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.05, pruned for LD and Fall 2020 missing data&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004424.rdf
	Name: dapc_assigned_genetic_cluster_g90maf05_ldprunedrsq05
	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.05 and pruned for LD&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004425.rdf
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	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.05 and pruned for Fall 2020 missing data&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004426.rdf
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	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using DAPC approach with SNP set filtered for MAF &amp;gt; 0.05&lt;/p&gt; 
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	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.01, pruned for LD and Fall 2020 missing data&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.01 and pruned for LD&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.01 and pruned for Fall 2020 missing data&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.01&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.025, pruned for LD and Fall 2020 missing data&lt;/p&gt; 
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	Name: snmf_primary_ancestry_cluster_g90maf025_ldprunedrsq05
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.025 and pruned for LD&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.025 and pruned for Fall 2020 missing data&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/1004434.rdf
	Name: snmf_primary_ancestry_cluster_g90maf025
	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.025&lt;/p&gt; 
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	Name: snmf_primary_ancestry_cluster_g90maf05_g20f2020_ldprunedrsq05
	Units: unitless
	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.05, pruned for LD and Fall 2020 missing data&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.05 and pruned for LD&lt;/p&gt; 
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	Description: &lt;p&gt;Individual genetic cluster assignments using sNMF approach with SNP set filtered for MAF &amp;gt; 0.05 and pruned for Fall 2020 missing data&lt;/p&gt; 
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                <gco:CharacterString>&amp;lt;p&amp;gt;These data were published in Truskey et al. 2025 (Evolutionary Applications). All figure numbers and supplementary materials mentioned refer to Truskey et al. 2025 (Evolutionary Applications).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Restoration experiment and sample collection&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;In April 2017, we collaborated with local oyster farmers to source oyster eyed-larvae from four commercial hatcheries for the construction of new experimental oyster reefs in Ninigret Pond (Charlestown, Rhode Island, USA). Hatchery sources were selected across a broad geographic sampling range to maximize diversity (Figure&amp;amp;nbsp;1a of Truskey et al. 2025). They included two regional hatcheries, one from Massachusetts (MA) and one from New York (NY), and two more distant hatcheries, one from Maine (ME) and one from Virginia (VA). A local Rhode Island hatchery facility received oyster eyed-larvae from each source hatchery, set the eyed-larvae on dead oyster and/or clam shell (hereafter referred to as spat-on-shell oysters), and distributed the spat-on-shell oysters to three local oyster growers (Grower 1: MA; Grower 2: ME, NY, VA; Grower 3: NY, VA) who maintained these juvenile oysters on separate leased oyster farm plots prior to reef construction. Immediately prior to reef construction, we collected 20 juvenile spat-on-shell oysters from each grower-hatchery source combination for genetic analysis (&amp;lt;em&amp;gt;n&amp;lt;/em&amp;gt; = 6 combinations; Grower 1-MA; Grower 2-ME; Grower 2-NY; Grower 2-VA; Grower 3-NY; Grower 3-VA).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;In October and November 2017, we constructed 16 subtidal reefs within a no-harvest Shellfish Management Area in Ninigret Pond. Reefs were created across four 0.025-acre experimental blocks, with four reefs per block (Figure&amp;amp;nbsp;2 of Truskey et al. 2025). Each reef consisted of a base layer of 0.25 cubic yards of dead oyster or clam shell deployed in October and topped with 1.25 cubic yards of spat-on-shell oysters in early November from the stock grown out by the local oyster growers. Our experiment was originally designed to seed three reefs per block with a different single hatchery source from the four available hatchery sources and to seed the fourth reef per block with a mixed combination of the three sources (e.g., Reef 1: ME, Reef 2: MA, Reef 3: NY, Reef 4: ME+MA+NY). However, analysis of the hatchery samples from oyster growers collected prior to reef construction revealed an early, unintended mixing of some of the sources (Appendix&amp;amp;nbsp;S1 of Truskey et al. 2025; Figure&amp;amp;nbsp;S1 of Truskey et al. 2025), resulting in mixtures of multiple sources on 12 out of the 16 constructed reefs. Thus, we focused our analyses on the actual genetic composition of each reef as determined by genetic sampling at two time points (fall 2018, fall 2020).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;In fall 2018, we haphazardly sampled live oysters from each reef on scuba or snorkel (&amp;lt;em&amp;gt;N&amp;lt;/em&amp;gt; = 512 individuals total, 32 per reef). Oysters were put on ice and transported to the Northeastern University Marine Science Center where they were held at −80°C until DNA extraction. By the fall of 2020, live oyster densities on all experimental reefs had declined, reflecting mortality of the original planted oysters and a lack of recruitment, consistent with other data from this system (Barrett et&amp;amp;nbsp;al.&amp;amp;nbsp;2024). To assess whether this mortality was associated with a consistent change in the genetic composition of surviving oysters on reefs, we repeated our sampling in fall 2020 and compared the resulting reef genetic profiles to those from fall 2018. Reef sample sizes varied at this time point due to low live abundances (&amp;lt;em&amp;gt;N&amp;lt;/em&amp;gt; = 249 individuals total, ranging from 8 to 32 per reef).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;DNA extraction, RADseq library preparation, and bioinformatics&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Genomic DNA was extracted using the E-Z 96 Tissue DNA Kit (Omega-Biotek, Norcross, GA) following the animal tissue protocol with tissue centrifugation. Double-digest restriction-site-associated DNA (ddRAD) libraries with individually barcoded samples were prepared in three batches following Parchman et al. (2012): (1) initial hatchery samples (n = 120), (2) fall 2018 reef samples (n = 480; 30 oysters per reef across 16 reefs), and (3) fall 2020 reef samples (n = 248). For additional details on ddRAD library preparation, see Appendix S2 of Truskey et al. 2025. All libraries were sequenced with 100-bp single-end reads on an Illumina platform. The initial and fall 2020 batches were sequenced on a single lane of the Illumina HiSeq 2500 at Tufts University Core Facility Genomics; the fall 2018 batch was sequenced on two lanes of the Illumina NovaSeq 6000 at the University of Texas at Austin Genomic Sequencing and Analysis Facility.&amp;lt;/p&amp;gt;</gco:CharacterString>
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                        <gco:CharacterString>Specified by the Principal Investigator(s)</gco:CharacterString>
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;SNP calling, filtering, and defining datasets&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Raw sequence quality was assessed with FastQC v0.11.9 (Andrews 2010), and files were demultiplexed using the process_radtags function in STACKS v2.41 (Catchen et al. 2013). Read trimming, mapping, SNP calling, and genotyping were performed with the dDocent pipeline v2.9.4 (Puritz et al. 2014), with reads mapped to the &amp;lt;em&amp;gt;C. virginica&amp;lt;/em&amp;gt; genome pruned for haplotigs (Puritz et al. 2024). Variant calling was performed using Freebayes v1.3.6 (Garrison and Marth 2012). SNP loci were then filtered using vcftools v0.1.16 (Danecek et al. 2011) following standard iterative quality filtering procedures for RADseq-generated SNP data (O'Leary et al. 2018), including filters for minor allele count, base quality, genotype call rate, and read depth, followed by individual-level filtering for missing data. Because genetic assignment approaches can be sensitive to the SNP dataset used, we generated 12 SNP sets varying in minor allele frequency (MAF) threshold, locus-level filtering for missingness specific to the fall 2020 library, and pruning for high linkage disequilibrium (LD), to evaluate the robustness of downstream genetic cluster assignments to these bioinformatic decisions. Filtering outcomes for each SNP set are detailed in Table S1 of Truskey et al. 2025.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Individual genetic assignments&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Individual genetic assignments to one of four genetic clusters (K = 4) were generated using discriminant analysis of principal components (DAPC; adegenet v2.1.10, Jombart 2008) and sparse non-negative matrix factorization (sNMF; LEA v3.10.0, Frichot and Francois 2015), applied independently to each of the 12 SNP sets, yielding 24 genetic assignment sets in total. Both approaches supported an optimal K = 4 (Figures S3-S4 of Truskey et al. 2025). For sNMF, individual assignments reflect the single cluster assignment with the highest admixture coefficient under K = 4. The primary genetic assignment referred to in the dataset and used in downstream analyses reflects DAPC assignments from the LD-pruned SNP set filtered for MAF &amp;amp;gt; 0.01 and fall 2020 library-specific missingness. Additional details on DAPC and sNMF runs and outcomes are provided in Appendix S3 of Truskey et al. 2025.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The individuals presented in this dataset are those retained after SNP filtering steps and not sampled from single-source reefs at the start of the experiment in fall 2018 as reflected by the individual genetic assignments. Genetic assignments for all individuals retained after SNP filtering (n=803), including those from single-source fall 2018 reefs, are provided in the related Sequence Metadata dataset.&amp;lt;/p&amp;gt;</gco:CharacterString>
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