natgillin/translations-raw huggingface dataset:
The objective is that human pressures on the seabed do not hinder the ecosystem components to retain their natural diversity, productivity and dynamic ecological processes, having regard to ecosystem resilience.
Cilj je preprečiti, da bi pritiski na morsko dno zaradi človekovega delovanja ovirali sestavne dele ekosistema pri ohranjanju njihove naravne raznolikosti, produktivnosti in dinamičnih ekoloških procesov ob upoštevanju odpornosti ekosistema.
The scale of assessment for this descriptor may be particularly challenging because of the patchy nature of the features of some benthic ecosystems and of several human pressures.
Obseg ocene za ta deskriptor lahko zaradi neenotne narave značilnosti nekaterih bentoških ekosistemov in pritiskov zaradi človekovega delovanja pomeni poseben izziv.
Assessment and monitoring needs to be carried out further to an initial screening of impacts and threats to biodiversity features and human pressures, as well as an integration of assessment results from smaller to broader scales, covering where appropriate a subdivision, sub-region or region [19].
Ocenjevanje in spremljanje je treba izvajati poleg začetnega preverjanja vplivov in nevarnosti za poteze biotske raznovrstnosti in pritiskov zaradi človekovega delovanja ter povezovanja rezultatov ocen od majhnega do širšega obsega, ki po potrebi zajemajo pododdelek, podregijo ali regijo [19].
Physical damage, having regard to substrate characteristics
Fizična škoda ob upoštevanju značilnosti substrata
The main concern for management purposes is the magnitude of impacts of human activities on seafloor substrates structuring the benthic habitats.
Glavni razlog za zaskrbljenost glede upravljanja je obseg vplivov človekovih dejavnosti na substrat morskega dna, ki oblikuje bentoške habitate.
Among the substrate types, biogenic substrates, which are the most sensitive to physical disturbance, provide a range of functions that support benthic habitats and communities.
Med različnimi vrstami substrata je biogeni substrat, ki je najbolj občutljiv na fizične motnje in z različnimi funkcijami podpira bentoške habitate in skupnosti.
Type, abundance, biomass and areal extent of relevant biogenic substrate (6.1.1)
Vrsta, številčnost, biomasa in območje razširjenosti zadevnega biogenega substrata (6.1.1)
Extent of the seabed significantly affected by human activities for the different substrate types (6.1.2).
Obseg morskega dna, na katerega znatno vplivajo človekove dejavnosti, za različne vrste substrata (6.1.2).
Condition of benthic community
Stanje bentoške združbe
The characteristics of the benthic community such as species composition, size composition and functional traits provide an important indication of the potential of the ecosystem to function well.
Značilnosti bentoške združbe, kot so vrstna sestava, velikostna sestava in funkcionalne značilnosti, so pomemben pokazatelj potenciala za dobro delovanje ekosistema.
Information on the structure and dynamics of communities is obtained, as appropriate, by measuring species diversity, productivity (abundance or biomass), tolerant or sensitive taxa and taxocene dominance and size composition of a community, reflected by the proportion of small and large individuals.
Informacije o strukturi in dinamiki združb se pridobijo, če je primerno, z merjenjem raznolikosti vrst, produktivnosti (številčnost ali biomasa), odpornih ali občutljivih taksonov in taksonomske dominantnosti ter velikostne sestave združbe, ki je izražena z deležem majhnih in velikih rib.
Presence of particularly sensitive and/or tolerant species (6.2.1)
Prisotnost posebej občutljivih in/ali odpornih vrst (6.2.1)
Multi-metric indexes assessing benthic community condition and functionality, such as species diversity and richness, proportion of opportunistic to sensitive species (6.2.2)
Multimetrijski indeksi za oceno stanja in funkcionalnosti bentoške združbe, kot so raznolikost in bogastvo vrst ter delež oportunističnih in občutljivih vrst (6.2.2)
Proportion of biomass or number of individuals in the macrobenthos above some specified length/size (6.2.3)
Delež biomase ali število osebkov v makrobentoški združbi nad določeno dolžino/velikostjo (6.2.3)
Parameters describing the characteristics (shape, slope and intercept) of the size spectrum of the benthic community (6.2.4).
Parametri, ki opisujejo značilnosti (oblika, naklon in odsek) spektra velikosti bentoške združbe (6.2.4).
Permanent alteration of hydrographical conditions does not adversely affect marine ecosystems.
Trajna sprememba hidrografskih razmer ne škoduje morskim ekosistemom.
Permanent alterations of the hydrographical conditions by human activities may consist for instance of changes in the tidal regime, sediment and freshwater transport, current or wave action, leading to modifications of the physical and chemicals characteristics set out in Table 1 of Annex III to Directive 2008/56/EC.
Trajne spremembe hidrografskih razmer zaradi človekovih dejavnosti lahko na primer vključujejo spremembe režima bibavice, transporta sedimentov in sladke vode, tokov ali valovanja, ki povzročijo spremembe fizičnih in kemičnih značilnosti iz tabele 1 Priloge III k Direktivi 2008/56/ES.
Such changes may be particularly relevant whenever they have the potential to affect marine ecosystems at a broader scale and their assessment may provide an early warning of possible impacts on the ecosystem.
Takšne spremembe so zlasti pomembne, če lahko v večjem obsegu vplivajo na morske ekosisteme, zato se lahko z njihovo oceno vnaprej opozori na morebitne vplive na ekosistem.
For coastal waters, Directive 2000/60/EC sets hydromorphological objectives that need to be addressed through measures in the context of river basin management plans.
Za obalne vode, Direktiva 2000/60/ES določa hidromorfološke cilje, ki jih je treba uresničevati z ukrepi v okviru načrtov upravljanja povodij.
A case by case approach is necessary to assess the impact of activities.
Za oceno učinka dejavnosti je potreben pristop, pri katerem se obravnava vsak primer posebej.
Tools such as environmental impact assessment, strategic environmental assessment and maritime spatial planning may contribute to evaluate and assess the extent and the cumulative aspects of impacts from such activities.
Instrumenti, kot so presoja vplivov na okolje, strateška okoljska presoja in pomorsko prostorsko načrtovanje, so lahko koristni pri presoji in oceni obsega ter kumulativnih vidikov vplivov takšnih dejavnosti.
It is however important to ensure that any such tools provide for adequate elements to assess potential impacts on the marine environment, including transboundary considerations.
Pomembno pa je zagotoviti, da imajo vsi takšni instrumenti ustrezne elemente za oceno morebitnih vplivov na morsko okolje, vključno s čezmejnimi premisleki.
Spatial characterisation of permanent alterations
Prostorska opredelitev trajnih sprememb
Extent of area affected by permanent alterations (7.1.1)
Velikost območja, na katerem je prišlo do trajnih sprememb (7.1.1)
Impact of permanent hydrographical changes
Učinek trajnih hidrografskih sprememb
Spatial extent of habitats affected by the permanent alteration (7.2.1)
Velikost območja habitatov, na katerih je prišlo do trajnih sprememb (7.2.1)
Changes in habitats, in particular the functions provided (e.g. spawning, breeding and feeding areas and migration routes of fish, birds and mammals), due to altered hydrographical conditions (7.2.2).
Spremembe habitatov, zlasti spremembe predvidenih funkcij (npr. drstenje, območja vzreje in hranjenja ter selitvene poti rib, ptic in sesalcev), zaradi spremenjenih hidrografskih razmer (7.2.2).
The concentration of contaminants in the marine environment and their effects need to be assessed taking into account the impacts and threats to the ecosystem [20].
Oceniti je treba koncentracijo onesnaževal v morskem okolju in njihove vplive, pri čemer se upoštevajo vplivi in grožnje za ekosistem [20].
Relevant provisions of Directive 2000/60/EC in territorial and/or coastal waters have to be taken into consideration to ensure proper coordination of the implementation of the two legal frameworks, having also regard to the information and knowledge gathered and approaches developed in regional sea conventions.
Upoštevati je treba ustrezne določbe iz Direktive 2000/60/ES, ki se uporabljajo za teritorialne vode in/ali obalne vode, da se zagotovi ustrezno usklajeno izvajanje obeh zakonodajnih okvirov, pri čemer je treba upoštevati tudi informacije, znanje in pristope, pridobljene v okviru regionalnih konvencij o morjih.
The Member States have to consider the substances or groups of substances, where relevant for the marine environment, that:
Ko je to pomembno za morsko okolje, morajo države članice obravnavati snovi ali skupine snovi, ki:
exceed the relevant Environmental Quality Standards set out pursuant to Article 2(35) and Annex V to Directive 2000/60/EC in coastal or territorial waters adjacent to the marine region or sub-region, be it in water, sediment and biota; and/or
presegajo ustrezne okoljske standarde kakovosti, določene v skladu s členom 2(35) in Prilogo V Direktive 2000/60/ES, v vodnih telesih obalnih voda ali teritorialnih voda, ki mejijo na morsko regijo ali podregijo, v vodi, sedimentu in živih organizmih, in/ali
are listed as priority substances in Annex X to Directive 2000/60/EC and further regulated in Directive 2008/105/EC, which are discharged into the concerned marine region, sub-region or subdivision; and/or
so v Prilogi X k Direktivi 2000/60/ES uvrščene kot prednostne snovi in jih nadalje ureja Direktiva 2008/105/ES ter se odvajajo v zadevno morsko regijo, podregijo ali pododdelek, in/ali
are contaminants and their total releases (including losses, discharges or emissions) may entail significant risks to the marine environment from past and present pollution in the marine region, sub-region or subdivision concerned, including as a consequence of acute pollution events following incidents involving for instance hazardous and noxious substances.
so onesnaževala in bi lahko njihovo skupno sproščanje (vključno z izgubami, izpusti ali emisijami) zaradi pretekle ali sedanje onesnaženosti pomenilo veliko tveganje za morsko okolje v zadevni morski regiji, podregiji ali pododdelku, tudi kot posledica akutnega onesnaženja po nesrečah, v katere so npr. vpletene nevarne in zdravju škodljive snovi.
Progress towards good environmental status will depend on whether pollution is progressively being phased out, i.e. the presence of contaminants in the marine environment and their biological effects are kept within acceptable limits, so as to ensure that there are no significant impacts on or risk to the marine environment.
Napredek pri doseganju dobrega okoljskega stanja bo odvisen od tega, ali se onesnaženje postopno odpravlja, tj. prisotnost onesnaževalcev v morskem okolju in njihovi biološki vplivi se ohranjajo v sprejemljivih mejah, da bi se preprečili pomembni vplivi na morsko okolje ali tveganje zanj.
Concentration of contaminants
Koncentracija onesnaževal
Concentration of the contaminants mentioned above, measured in the relevant matrix (such as biota, sediment and water) in a way that ensures comparability with the assessments under Directive 2000/60/EC (8.1.1)
Koncentracija navedenih onesnaževal, izmerjena v ustreznem matriksu (kot so živi organizmi, sediment in voda), tako da je mogoča primerjava z ocenami iz Direktive 2000/60/ES) (8.1.1)
Effects of contaminants
Vplivi onesnaževal
Levels of pollution effects on the ecosystem components concerned, having regard to the selected biological processes and taxonomic groups where a cause/effect relationship has been established and needs to be monitored (8.2.1)
Ravni vplivov onesnaženja na zadevne sestavne dele ekosistema, pri čemer se upoštevajo izbrani biološki procesi in taksonomske skupine, v zvezi s katerimi je bila ugotovljena vzročnoposledična zveza in ki jih je treba spremljati (8.2.1)
Occurrence, origin (where possible), extent of significant acute pollution events (e.g. slicks from oil and oil products) and their impact on biota physically affected by this pollution (8.2.2).
Pojavnost, izvor (po možnosti), obseg znatnega akutnega onesnaženja (npr. madeži nafte in naftnih derivatov) in njihov vpliv na žive organizme, ki so fizično ogroženi zaradi tega onesnaženja (8.2.2).
In the different regions or sub-regions, Member States need to monitor in edible tissues (muscle, liver, roe, flesh, soft parts as appropriate) of fish, crustaceans, molluscs and echinoderms, as well as seaweed, caught or harvested in the wild, the possible presence of substances for which maximum levels are established at European, regional, or national level for products destined to human consumption.
Države članice morajo v različnih regijah in podregijah pri užitnih tkivih (mišicah, jetrih, ikrah, mehkih tkivih) rib, rakov, mehkužcev, iglokožcev ter morski travi, ulovljenih ali pobranih v naravi, spremljati morebitno prisotnost snovi, za katere so na evropski, regionalni ali nacionalni ravni določene zgornje mejne vrednosti za izdelke, namenjene za prehrano ljudi.
Levels, number and frequency of contaminants
Ravni, število in pogostost onesnaževal
Actual levels of contaminants that have been detected and number of contaminants which have exceeded maximum regulatory levels (9.1.1)
Dejanske ugotovljene ravni onesnaževal in število onesnaževal, katerih mejne vrednosti so bile presežene (9.1.1)
Frequency of regulatory levels being exceeded (9.1.2).
Pogostost preseganja mejnih vrednosti (9.1.2).
The distribution of litter is highly variable, which needs to be taken into consideration for monitoring programmes.
V programih spremljanja je treba upoštevati, da je razporeditev odpadkov zelo spremenljiva.
It is necessary to identify the activity to which it is linked including, where possible, its origin.
Opredeliti je treba dejavnost, s katero so povezani, ter izvor, če je to mogoče.
There is still a need for further development of several indicators, notably those relating to biological impacts and to micro-particles, as well as for the enhanced assessment of their potential toxicity [21].
Še vedno je treba nadalje razviti več kazalcev, predvsem tiste, ki so povezani z biološkimi vplivi in mikrodelci, ter izboljšati oceno njihove potencialne strupenosti [21].
Characteristics of litter in the marine and coastal environment
Značilnosti odpadkov v morskem in obalnem okolju
Trends in the amount of litter washed ashore and/or deposited on coastlines, including analysis of its composition, spatial distribution and, where possible, source (10.1.1)
Trendi glede količine odpadkov, naplavljenih na kopno in/ali odloženih na obalo, vključno z analizo njihove sestave, prostorsko razporeditvijo in izvorom, če je to mogoče (10.1.1)
Trends in the amount of litter in the water column (including floating at the surface) and deposited on the sea-floor, including analysis of its composition, spatial distribution and, where possible, source (10.1.2)
Trendi glede količine odpadkov v vodnem stolpu (tudi plavajočih na gladini) in odloženih na morsko dno, vključno z analizo njihove sestave, prostorsko razporeditvijo in izvorom, če je to mogoče (10.1.2)
Trends in the amount, distribution and, where possible, composition of micro-particles (in particular micro-plastics) (10.1.3)
trendi glede količine, razporeditve in po možnosti sestave mikrodelcev (zlasti mikroplastike) (10.1.3)
Impacts of litter on marine life
Vplivi odpadkov na morske organizme
Trends in the amount and composition of litter ingested by marine animals (e.g. stomach analysis) (10.2.1).
Trendi glede količine in sestave odpadkov, ki jih zaužijejo morske živali (npr. analiza vsebine želodca) (10.2.1).
This indicator needs to be developed further, based on the experience in some sub-regions (e.g. North Sea), to be adapted in other regions.
Na podlagi izkušenj v nekaterih podregijah (npr. v Severnem morju) je treba ta kazalec nadalje razviti, da se bo prilagodil drugim regijam.
Together with underwater noise, which is highlighted throughout Directive 2008/56/EC, other forms of energy input have the potential to impact on components of marine ecosystems, such as thermal energy, electromagnetic fields and light.
Poleg podvodnega hrupa, ki je izpostavljen v celotni Direktivi 2008/56/ES, lahko tudi druge oblike dovedene energije vplivajo na sestavne dele morskih ekosistemov, npr. toplotna energija, elektromagnetna polja in svetloba.
Additional scientific and technical progress is still required to support the further development of criteria related to this descriptor [22], including in relation to impacts of introduction of energy on marine life, relevant noise and frequency levels (which may need to be adapted, where appropriate, subject to the requirement of regional cooperation).
Še vedno je potreben dodaten znanstven in tehnični napredek za podporo nadaljnjemu razvoju meril, povezanih s tem deskriptorjem [22], tudi v zvezi z vplivi dovajanja energije na morske organizme, zadevnimi stopnjami hrupa in frekvenc (po potrebi bi lahko bila potrebna prilagoditev v skladu z zahtevami regionalnega sodelovanja).
At the current stage, the main orientations for the measurement of underwater noise have been identified as a first priority in relation to assessment and monitoring [23], subject to further development, including in relation to mapping.
V tej fazi so bile glavne usmeritve za merjenje podvodnega hrupa opredeljene kot glavna prednostna naloga v zvezi z ocenjevanjem in spremljanjem [23], ki jih je treba nadalje razviti, tudi v zvezi s kartiranjem.
Anthropogenic sounds may be of short duration (e.g. impulsive such as from seismic surveys and piling for wind farms and platforms, as well as explosions) or be long lasting (e.g. continuous such as dredging, shipping and energy installations) affecting organisms in different ways.
Antropogeni zvok je lahko kratkotrajen (npr. impulzni, ki nastaja pri seizmičnih raziskavah, postavljanju opornikov za vetrne elektrarne in platforme ter eksplozijah) ali dolgotrajen (npr. neprekinjen, ki nastaja pri poglabljanju dna, ladijskem prometu in energetskih napravah) in vpliva na organizme na različne načine.
Most commercial activities entailing high level noise levels affecting relatively broad areas are executed under regulated conditions subject to a license.
Večina gospodarskih dejavnosti, ki povzročajo visoke ravni hrupa in vplivajo na sorazmerno velika območja, se izvaja pod določenimi pogoji in z dovoljenjem.
This creates the opportunity for coordinating coherent requirements for measuring such loud impulsive sounds.
To omogoča usklajevanje skladnih zahtev glede merjenja takšnega glasnega impulznega hrupa.
Distribution in time and place of loud, low and mid frequency impulsive sounds
Časovna in prostorska razporeditev impulznega hrupa pri visoki, nizki in srednji frekvenci
Proportion of days and their distribution within a calendar year over areas of a determined surface, as well as their spatial distribution, in which anthropogenic sound sources exceed levels that are likely to entail significant impact on marine animals measured as Sound Exposure Level (in dB re 1μPa2.s) or as peak sound pressure level (in dB re 1μPapeak) at one metre, measured over the frequency band 10 Hz to 10 kHz (11.1.1)
Delež dni in njihova razporeditev v koledarskem letu na območju določene površine ter njihova prostorska razporeditev, kadar antropogeni zvočni viri presežejo visoke ravni, ki pomenijo verjeten znaten vpliv na morske živali, merjene kot raven izpostavljenosti zvoku (v dB re 1μPa2 s) ali najvišja raven zvočnega tlaka (v dB re 1μPapeak) na globini enega metra in v frekvenčnem pasu 10 Hz do 10 kHz (11.1.1).
Continuous low frequency sound
Neprekinjen nizkofrekvenčni zvok
Trends in the ambient noise level within the 1/3 octave bands 63 and 125 Hz (centre frequency) (re 1μΡa RMS; average noise level in these octave bands over a year) measured by observation stations and/or with the use of models if appropriate (11.2.1).
Trendi glede ravni hrupa v okolju znotraj tretjinskih pasov oktave 63 in 125 Hz (osrednja frekvenca) (re 1μΡa RMS; povprečna raven hrupa v teh pasovih oktave v enem letu), ki se merijo s statistično reprezentativnim sklopom opazovalnih postaj in/ali po potrebi z uporabo modelov (11.2.1).
See recitals 3 and 4.
Glej uvodni izjavi 3 in 4.
OJ L 348, 24.12.2008, p. 84.
UL L 348, 24.12.2008, str. 84.
See recital 2.
Glej uvodno izjavo 2.
See points 3 to 6 in Part A.
Glej točke 3 do 6 v delu A.
See point 6 in Part A.
Glej točko 6 v delu A.
‘Assessment, monitoring and reporting of conservation status — Preparing the 2001-2007 report under Article 17 of the Habitats Directive’, 15 March 2005, accepted in the Habitats Committee on 20 April 2005.
„Ocenjevanje in spremljanje ohranjenosti ter poročanje o njem – Priprava poročila za obdobje 2001–2007 v okviru člena 17 direktive o habitatih“ z dne 15. marca 2005, ki ga je sprejel Odbor za habitate 20. aprila 2005.
Council Regulation (EC) No 708/2007 of 11 June 2007 concerning use of alien and locally absent species in aquaculture (OJ L 168, 28.6.2007, p. 1).
Uredba Sveta (ES) št. 708/2007 z dne 11. junija 2007 o uporabi tujih in lokalno neprisotnih vrst v ribogojstvu (UL L 168, 28.6.2007, str. 1.)
See Annex IV to Regulation (EC) No 708/2007.
Glej Prilogo IV k Uredbi (ES) št. 708/2007.
See point 9 in Part A.
Glej točko 9 v delu A.
Communication ‘Implementing sustainability in EU fisheries through maximum sustainable yield’ (COM(2006) 360 final).
Sporočilo „Zagotovitev trajnosti v ribištvu EU z največjim trajnostnim donosom“, (COM(2006) 360 konč.)
See point 7 in Part A.
Glej točko 7 v delu A.
See points 3 and 4 in Part A.
Glej točki 3 in 4 v delu A.
In relation to biodiversity at the level of species, the three criteria for assessing progress towards good environmental status, as well as the indicators related respectively to them, are the following:1.1. Species distribution
Kar zadeva biotsko raznovrstnost na ravni vrst, so merila za oceno napredka pri doseganju dobrega okoljskega stanja in z njimi povezani kazalci naslednji:1.1 Razširjenost vrst
The criteria for assessing the extent to which good environmental status is being achieved are specified and numbered in Part B in relation to each of the eleven descriptors of good environmental status set out in Annex I to Directive 2008/56/EC. The criteria are accompanied by a list of related indicators to make such criteria operational and allow subsequent progress.
Merila za presojo, v kolikšni meri je bilo doseženo dobro okoljsko stanje, so za vsakega od enajstih deskriptorjev dobrega okoljskega stanja iz Priloge I k Direktivi 2008/56/ES določena in navedena v delu B. Merila spremlja seznam z njimi povezanih kazalcev, na podlagi katerih bodo ta merila pripravljena za izvajanje in bodo omogočala nadaljnji napredek.
As to the later, there are cases where it also entails an understanding of population health and inter- and intra-specific relationships. It is also necessary to assess separately subspecies and populations where the initial assessment, or new information available, identifies impacts and potential threats to the status of some of them.
Prav tako je treba opraviti ločeno presojo podvrst in populacij, kadar se na podlagi začetne presoje ali novih razpoložljivih informacij ugotovijo vplivi in morebitne grožnje za stanje nekaterih od teh vrst ali populacij.
Guidance Document on the Eutrophication Assessment in the Context of European Water Policies, Document No 23. European Commission (2009). See http://circa.europa.eu/Public/irc/env/wfd/library
Napotki za oceno evtrofikacije v okviru evropskih vodnih politik, dokument št. 23. Evropska komisija (2009): Glej http://circa.europa.eu/Public/irc/env/wfd/library
concerning the conclusion of an Agreement between the European Community and the Swiss Confederation in the audiovisual field, establishing the terms and conditions for the participation of the Swiss Confederation in the Community programme MEDIA 2007, and a Final Act
o sklenitvi Sporazuma med Evropsko skupnostjo in Švicarsko konfederacijo na avdiovizualnem področju, ki določa pogoje za sodelovanje Švicarske konfederacije v programu Skupnosti MEDIA 2007, in Sklepne listine