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169 results for “conservation effectiveness”
Data for "Let's not wing it: Effective conservation of subterranean-roosting bats"
<p>Database as both excel (.xls) and tab-delimited (.csv) associated with the publication: </p> <p>Meierhofer M.B., et al. (2023) Let’s not wing it: Effective conservation of subterranean-roosting bats. <em>Conservation biology.</em></p> <p>Please refer to the main publication for a detailed description. An explanation of the database is available in the Metadata file uploaded alongside the database. R code to reproduce the analysis pipeline is available on GitHub:</p> <p>https://github.com/StefanoMammola/Analysis_Cave_bat_conservation.git</p>
Embeddings from protein language models predict conservation and variant effects
<p>For this work, we used protein language model representations (embeddings) to predict sequence conservation without multiple sequence alignments (MSAs). Embeddings alone predicted residue conservation almost as accurately from single sequences as ConSeq using MSAs (two-state Matthew Correlation Coefficient – MCC - for ProtT5 embeddings of 0.596±0.006 vs. 0.608±0.006 for ConSeq).</p> <p><strong><em>ConSurf10k</em>- Dataset for the development of ProtT5cons:</strong> The method (ProtT5cons) predicting residue conservation used <em>ConSurf-DB </em>(Ben Chorin et al. 2020). This resource provided sequences and conservation for 89,673 proteins. For all, experimental high-resolution three-dimensional (3D) structures were available in the Protein Data Bank (PDB) (Berman et al. 2000). As standard-of-truth for the conservation prediction, we used the values from ConSurf-DB generated using HMMER (Mistry et al. 2013), CD-HIT (Fu et al. 2012), and MAFFT-LINSi (Katoh and Standley 2013) to align proteins in the PDB (Burley et al. 2019). For proteins from families with over 50 proteins in the resulting MSA, an evolutionary rate at each residue position is computed and used along with the MSA to reconstruct a phylogenetic tree. The ConSurf-DB conservation scores ranged from 1 (most variable) to 9 (most conserved). The PISCES server (Wang and Dunbrack 2003) was used to redundancy reduce the data set such that no pair of proteins had more than 25% pairwise sequence identity. We removed proteins with resolutions >2.5Å, those shorter than 40 residues, and those longer than 10,000 residues. The resulting data set (ConSurf10k) with 10,507 proteins (or domains) was randomly partitioned into training (9,392 sequences), cross-training/validation (555) and test (519) sets.</p> <p>Uploaded data:</p> <ul> <li>ConSuf10k_PDBid_seq_cons.fasta: fasta file with PDBid, sequence and conservation annotation</li> <li>consurf10k_test_ids.txt: txt file with id's of test set</li> <li>consurf10k_train_ids.txt: txt file with id's of train set</li> <li>consurf10k_val_ids.txt: txt file with id's of cross-validation set</li> </ul>
Easement_cost-effectiveness: Effects of disputes and easement violations on the cost-effectiveness of land conservation
<p>This repository includes the data and files for the example analysis of the following paper published in PeerJ:</p> <p>Schuster and Arcese (2015) Effects of disputes and easement violations on the cost-effectiveness of land conservation. PeerJ x:xxxx</p>
Reassessing science communication for effective farmland biodiversity conservation.
<p>Data set and code for analysing a communication case study about biodiversity conservation and farming in the European decision-making environment. It includes: (1) a literature corpus, consisting of 5988 digital press releases and news texts, covering the period of 2015-2020, from 40 different organizations involved in European farming and food decision-making processes; (2) R code scripts for analysis and graphic representation.</p>
Air temperature and humidity effects on the performance of conservation detection dogs
<p>This is the dataset which underlies the submitted manuscript entitled " <strong>Air temperature and humidity effects on the performance of conservation detection dogs</strong>".</p> <p>The uploaded data contain an xlsx file,which includes the data, as well as a txt readme file, which explains the header information in the data file.</p>
Supplementary material 2 from: Trochet A, Schmeller D (2013) Effectiveness of the Natura 2000 network to cover threatened species. Nature Conservation 4: 35-53. https://doi.org/10.3897/natureconservation.4.3626
Supplementary material 2 from: Trochet A, Schmeller D (2013) Effectiveness of the Natura 2000 network to cover threatened species. Nature Conservation 4: 35-53. https://doi.org/10.3897/natureconservation.4.3626
Supplementary material 1 from: Pontoppidan M, Nachman G (2013) Spatial Amphibian Impact Assessment – a management tool for assessment of road effects on regional populations of Moor frogs (Rana arvalis). Nature Conservation 5: 29-52. https://doi.org/10.3897/natureconservation.5.4612
Full model description following the protocol suggested by Grimm et al. (2006, 2010) and model parameterisation. (doi: 10.3897/natureconservation.5.4612.app). File format: Adobe PDF document (pdf).:
Figure 1. A in Habitat description of the rare orchid Didymoplexis verrucosa for more effective conservation
Figure 1. A, Location of the province of KwaZulu-Natal within South Africa; B, northern KwaZulu-Natal showing the very limited extent of remaining forest ecosystems shaded in black with degree grid lines for spatial reference; C, study area shaded in grey south of the coastal town of Mtunzini with quarter degree grid lines for spatial reference.
Raw data for: Spatial and temporal variation in farmland bird nesting ecology: Implications for effective Corn Bunting Emberiza calandra conservation
<p>These are raw data accompanying the study "<span>Spatial and temporal variation in farmland bird nesting ecology: Implications for effective Corn Bunting Emberiza calandra conservation</span>". All information on data origin, data analysis, and derived implications will be available with the original publiation.</p>
Data from: Variation and conservation implications of the effectiveness of anti-bear interventions
<p>Human-bear conflicts triggered by nuisance behaviour in public places and damage to livestock, crops, beehives and trees are among the main threats to bear populations globally. The effectiveness of interventions used to minimize bear-caused damage is insufficiently known and comparative reviews are lacking. We conducted a meta-analysis of 77 cases from 48 publications and used the relative risk of damage to compare the effectiveness of non-invasive interventions, invasive management (translocations) and lethal control (shooting) against bears. We show that the most effective interventions are electric fences (95% confidence interval = 79.2-100% reduction in damage), calving control (100%) and livestock replacement (99.8%), but the latter two approaches were applied in only one case each and need more testing. Deterrents varied widely in their effectiveness (13.7-79.5%) and we recommend applying these during the peak periods of damage infliction. We found shooting (-34.2 to 100%) to have a short-term positive effect with its effectiveness decreasing significantly and linearly over time. We did not find relationships between bear density and intervention effectiveness, possibly due to differences in spatial scales at which they were measured (large scales for densities and local fine scales for effectiveness). We appeal for more effectiveness studies and their scientific publishing in regard to under-represented conflict species and regions.</p>
Can at-risk species serve as effective conservation surrogates? Case study in northeastern US shrublands
<p>Targeted, single-species management and ecosystem-based management are generally considered disparate conservation approaches. In imperiled ecosystems, these approaches may be complementary, when habitat management for targeted at-risk species provides broad ecosystem benefits through an umbrella or surrogate species effect. In the northeastern United States, extensive management has been ongoing since 2011 to restore declining habitat for an at-risk shrubland habitat specialist, the New England cottontail (<i>Sylvilagus transitionalis</i>), with the goal that other shrubland-obligate wildlife will also benefit; yet the efficacy of these efforts has not been evaluated. In this study, we assessed whether habitat management targeting New England cottontail provides conservation benefits for shrubland-obligate birds. Specifically, we (1) identified shrubland-obligate birds that are indicative of the microhabitat conditions and habitat types suitable for New England cottontails, and (2) determined microhabitat and patch-level influences on shrubland bird occupancy at sites occupied by or managed for New England cottontail. Through avian point count surveys and indicator species analyses, we identified 12 shrubland-obligate bird species on patches occupied by New England cottontail and in microhabitat conditions suitable for New England cottontail. Occupancy models for five shrubland bird species further identified species-specific habitat associations. Generalized linear models showed that shrubland bird species richness was positively associated with herbaceous vegetation and low shrubs, indicating that shrublands managed for the purpose of cottontail colonization can also benefit a suite of shrubland birds before the habitat is dense enough to provide cover for cottontails. Our findings show that managing habitat for New England cottontail on a variety of site types can maintain a range of microhabitat conditions to support a high diversity of shrubland-obligate birds. These findings provide evidence for broad ecosystem benefits of managing for New England cottontail and exemplify the value of at-risk habitat specialists as conservation surrogates in imperiled ecosystems.</p>
Cross-seasonal effects in the American Woodcock: conditions prior to fall migration relate to migration strategy and its implications for conservation
<p>How post-breeding habitat quality and body composition of migratory birds carry over to influence fall migration strategies and residency merits consideration when creating cross-seasonal conservation plans, especially in breeding populations that are partial migrants. We assessed the influence of post-breeding habitat quality on departure body composition and fall migration patterns in a southern New England breeding population of American Woodcock (<em>Scolopax minor</em>). Woodcock that overwintered near breeding areas (<em>n</em>=5) had less fat upon capture in fall and used lower quality habitat during the fall than birds that eventually departed on migration (<em>n</em>=17). Woodcock that departed earlier were long-distance migrants that had inhabited higher-quality landscapes prior to migration, departed with less fat or similar fat stores, stopped over for shorter periods on migration, and arrived earlier on their more southerly wintering areas. In contrast, woodcock that departed later were short-distance migrants that had inhabited lower quality landscapes prior to migration yet stored similar or more fat upon departure, stopped over for longer periods on migration, and arrived relatively late to their more northerly wintering areas. These differences in migration strategies were evident under the same fall environmental conditions and did not appear related to individuals responding to their own condition as would be expected if they were class condition-based carry-over effects. As such, the southern New England breeding population of woodcock are best categorized as non-facultative partial migrants (i.e., includes residents, short-distance migrants, and long-distance migrants) that demonstrate weak connectivity between life stages; such populations are excellent for the study of the costs and benefits of migration. The stopover and wintering areas used by woodcock in the coastal mid-Atlantic deserve conservation and management attention in order to preserve critical habitat throughout their wintering range.</p>
Freshwater invertebrates - diversity and function of stream macroinvertebrates: Effects of habitat conversion and strategies for conservation
<b>Description: </b><p>Freshwater invertebrate communities from stream sites along a habitat disturbance gradient (including old growth forest, logged forest, oil palm with riparian buffers, and oil palm with no buffers) within the SAFE Project experimental area, SAFE surrounding area, Maliau Basin, and Danum Valley.</p><p><b>Project: </b>This dataset was collected as part of the following SAFE research project: <a href="https://www.safeproject.net/projects/project_view/121"><b>Diversity and function of stream macroinvertebrates: Effects of habitat conversion and strategies for conservation</b></a></p><p><b>Funding: </b>These data were collected as part of research funded by: </p><ul><li>Sime Darby Foundation (Research, SAFE Project)</li><li>NERC (Studentship, 1122589.0)</li><li>Proforest (Research)</li><li>Varley Gradwell Travelling Fellowship (Research)</li><li>Tim Whitmore Fund (Research)</li><li>Panton Trust (Research)</li><li>Cambridge University Commonwealth Fund (Research)</li></ul><p>This dataset is released under the CC-BY 4.0 licence, requiring that you cite the dataset in any outputs, but has the additional condition that you acknowledge the contribution of these funders in any outputs.</p><p></p><p><b>Permits: </b>These data were collected under permit from the following authorities:</p><ul><li>Sabah Biodiversity Centre (SABC) (Research licence JKM/MBS.1000-2/2(37))</li><li>Sabah Biodiversity Centre (SABC) (Research licence JKM/MBS.1000-2/2(68))</li><li>Sabah Biodiversity Centre (SABC) (Research licence JKM/MBS:1000-2/2(230))</li></ul><p></p><p><b>XML metadata: </b>GEMINI compliant metadata for this dataset is available <a href="https://www.safeproject.net/datasets/xml_metadata?id=6368114">here</a></p><p><b>Files: </b>This consists of 1 file: 2_Luke_Inverts_V4_mfh.xlsx</p><p><b>2_Luke_Inverts_V4_mfh.xlsx</b></p><p>This file contains dataset metadata and 7 data tables:</p><ol><li><p><b>Water striders (Gerromorpha)</b> (described in worksheet Gerro)</p><p>Description: Manually captured waterstriders. Rows represent potential functional group/body size x sample site/date combinations, but not each combination had individuals collected.</p><p>Number of fields: 66</p><p>Number of data rows: 33905</p><p>Fields: </p><ul><li><b>Locations</b>: Transect sampled (Field type: location)</li><li><b>Stream</b>: Stream IDs of where the bugs were collected (Field type: id)</li><li><b>Distance</b>: The 10-m section of the stream transect where bugs were collected (Field type: replicate)</li><li><b>CollectionDate</b>: Dates of when the bugs were collected (Field type: date)</li><li><b>Time</b>: The times of when the bugs were collected (Field type: replicate)</li><li><b>PotCode</b>: Pot ID. For example, 1 of 1 means there is only 1 pot for a particular Distance, 1 of 2 means it is the first pot out of 2 for a particular Distance, and so on (Field type: replicate)</li><li><b>ID</b>: The ID number for the pots, each Distance can consists of 1 to 3 pots of samples and each pot has its own ID (Field type: id)</li><li><b>HabitatType</b>: Habitat type (Field type: categorical)</li><li><b>HabitatTypeReplicate</b>: Replicate IDs for the habitat types. For example, the ID for stream 0m at 40-50m as the first replicate for LF/ Logged Forest is LF1.1, while for stream 0m at 20-30m is LF1.2, and so on (Field type: replicate)</li><li><b>SortDate</b>: Dates of when sortings were done (Field type: comments)</li><li><b>Family</b>: Family of the bugs collected (Field type: taxa)</li><li><b>Group</b>: Groups of the bugs based on body forms: 1) CGP (Cylindrostethinae, Gerrinae, and Ptilomerinae), 2) Halobatinae, and 3) Veliidae (Field type: taxa)</li><li><b>LifeStage</b>: Life stage of the bugs collected: either Juvenile (J) or Adult (A) (Field type: categorical trait)</li><li><b>Length</b>: The body length of the bugs collected (rounded) (Field type: numeric trait)</li><li><b>LengthRange</b>: The body length range of the bugs collected (Field type: id)</li><li><b>PredictedBiomass</b>: The predicted biomass of the bugs collected, calculated using power regression equations. Zeros indicate groups for which no individuals were present. a. Group CGP = Abundance in any of the cell from column W until BO * (0.04 * (the cell of the Column O (needs to be at the same row as the Abundance cell chosen from any of the column W until BO)/ representing the body length ^ 2.271)), b. Group Halobatinae = the same as above but with 0.072 and 2.218 as the coefficient a and b respectively, c. Group Veliidae = the same as above but with 0.041 and 2.32 as the coefficient a and b respectively. (Field type: numeric)</li><li><b>AdultWing</b>: Adult bug's ID based on the presence of wings (if the individual insect is a juvenile, the cell says 'None', instead of 'Winged' or 'Wingless') (Field type: categorical trait)</li><li><b>AdultWingAbund</b>: Adult bug's abundance based on the presence of wings (Field type: abundance)</li><li><b>PtilomeraMF</b>: Ptilomera sp. IDs based on sex: either male or female (Field type: categorical trait)</li><li><b>Note</b>: Notes about people who have sorted the bugs before Martina Harianja (if no one hasn't worked on a particular sample, it's written as 'None') (Field type: comments)</li><li><b>PtilomeraMFAbund</b>: Abundance of either male or female adult Ptilomera sp. (Field type: abundance)</li><li><b>4spot</b>: Abundance (Field type: abundance)</li><li><b>C.scrutator</b>: Abundance (Field type: abundance)</li><li><b>Cylindrosthetus.sp.</b>: Abundance (Field type: abundance)</li><li><b>Limnometra.sp.</b>: Abundance (Field type: abundance)</li><li><b>Metrocoris.sp.1</b>: Abundance (Field type: abundance)</li><li><b>Metrocoris.sp.2</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies15</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies20</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies24</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies25</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies27</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies28</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies29</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies30</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies31</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies33</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies34</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies35</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies36</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies37</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies38</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies4</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies40</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies41</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies42</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies43</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies44</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies45</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies46</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies47</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies6</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies7</b>: Abundance (Field type: abundance)</li><li><b>Morphospecies7.sp.2</b>: Abundance (Field type: abundance)</li><li><b>Potamometropsis.sp.</b>: Abundance (Field type: abundance)</li><li><b>Ptilomera.sp.</b>: Abundance (Field type: abundance)</li><li><b>Rhagovelia.sp.</b>: Abundance (Field type: abundance)</li><li><b>Rhagovelia.sp.2</b>: Abundance (Field type: abundance)</li><li><b>Rhagovelia.sp.3</b>: Abundance (Field type: abundance)</li><li><b>Rheumatogonus.sp.1</b>: Abundance (Field type: abundance)</li><li><b>Rheumatogonus.sp.2</b>: Abundance (Field type: abundance)</li><li><b>Strongylovelia.sp.</b>: Abundance (Field type: abundance)</li><li><b>Tenagogonus.sp.1</b>: Abundance (Field type: abundance)</li><li><b>Tenagogonus.sp.2</b>: Abundance (Field type: abundance)</li><li><b>Ventidius.sp.</b>: Abundance (Field type: abundance)</li><li><b>Ventidius.sp.2</b>: Abundance (Field type: abundance)</li></ul></li><li><p><b>10m Chironomids</b> (described in worksheet Chiron_10m)</p><p>Description: Sampled from the streambed using a Surber sampler in 2012/2013. Suber sample had quadrat area of 0.33m2 and 250 μm mesh net. Sampling done at regularly spaced points along the 200m long dragonfly transects.</p><p>Number of fields: 51</p><p>Number of data rows: 151</p><p>Fields: </p><ul><li><b>Locations</b>: Location within the SAFE landscape (Field type: location)</li><li><b>Stream</b>: Stream name (Field type: id)</li><li><b>Distance</b>: Distance along the stream transect (Field type: numeric)</li><li><b>StreamDistance</b>: Stream and distance ID (Field type: id)</li><li><b>PointLocation</b>: Point location on stream transect (Field type: location)</li><li><b>SampleDate</b>: Date sample was collected (Field type: date)</li><li><b>SampleTime</b>: Time sample was collected (Field type: time)</li><li><b>Cladotanytarsus6teeth</b>: Cladotanytarsus6teeth abundance (Field type: abundance)</li><li><b>Cladotanytarsus5teeth</b>: Cladotanytarsus5teeth abundance (Field type: abundance)</li><li><b>Orthocladius</b>: Orthocladius abundance (Field type: abundance)</li><li><b>CricotopusWorn</b>: CricotopusWorn abundance (Field type: abundance)</li><li><b>CricotopusCylindraceus</b>: CricotopusCylindraceus abundance (Field type: abundance)</li><li><b>CricotopusOliveri</b>: CricotopusOliveri abundance (Field type: abundance)</li><li><b>Thienemanniella</b>: Thienemanniella abundance (Field type: abundance)</li><li><b>Thienemanniella2</b>: Thienemanniella2 abundance (Field type: abundance)</li><li><b>KelianA</b>: KelianA abundance (Field type: abundance)</li><li><b>KelianB</b>: KelianB abundance (Field type: abundance)</li><li><b>KelianC</b>: KelianC abundance (Field type: abundance)</li><li><b>TanytarsusMendax</b>: TanytarsusMendax abundance (Field type: abundance)</li><li><b>TanytarsusNemorosus</b>: TanytarsusNemorosus abundance (Field type: abundance)</li><li><b>PolypedilumType2</b>: PolypedilumType2 abundance (Field type: abundance)</li><li><b>PolypedilumConvictum</b>: PolypedilumConvictum abundance (Field type: abundance)</li><li><b>PolypedilumSp3</b>: PolypedilumSp3 abundance (Field type: abundance)</li><li><b>Chironomini1stInstar</b>: Chironomini1stInstar abundance (Field type: abundance)</li><li><b>ChironominiGenusB</b>: ChironominiGenusB abundance (Field type: abundance)</li><li><b>ChironominiPhoto1</b>: ChironominiPhoto1 abundance (Field type: abundance)</li><li><b>ChironominiPhoto2</b>: ChironominiPhoto2 abundance (Field type: abundance)</li><li><b>ChironominiPhoto3</b>: ChironominiPhoto3 abundance (Field type: abundance)</li><li><b>ChironominiPhoto5</b>: ChironominiPhoto5 abundance (Field type: abundance)</li><li><b>CorynoneuraLobata</b>: CorynoneuraLobata abundance (Field type: abundance)</li><li><b>Thienemannimyia</b>: Thienemannimyia abundance (Field type: abundance)</li><li><b>Parametriocnemus</b>: Parametriocnemus abundance (Field type: abundance)</li><li><b>Ceratopogonidae</b>: Ceratopogonidae abundance (Field type: abundance)</li><li><b>Cardiocladius</b>: Cardiocladius abundance (Field type: abundance)</li><li><b>Ablabesmyia</b>: Ablabesmyia abundance (Field type: abundance)</li><li><b>Stenochironomus</b>: Stenochironomus abundance (Field type: abundance)</li><li><b>Cryptochironomus</b>: Cryptochironomus abundance (Field type: abundance)</li><li><b>Nanocladius</b>: Nanocladius abundance (Field type: abundance)</li><li><b>Stictochironomus</b>: Stictochironomus abundance (Field type: abundance)</li><li><b>Nilotanypus</b>: Nilotanypus abundance (Field type: abundance)</li><li><b>Rheotanytarsus</b>: Rheotanytarsus abundance (Field type: abundance)</li><li><b>RheocricotopusChalybeatus</b>: RheocricotopusChalybeatus abundance (Field type: abundance)</li><li><b>Dicrotendipes</b>: Dicrotendipes abundance (Field type: abundance)</li><li><b>Paratendipes</b>: Paratendipes abundance (Field type: abundance)</li><li><b>Pseudorthocladius</b>: Pseudorthocladius abundance (Field type: abundance)</li><li><b>Kiefferulus</b>: Kiefferulus abundance (Field type: abundance)</li><li><b>Paracladopelma</b>: Paracladopelma abundance (Field type: abundance)</li><li><b>Microtendipes</b>: Microtendipes abundance (Field type: abundance)</li><li><b>Eukiefferiella</b>: Eukiefferiella abundance (Field type: abundance)</li><li><b>Diamesinae</b>: Diamesinae abundance (Field type: abundance)</li><li><b>TanytarsiniSurfaceTooth</b>: TanytarsiniSurfaceTooth abundance (Field type: abundance)</li></ul></li><li><p><b>10m Ephemeroptera, Plecoptera, Tricoptera (EPT)</b> (described in worksheet EPTabun_10m)</p><p>Description: Sampled from the streambed using a Surber sampler in 2012/2013. Suber sample had quadrat area of 0.33m2 and 250 μm mesh net. Sampling done at regularly spaced points along the 200m long dragonfly transects.</p><p>Number of fields: 34</p><p>Number of data rows: 78</p><p>Fields: </p><ul><li><b>Locations</b>: Location within the SAFE landscape (Field type: location)</li><li><b>Stream</b>: Stream name (Field type: id)</li><li><b>StreamDistance</b>: Distance along the stream transect (Field type: id)</li><li><b>Distance</b>: Stream and distance ID (Field type: id)</li><li><b>PointLocation</b>: Point location on stream transect (Field type: location)</li><li><b>SampleDate</b>: Date sample was collected (Field type: date)</li><li><b>SampleTime</b>: Time sample was collected (Field type: time)</li><li><b>Baetidae</b>: Baetidae abundance (Field type: abundance)</li><li><b>Leptophlebiidae</b>: Leptophlebiidae abundance (Field type: abundance)</li><li><b>Heptageniidae</b>: Heptageniidae abundance (Field type: abundance)</li><li><b>Caenidae</b>: Caenidae abundance (Field type: abundance)</li><li><b>Tricorythidae</b>: Tricorythidae abundance (Field type: abundance)</li><li><b>Euthyplociidae</b>: Euthyplociidae abundance (Field type: abundance)</li><li><b>Potamanthidae</b>: Potamanthidae abundance (Field type: abundance)</li><li><b>Oligoneuriidae</b>: Oligoneuriidae abundance (Field type: abundance)</li><li><b>Ephemeridae</b>: Ephemeridae abundance (Field type: abundance)</li><li><b>EphemUnknown</b>: EphemUnknown abundance (Field type: abundance)</li><li><b>Perlidae</b>: Perlidae abundance (Field type: abundance)</li><li><b>Nemouridae</b>: Nemouridae abundance (Field type: abundance)</li><li><b>Leuctridae</b>: Leuctridae abundance (Field type: abundance)</li><li><b>Peltoperlidae</b>: Peltoperlidae abundance (Field type: abundance)</li><li><b>PlecopUnkown</b>: PlecopUnkown abundance (Field type: abundance)</li><li><b>Dipsuedopsidae</b>: Dipsuedopsidae abundance (Field type: abundance)</li><li><b>Hydropsychidae</b>: Hydropsychidae abundance (Field type: abundance)</li><li><b>Leptoceridae</b>: Leptoceridae abundance (Field type: abundance)</li><li><b>Xiphocentronidae</b>: Xiphocentronidae abundance (Field type: abundance)</li><li><b>Polycentropodidae</b>: Polycentropodidae abundance (Field type: abundance)</li><li><b>Psychomyiidae</b>: Psychomyiidae abundance (Field type: abundance)</li><li><b>Ecnomidae</b>: Ecnomidae abundance (Field type: abundance)</li><li><b>Philopotamidae</b>: Philopotamidae abundance (Field type: abundance)</li><li><b>Hydroptilidae</b>: Hydroptilidae abundance (Field type: abundance)</li><li><b>Lepidostomatidae</b>: Lepidostomatidae abundance (Field type: abundance)</li><li><b>Calamoceratidae</b>: Calamoceratidae abundance (Field type: abundance)</li><li><b>TrichopUnknown</b>: TrichopUnknown abundance (Field type: abundance)</li></ul></li><li><p><b>10m Odonata nymphs</b> (described in worksheet OdonataNymph)</p><p>Description: Sampled from the streambed using a Surber sampler in 2012/2013. Suber sample had quadrat area of 0.33m2 and 250 μm mesh net. Sampling done at regularly spaced points along the 200m long dragonfly transects.</p><p>Number of fields: 29</p><p>Number of data rows: 151</p><p>Fields: </p><ul><li><b>Locations</b>: Location within the SAFE landscape (Field type: location)</li><li><b>Stream</b>: Stream name (Field type: id)</li><li><b>Distance</b>: Distance along the stream transect (Field type: numeric)</li><li><b>StreamDistance</b>: Stream and distance ID (Field type: id)</li><li><b>SiteCode</b>: Point location on stream transect (Field type: location)</li><li><b>Date</b>: Date sample was collected (Field type: date)</li><li><b>Time</b>: Time sample was collected (Field type: time)</li><li><b>ChlorogomphidaeChlorogomphus</b>: ChlorogomphidaeChlorogomphus abundance (Field type: abundance)</li><li><b>GomphidaeLeptogomphus</b>: GomphidaeLeptogomphus abundance (Field type: abundance)</li><li><b>GomphidaeMegalogomphus</b>: GomphidaeMegalogomphus abundance (Field type: abundance)</li><li><b>GomphidaeBurmagomphus</b>: GomphidaeBurmagomphus abundance (Field type: abundance)</li><li><b>GomphidaeOnychogomphus</b>: GomphidaeOnychogomphus abundance (Field type: abundance)</li><li><b>GomphidaeGomphidia</b>: GomphidaeGomphidia abundance (Field type: abundance)</li><li><b>GomphidaeSinogomphus</b>: GomphidaeSinogomphus abundance (Field type: abundance)</li><li><b>GomphidaeHeliogomphus</b>: GomphidaeHeliogomphus abundance (Field type: abundance)</li><li><b>GomphidaeIctinogomphus</b>: GomphidaeIctinogomphus abundance (Field type: abundance)</li><li><b>GomphidaeUnknown</b>: GomphidaeUnknown abundance (Field type: abundance)</li><li><b>MacromiidaeUnknown1</b>: MacromiidaeUnknown1 abundance (Field type: abundance)</li><li><b>MacromiidaeMacromia</b>: MacromiidaeMacromia abundance (Field type: abundance)</li><li><b>MacromiidaeUnknown2</b>: MacromiidaeUnknown2 abundance (Field type: abundance)</li><li><b>LibellulidaeUnknown</b>: LibellulidaeUnknown abundance (Field type: abundance)</li><li><b>LibellulidaeTrithemis</b>: LibellulidaeTrithemis abundance (Field type: abundance)</li><li><b>EuphaeidaeEuphaea</b>: EuphaeidaeEuphaea abundance (Field type: abundance)</li><li><b>CalopterygidaeVestalis</b>: CalopterygidaeVestalis abundance (Field type: abundance)</li><li><b>PhilosinidaeRhinagrion</b>: PhilosinidaeRhinagrion abundance (Field type: abundance)</li><li><b>PlatystictidaeUnknown</b>: PlatystictidaeUnknown abundance (Field type: abundance)</li><li><b>LestidaeUnknown</b>: LestidaeUnknown abundance (Field type: abundance)</li><li><b>ChlorocyphidaeUnknown</b>: ChlorocyphidaeUnknown abundance (Field type: abundance)</li><li><b>Unknown</b>: Unknown abundance (Field type: abundance)</li></ul></li><li><p><b>10m benthic insects, order-level</b> (described in worksheet Order_10m)</p><p>Description: Sampled from the streambed using a Surber sampler in 2012/2013. Suber sample had quadrat area of 0.33m2 and 250 μm mesh net. Sampling done at regularly spaced points along the 200m long dragonfly transects.</p><p>Number of fields: 34</p><p>Number of data rows: 151</p><p>Fields: </p><ul><li><b>Locations</b>: Location within the SAFE landscape (Field type: location)</li><li><b>Stream</b>: Stream name (Field type: id)</li><li><b>Distance</b>: Distance along the stream transect (Field type: numeric)</li><li><b>StreamDistance</b>: Stream and distance ID (Field type: id)</li><li><b>PointLocations</b>: Point location on stream transect (Field type: location)</li><li><b>SampleDate</b>: Date sample was collected (Field type: date)</li><li><b>SampleTime</b>: Time sample was collected (Field type: time)</li><li><b>EphemeropteraWhole</b>: EphemeropteraWhole abundance (Field type: abundance)</li><li><b>EphemeropteraPart</b>: EphemeropteraPart abundance (Field type: abundance)</li><li><b>Ephemeroptera</b>: Ephemeroptera abundance (Field type: abundance)</li><li><b>PlecopteraWhole</b>: PlecopteraWhole abundance (Field type: abundance)</li><li><b>PlecopteraPart</b>: PlecopteraPart abundance (Field type: abundance)</li><li><b>Plecoptera</b>: Plecoptera abundance (Field type: abundance)</li><li><b>TrichopteraWhole</b>: TrichopteraWhole abundance (Field type: abundance)</li><li><b>TrichopteraPart</b>: TrichopteraPart abundance (Field type: abundance)</li><li><b>Trichoptera</b>: Trichoptera abundance (Field type: abundance)</li><li><b>ColeopteraLarvaeWhole</b>: ColeopteraLarvaeWhole abundance (Field type: abundance)</li><li><b>ColeopteraLarvaePart</b>: ColeopteraLarvaePart abundance (Field type: abundance)</li><li><b>ColeopteraAdultWhole</b>: ColeopteraAdultWhole abundance (Field type: abundance)</li><li><b>ColeopteraAdultPart</b>: ColeopteraAdultPart abundance (Field type: abundance)</li><li><b>Coleoptera</b>: Coleoptera abundance (Field type: abundance)</li><li><b>DipteraWhole</b>: DipteraWhole abundance (Field type: abundance)</li><li><b>DipteraPart</b>: DipteraPart abundance (Field type: abundance)</li><li><b>Diptera</b>: Diptera abundance (Field type: abundance)</li><li><b>OdonataWhole</b>: OdonataWhole abundance (Field type: abundance)</li><li><b>OdonataPart</b>: OdonataPart abundance (Field type: abundance)</li><li><b>Odonata</b>: Odonata abundance (Field type: abundance)</li><li><b>Heteroptera</b>: Heteroptera abundance (Field type: abundance)</li><li><b>Mites</b>: Mites abundance (Field type: abundance)</li><li><b>Isopods</b>: Isopods abundance (Field type: abundance)</li><li><b>Worms</b>: Worms abundance (Field type: abundance)</li><li><b>OtherWhole</b>: OtherWhole abundance (Field type: abundance)</li><li><b>OtherPart</b>: OtherPart abundance (Field type: abundance)</li><li><b>Other</b>: Other abundance (Field type: abundance)</li></ul></li><li><p><b>10m bottle traps, for crabs, shrimps, snails</b> (described in worksheet Bottletraps_nov2015)</p><p>Description: Crabs, shrimps, snails. Sampled using bottle traps baited with fish/bread. Sampling done at regularly spaced points along the 200m long dragonfly transects. </p><p>Number of fields: 13</p><p>Number of data rows: 999</p><p>Fields: </p><ul><li><b>Locations</b>: Location within the SAFE landscape (Field type: location)</li><li><b>Stream</b>: Stream name (Field type: id)</li><li><b>Date</b>: Date trap set (Field type: date)</li><li><b>ArrivalTime</b>: Trap set time (Field type: time)</li><li><b>LeavingTime</b>: Trap collection time (Field type: time)</li><li><b>Weather</b>: Weather comments (Field type: comments)</li><li><b>People</b>: Observer (Field type: comments)</li><li><b>Distance</b>: Distance along the stream transect (Field type: numeric)</li><li><b>IDnumber</b>: Trap number (Field type: id)</li><li><b>Shrimps</b>: Shrimps abundance (Field type: abundance)</li><li><b>Snails</b>: Snails abundance (Field type: abundance)</li><li><b>Crabs</b>: Crabs abundance (Field type: abundance)</li><li><b>Fish</b>: Fish abundance (Field type: abundance)</li></ul></li><li><p><b>200m transects, adult dragonflies</b> (described in worksheet Dragonflies_2012_2013)</p><p>Description: Adult dragonflies. Caught along 200m long transects using butterfly nets. </p><p>Number of fields: 23</p><p>Number of data rows: 1872</p><p>Fields: </p><ul><li><b>Location</b>: Location within the SAFE landscape (Field type: location)</li><li><b>Stream</b>: Stream name (Field type: id)</li><li><b>Date</b>: Distance along the stream transect (Field type: date)</li><li><b>Weather</b>: Stream and distance ID (Field type: comments)</li><li><b>WeatherIssues</b>: Weather issues (0 - no issues, 1 - issues) (Field type: numeric)</li><li><b>PeopleIssues</b>: People issues (0 - no issues, 1 - issues) (Field type: numeric)</li><li><b>People</b>: Observers (Field type: comments)</li><li><b>DragonflyNo</b>: Dragonfly catch number per day (Field type: id)</li><li><b>UniqueID</b>: Individual dragonfly ID (Field type: id)</li><li><b>Time</b>: Time of catch (Field type: time)</li><li><b>Photos</b>: How many photos were taken of that individual dragonfly (in order to assist with photo sorting later on) (Field type: id)</li><li><b>HeadColour</b>: Head colour (Field type: comments)</li><li><b>ThoraxColour</b>: Thorax colour (Field type: comments)</li><li><b>AbdomenColour</b>: Abdomen colour (Field type: comments)</li><li><b>WingColour</b>: Wing colour (Field type: comments)</li><li><b>Pair</b>: Whether a male/female mating pair or not (knowing this could sometimes help with ID decisions later on, especially for females which are poorly known) (Field type: categorical)</li><li><b>Point10m</b>: Point of catch along the transect (10m intervals along he transect) (Field type: numeric)</li><li><b>Habitat</b>: Habitat type (Field type: comments)</li><li><b>Activity</b>: What was the dragon fly doing (Field type: comments)</li><li><b>DateIDing</b>: Date of ID (Field type: date)</li><li><b>PeopleIDing</b>: Person Iding (JA= James Austin, RD= Rory Dow, SHL = Sarah Luke) (Field type: categorical)</li><li><b>Species</b>: Species of dragonfly (Field type: taxa)</li><li><b>MaleFemale</b>: Sex of dragonfly (Field type: categorical)</li></ul></li></ol><p><b>Date range: </b>2011-07-03 to 2015-04-18</p><p><b>Latitudinal extent: </b>4.5755 to 4.9618</p><p><b>Longitudinal extent: </b>116.9641 to 117.7965</p><p><b>Taxonomic coverage: </b><br> All taxon names are validated against the GBIF backbone taxonomy. If a dataset uses a synonym, the accepted usage is shown followed by the dataset usage in brackets. Taxa that cannot be validated, including new species and other unknown taxa, morphospecies, functional groups and taxonomic levels not used in the GBIF backbone are shown in square brackets.</p><div> -  Animalia <br> -  -  Annelida <br> -  -  Arthropoda <br> -  -  -  Crabs <br> -  -  -  Insecta <br> -  -  -  -  Coleoptera <br> -  -  -  -  Coleoptera <br> -  -  -  -  Coleoptera <br> -  -  -  -  Coleoptera <br> -  -  -  -  Coleoptera <br> -  -  -  -  Diptera <br> -  -  -  -  -  Ceratopogonidae <br> -  -  -  -  -  Chironomidae <br> -  -  -  -  -  -  <i>Ablabesmyia</i> <br> -  -  -  -  -  -  <i>Cardiocladius</i> <br> -  -  -  -  -  -  Chironomini1stInstar <br> -  -  -  -  -  -  ChironominiGenusB <br> -  -  -  -  -  -  ChironominiPhoto1 <br> -  -  -  -  -  -  ChironominiPhoto2 <br> -  -  -  -  -  -  ChironominiPhoto3 <br> -  -  -  -  -  -  ChironominiPhoto5 <br> -  -  -  -  -  -  <i>Cladotanytarsus</i> <br> -  -  -  -  -  -  <i>Cladotanytarsus</i> <br> -  -  -  -  -  -  <i>Cricotopus</i> <br> -  -  -  -  -  -  -  <i>Cricotopus cylindraceus</i> <br> -  -  -  -  -  -  -  <i>Cricotopus olivetus</i> <br> -  -  -  -  -  -  <i>Cryptochironomus</i> <br> -  -  -  -  -  -  Diamesinae <br> -  -  -  -  -  -  <i>Dicrotendipes</i> <br> -  -  -  -  -  -  <i>Eukiefferiella</i> <br> -  -  -  -  -  -  KelianA <br> -  -  -  -  -  -  KelianB <br> -  -  -  -  -  -  KelianC <br> -  -  -  -  -  -  <i>Kiefferulus</i> <br> -  -  -  -  -  -  <i>Microtendipes</i> <br> -  -  -  -  -  -  <i>Nanocladius</i> <br> -  -  -  -  -  -  <i>Nilotanypus</i> <br> -  -  -  -  -  -  <i>Orthocladius</i> <br> -  -  -  -  -  -  <i>Paracladopelma</i> <br> -  -  -  -  -  -  <i>Parametriocnemus</i> <br> -  -  -  -  -  -  <i>Paratendipes</i> <br> -  -  -  -  -  -  <i>Polypedilum</i> <br> -  -  -  -  -  -  -  <i>Polypedilum convictum</i> <br> -  -  -  -  -  -  <i>Polypedilum</i> <br> -  -  -  -  -  -  -  <i>Polypedilum convictum</i> <br> -  -  -  -  -  -  <i>Pseudorthocladius</i> <br> -  -  -  -  -  -  <i>Rheotanytarsus</i> <br> -  -  -  -  -  -  <i>Stenochironomus</i> <br> -  -  -  -  -  -  <i>Stictochironomus</i> <br> -  -  -  -  -  -  TanytarsiniSurfaceTooth <br> -  -  -  -  -  -  <i>Thienemanniella</i> <br> -  -  -  -  -  -  <i>Thienemanniella</i> <br> -  -  -  -  -  -  <i>Thienemannimyia</i> <br> -  -  -  -  -  -  <i>Corynoneura</i> <br> -  -  -  -  -  -  -  <i>Corynoneura lobata</i> <br> -  -  -  -  -  -  <i>Tanytarsus</i> <br> -  -  -  -  -  -  -  <i>Tanytarsus mendax</i> <br> -  -  -  -  -  -  -  <i>Tanytarsus nemorosus</i> <br> -  -  -  -  -  -  <i>Rheocricotopus</i> <br> -  -  -  -  -  -  -  <i>Rheocricotopus chalybeatus</i> <br> -  -  -  -  Diptera <br> -  -  -  -  -  Ceratopogonidae <br> -  -  -  -  -  Chironomidae <br> -  -  -  -  -  -  <i>Ablabesmyia</i> <br> -  -  -  -  -  -  <i>Cardiocladius</i> <br> -  -  -  -  -  -  Chironomini1stInstar <br> -  -  -  -  -  -  ChironominiGenusB <br> -  -  -  -  -  -  ChironominiPhoto1 <br> -  -  -  -  -  -  ChironominiPhoto2 <br> -  -  -  -  -  -  ChironominiPhoto3 <br> -  -  -  -  -  -  ChironominiPhoto5 <br> -  -  -  -  -  -  <i>Cladotanytarsus</i> <br> -  -  -  -  -  -  <i>Cladotanytarsus</i> <br> -  -  -  -  -  -  <i>Cricotopus</i> <br> -  -  -  -  -  -  -  <i>Cricotopus cylindraceus</i> <br> -  -  -  -  -  -  -  <i>Cricotopus olivetus</i> <br> -  -  -  -  -  -  <i>Cryptochironomus</i> <br> -  -  -  -  -  -  Diamesinae <br> -  -  -  -  -  -  <i>Dicrotendipes</i> <br> -  -  -  -  -  -  <i>Eukiefferiella</i> <br> -  -  -  -  -  -  KelianA <br> -  -  -  -  -  -  KelianB <br> -  -  -  -  -  -  KelianC <br> -  -  -  -  -  -  <i>Kiefferulus</i> <br> -  -  -  -  -  -  <i>Microtendipes</i> <br> -  -  -  -  -  -  <i>Nanocladius</i> <br> -  -  -  -  -  -  <i>Nilotanypus</i> <br> -  -  -  -  -  -  <i>Orthocladius</i> <br> -  -  -  -  -  -  <i>Paracladopelma</i> <br> -  -  -  -  -  -  <i>Parametriocnemus</i> <br> -  -  -  -  -  -  <i>Paratendipes</i> <br> -  -  -  -  -  -  <i>Polypedilum</i> <br> -  -  -  -  -  -  -  <i>Polypedilum convictum</i> <br> -  -  -  -  -  -  <i>Polypedilum</i> <br> -  -  -  -  -  -  -  <i>Polypedilum convictum</i> <br> -  -  -  -  -  -  <i>Pseudorthocladius</i> <br> -  -  -  -  -  -  <i>Rheotanytarsus</i> <br> -  -  -  -  -  -  <i>Stenochironomus</i> <br> -  -  -  -  -  -  <i>Stictochironomus</i> <br> -  -  -  -  -  -  TanytarsiniSurfaceTooth <br> -  -  -  -  -  -  <i>Thienemanniella</i> <br> -  -  -  -  -  -  <i>Thienemanniella</i> <br> -  -  -  -  -  -  <i>Thienemannimyia</i> <br> -  -  -  -  -  -  <i>Corynoneura</i> <br> -  -  -  -  -  -  -  <i>Corynoneura lobata</i> <br> -  -  -  -  -  -  <i>Tanytarsus</i> <br> -  -  -  -  -  -  -  <i>Tanytarsus mendax</i> <br> -  -  -  -  -  -  -  <i>Tanytarsus nemorosus</i> <br> -  -  -  -  -  -  <i>Rheocricotopus</i> <br> -  -  -  -  -  -  -  <i>Rheocricotopus chalybeatus</i> <br> -  -  -  -  Diptera <br> -  -  -  -  -  Ceratopogonidae <br> -  -  -  -  -  Chironomidae <br> -  -  -  -  -  -  <i>Ablabesmyia</i> <br> -  -  -  -  -  -  <i>Cardiocladius</i> <br> -  -  -  -  -  -  Chironomini1stInstar <br> -  -  -  -  -  -  ChironominiGenusB <br> -  -  -  -  -  -  ChironominiPhoto1 <br> -  -  -  -  -  -  ChironominiPhoto2 <br> -  -  -  -  -  -  ChironominiPhoto3 <br> -  -  -  -  -  -  ChironominiPhoto5 <br> -  -  -  -  -  -  <i>Cladotanytarsus</i> <br> -  -  -  -  -  -  <i>Cladotanytarsus</i> <br> -  -  -  -  -  -  <i>Cricotopus</i> <br> -  -  -  -  -  -  -  <i>Cricotopus cylindraceus</i> <br> -  -  -  -  -  -  -  <i>Cricotopus olivetus</i> <br> -  -  -  -  -  -  <i>Cryptochironomus</i> <br> -  -  -  -  -  -  Diamesinae <br> -  -  -  -  -  -  <i>Dicrotendipes</i> <br> -  -  -  -  -  -  <i>Eukiefferiella</i> <br> -  -  -  -  -  -  KelianA <br> -  -  -  -  -  -  KelianB <br> -  -  -  -  -  -  KelianC <br> -  -  -  -  -  -  <i>Kiefferulus</i> <br> -  -  -  -  -  -  <i>Microtendipes</i> <br> -  -  -  -  -  -  <i>Nanocladius</i> <br> -  -  -  -  -  -  <i>Nilotanypus</i> <br> -  -  -  -  -  -  <i>Orthocladius</i> <br> -  -  -  -  -  -  <i>Paracladopelma</i> <br> -  -  -  -  -  -  <i>Parametriocnemus</i> <br> -  -  -  -  -  -  <i>Paratendipes</i> <br> -  -  -  -  -  -  <i>Polypedilum</i> <br> -  -  -  -  -  -  -  <i>Polypedilum convictum</i> <br> -  -  -  -  -  -  <i>Polypedilum</i> <br> -  -  -  -  -  -  -  <i>Polypedilum convictum</i> <br> -  -  -  -  -  -  <i>Pseudorthocladius</i> <br> -  -  -  -  -  -  <i>Rheotanytarsus</i> <br> -  -  -  -  -  -  <i>Stenochironomus</i> <br> -  -  -  -  -  -  <i>Stictochironomus</i> <br> -  -  -  -  -  -  TanytarsiniSurfaceTooth <br> -  -  -  -  -  -  <i>Thienemanniella</i> <br> -  -  -  -  -  -  <i>Thienemanniella</i> <br> -  -  -  -  -  -  <i>Thienemannimyia</i> <br> -  -  -  -  -  -  <i>Corynoneura</i> <br> -  -  -  -  -  -  -  <i>Corynoneura lobata</i> <br> -  -  -  -  -  -  <i>Tanytarsus</i> <br> -  -  -  -  -  -  -  <i>Tanytarsus mendax</i> <br> -  -  -  -  -  -  -  <i>Tanytarsus nemorosus</i> <br> -  -  -  -  -  -  <i>Rheocricotopus</i> <br> -  -  -  -  -  -  -  <i>Rheocricotopus chalybeatus</i> <br> -  -  -  -  Ephemeroptera <br> -  -  -  -  -  Baetidae <br> -  -  -  -  -  Caenidae <br> -  -  -  -  -  Ephemeridae <br> -  -  -  -  -  Ephemeridae <br> -  -  -  -  -  Euthyplociidae <br> -  -  -  -  -  Heptageniidae <br> -  -  -  -  -  Leptophlebiidae <br> -  -  -  -  -  Oligoneuriidae <br> -  -  -  -  -  Potamanthidae <br> -  -  -  -  -  Tricorythidae <br> -  -  -  -  Ephemeroptera <br> -  -  -  -  -  Baetidae <br> -  -  -  -  -  Caenidae <br> -  -  -  -  -  Ephemeridae <br> -  -  -  -  -  Ephemeridae <br> -  -  -  -  -  Euthyplociidae <br> -  -  -  -  -  Heptageniidae <br> -  -  -  -  -  Leptophlebiidae <br> -  -  -  -  -  Oligoneuriidae <br> -  -  -  -  -  Potamanthidae <br> -  -  -  -  -  Tricorythidae <br> -  -  -  -  Ephemeroptera <br> -  -  -  -  -  Baetidae <br> -  -  -  -  -  Caenidae <br> -  -  -  -  -  Ephemeridae <br> -  -  -  -  -  Ephemeridae <br> -  -  -  -  -  Euthyplociidae <br> -  -  -  -  -  Heptageniidae <br> -  -  -  -  -  Leptophlebiidae <br> -  -  -  -  -  Oligoneuriidae <br> -  -  -  -  -  Potamanthidae <br> -  -  -  -  -  Tricorythidae <br> -  -  -  -  Odonata <br> -  -  -  -  -  Chlorocyphidae <br> -  -  -  -  -  -  <i>Rhinocypha</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha stygia</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha aurofulgens</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha humeralis</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha stygia</i> <br> -  -  -  -  -  -  <i>Libellago</i> <br> -  -  -  -  -  -  -  <i>Libellago phaethon</i> <br> -  -  -  -  -  -  -  <i>Libellago semiopaca</i> <br> -  -  -  -  -  -  <i>Heliocypha</i> <br> -  -  -  -  -  -  -  <i>Heliocypha biseriata</i> <br> -  -  -  -  -  -  -  <i>Heliocypha biseriata</i> <br> -  -  -  -  -  Gomphidae <br> -  -  -  -  -  -  <i>Burmagomphus</i> <br> -  -  -  -  -  -  -  <i>Burmagomphus insularis</i> <br> -  -  -  -  -  -  <i>Gomphidia</i> <br> -  -  -  -  -  -  <i>Heliogomphus</i> <br> -  -  -  -  -  -  -  <i>Heliogomphus blandulus</i> <br> -  -  -  -  -  -  <i>Ictinogomphus</i> <br> -  -  -  -  -  -  <i>Leptogomphus</i> <br> -  -  -  -  -  -  -  <i>Leptogomphus williamsoni</i> <br> -  -  -  -  -  -  <i>Megalogomphus</i> <br> -  -  -  -  -  -  <i>Onychogomphus</i> <br> -  -  -  -  -  -  <i>Sinogomphus</i> <br> -  -  -  -  -  -  <i>Phaenandrogomphus</i> <br> -  -  -  -  -  -  -  <i>Phaenandrogomphus safei</i> <br> -  -  -  -  -  Lestidae <br> -  -  -  -  -  Libellulidae <br> -  -  -  -  -  -  <i>Trithemis</i> <br> -  -  -  -  -  -  -  <i>Trithemis aurora</i> <br> -  -  -  -  -  -  -  <i>Trithemis festiva</i> <br> -  -  -  -  -  -  <i>Orthetrum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum chrysis</i> <br> -  -  -  -  -  -  -  <i>Orthetrum glaucum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum testaceum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum pruinosum</i> <br> -  -  -  -  -  -  -  -  <i>Orthetrum pruinosum schneideri</i> <br> -  -  -  -  -  -  <i>Tetrathemis</i> <br> -  -  -  -  -  -  <i>Lyriothemis</i> <br> -  -  -  -  -  -  -  <i>Lyriothemis cleis</i> <br> -  -  -  -  -  -  <i>Camacinia</i> <br> -  -  -  -  -  -  -  <i>Camacinia gigantea</i> <br> -  -  -  -  -  -  <i>Onychothemis</i> <br> -  -  -  -  -  -  -  <i>Onychothemis culminicola</i> <br> -  -  -  -  -  -  <i>Pantala</i> <br> -  -  -  -  -  -  -  <i>Pantala flavescens</i> <br> -  -  -  -  -  -  <i>Zygonyx</i> <br> -  -  -  -  -  -  -  <i>Zygonyx iris</i> <br> -  -  -  -  -  -  -  -  <i>Zygonyx iris errans</i> <br> -  -  -  -  -  -  <i>Cratilla</i> <br> -  -  -  -  -  -  -  <i>Cratilla lineata</i> <br> -  -  -  -  -  -  <i>Tyriobapta</i> <br> -  -  -  -  -  -  -  <i>Tyriobapta torrida</i> <br> -  -  -  -  -  -  <i>Neurothemis</i> <br> -  -  -  -  -  -  -  <i>Neurothemis fluctuans</i> <br> -  -  -  -  -  -  -  <i>Neurothemis ramburii</i> <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Platystictidae <br> -  -  -  -  -  -  <i>Drepanosticta</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta actaeon</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta rufostigma</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta versicolor</i> <br> -  -  -  -  -  Megapodagrionidae <br> -  -  -  -  -  -  <i>Rhinagrion</i> <br> -  -  -  -  -  -  -  <i>Rhinagrion elopurae</i> <br> -  -  -  -  -  Amphipterygidae <br> -  -  -  -  -  -  <i>Devadatta</i> <br> -  -  -  -  -  -  -  <i>Devadatta tanduk</i> <br> -  -  -  -  -  Platycnemididae <br> -  -  -  -  -  -  <i>Coeliccia</i> <br> -  -  -  -  -  -  -  <i>Coeliccia arcuata</i> <br> -  -  -  -  -  -  -  <i>Coeliccia borneensis</i> <br> -  -  -  -  -  -  -  <i>Coeliccia cyaneothorax</i> <br> -  -  -  -  -  -  <i>Copera</i> <br> -  -  -  -  -  -  -  <i>Copera vittata</i> <br> -  -  -  -  -  Protoneuridae <br> -  -  -  -  -  -  <i>Prodasineura</i> <br> -  -  -  -  -  -  -  <i>Prodasineura hosei</i> <br> -  -  -  -  -  -  -  <i>Prodasineura verticalis</i> <br> -  -  -  -  -  Euphaeidae <br> -  -  -  -  -  -  <i>Euphaea</i> <br> -  -  -  -  -  -  -  <i>Euphaea impar</i> <br> -  -  -  -  -  -  -  <i>Euphaea subcostalis</i> <br> -  -  -  -  -  -  <i>Dysphaea</i> <br> -  -  -  -  -  -  -  <i>Dysphaea dimidiata</i> <br> -  -  -  -  -  -  -  <i>Dysphaea ulu</i> <br> -  -  -  -  -  Aeshnidae <br> -  -  -  -  -  -  <i>Tetracanthagyna</i> <br> -  -  -  -  -  -  -  <i>Tetracanthagyna degorsi</i> <br> -  -  -  -  -  Cordulegastridae <br> -  -  -  -  -  -  <i>Chlorogomphus</i> <br> -  -  -  -  -  Corduliidae <br> -  -  -  -  -  -  <i>Macromia</i> <br> -  -  -  -  -  -  -  <i>Macromia westwoodii</i> <br> -  -  -  -  -  -  <i>Macromidia</i> <br> -  -  -  -  -  -  -  <i>Macromidia fulva</i> <br> -  -  -  -  -  Coenagrionidae <br> -  -  -  -  -  -  <i>Pseudagrion</i> <br> -  -  -  -  -  -  -  <i>Pseudagrion pilidorsum</i> <br> -  -  -  -  -  -  <i>Agriocnemis</i> <br> -  -  -  -  -  -  -  <i>Agriocnemis femina</i> <br> -  -  -  -  -  -  <i>Stenagrion</i> <br> -  -  -  -  -  -  -  <i>Stenagrion dubium</i> <br> -  -  -  -  -  Calopterygidae <br> -  -  -  -  -  -  <i>Vestalis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amaryllis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amnicola</i> <br> -  -  -  -  -  -  -  <i>Vestalis amoena</i> <br> -  -  -  -  -  -  -  <i>Vestalis anacolosa</i> <br> -  -  -  -  -  -  <i>Vestalis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amaryllis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amnicola</i> <br> -  -  -  -  -  -  -  <i>Vestalis amoena</i> <br> -  -  -  -  -  -  -  <i>Vestalis anacolosa</i> <br> -  -  -  -  -  -  <i>Neurobasis</i> <br> -  -  -  -  -  -  -  <i>Neurobasis longipes</i> <br> -  -  -  -  Odonata <br> -  -  -  -  -  Chlorocyphidae <br> -  -  -  -  -  -  <i>Rhinocypha</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha stygia</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha aurofulgens</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha humeralis</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha stygia</i> <br> -  -  -  -  -  -  <i>Libellago</i> <br> -  -  -  -  -  -  -  <i>Libellago phaethon</i> <br> -  -  -  -  -  -  -  <i>Libellago semiopaca</i> <br> -  -  -  -  -  -  <i>Heliocypha</i> <br> -  -  -  -  -  -  -  <i>Heliocypha biseriata</i> <br> -  -  -  -  -  -  -  <i>Heliocypha biseriata</i> <br> -  -  -  -  -  Gomphidae <br> -  -  -  -  -  -  <i>Burmagomphus</i> <br> -  -  -  -  -  -  -  <i>Burmagomphus insularis</i> <br> -  -  -  -  -  -  <i>Gomphidia</i> <br> -  -  -  -  -  -  <i>Heliogomphus</i> <br> -  -  -  -  -  -  -  <i>Heliogomphus blandulus</i> <br> -  -  -  -  -  -  <i>Ictinogomphus</i> <br> -  -  -  -  -  -  <i>Leptogomphus</i> <br> -  -  -  -  -  -  -  <i>Leptogomphus williamsoni</i> <br> -  -  -  -  -  -  <i>Megalogomphus</i> <br> -  -  -  -  -  -  <i>Onychogomphus</i> <br> -  -  -  -  -  -  <i>Sinogomphus</i> <br> -  -  -  -  -  -  <i>Phaenandrogomphus</i> <br> -  -  -  -  -  -  -  <i>Phaenandrogomphus safei</i> <br> -  -  -  -  -  Lestidae <br> -  -  -  -  -  Libellulidae <br> -  -  -  -  -  -  <i>Trithemis</i> <br> -  -  -  -  -  -  -  <i>Trithemis aurora</i> <br> -  -  -  -  -  -  -  <i>Trithemis festiva</i> <br> -  -  -  -  -  -  <i>Orthetrum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum chrysis</i> <br> -  -  -  -  -  -  -  <i>Orthetrum glaucum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum testaceum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum pruinosum</i> <br> -  -  -  -  -  -  -  -  <i>Orthetrum pruinosum schneideri</i> <br> -  -  -  -  -  -  <i>Tetrathemis</i> <br> -  -  -  -  -  -  <i>Lyriothemis</i> <br> -  -  -  -  -  -  -  <i>Lyriothemis cleis</i> <br> -  -  -  -  -  -  <i>Camacinia</i> <br> -  -  -  -  -  -  -  <i>Camacinia gigantea</i> <br> -  -  -  -  -  -  <i>Onychothemis</i> <br> -  -  -  -  -  -  -  <i>Onychothemis culminicola</i> <br> -  -  -  -  -  -  <i>Pantala</i> <br> -  -  -  -  -  -  -  <i>Pantala flavescens</i> <br> -  -  -  -  -  -  <i>Zygonyx</i> <br> -  -  -  -  -  -  -  <i>Zygonyx iris</i> <br> -  -  -  -  -  -  -  -  <i>Zygonyx iris errans</i> <br> -  -  -  -  -  -  <i>Cratilla</i> <br> -  -  -  -  -  -  -  <i>Cratilla lineata</i> <br> -  -  -  -  -  -  <i>Tyriobapta</i> <br> -  -  -  -  -  -  -  <i>Tyriobapta torrida</i> <br> -  -  -  -  -  -  <i>Neurothemis</i> <br> -  -  -  -  -  -  -  <i>Neurothemis fluctuans</i> <br> -  -  -  -  -  -  -  <i>Neurothemis ramburii</i> <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Platystictidae <br> -  -  -  -  -  -  <i>Drepanosticta</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta actaeon</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta rufostigma</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta versicolor</i> <br> -  -  -  -  -  Megapodagrionidae <br> -  -  -  -  -  -  <i>Rhinagrion</i> <br> -  -  -  -  -  -  -  <i>Rhinagrion elopurae</i> <br> -  -  -  -  -  Amphipterygidae <br> -  -  -  -  -  -  <i>Devadatta</i> <br> -  -  -  -  -  -  -  <i>Devadatta tanduk</i> <br> -  -  -  -  -  Platycnemididae <br> -  -  -  -  -  -  <i>Coeliccia</i> <br> -  -  -  -  -  -  -  <i>Coeliccia arcuata</i> <br> -  -  -  -  -  -  -  <i>Coeliccia borneensis</i> <br> -  -  -  -  -  -  -  <i>Coeliccia cyaneothorax</i> <br> -  -  -  -  -  -  <i>Copera</i> <br> -  -  -  -  -  -  -  <i>Copera vittata</i> <br> -  -  -  -  -  Protoneuridae <br> -  -  -  -  -  -  <i>Prodasineura</i> <br> -  -  -  -  -  -  -  <i>Prodasineura hosei</i> <br> -  -  -  -  -  -  -  <i>Prodasineura verticalis</i> <br> -  -  -  -  -  Euphaeidae <br> -  -  -  -  -  -  <i>Euphaea</i> <br> -  -  -  -  -  -  -  <i>Euphaea impar</i> <br> -  -  -  -  -  -  -  <i>Euphaea subcostalis</i> <br> -  -  -  -  -  -  <i>Dysphaea</i> <br> -  -  -  -  -  -  -  <i>Dysphaea dimidiata</i> <br> -  -  -  -  -  -  -  <i>Dysphaea ulu</i> <br> -  -  -  -  -  Aeshnidae <br> -  -  -  -  -  -  <i>Tetracanthagyna</i> <br> -  -  -  -  -  -  -  <i>Tetracanthagyna degorsi</i> <br> -  -  -  -  -  Cordulegastridae <br> -  -  -  -  -  -  <i>Chlorogomphus</i> <br> -  -  -  -  -  Corduliidae <br> -  -  -  -  -  -  <i>Macromia</i> <br> -  -  -  -  -  -  -  <i>Macromia westwoodii</i> <br> -  -  -  -  -  -  <i>Macromidia</i> <br> -  -  -  -  -  -  -  <i>Macromidia fulva</i> <br> -  -  -  -  -  Coenagrionidae <br> -  -  -  -  -  -  <i>Pseudagrion</i> <br> -  -  -  -  -  -  -  <i>Pseudagrion pilidorsum</i> <br> -  -  -  -  -  -  <i>Agriocnemis</i> <br> -  -  -  -  -  -  -  <i>Agriocnemis femina</i> <br> -  -  -  -  -  -  <i>Stenagrion</i> <br> -  -  -  -  -  -  -  <i>Stenagrion dubium</i> <br> -  -  -  -  -  Calopterygidae <br> -  -  -  -  -  -  <i>Vestalis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amaryllis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amnicola</i> <br> -  -  -  -  -  -  -  <i>Vestalis amoena</i> <br> -  -  -  -  -  -  -  <i>Vestalis anacolosa</i> <br> -  -  -  -  -  -  <i>Vestalis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amaryllis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amnicola</i> <br> -  -  -  -  -  -  -  <i>Vestalis amoena</i> <br> -  -  -  -  -  -  -  <i>Vestalis anacolosa</i> <br> -  -  -  -  -  -  <i>Neurobasis</i> <br> -  -  -  -  -  -  -  <i>Neurobasis longipes</i> <br> -  -  -  -  Odonata <br> -  -  -  -  -  Chlorocyphidae <br> -  -  -  -  -  -  <i>Rhinocypha</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha stygia</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha aurofulgens</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha humeralis</i> <br> -  -  -  -  -  -  -  <i>Rhinocypha stygia</i> <br> -  -  -  -  -  -  <i>Libellago</i> <br> -  -  -  -  -  -  -  <i>Libellago phaethon</i> <br> -  -  -  -  -  -  -  <i>Libellago semiopaca</i> <br> -  -  -  -  -  -  <i>Heliocypha</i> <br> -  -  -  -  -  -  -  <i>Heliocypha biseriata</i> <br> -  -  -  -  -  -  -  <i>Heliocypha biseriata</i> <br> -  -  -  -  -  Gomphidae <br> -  -  -  -  -  -  <i>Burmagomphus</i> <br> -  -  -  -  -  -  -  <i>Burmagomphus insularis</i> <br> -  -  -  -  -  -  <i>Gomphidia</i> <br> -  -  -  -  -  -  <i>Heliogomphus</i> <br> -  -  -  -  -  -  -  <i>Heliogomphus blandulus</i> <br> -  -  -  -  -  -  <i>Ictinogomphus</i> <br> -  -  -  -  -  -  <i>Leptogomphus</i> <br> -  -  -  -  -  -  -  <i>Leptogomphus williamsoni</i> <br> -  -  -  -  -  -  <i>Megalogomphus</i> <br> -  -  -  -  -  -  <i>Onychogomphus</i> <br> -  -  -  -  -  -  <i>Sinogomphus</i> <br> -  -  -  -  -  -  <i>Phaenandrogomphus</i> <br> -  -  -  -  -  -  -  <i>Phaenandrogomphus safei</i> <br> -  -  -  -  -  Lestidae <br> -  -  -  -  -  Libellulidae <br> -  -  -  -  -  -  <i>Trithemis</i> <br> -  -  -  -  -  -  -  <i>Trithemis aurora</i> <br> -  -  -  -  -  -  -  <i>Trithemis festiva</i> <br> -  -  -  -  -  -  <i>Orthetrum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum chrysis</i> <br> -  -  -  -  -  -  -  <i>Orthetrum glaucum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum testaceum</i> <br> -  -  -  -  -  -  -  <i>Orthetrum pruinosum</i> <br> -  -  -  -  -  -  -  -  <i>Orthetrum pruinosum schneideri</i> <br> -  -  -  -  -  -  <i>Tetrathemis</i> <br> -  -  -  -  -  -  <i>Lyriothemis</i> <br> -  -  -  -  -  -  -  <i>Lyriothemis cleis</i> <br> -  -  -  -  -  -  <i>Camacinia</i> <br> -  -  -  -  -  -  -  <i>Camacinia gigantea</i> <br> -  -  -  -  -  -  <i>Onychothemis</i> <br> -  -  -  -  -  -  -  <i>Onychothemis culminicola</i> <br> -  -  -  -  -  -  <i>Pantala</i> <br> -  -  -  -  -  -  -  <i>Pantala flavescens</i> <br> -  -  -  -  -  -  <i>Zygonyx</i> <br> -  -  -  -  -  -  -  <i>Zygonyx iris</i> <br> -  -  -  -  -  -  -  -  <i>Zygonyx iris errans</i> <br> -  -  -  -  -  -  <i>Cratilla</i> <br> -  -  -  -  -  -  -  <i>Cratilla lineata</i> <br> -  -  -  -  -  -  <i>Tyriobapta</i> <br> -  -  -  -  -  -  -  <i>Tyriobapta torrida</i> <br> -  -  -  -  -  -  <i>Neurothemis</i> <br> -  -  -  -  -  -  -  <i>Neurothemis fluctuans</i> <br> -  -  -  -  -  -  -  <i>Neurothemis ramburii</i> <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Macromiidae <br> -  -  -  -  -  Platystictidae <br> -  -  -  -  -  -  <i>Drepanosticta</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta actaeon</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta rufostigma</i> <br> -  -  -  -  -  -  -  <i>Drepanosticta versicolor</i> <br> -  -  -  -  -  Megapodagrionidae <br> -  -  -  -  -  -  <i>Rhinagrion</i> <br> -  -  -  -  -  -  -  <i>Rhinagrion elopurae</i> <br> -  -  -  -  -  Amphipterygidae <br> -  -  -  -  -  -  <i>Devadatta</i> <br> -  -  -  -  -  -  -  <i>Devadatta tanduk</i> <br> -  -  -  -  -  Platycnemididae <br> -  -  -  -  -  -  <i>Coeliccia</i> <br> -  -  -  -  -  -  -  <i>Coeliccia arcuata</i> <br> -  -  -  -  -  -  -  <i>Coeliccia borneensis</i> <br> -  -  -  -  -  -  -  <i>Coeliccia cyaneothorax</i> <br> -  -  -  -  -  -  <i>Copera</i> <br> -  -  -  -  -  -  -  <i>Copera vittata</i> <br> -  -  -  -  -  Protoneuridae <br> -  -  -  -  -  -  <i>Prodasineura</i> <br> -  -  -  -  -  -  -  <i>Prodasineura hosei</i> <br> -  -  -  -  -  -  -  <i>Prodasineura verticalis</i> <br> -  -  -  -  -  Euphaeidae <br> -  -  -  -  -  -  <i>Euphaea</i> <br> -  -  -  -  -  -  -  <i>Euphaea impar</i> <br> -  -  -  -  -  -  -  <i>Euphaea subcostalis</i> <br> -  -  -  -  -  -  <i>Dysphaea</i> <br> -  -  -  -  -  -  -  <i>Dysphaea dimidiata</i> <br> -  -  -  -  -  -  -  <i>Dysphaea ulu</i> <br> -  -  -  -  -  Aeshnidae <br> -  -  -  -  -  -  <i>Tetracanthagyna</i> <br> -  -  -  -  -  -  -  <i>Tetracanthagyna degorsi</i> <br> -  -  -  -  -  Cordulegastridae <br> -  -  -  -  -  -  <i>Chlorogomphus</i> <br> -  -  -  -  -  Corduliidae <br> -  -  -  -  -  -  <i>Macromia</i> <br> -  -  -  -  -  -  -  <i>Macromia westwoodii</i> <br> -  -  -  -  -  -  <i>Macromidia</i> <br> -  -  -  -  -  -  -  <i>Macromidia fulva</i> <br> -  -  -  -  -  Coenagrionidae <br> -  -  -  -  -  -  <i>Pseudagrion</i> <br> -  -  -  -  -  -  -  <i>Pseudagrion pilidorsum</i> <br> -  -  -  -  -  -  <i>Agriocnemis</i> <br> -  -  -  -  -  -  -  <i>Agriocnemis femina</i> <br> -  -  -  -  -  -  <i>Stenagrion</i> <br> -  -  -  -  -  -  -  <i>Stenagrion dubium</i> <br> -  -  -  -  -  Calopterygidae <br> -  -  -  -  -  -  <i>Vestalis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amaryllis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amnicola</i> <br> -  -  -  -  -  -  -  <i>Vestalis amoena</i> <br> -  -  -  -  -  -  -  <i>Vestalis anacolosa</i> <br> -  -  -  -  -  -  <i>Vestalis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amaryllis</i> <br> -  -  -  -  -  -  -  <i>Vestalis amnicola</i> <br> -  -  -  -  -  -  -  <i>Vestalis amoena</i> <br> -  -  -  -  -  -  -  <i>Vestalis anacolosa</i> <br> -  -  -  -  -  -  <i>Neurobasis</i> <br> -  -  -  -  -  -  -  <i>Neurobasis longipes</i> <br> -  -  -  -  Plecoptera <br> -  -  -  -  -  Leuctridae <br> -  -  -  -  -  Nemouridae <br> -  -  -  -  -  Peltoperlidae <br> -  -  -  -  -  Perlidae <br> -  -  -  -  Plecoptera <br> -  -  -  -  -  Leuctridae <br> -  -  -  -  -  Nemouridae <br> -  -  -  -  -  Peltoperlidae <br> -  -  -  -  -  Perlidae <br> -  -  -  -  Plecoptera <br> -  -  -  -  -  Leuctridae <br> -  -  -  -  -  Nemouridae <br> -  -  -  -  -  Peltoperlidae <br> -  -  -  -  -  Perlidae <br> -  -  -  -  Plecoptera <br> -  -  -  -  -  Leuctridae <br> -  -  -  -  -  Nemouridae <br> -  -  -  -  -  Peltoperlidae <br> -  -  -  -  -  Perlidae <br> -  -  -  -  Trichoptera <br> -  -  -  -  -  Calamoceratidae <br> -  -  -  -  -  Dipseudopsidae <br> -  -  -  -  -  Ecnomidae <br> -  -  -  -  -  Hydropsychidae <br> -  -  -  -  -  Hydroptilidae <br> -  -  -  -  -  Lepidostomatidae <br> -  -  -  -  -  Leptoceridae <br> -  -  -  -  -  Philopotamidae <br> -  -  -  -  -  Polycentropodidae <br> -  -  -  -  -  Psychomyiidae <br> -  -  -  -  -  Xiphocentronidae <br> -  -  -  -  Trichoptera <br> -  -  -  -  -  Calamoceratidae <br> -  -  -  -  -  Dipseudopsidae <br> -  -  -  -  -  Ecnomidae <br> -  -  -  -  -  Hydropsychidae <br> -  -  -  -  -  Hydroptilidae <br> -  -  -  -  -  Lepidostomatidae <br> -  -  -  -  -  Leptoceridae <br> -  -  -  -  -  Philopotamidae <br> -  -  -  -  -  Polycentropodidae <br> -  -  -  -  -  Psychomyiidae <br> -  -  -  -  -  Xiphocentronidae <br> -  -  -  -  Trichoptera <br> -  -  -  -  -  Calamoceratidae <br> -  -  -  -  -  Dipseudopsidae <br> -  -  -  -  -  Ecnomidae <br> -  -  -  -  -  Hydropsychidae <br> -  -  -  -  -  Hydroptilidae <br> -  -  -  -  -  Lepidostomatidae <br> -  -  -  -  -  Leptoceridae <br> -  -  -  -  -  Philopotamidae <br> -  -  -  -  -  Polycentropodidae <br> -  -  -  -  -  Psychomyiidae <br> -  -  -  -  -  Xiphocentronidae <br> -  -  -  -  Hemiptera <br> -  -  -  -  -  Heteroptera <br> -  -  -  -  -  Gerridae <br> -  -  -  -  -  -  Halobatinae <br> -  -  -  -  -  -  [4spot] <br> -  -  -  -  -  -  [Morphospecies15] <br> -  -  -  -  -  -  [Morphospecies25] <br> -  -  -  -  -  -  [Morphospecies27] <br> -  -  -  -  -  -  [Morphospecies28] <br> -  -  -  -  -  -  [Morphospecies29] <br> -  -  -  -  -  -  [Morphospecies33] <br> -  -  -  -  -  -  [Morphospecies34] <br> -  -  -  -  -  -  [Morphospecies35] <br> -  -  -  -  -  -  [Morphospecies42] <br> -  -  -  -  -  -  [Morphospecies46] <br> -  -  -  -  -  -  [Morphospecies47] <br> -  -  -  -  -  -  [Morphospecies6] <br> -  -  -  -  -  -  <i>Limnometra</i> <br> -  -  -  -  -  -  -  [Limnometra.sp.] <br> -  -  -  -  -  -  <i>Tenagogonus</i> <br> -  -  -  -  -  -  -  [Tenagogonus.sp.1] <br> -  -  -  -  -  -  -  [Tenagogonus.sp.2] <br> -  -  -  -  -  -  <i>Ptilomera</i> <br> -  -  -  -  -  -  -  [Ptilomera.sp.] <br> -  -  -  -  -  -  <i>Potamometropsis</i> <br> -  -  -  -  -  -  -  [Potamometropsis.sp.] <br> -  -  -  -  -  -  <i>Metrocoris</i> <br> -  -  -  -  -  -  -  [Metrocoris.sp.1] <br> -  -  -  -  -  -  -  [Metrocoris.sp.2] <br> -  -  -  -  -  -  <i>Cylindrostethus</i> <br> -  -  -  -  -  -  -  <i>Cylindrostethus scrutator</i> <br> -  -  -  -  -  -  -  [Cylindrostethus.sp.] <br> -  -  -  -  -  Veliidae <br> -  -  -  -  -  -  [Morphospecies20] <br> -  -  -  -  -  -  [Morphospecies24] <br> -  -  -  -  -  -  [Morphospecies30] <br> -  -  -  -  -  -  [Morphospecies31] <br> -  -  -  -  -  -  [Morphospecies36] <br> -  -  -  -  -  -  [Morphospecies37] <br> -  -  -  -  -  -  [Morphospecies38] <br> -  -  -  -  -  -  [Morphospecies4] <br> -  -  -  -  -  -  [Morphospecies40] <br> -  -  -  -  -  -  [Morphospecies41] <br> -  -  -  -  -  -  [Morphospecies43] <br> -  -  -  -  -  -  [Morphospecies44] <br> -  -  -  -  -  -  [Morphospecies45] <br> -  -  -  -  -  -  [Morphospecies7] <br> -  -  -  -  -  -  [Morphospecies7.sp.2] <br> -  -  -  -  -  -  <i>Rhagovelia</i> <br> -  -  -  -  -  -  -  [Rhagovelia.sp.] <br> -  -  -  -  -  -  -  [Rhagovelia.sp.2] <br> -  -  -  -  -  -  -  [Rhagovelia.sp.3] <br> -  -  -  -  -  -  <i>Strongylovelia</i> <br> -  -  -  -  -  -  -  [Strongylovelia.sp.] <br> -  -  -  -  -  Gerridae <br> -  -  -  -  -  -  Halobatinae <br> -  -  -  -  -  -  [4spot] <br> -  -  -  -  -  -  [Morphospecies15] <br> -  -  -  -  -  -  [Morphospecies25] <br> -  -  -  -  -  -  [Morphospecies27] <br> -  -  -  -  -  -  [Morphospecies28] <br> -  -  -  -  -  -  [Morphospecies29] <br> -  -  -  -  -  -  [Morphospecies33] <br> -  -  -  -  -  -  [Morphospecies34] <br> -  -  -  -  -  -  [Morphospecies35] <br> -  -  -  -  -  -  [Morphospecies42] <br> -  -  -  -  -  -  [Morphospecies46] <br> -  -  -  -  -  -  [Morphospecies47] <br> -  -  -  -  -  -  [Morphospecies6] <br> -  -  -  -  -  -  <i>Limnometra</i> <br> -  -  -  -  -  -  -  [Limnometra.sp.] <br> -  -  -  -  -  -  <i>Tenagogonus</i> <br> -  -  -  -  -  -  -  [Tenagogonus.sp.1] <br> -  -  -  -  -  -  -  [Tenagogonus.sp.2] <br> -  -  -  -  -  -  <i>Ptilomera</i> <br> -  -  -  -  -  -  -  [Ptilomera.sp.] <br> -  -  -  -  -  -  <i>Potamometropsis</i> <br> -  -  -  -  -  -  -  [Potamometropsis.sp.] <br> -  -  -  -  -  -  <i>Metrocoris</i> <br> -  -  -  -  -  -  -  [Metrocoris.sp.1] <br> -  -  -  -  -  -  -  [Metrocoris.sp.2] <br> -  -  -  -  -  -  <i>Cylindrostethus</i> <br> -  -  -  -  -  -  -  <i>Cylindrostethus scrutator</i> <br> -  -  -  -  -  -  -  [Cylindrostethus.sp.] <br> -  -  -  -  -  Macroveliidae <br> -  -  -  -  -  -  <i>Rheumatogonus</i> <br> -  -  -  -  -  -  -  [Rheumatogonus.sp.1] <br> -  -  -  -  -  -  -  [Rheumatogonus.sp.2] <br> -  -  -  -  -  -  <i>Ventidius</i> <br> -  -  -  -  -  -  -  [Ventidius.sp.] <br> -  -  -  -  -  -  -  [Ventidius.sp.2] <br> -  -  -  Shrimps <br> -  -  -  Arachnida <br> -  -  -  -  Mites <br> -  -  -  Malacostraca <br> -  -  -  -  Isopoda <br> -  -  Mollusca <br> -  -  -  Gastropoda <br> -  -  Chordata <br> -  -  -  Actinopterygii <br></div><p></p>
Niche dynamics of Memecylon in Sri Lanka: distribution patterns, climate change effects, and conservation priorities
<p><b>Aim</b>: Recent climate projections have shown that the distribution of organisms in island biotas is highly affected by climate change. Here, we present the results of the analysis of niche dynamics of a plant group, <i>Memecylon</i> on Sri Lanka, an island, using species occurrences and climate data. We aim to determine which climate variables explain current distribution, model how climate change impacts the availability of suitable habitat for <i>Memecylon,</i> and determine conservation priority areas for Sri Lankan <i>Memecylon</i>.</p> <p><b>Location</b>: Sri Lanka</p> <p><b>Methods</b>: We used georeferenced occurrence data of Sri Lankan <i>Memecylon</i> to develop ecological niche models and assess both current and future potential distributions under six climate change scenarios in 2041-2060 and 2061-2080. We also overlaid land-cover, and protected area maps and performed a gap analysis to understand the impacts of land-cover changes on <i>Memecylon</i> distributions and propose new areas for conservation.</p> <p><b>Results</b>: Differences among suitable habitats of <i>Memecylon</i> were found to be related to patterns of endemism. Under varying future climate scenarios, endemic groups were predicted to experience habitat shifts, gains, or losses. The narrow endemic <i>Memecylon </i>restricted to the montane zone were predicted to be the most impacted by climate change. Projections also indicated that changes in species' habitats can be expected as early as 2041-2060. Gap analysis showed that while narrow endemic categories are considerably protected as demonstrated by their overlap with protected areas, more conservation efforts in Sri Lankan forests containing wide endemic and non-endemic <i>Memecylon</i> are needed.</p> <p><b>Main conclusions</b>: This research helped clarify general patterns of responses of Sri Lankan <i>Memecylon </i>to global climate change. Data from this study are useful for designing measures aimed at filling the gaps in forest conservation on this island.</p>
Modeling liquid transport in the Earth's mantle as two-phase flow: Effect of an enforced positive porosity on liquid flow and mass conservation
<p>These data files include the raw data for the figures shown in Lee et al. titled as 'Modeling liquid transport in the Earth’s mantle as two-phase flow: Effect of an enforced positive porosity on liquid flow and mass conservation'. <br> </p>
Data supplementing Lichtenberg et al. (2023) Differential effects of soil conservation practices on arthropods and crop yields. Journal of Applied Entomology
<p>This dataset contains data and scripts that supplement the publication</p> <p>Lichtenberg et al. Differential effects of soil conservation practices on arthropods and crop yields. J. Appl. Entomol. 147: 931-940. <a href="https://doi.org/10.1111/jen.13188">https://doi.org/10.1111/jen.13188</a></p> <p>Please cite the above article if you use any of the included data or code.</p> <p>Files are described in README.md.</p>
The Effects of Fibrinogen Concentrate Infusion on Blood Loss and Allogeneic Blood Conservation in Scoliosis Surgery
ClinicalTrials.gov study NCT03183479. IPD Sharing: YES. Countries: 1. Publications: 1.
A Randomized Controlled Trial on the Effectiveness of Early Versus Conservative Rehabilitation Following Rotator Cuff Repair
ClinicalTrials.gov study NCT07324174. IPD Sharing: NO. Countries: 1. Publications: 26.
Land use and ecosystem service value spatiotemporal dynamics, topographic gradient effect and their driving factors in typical alpine ecosystems of the east Qinghai-Tibet Plateau: Implications for conservation and development
Open the record for dataset details and reuse information.
Data from: Variation and conservation implications of the effectiveness of anti-bear interventions
Open the record for dataset details and reuse information.
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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.
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.
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.
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.
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.