natgillin/translations-raw huggingface dataset:
bromerede diphenylethere
Brominated diphenylethers
chloralkaner, C10-13
Chloroalkanes, C10-13
chlorpyrifos (chlorpyrifosethyl)
Chlorpyrifos (Chlorpyrifos-ethyl)
di(2-ethylhexyl)phthalat (DEHP)
Di(2-ethylhexyl)phthalate (DEHP)
hexachlorcyclohexan
Hexachlorocyclohexane
nonylphenoler
Nonylphenols
octylphenoler [6]
Octylphenols [6]
polyaromatiske kulbrinter (PAH) [7]
Polyaromatic hydrocarbons (PAH) [7]
tributyltinforbindelser
Tributyltin compounds
trichlorbenzener
Trichlorobenzenes
dioxiner og dioxinlignende forbindelser
Dioxins and dioxin-like compounds
hexabromcyclododecaner (HBCDD)
Hexabromocyclododecanes (HBCDD)
heptachlor og heptachlorepoxid
Heptachlor and heptachlor epoxide
EU-nummer: Den Europæiske Fortegnelse over Markedsførte Kemiske Stoffer (Einecs) eller Den Europæiske Liste over Anmeldte Kemiske Stoffer (Elincs).
EU-number: European Inventory of Existing Commercial Substances (EINECS) or European List of Notified Chemical Substances (ELINCS).
Hvor der er udvalgt en gruppe af stoffer, er typiske enkeltstoffer udpeget til fastsættelse af miljøkvalitetskrav, medmindre andet udtrykkelig er angivet.
Where groups of substances have been selected, unless explicitly noted, typical individual representatives are defined in the context of the setting of environmental quality standards.
Kun tetra-, penta-, hexa- og heptabrombiphenylether (CAS -nummer henholdsvis 40088-47-9, 32534-81-9, 36483-60-0, 68928-80-3).
Only Tetra, Penta, Hexa and Heptabromodiphenylether (CAS -numbers 40088-47-9, 32534-81-9, 36483-60-0, 68928-80-3, respectively).
Nonylphenol (CAS 25154-52-3, EU 246-672-0), herunder isomererne 4-nonylphenol (CAS 104-40-5, EU 203-199-4) og 4-nonylphenol (forgrenet) (CAS 84852-15-3, EU 284-325-5).
Nonylphenol (CAS 25154-52-3, EU 246-672-0) including isomers 4-nonylphenol (CAS 104-40-5, EU 203-199-4) and 4-nonylphenol (branched) (CAS 84852-15-3, EU 284-325-5).
Octylphenol (CAS 1806-26-4, EU 217-302-5) herunder isomeren 4-(1,1,3,3-tetramethylbutyl)-phenol (CAS 140-66-9, EU 205-426-2).
Octylphenol (CAS 1806-26-4, EU 217-302-5) including isomer 4-(1,1',3,3'-tetramethylbutyl)-phenol (CAS 140-66-9, EU 205-426-2).
Herunder benzo(a)pyren (CAS 50-32-8, EU 200-028-5), benzo(b)fluoranthen (CAS 205-99-2, EU 205-911-9), benzo(g,h,i)perylen (CAS 191-24-2, EU 205-883-8), benzo(k)fluoranthen (CAS 207-08-9, EU 205-916-6) og indeno(1,2,3-cd)pyren (CAS 193-39-5, EU 205-893-2), men ikke anthracen, fluoranthen og naphthalen, som er opført særskilt.
Including benzo(a)pyrene (CAS 50-32-8, EU 200-028-5), benzo(b)fluoranthene (CAS 205-99-2, EU 205-911-9), benzo(g,h,i)perylene (CAS 191-24-2, EU 205-883-8), benzo(k)fluoranthene (CAS 207-08-9, EU 205-916-6), indeno(1,2,3-cd)pyrene (CAS 193-39-5, EU 205-893-2) and excluding anthracene, fluoranthene and naphthalene, which are listed separately.
Herunder tributyltin-kation (CAS 36643-28-4).
Including tributyltin-cation (CAS 36643-28-4).
Dette gælder for følgende forbindelser:7 polychlorerede dibenzo-p-dioxiner (PCDD): 2,3,7,8-T4CDD (CAS 1746-01-6), 1,2,3,7,8-P5CDD (CAS 40321-76-4), 1,2,3,4,7,8-H6CDD (CAS 39227-28-6), 1,2,3,6,7,8-H6CDD (CAS 57653-85-7), 1,2,3,7,8,9-H6CDD (CAS 19408-74-3), 1,2,3,4,6,7,8-H7CDD (CAS 35822-46-9) og 1,2,3,4,6,7,8,9-O8CDD (CAS 3268-87-9)10 polychlorerede dibenzofuraner (PCDF): 2,3,7,8-T4CDF (CAS 51207-31-9), 1,2,3,7,8-P5CDF (CAS 57117-41-6), 2,3,4,7,8-P5CDF (CAS 57117-31-4), 1,2,3,4,7,8-H6CDF (CAS 70648-26-9), 1,2,3,6,7,8-H6CDF (CAS 57117-44-9), 1,2,3,7,8,9-H6CDF (CAS 72918-21-9), 2,3,4,6,7,8-H6CDF (CAS 60851-34-5), 1,2,3,4,6,7,8-H7CDF (CAS 67562-39-4), 1,2,3,4,7,8,9-H7CDF (CAS 55673-89-7), 1,2,3,4,6,7,8,9-O8CDF (CAS 39001-02-0)12 dioxinlignende polychlorerede biphenyler (DL-PCB): 3,3,4,4-T4CB (PCB 77, CAS 32598-13-3), 3,3,4,5-T4CB (PCB 81, CAS 70362-50-4), 2,3,3,4,4-P5CB (PCB 105, CAS 32598-14-4), 2,3,4,4,5-P5CB (PCB 114, CAS 74472-37-0), 2,3,4,4,5-P5CB (PCB 118, CAS 31508-00-6), 2,3,4,4,5-P5CB (PCB 123, CAS 65510-44-3), 3,3,4,4,5-P5CB (PCB 126, CAS 57465-28-8), 2,3,3,4,4,5-H6CB (PCB 156, CAS 38380-08-4), 2,3,3,4,4,5-H6CB (PCB 157, CAS 69782-90-7), 2,3,4,4,5,5-H6CB (PCB 167, CAS 52663-72-6), 3,3,4,4,5,5-H6CB (PCB 169, CAS 32774-16-6) og 2,3,3,4,4,5,5-H7CB (PCB 189, CAS 39635-31-9).
This refers to the following compounds:7 polychlorinated dibenzo-p-dioxins (PCDDs): 2,3,7,8-T4CDD (CAS 1746-01-6), 1,2,3,7,8-P5CDD (CAS 40321-76-4), 1,2,3,4,7,8-H6CDD (CAS 39227-28-6), 1,2,3,6,7,8-H6CDD (CAS 57653-85-7), 1,2,3,7,8,9-H6CDD (CAS 19408-74-3), 1,2,3,4,6,7,8-H7CDD (CAS 35822-46-9), 1,2,3,4,6,7,8,9-O8CDD (CAS 3268-87-9)10 polychlorinated dibenzofurans (PCDFs): 2,3,7,8-T4CDF (CAS 51207-31-9), 1,2,3,7,8-P5CDF (CAS 57117-41-6), 2,3,4,7,8-P5CDF (CAS 57117-31-4), 1,2,3,4,7,8-H6CDF (CAS 70648-26-9), 1,2,3,6,7,8-H6CDF (CAS 57117-44-9), 1,2,3,7,8,9-H6CDF (CAS 72918-21-9), 2,3,4,6,7,8-H6CDF (CAS 60851-34-5), 1,2,3,4,6,7,8-H7CDF (CAS 67562-39-4), 1,2,3,4,7,8,9-H7CDF (CAS 55673-89-7), 1,2,3,4,6,7,8,9-O8CDF (CAS 39001-02-0)12 dioxin-like polychlorinated biphenyls (PCB-DL): 3,3',4,4'-T4CB (PCB 77, CAS 32598-13-3), 3,3',4',5-T4CB (PCB 81, CAS 70362-50-4), 2,3,3',4,4'-P5CB (PCB 105, CAS 32598-14-4), 2,3,4,4',5-P5CB (PCB 114, CAS 74472-37-0), 2,3',4,4',5-P5CB (PCB 118, CAS 31508-00-6), 2,3',4,4',5'-P5CB (PCB 123, CAS 65510-44-3), 3,3',4,4',5-P5CB (PCB 126, CAS 57465-28-8), 2,3,3',4,4',5-H6CB (PCB 156, CAS 38380-08-4), 2,3,3',4,4',5'-H6CB (PCB 157, CAS 69782-90-7), 2,3',4,4',5,5'-H6CB (PCB 167, CAS 52663-72-6), 3,3',4,4',5,5'-H6CB (PCB 169, CAS 32774-16-6), 2,3,3',4,4',5,5'-H7CB (PCB 189, CAS 39635-31-9).
CAS 52315-07-8 gælder for en isomerblanding af cypermethrin, alpha-cypermethrin (CAS 67375-30-8), beta-cypermethrin (CAS 65731-84-2), theta-cypermethrin (CAS 71697-59-1) og zeta-cypermethrin (52315-07-8).
CAS 52315-07-8 refers to an isomer mixture of cypermethrin, alpha-cypermethrin (CAS 67375-30-8), beta-cypermethrin (CAS 65731-84-2), theta-cypermethrin (CAS 71697-59-1) and zeta-cypermethrin (52315-07-8).
Dette gælder for 1,3,5,7,9,11-hexabromcyclododecan (CAS 25637-99-4), 1,2,5,6,9,10- hexabromcyclododecan (CAS 3194-55-6), α-hexabromcyclododecan (CAS 134237-50-6), β-hexabromcyclododecan (CAS 134237-51-7) og γ-hexabromcyclododecan (CAS 134237-52-8).«
This refers to 1,3,5,7,9,11-Hexabromocyclododecane (CAS 25637-99-4), 1,2,5,6,9,10- Hexabromocyclododecane (CAS 3194-55-6), α-Hexabromocyclododecane (CAS 134237-50-6), β-Hexabromocyclododecane (CAS 134237-51-7) and γ- Hexabromocyclododecane (CAS 134237-52-8).’.
AA årsgennemsnit
AA annual average.
Enhed [μg/l] for kolonne 4 til 7
Unit [μg/l] for columns (4) to (7)
[μg/kg våd vægt] for kolonne 8
[μg/kg wet weight] for column (8)
MAC-EQS [4]Andet overfladevand
MAC-EQS [4]Other surface waters
bromerede diphenylethere [5]
Brominated diphenylethers [5]
C10-13-chloralkaner [8]
C10-13 Chloroalkanes [8]
cyclodien-pesticider:
Cyclodiene pesticides:
DDT i alt [7] [9]
DDT total [7], [9]
1,2-dichloroethan
1,2-Dichloroethane
di(2-ethylhexyl)phthalat (DEHP)
Di(2-ethylhexyl)-phthalate (DEHP)
hexachlorcyclohexan
Hexachloro-cyclohexane
octylphenoler
Octylphenols
pentachlorphenol
Pentachloro-phenol
polyaromatiske kulbrinter (PAH) [11]
Polyaromatic hydrocarbons (PAH) [11]
benzo(b)fluor-anthen
Benzo(b)fluor-anthene
se fodnote 11
see footnote 11
benzo(k)fluor-anthen
Benzo(k)fluor-anthene
benzo(g,h,i) perylen
Benzo(g,h,i)-perylene
indeno(1,2,3-cd)pyren
Indeno(1,2,3-cd)-pyrene
tetrachlorethylen [7]
Tetrachloro-ethylene [7]
trichlor-ethylen [7]
Trichloro-ethylene [7]
tributyltinforbindelser (tributyltinkation)
Tributyltin compounds (Tributyltin-cation)
trichlorbenzener
Trichloro-benzenes
anvendes ikke [10]
not applicable [10]
Se fodnote 10 i bilag X til direktiv 2000/60/EF
See footnote 10 in Annex X to Directive 2000/60/EC
Summen af PCDD + PCDF + PCB-DL
Sum of PCDD+PCDF+PCB-DL
hexabromcyclododecan (HBCDD)
Hexabromocyclododecane (HBCDD)
Se fodnote 12 i bilag X til direktiv 2000/60/EF.
See footnote 12 in Annex X to Directive 2000/60/EC
Denne parameter er EQS udtrykt som årsgennemsnit (AA-EQS).
This parameter is the EQS expressed as an annual average value (AA-EQS).
Denne parameter er EQS udtrykt som højeste tilladte koncentration (MAC-EQS).
This parameter is the EQS expressed as a maximum allowable concentration (MAC-EQS).
Hvis der under MAC-EQS er anført »anvendes ikke«, betragtes AA-EQS-værdierne som beskyttelse mod kortvarig høj forurening i kontinuerlige udledninger, da de er væsentligt lavere end de værdier, der er afledt af den akutte toksicitet.
Where the MAC-EQS are marked as “not applicable”, the AA-EQS values are considered protective against short-term pollution peaks in continuous discharges since they are significantly lower than the values derived on the basis of acute toxicity.
For den gruppe prioriterede stoffer, som bromerede diphenylethere (nr. 5) omfatter, gælder EQS for summen af koncentrationer af congenerne nummer 28, 47, 99, 100, 153 og 154.
For the group of priority substances covered by brominated diphenylethers (No 5), the EQS refers to the sum of the concentrations of congener numbers 28, 47, 99, 100, 153 and 154.
For cadmium og cadmiumforbindelser (nr. 6) afhænger EQS-værdierne af vandets hårdhedsgrad, som opdeles i fem klasser (klasse 1: < 40 mg CaCO3/l, klasse 2: 40 til < 50 mg CaCO3/l, klasse 3: 50 til < 100 mg CaCO3/l, klasse 4: 100 til < 200 mg CaCO3/l og klasse 5: ≥ 200 mg CaCO3/l).
For Cadmium and its compounds (No 6) the EQS values vary depending on the hardness of the water as specified in five class categories (Class 1: < 40 mg CaCO3/l, Class 2: 40 to < 50 mg CaCO3/l, Class 3: 50 to < 100 mg CaCO3/l, Class 4: 100 to < 200 mg CaCO3/l and Class 5: ≥ 200 mg CaCO3/l).
Dette stof er ikke et prioriteret stof, men et af de andre forurenende stoffer, for hvilke miljøkvalitetskravene er identiske med de EQS-værdier, der er fastsat i den lovgivning, der var gældende indtil den 13. januar 2009.
This substance is not a priority substance but one of the other pollutants for which the EQS are identical to those laid down in the legislation that applied prior to 13 January 2009.
Der er ingen indikatorparameter for denne gruppe af stoffer.
No indicative parameter is provided for this group of substances.
Indikatorparametrene skal defineres på grundlag af analysemetoden.
The indicative parameter(s) must be defined through the analytical method.
DDT i alt udgøres af summen af isomererne 1,1,1-trichlor-2,2-bis(p-chlorphenyl)ethan (CAS-nummer 50-29-3; EU-nummer 200-024-3); 1,1,1-trichlor-2-(o-chlorphenyl)-2-(p-chlorphenyl)ethan (CAS-nummer 789-02-6; EU-nummer 212-332-5); 1,1-dichlor-2,2-bis(p-chlorphenyl)ethylen (CAS-nummer 72-55-9; EU-nummer 200-784-6) og 1,1-dichlor-2,2-bis(p-chlorphenyl)ethan (CAS-nummer 72-54-8; EU-nummer 200-783-0).
DDT total comprises the sum of the isomers 1,1,1-trichloro-2,2 bis (p-chlorophenyl) ethane (CAS number 50-29-3; EU number 200-024-3); 1,1,1-trichloro-2 (o-chlorophenyl)-2-(p-chlorophenyl) ethane (CAS number 789-02-6; EU Number 212-332-5); 1,1-dichloro-2,2 bis (p-chlorophenyl) ethylene (CAS number 72-55-9; EU Number 200-784-6); and 1,1-dichloro-2,2 bis (p-chlorophenyl) ethane (CAS number 72-54-8; EU Number 200-783-0).
Der foreligger ikke tilstrækkelige oplysninger til, at der kan fastsættes en MAC-EQS for disse stoffer.
There is insufficient information available to set a MAC-EQS for these substances.
For denne gruppe prioriterede stoffer, polyaromatiske kulbrinter (PAH) (nr. 28), gælder EQS for biota og tilsvarende AA-EQS i vand for koncentrationen af benzo(a)pyren, hvis toksicitet de er baseret på.
For the group of priority substances of polyaromatic hydrocarbons (PAH) (No 28), the biota EQS and corresponding AA-EQS in water refer to the concentration of benzo(a)pyrene, on the toxicity of which they are based.
Benzo(a)pyren kan betragtes som markør for de øvrige PAH'er, og derfor behøver kun benzo(a)pyren at blive overvåget med henblik på sammenligning med EQS for biota eller de tilsvarende AA-EQS i vand.
Benzo(a)pyrene can be considered as a marker for the other PAHs, hence only benzo(a)pyrene needs to be monitored for comparison with the biota EQS or the corresponding AA-EQS in water.
Kvalitetskrav for biota gælder for fisk, med mindre andet er anført.
Unless otherwise indicated, the biota EQS relate to fish.
Et alternativt biotataxon eller en anden matrice kan overvåges i stedet, forudsat at de EQS, der anvendes, giver et tilsvarende niveau af beskyttelse.
An alternative biota taxon, or another matrix, may be monitored instead, as long as the EQS applied provides an equivalent level of protection.
Disse EQS gælder for biotilgængelige koncentrationer af stofferne.
These EQS refer to bioavailable concentrations of the substances.
PCDD: polychlorerede dibenzo-p-dioxiner; PCDF: polychlorerede dibenzofuraner; PCB-DL: dioxinlignende polychlorerede biphenyler; TEQ: toksicitetsækvivalenter ifølge Verdenssundhedsorganisationens toksicitetsækvivalensfaktorer fra 2005.«
PCDD: polychlorinated dibenzo-p-dioxins; PCDF: polychlorinated dibenzofurans; PCB-DL: dioxin-like polychlorinated biphenyls; TEQ: toxic equivalents according to the World Health Organisation 2005 Toxic Equivalence Factors.’
Der bør tages højde for de reviderede EQS for eksisterende prioriterede stoffer for første gang i vandområdeplaner, der omfatter perioden 2015-2021.
The revised EQS for existing priority substances should be taken into account for the first time in river basin management plans covering the period 2015 to 2021.
Der bør tages højde for de nyligt identificerede prioriterede stoffer og EQS hertil i fastlæggelsen af supplerende overvågningsprogrammer, og i de foreløbige indsatsprogrammer, der forelægges inden udgangen af 2018.
The newly identified priority substances and their EQS should be taken into account in the establishment of supplementary monitoring programmes and in preliminary programmes of measures to be submitted by the end of 2018.
Med det formål at opnå god kemisk tilstand for overfladevand bør de reviderede EQS for eksisterende prioriterede stoffer opfyldes inden udgangen af 2021 og for nyligt identificerede prioriterede stoffer inden udgangen af 2027, jf. dog artikel 4, stk. 4-9, i direktiv 2000/60/EF, som bl.a. omfatter bestemmelser om forlængelse af fristen for opnåelse af god kemisk tilstand for overfladevand eller om at tilstræbe mindre strenge miljømål for specifikke vandområder på grund af uforholdsmæssige omkostninger og/eller samfundsøkonomiske behov, forudsat at der ikke sker yderligere forværring af berørte vandområders tilstand.
With the aim of achieving good surface water chemical status, the revised EQS for existing priority substances should be met by the end of 2021 and the EQS for newly identified priority substances by the end of 2027, without prejudice to Article 4(4) to (9) of Directive 2000/60/EC, which includes inter alia provisions for extending the deadline for achieving good surface water chemical status or achieving less stringent environmental objectives for specific bodies of water on the grounds of disproportionate cost and/or socio-economic need, provided that no further deterioration occurs in the status of the affected bodies of water.
Kommissionen tillægges beføjelser til at vedtage de delegerede retsakter, der er omhandlet i artikel 3, stk. 8, for en periode på seks år fra den 13. september 2013.
The power to adopt delegated acts referred to in Article 3(8) shall be conferred on the Commission for a period of six years from 13 September 2013.
Kommissionen udarbejder en rapport vedrørende delegationen af beføjelser senest ni måneder inden udløbet af seksårsperioden.
The Commission shall draw up a report in respect of the delegation of power not later than nine months before the end of the six-year period.
Medlemsstaterne sætter de nødvendige love og administrative bestemmelser i kraft for at efterkomme dette direktiv senest den 14. september 2015.
Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive by 14 September 2015.
For stof nr. 15 (fluoranthen) og 28 (PAH'er) gælder EQS for biota for krebsdyr og bløddyr.
For substances numbered 15 (Fluoranthene) and 28 (PAHs), the biota EQS refers to crustaceans and molluscs.
Overvågning af fluoranthen og PAH'er i fisk er ikke hensigtsmæssig med henblik på vurdering af den kemiske tilstand.
For the purpose of assessing chemical status, monitoring of Fluoranthene and PAHs in fish is not appropriate.
For stof nr. 37 (dioxiner og dioxinlignende forbindelser) gælder EQS for biota for fisk, krebsdyr og bløddyr, i overensstemmelse med afsnit 5.3 i bilaget til forordning (EU) nr. 1259/2011 af 2. december 2011 om ændring af Kommissionens forordning (EF) nr. 1881/2006 for så vidt angår grænseværdier for dioxiner, dioxinlignende PCB'er og ikke-dioxinlignende PCB'er i fødevarer (EUT L 320 af 3.12.2011, s. 18).
For substance number 37 (Dioxins and dioxin-like compounds), the biota EQS relates to fish, crustaceans and molluscs, in line with section 5.3 of the Annex to Commission Regulation (EU) No 1259/2011 of 2 December 2011 amending Regulation (EC) No 1881/2006 as regards maximum levels for dioxins, dioxin-like PCBs and non-dioxin-like PCBs in foodstuffs (OJ L 320, 3.12.2011, p. 18).
Europa-Parlamentets og Rådets direktiv 2013/40/EU
Directive 2013/40/EU of the European Parliament and of the Council
om angreb på informationssystemer og om erstatning af Rådets rammeafgørelse 2005/222/RIA
on attacks against information systems and replacing Council Framework Decision 2005/222/JHA
under henvisning til traktaten om Den Europæiske Unions funktionsmåde, særlig artikel 83, stk. 1,
Having regard to the Treaty on the Functioning of the European Union, and in particular Article 83(1) thereof,
Dette direktivs formål er at tilnærme medlemsstaternes strafferet til hinanden med hensyn til angreb på informationssystemer ved at fastsætte minimumsregler for definitionen af strafbare handlinger og de relevante sanktioner og at forbedre samarbejdet mellem de kompetente myndigheder, herunder politiet og andre specialiserede retshåndhævende myndigheder i medlemsstaterne samt kompetente specialiserede EU-agenturer og -organer, som f.eks. Eurojust, Europol og dets europæiske center for bekæmpelse af it-kriminalitet og Det Europæiske Agentur for Net- og Informationssikkerhed (ENISA).
The objectives of this Directive are to approximate the criminal law of the Member States in the area of attacks against information systems by establishing minimum rules concerning the definition of criminal offences and the relevant sanctions and to improve cooperation between competent authorities, including the police and other specialised law enforcement services of the Member States, as well as the competent specialised Union agencies and bodies, such as Eurojust, Europol and its European Cyber Crime Centre, and the European Network and Information Security Agency (ENISA).
Informationssystemer er et centralt element i det politiske, sociale og økonomiske samspil i Unionen.
Information systems are a key element of political, social and economic interaction in the Union.
Samfundet er dybt afhængigt af sådanne systemer og bliver det i stadig større udstrækning.
Society is highly and increasingly dependent on such systems.
Disse systemers funktionsdygtighed og sikkerhed i Unionen er en forudsætning for udviklingen af det indre marked og af en konkurrencedygtig og innovativ økonomi.
The smooth operation and security of those systems in the Union is vital for the development of the internal market and of a competitive and innovative economy.
Der bør sikres et passende beskyttelsesniveau for informationssystemer som led i en effektiv overordnet ramme for forebyggende foranstaltninger, der ledsager de strafferetlige foranstaltninger over for it-kriminalitet.
Ensuring an appropriate level of protection of information systems should form part of an effective comprehensive framework of prevention measures accompanying criminal law responses to cybercrime.
Angreb på informationssystemer, og især angreb som led i organiseret kriminalitet, er en voksende trussel såvel i Unionen som globalt, og der er i stigende grad bekymring for mulige terrorangreb eller politisk motiverede angreb på informationssystemer, der indgår i medlemsstaternes og Unionens kritiske infrastruktur.
Attacks against information systems, and, in particular, attacks linked to organised crime, are a growing menace in the Union and globally, and there is increasing concern about the potential for terrorist or politically motivated attacks against information systems which form part of the critical infrastructure of Member States and of the Union.
Dette udgør en trussel mod etableringen af et sikrere informationssamfund og et område med frihed, sikkerhed og retfærdighed og kræver derfor en reaktion på EU-niveau samt bedre samarbejde og koordination på internationalt niveau.
This constitutes a threat to the achievement of a safer information society and of an area of freedom, security, and justice, and therefore requires a response at Union level and improved cooperation and coordination at international level.
Der findes adskillige kritiske infrastrukturer i Unionen, hvis afbrydelse eller ødelæggelse ville få betydelige konsekvenser på tværs af grænserne.
There are a number of critical infrastructures in the Union, the disruption or destruction of which would have a significant cross-border impact.
Det er blevet klart ud fra behovet for at øge Unionens evne til at beskytte kritisk infrastruktur, at foranstaltningerne mod it-angreb bør suppleres af strenge strafferetlige sanktioner, der afspejler disse angrebs alvorlige karakter.
It has become apparent from the need to increase the critical infrastructure protection capability in the Union that the measures against cyber attacks should be complemented by stringent criminal penalties reflecting the gravity of such attacks.
Kritisk infrastruktur kan forstås som aktiver, systemer eller dele deraf, der befinder sig i medlemsstaterne, og som er væsentlige for opretholdelsen af vitale samfundsmæssige funktioner, menneskers sundhed, sikkerhed og økonomiske eller sociale velfærd, såsom kraftværker, transportnetværk og statslige netværk, og hvis afbrydelse eller ødelæggelse i væsentlig grad ville påvirke en medlemsstat som følge af, at disse funktioner ikke kan opretholdes.
Critical infrastructure could be understood to be an asset, system or part thereof located in Member States, which is essential for the maintenance of vital societal functions, health, safety, security, economic or social well-being of people, such as power plants, transport networks or government networks, and the disruption or destruction of which would have a significant impact in a Member State as a result of the failure to maintain those functions.
Der er tegn på en tendens til stadig farligere og gentagne omfattende angreb på informationssystemer, der ofte kan være kritiske for medlemsstaterne eller for enkelte funktioner i den offentlige eller private sektor.
There is evidence of a tendency towards increasingly dangerous and recurrent large-scale attacks conducted against information systems which can often be critical to Member States or to particular functions in the public or private sector.
Denne tendens falder sammen med udviklingen af stadigt mere avancerede metoder, f.eks. oprettelsen og anvendelsen af såkaldte botnet, der indebærer flere stadier af en strafbar handling, hvor hvert stadium i sig selv kan udgøre en alvorlig risiko for samfundets interesser.
This tendency is accompanied by the development of increasingly sophisticated methods, such as the creation and use of so-called ‘botnets’, which involves several stages of a criminal act, where each stage alone could pose a serious risk to public interests.
Dette direktiv sigter bl.a. mod at indføre strafferetlige sanktioner for oprettelse af botnet, dvs. den handling, som går ud på gennem målrettede it-angreb, at etablere fjernstyring af et betydeligt antal computere ved at inficere dem med skadelig software.
This Directive aims, inter alia, to introduce criminal penalties for the creation of botnets, namely, the act of establishing remote control over a significant number of computers by infecting them with malicious software through targeted cyber attacks.