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2,785 results for “genotyping”

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zenodo32/100

FIGURE 41 in A revision of the genus Lepidobrya Womersley (Collembola: Entomobryidae) based on morphology and sequence data of the genotype

FIGURE 41. Abundance in numbers per trap day of Lepidobrya mawsoni on Macquarie Island from December 1992 until December 1993.

opennotspecifiedDec 2017View details →
zenodo32/100

Dataset from 'Billino,J., Hennig, J., & Gegenfurtner K.R. (2016). Association between COMT genotype and the control of memory guided saccades: Individual differences in healthy adults reveal a detrimental role of dopamine. Vision Research. doi: 10.1016/j.visres.2016.10.001'

<p>Dataset associated with the following publication:</p> <p>Billino,J., Hennig, J., &amp; Gegenfurtner K.R. (2016). Association between COMT genotype and the control of memory guided saccades: Individual differences in healthy adults reveal a detrimental role of dopamine. Vision Research. doi: 10.1016/j.visres.2016.10.001 <span><a></a></span></p> <p>--------------------------------------------------------------</p> <p>The folder contains 4 data files and 1 description file  providing column labels.<br> The data file 'maindata.txt' contains the complete dataset including all analyzed parameters.<br> The data file 'accuracybydelay.txt' contains accuracy data across delay conditions, providing the dataset for Figure 3A.<br> The data file 'accuracybyamplitude.txt' contains accuracy data across target amplitude conditions, providing the dataset for Figure 3B.<br> The data file 'singlesublanding.txt' contains landing positions of primary memory guided saccades from three subjects of different genotype groups, providing the dataset for Figure 3C.</p> <p>-------------------------------------------------------------</p> <p>For further questions, please contact:<br> jutta.billino[at]psychol.uni-giessen.de</p>

opencc-by-4.0Oct 2016View details →
zenodo32/100

Locityper loci database, 1KGP genotypes and benchmarking data

Open the record for dataset details and reuse information.

opencc-by-4.0May 2024View details →
dryad32/100

Genotype likelihoods for low-coverage whole-genome sequencing data of yellow warblers

<p>The following datasets include the required input files used to empirically test population assignment in WGSassign on Yellow Warbler data. The file "yewa.known.ind105.ds_2x.beagle.gz" includes the filtered variants of 105 Yellow Warbler individuals output as genotype likelihoods and stored in a Beagle-formatted file. The ID file, "yewa.known.ind105.reference.IDs.txt", is a tab-delimited file with 2 columns, the first being the sample ID, and the second being the known reference population. The sample order in the ID file should match that of the input beagle file. To measure the assignment accuracy of WGSassign, we used leave-one-out cross validation using the input beagle file and our ID file.</p>

opencc-zeroJan 2024View details →
zenodo32/100

Contribution of parasite and host genotype to immunopathology of schistosome infections

<p>The present dataset contains all the phenotype data (.csv files) and R scripts used for data analysis and generation of figures (Fig. 2-6) present in the manuscript entitled "Contribution of parasite and host genotype to immunopathology of schistosome infections."</p>

opencc-by-4.0Dec 2023View details →
zenodo32/100

Iranian Sheep Genotypes

Open the record for dataset details and reuse information.

opencc-by-4.0Mar 2024View details →
zenodo32/100

Defensive symbiont genotype distributions are linked to parasitoid attack networks - Dataset and scripts

<p>This R project includes data and scripts for paper - Defensive symbiont genotype distributions are linked to parasitoid attack networks</p> <p>Script for analysis:</p> <p>&nbsp; &nbsp; Run all the scripts in order, to get all analyses and results in this paper.&nbsp;</p> <p>&nbsp; &nbsp; Script_0_package_install_load.R:&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Installs and loads the necessary R packages required for all subsequent scripts.<br>&nbsp; &nbsp; &nbsp; &nbsp; This R project</p> <p>&nbsp; &nbsp; Script_1_Extract_from_Table_S2.R<br>&nbsp; &nbsp; &nbsp; &nbsp; Extracts information from:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Table_S2.csv (located in /Rawdata/) &nbsp; &nbsp;Data_4_Aphid_sequences.fas<br>&nbsp; &nbsp; &nbsp; &nbsp; Generates 10 files for further analyses:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid relatedness distance:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid_phylogenetic_relatedness_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid_phylogenetic_relatedness_22species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid_phylogenetic_relatedness_31species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella - Aphid Matrices:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella_Aphid_matrix_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella_Aphid_matrix_22species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella_Aphid_matrix_31species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Parasitoid - Aphid Matrices:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Para_Aphid_matrix_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Para_Aphid_matrix_22species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Plant - Aphid Matrices:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Plant_Aphid_matrix_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Plant_Aphid_matrix_31species.csv</p> <p><br>&nbsp; &nbsp; Script_2_BarPlot_Fig1.R:&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Generates Fig. 1 using:&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Data_11_Parasitoid_genus_aphid_22_species_Fig.1.csv &nbsp;Data_12_Plant_genus_aphid_31_species_Fig.1.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; The bar order in Fig. 1 is arranged by proportion, which is not directly supported in the ggplot2 package in R. Therefore, we need manually reordered if using the first plot code; or, manually colour it using the second plot code.&nbsp;</p> <p><br>&nbsp; &nbsp; Script_3_MMRR_analysis.R<br>&nbsp; &nbsp; &nbsp; &nbsp; Uses 10 distance/distribution matrices of Parasitoid, Plant, Hamiltonella, and Aphid relationships to compute matrix correlations with the MMRR (Multiple Matrix Regression with Randomization) model.</p> <p><br>&nbsp; &nbsp; Script_4_Species_linkage_Fig2_FigS4.R<br>&nbsp; &nbsp; &nbsp; &nbsp; Uses 7 distribution matrices of Parasitoid, Plant, and Hamiltonella relationships with Aphids (excluding Aphid genetic distance matrices) to generate the species linkage diagrams for Fig. 2 and Fig. S4, For aesthetic purposes, unconnected sample points have been moved.</p> <p><br>&nbsp; &nbsp; Script_5_MMRR_Fig3_FigS5.R<br>&nbsp; &nbsp; &nbsp; &nbsp; Plots the MMRR correlations using the 10 distance/distribution matrices for Parasitoid, Plant, Hamiltonella, and Aphid relationships (Fig. 3 &amp; Fig. S5).&nbsp;</p> <p>&nbsp; &nbsp; Script_6_parasitoid_specialization_Fig4.R<br>&nbsp; &nbsp; &nbsp; &nbsp; Computes specialization levels using the H2 Index for:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Parasitoid-Aphid<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid-Hamiltonella<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Parasitoid-Hamiltonella relationships&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Generates Figure 4.</p> <p>&nbsp; &nbsp; Script_7_Ecologicial_indices&amp;plots_Table1_FigS3.R<br>&nbsp; &nbsp; &nbsp; &nbsp; Uses 7 distribution matrices of Parasitoid, Plant, and Hamiltonella relationships with Aphids (excluding Aphid genetic distance matrices) to:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Calculate ecological indices (Richness, Shannon Index, Simpson Index).<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Use linear models to analyze the relationships between Parasitoid/Plant-Aphid and Aphid-Hamiltonella communities. &nbsp;&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Outputs results for Table 1 and Figure S3.</p> <p><br>&nbsp; &nbsp; Script_8_Bubble_plot_FigS2.R<br>&nbsp; &nbsp; &nbsp; &nbsp; This script using&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella_Aphid_matrix_31species.csv&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; and two phylogeny trees&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Data_8_Aphid_species_phylogeny.txt &amp;&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Data_9_Hamiltonella_phylogeny.txt<br>&nbsp; &nbsp; &nbsp; &nbsp; To create a Cophylogeny tree of Hamiltonella strains and aphid species that we identified in this study and previously known strains. (Fig. S2)</p> <p>&nbsp; &nbsp; Script_9_DADA2_pipeline.R<br>&nbsp; &nbsp; &nbsp; &nbsp; This script is the DADA2 pipeline used to processing the raw COI sequencing data into ASV (Amplicon Sequence Variant) count files. After processing, the ASV files required manual curation to link each ASV with a distinct parasitoid and aphid species name based on BLAST results. In our updated version, we have provided both the raw data (BioProject PRJNA1139364) as well as the manually curated files (Data_1 and Data_2) which includes the ASV species names. All subsequent analyses can be reproduced using the curated datasets (Data_1 and Data_2), ensuring clarity and replicability for users.<br>&nbsp; &nbsp; &nbsp; &nbsp; We have incorporated the SRA Toolkit to streamline the process. This allows users to download raw SRR sequencing files directly and convert them into FASTQ files, which can then be input into the DADA2 pipeline. The pipeline produces two ASV count files, one for each sequencing run.</p> <p>&nbsp;</p> <p>Raw data and inofrmation:</p> <p>&nbsp; &nbsp; Table_S2.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; The Dataset from Supplementary Table S2: After manual pooling the Parasitoid/Aphid species based on the Data_1,2 and 6.<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; No: the number of this sample<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; City: The city that collected this sample<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Location: the location of sample collection<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Sample category: Aphid mummies or alive aphids<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Sample code: the name of sample (self defined)<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Collection year: when this sample was collected<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid taxa / Wasp taxa / Plant species /Hamiltonella strain: The Aphid/Parasitoid/Plant/Hamiltonella species&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Sequencing method: Illumina or Sanger sequencing &nbsp;&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Sequencing date: the date of sending this sample to sequencing<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Data source: From this study or from Wu et al. 2022: Local adaptation to hosts and parasitoids shape Hamiltonella defensa genotypes across aphid species</p> <p>&nbsp; &nbsp; Data_1_Deep_sequencing_data_block_1.xlsx &amp; Data_2_Deep_sequencing_data_block_2.xlsx&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Sample: The sample name from Illumina sequencing, which can later be found on GenBank (BioProject PRJNA1139364).<br>&nbsp; &nbsp; &nbsp; &nbsp; Aphid: The detected aphid species for each sample.<br>&nbsp; &nbsp; &nbsp; &nbsp; Parasitoid: The detected parasitoid species.<br>&nbsp; &nbsp; &nbsp; &nbsp; The remaining columns contain ASV (Amplicon Sequence Variant) data derived from high-throughput barcoding sequencing.<br>&nbsp; &nbsp; &nbsp; &nbsp; Data1 and Data_2 are the manually curated versions of the BioProject PRJNA1139364 with added species names for each ASV.&nbsp;</p> <p>&nbsp; &nbsp; Data_3_Parasitoid sequences.fas &amp;&nbsp;<br>&nbsp; &nbsp; Data_4_Aphid sequences.fas &amp;&nbsp;<br>&nbsp; &nbsp; Data_5_Hamiltonella sequences.fas,<br>&nbsp; &nbsp; &nbsp; &nbsp; FASTA files for:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Parasitoid species<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid species<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella strains<br>&nbsp; &nbsp; &nbsp; &nbsp; These sequences were used for phylogenetic reconstruction and subsequent analyses.</p> <p>&nbsp; &nbsp; Data_6_Parasitoid_Aphid_pooled_table.xlsx&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Contains the OTU (Operational Taxonomic Unit) manual pooling results for Parasitoid and Aphid species based on 99% (4 base pair) sequence similarity:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Parasitoid pooling together group &amp; Aphid pooling together group: Original names from Illumina sequencing.<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Original name: Representative sequences for each group.<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Pooled species name: Final species names used in all analyses.<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Pooled sequences: Final representative sequences used in all analyses.<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; The result of manual pooling see the Table_S2.csv</p> <p>&nbsp; &nbsp; Data_7_Parasitoid_species_phylogeny.txt &amp; Data_8_Aphid_species_phylogeny.txt &amp; Data_9_Hamiltonella_phylogeny.txt&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Phylogenetic trees for:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Parasitoid species<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Aphid species<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella strains<br>&nbsp; &nbsp; &nbsp; &nbsp; These trees were generated using the PhyML tool on the ATGC Montpellier platform, original fasta file was Data_3, 4 &amp; 5.</p> <p>&nbsp; &nbsp; Data_10_aphid_host_info.csv&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Provides aphid host information for generating Figure 2 and Figure S4:<br>&nbsp; &nbsp; &nbsp; &nbsp; Aphid: Names of aphid species included in this study.<br>&nbsp; &nbsp; &nbsp; &nbsp; Host: Host categories:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; 1: Herb aphids<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; 2: Grass aphids<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; 3: Tree aphids<br>&nbsp; &nbsp; &nbsp; &nbsp; Host_category: Detailed descriptions of host categories.</p> <p>&nbsp; &nbsp; Data_11_Parasitoid_genus_aphid_22_species_Fig.1.csv &amp; Data_12_Plant_genus_aphid_31_species_Fig.1.csv&nbsp;<br>&nbsp; &nbsp; &nbsp; &nbsp; Reduced matrices used for Figure 1, created by merging data from:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; OTUs associated with the same parasitoid species.<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Plant species belonging to the same genus.</p> <p>&nbsp; &nbsp; 7 Distribution Matrices (from Script_1_Extract_from_Table_S2.R)<br>&nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella-Aphid Matrices:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp;Hamiltonella_Aphid_matrix_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella_Aphid_matrix_22species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Hamiltonella_Aphid_matrix_31species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; Parasitoid-Aphid Matrices:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Para_Aphid_matrix_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Para_Aphid_matrix_22species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; Plant-Aphid Matrices:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Plant_Aphid_matrix_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Plant_Aphid_matrix_31species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; Structure:<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Rows represent aphid species.<br>&nbsp; &nbsp; &nbsp; &nbsp; &nbsp; &nbsp; Columns represent Hamiltonella strains, parasitoid species, or host plant species linked to each aphid species.<br>&nbsp; &nbsp; &nbsp; &nbsp; Usage: These matrices were used to generate Figures 2, 3, 4, Figures S2, S3, S4, S5, and for MMRR tests, ecological indices, and H2 index calculations.</p> <p>&nbsp; &nbsp; 3 Aphid phylogenetic relatedness matrices derived from Script_1_Extract_from_Table_S2.R<br>&nbsp; &nbsp; &nbsp; &nbsp; Aphid_phylogenetic_relatedness_16species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; Aphid_phylogenetic_relatedness_22species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; Aphid_phylogenetic_relatedness_31species.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; These matrices provide phylogenetic distance information, showing pairwise genetic distances between the 31 aphid species included in this study.</p> <p>&nbsp; &nbsp; SraRunTable.csv<br>&nbsp; &nbsp; &nbsp; &nbsp; The BioProject (PRJNA1139364) information downloaded directly from Genbank.&nbsp;</p>

opencc-by-4.0Jul 2024View details →
dryad32/100

Genotyping validates the efficacy of photographic identification in a capture-mark-recapture study based on the head scale patterns of the prairie lizard (Sceloporus consobrinus)

Population studies often incorporate capture-mark-recapture (CMR) techniques to gather information on long-term biological and demographic characteristics. A fundamental requirement for CMR studies is that an individual must be uniquely and permanently marked to ensure reliable reidentification throughout its lifespan. Photographic identification involving automated photographic identification software has become a popular and efficient non-invasive method for identifying individuals based on natural markings. However, few studies have a) robustly assessed the performance of automated programs by using a double-marking system or b) determined their efficacy for long-term studies by incorporating multi-year data. Here, we evaluated the performance of the program Interactive Individual Identification System (I<sup>3</sup>S) by cross-validating photographic identifications based on the head scale pattern of the prairie lizard (<i>Sceloporus consobrinus</i>) with individual microsatellite genotyping (N=863). Further, we assessed the efficacy of the program to identify individuals over time by comparing error rates between within-year and between-year recaptures. Recaptured lizards were correctly identified by I<sup>3</sup>S in 94.1% of cases. We estimated a false rejection rate (FRR) of 5.9% and a false acceptance rate (FAR) of 0%. By using I<sup>3</sup>S we correctly identified 97.8% of within-year recaptures (FRR=2.2%; FAR=0%) and 91.1% of between-year recaptures (FRR=8.9%; FAR=0%). Misidentifications were primarily due to poor photo quality (N=4). However, two misidentifications were caused by indistinct scale configuration due to scale damage (N=1) and ontogenetic changes in head scalation between capture events (N=1). We conclude that automated photographic identification based on head scale patterns is a reliable and accurate method for identifying individuals over time. Because many lizard or reptilian species possess variable head squamation, this method has potential for successful application in many species.

opencc-zeroNov 2021View details →
dryad32/100

Strong genotype-by-genotype interactions between aphid-defensive symbionts and parasitoids persist across different biotic environments

<p><span><span><span><span><span><span><span><span><span><span><span>The dynamics of coevolution between hosts and parasites are influenced by their genetic interactions. Highly specific interactions, where the outcome of an infection depends on the precise combination of host and parasite genotypes (G × G interactions), have the potential to maintain genetic variation by inducing negative frequency-dependent selection. The importance of this effect also rests on whether such interactions are consistent across different environments or modified by environmental variation (G × G × E interaction). In the black bean aphid, <i>Aphis fabae</i>, resistance to its parasitoid <i>Lysiphlebus fabarum</i> is largely determined by the possession of a heritable bacterial endosymbiont, <i>Hamiltonella defensa</i>, with strong G × G interactions between <i>H. defensa</i> and <i>L. fabarum</i>. A key environmental factor in this system is the host plant on which the aphid feeds. Here, we exposed genetically identical aphids harbouring three different strains of <i>H. defensa</i> to three asexual genotypes of <i>L. fabarum </i>and measured parasitism success on three common host plants of <i>A. fabae</i>, namely <i>Vicia faba</i>, <i>Chenopodium album</i> and <i>Beta vulgaris</i>. As expected, we observed the pervasive G × G interaction between <i>H. defensa</i> and <i>L. fabarum</i>, but despite strong main effects of the host plants on average rates of parasitism, this interaction was not altered significantly by the host plant environment (no G × G × E interaction). The symbiont-conferred specificity of resistance is thus likely to mediate the coevolution of <i>A. fabae </i>and <i>L. fabarum</i>, even when played out across diverse host plants of the aphid.</span></span></span></span></span></span></span></span></span></span></span></p>

opencc-zeroNov 2021View details →
dryad32/100

A method for identifying environmental stimuli and genes responsible for genotype-by-environment interactions from a large-scale multi-environment data set

<p>It has not been fully understood in real fields what environment stimuli cause the genotype-by-environment (G × E) interactions, when they occur, and what genes react to them. Large-scale multi-environment data sets are attractive data sources for these purposes because they potentially experienced various environmental conditions. In this study, we developed a data-driven approach termed <u>E</u>nvironmental <u>C</u>ovariate Search Affecting <u>G</u>enetic <u>C</u>orrelations (ECGC) to identify environmental stimuli and genes responsible for the G × E interactions from large-scale multi-environment data sets. ECGC was applied to a soybean (<i>Glycine max</i>) data set that consisted of 25,158 records collected at 52 environments. ECGC illustrated what meteorological factors shaped the G × E interactions in six traits including yield, flowering time, and protein content and when they were involved. For example, it illustrated the relevance of precipitation around sowing dates and hours of sunshine just before maturity to the interactions observed for yield. Moreover, genome-wide association mapping on the sensitivities to the identified stimuli discovered candidate and known genes responsible for the G × E interactions. Our results demonstrate the capability of data-driven approaches to bring novel insights on the G × E interactions observed in fields. This dataset provides the data used in this study and supplementary tables cited in the manuscript.</p>

opencc-zeroDec 2021View details →
dryad32/100

Transgenerational plasticity of dispersal-related traits in a ciliate: genotype-dependency and fitness consequences

<p>The data presented here are those used in the paper : CAYUELA H., JACOB S., SCHTICKZELLE N., VERDONCK R., PHILIPPE H., LAPORTE M., HUET M., BERNATCHEZ L., LEGRAND D. Transgenerational plasticity of dispersal-related traits in a ciliate: genotype-dependency and fitness consequences. Oikos. DOI: 10.1111/oik.08846</p> <p>Phenotypic plasticity, the ability of one genotype to produce different phenotypes in different environments, plays a central role in species' response to environmental changes. Transgenerational plasticity (TGP) allows the transmission of this environmentally-induced phenotypic variation across generations, and can influence adaptation. To date, the genetic control of TGP, its long-term stability, and its potential costs remain largely unknown, mostly because empirical demonstrations of TGP across many generations in several genetic backgrounds are scarce. In the paper of Cayuela et al., we examined how genotype determines the TGP of phenotypic traits related to dispersal, a fundamental process in ecology and evolution. We used an experimental approach in <i>Tetrahymena thermophila</i>, a ciliate model-species, to determine if and how phenotypic changes expressed following a dispersal treatment are inherited over multiple generations. The data include morphological and movement traits, dispersal rates, and cell growth data measured before and after dispersal trials. We considered different genotypes and different populations within each genotype.</p>

opencc-zeroJan 2022View details →
dryad32/100

Data from: Genome-wide sequence-based genotyping supports a nonhybrid origin of Castanea alabamensis

<p>The genus Castanea in North America contains multiple tree and shrub taxa of conservation concern. The two species within the group, American chestnut (Castanea dentata) and chinquapin (C. pumila sensu lato), display remarkable morphological diversity across their distributions in the eastern United States and southern Ontario. Previous investigators have hypothesized that hybridization between C. dentata and C. pumila has played an important role in generating morphological variation in wild populations. A putative hybrid taxon, Castanea alabamensis, was identified in northern Alabama in the early 20th century; however, the question of its hybridity has been unresolved. We tested the hypothesized hybrid origin of C. alabamensis using genome-wide sequence-based genotyping of C. alabamensis, all currently recognized North American Castanea taxa, and two Asian Castanea species at &gt;100,000 single-nucleotide polymorphism (SNP) loci. With these data, we generated a high-resolution phylogeny, tested for admixture among taxa, and analyzed population genetic structure of the study taxa. Bayesian clustering and principal components analysis provided no evidence of admixture between C. dentata and C. pumila in C. alabamensis genomes. Phylogenetic analysis of genome-wide SNP data indicated that C. alabamensis forms a distinct group within C. pumila sensu lato. Our results are consistent with the model of a nonhybrid origin for C. alabamensis. Our finding of C. alabamensis as a genetically and morphologically distinct group within the North American chinquapin complex provides further impetus for the study and conservation of the North American Castanea species.</p>

opencc-zeroFeb 2022View details →
dryad32/100

Screening coffee genotypes for brown eye spot resistance in Brazil

<p><span>Several researchers have attempted to develop coffee plants that are resistant to brown eye spot (BES); however, no coffee cultivars are resistant to the disease. In the present study, a blend of strains from <i>Cercospora coffeicola </i>was inoculated into 19 Brazilian commercial cultivars and 41 accessions from the Germplasm Collection of Minas Gerais to evaluate the genetic resistance ability within the population and select superior genotypes for the breeding program. After predicting the genotypic values of the studied material, the evaluations number necessary for selecting genotypes with accuracy and efficiency was determined based on the data of severity to BES. The action of defense mechanisms plant was also investigated by assessing the levels of total soluble phenolic compounds and soluble lignin in contrasting genotypes for disease susceptibility. Based on the results, the accession MG 1207 Sumatra, had an intrinsic genetic capacity to maintain low levels of severity to BES.  The genotype MG 1207 Sumatra can substantially contribute to the development of new cultivars, which may lead to the reduced use of pesticides. According to the accuracy and efficiency results obtained, four evaluations BES severity are sufficient to achieve accuracy, providing expressive genetic gains. Finally, the levels of lignin and phenolic compounds were not found to be associated with the resistance of coffee genotypes to BES.</span></p>

opencc-zeroFeb 2022View details →
dryad32/100

SNP genotypes for healthy and CIM-affected GSDs

<p>German shepherd dogs (GSDs) are predisposed to an inherited motility disorder of the esophagus, termed congenital idiopathic megaesophagus (CIM), in which swallowing is ineffective and the esophagus is enlarged. Affected puppies are unable to properly pass food into their stomachs and consequently regurgitate their meals and show a failure to thrive, often leading to euthanasia. Here, we generated genome-wide SNP profiles for healthy and CIM-affected GSDs using the Illumina CanineHD BeadChip, containing 220,853 SNPs.</p>

opencc-zeroFeb 2022View details →
dryad32/100

Association of physical activity and APOE genotype with longitudinal cognitive change in early PD

<p><b>Objective:</b> To determine whether greater physical activity could modify the negative association of <i>APOE</i> <span>ε4 with longitudinal cognitive changes in early Parkinson's disease (PD) and to uncover the disease-specific mechanism for </span>explaining such benefits of physical activity<span>.</span></p> <p><b>Methods:</b> We used data from the Parkinson's Progression Markers Initiative cohort. Because self-reported physical activity, measured by the Physical Activity Scale of the Elderly, was initiated at 2 years after enrollment, this longitudinal analysis was based on assessments performed at years 2, 3, and 4. Cognitive function was measured annually with the Montreal Cognitive Assessment (MoCA). Dopamine transporter (DAT) imaging was performed at years 2 and 4. We assessed the interactive associations between physical activity and the <i>APOE</i> ε4 allele on the longitudinal changes in MoCA scores and striatal DAT activities.</p> <p><b>Results:</b> A total of 173 early PD patients (age 63.3±10.0 years; 27% <i>APOE</i> ε4 <span>carriers</span>) were included. The <i>APOE</i> ε4 allele showed a steeper rate of cognitive decline than the non-<i>APOE</i> ε4 allele (estimate -1.33; 95% CI, -2.12 to -0.47; <i>p</i>=0.002). However, there was a significant interaction between physical activity and <i>APOE</i> ε4, such that higher physical activity was related to slower <i>APOE</i> ε4-related cognitive decline (estimate 0.007; 95% CI, 0.003 to 0.011; <i>p</i>=0.001). No<span> significant interaction was found between physical activity and the <i>APOE</i> ε4 allele regarding the change in striatal DAT activities.</span></p> <p><span><span><b>Conclusion:</b> Increased physical activity attenuated <i>APOE</i> ε<span>4</span>-related vulnerability to early cognitive decline in PD patients. T<span>his protective effect did not appear to be mediated by striatal dopaminergic function.</span></span></span></p> <p><span><span><b>Classification of evidence</b>: This study provides Class II evidence that increased physical activity was associated with decreased <i>APOE</i> ε4-related early cognitive decline in PD patients.</span></span></p>

opencc-zeroFeb 2022View details →
dryad32/100

Data from: Genotyping-in-Thousands by sequencing panel development and application to inform kokanee salmon (Oncorhynchus nerka) fisheries management at multiple scales

<p>The ability to differentiate life history variants is vital for estimating fisheries management parameters, yet traditional survey methods can be inaccurate in mixed-stock fisheries. Such is the case for kokanee, the resident freshwater form of sockeye salmon (<i>Oncorhynchus nerka</i>), which exhibits various reproductive ecotypes (stream-, shore-, deep-spawning) that co-occur with each other and/or anadromous <i>O. nerka</i> in some systems across their pan-Pacific distribution. Here, we developed a multi-purpose Genotyping-in-Thousands by sequencing (GT-seq) panel of 288 targeted single nucleotide polymorphisms (SNPs) to enable accurate kokanee stock identification by geographic basin, migratory form, and reproductive ecotype across British Columbia, Canada. The GT-seq panel exhibited high self-assignment accuracy (93.3%) and perfect assignment of individuals not included in the baseline to their geographic basin, migratory form, and reproductive ecotype of origin. The GT-seq panel was subsequently applied to Wood Lake, a valuable mixed-stock fishery, revealing high concordance (&gt;98%) with previous assignments to ecotype using microsatellites and TaqMan<span> </span>SNP genotyping assays, while improving resolution, extending a long-term time-series, and demonstrating the scalability of this approach for this system and others.</p>

opencc-zeroFeb 2022View details →
dryad32/100

Schistosoma mansoni raw genotype calls from exome data

<p><em>Schistosoma mansoni, </em>a snail-vectored, blood fluke that infects humans, was introduced into the Americas from Africa during the Trans-Atlantic slave trade. As this parasite shows strong specificity to the snail intermediate host, we expected that adaptation to S. American <em>Biomphalaria</em> spp. snails would result in population bottlenecks and strong signatures of selection. We scored 475,081 single nucleotide variants (SNVs) in 143 <em>S. mansoni</em> from the Americas (Brazil, Guadeloupe, and Puerto Rico) and Africa (Cameroon, Niger, Senegal, Tanzania, and Uganda), and used these data to ask: (i) Was there a population bottleneck during colonization? (ii) Can we identify signatures of selection associated with colonization? And (iii) what were the source populations for colonizing parasites? We found a 2.4-2.9-fold reduction in diversity and much slower decay in linkage disequilibrium (LD) in parasites from East to West Africa. However, we observed similar nuclear diversity and LD in West Africa and Brazil, suggesting no strong bottlenecks and limited barriers to colonization. We identified five genome regions showing selection in the Americas, compared with three in West Africa and none in East Africa, which we speculate may reflect adaptation during colonization. Finally, we infer that unsampled African populations from central African regions between Benin and Angola, with contributions from Niger, are likely the major source(s) for Brazilian <em>S. mansoni</em>. The absence of a bottleneck suggests that this is a rare case of a serendipitous invasion, where <em>S. mansoni </em>parasites were preadapted to the Americas and were able to establish with relative ease.</p>

opencc-zeroMar 2022View details →
dryad32/100

Impatiens glandulifera SNP and SilicoDArT genotyping data

<p>We conducted genomic characterization based on SNP and SilicoDArT markers on the invasive Himalayan balsam (<i>Impatiens glandulifera</i>) plants originating from the native and non-native regions of their distribution. When genetic relationships were explored by PCoA based on SNP and SilicoDArT marker data, the first, second and third principal coordinates explained altogether 37.4% and 31.0% of the variability, respectively. Samples from the UK, Canada and Pakistan grouped together, while Indian plants were clearly distinct based on SNP markers but relatively close to the UK-Canada-Pakistan group based on SilicoDArT markers. Constructed trees differentiated the individuals into clusters resembling the patterns observed by PCoA.<span> The Bayesian BAPS analysis revealed that the individuals were distributed in seven clusters, representing samples from each of the four Finnish populations, India, Pakistan and the combination of the UK and Canada. Similar clustering was visible in the constructed UPGMA tree. The Indian cluster did not display any ancestral gene flow with the others, while the Pakistani cluster showed ancestral gene flow only with the combined UK and Canada cluster. Furthermore, the latter cluster displayed ancestral gene flow with the Finnish populations varying from 0% to 3.1%. The AMOVA analysis showed that 45% and 26% of genetic variation was present among the <i>I. glandulifera</i> groups/populations and the rest within them based on SNP and SilicoDArT markers, respectively. Overall, the Bayesian BAPS analysis</span> <span>and the following gene flow network were the most informative tools for resolving relationships among native and introduced plants. </span></p>

opencc-zeroMar 2022View details →
dryad32/100

Field data and microsatellite genotypes of Cercidiphyllum japonicum

<p>Field data and genotypes at five microsatellite loci of 281 <i>Cercidiphyllum japonicum </i>adults of a population distributed over a ca. 80 ha along a stream and 755 <i>C. japonicum </i>current-year seedlings sampled at approximate center of the populatoin. The population is located in Iwanazawa Forest Reserve (43°13′N, 142°34′E), University of Tokyo Hokkaido Forest, in central Hokkaido, Japan.</p>

opencc-zeroMar 2022View details →
dryad32/100

Data from: Competitive consequences determined by phenotypic but not genetic distance: a study with asexual Daphnia genotypes

<p><span><span>1. How </span><span>evolutionary relatedness influences the strength of competitive interactions among </span><span>genetically isolated populations has been a long-standing interest in ecology. Darwin's </span><span>"Competition </span><span>R</span><span>elatedness Hypothesis (CRH)" states that, since closely related species should compete more strongly, they are less likely to coexist, while </span><span>Herbert's </span><span>"Bimodal </span><span>Competition Hypothesis (BCH)" predicts that competitive exclusion is less likely to occur when the competing species are genetically close or distant.</span></span></p> <p><span>2. T</span><span>o test these hypotheses,</span><span> we</span><span> experimentally examined the difference in the competitive ability and life tables of fecundity</span><span> </span><span>and survivorship among four different genotypes of </span><span>asexual</span><span> Daphnia cf. pulex </span><span>that diverged from a single ancestral genotype</span><span>.</span></p> <p><span>3. </span><span>The experiments showed that the competitive consequences differed depending on the pairing of the competing genotypes, and that the degree of the competitive exclusion was lower when the competing genotypes were genetically closer to each other. These results partially supported the BCH but not the CRH at all. More importantly, the degree of competitive exclusion was better predicted by the phenotypic rather than genetic distances between the competing genotypes.</span></p> <p><span>4. </span><span>The life table experiments revealed that competitively inferior genotypes had higher early reproduction rates, but survival rates decreased with age and thus body size, probably a result of selection by predation pressures found in nature.</span></p> <p><span>5. </span><span>These results indicate that competitive superiority is highly dependent on selection pressures that given organisms have been evolutionally subjected to, and, that genetic similarity is not necessarily an appropriate measure for predicting the completive exclusion on an ecological time scale. </span><span>To predict competitive relationships among the organisms, it is essential to comprehend their phenotypic differences rather than simply knowing their genetic or phylogenetic relationships.</span></p>

opencc-zeroApr 2022View details →

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Allen Brain Atlas

Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.

allen-brain-atlas
neuroscienceopenDocumentation, web resources, and API references are available online.
Last verified 2026-04-30Open record

Annotated Behaviour and Observability Dataset (ABODe)

ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.

abode-home-cage
behavioral-neuroscienceopenThe DataShare record exposes download links for annotations, documentation, license text, and the zipped per-snippet data directory.
Last verified 2026-04-30Open record

DANDI Archive for NWB datasets

DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.

dandi-nwb
electrophysiologyopenPublished Dandiset metadata and archive endpoints are available through the production DANDI API.
Last verified 2026-04-30Open record

International Brain Laboratory public data

The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.

ibl
behavioral-neuroscienceopenPublic sessions can be searched and loaded from the IBL public data server through ONE.
Last verified 2026-04-29Open record

OpenNeuro

OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.

openneuro
neuroscienceopenPublished datasets are available on demand over the internet.
Last verified 2026-04-29Open record

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