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282 results for “Montenegro”
Figures 11–13 in Abrolophus balkanicus sp. nov. from Montenegro, with redescriptions of A. stanislavae (Haitlinger, 1986) and A. wratislaviensis (Haitlinger, 1986) and notes on A. podorasensis (Haitlinger, 2007) (Acari: Erythraeidae)
Figures 11–13. Abrolophus stanislavae (Haitlinger) (larva). 11. Ventral view of idiosoma; 12. Ventral view (right) and dorsal view of gnathosoma (left); 13. Palptarsus.
Figures 19–21 in Abrolophus balkanicus sp. nov. from Montenegro, with redescriptions of A. stanislavae (Haitlinger, 1986) and A. wratislaviensis (Haitlinger, 1986) and notes on A. podorasensis (Haitlinger, 2007) (Acari: Erythraeidae)
Figures 19–21. Abrolophus wratislaviensis (Haitlinger) (larva). 19. Ventral view of idiosoma; 20. Ventral view (right) and dorsal view of gnathosoma (right); 21. Palptarsus.
Figures 3–5 in Abrolophus balkanicus sp. nov. from Montenegro, with redescriptions of A. stanislavae (Haitlinger, 1986) and A. wratislaviensis (Haitlinger, 1986) and notes on A. podorasensis (Haitlinger, 2007) (Acari: Erythraeidae)
Figures 3–5. Abrolophus balkanicus sp. nov. (larva). 3. Ventral view of idiosoma; 4. Ventral view (right) and dorsal view of gnathosoma (left); 5. Palptarsus.
Figures 17–18 in Abrolophus balkanicus sp. nov. from Montenegro, with redescriptions of A. stanislavae (Haitlinger, 1986) and A. wratislaviensis (Haitlinger, 1986) and notes on A. podorasensis (Haitlinger, 2007) (Acari: Erythraeidae)
Figures 17–18. Abrolophus wratislaviensis (Haitlinger) (larva). 17. Dorsal view of idiosoma; 18. Scutum.
National Checklists: Montenegro Species List
Data from: GBIF.org (23 January 2025) GBIF Occurrence Download <a href="https://doi.org/10.15468/dl.vd2ajk" target="_blank" rel="noopener">https://doi.org/10.15468/dl.vd2ajk</a>
Results from the monitoring of veterinary medicinal product residues and other substances in live animals and animal products - Montenegro
<p>This dataset contains the monitoring results of veterinary medicinal product residues and other substances measured in live animals and animal products analysed by the national competent authority of Montenegro. The presence of unauthorised substances, residues of veterinary medicinal products in food may pose a risk factor for public health.</p> <p>For this reason and in order to ensure a high level of consumer protection, a comprehensive legislative framework has been established in the European Union (EU) which defines maximum limits permitted in food and monitoring programmes for the control of the presence of these substances in the food chain. Regulation (EU) No 37/2010 establishes maximum limits for residues of veterinary medicinal products in food-producing animals and animal products. Maximum residue levels for pesticides in or on food and feed of plant and animal origin are laid down in Regulation (EC) No 396/2005. Commission Implementing Regulation (EU) 2022/1646 lays down practical arrangements for and specific content of official controls of the use of veterinary medicinal products in live animals and products of animal origin through three different official national control plans: a national risk-based control plan for production in the Member States, a national randomised surveillance plan for production in the Member States and a national risk-based control plan for third-country imports. Additionally, Commission Delegated Regulation (EU) 2022/1644 lays down the range of samples and stage of production, processing and distribution at which the samples are to be taken.</p> <p>Since 2018 until 2022, the data on the national residue monitoring plan were reported to EFSA in accordance with Council Directive 96/23/EC.</p> <p>The chemical monitoring data collected and published by EFSA include the analytical results provided by EU Member States and three pre-accession countries: Bosnia-Herzegovina, Montenegro, North Macedonia and Serbia.</p> <p>The dataset contains the results of laboratory tests from samples taken from bovines, pigs, sheep, goats, horses, poultry, rabbits, farmed game, wild game aquaculture, milk, eggs and honey.</p> <p>The dataset contains the results of laboratory tests from samples taken from bovines, pigs, sheep, goats, horses, poultry, rabbits, farmed game, wild game aquaculture, milk, eggs and honey, and from 2023 also samples from casings, insects and reptiles.</p> <p>Targeted samples are taken with the aim of detecting illegal treatment or controlling compliance with the maximum levels laid down in the relevant legislation. This means that, in their national plans Member States target the groups of animals (species, gender, age) where the probability of finding residues is the highest. Conversely, the objective of random sampling is to collect significant data to evaluate, for example, consumer exposure to a specific substance.</p> <p>Suspect samples are taken as a consequence of i) non-compliant results on samples taken in accordance with the control plans, ii) possession or presence of prohibited substances at any point during manufacture, storage, distribution or sale through the food and feed production chain, or iii) suspicion or evidence of illegal treatment or non-compliance with the withdrawal period for an authorised medicinal veterinary product.</p> <p>Residues of pharmacologically active substances mean active substances, excipients or degradation products and their metabolites, which remain in food.</p> <p>Unauthorised substances mean substances that are not authorised as veterinary medicinal products or as a feed additive under European Union legislation.</p> <p>Prohibited substances mean substances which are prohibited for use in food producing animals according to the European Union legislation.</p> <p>Non-compliant sample is a sample that has been analysed for the presence of one or more substances and failed to comply with the legal provisions for at least one substance. Thus, a sample can be non-compliant for one or more substances.</p> <p><strong>REPORTING AUTHORITIES CONTRIBUTING TO EACH DATA COLLECTION:</strong></p> <p>VMPR_2023 – Center for Eco-Toxicological Research</p> <p>VMPR_2022 – Center for Eco-Toxicological Research</p> <p>VMPR_2021 – Center for Eco-Toxicological Research</p> <p>VMPR_2020 – Center for Eco-Toxicological Research</p> <p>VMPR_2019 – Center for Eco-Toxicological Research</p> <p>VMPR_2018 – Center for Eco-Toxicological Research - Administration for Food safety, Veterinary and Phytosanitary Affairs</p> <p> </p>
Fig. 1 in Colias caucasica balcanica (Pieridae) rediscovered in Montenegro, with additional new records for Serbia
Fig. 1. Antheraea yamamai (Guérin-Méneville, 1861) male, Montenegro, Pivska planina Mt., Polje Crkvičko village, Rudine, 07.08.2015, in coll. NMNHS. Photo: Stoyan Beshkov.
Figure 1 in New records and updated distribution of the endemic Balkan rock lizards Dinarolacerta spp. in Montenegro
Figure 1. Updated distribution of D. mosorensis (circles) and D. montenegrina (triangles) in Montenegro (locality numbers explained in Appendix I). Solid symbols – new records; open symbols - literature data.
Figure 1 in Checklist of the pseudoscorpions (Arachnida: Pseudoscorpiones) of Montenegro
Figure 1. UTM map of the current distribution of 25 pseudoscorpion species and 4 subspecies in Montenegro (modified after Ćurĉić et al., 2004b).
Figure 1 in First record of Harmonia axyridis (Pallas, 1773) (Coleoptera: Coccinellidae) from Montenegro
Figure 1. Left: The locality where Harmonia axyridis has been found in Montenegro: Ravnjak, Mojkovac Municipality. Right: Harmonia axyridis specimen observed in Ravnjak, Mojkovac Municipality. Photos: Aleksandra Gligorović
Figure S1 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure S1. Snail counts (y axis) at sites A (above) and B (below) for the three cohorts showing unmarked and recaptures separately for each visit: juveniles too small to mark, juveniles newly dotted, dotted juveniles recaptured, newly marked adult and subadult individuals, already marked adult and subadult individuals (recaptures).
Figure 9 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 9. Temperature and humidity profiles at sites A, B, and C between April and December 2017. TA = temperature at site A (three loggers), TB = temperature at site B (three loggers), TC = temperature at site C (three loggers). HA, HB, HC = humidity profile at sites A, B, and C, respectively. Some missing data are due to temporal failure of some loggers. Humidity loggers stopped to function completely in the middle of October at all three sites.
Figure 7 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 7. Minimum distances (in meters, x axis) of numbered individuals (y axis: absolute numbers of individuals) from sites A and B, over all subsequent observations.
Figure 6 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 6. Minimum distances (in meters, x axis) of numbered individuals (y axis: absolute numbers of individuals) from site A and B of all observations with a ~1-week interval.
Figure 3 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 3. Snail counts at site A (above) and site B (below); juv. small = small juveniles (too small to mark); juv. dotted = dotted individuals; subadults and adults = numbered subadults/adults.
Figure 8 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 8. Sum of MDs (in meters, x axis) over all subsequent observations (over the season) of numbered individuals (y axis: absolute numbers of individuals) from sites A and B.
Figure 2. M in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 2. M. subcristata shell-size classes: (A) small juveniles (too small to mark), appr. 8 mm shell height), (B) dotted juvenile, appr. 12 mm; (C) numbered adult, appr. 20 mm.
Figure 5 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 5. Population estimated according to Jolly-Seber for site A (above), site B (below). Y axis: estimated number of individuals.
Figure 1 in First data on population estimates and dispersal of Montenegrina subcristata - a field study at Virpazar, Montenegro
Figure 1. Study area with three study sites (A, B, C). Note that due to the perspective view site B and C appear much smaller.
Figure 1 in Contribution to the knowledge of the caddisfly fauna of Montenegro - New data and records from the karstic springs of Lake Skadar basin
Figure 1. Map of the study area. The numbers correspond to spring identification numbers in Table 1.
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