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48 results for “Ixodes ricinus”
Figure 2 in Factors influencing the level of infestation of Ixodes ricinus (Acari: Ixodidae) on Lacerta agilis and Zootoca vivipara (Squamata: Lacertidae)
Figure 2 Mean number (± SE) of ticks per body size class (I to IV), and sex-age category (juv: juvenile; F: female, M: male), found in (A) transformed conditions and (B) natural conditions.
Figure 1 in Factors influencing the level of infestation of Ixodes ricinus (Acari: Ixodidae) on Lacerta agilis and Zootoca vivipara (Squamata: Lacertidae)
Figure 1 Mean number (± SE) of ticks per body size class (I to IV) and Sex-age category (juv: juvenile; F: female, M: male), found on (A) Zootoca viviparaand (B)Lacerta agilis.
Figure 3 in Factors influencing the level of infestation of Ixodes ricinus (Acari: Ixodidae) on Lacerta agilis and Zootoca vivipara (Squamata: Lacertidae)
Figure 3 Mean number of ticks found on different locations on the lizards bodies (± standard errors).
Fig. 1 in Infestation With Ixodes Ricinus Ticks On Migrating Passerine Birds In Lithuania And Norway
Fig. 1 Molecular taxonomical identification of the I. ricinus by PCR assay. Lines 1 and 15 – 50 bp marker; Line 2 –negative control; Lines 2-13 –positive results: amplified 150 bp specific fragment for I. ricinus; Line 14 – positive control of I. ricinus (150 bp)
Annotation table - Whole body transcriptomes of the tick Ixodes ricinus at different stage and feeding conditions
<p>Annotation table for a <em>de novo</em> assembled transcriptome of<em> Ixodes ricinus</em> in different stages and conditions.</p> <p>Description of the fields of each column (Trinotate results, and additionnal statistics):</p> <p>1. Contig_name: name of the contig (Trinity assembly)</p> <p>2. sprot_Top_BLASTX_hit: first hit of the blastx search against SwissProt (https://data.broadinstitute.org/Trinity/Trinotate v2.0 RESOURCES/)</p> <p>3. TrEMBL_Top_BLASTX_hit: first hit of the blastx search against Uniref90 (https://data.broadinstitute.org/Trinity/Trinotate v2.0 RESOURCES/)</p> <p>4. RNAMMER: identification of non-coding RNAs</p> <p>5. prot_id: identifier of the predicted protein (TransDecoder)</p> <p>6. prot_coords: coordinates (start, end and strand) of the predicted protein on the contig</p> <p>7. sprot_Top_BLASTP_hit: first hit of the blastp search between the predicted protein and SwissProt (https://data.broadinstitute.org/Trinity/Trinotate v2.0 RESOURCES/)</p> <p>8. TrEMBL_Top_BLASTP_hit: first hit of the blastp search between the predicted protein and Uniref90 (https://data.broadinstitute.org/Trinity/Trinotate v2.0 RESOURCES/)</p> <p>9. Pfam: result of the search against PfamA database</p> <p>10. SignalP: prediction of a signal peptide with SignalP</p> <p>11. TmHMM: prediction of a transmembrane domain with THMM</p> <p>12. eggnog: eggNOG database of orthologous genes (v3.0) assignation</p> <p>13. gene_ontology_blast: GO assignation based on blast results</p> <p>14. gene_ontology_pfam: GO assignation based on pfam results</p> <p>15. Contig_length: length of the contig in bp</p> <p>16. Busco_Id: name of the BUSCO (v1)</p> <p>17. Busco_status: status of the BUSCO (complete/fragmented/duplicated)</p> <p>18-32: Kallisto read counts for the 15 libraries</p> <p>A, B, C: unfed nymphs (replicates 1, 2, 3)</p> <p>D, E, F: partially fed nymphs (replicates 1, 2, 3)</p> <p>G, H, I: males (unfed) (replicates 1, 2, 3)</p> <p>J, K, L: unfed adult females (replicates 1, 2, 3)</p> <p>M, N, O: partially fed adult females (replicates 1, 2, 3)</p> <p>33. log2FoldChange_UnfedVsPartiallyFed: log fold change in base 2 of expression (comparison between "unfed" -including males- and "fed" ticks)</p> <p>34. pvalue_UnfedVsPartiallyFed: p-value of the comparison between "unfed" -including males- and "fed" ticks</p> <p>35. log2FoldChange_MaleVsFemale: log fold change in base 2 of expression (comparison between "males" and "females")</p> <p>36. pvalue_MaleVsFemale: p-value of the comparison between "males" and "females"</p> <p>37. log2FoldChange_NymphsVsAdults: log fold change in base 2 of expression (comparison between "nymphs" and "adults" -males and females-)</p> <p>38. pvalue_NymphsVsAdults: p-value of the comparison between "nymphs" and "adults" -males and females-)</p> <p> </p> <p> </p>
Fig. 4 in Ticks on the move-climate change-induced range shifts of three tick species in Europe: current and future habitat suitability for Ixodes ricinus in comparison with Dermacentor reticulatus and Dermacentor marginatus
Fig. 4 Area projected as suitable or unsutable under current and future (2081–2100) climatic conditions (km2) for the three tick species in comparison. a Ixodes ricinus. b Dermacentor reticulatus. c D. marginatus. The corresponding maps are shown in Figs. 1–3 in the main document. Future suitable conditions refers to the area (km2) projected as unsuitable under current climatic conditions but suitable under future climatic conditions (i.e., potential new range). Continuing suitable conditions refers to area (km2) projected as suitable under current climatic conditions as well as under future climatic conditions (i.e., stable presence). Continuing unsuitable conditions refers to area (km 2) projected as unsuitable under current climatic conditions as well as under future climatic conditions (i.e. stable absence). Future unsuitable conditions refers to the area (km.2) projected as suitable under current climatic conditions but unsuitable under future climatic conditions (i.e., potential extinction)
Fig. 2 Projected future changes for Dermacentor reticulatus until 2080–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585 in Ticks on the move-climate change-induced range shifts of three tick species in Europe: current and future habitat suitability for Ixodes ricinus in comparison with Dermacentor reticulatus and Dermacentor marginatus
Fig. 2 Projected future changes for Dermacentor reticulatus until 2080–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585. In dark blue: area projected as suitable under current climatic conditions but unsuitable under future climatic conditions (i.e., potential extinction). In light blue: area projected as unsuitable under current climatic conditions as well as under future climatic conditions (i.e., stable absence). In orange: area projected as suitable under current climatic conditions as well as under future climatic conditions (i.e., stable range). In red: area projected as unsuitable under current climatic conditions but suitable under future climatic conditions (i.e., potential new range). AUC = 0.8333 (average over 10 replicates using cross-validation, standard deviation = 0.001113603). Threshold to transform the logistic model output: 0.3816 (10% omission rate threshold). Maps were built using ESRI ArcGIS (Release 10.7, www.esri.com). Projection: Europe Albers Equal Area Conic
Fig. 2 Projected future changes for Dermacentor reticulatus until 2080–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585 in Ticks on the move-climate change-induced range shifts of three tick species in Europe: current and future habitat suitability for Ixodes ricinus in comparison with Dermacentor reticulatus and Dermacentor marginatus
Fig. 2 Projected future changes for Dermacentor reticulatus until 2080–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585. In dark blue: area projected as suitable under current climatic conditions but unsuitable under future climatic conditions (i.e., potential extinction). In light blue: area projected as unsuitable under current climatic conditions as well as under future climatic conditions (i.e., stable absence). In orange: area projected as suitable under current climatic conditions as well as under future climatic conditions (i.e., stable
Fig. 4 in Ticks on the move-climate change-induced range shifts of three tick species in Europe: current and future habitat suitability for Ixodes ricinus in comparison with Dermacentor reticulatus and Dermacentor marginatus
Fig. 4 Area projected as suitable or unsutable under current and future (2081–2100) climatic conditions (km2) for the three tick species in comparison. a Ixodes ricinus. b Dermacentor reticulatus. c D. marginatus. The corresponding maps are shown in Figs. 1–3 in the main document. Future suitable conditions refers to the area (km2) projected as unsuitable under current climatic conditions but suitable under future climatic conditions (i.e., potential new range). Continuing suitable conditions refers to area (km2) projected as suitable under
Fig. 1 Projected future changes for Ixodes ricinus until 2081–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585 in Ticks on the move-climate change-induced range shifts of three tick species in Europe: current and future habitat suitability for Ixodes ricinus in comparison with Dermacentor reticulatus and Dermacentor marginatus
Fig. 1 Projected future changes for Ixodes ricinus until 2081–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585. In dark blue: area projected as suitable under current climatic conditions but unsuitable under future climatic conditions (i.e., potential extinction). In light blue: area projected as unsuitable under current climatic conditions as well as under future climatic conditions (i.e., stable absence). In orange: area projected as suitable under current climatic conditions as well as under future climatic conditions (i.e., stable range). In red:
Fig. 5 in Ticks on the move-climate change-induced range shifts of three tick species in Europe: current and future habitat suitability for Ixodes ricinus in comparison with Dermacentor reticulatus and Dermacentor marginatus
Fig. 5 Potential co-occurrence under current and future climatic conditions. a Under near current climatic conditions (1970–2000). b Under projected future climatic conditions (exemplarily for SSP 245) for the period 2041–2060. c Under projected future climatic conditions (SSP 245) for the period 2081–2100. Colors indicate areas where climatic suitability is projected for the respective species; for non-mentioned species ("none of them"), the area is climatically unsuitable according to the modelling results. The thresholds to transform the logistic model output (10% omission rate threshold) are as follows: 0.3368 for Ixodes ricinus, 0.3816 for Dermacentor reticulatus, and 0.4298 for D. marginatus. Maps were built using ESRI Arc-GIS (Release 10.7, www.esri.com). Projection: Europe Albers Equal Area Conic. (A hatch-based version of this figure is additionally provided in the Supplementary Material: Figure S11.)
Fig. 3 Projected future changes for Dermacentor marginatus until 2080–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585 in Ticks on the move-climate change-induced range shifts of three tick species in Europe: current and future habitat suitability for Ixodes ricinus in comparison with Dermacentor reticulatus and Dermacentor marginatus
Fig. 3 Projected future changes for Dermacentor marginatus until 2080–2100. a SSP 126. b SSP 245. c SSP 370. d SSP 585. In dark blue: area projected as suitable under current climatic conditions but unsuitable under future climatic conditions (i.e., potential extinction). In light blue: area projected as unsuitable under current climatic conditions as well as under future climatic conditions (i.e., stable absence). In orange: area projected as suitable under current climatic conditions as well as under future climatic conditions (i.e., stable range). In red: area projected as unsuitable under current climatic conditions but suitable under future climatic conditions (i.e., potential new range). AUC = 0.8229 (average over 10 replicates using cross-validation, standard deviation = 0.001121953). Threshold to transform the logistic model output: 0.4298 (10% omission rate threshold). Maps were built using ESRI ArcGIS (Release 10.7, www.esri.com). Projection: Europe Albers Equal Area Conic
Figure 1 in The occurrence of three tick-borne pathogens in Ixodes ricinus ticks collected from the area of the Kraków-Częstochowa Upland (Southern Poland)
Figure 1 Locations of the Kraków-Częstochowa Upland in Poland and the location of the studied areas.
Fig.1 in Distribution Of Ixodes Ricinus (Arachnida, Ixodidae) In Ukraine In The Context Of Tick Hazard, And Factors Favoring Its Persistence In Conditions Of Fast-Going Environmental Change
Fig.1. The hiatus in the range that has been noted on the territory of Ukraine: 1 — European area of distribution; 2 — Crimean area of distribution; 3 — Caucasian-Western Asian area of distribution; 4 — zone of disjunction (after fig. 1 Akimov & Nebogatkin, 1996 with changes).
Fig. 2 in Distribution Of Ixodes Ricinus (Arachnida, Ixodidae) In Ukraine In The Context Of Tick Hazard, And Factors Favoring Its Persistence In Conditions Of Fast-Going Environmental Change
Fig. 2. Distribution of I. ricinus on the territory of Ukraine, from the point of view of tick-borne danger.
Fig. 2 in Prédation des tiques Ixodes ricinus par les fourmis des bois Formica pratensis - expérience préliminaire
Fig. 2 (à droite). Tiques Ixodes ricinus. De bas en haut: larve, nymphe, mâle adulte et femelle adulte (1 carré = 1 mm2). (Photo Olivier Rais, Université de Neuchâtel)
Figure 2. Ixodes ricinus A in A contribution to the tick (Acari: Ixodidae) fauna of Turkey: The first record of Ixodes inopinatus Estrada-Peña, Nava & Petney
Figure 2. Ixodes ricinus A. Dorsal view of male, B. Several rows of setae in the lateral margin of the conscutum of male, C. Internal spurs of coxa I of female, D. Spiracular plate with concentric five rows goblets of female.
Identification and expression of short neuropeptide F and its receptors in the tick Ixodes ricinus
<p>The open datasets include raw data covering results published in paper by Medla et al., 2023 (https://doi.org/10.1016/j.jinsphys.2023.104524)</p>
Fig. 2 in Infestation With Ixodes Ricinus Ticks On Migrating Passerine Birds In Lithuania And Norway
Fig. 2 Larval and nymphal infestation rates of passerine migratory birds in Norway and Lithuania
Fig. 1 in Prédation des tiques Ixodes ricinus par les fourmis des bois Formica pratensis - expérience préliminaire
Fig. 1 (à gauche). Ouvrières de Formica pratensis. (Photo Christine Dobler Gross)
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