natgillin/translations-raw huggingface dataset:
A summary on the biology of H. aculeifer is provided in Appendix 7. Background information on the ecology of the mite species and the use in ecotoxicological testing is available (4), (5), (6), (7), (8), (9), (10), (11), (12).
Sažetak biologije vrste H. aculeifer naveden je u Dodatku 7. Osnovne informacije o ekologiji vrsta grinja i njihovoj uporabi u ekotoksikološkim ispitivanjima mogu se pronaći u literaturi (4), (5), (6), (7), (8), (9), (10), (11), (12).
These measurements should be carried out in additional samples without mites, both from the control soil and from each test concentration soil. The soil pH should not be adjusted when acidic or basic chemicals are tested.
Ta se određivanja provode na dodatnim uzorcima bez grinja, uzetima iz kontrolnog tla i iz tla svake ispitne koncentracije. pH-vrijednost tla nije potrebno prilagođavati ako se ispituju kisele ili lužnate kemikalije.
Phylogenetic studies of the free-living and arthropod associated Laelapidae (Acari: Mesostigmata). Gayana Zool.
Gayana Zool.
Tenorio, J. M. (1982). Hypoaspidinae (Acari: Gamasida: Laelapidae) of the Hawaiian Islands.
Tenorio, J. M. (1982.) Hypoaspidinae (Acari: Gamasida: Laelapidae) of the Hawaiian Islands.
Bakker, F.M., Feije, R., Grove, A. J., Hoogendorn, G., Jacobs, G., Loose, E.D. and van Stratum, P. (2003). A laboratory test protocol to evaluate effects of plant protection products on mortality and reproduction of the predatory mite Hypoaspis aculeifer Canestrini (Acari: Laelapidae) in standard soil.
Bakker, F. M., Feije, R., Grove, A. J., Hoogendorn, G., Jacobs, G., Loose, E.D. i van Stratum, P. (2003.) A laboratory test protocol to evaluate effects of plant protection products on mortality and reproduction of the predatory mite Hypoaspis aculeifer Canestrini (Acari: Laelapidae) in standard soil.
Ruf, A. (1995). Sex ratio and clutch size control in the soil inhabiting predatory mite Hypoaspis aculeifer (Canestrini 1883) (Mesostigmata, Dermanyssidae).
Ruf, A. (1995.) Sex ratio and clutch size control in the soil inhabiting predatory mite Hypoaspis aculeifer (Canestrini 1883.) (Mesostigmata, Dermanyssidae).
Ruf, A. (1996). Life-history patterns in soil-inhabiting mesostigmatid mites.
Ruf, A. (1996.) Life-history patterns in soil-inhabiting mesostigmatid mites.
Test on the predatory mite Hypoaspis aculeifer preying on the collembolan Folsomia fimetaria. In:
Lokke, H. i van Gestel, C. A. M.:
Fairbrother, A., Glazebrook, P.W., Van Straalen, N.M. and Tarazona, J.V. (eds.). SETAC Press, Pensacola, USA.
Fairbrother, A., Glazebrook, P. W., van Straalen, N. M. i Tarazona, J. V. (ur.).
Petersen, H. (1978). Some properties of two high-gradient extractors for soil microarthropods, and an attempt to evaluate their extraction efficiency.
Petersen, H. (1978.) Some properties of two high-gradient extractors for soil microarthropods, and an attempt to evaluate their extraction efficiency.
Ecological methods. With particular reference to the study of insect populations.
With particular reference to the study of insect populations.
Ignatowicz, S. (1974). Observations on the biology and development of Hypoaspis aculeifer Canestrini, 1885 (Acarina, Gamasides).
Ignatowicz, S. (1974.) Observations on the biology and development of Hypoaspis aculeifer Canestrini, 1885 (Acarina, Gamasides).
Kevan, D.K. McE. and Sharma, G.D. (1964). Observations on the biology of Hypoaspis aculeifer (Canestrini, 1884), apparently new to North America (Acarina: Mesostigmata: Laelaptidae).
Kevan, D. K. McE. i Sharma, G. D. (1964.) Observations on the biology of Hypoaspis aculeifer (Canestrini, 1884), apparently new to North America (Acarina: Mesostigmata: Laelaptidae).
OECD (2006c). Current Approaches in the Statistical Analysis of Ecotoxicity Data:
OECD (2006.c) Current Approaches in the Statistical Analysis of Ecotoxicity Data:
F. Faraji, Ph.D.
dr. sc.
TEST ACCEPTANCE CRITERIA 12. For the test results to be acceptable the following conditions apply:
Za prihvatljivost rezultata ispitivanja primjenjuju se sljedeći uvjeti:
Any water in which the test species shows suitable long-term survival and growth may be used as test water. It should be of constant quality during the period of the test.
Kao ispitna voda može se upotrijebiti svaka voda koja je prikladna za dugoročno preživljavanje i rast pokusne vrste.
Final report of the Validation of the 21-day Fish Screening Assay for the Detection of Endocrine Active Substances.
Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1A).
Unpublished report dated 15 December 2007. US Environmental Protection Agency, Washington, DC.
Neobjavljeno izvješće od 15. prosinca 2007.
None unless DO concentration falls below 60 % air saturation None unless DO concentration falls below 60 % air saturation None unless DO concentration falls below 60 % air saturation
Nikakvo, osim ako koncentracija otopljenog kisika padne ispod 60 % zasićenja kisikom
mean temperature of 25 ± 2 °C; 90 % survival of fish in the controls;
srednja temperatura od 25 ± 2 °C;
measured test concentrations within 20 % of mean measured values per treatment level. Dissolved oxygen > 60 % of saturation; mean temperature of 24 ± 2 °C; 90 % survival of fish in the controls;
90 % preživljavanja riba u kontrolnim skupinama;
Some chemical characteristics of acceptable dilution water Component
srednja temperatura od 25 ± 2 °C;
Concentrations Particulate matter
90 % preživljavanja riba u kontrolnim skupinama;
< 20 mg/l Total organic carbon < 2 mg/l Unionised ammonia < 1 μg/l Residual chlorine < 10 μg/l Total organophosphorus pesticides < 50 ng/l Total organochlorine pesticides plus polychlorinated biphenyls < 50 ng/l Total organic chlorine < 25 ng/l
izmjerene ispitne koncentracije unutar 20 % srednjih izmjerenih vrijednosti po razini tretmana.
Two or three combined plastic/ceramic/glass or stainless steel spawning tiles and trays are placed in each of the test chamber (e.g., 80 mm length of grey semi-circular guttering sitting on a lipped tray of 130mm length) (see picture). Properly seasoned PVC or ceramic tiles have demonstrated to be appropriate for a spawning substrate (Thorpe et al, 2007).
Dvije ili tri kombinirane pločice i ladice za mrijest od plastike/keramike/stakla ili nehrđajućeg čelika smještaju se u svaku ispitnu komoru (primjerice sivi polukružni oluk dugačak 80 mm koji se nalazi na ladici U-profila dugačkoj 130 mm (vidi sliku). Pravilno obrađene plastične ili keramičke pločice pokazale su se prikladnima za supstrat za mrijest (Thorpe et al, 2007.).
Procedure 1B: Fathead Minnow, Blood Collection from Heart
Postupak 1.B debeloglava gavčica, uzimanje krvi iz srca
Dunn test Yes
Dunnettov test na ugniježđenoj ANOVA-i
<=3 reps per conc Nested ANOVA not normal
Test trendova postupnims nižavanjem na s rednjoj vrijednosti ponavljanja
however, this route of exposure is not commonly used. The choice of method should be documented and analytically verified.
međutim, ovaj način izlaganja obično se ne upotrebljava Izbor metode potrebno je dokumentirati i analitički provjeriti.
In addition to the developmental stage selection, an optional size selection of the experimental animals may be used. For this purpose, the whole body length (not SVL) should be measured at day 0 for a sub-sample of approximately 20 NF stage 51 tadpoles. After calculation of the mean whole body length for this group of animals, minimum and maximum limits for the whole body length of experimental animals can be set by allowing a range of the mean value ± 3 mm (mean values of whole body length range between 24,0 and 28,1 mm for stage 51 tadpoles). However, developmental staging is the primary parameter in determining the readiness of each test animal. Tadpoles exhibiting grossly visible malformations or injuries should be excluded from the assay. 25. Tadpoles that meet the stage criteria described above are held in a tank of clean culture water until the staging process is completed.
Osim odabira stadija razvoja, može se odabrati fakultativna veličina pokusnih životinja.
OECD (2008) Report of the Validation Peer Review for the Amphibian Metamorphosis Assay and Agreement of the Working Group of the National Coordinators of the Test Guidelines Programme on the Follow-up of this Report. Environmental Health and Safety Publications.
OECD (2008.) Report of the Validation Peer Review for the Amphibian Metamorphosis Assay and Agreement of the Working Group of the National Coordinators of the Test Guidelines Programme on the Follow-up of this Report.
In addition to the standard ANOVA F-tests for the effects of Conc, LateStage, and their interactions, the interaction F-test can be “sliced” into two additional ANOVA F-test, one on the mean responses across concentrations for LateStage = ’No’ and another on the mean responses across concentrations for LateStage = ’Yes’. Further comparisons of treatment means against control are done within each level of LateStage.
Osim standardnih ANOVA F-testova za učinke koncentracije, kasnog stadija i njihove interakcije, interakcijski F-test može se podijeliti na dva dodatna ANOVA F-testa, jedan za srednje vrijednosti reakcija unutar koncentracija za kasniji stadij = „Ne” i drugi za srednje vrijednosti reakcija unutar koncentracija za kasni stadij = „Da.” Daljnje usporedbe srednjih vrijednosti obrada s kontrolom vrše se unutar svake razine kasnog stadija.
ISO (1999) Soil Quality — Effects of soil pollutants on Collembola (Folsomia candida): Method for determination of effects on reproduction.
ISO (1999.) Soil Quality – Effects of soil pollutants on Collembola (Folsomia candida):
Oikos 39:
Oikos 39: 287.
Acta Zoologica Fennica 195:
Acta Zoologica Fennica 195.: 111.
However, until a validated acute guideline is available a chronic test according to Chapter C.28 of this Annex may be considered. Examples of reference toxicants used successfully in ring-tests and validation studies are:
Međutim, dok ne bude dostupna potvrđena smjernica za akutnu toksičnost, u obzir se može uzeti ispitivanje kronične toksičnosti u skladu s poglavljem C.28. ovog Priloga.
lindane, trifluralin, pentachlorophenol, cadmium chloride and potassium chloride. (1) (3) (6) (7) (18). VALIDITY OF THE TEST
Primjeri referentnih toksičnih tvari koje se uspješno upotrebljavaju u prstenastim testovima i validacijskim studijama jesu:
for C. riparius and C. yoshimatsui, 85 % of the total emerged adult midges from the control treatment in both generations should occur between 12 and 23 days after the insertion of the first instar larvae into the vessels; for C. dilutus, a period of 20 to 65 days is acceptable; the mean sex ratio of fully emerged and alive adults (as female or male fraction) in the control treatment of both generations should be at least 0,4, but not exceed 0,6; for each breeding cage the number of egg ropes in the controls of the 1st generation should be at least 0,6 per female added to the breeding cage; the fraction of fertile egg ropes in each breeding cage of the controls of the 1st generation should be at least 0,6; at the end of the exposure period for both generations, pH and the dissolved oxygen concentration should be measured in each vessel. The oxygen concentration should be at least 60 % of the air saturation value (ASV [9]), and the pH of overlying water should be between 6 and 9 in all test vessels; the water temperature should not differ by more than ± 1,0 °C. DESCRIPTION OF THE METHOD Test vessels and breeding cages 11. The larvae are exposed in 600 ml glass beakers measuring ca. 8,5 cm in diameter (see Appendix 5). Other vessels are suitable, but they should guarantee a suitable depth of overlying water and sediment.
prosječna uspješnost preobrazbe u kontrolnoj skupini trebala bi iznositi najmanje 70 % na kraju razdoblja izlaganja za obje generacije (1)(7);
Selection of species 12. The species to be used in the test is preferably Chironomus riparius.
Što se tiče posude za kristalizaciju, omjer dubine sloja sedimenta i dubine vode iznad sedimenta trebao bi biti otprilike 1: 4.
Butler (1999), Palearctic and Nearctic Chironomus (Camptochironomus) tentans Fabricius are different species (Diptera: Chironomidae).
Butler (1999.), Palearctic and Nearctic Chironomus (Camptochironomus) tentans Fabricius are different species (Diptera: Chironomidae).
Rowland (2006), Interlaboratory evaluation of Hyalella azteca and Chironomus tentans short-term and long-term sediment toxicity tests, Environ.
Rowland (2006.), Interlaboratory evaluation of Hyalella azteca and Chironomus tentans short-term and long-term sediment toxicity tests, Environ.
Rodgers (1994), Development of formulated reference sediments for freshwater and estuarine sediment testing, Environ.
Rodgers (1994.), Development of formulated reference sediments for freshwater and estuarine sediment testing, Environ.
Maes (2009), Chronic toxicity of fenoxycarb to the midge Chironomus riparius after exposure in sediments of different composition.
Maes (2009.), Chronic toxicity of fenoxycarb to the midge Chironomus riparius after exposure in sediments of different composition.
Scott (1992), A simple method for the analysis of clustered binary data.
Scott (1992.), A simple method for the analysis of clustered binary data.
Versteeg (1992), A statistical procedure for modelling continuous toxicity data, Environ.
Versteeg (1992.), A statistical procedure for modelling continuous toxicity data, Environ.
Ankley (1997), Chironomus tentans life-cycle test:
Ankley (1997.), Chironomus tentans life-cycle test:
E tube (plastic or glass, inner diameter ca. 8 mm) to collect adult midges from vessel Schematic presentation of a life-cycle test:
E cjevčica (plastična ili staklena, unutarnjeg promjera otprilike 8 mm) za sakupljanje odraslih mušica iz posude
A 1st generation — test vessels containing a sediment-water system, eight replicates, 20 first instar larvae per vessel B four test vessels for each breeding cage, A and B C breeding cages (A and B) for swarming, mating and oviposition D crystallising dishes for deposition of egg ropes E micro plates, one well for each egg rope
Shematski prikaz ispitivanja životnog ciklusa:
Length (standard length) > 20 mm > 14 mm
Dužina (standardna dužina)
Outliers from the acceptance criteria (in controls) should be highlighted. Survival should be presented as percentage per replicate and per concentration.
Potrebno je istaknuti netipične vrijednosti u odnosu na kriterije prihvatljivosti (u kontrolama).
Clear indication of the results obtained on the different endpoints observed: embryo survival and hatching success; external abnormalities;
Potrebno je istaknuti netipične vrijednosti u odnosu na validacijske kriterije (u kontrolama),
Panter, G.H., T.H. Hutchinson, R. Lange, C.M. Lye, J.P.
Panter, G. H., T. H. Hutchinson, R. Lange, C. M. Lye, J. P. Sumpter, M. Zerulla i C. R. Tyler (2002.), ‚Utility of a juvenile fathead minnow screening assay for detecting (anti-)estrogenic substances’, Environmental Toxicology and Chemistry 21, str. 319.
Sun, L.W., J.M. Zha, P.A.
Sun, L. W., J. M. Zha, P. A. Spear i Z. J. Wang (2007.), ‚Toxicity of the aromatase inhibitor letrozole to Japanese medaka (Oryzias latipes) eggs, larvae and breeding adults’, Comparative Biochemistry and Physiology C-Toxicology & Pharmacology 145, str. 533.
Parks, L.G., A.O. Cheek, N.D. Denslow, S.A. Heppell, J.A.
Parks, L. G., A. O. Cheek, N. D. Denslow, S. A. Heppell, J. A. McLachlan, G. A. LeBlanc i C. V.Sullivan (1999.), ‚Fathead minnow (Pimephales promelas) vitellogenin: purification, characterization and quantitative immunoassay for the detection of estrogenic compounds’, Comparative Biochemistry and Physiology C-Toxicology & Pharmacology 123, str. 113.
Nilsen, B.M., K. Berg, J.K. Eidem, S.I.
Nilsen, B. M., K. Berg, J. K. Eidem, S. I. Kristiansen, F. Brion, J. M. Porcher i A. Goksoyr (2004.), ‚Development of quantitative vitellogenin-ELISAs for fish test species used in endocrine disruptor screening’, Analytical and Bioanalytical Chemistry 378, str. 621.
Panter, G.H., T.H. Hutchinson, K.S. Hurd, J. Bamforth, R.D.
Panter, G. H., T. H. Hutchinson, K. S. Hurd, J. Bamforth, R. D. Stanley, S. Duffell, A. Hargreaves, S. Gimeno i C. R. Tyler (2006.), ‚Development of chronic tests for endocrine active chemicals – Part 1. An extended fish early-life stage test for oestrogenic active chemicals in the fathead minnow (Pimephales promelas)’, Aquatic Toxicology 77, str. 279.
Panter, G.H., T.H. Hutchinson, K.S. Hurd, A. Sherren, R.D.
Panter, G. H., T. H. Hutchinson, K. S. Hurd, A. Sherren, R. D. Stanley i C. R. Tyler (2004.), ‚Successful detection of (anti-) androgenic and aromatase inhibitors in pre-spawning adult fathead minnows (Pimephales promelas) using easily measured endpoints of sexual development’, Aquatic Toxicology 70, str. 11.
Experimental conditions for the FSDT (freshwater species) 1. Recommended species
Uvjeti pokusa za ispitivanje spolnog razvoja riba (slatkovodne vrste)
Test type Flow-through or semi-static
Koljuška (Gasterostreus aculeatus)
Water temperature 25 ± 2 °C 27 ± 2 °C
Protočno ili polustatično
20 ± 2 °C 4. Illumination quality
Protočno ili polustatično
growth (Fish wet weight, blotted dry) > 120 mg Length (standard length) > 20mm Length (standard length) > 14 mm
Rast (mokra masa ribe osušene upijajućim materijalom) > 120 mg
Important: The tubes should be numbered properly so that the head and tail from the fish can be related to their respective body-section used for gonad histology.
cijevi bi trebale biti pravilno označene brojevima tako da se glava i rep ribe mogu povezati s odgovarajućom sekcijom tijela upotrijebljenom za histološku analizu spolnih žlijezda.
Normalising transform? Nested ANOVA not normal
Srednja vrijednost ponavljanja nije normalna ili nije homogena
Dunn or Mann-Whitney U-test w/Bonferroni-Holm adjustment to determine NOEC Yes
Primijeniti Jonckheere-Terpstrin test postupnim snižavanjem (+) radi utvrđivanja NOEC-a
PCR-buffer 2: 20 g Chelex (e.g. Biorad, Munich, GE) To swell in 100 ml dest. H2O → autoclave Determination of genetic sex (by PCR-method) in medaka (Prepared by the Laboratory for Aquatic Organisms of Bayer CropScience AG and Universität Würzburg Biozentrum) The prepared and frozen tubes (described in the above section) will be thawed on ice. After that, they will be centrifuged using an Eppendorf centrifuge (30 sec at max. speed, at room temperature). For the PCR, the clear supernatant separated from the precipitate will be used. It has absolutely to be avoided that any traces of Chelex (localized in the precipitate) are transferred to the PCR reaction, because this will interfere with the “Taq”-polymerase activity.
PCR-pufer 2:
Preparation of the “Reaction Mix” (25 μl per sample): Volume Final Concentration Template DNA
Određivanje genetskog spola (metodom PCR-a) u medake (pripremili Laboratorij za vodene organizme Bayer CropScience AG-a i Universität Würzburg Biozentrum)
0,5μl-2μl 10xPCR-buffer with MgCl2 2,5μl 1x
Pripremljene i zamrznute cijevi (opisane u prethodnom odjeljku) otapaju se na ledu.
Nucleotides (each of dATP, dCTP, dGTP, dTTP) 4μl (5mM)
Nakon toga centrifugiraju se primjenom centrifuge za Eppendorfove epruvetice (30 sekundi pri maksimalnoj brzini na sobnoj temperaturi).
Forward Primer (10μM) (see below 3-5) 0,5μl
Za PCR upotrebljava se bistri supernatant odvojen od taloga.
Reverse Primer (10μM) (see below 3-5) 0,5μl 200nM DMSO 1,25μl 5 % Water (PCR grade) up to 25μl Taq E- Polymerase 0,3μl 1,5U 10xPCR-buffer with MgCl2:
Apsolutno se mora izbjeći prijenos bilo kakvih tragova Chelexa (lokaliziranog u talogu) na reakciju PCR jer će to utjecati na djelovanje polimeraze Taq.
For each PCR (see below 3-5) the special primer as a new combination of “Reaction-Mix” and the adequate needed amount of template DNA for each sample (see above) is needed. The respective volumes will be transferred into new tubes using pipettes.
0,5 μl – 2 μl
5 μl (25 mM)
5 μl (25 mM)
2,5 mM
2,5 mM
The selection of which method to use depends on a number of factors; the following Table is given to help the selection.
Odabir metode ovisi o brojnim čimbenicima, a sljedeća tablica služi kao pomoć pri odabiru.
If samples are preserved (paragraph 24) for analysis at a later time, take more samples than the required minimum number of five. Analyse the last samples first, and by a step-wise “backwards” selection of appropriate samples for analysis, it is possible to obtain a good description of the biodegradation curve with a relatively small number of analytical determinations.
Ako se uzorci čuvaju (stavak 24.) za kasniju analizu, treba uzeti više uzoraka od minimalno potrebnih pet. Prvo se analiziraju zadnji uzorci, a postupnim odabirom odgovarajućih uzoraka za analizu obrnutim redoslijedom moguće je dobiti dobar opis krivulje biorazgradnje s relativno malim brojem analitičkih određivanja.
Agriculture Canada (1987).
Agriculture Canada (1987.).
Dutch Commission for Registration of Pesticides (1991).
Dutch Commission for Registration of Pesticides (1991.).
BBA (1986).
BBA (1986.).
SETAC (1995).
SETAC (1995.).
26, 305 (1962).
26, 305 (1962.).
The water should be of constant quality during the period of a test. The pH of the overlying water should be between 6 and 9.
Tijekom razdoblja ispitivanja voda bi trebala biti stalne kakvoće. pH-vrijednost vode iznad sedimenta trebala bi biti između šest i devet.
If any solubilising agent is used for application of the test substance, a solvent control should be run (at least 3 replicates should be sampled at start, 3 at the end of the uptake phase, and 3 at the end of the elimination phase). In this case, at least 4 replicates of a negative control (no solvent) should be provided for sampling at the end of the uptake phase.
Ako je za primjenu ispitivane tvari upotrijebljeno bilo kakvo otapajuće sredstvo, potrebno je oformiti kontrolnu skupinu s otapalom (najmanje tri višestruka određivanja trebala bi biti uzorkovana na početku, tri na kraju apsorpcije i tri na kraju eliminacije) U tom slučaju potrebno je pružiti najmanje četiri višestruka određivanja iz negativne kontrole (bez otapala) za uzorkovanje na kraju faze apsorpcije.
end of uptake phase; retaining of sufficient subsamples of worms for determination of analytical background values, wet and dry weight, and lipid content;
završetak faze apsorpcije, zadržavanje dovoljnog broja poduzoraka crva radi određivanja analitičkih pozadinskih vrijednosti, mokre i suhe mase te sadržaja lipida;
& Gilberg, D. (2006).
& Gilberg, D. (2006.).
Validity assessment of log Kow/log BCF correlations. In:
Validity assessment of log Kow/log BCF correlations. u:
U.S. EPA (1996).
US EPA (1996.).
& Buijze, A. (1994).
& Buijze, A. (1994.).
Hydrobiologia 377:
Hydrobiologia 377: 183.
& Navarro, E. (1999).
& Navarro, E. (1999.).
Life cycles of mass species of Tubificidae (Oligochaeta). In:
Life cycles of mass species of Tubificidae (Oligochaeta). u:
Council Implementing Regulation (EU) 2016/276
Provedbena uredba Vijeća (EU) 2016/276
of 25 February 2016
od 25. veljače 2016.
On 25 February 2016, the Council adopted Decision (CFSP) 2016/280 amending Decision 2012/642/CFSP concerning restrictive measures against Belarus [2], extending the application of the restrictive measures until 28 February 2017 and amending Annex I and deleting Annex II to that Decision.
Vijeće je 25. veljače 2016. donijelo Odluku (ZVSP) 2016/280 o izmjeni Odluke 2012/642/ZVSP o mjerama ograničavanja protiv Bjelarusa [2], kojom je primjena mjera ograničavanja produljena do 28. veljače 2017. te kojom je izmijenjen Prilog I. i izbrisan Prilog II. toj Odluci.
Done at Brussels, 25 February 2016.
Sastavljeno u Bruxellesu 25. veljače 2016.
Council Decision (CFSP) 2016/280 of 25 February 2016 amending Decision 2012/642/CFSP concerning restrictive measures against Belarus (see page 30 of this Official Journal).
Odluka Vijeća (ZVSP) 2016/280 od 25. veljače 2016. o izmjeni Odluke 2012/642/ZVSP o mjerama ograničavanja protiv Bjelorusa (vidjeti str. 30. ovog Službenog lista).
Persons referred to in Article 2(1)
Osobe iz članka 2. stavka 1.
Reasons for listing
Razlozi za uvrštenje na popis