natgillin/translations-raw huggingface dataset:
P. F. Landrum, M. L. Gedeon, G. A. Burton, M. S. Greenberg og C. D. Rowland (2002), Biological Responses of Lumbriculus variegatus Exposed to Fluoranthene-Spiked Sediment, Arch.
The temperature in the test vessels should be 24 ± 2 °C. The pH of the control medium should not increase by more than 1,5 units during the test.
Environ.
EyCx (frond number); and EyCx (total frond area, dry weight, or fresh weight).
C. G. Ingersoll, E. L. Brunson, N. Wang, F. J. Dwyer, G. T. Ankley, D. R. Mount, J. Huckins, J. Petty og P. F. Landrum (2003), Uptake and depuration of non-ionic organic contaminants from sediment by the oligochaete, Lumbriculus variegatus, Environmental Toxicology and Chemistry 22, 872-885.
Water quality — Determination of growth inhibition (7-d) Lemna minor, duckweed.
R. O. Brinkhurst (1971).
SWEDEN
J. L. Kaster, J. V. Klump, J. Meyer, J. Krezoski og M. E. Smith (1984), Comparison of defecation rates of Limnodrilus hoffmeisteri using two different methods, Hydrobiologia 11, 181-184.
(mg/ߦl)
M. Martinez-Madrid, P. Rodriguez, J. I. Perez-Iglesias og E. Navarro (1999), Sediment toxicity bioassays for assessment of contaminated sites in the Nervion river (Northern Spain).
The pH is adjusted to 6,5 ± 0,2 with either 0,1 or 1 mol HCl or NaOH, and the volume adjusted to one litre with deionised water.
Environment Canada (1995), Guidance document on measurement of toxicity test precision using control sediments spiked with a reference toxicant, Environmental Protection Series Report EPS 1/RM/30.
Stock solutions are prepared in sterile distilled or deionised water.
Toxicol.
(I. Sims, P. Whitehouse and R. Lacey.
Supplerende litteratur om statistiske metoder:
WRc plc — Environment Agency.)
Dunnett (1964), New tables for multiple comparisons with a control, Biometrics 20, 482-491.
(mg/ߦl) [1]
6, 65-70.
22 °C ± 10 °C;
R. G. Miller Jr.
350 ± 50 μE/m2/s.
S. S. Shapiro og M. B. Wilk (1965), An analysis of variance test for normality (complete samples), Biometrika 52:
For crop protection products, the physical/chemical properties and use pattern of the test chemical, its maximum concentration or application rate, the number of applications per season and/or the persistence of the test chemical need to be considered.
591-611.
The number and spacing of the concentrations or rates should be sufficient to generate a reliable dose-response relationship and regression equation and give an estimate of the ECx. or ERx.
D. A. Williams (1971), A test for differences between treatment means when several dose levels are compared with a zero dose control, Biometrics 27, 103-117.
The selected concentrations/rates should encompass the ECx or ERx values that are to be determined.
M. E. Casanueva (1993), Phylogenetic studies of the free-living and arthropod associated Laelapidae (Acari: Mesostigmata), Gayana Zool.
US EPA.
F. M. Bakker, R. Feije, A. J. Grove, G. Hoogendorn, G. Jacobs, E. D. Loose og P. van Stratum (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, JSS — Journal of Soils and Sediments 3, 73-77.
AFNOR, X31-201.
A. Ruf (1991), Do females eat males?:
Hale, B., Hall, J.C., Solomon, K., and Stephenson, G. (1994).
Laboratory studies on the popualation development of Hypoaspis aculeifer (Acari: Parasitiformes), in:
Soil Texture Classification (US and FAO systems):
F. Dusbabek og V. Bukva (eds.):
Audus, L.J.
s. 621-628.
Boutin, C.;
H. Lokke og C. A. M. van Gestel, Handbook of soil invertebrate toxicity tests, John Wiley Sons, Chichester, s. 239-251.
Patterns of sensitivity of plant species to various herbicides — An analysis with two databases.
Glazebrook, N. M. Van Straalen og J. V. Tarazona (eds.), SETAC Press, Pensacola, USA, s. 128 ff.
Guidance Document, Current Approaches in the Statistical Analysis of Ecotoxicity Data:
H.-J.
Hatzios, K.K. and Penner, D. (1985).
Schlosser og F. Riepert (1991/92), Entwicklung eines Prüfverfahrens für Chemikalien an Bodenraubmilben (Gamasina), Teil 1:
Hamill, P.B., Marriage, P.B. and G. Friesen.
Soil Organisms and Functions, Bull. OEPP/EPPO Bull., 33, 195-209.
14-21
Glazebrock, N. M. Van Straalen og J. V. Tarazona (2002), Test methods to determine hazards of sparingly soluble metal compounds in soils, SETAC Press, Pensacola, FL, USA.
25-61 (14, 29)
H. Chi (1981), Die Vermehrungsrate von Hypoaspis aculeifer Canestrini (Acarina, Laelapidae) bei Ernährung mit Onychiurus fimatus Gisin (Collenbola), Ges.allg..angew.
10-20 (6, 21)
H. J. Schlosser og F. Riepert (1992), Entwicklung eines Prüfverfahrens für Chemikalien an Bodenraubmilden (Gamasina), Zool.Beitr.
10-20 (6, 10)
Ges.
14-28
D. K. Kevan, McE., og G. D. Sharma (1964), Observations on the biology of Hypoaspis aculeifer (Canestrini, 1884), apparently new to North America (Acarina: Mesostigmata: Laelaptidae), Acarologia 6, 647-658.
5-8 (4, 14, 29)
Litteraturliste
2,1 -2,3 (14, 19)
OECD (2006a), Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1A), OECD Environmental Health and Safety Publications Series on Testing and Assessment No.60, ENV/JM/MONO(2006)27.
7-9 (14, 19)
OECD (2006b), Report of the Initial Work Towards the Validation of the 21-Day Fish Screening Assay for the Detection of Endocrine active Substances (Phase 1B), OECD Environmental Health and Safety Publications Series on Testing and Assessment No.61, ENV/JM/MONO(2006)29.
POST (4, 22 — 26)
purification, characterization and quantitative immunoassay for the detection of estrogenic compounds, Comparative Biochemistry and Physiology, Part C Pharmacology, toxicology and endocrinology;
Clapham, A.R., Tutin, T.G., & Warburg, E.F.
G. H. Panter, C. R. Tyler, S. Maddix, P. M. Campbell, T. H. Hutchinson, R. Länge, C. Lye og J. P. Sumpter (1999), Application of an ELISA to quantify vitellogenin concentrations in fathead minnows (Pimephales promelas) exposed to endocrine disrupting chemicals, CEFIC-EMSG research report reference AQ001, CEFIC, Bruxelles, Belgien.
Cambridge University Press, Cambridge
Homung, T. R. Henry, J. S. Denny, R. L. Leino, V. S. Wilson, M. C. Cardon, P. C. Hartig og L. E. Gray (2003), Effects of the androgenic growth promoter 17-beta-trenbolone on fecundity and reproductive endocrinology of the fathead minnow, Environmental Toxicology and Chemistry;
Flynn, S., Turner, R.M., and Dickie, J.B.
E Vorter på underkæben, tæt på munden, normalt små og sædvanligvis i par. Varierende hos hanner i kontroller eller behandlede hanner og hos behandlede hunner.
Marrs, R.H., Frost, A.J., & Plant, R.A.
F Vorter ventralt i forhold til E, normalt små og i par. Tilstedeværende hos hanner i kontroller og hos hunner, der eksponeres for androgener.
Marrs, R.H., Frost, A.J., Plant, R.A., & Lunnis, P. 1993.
S. R. Miles-Richardson, V. J. Kramer, S. D. Fitzgerald, J. A. Render, B. Yamini, S. J. Barbee og J. P. Giesy (1999), Effects of waterborne exposure of 17-estradiol on secondary sex characteristics and gonads of fathead minnows (Pimephales promelas), Aquat Toxicol 47:129-145.
National Plant Data Centre, Baton Rouge, LA 70874-4490 USA
Fodringen i præeksponeringsperioden justeres omhyggeligt, så den opfylder kravene til haletudsernes udvikling, dvs. at der gives de nyudklækkede haletudser små portioner foder flere gange om dagen (mindst to).
350 ± 50 ppm;
OECD anbefaler højst 100 μl/l i sit Guidance Document, mens det i en senere oversigt anbefales, at der bruges opløsningsmiddelkoncentrationer helt ned til 20 μl/l fortyndingsvand (12).
The vehicle is sprayed on or mixed with a small amount, for example 2,5 g, of fine quartz sand.
Med henblik på denne test fastsættes den høje teststofkoncentration ved testkemikaliets opløselighedsgrænse, den maksimalt tolererede koncentration (MTC) for akut toksiske kemikalier eller 100 mg/l, alt efter hvilken der er lavest.
Alternatively, a multiple U-test, e.g. the Bonferroni-U-test according to Holm (29), or when these data exhibit heteroscedasticity but are otherwise consistent with a underlying monotone dose-response, an other non-parametric test [e.g. Jonckheere-Terpstra (30) (31) or Shirley (32) (33)] can be applied and would generally be preferred to unequal-variance t-tests. (see also the scheme in Appendix 7).
anvendte statistiske analyseteknikker og begrundelse for de anvendte teknikker, resultater af den statistiske analyse, helst i tabelform
Römbke, J. (1989).
Et centralt kriterium for at betegne tilfælde af abnorm morfologisk udvikling som »asynkron udvikling« er, at den relative timing af vævsremodellering og vævsmorfogenese er forstyrret, mens de berørte vævs morfologi ikke er åbenlyst abnorm.
Entwicklung eines Reproduktionstests an Bodenorganismen — Enchytraeen.
Et eksempel til at illustrere denne fortolkning af makroskopiske morfologiske abnormiteter er, at forsinket baglemsmorfogenese i forhold til udviklingen af andre væv vil opfylde kriteriet for »asynkron udvikling«, mens tilfælde af manglende baglemmer, abnorme fingre eller tæer (f.eks. ektrodaktylia, polydaktylia) eller andre åbenlyse misdannelser af lemmer ikke skal betragtes som »asynkron udvikling«.
Römbke, J. and Moser, T. (1999).
Environmental Health and Safety Publications, Series on Testing and Assessment.
Westheide, W. and Bethge-Beilfuss, D. (1991).
OECD (2006) Current Approaches in the Statistical Analysis of Ecotoxicity Data:
Römbke, J. (1995).
Edwards (1955) Simple techniques for rearing Collembola, Symphyla and other small soil inhabiting arthropods.
Bell, A.W.
Williams (1971), A test for differences between treatment means when several dose levels are compared with a zero dose control.
Hoeven, N. van der, (1998).
Williams (1972), The comparison of several dose levels with a zero dose control.
355-361
D. Jungmann, C. Bandow, T. Gildemeister, R. Nagel, T.G. Preuss, H.T. Ratte, C. Shinn, L. Weltje og H.M.
Holm, S., (1979):
J.N.K. Rao og A.J.
Jonckheere, A. R. (1954);
E.R.
Terpstra, T. J. (1952);
Christensen (1984), Dose-response functions in aquatic toxicity testing and the Weibull model, Water Res., 18:
Shirley, E. A. (1979);
R.D. Bruce og D.J.
Sokal, R.R. and F.J.
Slob (2002), Dose-response modelling of continuous endpoints.
2nd edition.
D.A. Benoit, P.K. Sibley, J.L. Juenemann, og G.T.
Christensen, E.R., (1984).
Development and validation of a new test system, red. af M. Streloke og H. Köpp.
Van Ewijk, P.H. and J.A.
2 (± 0,5)
After shaking, the suspension is left to settle for at least 2 hours but not for longer than 24 hours.
30-50
The pH of the liquid phase is then measured using a pH-meter, that has been calibrated before each measurement using an appropriate series of buffer solutions (e.g. pH 4,0 and 7,0).
> 150 mg
Enchytraeus crypticus (Westheide & Graefe 1992):
> 120 mg
Enchytraeus buchholzi (Vejdovsky 1879):
Til gennemstrømningstest anbefales en belastningsgrad på højst 0,5 g/l pr. døgn og højst 5 g/l opløsning på noget tidspunkt Senest 28 dage efter befrugtning omfordeles antallet af fisk pr. replikat, så hvert replikat indeholder et så lige antal fisk som muligt.
Enchytraeus bulbosus (Nielsen & Christensen 1963):
anvendt testprocedure (f.eks. gennemstrømning semistatisk/udskiftning), testdesign, herunder testkoncentrationer, metode til fremstilling af stamopløsninger (i et bilag), udskiftningsfrekvens (hvis der bruges opløsningsmiddel og koncentrationer heraf, skal det anføres)
the duration of the reproduction test can (but need not) be shorter, i.e. four instead of six weeks; however, the duration of the Range-Finding Test should not be changed;
Resultater, der afviger fra validitetskriterierne (i kontrollerne), fremhæves.
Phillips, C.T., Checkai, R.T. and Kuperman, R.G.
Osborne, P. Matthiessen og J.P.
At least four replicates per treatment?
H. Holbech, L. Andersen, G.I.
No success
F. Brion, B.M.
Esterases of earthworm — III.
K.A. Kidd, P.J.
SETAC (1998).
Lazorchak og R.W.
EPA (1996).
Indlejret ANOVA ikke normal
Sci.
De klargjorte og frosne rør (beskrevet i ovenstående afsnit) optøs på is. Herefter centrifugeres de under anvendelse af en Eppendorf-centrifuge (30 sekunder ved maksimal hastighed ved stuetemperatur).
Transform data Data:
Undertiden giver de to beregningsmåder (procent af ThOD eller procent af COD) ikke de samme resultater, men man skal helst bruge ThOD, da nogle stoffer ikke iltes fuldstændigt i COD-testen.
discussion of results, including any deviations from the procedures in this test method and discuss any deviations in the test results due to interferences and errors from what would be expected;
Højere afvigelser blev også påvist i beholdere med et volumen på < 150 ml. Endelige pH-værdier for testmediet lå i området 6,5-7,0.
Shelton DR, Tiedje JM (1984).
Sørg for, at det samlede volumen af væske V1 og headspacevolumen Vh er det samme i alle beholdere, og noter og registrer værdierne af V1 og Vh.
Appl.
Væskevolumen (Vl ) (liter):
Concentration of inoculum in test bottles (g/l)
Jordprøverne (undtagen dem, der bruges til ældning af testkemikaliet) lufttørres ved stuetemperatur (helst ved 20-25 °C) Disaggregering bør foretages med mindst mulig kraft, således at den oprindelige jordstruktur ændres mindst muligt.
Using a 500 μm mesh, most of the sediment particles will pass the sieve very quickly; however, sieving should be done quickly, in order to prevent the worms from crawling into or through the mesh.
M.H.
chemical identification data (common name, chemical name, structural formula, CAS number, etc.) including purity and analytical method for quantification of test chemical;
John Wiley & Sons, Inc.,
source of the test chemical, identity and concentration of any solvent used.
F. Scheffer og P. Schachtschabel (1998).
ASTM International (2002).
J.B. Weber, L.R. Swain, H.J. Strek og J.L.
U.S. EPA (2000).
Inherent Biodegradability in Soil (vedtaget 12. maj 1981).
Riedhammer C. & B. Schwarz-Schulz (2001).
N. Drescher (1985).
ASTM International (2004).
N. Burkhard, D.O. Eberle og J.A.
Egeler, Ph., Meller, M., Schallnaß, H.J.
Guth (1985).
In co-operation with R. Nagel and B. Karaoglan.
C.I.
Environment Canada (2003).
C.S.
Nikkilä A., Halme A., Kukkonen J.V.K.
Fjernelse af replikater til prøveudtagning, kontrol af luftforsyning, ormenes adfærd, vandkvalitet (se punkt 52), udtagning af vand-, sediment- og ormeprøver til bestemmelse af teststoffets koncentration
Environment Canada (1995).
Folia urticae, pulveriserede blade af Urtica sp. (brændenælde), findelt (partikelstørrelse ≤ 0,5 mm) eller en blanding af pulveriserede blade af Urtica sp. med α-cellulose (1: 1), i overensstemmelse med farmaceutiske standarder til konsum, ud over tørt sediment
Mount, D.R., Dawson, T.D.
Suspensionen konditioneres i mindst to dage med forsigtig omrøring ved 20 ± 2 °C for at stabilisere pH-værdien og opnå en stabil mikrobiel komponent. pH-værdien måles igen og justeres om nødvendigt til 6,0 ± 0,5 med CaCO3.
OECD 2006.
Environ.Toxicol.
Dissolve 2,59 g NaHCO3 in deionised water; make up to 1 l with deionised water
Ph.
OECD (1992).
Egeler, M. Meller, H. J. Schallnaß og D. Gilberg (2006).
e.g. Urtica powder (Folia urticae), leaves of Urtica dioica (stinging nettle), finely ground (particle size ≤ 0,5 mm); in accordance with pharmacy standards, for human consumption;
Rapport til den tyske miljøstyrelse (Umweltbundesamt Dessau), R&D No.:
If elevated ammonia concentrations are expected, e.g. if the test chemical is known to inhibit nitrification, it may be useful to replace 50 % of the nitrogen-rich urtica powder by cellulose (e.g., α-Cellulose powder, chemically pure, particle size ≤ 0,5 mm; (1) (2)).
Levine, L.A. Buttel, A.C.
Preparation
, Toxicokinetics in aquatic systems:
Finland
Markwell, D.W.
Via Mornera 25
Gabric, D.W.
I-20047 Brugherio MI
C. Franke, G. Studinger, G. Berger, S. Böhling, U. Bruckmann, D. Cohors-Fresenborg og U. Jöhncke (1994), The assessment of bioaccumulation.
MDD:
Leppänen og J.V.K.
Ruf, A. (1991).
Ozretich, J.L.
Ruf, A. (1996).
Evaluation of selected lipid methods for normalising pollutant bioaccumulation.
Løkke, H., Janssen, C.R., Lanno, R.P., Römbke, J., Rundgren, S. and Van Straalen, N.M.
Van Straalen (2003), Dietary zinc reduces uptake but not metallothionein binding and elimination of cadmium in the springtail Orchesella cincta.
Schlosser, H.J., und Riepert, F. 1992.
A. Mudroch, J.M.
Southwood, T.R.E.
Hermens (1996).
Ignatowicz, S. (1974).
Toxicity and toxicokinetics for benthic organisms;
Kevan, D.K.
C. Bonacina, A. Pasteris, G. Bonomi og D. Marzuoli (1994), Quantitative observations on the population ecology of Branchiura sowerbyi (Oligochaeta, Tubificidae).
ENV/JM/MONO(2006)18
Væskeformigt affald, der indeholder dette kemikalie, skal bortskaffes på behørig vis og må ikke udledes direkte i spildevandssystemet.
Developmental time from egg to adult female is approximately 20 days at 20 °C.
Rådets gennemførelsesforordning (EU) 2016/276
Council Implementing Regulation (EU) 2016/276
under henvisning til Rådets forordning (EF) nr. 765/2006 af 18. maj 2006 om restriktive foranstaltninger over for Belarus [1], særlig artikel 8a, stk. 1,
Having regard to Council Regulation (EC) No 765/2006 of 18 May 2006 concerning restrictive measures in respect of Belarus [1], and in particular Article 8a(1) thereof,
Den 25. februar 2016 vedtog Rådet afgørelse (FUSP) 2016/280 om ændring af afgørelse 2012/642/FUSP om restriktive foranstaltninger over for Hviderusland [2], hvorved anvendelsen af de restriktive foranstaltninger over for Hviderusland forlængedes indtil den 28. februar 2017 og bilag I til nævnte afgørelse ændredes og bilag II til nævnte afgørelse udgik.
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.
Rådets forordning (FUSP) 2016/280 af 25. februar 2016 om ændring af afgørelse 2012/642/FUSP om restriktive foranstaltninger over for Hviderusland (se side 30 i denne EUT).
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).
Personer, der er omhandlet i artikel 2, stk. 1
Persons referred to in Article 2(1)
Управлениe Делами Президентаул.
Former Head of the Special Response Group at the Ministry of Interior (SOBR).
Departementschef i præsidentens administration.
Businessman, Head of “Honour”, the Ministry of Interior's Association of the veterans from special forces from the Ministry of Interior.
Sheiman er fortsat præsidentens særlige assistent/rådgiver.
Hrodna region
Tidligere indenrigsminister og også tidligere chef for præsidentens sikkerhedstjeneste.
Маркса, 38
Tidligere leder af den særlige indsatsgruppe i indenrigsministeriet (SOBR).
Минск
Ansvarlig for Yuri Zakharenkos, Viktor Gonchars, Anatoly Krasovskis og Dmitri Zavadskis uopklarede forsvinden i Hviderusland i 1999-2000.
Head of the Management Department of the President's Administration.
Nøgleperson i forbindelse med Yuri Zakharenkos, Viktor Gonchars, Anatoly Krasovskis og Dmitri Zavadskis uopklarede forsvinden i Hviderusland i 1999-2000.
Former Secretary of the Security Council.
Tidligere minister for turisme og sport, tidligere indenrigsminister og præsidentens tidligere vicekabinetschef.«
Sheiman remains a Special Assistant/Aid to the President.
Dijkhoff
Onory, Sakhalin Region
Formand
Orchestrated the unresolved disappearances of Yuri Zakharenko, Viktor Gonchar, Anatoly Krasovski and Dmitri Zavadski in Belarus in 1999-2000.
Paulichenka, Dzmitry Valerievich,
Former Minister of Tourism and Sports, former Minister of Interior and former Deputy Head of the Presidential Administration.’
Rådets forordning (EU) 2016/277
Council Regulation (EU) 2016/277
Rådets forordning (EF) nr. 765/2006 [2], som ændret, foreskriver indefrysning af aktiver tilhørende præsident Lukashenko og visse embedsmænd i Belarus samt af aktiver tilhørende personer, der er ansvarlige for alvorlige krænkelser af menneskerettighederne eller undertrykkelse af civilsamfundet og den demokratiske opposition, og personer og enheder, der drager fordel af eller støtter Lukashenkoregimet, herunder især personer og enheder, der yder finansiel eller materiel støtte til regimet.
Council Regulation (EC) No 765/2006 [2] provides for a freezing of the assets of President Lukashenko and certain officials of Belarus, as well as of assets of persons responsible for serious violations of human rights or the repression of civil society and democratic opposition, and of persons and entities benefiting from or supporting the Lukashenko regime, including, in particular, persons and entities providing financial or material support to that regime.
Indefrysningen af aktiver bør opretholdes for så vidt angår fire personer, der er opført i bilag I til forordning (EF) nr. 765/2006.
The application of the asset freeze should be maintained in respect of four persons listed in Annex I to Regulation (EC) No 765/2006.
Alle de i bilag IV til forordning (EF) nr. 765/2006 opførte personer og enheder, for hvem indefrysningen af aktiver blev suspenderet, bør udgå, og suspensionen af anvendelsen af forbuddene bør bringes til ophør.
All persons and entities listed in Annex IV to Regulation (EC) No 765/2006 in respect of which the application of the asset freeze was suspended should be deleted, and the suspension of the application of the prohibition should be brought to an end.
Da denne foranstaltning falder ind under traktatens anvendelsesområde, er lovgivning på EU-plan nødvendig for at kunne gennemføre den, navnlig for at sikre at de økonomiske aktører i alle medlemsstater anvender den på samme måde.
This measure falls within the scope of the Treaty and regulatory action at the level of the Union is therefore necessary in order to give effect to it, in particular with a view to ensuring its uniform application by economic operators in all Member States.
Forordning (EF) nr. 765/2006 bør derfor ændres i overensstemmelse hermed —
Regulation (EC) No 765/2006 should therefore be amended accordingly,
Artikel 2, stk. 6, udgår.
in Article 2, paragraph 6 is deleted;
Artikel 8b udgår.
Article 8b is deleted;
Rådets forordning (EF) nr. 765/2006 af 18. maj 2006 om restriktive foranstaltninger over for Belarus (EUT L 134 af 20.5.2006, s. 1).
Council Regulation (EC) No 765/2006 of 18 May 2006 concerning restrictive measures in respect of Belarus (OJ L 134, 20.5.2006, p. 1).
Kommissionens gennemførelsesforordning (EU) 2016/278
Commission Implementing Regulation (EU) 2016/278
om ophævelse af den endelige antidumpingtold på importen af visse skruer, bolte, møtrikker og lignende varer af jern og stål med oprindelse i Folkerepublikken Kina, udvidet til også at omfatte importen af visse skruer, bolte, møtrikker og lignende varer af jern og stål afsendt fra Malaysia, uanset om varerne er angivet med oprindelse i Malaysia eller ej
repealing the definitive anti-dumping duty imposed on imports of certain iron or steel fasteners originating in the People's Republic of China, as extended to imports of certain iron or steel fasteners consigned from Malaysia, whether declared as originating in Malaysia or not
under henvisning til Europa-Parlamentets og Rådets forordning (EU) 2015/476 af 11. marts 2015 om de foranstaltninger, Unionen kan træffe på grundlag af en rapport vedtaget af WTO's Tvistbilæggelsesorgan vedrørende antidumping- og antisubsidieforanstaltninger [1] (»WTO-bemyndigelsesforordningen«), særlig artikel 1, stk. 1, litra a), og
Having regard to Regulation (EU) 2015/476 of the European Parliament and of the Council of 11 March 2015 on the measures that the Union may take following a report adopted by the WTO Dispute Settlement Body concerning anti-dumping and anti-subsidy matters [1] (‘the WTO enabling Regulation’), and in particular Article 1(1)(a) thereof,
Rådet indførte ved forordning (EF) nr. 91/2009 [2] en endelig antidumpingtold på importen af visse skruer, bolte, møtrikker og lignende varer af jern eller stål med oprindelse i Folkerepublikken Kina (»Kina«).
The Council by Regulation (EC) No 91/2009 [2] imposed a definitive anti-dumping duty on imports of certain iron or steel fasteners originating in the People's Republic of China (‘China’).