natgillin/translations-raw huggingface dataset:
For each of the qualitative descriptors listed in Annex I to Directive 2008/56/EC, and on the basis of the indicative lists in Annex III to that Directive, it is necessary to define the criteria, including the criteria elements and, where appropriate, the threshold values, to be used.
Prav tako je treba določiti metodološke standarde, vključno z geografskimi merili presoje in načinom, kako bi bilo treba ta merila uporabljati.
Threshold values are intended to contribute to Member States' determination of a set of characteristics for good environmental status and inform their assessment of the extent to which good environmental status is being achieved.
Ta merila in metodološki standardi zagotavljajo doslednost in omogočajo primerjavo presoje, v kolikšni meri je bilo v različnih morskih regijah ali podregijah doseženo dobro okoljsko stanje.
It is also necessary to set out methodological standards, including the geographic scales for assessment and how the criteria should be used.
Da bi zagotovili primerljivost podrobnosti vsakega posodabljanja, ki ga države članice opravijo po pregledih nekaterih elementov svojih morskih strategij, ki so bili posredovani v skladu s členom 17(3) Direktive 2008/56/ES, bi bilo treba opredeliti specifikacije in standardizirane metode za spremljanje ter presojo, in sicer ob upoštevanju obstoječih specifikacij in standardov na ravni Unije ali mednarodni ravni ter na regionalni ali podregionalni ravni.
Those criteria and methodological standards are to ensure consistency and allow for comparison, between marine regions or subregions, of assessments of the extent to which good environmental status is being achieved.
Države članice bi morale pri določanju niza značilnosti za dobro okoljsko stanje v skladu s členom 9(1) Direktive 2008/56/ES in pri vzpostavljanju usklajenih programov spremljanja v skladu s členom 11 navedene direktive uporabljati merila in metodološke standarde, specifikacije in standardizirane metode za spremljanje ter presojo, določene v tem sklepu, v povezavi z elementi ekosistema, antropogenimi pritiski in človekovimi dejavnostmi, navedenimi v okvirnem seznamu Priloge III k navedeni direktivi in s sklicevanjem na začetno presojo, izvedeno v skladu s členom 8(1) navedene direktive.
To ensure comparability between the details of any updates by the Member States following the reviews of certain elements of their marine strategies, sent under Article 17(3) of Directive 2008/56/EC, specifications and standardised methods for monitoring and assessment should be defined, taking into account existing specifications and standards at Union or international level, including regional or subregional level.
Da bi vzpostavili jasno povezavo med določitvijo niza značilnosti dobrega okoljskega stanja in presojo napredka pri doseganju tega cilja, je merila in metodološke standarde primerno organizirati na podlagi kakovostnih deskriptorjev iz Priloge I k Direktivi 2008/56/ES, in sicer ob upoštevanju okvirnih seznamov elementov ekosistema, antropogenih pritiskov in človekovih dejavnosti, določenih v Prilogi III k navedeni direktivi.
Member States should apply the criteria, methodological standards, specifications and standardised methods for monitoring and assessment laid down in this Decision in combination with the ecosystem elements, anthropogenic pressures and human activities listed in the indicative lists of Annex III to Directive 2008/56/EC and by reference to the initial assessment made pursuant to Article 8(1) of that Directive, when determining a set of characteristics for good environmental status in accordance with Article 9(1) of that Directive, and when establishing coordinated monitoring programmes under Article 11 of that Directive.
Nekatera navedena merila in metodološki standardi se nanašajo predvsem na presojo okoljskega stanja in prevladujočih pritiskov ter vplivov iz točke (a) oziroma (b) člena 8(1) Direktive 2008/56/ES.
In order to establish a clear link between the determination of a set of characteristics for good environmental status and the assessment of progress towards its achievement, it is appropriate to organise the criteria and methodological standards on the basis of the qualitative descriptors laid down in Annex I to Directive 2008/56/EC, taking into account the indicative lists of ecosystem elements, anthropogenic pressures and human activities laid down in Annex III to that Directive.
V primerih, kjer mejne vrednosti niso določene, bi morale države članice mejne vrednosti določiti s sodelovanjem na ravni Unije, regije ali podregije, na primer s sklicevanjem na obstoječe vrednosti ali z razvojem novih na podlagi konvencij o regionalnih morjih.
Some of those criteria and methodological standards relate in particular to the assessment of environmental status or of predominant pressures and impacts under points (a) or (b) of Article 8(1) of Directive 2008/56/EC, respectively.
V primerih, kjer bi bilo treba mejne vrednosti določiti s sodelovanjem na ravni Unije (za deskriptorje o morskih odpadkih, podvodnem hrupu in neoporečnosti morskega dna), bo to storjeno v okviru skupne strategije izvajanja, ki so jo države članice in Komisija vzpostavile za namene Direktive 2008/56/ES.
In cases where no threshold values are laid down, Member States should establish threshold values through Union, regional or subregional cooperation, for instance by referring to existing values or developing new ones in the framework of the Regional Sea Conventions.
Ko bo sodelovanje na ravni Unije, regij ali podregij vzpostavljeno, bodo te mejne vrednosti po tem, ko bodo kot del poročanja držav članic v skladu s členom 17(3) Direktive 2008/56/ES poslane Komisiji, postale del niza značilnosti za dobro okoljsko stanje držav članic.
In cases where threshold values should be established through cooperation at Union level (for the descriptors on marine litter, underwater noise and seabed integrity), this will be done in the framework of the Common Implementation Strategy set up by the Member States and the Commission for the purposes of Directive 2008/56/EC.
Dokler te mejne vrednosti niso določene s sodelovanjem na ravni Unije, regij ali podregij, bi moralo biti državam članicam omogočeno, da uporabljajo nacionalne mejne vrednosti, smerne trende ali mejne vrednosti na podlagi pritiska kot približke.
Once established through Union, regional or subregional cooperation, these threshold values will only become part of Member States' sets of characteristics for good environmental status when they are sent to the Commission as part of Member States' reporting under Article 17(3) of Directive 2008/56/EC.
Mejne vrednosti bi morale odražati, kjer je to primerno, raven kakovosti, ki odraža pomen negativnega vpliva na merilo, in bi morale biti določene glede na referenčno stanje.
Until such threshold values are established through Union, regional or subregional cooperation, Member States should be able to use national threshold values, directional trends or pressure-based threshold values as proxies.
Mejne vrednosti bi morale biti skladne z zakonodajo Unije in določene v okviru ustreznih geografskih meril presoje, ki odražajo različne biotske in abiotske značilnosti regij, podregij in pododdelkov.
Threshold values should reflect, where appropriate, the quality level that reflects the significance of an adverse effect for a criterion and should be set in relation to a reference condition.
To pomeni, da čeprav bi postopek za določitev mejnih vrednosti potekal na ravni Unije, bi to lahko povzročilo določitev različnih mejnih vrednostih, ki so značilne za posamezno regijo, podregijo ali pododdelek.
Threshold values should be consistent with Union legislation and set at appropriate geographic scales to reflect the different biotic and abiotic characteristics of the regions, subregions and subdivisions.
Mejne vrednosti bi bilo treba določiti tudi na podlagi previdnostnega načela, ki odraža možna tveganja za morsko okolje.
This means that even if the process to establish threshold values takes place at Union level, this may result in the setting of different threshold values, which are specific to a region, subregion or subdivision.
Pri določitvi mejnih vrednosti bi bilo treba upoštevati dinamično naravo morskih ekosistemov in njihovih elementov, ki se lahko spreminjajo v času in prostoru preko hidroloških in podnebnih sprememb, razmerij med plenilcem in plenom ter drugih okoljskih dejavnikov.
Threshold values should also be set on the basis of the precautionary principle, reflecting the potential risks to the marine environment.
Mejne vrednosti bi morale odražati tudi dejstvo, da se lahko morski ekosistem v primeru poslabšanja vrne v stanje, ki odraža prevladujoče fiziografske, geografske, podnebne in biološke razmere in ne specifičnega preteklega stanja.
The setting of threshold values should accommodate the dynamic nature of marine ecosystems and their elements, which can change in space and time through hydrological and climatic variation, predator-prey relationships and other environmental factors.
V skladu s členom 1(3) Direktive 2008/56/ES je treba zagotoviti, da je skupna obremenitev človekovih dejavnosti ohranjena v mejah, ki so skladne z doseganjem dobrega okoljskega stanja, in da ni ogrožena sposobnost morskih ekosistemov, da se odzovejo na spremembe, ki jih povzročajo ljudje.
Threshold values should also reflect the fact that marine ecosystems may recover, if deteriorated, to a state that reflects prevailing physiographic, geographic, climatic and biological conditions, rather than return to a specific state of the past.
To lahko pomeni, da mejne vrednosti za nekatere pritiske in njihovi vplivi na okolje niso nujno doseženi na vseh področjih morskih voda držav članic, in sicer pod pogojem, da to ne ogroža doseganja ciljev Direktive 2008/56/ES ter obenem omogoča trajnostno uporabo morskega blaga in storitev.
In accordance with Article 1(3) of Directive 2008/56/EC, the collective pressure of human activities needs to be kept within levels compatible with the achievement of good environmental status, ensuring that the capacity of marine ecosystems to respond to human-induced changes is not compromised.
Določiti je treba mejne vrednosti, ki bodo del niza značilnosti, ki jih uporabljajo države članice pri določanju dobrega okoljskega stanja v skladu s členom 9(1) Direktive 2008/56/ES, in v kolikšni meri je treba te mejne vrednosti doseči.
This may entail, where appropriate, that threshold values for certain pressures and their environmental impacts are not necessarily achieved in all areas of Member States' marine waters, provided that this does not compromise the achievement of the objectives of Directive 2008/56/EC, while enabling the sustainable use of marine goods and services.
Zato mejne vrednosti same po sebi ne pomenijo določitve dobrega okoljskega stanja držav članic.
It is necessary to lay down threshold values which will be part of the set of characteristics used by Member States in their determination of good environmental status in accordance with Article 9(1) of Directive 2008/56/EC, and the extent to which the threshold values are to be achieved.
Države članice bi morale navesti, v kolikšni meri je bilo doseženo dobro okoljsko stanje, izraženo kot delež njihovih morskih voda, v katerih so bile dosežene mejne vrednosti, ali kot delež elementov meril (vrste, onesnaževala itd.), ki so dosegli mejne vrednosti.
Threshold values therefore do not, by themselves, constitute Member States' determinations of good environmental status.
Glede na pogosto počasen odziv morskega okolja na spremembe bi morale države članice pri presoji stanja svojih morskih voda v skladu s členom 17(2)(a) Direktive 2008/56/ES navesti, če se je stanje izboljšalo, poslabšalo ali je stabilno v primerjavi s prejšnjim obdobjem poročanja.
Member States should express the extent to which good environmental status is being achieved as the proportion of their marine waters over which the threshold values have been achieved or as the proportion of criteria elements (species, contaminants, etc.) that have achieved the threshold values.
Kadar mejne vrednosti, določene v skladu s tem sklepom, za posamezno merilo niso izpolnjene, bi morale države članice razmisliti o sprejetju ustreznih ukrepov ali izvajanju dodatnih raziskav in preiskav.
When assessing the status of their marine waters in accordance with Article 17(2)(a) of Directive 2008/56/EC, Member States should express any change in status as improving, stable or deteriorating compared to the previous reporting period, in view of the often slow response of the marine environment to change.
Kadar so države članice dolžne sodelovati na regionalni ali podregionalni ravni, bi morale, kjer je to praktično in primerno, uporabljati obstoječe regionalne institucionalne strukture sodelovanja, vključno s tistimi, ki jih določajo konvencije o regionalnih morjih, kot je določeno v skladu s členom 6 Direktive 2008/56/ES.
Where threshold values, set in accordance with this Decision, are not met for a particular criterion, Member States should consider taking appropriate measures or carrying out further research or investigation.
Ko posebna merila in metodološki standardi niso na voljo, kar vključuje tudi integracijo meril, specifikacije in standardizirane metode za spremljanje ter presojo, bi morale države članice, kjer je to praktično in primerno, nadgraditi tiste, ki so bili razviti na mednarodni, regionalni ali podregionalni ravni, na primer tiste, ki so bili dogovorjeni s konvencijami o regionalnih morjih ali drugimi mednarodnimi mehanizmi.
Where Member States are required to cooperate at regional or subregional level, they should use, where practical and appropriate, existing regional institutional cooperation structures, including those under Regional Sea Conventions, as provided under Article 6 of Directive 2008/56/EC.
V nasprotnem primeru se lahko države članice odločijo, kjer je to primerno, da se bodo med seboj usklajevale znotraj regije ali podregije.
Similarly, in the absence of specific criteria, methodological standards, including for integration of the criteria, specifications and standardised methods for monitoring and assessment, Member States should build upon, where practical and appropriate, those developed at international, regional or subregional level, for instance those agreed in the framework of the Regional Sea Conventions, or other international mechanisms.
Poleg tega se lahko država članica na podlagi značilnosti svojih morskih voda tudi odloči, da bo v podporo pri izvajanju Direktive 2008/56/ES upoštevala dodatne elemente, ki niso določeni v tem sklepu in niso obravnavani na mednarodni, regionalni ali podregionalni ravni, ali razmislila o uporabi elementov tega sklepa za somornice, kot so opredeljene v členu 2(6) Direktive 2000/60/ES.
Otherwise, Member States may choose to coordinate amongst themselves within the region or subregion, where relevant.
Za spremljanje in presojo svojih morskih voda na učinkovit in uspešen način ter lažjo določitev prednostnih ukrepov, ki jih je treba sprejeti za dosego dobrega okoljskega stanja, bi morale imeti države članice pod določenimi pogoji dovolj prožnosti, da se osredotočijo na prevladujoče pritiske in njihov okoljski vpliv na različne elemente ekosistema v posamezni regiji ali podregiji.
In addition, a Member State may also decide, on the basis of the specificities of its marine waters, to consider additional elements not laid down in this Decision and not dealt with at international, regional or subregional level, or to consider applying elements of this Decision to its transitional waters, as defined in Article 2(6) of Directive 2000/60/EC, in support of the implementation of Directive 2008/56/EC.
V ta namen bi morale države članice najprej imeti možnost, da če je to upravičeno, določijo, da nekatera merila niso primerna za uporabo.
Member States should have sufficient flexibility, under specified conditions, to focus on the predominant pressures and their environmental impacts on the different ecosystem elements in each region or subregion in order to monitor and assess their marine waters in an efficient and effective manner and to facilitate prioritisation of actions to be taken to achieve good environmental status.
Nadalje bi morale države članice imeti možnost, da se ne odločijo za uporabo nekaterih elementov meril ali za izbiro dodatnih elementov oziroma da se osredotočijo na nekatere matrikse ali območja svojih morskih voda, in sicer pod pogojem, da to temelji na oceni tveganja v zvezi s pritiski in njihovimi učinki.
For that purpose, firstly, Member States should be able to consider that some of the criteria are not appropriate to apply, provided this is justified.
Nazadnje bi bilo treba uvesti razlikovanje med primarnimi in sekundarnimi merili.
Secondly, Member States should have the possibility to decide not to use certain criteria elements or to select additional elements or to focus on certain matrices or areas of their marine waters, provided that this is based on a risk assessment in relation to the pressures and their impacts.
Medtem ko bi bilo primarna merila treba uporabljati za zagotavljanje doslednosti po vsej Uniji, bi za sekundarna merila morala veljati določena mera prožnosti.
Finally, a distinction should be introduced between primary and secondary criteria.
Države članice bi morale po potrebi odločati o uporabi sekundarnega merila, da se dopolni primarno merilo ali kadar za posamezno merilo obstaja tveganje, da morsko okolje ne bo doseglo ali ohranilo dobrega okoljskega stanja.
While primary criteria should be used to ensure consistency across the Union, flexibility should be granted with regard to secondary criteria.
Merila, vključno z mejnimi vrednostmi, metodološkimi standardi, specifikacijami in standardiziranimi metodami za spremljanje ter presojo, bi morala temeljiti na najboljših razpoložljivih znanstvenih dognanjih.
The use of a secondary criterion should be decided by Member States, where necessary, to complement a primary criterion or when, for a particular criterion, the marine environment is at risk of not achieving or not maintaining good environmental status.
Za podporo nadaljnjemu razvoju nekaterih meril je še vedno potreben dodaten znanstveni in tehnični napredek, ki bi ga bilo treba uporabljati v skladu z dostopnim znanjem in razumevanjem.
Criteria, including threshold values, methodological standards, specifications and standardised methods for monitoring and assessment should be based on the best available science.
Sklep 2010/477/EU bi zato bilo treba razveljaviti.
However, additional scientific and technical progress is still required to support the further development of some of them, and should be used as the knowledge and understanding become available.
Ukrepi iz tega sklepa so v skladu z mnenjem regulativnega odbora –
Decision 2010/477/EU should therefore be repealed.
SPREJELA NASLEDNJI SKLEP:
The measures provided for in this Decision are in accordance with the opinion of the Regulatory Committee,
Člen 1
HAS ADOPTED THIS DECISION:
Vsebina
Article 1
Ta sklep določa:
Subject matter
merila in metodološke standarde, ki jih morajo države članice uporabiti pri določanju niza značilnosti za dobro okoljsko stanje v skladu s členom 9(1) Direktive 2008/56/ES na podlagi prilog I in III ter na podlagi začetne presoje, izvedene v skladu s členom 8(1) te direktive, da presodijo, v kolikšni meri je bilo doseženo dobro okoljsko stanje v skladu s členom 9(3) te direktive;
This Decision lays down:
specifikacije in standardizirane metode za spremljanje ter presojo v skladu s členom 11(4) Direktive 2008/56/ES, ki jih države članice uporabijo pri vzpostavljanju usklajenih programov spremljanja v skladu s členom 11 navedene direktive;
criteria and methodological standards to be used by Member States when determining a set of characteristics for good environmental status in accordance with Article 9(1) of Directive 2008/56/EC, on the basis of Annexes I and III and by reference to the initial assessment made pursuant to Article 8(1) of that Directive, to assess the extent to which good environmental status is being achieved, in accordance with Article 9(3) of that Directive;
časovni okvir za določitev mejnih vrednosti, seznamov elementov meril in metodoloških standardov na ravni Unije, regij in podregij;
specifications and standardised methods for monitoring and assessment, to be used by Member States when establishing coordinated monitoring programmes under Article 11 of Directive 2008/56/EC, in accordance with Article 11(4) of that Directive;
obvezno sporočanje za elemente meril, mejne vrednosti in metodološke standarde.
a timeline for the establishment of threshold values, lists of criteria elements and methodological standards through Union, regional or subregional cooperation;
Člen 2
a notification requirement for criteria elements, threshold values and methodological standards.
Opredelitev pojmov
Article 2
Za namene tega sklepa se uporabljajo opredelitve pojmov iz člena 3 Direktive 2008/56/ES.
For the purposes of this Decision, the definitions laid down in Article 3 of Directive 2008/56/EC shall apply.
„podregije“ pomenijo podregije, navedene v členu 4(2) Direktive 2008/56/ES;
The following definitions shall also apply:
„pododdelki“ pomenijo pododdelke iz člena 4(2) Direktive 2008/56/ES;
‘subregions’ means the subregions listed in Article 4(2) of Directive 2008/56/EC;
„invazivne neavtohtone vrste“ pomenijo „invazivne tujerodne vrste“ v smislu člena 3(2) Uredbe (EU) št. 1143/2014 Evropskega parlamenta in Sveta [12];
‘subdivisions’ means subdivisions as referred to in Article 4(2) of Directive 2008/56/EC;
„elementi meril“ pomenijo sestavne dele ekosistema, zlasti njegove biološke elemente (vrste, habitate in njihove skupnosti) ali vidike pritiskov na morsko okolje (biološki, fizikalni, snovi, odpadki in energija), za katere se izvede presoja v smislu vsakega merila;
‘invasive non-indigenous species’ means ‘invasive alien species’ within the meaning of Article 3(2) of Regulation (EU) No 1143/2014 of the European Parliament and of the Council [12];
„mejna vrednost“ pomeni vrednost ali razpon vrednosti, ki omogoča presojo dosežene ravni kakovosti za določeno merilo, s čimer prispeva k presoji, v kolikšni meri je bilo doseženo dobro okoljsko stanje.
‘criteria elements’ means constituent elements of an ecosystem, particularly its biological elements (species, habitats and their communities), or aspects of pressures on the marine environment (biological, physical, substances, litter and energy), which are assessed under each criterion;
Člen 3
‘threshold value’ means a value or range of values that allows for an assessment of the quality level achieved for a particular criterion, thereby contributing to the assessment of the extent to which good environmental status is being achieved.
Uporaba meril, metodoloških standardov, specifikacij in standardiziranih metod
Article 3
Države članice za izvajanje tega sklepa uporabljajo primarna merila in metodološke standarde, specifikacije in standardizirane metode, določene v prilogi.
Use of criteria, methodological standards, specifications and standardised methods
Na podlagi začetne presoje ali poznejših posodobitev, izvedenih v skladu s členom 8 in členom 17(2)(a) Direktive 2008/56/ES, lahko države članice v utemeljenih okoliščinah menijo, da ni primerno uporabiti enega ali več primarnih meril.
Member States shall use primary criteria and associated methodological standards, specifications and standardised methods laid down in the Annex to implement this Decision.
V takih primerih države članice Komisiji predložijo utemeljitev v okviru obvestila, poslanega v skladu s členom 9(2) ali členom 17(3) Direktive 2008/56/ES.
However, on the basis of the initial assessment or its subsequent updates carried out in accordance with Articles 8 and 17(2)(a) of Directive 2008/56/EC, Member States may consider, in justified circumstances, that it is not appropriate to use one or more of the primary criteria.
Država članica v skladu z obveznostjo regionalnega sodelovanja iz členov 5 in 6 Direktive 2008/56/ES obvesti druge države članice, ki si delijo morsko regijo ali podregijo, preden se odloči, da v skladu s prvim pododstavkom ne bo uporabila primarnega merila.