natgillin/translations-raw huggingface dataset:
Non-indigenous species introduced by human activities are at levels that do not adversely alter the ecosystem.
Tujerodne vrste, ki so posledica človekovih dejavnosti, so na ravneh, ki ne škodujejo ekosistemu.
The identification and assessment of pathways and vectors of spreading of non-indigenous species as a result of human activities is a prerequisite to prevent that such species introduced as a result of human activities reach levels that adversely affect the ecosystems and to mitigate any impacts.
Opredelitev in presoja poti in načinov razširjanja tujerodnih vrst, kot posledica človekove dejavnosti, iz začetne presoje, sta pogoj za preprečevanje, da bi te vrste, uvedene kot posledica človekove dejavnosti, dosegle raven razširjenosti, ki bi škodljivo vplivala na ekosisteme, in za ublažitev vseh možnih vplivov.
The initial assessment has to take into account that some introductions due to human activities are already regulated at Union level [10] to assess and minimise their possible impact on aquatic ecosystems and that some non-indigenous species have commonly been used in aquaculture for a long time and are already subject to specific permit treatment within the existing Regulations [11].
Pri začetni presoji je treba upoštevati, da je uvedba nekaterih vrst kot posledica človekove dejavnosti že urejena na ravni Unije [10], da se oceni in zmanjša njihov možen vpliv na vodne ekosisteme, ter da je uporaba nekaterih tujerodnih vrst v ribogojstvu že dalj časa običajna praksa in je v zvezi s tem že treba pridobiti dovoljenje v skladu z veljavnimi uredbami [11].
There is still only limited knowledge about the effects of the non-indigenous species on the environment.
Še vedno niso znani vsi vplivi tujerodnih vrst na okolje.
Additional scientific and technical development is required for developing potentially useful indicators [12], especially of impacts of invasive non-indigenous species (such as bio-pollution indexes), which remain the main concern for achieving good environmental status.
Potreben je dodaten znanstveni in tehnični razvoj za razvoj potencialno uporabnih kazalcev [12], zlasti v zvezi z vplivi invazivnih tujerodnih vrst (kot so indeksi biološkega onesnaženja), ki so še vedno glavna težava pri doseganju dobrega okoljskega stanja.
The priority in relation to assessment and monitoring [13] relates to state characterisation, which is a prerequisite for assessment of the magnitude of impacts but does not determine in itself the achievement of good environmental status for this descriptor.
Prednostna naloga v zvezi s presojo in spremljanjem [13] je povezana z opredelitvijo stanja, kar je pogoj za presojo obsega vplivov, vendar sama po sebi ne določa doseganja dobrega okoljskega stanja za zadevni deskriptor.
Abundance and state characterisation of non-indigenous species, in particular invasive species
Številčnost (abundanca) in opredelitev stanja tujerodnih vrst, zlasti invazivnih vrst
Trends in abundance, temporal occurrence and spatial distribution in the wild of non-indigenous species, particularly invasive non-indigenous species, notably in risk areas, in relation to the main vectors and pathways of spreading of such species (2.1.1)
Trendi glede številčnosti, časovni pojav in prostorska porazdelitev tujerodnih vrst v naravi, zlasti invazivnih tujerodnih vrst, predvsem na področjih tveganja, v zvezi z glavnimi potmi(vektorji) in načini širjenja teh vrst (2.1.1)
Environmental impact of invasive non-indigenous species
Okoljski vpliv invazivnih tujerodnih vrst
Ratio between invasive non-indigenous species and native species in some well studied taxonomic groups (e.g. fish, macroalgae, molluscs) that may provide a measure of change in species composition (e.g. further to the displacement of native species) (2.2.1)
Razmerje med invazivnimi tujerodnimi vrstami in domorodnimi vrstami v nekaterih dobro preučevanih taksonomskih skupinah (npr. ribe, makroalge in mehkužci), ki se lahko uporabi kot merilo za spremembe v vrstni sestavi (npr. ob izpodrivanju domorodnih vrst) (2.2.1)
Impacts of non-indigenous invasive species at the level of species, habitats and ecosystem, where feasible (2.2.2).
Vplivi tujerodnih invazivnih vrst na ravni vrst, habitatov in ekosistemov, ko je to izvedljivo (2.2.2).
This section applies for all the stocks covered by Regulation (EC) No 199/2008 (within the geographical scope of Directive 2008/56/EC) and similar obligations under the common fisheries policy.
Ta oddelek se uporablja za vse staleže iz Uredbe (ES) št. 199/2008 (za geografski obseg Direktive 2008/56/ES) in podobne obveznosti v okviru skupne ribiške politike.
For these and for other stocks, its application depends on the data available (taking the data collection provisions of Regulation (EC) No 199/2008 into account), which will determine the most appropriate indicators to be used.
Pri teh in drugih staležih je uporaba tega oddelka odvisna od razpoložljivih podatkov (ob upoštevanju določb o zbiranju podatkov iz Uredbe (ES) št. 199/2008), na podlagi katerih se določijo najustreznejši kazalci, ki naj bi se upoštevali.
For this descriptor, the three criteria for assessing progress towards good environmental status, as well as the indicators related respectively to them, are the following.
Za ta deskriptor so merila za oceno napredka pri doseganju dobrega okoljskega stanja in z njimi povezani kazalci naslednji:
Level of pressure of the fishing activity
Raven obremenitve ribolovne dejavnosti (Velikost ribolovnega napora)
Primary indicator.
Primarni kazalec.
The primary indicator for the level of pressure of the fishing activity is the following:
Primarni kazalec za raven pritiska ribolovne dejavnosti – ribolovnega napora je:
Fishing mortality (F) (3.1.1).
Ribolovna umrljivost (F) (3.1.1).
Achieving or maintaining good environmental status requires that F values are equal to or lower than FMSY, the level capable of producing Maximum Sustainable Yield (MSY).
Za doseganje ali ohranitev dobrega okoljskega stanja morajo biti vrednosti F enake ali manjše od vrednosti FMSY, tj. raven, na kateri se lahko doseže največji trajnostni donos (MSY).
This means that in mixed fisheries and where ecosystem interactions are important, long term management plans may result in exploiting some stocks more lightly than at FMSY levels in order not to prejudice the exploitation at FMSY of other species [14].
To pomeni, da se lahko v mešanem ribolovu in v primerih pomembnega medsebojnega vpliva ekosistemov v okviru dolgoročnih načrtov upravljanja nekateri staleži izkoriščajo na ravneh, nižjih od ravni FMSY, da bi se preprečilo poseganje v izkoriščanje drugih vrst na ravni FMSY [14].
F is estimated from appropriate analytical assessments based on the analysis of catch (to be taken as all removals from the stock, including discards and unaccounted catch) at age or at length and ancillary information.
Vrednost F se določi z ustreznimi analitičnimi ocenami, ki temeljijo na analizi ulova (tj. vse odstranitve iz staleža, vključno z zavržki in neevidentiranim ulovom) glede na starost ali dolžino in dodatnih informacijah.
Where the knowledge of the population dynamics of the stock do not allow to carry out simulations, scientific judgement of F values associated to the yield-per-recruit curve (Y/R), combined with other information on the historical performance of the fishery or on the population dynamics of similar stocks, can be used.
Če poznavanje dinamike populacije staleža ni zadostno za izvajanje simulacij, se lahko uporabi znanstvena presoja vrednosti F, povezanih s krivuljo donosa na prirast (Y/R), skupaj z drugimi informacijami o pretekli uspešnosti ribolova ali dinamiki populacije podobnih staležev.
Secondary indicators (if analytical assessments yielding values for F are not available):
Sekundarni kazalci (če niso na voljo analitične ocene, s katerimi se določijo vrednosti F):
Ratio between catch and biomass index (hereinafter ‘catch/biomass ratio’) (3.1.2).
Razmerje med ulovom in biomasnim indeksom (v nadaljnjem besedilu: razmerje ulov/biomasa (3.1.2).
The value for the indicator that reflects FMSY needs to be determined by scientific judgement following analysis of the observed historical trends of the indicator combined with other information on the historical performance of the fishery.
Vrednost kazalca, ki izraža FMSY, je treba določiti z znanstveno presojo na podlagi analize ugotovljenih preteklih trendov kazalca in drugih informacij o pretekli uspešnosti ribolova.
Where stock production-based assessments are available, the catch/biomass ratio yielding MSY can be taken as indicative reference.
Če so na voljo ocene staležev na podlagi proizvodnje, se lahko razmerje ulov/biomasa, s katerim se določi največji trajnostni donos, uporabi kot okvirna referenca.
Alternatively to the catch/biomass ratio, secondary indicators may be developed on the basis of any other appropriate proxy for fishing mortality, adequately justified.
Za razliko od razmerja ulov/biomasa se lahko sekundarni kazalci razvijejo na podlagi katerega koli drugega ustrezno utemeljenega približka za ribolovno umrljivost.
Reproductive capacity of the stock
Sposobnost razmnoževanja staleža
The primary indicator for the reproductive capacity of the stock is the following:
Primarni kazalec za sposobnost razmnoževanja staleža je:
Spawning Stock Biomass (SSB) (3.2.1).
Biomasa drstitvenega staleža (BDS)(3.2.1).
This is estimated from appropriate analytical assessments based on the analysis of catch at age or at length and ancillary information.
Ta kazalec se določi z ustreznimi analitičnimi ocenami, ki temeljijo na analizi ulova glede na starost ali dolžino in dodatnih informacijah.
Where an analytical assessment allows the estimation of SSB, the reference value reflecting full reproductive capacity is SSBMSY, i.e. the spawning stock biomass that would achieve MSY under a fishing mortality equal to FMSY.
Če omogoča analitična ocena določitev BDS, je referenčna vrednost, ki izraža polno sposobnost razmnoževanja, BDSMSY, tj. biomasa drstitvenega staleža, s katero se lahko doseže največji trajnostni donos ob ribolovni umrljivosti, ki je enaka ravni FMSY.
Any observed SSB value equal to or greater than SSBMSY is considered to meet this criterion.
Za vse ugotovljene vrednosti BDS, ki so enake ali večje od BDSMSY, se obravnava, da so v skladu s tem merilom.
Further research is needed to address the fact that a SSB corresponding to MSY may not be achieved for all stocks simultaneously due to possible interactions between them.
V zvezi z dejstvom, da BDS, ki ustreza MSY, morda ni mogoče doseči za vse staleže hkrati zaradi morebitne interakcije med njimi, so potrebne dodatne raziskave.
Where simulation models do not allow the estimation of a reliable value for SSBMSY, then the reference to be used for the purpose of this criterion is SSBpa, which is the minimum SSB value for which there is a high probability that the stock is able to replenish itself under the prevailing exploitation conditions.
Če modeli za simulacijo ne omogočajo določitve zanesljive vrednosti BDSMSY, je referenčna vrednost, ki se uporabi za namene tega merila, vrednost BDSpa, ki je najmanjša vrednost BDS, pri kateri je zelo verjetno, da se bo lahko stalež obnovil pod prevladujočimi pogoji izkoriščanja.
Secondary indicators (if analytical assessments yielding values for SSB are not available):
Sekundarni kazalci (če niso na voljo analitične ocene, s katerimi se določijo vrednosti BDS):
Biomass indices (3.2.2).
Biomasni indeksi (3.2.2).
It can be used if such indices can be obtained for the fraction of the population that is sexually mature.
Ti kazalci se lahko uporabijo, če se lahko navedeni indeksi določijo za del populacije, ki je spolno zrela.
In such cases, such indices need to be used when scientific judgement is able to determine, through detailed analysis of the historical trends of the indicator combined with other information on the historical performance of the fishery, that there is a high probability that the stock will be able to replenish itself under the prevailing exploitation conditions.
V takšnih primerih je treba navedene indekse uporabiti, kadar se z znanstveno presojo, ki temelji na podrobni analizi preteklih trendov kazalca in drugih informacij o pretekli uspešnosti ribolova, ugotovi velika verjetnost, da se bo lahko stalež obnovil pod prevladujočimi pogoji izkoriščanja.
Population age and size distribution
Razporeditev starosti in velikosti populacije
Primary indicators.
Primarni kazalci.
Healthy stocks are characterised by high proportion of old, large individuals.
Za zdrave staleže je značilna visoka stopnja preživetja starih in velikih rib.
Indicators based on the relative abundance of large fish include:
Kazalci, ki temeljijo na relativni številčnosti velikih rib, vključujejo:
Proportion of fish larger than the mean size of first sexual maturation (3.3.1)
Delež rib, ki so večje od povprečja v času, ko dosežejo spolno zrelost (3.3.1)
Mean maximum length across all species found in research vessel surveys (3.3.2)
Povprečje največjih dolžin vseh vrst, odkritih v raziskavah z raziskovalnimi plovili (3.3.2)
95 % percentile of the fish length distribution observed in research vessel surveys (3.3.3).
percentil razporeditve dolžine rib, ugotovljene v raziskavah z raziskovalnimi plovili (3.3.3)
Secondary indicator:
Sekundarni kazalec:
Size at first sexual maturation, which may reflect the extent of undesirable genetic effects of exploitation (3.3.4).
Velikost ribe, ko doseže spolno zrelost, kar lahko kaže na obseg neželenih genetskih vplivov izkoriščanja (3.3.4).
For the two sets of indicators (proportion of old fish and size at first sexual maturation), expert judgement is required for determining whether there is a high probability that the intrinsic genetic diversity of the stock will not be undermined.
Za ta dva sklopa kazalcev (delež starih rib in velikost ribe, ko doseže spolno zrelost) je potrebna strokovna presoja za določitev, ali je verjetnost, da bistvena genska raznovrstnost staleža ne bo ogrožena, velika.
The expert judgement needs to be made following an analysis of the time series available for the indicator, together with any other information on the biology of the species.
Strokovna presoja mora temeljiti na analizi časovnega razporeda, ki je na voljo za kazalec, in vseh drugih informacijah o biologiji vrst.
All elements of the marine food webs, to the extent that they are known, occur at normal abundance and diversity and levels capable of ensuring the long-term abundance of the species and the retention of their full reproductive capacity.
Vsi elementi morskih prehranjevalnih spletov so, kolikor je znano, prisotni v normalnih količinah (abundancah) in so normalno raznoliki ter se pojavljajo na ravneh, ki lahko zagotavljajo dolgoročno številčnost vrst in ohranitev njihove polne sposobnosti razmnoževanja.
This descriptor concerns important functional aspects such as energy flows and the structure of food webs (size and abundance).
Ta deskriptor se nanaša na pomembne funkcionalne vidike, kot so energijski pretoki in struktura prehranjevalnih spletov (velikost in številčnost).
Additional scientific and technical support is required, at this stage, for the further development of criteria and potentially useful indicators to address the relationships within the food web [15].
Na tej stopnji je potrebna dodatna znanstvena in tehnična podpora za nadaljnji razvoj meril in kazalcev, ki so potencialno uporabni za obravnavanje odnosov znotraj prehranjevalnih spletov [15].
Productivity (production per unit biomass) of key species or trophic groups
Produktivnost (proizvodnja na enoto biomase) ključnih vrst ali trofičnih skupin
To address energy flows in food webs, adequate indicators need to be developed further to assess the performance of the main predator-prey processes, reflecting the long-term viability of components in the part of the food web that they inhabit, based on the experience in some sub-regions in selecting appropriate species (e.g. mammals, seabirds).
Za obravnavanje energijskih pretokov v prehranjevalnih spletih je treba nadalje razviti ustrezne kazalce, da se oceni uspešnost glavnih procesov med plenilcem in plenom, ki izraža dolgoročno sposobnost preživetja sestavnih delov v delu prehranjevalnega spleta, ki ga naseljujejo, na podlagi izkušenj v nekaterih podregijah pri izboru ustreznih vrst (npr. sesalci, morske ptice).
Performance of key predator species using their production per unit biomass (productivity) (4.1.1).
Uspešnost ključnih plenilskih vrst, pri čemer se uporabi njihova proizvodnja na enoto biomase (produktivnost) (4.1.1).
Proportion of selected species at the top of food webs
Delež izbranih vrst na vrhu prehranjevalnih spletov
To address the structure of food webs, size and abundance of components, there is a need to assess the proportion of selected species at the top of food webs.
Za obravnavanje strukture prehranjevalnih spletov ter velikosti in številčnosti sestavnih delov je treba oceniti delež izbranih vrst na vrhu prehranjevalnih spletov.
Indicators need to be further developed, based on the experience in some sub-regions.
Na podlagi izkušenj v nekaterih podregijah je treba nadalje razviti kazalce.
For large fish, data are available from fish monitoring surveys.
Za velike ribe so na voljo podatki iz raziskav za spremljanje rib.
Large fish (by weight) (4.2.1).
Velike ribe (glede na težo) (4.2.1).
Abundance/distribution of key trophic groups/species
Številčnost/razporeditev ključnih trofičnih skupin/vrst
Abundance trends of functionally important selected groups/species (4.3.1).
Trendi številčnosti funkcionalno pomembnih izbranih skupin/vrst (4.3.1).
It is necessary to identify changes in population status potentially affecting food web structure.
Opredeliti je treba spremembe stanja populacije, ki bi lahko vplivale na strukturo prehranjevalnega spleta.
Detailed indicators need to be further specified, taking account of their importance to the food webs, on the basis of suitable groups/species in a region, sub-region or subdivision, including where appropriate:
Podrobne kazalce je treba dodatno določiti, pri čemer se upošteva njihov pomen za njihove prehranjevalne splete, na podlagi ustreznih skupin/vrst v regiji, podregiji ali pododdelku, po potrebi vključno s:
groups with fast turnover rates (e.g. phytoplankton, zooplankton, jellyfish, bivalve molluscs, short-living pelagic fish) that will respond quickly to ecosystem change and are useful as early warning indicators,
skupinami, ki se hitro obnavljajo (npr. fitoplankton, zooplankton, meduze, školjke, kratkoživeče pelagične ribe) in se bodo hitro odzvale na spremembo ekosistema, zaradi česar se lahko uporabijo kot kazalci za zgodnje opozarjanje,
groups/species that are targeted by human activities or that are indirectly affected by them (in particular, by-catch and discards),
skupinami/vrstami, v katere so usmerjene človekove dejavnosti ali na katere te dejavnosti posredno vplivajo (zlasti prilov in zavržki),
habitat-defining groups/species,
skupinami/vrstami, ki opredeljujejo habitat,
groups/species at the top of the food web,
skupinami/vrstami na vrhu prehranjevalnega spleta,
long-distance anadromous and catadromous migrating species,
anadromnimi in katadromnimi vrstami, ki se selijo na velike razdalje,
groups/species that are tightly linked to specific groups/species at another trophic level.
skupinami/vrstami, ki so tesno povezane s posebnimi skupinami/vrstami na drugi trofični ravni.
Human-induced eutrophication is minimised, especially adverse effects thereof, such as losses in biodiversity, ecosystem degradation, harmful algal blooms and oxygen deficiency in bottom waters.
Evtrofikacija, ki jo povzroči človek, in zlasti njeni škodljivi učinki, kot so upad biotske raznovrstnosti, degradacija ekosistemov, škodljivo cvetenje alg in pomanjkanje kisika v spodnjih plasteh voda, so minimalni.
The assessment of eutrophication in marine waters needs to take into account the assessment for coastal and transitional waters under Directive 2000/60/EC (Annex V, 1.2.3 and 1.2.4) and related guidance [16], in a way which ensures comparability, taking also into consideration the information and knowledge gathered and approaches developed in the framework of regional sea conventions.
Ocena evtrofikacije v morskih vodah mora z zagotavljanjem primerljivosti upoštevati oceno za obalne vode in smernice v skladu z Direktivo 2000/60/ES (odstavka 1.2.3 in 1.2.4 Priloge V) in povezana vodila [16], pri čemer se upoštevajo tudi informacije, znanje in pristopi, pridobljeni v okviru regionalnih konvencij o morjih.
Based on a screening procedure as part of the initial assessment, risk-based considerations may be taken into account to assess eutrophication in an efficient manner [17].
Na podlagi postopka preverjanja, ki se izvede kot del začetne presoje, se za učinkovito oceno evtrofikacije lahko upoštevajo premisleki na podlagi tveganja [17].
The assessment needs to combine information on nutrient levels and on a range of those primary effects and of secondary effects which are ecologically relevant [18], taking into account relevant temporal scales.
Ocena mora združevati informacije o vsebnosti hranilnih snovi ter o različnih, ekološko pomembnih [18], primarnih in sekundarnih vplivih, pri čemer se upoštevajo ustrezni časovni razponi.
Considering that the concentration of nutrients is related to nutrient loads from rivers in the catchment area, cooperation with landlocked Member States using established cooperation structures in accordance with the third subparagraph of Article 6(2) of Directive 2008/56/EC is particularly relevant.
Ker je koncentracija hranilnih snovi povezana z obogatitvijo vode s hranilnimi snovmi iz rek na prispevnem območju, je zlasti pomembno sodelovanje z neobalnimi državami članicami po ustaljenih strukturah sodelovanja v skladu s tretjim pododstavkom člena 6(2) Direktive 2008/56/ES.
Nutrients levels
Vsebnost hranilnih snovi
Nutrients concentration in the water column (5.1.1)
Koncentracija hranilnih snovi v vodnem stolpu (5.1.1)
Nutrient ratios (silica, nitrogen and phosphorus), where appropriate (5.1.2)
Deleži hranilnih snovi (silicij, dušik in fosfor), kadar je to potrebno (5.1.2)
Direct effects of nutrient enrichment
Neposredni vplivi obogatitve s hranilnimi snovmi (evtrofikacije)
Chlorophyll concentration in the water column (5.2.1)
Koncentracija klorofila v vodnem stolpu (5.2.1)
Water transparency related to increase in suspended algae, where relevant (5.2.2)
Bistrost vode, v povezavi s povečanjem števila lebdečih alg, kadar je to smotrno (5.2.2)
Abundance of opportunistic macroalgae (5.2.3)
Številčnost oportunističnih makroalg (5.2.3)
Species shift in floristic composition such as diatom to flagellate ratio, benthic to pelagic shifts, as well as bloom events of nuisance/toxic algal blooms (e.g. cyanobacteria) caused by human activities (5.2.4)
Sprememba vrst v rastlinski sestavi, npr. razmerje med kremenastimi in bičkastimi algami, spremembe iz bentoških v pelagične vrste ter cvetenje škodljivih/strupenih alg (npr. cianobakterija), ki jo povzročijo človekove dejavnosti (5.2.4)
Indirect effects of nutrient enrichment
Posredni vplivi obogatitve s hranilnimi snovmi (evtrofikacije)
Abundance of perennial seaweeds and seagrasses (e.g. fucoids, eelgrass and Neptune grass) adversely impacted by decrease in water transparency (5.3.1)
Številčnost večletnih morskih alg in trav (npr. alge iz reda Fucales, prava morska trava in neptunska trava), na katero škodljivo vpliva zmanjšanje bistrosti vode (5.3.1)
Dissolved oxygen, i.e. changes due to increased organic matter decomposition and size of the area concerned (5.3.2).
Raztopljen kisik, tj. spremembe zaradi povečane organske razgradnje in velikosti zadevnega območja (5.3.2).
Sea-floor integrity is at a level that ensures that the structure and functions of the ecosystems are safeguarded and benthic ecosystems, in particular, are not adversely affected.
Neoporečnost morskega dna je na ravni, ki zagotavlja zaščito strukture in funkcije ekosistemov ter preprečuje škodljive vplive zlasti na bentoške ekosisteme.