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68 results for “North Macedonia”
Results complementing the European Union summary report on surveillance for the presence of transmissible spongiform encephalopathies (TSE) - North Macedonia
<p>This dataset contains TSE surveillance results in cattle, sheep, goats, cervids and other species, and genotyping in sheep, pursuant to Regulation (EC) 999/2001.</p> <p><strong>Reporting authorities contributing to each data collection</strong>:</p> <ul> <li>TSE_2023_MK: Food and Veterinary Agency (FVA)</li> <li>TSE_2022_MK: Food and Veterinary Agency (FVA)</li> <li>TSE_2021_MK: Food and Veterinary Agency (FVA)</li> <li>TSE_2020_MK: Food and Veterinary Agency (FVA)</li> <li>TSE_2019_MK: Food and Veterinary Agency (FVA)</li> </ul>
Dataset for Green Transition Policies, Stakeholders and Practices in North Macedonia
<p>This dataset contributed to deliverable 4.2 Regional Mapping Report and shows the North Macedonian mapping. This report is the second deliverable of WP4 – Measuring and assessing impacts and costs of a just green transition in the WB, of the GreenFORCE project. It was jointly authored by the WB project partners, as well as 2 subcontracted parties from the region.</p> <p>The EU Economic and Investment Plan for the WB includes a green agenda for the WB, with pillars to be pursued for transitioning towards a carbon-neutral economy. Such a shift will surely challenge the economies and societies in the WB. The social and policy context is yet fragile to allow for the development and mass distribution of green transition technologies, while human resources are not prepared and/or are insufficient to produce and implement innovation. Yet, the green transition also paves the way towards new development and resilience opportunities. The research will inform on the readiness/potential of societal actors (industry, academia, policymakers, civic society) to embrace the pathways to transformation, and will propose a framework for continuous monitoring of impacts and costs. The key findings and lessons learnt derived within WP4 will be transferred into the scientific papers and policy briefs (WP 2 & 3) and published under the dissemination events (WP5).</p> <p>Regional mapping is a key task for the research, contributing to initial data gathering and the refinement of the research proposal, and to the sub-question on the identification of sectors and territories affected by the transitions and current progress of transition practices. This is a participatory mapping, engaging local stakeholders and communities to reveal local knowledge. Each WB partner will produce the respective country report, and Co-PLAN will work on the final regional report.</p> <p>This deliverable is the final regional report. It will also include the mapping frame used to conduct the mapping process. The WB partners will do the mapping for their own countries. The PC will subcontract data gathering for the remaining countries. The mapping is done for actors, practices and policies in place, territories upon the level of relevance and potential for engaging in green transition; and sectors. All partners will design the mapping frame, using also knowledge from other mapping processes. The frame will contain the type of information to be collected, the standardisation of data entry, and the tailored instruments to be deployed for accessing information.</p>
North Macedonia results from the monitoring of pesticide residues in food
<p>This dataset contains the analytical results of pesticide residues measured in the food products analysed by the national competent authorities. Pesticide residues resulting from the use of plant protection products on crops that are used for food or feed production may pose a risk factor for public health. For this reason, a comprehensive legislative framework has been established in the European Union (EU), which defines rules for the approval of active substances used in plant protection products, the use of plant protection products and for pesticide residues in food. In order to ensure a high level of consumer protection, legal limits, so called “maximum residue levels” or briefly “MRLs”, are established in Regulation (EC) No 396/2005. EU-harmonised MRLs are set for all pesticides covering all types of food products. A default MRL of 0.01 mg/kg is applicable for pesticides not explicitly mentioned in the MRL legislation. Regulation (EC) No 396/2005 imposes on Member States the obligation to carry out controls to ensure that food placed on the market is compliant with the legal limits. The chemical monitoring data collected and published by EFSA include the analytical results provided by EU Member States, Iceland, Norway and three pre-accession countries: Bosnia-Herzegovina, Montenegro and North Macedonia. </p> <p>A sample is considered <strong>free of quantifiable residues</strong> if the analytes were not present in concentrations at or above the limit of quantification (LOQ). The LOQ is the smallest concentration of an analyte that can be quantified with the analytical method used to analyse the sample. It is commonly defined as the minimum concentration of the analyte in the test sample that can be determined with acceptable precision and accuracy.</p> <p>If a sample <strong>contains quantifiable residues</strong> but within the legally permitted limit (maximum residue level, MRL), it is described as a sample with quantified residue levels within the legal limits (below or at the MRL)</p> <p>A sample is considered <strong>non-compliant</strong> with the legal limit (MRL), if the measured residue concentrations clearly exceed the legal limits, taking into account the measurement uncertainty. It is current practice that the uncertainty of the analytical measurement is taken into account before legal or administrative sanctions are imposed on food business operators for infringement of the MRL legislation.</p> <p> </p> <p><strong>REPORTING AUTHORITIES CONTRIBUTING TO EACH DATA COLLECTION:</strong></p> <p>MOPER_2023 - Food and Veterinary Agency</p> <p>MOPER_2022 - Food and Veterinary Agency</p> <p>MOPER_2021 - Food and Veterinary Agency</p> <p>MOPER_2020 - Food and Veterinary Agency</p> <p>MOPER_2019 - Food and Veterinary Agency</p> <p>MOPER_2018 - Food and Veterinary Agency</p> <p>MOPER_2017 - Food and Veterinary Agency</p> <p> </p> <p><strong>We are seeking feedback on our open data please complete the survey at the link below:<br>https://ec.europa.eu/eusurvey/runner/9344dfa0-f384-cb72-65f6-6c187a6d0f14</strong></p>
Vulnerability tools - Maleshevski Mountains (North Macedonia)
<p><span>The MOVING project has developed accessible <strong>tools </strong>designed to assess susceptibility and vulnerability within the region, ready to be used by both experts and the general audience. This document synthesises crucial information for the Maleshevski Mountains Region, particularly focusing on the Participatory Vulnerability Matrix and the Spatial Vulnerability Map. Furthermore, it includes <strong>supplementary maps and figures </strong>detailing various aspects such as the delineation of Reference Landscape, distribution of land systems, areas affected by wildfires, susceptibility to floods across different return periods, severity of forest disturbances, rainfall erosivity, and more.</span></p>
Results from the monitoring of veterinary medicinal product residues and other substances in live animals and animal products - North Macedonia
<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 North Macedonia. 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, 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 – Food and Veterinary Agency</p> <p>VMPR_2022 – Food and Veterinary Agency</p> <p>VMPR_2021 – Food and Veterinary Agency</p> <p>VMPR_2020 – Faculty of Veterinary Medicine - Skopje</p> <p>VMPR_2019 – Faculty of Veterinary Medicine - Skopje</p> <p>VMPR_2018 – Food and Veterinary Agency</p> <p>VMPR_2017 – Food and Veterinary Agency</p>
DATASET - Mass Spectrometry - Snake venom proteomics of island and mainland V. ammodytes populations from North Macedonia
<p><strong><span>This DATASET collection includes the mass spectrometry files for proteomics venom investigation of island and mainland <em>V. ammodytes</em> populations from North Macedonia.</span></strong></p> <p><strong><span>Sample list:</span></strong></p> <ol> <li><span>Island - adult - male</span></li> <li><span>Island - adult - female</span></li> <li><span>Island - juvenile</span></li> <li><span>Island - subadult</span></li> <li><span>Mainland - adult</span></li> <li><span>Mainland - subadult</span></li> <li><span>Mainland - juvenile</span></li> </ol> <p><strong><span>Folders 01-07 - BOTTOM-UP PROTEOMICS</span></strong><span>: The venom pools were investigated by the bottom-up "snake venomics" (labelled as SVX) approach and in short: separated by RP-HPLC, followed by SDS-PAGE separation and the single bands were in-gel processed by DTT, IAC and finally o/n tryptic digested. Samples submitted to HPLC-MS/MS. Early peptidic fractions of the first HPLC run were directly submitted to HPLC-MS/MS analytic w/o further gel procession. Folders 01 to 07 include the MS and MS/MS spectra of the <em>V. ammodytes</em> sample pools from different populations. Files are included as RAW and MZML format.</span></p> <p><span>Used instrument: LTQ Orbitrap XL mass spectrometer (Thermo, Bremen, Germany) with an Agilent 1260 HPLC system (Agilent Technologies, Waldbronn, Germany) using a reversed-phase Grace Vydac 218MS C18 (2.1 × 150 mm; 5 </span><span>μ</span><span>m particle size) column.</span></p> <p><span>Modifications: UNIMOD:4 - \"Iodoacetamide derivative.\"</span></p> <p><span>Used protein database: Uniprot_8750_serpentes_CanNIso_2674_entries_220210_cRAP_220210.fasta</span></p>
Figure 2 in Shar Mountain National Park (R. North Macedonia) - shelter for caddisfly biodiversity in the country
Figure 2. Photos of the localities where the new species were recorded: a) S1 - Stream in Leshnica; b) S2 - Waterfall before v. Gajre; c) S3 – Uliverica; d) S4 - Stream above v. Novo Selo.
Figure 1 in Shar Mountain National Park (R. North Macedonia) - shelter for caddisfly biodiversity in the country
Figure 1. Map of the sampling localities (S1 – S4) on Shar Mountain (R. North Macedonia). Map prepared by Daniela Jovanovska, PhD.
Figure 3 in New Records of Stoneflies (Insecta: Plecoptera) in National Park Shar Mountain (R. North Macedonia)
Figure 3. Nemoura asceta Murányi, 2007 (dorsal view). First record for R. North Macedonia. © Ignac Sivec.
Figure 2 in New Records of Stoneflies (Insecta: Plecoptera) in National Park Shar Mountain (R. North Macedonia)
Figure 2. Sampling localities from where the newly recorded species were collected: a) L1 - Tributary of the river Pena, v. Brodec, b) L2- River of Bogovinje, v. Bogovinje, c) L3- Stream on the way to Mazdracha, d) L4 – Stream after Lisec village.
Figure 1 in New Records of Stoneflies (Insecta: Plecoptera) in National Park Shar Mountain (R. North Macedonia)
Figure 1. Map of the sampling localities (L1 ˗ L4) in Shar Mountain (R. of North Macedonia). Map created by Daniela Jovanovska, PhD.
Figs 1–4 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 1–4. Andrena kocoureki sp. nov., female. 1, habitus, lateral view. 2, head, frontal view. 3, metasoma, dorsal view. 4, tergal apex and pygidial plate, dorsal view. © Thomas J. Wood.
Figs 5–10 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 5–10. Andrena kocoureki sp. nov., female. 5, clypeus detail. 6, mesosoma, dorsal view. Andrena combinata (Christ, 1791), female. 7, clypeus detail. 8, mesosoma, dorsal view. Andrena lepida Schenck, 1853, female. 9, clypeus detail. 10, mesosoma, dorsal view. © Thomas J. Wood.
Figs 37–40. Andrena oulskii Radoszkowski, 1867, female. 37, specimen labels. 38 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 37–40. Andrena oulskii Radoszkowski, 1867, female. 37, specimen labels. 38, head, frontal view. 39, habitus, dorsal view. 40, lateral view. © Thomas J. Wood.
Figs 21–24 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 21–24. Andrena pirinia sp. nov., female. 21, habitus, lateral view. 22, habitus, dorsal view. 23, head, frontal view. Andrena anthrisci Blüthgen, 1925, female. 24, head, frontal view. © Thomas J. Wood.
Figs 15–20 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 15–20. Andrena kocoureki sp. nov., male. 15, mesosoma, dorsal view. 16, genitalia, dorsal view. Andrena combinata (Christ, 1791), male. 17, mesosoma, dorsal view. 18, genitalia, dorsal view. Andrena lepida Schenck, 1853, male. 19, mesosoma, dorsal view. 20, genitalia, dorsal view. © Thomas J. Wood.
Figs 31–36 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 31–36. Andrena pelagonia sp. nov., female. 31, habitus, lateral view. 32, head, frontal view. 33, clypeus detail. 34, mesosoma, dorsal view. 35, scopa, lateral view. 36, metasoma, dorsal view. © Thomas J. Wood.
Figs 11–14 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 11–14. Andrena kocoureki sp. nov., male. 11, habitus, lateral view. 12, head, frontal view. 13, head, lateral view. 14, metasoma, dorsal view. © Thomas J. Wood.
Figs 25–30 in Revision of the Andrena (Hymenoptera: Andrenidae) fauna of Bulgaria and North Macedonia with description of three new species
Figs 25–30. Andrena pirinia sp. nov., female. 25, head, dorsal view. 27, mesosoma, dorsal view. 29, metasoma, dorsal view; Andrena anthrisci Blüthgen, 1925, female. 26, head, dorsal view. 28, mesosoma, dorsal view. 30, metasoma, dorsal view. © Thomas J. Wood.
Figure 1 in First record of Chaetopteroides kosovarorum Ibrahimi & Oláh, 2013 (Insecta: Trichoptera) from the Republic of North Macedonia
Figure 1. Distribution of the Chaetopteroides kosovarorum. Yellow dots - previous records (Olah et al. 2013). Red dots – records from this investigation.
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