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130 results for “Bulgarian”
Ontolex-lemon and TIAD versions of Apertium Macedonian-Bulgarian dictionary
<p>OntoLex-lemon and TSV conversion of Apertium Bidix. For more details, see <a href="https://www.aclweb.org/anthology/2020.lrec-1.401/">https://www.aclweb.org/anthology/2020.lrec-1.401/</a></p> <p>Authors of the original data:</p> 2010-2013, Kevin Brubeck Unhammer 2010-2014, Francis M. Tyers 2010, Jim O'Regan 2010, Tihomir Rangelov 2011, Pminervini 2011, Trond Trosterud 2012, Anthony J. Bentley
Bulgarian 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.</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 is <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 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2022 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2021 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2020 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2019 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2018 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2017 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2016 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2015 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2014 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2013 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2012 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</p> <p>MOPER_2011 - Bulgarian Food Safety Agency - Risk Assesment Center on Food Chain</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>
Fig. 2 in Bithynia Danubialis, A New Species From The Bulgarian Danube (Gastropoda: Rissooidea: Bithyniidae)
Fig. 2. Bithynia danubialis sp. n.: 1–2 = the shell (holotype), 3 = operculum, 4 = pseudopenis in situ, 5 = penis in situ, 6 = penis with flagellum. Legend: e = eye, fl = flagellum, p = penis, pa = penial ap-
Companies in the Bulgarian Military-Industrial-Media-Complex
<p>Data supplement to a publication on the Bulgarian Military-Industrial-Media-Complex.</p>
Fig. 2 in An illustrated key to the Bulgarian freshwater crayfish species of family Astacidae (Crustacea: Decapoda)
Fig. 2. Astacus leptodactylus: a/ spines behind cervical groove; b/ rostrum; c/ abdominal pleura 2-4; d/ second gonopod with talon.
Fig. 3 in An illustrated key to the Bulgarian freshwater crayfish species of family Astacidae (Crustacea: Decapoda)
Fig. 3. Astacus astacus: a/ spines behind cervical groove; b/ rostrum; c/ abdominal pleura 2-4; d/ second gonopod.
Fig. 1 in The effect of pingers on cetaceans bycatch and target catch in the turbot gillnets in Bulgarian Black Sea
Fig. 1. Ph.phocoena bycatch rate (individuals per km of net and per soak time (days) by years in the control nets.
Fig. 2 in Cetacean mortality along the Bulgarian Black Sea Coast during 2017
Fig. 2. Distribution of recorded cetacean strandings along the (a) North Bulgarian coast and (b) South Bulgarian coast.
Fig. 1 in Cetacean mortality along the Bulgarian Black Sea Coast during 2017
Fig. 1. Percentage distribution (a), timing (b) and location (c) of the stranded cetaceans along Bulgarian Black Sea Coast during 2017.
Fig. 3 in Cetacean mortality along the Bulgarian Black Sea Coast during 2017
Fig. 3. Distribution frequency of different stages of decomposition of the stranded cetaceans by species (Tt - Tursiops truncatus ponticus, Pp - Phocoena phocoena relicta, Dd - Delphinus delphis ponticus, UI – Unidentified). Stage 1 – alive; stage 2 - fresh corpse; stage 3 - decayed, but the organs are mostly preserved; stage 4 - the organs could not be identified; stage 5 - mummified animal parts/a skeleton and its parts.
Fig. 2. S in The effect of pingers on cetaceans bycatch and target catch in the turbot gillnets in Bulgarian Black Sea
Fig. 2. S. maeoticus bycatch rate (individuals per km of net) by years in the active and control nets.
Fig.1 in Home range, movements and activity patterns of an exceptionally large male Brown Bear (Ursus arctos L.) in the area of the Bulgarian-Greek border (Western Rhodope Mts.)
Fig.1. Dominant male (supposed age of at least 15 years old) with scars of battles with rivals. Hunting Forestry Adjilarska (photo from a kamera-trap, D. Bukovsky, 17.03.2014 at a game-feeding station).
Fig 2. A in Home range, movements and activity patterns of an exceptionally large male Brown Bear (Ursus arctos L.) in the area of the Bulgarian-Greek border (Western Rhodope Mts.)
Fig 2. A century-old bear marking tree just on the Bulgarian/Greek border. The tree is marked also with white paint as a border pillar (photo N. Spassov).
Fig. 6 in Ground beetles (Coleoptera: Carabidae) from the region of Cape Emine (central Bulgarian Black sea coast). Part II. Ecological parameters and community structure
Fig. 6. Cluster analysis of the carabid assemblages of the region of Cape Emine, using the index of similarity of Jaccard.
Fig. 5 in Ground beetles (Coleoptera: Carabidae) from the region of Cape Emine (central Bulgarian Black sea coast). Part II. Ecological parameters and community structure
Fig. 5. Indices of α-diversity: Species diversity of Margalef, Shannon and Hill (left) and Evenness, Simpson's concentration of dominance and diversity (right).
Fig. 4 in Ground beetles (Coleoptera: Carabidae) from the region of Cape Emine (central Bulgarian Black sea coast). Part II. Ecological parameters and community structure
Fig. 4. Distribution of the specimens by gender in the individual sampling sites (♀ – female, ♂ – male, n – not determined) (number of specimens).
Fig. 2 in Ground beetles (Coleoptera: Carabidae) from the region of Cape Emine (central Bulgarian Black sea coast). Part II. Ecological parameters and community structure
Fig. 2. Distribution of specimens of ground beetles on the levels of the dominant structure for the entire carabid complex (number of specimens).
Fig. 3 in Ground beetles (Coleoptera: Carabidae) from the region of Cape Emine (central Bulgarian Black sea coast). Part II. Ecological parameters and community structure
Fig. 3. Distribution of the specimens by gender during the different seasons (♀ – female, ♂ – male, n – not determined) (number of specimens).
Fig. 4 in Ground beetles (Coleoptera: Carabidae) from the region of Cape Emine (Central Bulgarian Black sea coast). Part I. Taxonomic and zoogeographic structure, life forms, habitat and humidity preferences
Fig. 4. Proportions of the subclasses of life forms in the carabid complex (I – class Zoophaga, II – class Mixophytophaga).
Fig. 2. A in The Bulgarian Odonata database - current status, organisation and a case study new entries
Fig. 2. A summary of Odonata data for Bulgaria before and after 2001. Total Bulgaria = Total UTM-grids in Bulgaria; Total Odonata = Total UTM-grids with any data on Odonata; Total prior 2001 = UTM-grids with any data prior to 2001; Total after 2001 = UTM-grids with any data after 2001; No data after 2001 = UTM-grids with no data after 2001; No data before 2001 = UTM-grids with no data before 2001; Total b/a 2001 = UTM-grids with data before and after 2001.
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
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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.