natgillin/translations-raw huggingface dataset:
Since 1972 it is divided into two subspecies (Eisenia fetida and Eisenia andrei (10)).
Od leta 1972 se deli na dve podvrsti (Eisenia fetida in Eisenia andrei (10)).
According to Jaenike (36), they are true, separate species.
Jaenike trdi (36), da sta to pravi ločeni vrsti.
Eisenia fetida is easily recognised by its bright intersegmental yellow stripes whereas Eisenia andrei has a uniform, dark red colour.
Vrsto Eisenia fetida je mogoče brez težav prepoznati po svetlih rumenih črtah med kolobarji, Eisenia andrei pa je enotne temno rdeče barve.
Eisenia fetida and Eisenia andrei are commercially available, e.g. as fish bait.
Eisenia fetida in Eisenia andrei sta komercialno dostopni vrsti, npr. kot vaba za ribe.
In recent years, this species has often been used in ecotoxicological studies because of the simplicity of its breeding and testing, e.g. Kuperman et al.
V zadnjih letih se ta vrsta pogosto uporablja v ekotoksikoloških raziskavah, ker jo je preprosto gojiti in preskušati, npr. Kuperman idr.
American Chemical Society, Washington, DC, 2-1 to 2-52.
F., Rosenblatt, D. H., (ur.) American Chemical Society, Washington, DC, 2-1 do 2-52.
Series on Testing and Assessment No 19. ENV/JM/MONO(2000)7.
Series on Testing and Assessment No 19, ENV/JM/MONO(2000)7.
Academic Press: San Diego, CA, pp. 52-85.
Academic Press: San Diego, Kalifornija, str. 52–85.
(eds), Springer Verlag Heidelberg, pp. 229-258.
V: Toxicology of Inhaled Material, Witschi, H. P. in Brain, J. D. (ur.), Springer Verlag Heidelberg, str. 229–258.
In: Waalkes MP and Ward JM (eds) Carcinogenesis.
V: Waalkes, M. P. in Ward, J. M. (ur.) Carcinogenesis.
Report of the Consultation Meeting on Sub-chronic and Chronic Toxicity/Carcinogenicity Testing (Rome, 1995), internal working document, Environment Directorate, OECD, Paris.
Report of the Consultation Meeting on Sub-chronic and Chronic Toxicity/Carcinogenicity Testing (Rim, 1995), internal working document, Environment Directorate, OECD, Pariz.
In D’Arcy POF & Harron DWG (eds).
V: D’Arcy POF & Harron DWG (ur.).
Queen’s University Press, Belfast. pp 279-284.
Queen’s University Press, Belfast. str. 279–284.
Washington, D.C., US Dept. of Health and Human Services.
Washington D.C., US. Dept. of Health and Human Services.
Experience and Data from the OECD Activated Sludge Simulation Test. pp. 113-138.
Experience and Data from the OECD Activated Sludge Simulation Test, str. 113–138.
In: Laboratory Tests for Simulation of Water Treatment Processes CEC Water Pollution Report 18.
V: Laboratory Tests for Simulation of Water Treatment Processes CEC Water Pollution Report 18.
Technical Report TR70, Water Research Centre, Stevenage, UK.
Technical Report TR70, Water Research Centre, Stevenage, Združeno kraljestvo.
Hales SG, Feitjel T, King H, Fox K, Verstraete W.
Delavnica v Port Sunlightu, ZK.
SETAC- Europe, Brussels.
SETAC Europe, Bruselj.
In some circumstances, however, specific information is required relating the behaviour of a chemical to methods of waste water treatment involving biofilms, namely, percolating or trickling filters, rotating biological contactors, fluidised beds. To meet this need various devices have been developed. 2. Gerike et al.
Vendar pa so v nekaterih okoliščinah potrebne posebne informacije o odzivanju kemikalije na metode čiščenja odpadne vode, ki vključujejo biofilme, to so precejalniki, rotirajoči biološki kontaktorji in reaktorji s tehnologijo vrtinčnih plasti.
used large, pilot-scale trickling filters which they used in the coupled mode. These filters took up much space and required relatively large volumes of sewage or synthetic sewage. Truesdale et al.
Za izpolnitev te potrebe so bile razvite različne naprave.
Edited by M. Streloke and H.Köpp.
Uredila M. Streloke in H. Köpp.
Final Report to them European Commission.
Končno poročilo za Evropsko komisijo.
Report No: EC 3738.
Poročilo št.: EC 3738. Avgust 1994.
August 1994. WRc, UK.
WRc, Združeno kraljestvo.
From the WOSTA Workshop held in the Netherlands.
Z delavnice WOSTA, ki je potekala na Nizozemskem.
In ASTM International 2002 Annual Book of Standards.
V ASTM International 2002 Annual Book of Standards.
Elendt BP and Bias W-R (1990).
Elendt, B. P., in Bias, W.-R.
OECD Ring-test of methods for determining ready biodegradability: Chairman’s report (M. Hashimoto; MITI) and final report (M. Kitano and M. Takatsuki; CITI).
OECD Ring-test of methods for determining ready biodegradability: Chairman’s report (M. Hashimoto; MITI) and final report (M. Kitano in M. Takatsuki; CITI).
Ring-test of the ISO Headspace CO2 method: application to surfactants: Surfactant Ring Test-1, Report EU4697, Water Research Centre, May 1999, Medmenham, SL7 2HD, UK.
Ring-test of the ISO Headspace CO2 method: application to surfactants: Surfactant Ring Test-1, Report EU4697, Water Research Centre, maj 1999, Medmenham, SL7 2HD, Združeno kraljestvo.
ASTM International, E1676-04: 26 pp.
ASTM International, E1676–04: str. 26.
INRA, Annales de Zoologie-Ecologie animale, Paris, 671 p.
INRA, Annales de Zoologie-Ecologie animale, Paris, str. 671.
Elsevier Science Ltd, The Netherlands, pp. 555-576.
Elsevier Science Ltd., The Netherlands, str. 555–576.
Dissertation University Mainz, 156 pp.
Dissertation University Mainz, str. 156.
Second Edition, EPA 600/R-99/064, US, Environmental Protection Agency, Duluth, MN, March 2000.
Second Edition, EPA 600/R-99/064, US, Environmental Protection Agency, Duluth, MN, marec 2000.
The influence of soil characteristics on the toxicity of chemicals for earthworms; a review, In: Ecotoxicology of Earthworms (Ed. Becker, H, Edwards, PJ, Greig-Smith, PW & Heimbach, F).
The influence of soil characteristics on the toxicity of chemicals for earthworms; a review, In: Ecotoxicology of Earthworms (Ur. Becker, H, Edwards, PJ, Greig-Smith, PW & Heimbach, F).
Originating probably from the region of the Black Sea, they are distributed worldwide today, especially in anthropogenically modified habitats like compost heaps.
Izvirajo verjetno iz črnomorske regije, danes pa so razširjeni po vsem svetu, zlasti v antropogeno prilagojenih habitatih, kot so kompostni kupi.
Both can be used for ecotoxicological as well as bioaccumulation tests.
Obe podvrsti je mogoče uporabljati za ekotoksikološke in bioakumulacijske preskuse.
Sims RW and Gerard BM (1985).
Sims, R. W., in Gerard, B. M. (1985).
Westheide W and Graefe U (1992).
Westheide, W., in Graefe, U. (1992).
Westheide W and Müller MC (1996).
Westheide, W., in Müller, M. C. (1996).
On the day of randomisation, animals should be young adults 7 to 9 weeks of age. Body weights should be within ± 20 % of the mean weight for each sex.
Na dan randomizacije morajo biti živali mladi odrasli primerki, ki so stari 7 do 9 tednov in katerih telesna teža ne odstopa za več kot ± 20 % od povprečne teže za vsak spol.
A Method for the RoutineAssessment of Fore- and Hind-limb Grip Strength of Rats and Mice.
A Method for the Routine Assessment of Fore- and Hind-limb Grip Strength of Rats and Mice.
Ordinance of the degradability of detergents in washing and cleaning agents.
Uredba o razgradljivosti detergentov v pralnih in čistilnih sredstvih. Bundesgesetzblatt, Pt.
where: ER
pri čemer je:
Revision to the first edition dated June 1994.
Sprememba prve izdaje iz junija 1994.
Trace Nutrient Deficiency in Daphnia magna Cultured in Standard Medium for Toxicity Testing.
Trace Nutrient Deficiency in Daphnia magna Cultured in Standard Medium for Toxicity Testing.
J.A,.Oil Chem Soc.
J.A,. Oil Chem Soc.
Part 2: Determination of effects on reproduction.
Del 2: Določanje vplivov na razmnoževanje.
Availability of polycyclic aromatic hydrocarbons to earthworms (Eisenia andrei, Oligochaeta) in field-polluted soils and soil-sediment mixtures.
J. G. M (2003a). Availability of polycyclic aromatic hydrocarbons to earthworms (Eisenia andrei, Oligochaeta) in field-polluted soils and soil-sediment mixtures.
The apparatus consists of a microcolumn (Figure 1), maintained at constant temperature. It is connected either to a recirculating pump (Figure 2) or to a levelling vessel (Figure 3).
Aparaturo sestavlja mikrokolona (slika 1), v kateri se ohranja konstantna temperatura in ki je povezana bodisi z recirkulacijsko črpalko (slika 2) bodisi z nivojsko posodo (slika 3).
In: Handbook of Chemical Property Estimation Methods: Environmental Behavior of Organic Compounds, Lyman WJ, Reehl WF, Rosenblatt DH, Eds.
V: Handbook of Chemical Property Estimation Methods: Environmental Behavior of Organic Compounds, Lyman, W. J., Reehl, W.
ACD logP; Advanced Chemistry Development: Toronto, Ontario M5H 3V9, Canada, 2001.
ACD logP; Advanced Chemistry Development: Toronto, Ontario M5H 3V9, Kanada, 2001.
Comparisons of the effect along a dose range should avoid the use of multiple t-tests. The statistical methods should be selected during the design of the study.
Pri primerjavah učinka vzdolž odmernega območja se je treba izogibati večkratnim preskusom t. Statistične metode je treba izbrati med zasnovo študije.
Wat.Res.
Wat. Res.
Baumann et al.
Baumann idr.
Removal of synthetic detergents in sewage treatment processes: Trials of a new biologically attackable material.Wat.
Removal of synthetic detergents in sewage treatment processes: Trials of a new biologically attackable material. Wat.
Trimming should also be done very carefully and only after fixation to avoid tissue damage. Tissue damage could compromise histopathology analysis.
Pri odstranjevanju priraščenih tkiv je prav tako potrebna velika previdnost, opravi pa se lahko šele po fiksaciji, da se preprečijo poškodbe tkiv, ki lahko ogrozijo histopatološko analizo.
The test chemical remaining in solution is determined at regular intervals e.g. hourly depending on the degradability of the chemical, for a period not longer than 24h. Samples are centrifuged before appropriate analysis.
Preskusna kemikalija, ki ostane v raztopini, se določa v rednih presledkih, npr. vsako uro, odvisno od razgradljivosti kemikalije, vendar ne več kot 24 ur. Vzorci se pred ustrezno analizo centrifugirajo.
Houben-Weyl, ed, Methoden der Organischen Chemie: 386-390.
Houben-Weyl (ur.), Methoden der Organischen Chemie: 386–390.
Principles and Methods for the Assessment of Neurotoxicity Associated with Exposure to Chemicals.
Principles and Methods for the Assessment of Neurotoxicity Associated with Exposure to Chemicals. Environmental Health Criteria.
Journal of Applied Toxicology 21:15-23.
Journal of Applied Toxicology 21: 15–23.
ProbitP
VerjetnostP
“Surfactant Biodegradation”, 2nd Edn. Marcel Dekker Inc. New York, 1085 pp.
‚Surfactant Biodegradation‘, 2. izdaja, Marcel Dekker Inc. New York, 1085 str.
< 10 μg/l
< 10 μg /l
In: Earthworm Ecology — from Darwin to vermiculture. Satchell, J.E.
In: Earthworm Ecology – from Darwin to vermiculture.
In Lyman WJ, Reehl WF, Rosenblatt DH, eds, Handbook of chemical property estimation, American Chemical Society, Washington, D.C.
F., Rosenblatt, D. H. (ur.). Handbook of chemical property estimation, American Chemical Society, Washington, D.C.
Multi-component powder aerosol concentration may also be determined by gravimetric analysis. However, this requires analytical data which demonstrate that the composition of airborne material is similar to the starting material.
Z gravimetrično analizo se lahko določi tudi koncentracija večkomponentnega prašnega aerosola, vendar so za to potrebni analitski podatki, ki kažejo, da je sestava snovi v zraku podobna začetni snovi.
The preferred species is the rat. Justification should be provided if other species are used.
Najprimernejša vrsta je podgana, uporabo drugih vrst je treba utemeljiti.
Meller M, Egeler P, Rombke J, Schallnass H, Nagel R, Streit B (1998).
Meller, M., Egeler, P., Rombke, J., Schallnass, H., Nagel, R., Streit, B. (1998).
S. Sheppard, J. Bembridge, M. Holmstrup, L. Posthuma (eds.).
S. Sheppard, J. Bembridge, M. Holmstrup, L. Posthuma (ur.).
Soct
Sokt
Probit Analysis, 3rd ed. Cambridge University Press, London/New York.
Probit Analysis, 3. izdaja, Cambridge University Press, London/New York.
For benthic organisms, similar correlations have been found e.g. (30) (44). Likewise for terrestrial oligochaetes this correlation has been demonstrated e.g. (5) (6) (7) (14).
Podobna medsebojna odvisno je bila ugotovljena pri bentoških organizmih, npr. (30) (44), dokazana pa je tudi za kopenske maloščetince, npr. (5) (6) (7) (14).
< 1 μg/l
< 1 μg /l
Aeration is provided through a glass Pasteur pipette fixed 2-3 cm above the sediment layer (i.e. one or few bubbles/sec). When testing volatile chemicals, consideration may be given not to aerate the sediment-water system.
Kadar se preskušajo hlapne kemikalije, je mogoče razmisliti o tem, da se sistem vode in usedline ne bi prezračeval.
Environmental Protection Agency Washington, DC.
Environmental Protection Agency, Washington, DC.
Foran JA (Ed.).
Foran, J. A. (ur.).
Compudrug, Ltd, Budapest.
Compudrug, Ltd, Budimpešta.
Edition) Informa Healthcare, New York.
izdaja) Informa Healthcare, New York.
Harmonization of Animal Clinical Pathology Testing in Toxicity and Safety Studies.
Harmonisation of Animal Clinical Pathology Testing in Toxicity and Safety Studies.
Eds. Jacobsen BN, Muntau H, Angeletti G.
Ur. Jacobsen, B. N., Muntau, H., Angeletti, G.
Hales, SG. Feitjel, T. King, H. Fox, K. and Verstraete, W.
Delavnica v Port Sunlightu, Združeno kraljestvo.
Int.J. Air Wat.
Int. J. Air Wat.
Volume 11.05.
Zvezek 11.05.
Elendt, B.P. & W.-R.
Elendt, B. P. in Bias, W.-R.
& Eisentraeger, A. (eds.).
& Eisentraeger, A. (ur.).
Lewis Publishers Boca Raton, FL, USA.
Lewis Publishers Boca Raton, FL, ZDA.
Guidance Document 106 on Histologic evaluation of Endocrine and Reproductive Tests in Rodents ENV/JM/Mono(2009)11.
Guidance Document 106 on Histologic evaluation of Endocrine and Reproductive Tests in Rodents. ENV/JM/Mono(2009)11.
Nyholm, N. Berg, UT. Ingerslev, F. Min. of Env. and Energy, Copenhagen.
Nyholm, N., Berg, U. T., Ingerslev, F. Min. of Env. and Energy, Köbenhavn.
total number of midges emerged at the end of experiment (= i ) xi
dayi
Pinsuwan S, Li A and Yalkowsky S.H. (1995).
Pinsuwan, S., Li, A., in Yalkowsky, S. H. (1995).
Octanol/water partition coefficient.
Octanol/water partition coefficient. V: Lyman, W. J., Reehl, W.
When the solubility is low, a long time may be required to dissolve a test substance and at least 24 hours should be allowed. If, after 24 hours, the test substance is still not dissolved, more time (up to 96 hours) should be allowed or further dilution should be attempted to ascertain whether the column elution method or flask method should be used.
Kadar je topnost nizka, je lahko za raztopitev preskusne snovi potrebnega veliko časa, počakati pa je treba najmanj 24 ur. Če preskusna snov po 24 urah še vedno ni raztopljena, je treba počakati dlje (do 96 ur) ali jo dodatno razredčiti, da se ugotovi, ali je treba uporabiti metodo z izpiranjem kolone ali metodo z bučko.
For a compound with log POW of 8,23 (decachlorobiphenyl) 144 hours were sufficient for equilibration. Equilibrium is assessed by means of repeated sampling of a single vessel.
Za spojino z log POW 8,23 (dekaklorobifenil) je bilo za uravnoteženje potrebnih 144 ur. Ravnotežje se oceni z večkratnim vzorčenjem v isti posodi.
Nose-only exposures may be any duration up to 6 hours in rats. If mice are exposed nose-only, exposures generally should not exceed 4 hours.
Izpostavljenost nosu lahko pri podganah traja do 6 ur. Če se uporabljajo miši, izpostavljenost nosu navadno ne sme biti daljša od 4 ur. Če so potrebne dolgoročnejše študije, je treba to utemeljiti (glej GD 39 (2)).
Justification should be provided if longer duration studies are needed [see GD 39 (2)]. Animals exposed to aerosols in whole-body chambers should be housed individually to prevent ingestion of test chemical due to grooming of cage mates.
Živali, ki so izpostavljene aerosolom v komorah za izpostavljanje celega telesa, morajo biti nastanjene posamično, da se prepreči zaužitje preskusne kemikalije ob medsebojnem čiščenju primerkov v kletki.
Feed should be withheld during the exposure period unless exposure exceeds 6 hours. Water may be provided throughout a whole-body exposure.
V obdobju izpostavljenosti je treba živalim odrekati hrano, razen če je to obdobje daljše od 6 ur. Med izpostavljenostjo celega telesa lahko živali ves čas uživajo vodo.
C.10-A: Activated Sludge Units
C.10-A: Enote z aktivnim blatom
Boston, USA.
Boston, ZDA.
Spiked sediments of the chosen concentration are usually prepared by addition of a solution of the test substance directly to the sediment. A stock solution of the test substance dissolved in deionised water is mixed with the formulated sediment by rolling mill, feed mixer or hand mixing.
Usedline s primešano preskusno snovjo izbrane koncentracije se običajno pripravijo z dodatkom raztopine preskusne snovi neposredno v usedlino. osnovna raztopina preskusne snovi, raztopljene v deionizirani vodi, se zmeša s formulirano usedlino z valjčnim mlinom, mešalnikom za krmo ali ročno.
Slightly more food may be necessary for older larvae: 0,5-1 mg per larvae per day should be sufficient for the rest of the test. The food ration should be reduced in all treatments and control if fungal growth is seen or if mortality is observed in controls. If fungal development cannot be stopped the test is to be repeated. When testing strongly adsorbing substances (e.g. with log Kow > 5), or substances covalently binding to sediment, the amount of food necessary to ensure survival and natural growth of the organisms may be added to the formulated sediment before the stabilisation period. For this, plant material must be used instead of fish food, e.g. addition of 0,5 % (dry weight) finely ground leaves of e.g. stinging nettle (Urtica dioica), mulberry (Morus alba), white clover (Trifolium repens), spinach (Spinacia oleracea) or of other plant material (Cerophyl or alpha-cellulose) may be used. Incubation conditions
Zagotovi se rahlo prezračevanje vode nad usedlino v preskusnih posodah, po možnosti 24 ur po vnosu ličink, in se izvaja ves čas preskusa (paziti je treba, da koncentracija raztopljenega kisika ne pade pod 60 % ASV).
The development rate is preferred for the evaluation of these sediment toxicity studies as its variance is lower, and it is more homogeneous and closer to normal distribution as compared to development time. Hence, powerful parametric test procedures may be used with development rate rather than with development time.
Za oceno teh raziskav strupenosti v usedlini je primernejša hitrost razvoja, saj je njena varianca manjša, poleg tega je bolj homogena in bližje normalni porazdelitvi v primerjavi s časom razvoja.
Once adults are present within the breeding cage, all larval rearing vessels should be checked three times weekly for deposition of the gelatinous egg masses. If present, the egg masses should be carefully removed.
Ko so v kletki za razmnoževanje odrasli osebki, je treba vse posode za gojenje ličink trikrat tedensko preveriti zaradi morebitnih odloženih želatinastih jajčnih legel, ki jih je treba previdno odstraniti.
The composition of the formulated sediment should be as follows: Constituent
Sestava formulirane usedline mora biti naslednja:
dry weight Peat
Delež suhe
Then the peat suspension is mixed with the other constituents (sand and kaolin clay) and deionised water to obtain a homogeneous sediment with a water content in a range of 30-50 per cent of dry weight of the sediment. The pH of the final mixture is measured once again and is adjusted to 6,5 to 7,5 with CaCO3 if necessary.
Šotna suspenzija se nato zmeša z drugimi sestavinami (peskom in kaolinsko glino) in deionizirano vodo, da nastane homogena usedlina z vsebnostjo vode v razponu 30 do 50 % suhe teže usedline. pH končne mešanice se znova izmeri in po potrebi uravna na 6,5 do 7,5 s CaCO3.
x mean development rate per vessel i index of inspection interval
x hitrost razvoja trzač, preobraženih v intervalu i.
Calow P. (ed.).
Calow P. (ur.).
Council Implementing Regulation (EU) No 261/2014
Izvedbena uredba Sveta (EU) št. 261/2014
Having regard to Council Regulation (EU) No 753/2011 of 1 August 2011 concerning restrictive measures directed against certain individuals, groups, undertakings and entities in view of the situation in Afghanistan [1], and in particular Article 11(4) thereof,
ob upoštevanju Uredbe Sveta (EU) št. 753/2011 z dne 1. avgusta 2011 o omejevalnih ukrepih proti nekaterim posameznikom, skupinam, podjetjem in subjektom zaradi razmer v Afganistanu [1] in zlasti člena 11(4) Uredbe,
I. The entries in the list set out in Annex I to Regulation (EU) No 753/2011 for the persons below shall be replaced by the entries as set out below.
I. Vnosi na seznamu iz Priloge I k Uredbi (EU) št. 753/2011 za osebe v nadaljevanju se nadomestijo z naslednjimi vnosi:
Fazl Rabi (alias(a) Fazl Rabbi, (b) Fazal Rabi, (c) Faisal Rabbi)
Fazl Rabi (alias (a) Fazl Rabbi, (b) Fazal Rabi, (c) Faisal Rabbi)
Belongs to Kharoti tribe.
pripada plemenu Kharoti;
, ii) Haji Mohammed Plaza, Tol Aram Road, near Jamaluddin Afghani Road, Quetta, Pakistan
Haji Mohammed Plaza, Tol Aram Road, blizu Jamaluddin Afghani Road, Quetta, Pakistan
, iii) Kandahari Bazaar, Quetta, Pakistan
Kandahari Bazaar, Quetta, Pakistan ;
The entry in the list set out in Annex I to Regulation (EU) No 753/2011 for the person below shall be deleted.
Vnos na seznamu iz Priloge I k Uredbi (EU) št. 753/2011 za osebo v nadaljevanju se črta.
Reportedly deceased September 2013.
domnevno je umrl septembra 2013.
Council Regulation (EU) No 262/2014
Uredba Sveta (EU) št. 262/2014
Having regard to Council Common Position 2008/109/CFSP of 12 February 2008 concerning restrictive measures imposed against Liberia [1],
ob upoštevanju Skupnega stališča Sveta 2008/109/SZVP z dne 12. februarja 2008 o omejevalnih ukrepih proti Liberiji [1],
Council Regulation (EC) No 234/2004 [2] imposes a general ban on the provision of technical advice, assistance, training, financing and financial assistance related to military activities to any person, entity or body in Liberia.
Z Uredbo Sveta (ES) št. 234/2004 [2] je bila uvedena splošna prepoved zagotavljanja tehničnih nasvetov, pomoči, usposabljanja, financiranja in finančne pomoči v zvezi z vojaškimi dejavnostmi kateri koli osebi, subjektu ali organu v Liberiji.
On 10 December 2013, the United Nations Security Council adopted Resolution 2128 (2013) reaffirming the arms embargo imposed by paragraph 2 of Resolution 1521 (2003) and modified by paragraphs 1 and 2 of Resolution 1683 (2006), by paragraph 1(b) of Resolution 1731 (2006), by paragraphs 3, 4, 5 and 6 of Resolution 1903 (2009), and by paragraph 3 of Resolution 1961 (2010), and modifying the associated notification requirements.
Varnostni svet Združenih narodov je 10. decembra 2013 sprejel Resolucijo 2128 (2013), ki ponovno potrjuje embargo na orožje, ki je bil uveden v skladu z odstavkom 2 Resolucije 1521 (2003) in spremenjen v skladu z odstavkoma 1 in 2 Resolucije 1683 (2006), odstavkom 1(b) Resolucije 1731 (2006), odstavki 3, 4, 5 in 6 Resolucije 1903 (2009) ter odstavkom 3 Resolucije 1961 (2010), ter spreminja s tem povezane obveznosti priglasitve.
On 14 March 2014, the Council adopted Decision 2014/141/CFSP [3], which amends Common Position 2008/109/CFSP to that effect.
Svet je 14. marca 2014 sprejel Sklep 2014/141/SZVP [3], ki ustrezno spreminja Skupno stališče 2008/109/SZVP.
Some of those measures fall within the scope of the Treaty on the Functioning of the European Union and regulatory action at Union level is therefore necessary in order to implement them, in particular with a view to ensuring their uniform application by economic operators in all Member States.
Nekateri od navedenih ukrepov spadajo na področje uporabe Pogodbe o delovanju Evropske unije, zato je predvsem zaradi zagotovitve, da jih bodo gospodarski subjekti v vseh državah članicah enotno uporabljali, za njihovo izvajanje potrebno regulativno ukrepanje na ravni Unije.
Regulation (EC) No 234/2004 is amended as follows:
Uredba (ES) št. 234/2004 se spremeni:
in Article 3(1), point (b) is replaced by the following:
v členu 3(1) se točka (b) nadomesti z naslednjim:
technical assistance related to non-lethal equipment which is intended solely for humanitarian or protective use.’;
tehnične pomoči v zvezi z opremo, ki ni smrtonosna in je namenjena zgolj humanitarni ali zaščitni uporabi.“;