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National Checklists: Hungary 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 - Hungary
<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 Hungary. 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 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 – National Food Chain Safety Office</p> <p>VMPR_2022 – National Food Chain Safety Office</p> <p>VMPR_2021 – National Food Chain Safety Office</p> <p>VMPR_2020 – National Food Chain Safety Office</p> <p>VMPR_2019 – National Food Chain Safety Office</p> <p>VMPR_2018 – National Food Chain Safety Office</p> <p>VMPR_2017 – National Food Chain Safety Office</p>
Fig. 1 in Area Requirements Of Passerine Birds In The Reed Archipelago Of Lake Velence, Hungary
Fig. 1. Incidence functions of the 8 passerine bird species observed on the 109 reed islands at Lake Velence, Hungary. Abbreviations: Acraru = Acrocephalus arundinaceus, Acrsci = A. scirpaceus, Acrsch = A. schoenobaenus, Acrmel = A. melanopogon, Loclus = Locustella luscinioides, Panbia = Panurus biarmicus, Embsch = Emberiza schoeniclus, Lussve = Luscinia svecica
Fig. 10 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 10. Trends in the relative abundance of trophic guilds in Lake Fenéki (Piscivores: y = 0.06 + 0.003x; R2 = 0.757; P> 0.00001)
Fig. 9 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 9. Proportion of each species in the cumulative abundance of non-native fish species in Lake Fenéki
Fig. 7 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 7. PCA biplot of the arcsin-square root transformed relative abundance data of the whole sampling period (1992–2011) (Variables: Sampling years; Objects: Relative abundances) (abbreviations were constructed from the Latin names of the species, using the first 3 characters of genus and species
Fig. 5 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 5. Estimated number of species (SD's ignored in order to improve visibility) as a function of number of individuals collected in each sampling year
Fig. 8 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 8. PCA biplot of the arcsin-square root transformed relative abundance data of the period 1994–2011 (Variables: Sampling years; Objects: Relative abundances)
Fig. 4 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 4. Relationships between the age of Lake Fenéki and the Shannon–Weaver index (y = 0.414ln(x) + 0.852; R2 = 0.772; P <0.0001)
Fig. 3 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 3. Relationships between the age of Lake Fenéki and the number of fish species (y = 4.141ln(x) + 3.807; R2 = 0.759; P <0.0001)
Fig. 4 in Scale-Morphometry Study To Discriminate Gibel Carp (Carassius Gibelio) Populations In The Balaton-Catchment (Hungary)
Fig. 4. Relationship between Canonical Variates and environmental variables based on sampling sites separation
Fig. 1 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization
Fig. 1. Overlooking map of the Balaton-catchment, with the sampling site (Dark rectangle marked by the arrow indicates the flooded area of Lake Fenéki)
Fig. 2 in Scale-Morphometry Study To Discriminate Gibel Carp (Carassius Gibelio) Populations In The Balaton-Catchment (Hungary)
Fig. 2. Landmarks used to define the shape of the scales (Prussian carp). The areas of the scales are described with respect to the fish position
Fig. 3 in Scale-Morphometry Study To Discriminate Gibel Carp (Carassius Gibelio) Populations In The Balaton-Catchment (Hungary)
Fig. 3. Canonical Variate Analysis of Carassius gibelio from KBWPS I, KBWPS II, Balaton, Nagyberek, Hungary with landmark-based geometric geometric morphometrics based on scale shape. El-
Figs 3–4 in Dispersal History Of An Invasive Rodent In Hungary - Subfossil Finds Of Rattus Rattus
Figs 3–4. Skull (ventral view) of one of the black rats from site: 3 = Budapest, District XVII, Péceli Road (Roman Period); 4 = Dusnok–Szúnyogosi dűlő (Roman Period). Scale bars 10 mm
Fig. 1 in Dispersal History Of An Invasive Rodent In Hungary - Subfossil Finds Of Rattus Rattus
Fig. 1. Investigated archaeological sites in Hungary with small mammal fauna. = open air sites with using flotation method, black rat absence; = open air/cave sites with using flotation method,
CoMix social contact data (Hungary)
<p>CoMix social contact data for Hungary.</p> <p>We gratefully acknowledge the efforts of all teams involved in the implementation of the CoMix study in their country. More specifically: the team of Gergely Röst at the University of Szeged.</p>
Fig. 1 in Ladislavella Occulta (Jackiewicz, 1959) - A Species Of Aquatic Snails New For Hungary With Remarks On Its Distribution In Central And Eastern Europe
Fig. 1. Shells of Ladislavella occulta from Hungary and Poland. Upper row – Hungary, Bátorliget (HNHM), lower row – three paratypes of this species from Rawicz, Poland (ZIN). Scale bars: 2 mm
Fig. 2 in Ladislavella Occulta (Jackiewicz, 1959) - A Species Of Aquatic Snails New For Hungary With Remarks On Its Distribution In Central And Eastern Europe
Fig. 2. Shells of L. occulta (A-G) and L. terebra (H) from various countries of Central and Eastern Europe. A. Ukraine, Zhitomir Region, Dzerzhinsk (ZMB); B. Germany, Halle District, Salziger Lake (NMG); C. Ukraine, Transcarpathian Region, a pool in Khust District (LMBI); D. Russia, Moscow Region, Oka River basin, without exact locality (ZMMU); E. Russia, Republic of Mordovia, Alatyr' River near Obrochnoye station (ZIN); F. Russia, Kursk Region, Seym River near L'gov Town (ZIN); G. Ukraine, Poltava Region, Lubny District, Pleistocene deposits (ZIN); H. Russia, Barents Sea, Kolguev Island (ZMMU). Scale
Fig. 3. A in Ladislavella Occulta (Jackiewicz, 1959) - A Species Of Aquatic Snails New For Hungary With Remarks On Its Distribution In Central And Eastern Europe
Fig. 3. A map of Europe showing known findings of L. occulta. The Pleistocene records are not shown, This map is based on data published in literature (JACKIEWICZ 1998, 2000; BERAN 2008, STADNICHENKO 2004, ANISTRATENKO et al. 2018) and own data. Squares indicate findings identified by anatomical data; circles – findings based on empty shells. The location of Bátorliget is indicated by a star
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