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29 results for “Agrilus planipennis”
Data from: Testing the heat treatment dose for Agrilus planipennis prepupae using the Humble water bath
<p>The lethal heat treatment dose (time and temperature) for the pre-pupal life stage of <em>Agrilus planipennis</em> Fairmaire (Coleoptera: Buprestidae), emerald ash borer, was determined through an in vitro application using a carefully calibrated heat treatment apparatus. The lethal and sublethal effects of heat on A. planipennis prepupae were assessed through a ramped heat delivery application, simulating industrial kilns and conventional heat chamber operations, for treatments combining target temperatures of 54 °C, 55 °C, and 56 °C, and exposure durations of 0 min (i.e., kiln temperature ramp only), 15 min, or 30 min. Prepupal emerald ash borer larvae did not survive exposure to 56 °C for 15 min or longer, or to 55 °C for 30 min. Sublethal effects were observed for all other treatments. Sublethal effects included delayed development and failure to complete the pupal and adult life stages. The datasets and associated R statistical computing langauge code are deposited here.</p>
Fig. 3 in Effect of forest microhabitat and larval stage on overwintering survival, development, and phenology of Spathius galinae (Hymenoptera: Braconidae), biological control agent of emerald ash borer, Agrilus planipennis (Coleoptera: Buprestidae)
Fig. 3. Proportion of dead (A) and diapaused (B) Spathius galinae by stage at time of deployment, and overwintering microhabitat. Fate was determined by dis- secting all logs once emergence was complete. Letters of the same type and case within the same subfigure indicate significance when data are considered by stage alone (P <0.05).
Fig. 2 in Effect of forest microhabitat and larval stage on overwintering survival, development, and phenology of Spathius galinae (Hymenoptera: Braconidae), biological control agent of emerald ash borer, Agrilus planipennis (Coleoptera: Buprestidae)
Fig. 2. Deployment jar for logs containing emerald ash borer larvae parasitized by Spathius galinae. Logs were inserted in floral foam in 3.8 L polyethylene terephthalate jar with 2 mesh cutouts for ventilation and excess water drain- age. The jar was attached to the tree by resting the bottom of the jar on 2 nails hammered into the tree while a length of wire wrapped around the 2 nails on either side of the jar. Another wire looped around the neck of the jar and was fastened to the nail at the top. Water was added to the jars as needed to ensure adequate hydration of the logs and larvae.
Fig. 1. Experimental microhabitats near the USDA-ARS Louis A in Effect of forest microhabitat and larval stage on overwintering survival, development, and phenology of Spathius galinae (Hymenoptera: Braconidae), biological control agent of emerald ash borer, Agrilus planipennis (Coleoptera: Buprestidae)
Fig. 1. Experimental microhabitats near the USDA-ARS Louis A. Stearns Laboratory in Newark, Delaware, USA. Letters indicate habitat type and approximate experiment locations: (A) mature forest, a larger, more mature wooded area; (B) urban forest, small, highly disturbed woodlot.
Fig. 4 in Effect of forest microhabitat and larval stage on overwintering survival, development, and phenology of Spathius galinae (Hymenoptera: Braconidae), biological control agent of emerald ash borer, Agrilus planipennis (Coleoptera: Buprestidae)
Fig. 4. Survival analysis of Spathius galinae emergence from urban (A) and mature forest (B) sites over time by stage at time of deployment.
Data from: Testing the heat treatment dose for Agrilus planipennis prepupae using the Humble water bath
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The potential range of Agrilus planipennis according to current and future climate conditions
<p>This dataset is associated to the following reference:</p> <p>Jean-Pierre Rossi, Raphaëlle Mouttet, Pascal Rousse and Jean-Claude Streito<sup> </sup>(2024) Modelling the potential range of <em>Agrilus planipennis</em> in Europe according to current and future climate conditions. In press. Trees, Forests and People. https://doi.org/10.1016/j.tfp.2024.100559</p> <p>The files correspond to rasters saved as geotiff files. They can be used in geographical information systems.</p> <p><strong>Current climate conditions: 2001-2018. The maps correspond to the whole world.</strong></p> <p>CS_2001-2018_Bart.tif</p> <p>Climate suitability for Agrilus planipennis modelled using the BART algorithm and the reference conditions (2001-2018). The climate suitability ranges from 0 (unsuitable) to 1 (suitable).</p> <p>CS_2001-2018_Brt.tif</p> <p>Climate suitability for Agrilus planipennis modelled using the BRT algorithm and the reference conditions (2001-2018). The climate suitability ranges from 0 (unsuitable) to 1 (suitable).</p> <p>CS_2001-2018_Rf.tif</p> <p>Climate suitability for Agrilus planipennis modelled using the RF algorithm and the reference conditions (2001-2018). The climate suitability ranges from 0 (unsuitable) to 1 (suitable).</p> <p>CS_2001-2018_Bart_pres_abs.tif</p> <p>Reclassified climate suitability maps for Agrilus planipennis modelled using the algorithm BART and the reference conditions (2001-2018). The raster contains 2 classes: suitable conditions (raster value = 1) and unsuitable conditions (raster value = 0).</p> <p>CS_2001-2018_Brt_pres_abs.tif</p> <p>Reclassified climate suitability maps for Agrilus planipennis modelled using the algorithm BRT and the reference conditions (2001-2018). The raster contains 2 classes: suitable conditions (raster value = 1) and unsuitable conditions (raster value = 0).</p> <p>CS_2001-2018_Rf_pres_abs.tif</p> <p>Reclassified climate suitability maps for Agrilus planipennis modelled using the algorithm RF and the reference conditions (2001-2018). The raster contains 2 classes: suitable conditions (raster value = 1) and unsuitable conditions (raster value = 0).</p> <p>CS_2001-2018_committee.tif</p> <p>Map showing the percentage of algorithms indicating suitable climate conditions for Agrilus planipennis. The algorithms (BART, BRT and RF) are projected using the current climate conditions (2001-2018).</p> <p><strong>Future climate conditions: 2041-2060. The maps correspond to Europe.</strong></p> <p> CS_2041-2060_SSP1-2.6_committee.tif</p> <p>Map showing the percentage of algorithms indicating suitable climate conditions for Agrilus planipennis. The algorithms (BART, BRT and RF) are projected using the climate data associated with 11 GCMs for the period 2041-2060 and the SSP1-2.6.</p> <p> CS_2041-2060_SSP2-4.5_committee.tif</p> <p>Map showing the percentage of algorithms indicating suitable climate conditions for Agrilus planipennis. The algorithms (BART, BRT and RF) are projected using the climate data associated with 11 GCMs for the period 2041-2060 and the SSP2-4.5.</p> <p> CS_2041-2060_SSP3-7.0_committee.tif</p> <p>Map showing the percentage of algorithms indicating suitable climate conditions for Agrilus planipennis. The algorithms (BART, BRT and RF) are projected using the climate data associated with 11 GCMs for the period 2041-2060 and the SSP3-7.0.</p> <p> CS_2041-2060_SSP5-8.5_committee.tif</p> <p>Map showing the percentage of algorithms indicating suitable climate conditions for Agrilus planipennis. The algorithms (BART, BRT and RF) are projected using the climate data associated with 11 GCMs for the period 2041-2060 and the SSP5-8.5.</p> <p> </p> <p>BART: Bayesian Additive Regression Trees</p> <p>BRT: Boosted Regression Trees</p> <p>RF: Random Forest</p>
Agrilus planipennis ̶ Pest Report and Datasheet to support ranking of EU candidate priority pests
<p>These two files are part of the outputs produced under the mandate <a href="http://registerofquestions.efsa.europa.eu/roqFrontend/wicket/page?1-1.ILinkListener-contentPane-listContainer-pageable-21-mandateNumberLnk">M-2017-0056</a> of the European Commission requesting EFSA for technical assistance in the field of quarantine pests qualifying as priority pests as by Article 6(2) of the Regulation (EU) 2016/2031 <em>on protective measures against pests of plants</em>.</p> <p>Under the mandate EFSA produced: i) 1 methodology report (DOI available at the field "Related/alternate identifiers"), ii) 28 datasheets, one for each of the 28 candidate pests, and iii) 28 pest reports supporting the information provided in the datasheets.</p> <p>EFSA wishes to acknowledge the contribution of Hugh Evans, Christian MacQuarrie, Deborah McCullough, Hans Peter Ravn, Claire Rutledge, Denys Yemshanov to the EKE and the review conducted by Richard Baker.</p>
Data from: Plasticity drives extreme cold tolerance of emerald ash borer (Agrilus planipennis) during a polar vortex
<p>Invasive species must often survive combinations of environmental conditions that differ considerably from their native range; however, for a given species it is unclear whether improved tolerance is the result of phenotypic plasticity or genetic adaptation (or both).</p> <p><em>Agrilus planipennis</em> (Coleoptera: Buprestidae; the emerald ash borer) is an invasive pest of <em>Fraxinus</em> trees in North America and Europe. Previous studies in southwestern Ontario, Canada, showed that <em>A. planipennis</em> is freeze avoidant, preventing internal ice formation by accumulating molar concentrations of glycerol in its hemolymph and depressing its supercooling point (SCP, the temperature at which it freezes). The cold tolerance of these southwestern Ontario animals was used to predict potential distribution, revealing that some Canadian cities should be too cold to allow populations to persist. However, a small population of <em>A. planipennis</em> has persisted in Winnipeg, Manitoba, Canada, through several severe 'polar vortex' events.</p> <p>In 2018/19, we collected <em>A. planipennis</em> larvae and prepupae from Winnipeg, Manitoba and Southern Ontario, and found that individuals from Winnipeg were extremely cold tolerant – with SCPs as low as -52 °C in prepupae (compared to 32 °C in Southern Ontario), and survival of unfrozen individuals exposed to -50 °C for one hour. This cold tolerance was accompanied by higher hemolymph osmolality and glycerol concentration than in the SW Ontario individuals. To distinguish between phenotypic plasticity and local adaptation, in 2020/21 we overwintered Winnipeg-sourced individuals either outdoors in southwestern Ontario or in a simulated Winnipeg winter. Simulated Winnipeg winter individuals had cold tolerance similar to those overwintered in Winnipeg, while southwestern Ontario overwintered individuals had cold tolerance similar to those collected previously in the region. The simulated winter individuals had higher hemolymph glycerol concentrations than southwestern Ontario overwintered animals, at least in part due to greater dehydration. Thus, <em>A. planipennis</em> are cold-tolerant enough to survive some of the harshest winters where their host trees can grow, and most likely attain this cold tolerance via phenotypic plasticity. These findings raise the importance of delineating sensitivity of conclusions to unexpected phenotypic plasticity when predicting potential distributions of new invasives or responses to climate change.</p> <p>The data in this dataset are the SCPs and treatment data for the experimental animals used in these cold tolerance experiments. </p>
FIGURES 6A–6D. Agrilus planipennis Fairmaire, 1888 in Taxonomic, distributional and biological study of the genus Agrilus (Coleoptera: Buprestidae). Part II
FIGURES 6A–6D. Agrilus planipennis Fairmaire, 1888 in China, Jilin on Fraxinus. 6A, Jilin City; 6B, Erdaozun; 6C–6D, Jiaohe. 6A–6C, outbreak in urban areas; 6D, larval galleries on young tree.
FIGURES 5A–5F. Agrilus planipennis Fairmaire, 1888 in Taxonomic, distributional and biological study of the genus Agrilus (Coleoptera: Buprestidae). Part II
FIGURES 5A–5F. Agrilus planipennis Fairmaire, 1888 in China. 5A–5B, Badalingzhen (Beijing); 5C, 5E, Xiaolongmen (Beijing); 5D, Jilin City (Jilin); 5F, Erdaozun (Jilin). 5A, tree alley with infested Fraxinus velutina; 5B, larval galleries on Fraxinus velutina; 5C, 5E, old larval galleries on native Fraxinus sp.; 5D, 5F, single larval gallery on Fraxinus sp.
Data from: Plasticity drives extreme cold tolerance of emerald ash borer (Agrilus planipennis) during a polar vortex
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Data from: The effect of host condition on adult emerald ash borer (Agrilus planipennis) performance
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Figure 1 from: Rutledge C, Fierke M, Careless P, Worthley T (2013) First detection of Agrilus planipennis in Connecticut made by monitoring Cerceris fumipennis (Crabronidae) colonies. Journal of Hymenoptera Research 32: 75-81. https://doi.org/10.3897/jhr.32.4865
Figure 1 - Abandoned emerald ash borer next to the nest entrance of Cerceris fumipennis at a colony in Prospect CT.
Figures 40-45 from: Chamorro L, Jendek E (2012) Six new species of Agrilus Curtis, 1825 (Coleoptera, Buprestidae, Agrilinae) from the Oriental Region related to the emerald ash borer, A. planipennis Fairmaire, 1888 and synonymy of Sarawakita Obenberger, 1924. ZooKeys 239: 71-94. https://doi.org/10.3897/zookeys.239.3966
Figures 40-45 - Agrilus sapphirinus Jendek & Chamorro, sp. n. Holotype female: 40 ventral view 41 dorsal view 42 lateral view of head and pronotum 43 oblique-lateral view of head and pronotum 44 anterior view of head 45 lateral view.
Figures 33-39 from: Chamorro L, Jendek E (2012) Six new species of Agrilus Curtis, 1825 (Coleoptera, Buprestidae, Agrilinae) from the Oriental Region related to the emerald ash borer, A. planipennis Fairmaire, 1888 and synonymy of Sarawakita Obenberger, 1924. ZooKeys 239: 71-94. https://doi.org/10.3897/zookeys.239.3966
Figures 33-39 - Agrilus pseudolubopetri Jendek & Chamorro, sp. n. 33 female, last abdominal ventrite 34 female, apices of elytra 35 female, metathoracic leg 36 female, mesothoracic leg 37 male, anterior view of head 38 female, segment VIII, ventral view 39 female, scutellum.
Figures 28-32 from: Chamorro L, Jendek E (2012) Six new species of Agrilus Curtis, 1825 (Coleoptera, Buprestidae, Agrilinae) from the Oriental Region related to the emerald ash borer, A. planipennis Fairmaire, 1888 and synonymy of Sarawakita Obenberger, 1924. ZooKeys 239: 71-94. https://doi.org/10.3897/zookeys.239.3966
Figures 28-32 - Agrilus pseudolubopetri Jendek & Chamorro, sp. n. 28 female, dorsal view of head, pronotum, scutellum 29 male, dorsal view of head, pronotum, scutellum 30 female, ventral view of head and sternum 31 male, lateral view of head and pronotum 32 male, oblique-lateral view of head and pronotum.
Figures 24-25 from: Chamorro L, Jendek E (2012) Six new species of Agrilus Curtis, 1825 (Coleoptera, Buprestidae, Agrilinae) from the Oriental Region related to the emerald ash borer, A. planipennis Fairmaire, 1888 and synonymy of Sarawakita Obenberger, 1924. ZooKeys 239: 71-94. https://doi.org/10.3897/zookeys.239.3966
Figures 24-25 - Agrilus pseudolubopetri Jendek & Chamorro, sp. n. Male habitus and aedeagus: 24 dorsal view 25 ventral view.
Figures 19-23 from: Chamorro L, Jendek E (2012) Six new species of Agrilus Curtis, 1825 (Coleoptera, Buprestidae, Agrilinae) from the Oriental Region related to the emerald ash borer, A. planipennis Fairmaire, 1888 and synonymy of Sarawakita Obenberger, 1924. ZooKeys 239: 71-94. https://doi.org/10.3897/zookeys.239.3966
Figures 19-23 - Agrilus crepuscularis Jendek & Chamorro, sp. n. Holotype male: 19 last abdominal ventrite 20 elytral apices 21 oblique-lateral view of marginal and submarginal carinae 22 ventral view of head and prosternum 23 dorsal view of head and pronotum.
Figures 26-27 from: Chamorro L, Jendek E (2012) Six new species of Agrilus Curtis, 1825 (Coleoptera, Buprestidae, Agrilinae) from the Oriental Region related to the emerald ash borer, A. planipennis Fairmaire, 1888 and synonymy of Sarawakita Obenberger, 1924. ZooKeys 239: 71-94. https://doi.org/10.3897/zookeys.239.3966
Figures 26-27 - Agrilus pseudolubopetri Jendek & Chamorro, sp. n. Female habitus: 26 dorsal view 27 ventral view.
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