natgillin/translations-raw huggingface dataset:
This grant and these resources shall be taken from the funds allocated to the programmes referred to in Article 4(1) and, if necessary, from the funds allocated to other Community programmes the implementation of which has been entrusted to the Agency pursuant to Article 4(3).
Ta subvencija in sredstva se črpajo iz finančnih sredstev, dodeljenih zadevnim programom iz člena 4(1) in po potrebi iz sredstev drugih programov Skupnosti, ki jih izvaja agencija v skladu s členom 4(3).
The Agency shall be subject to supervision by the Commission and shall report regularly on progress in implementing the programmes for which it is responsible in accordance with the arrangements and at the intervals stipulated in the instrument of delegation.
Agencija je pod nadzorom Komisije in mora redno poročati o izvajanju programov, ki so ji dodeljeni, na način in tako pogosto, kakor je določeno v aktu o prenosu pooblastil.
Decision 2005/56/EC is hereby repealed.
Sklep 2005/56/ES se razveljavi.
References to the repealed Decision shall be construed as references to this Decision.
Sklicevanja na razveljavljeni sklep se razumejo kot sklicevanja na ta sklep.
OJ L 405, 30.12.2006, p. 41; corrected by OJ L 29, 3.2.2007, p. 16.
UL L 405, 30.12.2006, str. 41; popravljena različica v UL L 29, 3.2.2007, str. 16.
OJ L 65, 8.3.2003, p. 27.
UL L 65, 8.3.2003, str. 27.
on the definition of the criteria for the classification of waste facilities in accordance with Annex III of Directive 2006/21/EC of the European Parliament and of the Council concerning the management of waste from extractive industries
o opredelitvi meril za klasifikacijo objektov za ravnanje z odpadki v skladu s Prilogo III k Direktivi 2006/21/ES Evropskega parlamenta in Sveta o ravnanju z odpadki iz rudarskih in drugih ekstraktivnih dejavnosti
(notified under document number C(2009) 2856)
(notificirano pod dokumentarno številko C(2009) 2856)
Having regard to Directive 2006/21/EC of the European Parliament and of the Council of 15 March 2006 on the management of waste from extractive industries and amending Directive 2004/35/EC [1], and in particular Article 22(1)(g) thereof,
ob upoštevanju Direktive 2006/21/ES Evropskega parlamenta in Sveta z dne 15. marca 2006 o ravnanju z odpadki iz rudarskih in drugih ekstraktivnih dejavnosti ter o spremembi Direktive 2004/35/ES [1] in zlasti člena 22(1)(g) Direktive,
In order to ensure a common assessment of the criteria set out in Annex III to Directive 2006/21/EC, it is necessary to define a methodology and, where possible, to fix limit values, taking into account the different types of waste facilities, their behaviour in the short and long term as well as throughout their operating phase.
Za zagotovitev skupne ocene meril iz Priloge III k Direktivi 2006/21/ES je treba opredeliti metodologijo in, kadar je to mogoče, določiti mejne vrednosti, pri čemer je treba upoštevati različne vrste objektov za ravnanje z odpadki, njihovo kratko- in dolgoročno obnašanje ter tudi obnašanje med obratovanjem.
It is appropriate from a technical point of view to exempt waste facilities containing only inert waste or unpolluted soil from the assessment of the criteria concerning the presence of dangerous substances or hazardous waste.
S tehničnega vidika je objekte za ravnanje z odpadki, ki vsebujejo samo inertne odpadke ali neonesnažena tla, primerno izvzeti iz ocene meril, ki zadevajo prisotnost nevarnih snovi ali nevarnih odpadkov.
The potential hazard posed by a waste facility may change significantly during the operational and closure phases of the facility.
Potencialna nevarnost, ki jo predstavlja objekt za ravnanje z odpadki, se lahko znatno spremeni med obratovanjem in fazo zaprtja objekta.
Therefore, it is appropriate to review the classification of the facility as necessary and at least at the end of the operational phase.
Zato je primerno, da se klasifikacija objekta pregleda po potrebi ali vsaj ob zaključku obratovanja.
In order to assess the potential for loss of life and danger for human health in cases of loss of structural integrity, or incorrect operation, of a facility, the actual permanent presence of people in the potentially affected areas should be taken into account when assessing the significance of that potential loss of life or danger for human health.
Za oceno potencialne nevarnosti za življenje in zdravje ljudi v primerih izgube strukturne neoporečnosti ali nepravilnega obratovanja objekta je treba upoštevati dejansko stalno prisotnost ljudi na območjih, ki bi lahko bila prizadeta, kadar se ocenjuje resnost te potencialne nevarnosti za življenje ali zdravje ljudi.
A waste facility shall be classified under Category A in accordance with the first indent of Annex III of Directive 2006/21/EC if the predicted consequences in the short or the long term of a failure due to loss of structural integrity, or due to incorrect operation of a waste facility could lead to:
Objekt za ravnanje z odpadki spada v kategorijo A v skladu s prvo alineo Priloge III k Direktivi 2006/21/ES, če bi predvidene kratko- ali dolgoročne posledice okvare zaradi izgube strukturne neoporečnosti ali nepravilnega obratovanja objekta za ravnanje z odpadki lahko povzročile:
non-negligible potential for loss of life;
nezanemarljivo potencialno nevarnost za življenje;
serious danger to human health;
resno nevarnost za zdravje ljudi;
serious danger to the environment.
resno nevarnost za okolje.
For the purpose of the classification referred to in paragraph 1, the entire life-cycle of the facility, including the after-closure phase, shall be considered in the evaluation of the hazard potential of the facility.
Za namene klasifikacije iz odstavka 1 se pri vrednotenju nevarnostnega potenciala objekta upošteva celotni življenjski krog objekta, vključno s fazo po zaprtju.
For the purpose of this Decision, structural integrity of a waste facility shall mean its ability to contain the waste within the boundaries of the facility in the manner for which it was designed.
V tej odločbi strukturna neoporečnost objekta za ravnanje z odpadki pomeni njegovo sposobnost zadržanja odpadkov znotraj meja objekta na način, ki je bil predviden v njegovem načrtu.
The loss of structural integrity shall cover all possible failure mechanisms relevant to the structures of the waste facility concerned.
Izguba strukturne neoporečnosti zajema vse možne mehanizme okvare, ki se nanašajo na strukture zadevnega objekta za ravnanje z odpadki.
An evaluation of the consequences of the loss of structural integrity shall comprise the immediate impact of any material transported from the facility as a consequence of the failure and the resulting short and long term effects.
Vrednotenje posledic izgube strukturne neoporečnosti vključuje takojšnji vpliv katerega koli materiala, ki se prevaža z objekta zaradi okvare, ter posledične kratko- in dolgoročne učinke.
For the purpose of this Decision, incorrect operation of the waste facility shall mean any operation which may give rise to a major accident, including the malfunction of environmental protection measures and faulty or insufficient design.
V tej odločbi nepravilno obratovanje objekta za ravnanje z odpadki pomeni vsako obratovanje, ki lahko povzroči večjo nesrečo, vključno s slabim delovanjem ukrepov za varstvo okolja ter nestrokovnim ali pomanjkljivim načrtovanjem.
An assessment of the release of contaminants resulting from incorrect operation shall comprise the effects of short-term pulses as well as of the long-term release of contaminants.
Ocena izpusta onesnaževal zaradi nepravilnega obratovanja vključuje učinke kratkoročnih velikih koncentracij ter tudi dolgoročnega izpusta onesnaževal.
That assessment shall cover the operational period of the facility and as well as the long-term period following closure.
Navedena ocena zajema obratovalno obdobje objekta ter dolgoročno obdobje po njegovem zaprtju.
It shall include an evaluation of the potential hazards constituted by facilities containing reactive waste, regardless of the classification of the waste as hazardous or non-hazardous under Council Directive 91/689/EEC [3].
Vključuje vrednotenje potencialnih nevarnosti objektov, v katerih so reaktivni odpadki, ne glede na razvrščanje odpadkov med nevarne ali nenevarne odpadke na podlagi Direktive Sveta 91/689/EGS [3].
Member States shall assess the consequences of a failure due to loss of structural integrity or incorrect operation of a waste facility in accordance with paragraphs 2, 3 and 4.
Države članice ocenijo posledice okvare zaradi izgube strukturne neoporečnosti ali nepravilnega obratovanja objekta za ravnanje z odpadki v skladu z odstavki 2, 3 in 4.
The potential for loss of life or danger to human health shall be considered to be negligible or not serious if people other than workers operating the facility that might be affected are not expected to be present permanently or for prolonged periods in the potentially affected area.
Potencialna nevarnost za življenje ali zdravje ljudi se šteje za zanemarljivo ali neresno, če se razen zaposlenih, ki upravljajo objekt in ki bi lahko bili prizadeti, ne pričakuje stalna ali daljša prisotnost ljudi na območju, ki bi lahko bilo prizadeto.
Injuries leading to disability or prolonged states of ill-health shall count as serious dangers to human health.
Za poškodbe, ki povzročajo invalidnost ali daljša obdobja bolezni, se šteje, da pomenijo resno nevarnost za zdravje ljudi.
The potential danger for the environment shall be considered to be not serious if:
Potencialna nevarnost za okolje se ne šteje za resno, če:
the intensity of the potential contaminant source strength is decreasing significantly within a short time;
se intenzivnost moči potencialnega vira onesnaževanja v kratkem času znatno zmanjša;
the failure does not lead to any permanent or long-lasting environmental damage;
okvara ne povzroči trajne ali dolgoročne okoljske škode;
the affected environment can be restored through minor clean-up and restoration efforts.
se prizadeto okolje lahko povrne v prejšnje stanje z manjšimi ukrepi čiščenja in sanacije;
In establishing the potential for loss of life or danger to human health or to the environment, the specific evaluations of the extent of the potential impacts shall be considered in the context of the source-pathway-receptor chain.
Pri določitvi potencialne nevarnosti za življenje ali zdravje ljudi ali za okolje je treba v okviru koncepta „vir-pot-prejemnik“ upoštevati posebno vrednotenje obsega potencialnih učinkov.
Where there is no pathway between the source and the receptor, the facility concerned shall not be classified as Category A on the basis of failure due to loss of structural integrity or incorrect operation.
Kadar med virom in prejemnikom ni poti, objekt ne spada v kategorijo A na podlagi okvare zaradi izgube strukturne neoporečnosti ali nepravilnega obratovanja.
In the case of loss of structural integrity for tailings dams, human lives shall be deemed to be threatened where water or slurry levels are at least 0,7 m above ground or where water or slurry velocities exceed 0,5 m/s.
V primeru izgube strukturne neoporečnosti pregrad za zadrževanje jalovine se šteje, da so življenja ljudi ogrožena, kadar je nivo vode ali mulja najmanj 0,7 m nad tlemi oziroma kadar hitrost vode ali mulja presega 0,5 m/s.
The assessment of the potential for loss of life and danger to human health, shall comprise at least the following factors:
Ocena potencialne nevarnosti za življenje in zdravje ljudi vključuje vsaj naslednje dejavnike:
the size and properties of the facility including its design;
velikost in lastnosti objekta, vključno z njegovim načrtovanjem;
the quantity and quality including physical and chemical properties of the waste in the facility;
količino in kakovost, vključno s fizikalnimi in kemičnimi lastnostmi odpadkov v objektu;
the topography of the facility site, including damping features;
topografijo lokacije objekta, vključno z lastnostmi dušenja;
the travel time of a potential flood-wave to areas where people are present;
čas potovanja potencialnega poplavnega vala do območij, na katerih so prisotni ljudje;
the propagation velocity of the flood-wave;
hitrost širjenja poplavnega vala;
the predicted water or slurry level;
predvideni nivo vode ali mulja;
the rising rate of water or slurry levels;
stopnjo dvigovanja nivoja vode ali mulja;
any relevant, site-specific factors that may influence the potential for loss- of- life or for danger to human health.
vse pomembne dejavnike, ki so vezani na lokacijo in bi lahko vplivali na potencialno nevarnost za življenje ali zdravje ljudi.
In the case of waste heap slides any waste-mass in movement shall be deemed likely to threaten human lives if people are staying within range of the moving waste-mass.
V primeru plazenja jalovišča se za vsako maso odpadkov, ki se premika, šteje, da lahko ogrozi življenja ljudi, če se ljudje nahajajo v območju premikajoče se mase odpadkov.
The assessment of the potential for loss of life and danger to human health shall comprise at least the following factors:
Ocena potencialne nevarnosti za življenje in zdravje ljudi vključuje vsaj naslednje dejavnike:
slope angle of heap;
kot brežine jalovišča;
potential to build up internal groundwater within the heap;
možnost zbiranja podzemne vode v jalovišču;
underground stability;
stabilnost nosilnih tal;
topography;
topografijo;
proximity to water courses, constructions, buildings;
bližino vodotokov, gradbišč, zgradb;
mine workings;
rudarska dela;
any other site-specific factors that may significantly contribute to the risk posed by the structure.
vse ostale dejavnike, ki so vezani na lokacijo in bi lahko znatno prispevali k tveganju, ki ga predstavlja struktura.
The threshold referred to in the second indent of Annex III of Directive 2006/21/EC shall be determined, as the ratio of the weight on a dry matter basis of:
Mejna vednost iz druge alinee Priloge III k Direktivi 2006/21/ES se določi kot razmerje med težo na podlagi suhe snovi:
all waste classified as hazardous in accordance with Directive 91/689/EEC and expected to be present in the facility at the end of the planned period of operation, and
vseh odpadkov, ki veljajo za nevarne v skladu z Direktivo 91/689/EGS in za katere se pričakuje, da bodo prisotni v objektu ob koncu načrtovanega obdobja obratovanja, in
waste expected to be present in the facility at the end of the planned period of operation.
odpadkov, za katere se pričakuje, da bodo prisotni v objektu ob koncu načrtovanega obdobja obratovanja.
Where the ratio referred to in paragraph 1 exceeds 50 %, the facility shall be classified as Category A.
Kadar razmerje iz odstavka 1 presega 50 %, spada objekt v kategorijo A.
Where the ratio referred to paragraph 1 is between 5 % and 50 %, the facility shall be classified as Category A.
Kadar je razmerje iz odstavka 1 med 5 % in 50 %, spada objekt v kategorijo A.
However, that facility may not be classified as Category A where it is justified on the basis of a site specific risk assessment, with specific focus on the effects of the hazardous waste, carried out as part of the classification based on the consequences of failure due to loss of integrity or incorrect operation, and demonstrating that the facility should not be classified as Category A on the basis of the contents of hazardous waste.
Vendar je mogoče, da navedeni objekt ne spada v kategorijo A, kadar je upravičen na podlagi ocene tveganja, vezane na lokacijo, s posebnim poudarkom na učinkih nevarnih odpadkov, ki je bila opravljena kot del klasifikacije na podlagi posledic okvare zaradi izgube neoporečnosti ali nepravilnega obratovanja, ter je dokazano, da objekt ne spada v kategorijo A na podlagi vsebine nevarnih odpadkov.
Where the ratio referred in paragraph 1 is less than 5 %, then the facility shall not be classified as Category A on the basis of the contents of hazardous waste.
Kadar je razmerje iz odstavka 1 manjše od 5 %, objekt ne spada v kategorijo A na podlagi vsebine nevarnih odpadkov.
Member States shall assess whether the criterion set out in the third indent of Annex III of Directive 2006/21/EC is met in accordance with the considerations set out in paragraphs 2, 3, and 4.
Države članice ocenijo, ali je merilo iz tretje alinee Priloge III k Direktivi 2006/21/ES izpolnjeno v skladu s premisleki iz odstavkov 2, 3 in 4.
For planned tailing ponds, the following methodology shall be used:
Za načrtovane usedalne bazene jalovine se uporablja naslednja metodologija:
an inventory shall be carried out of the substances and preparations which are used in the processing and which are subsequently discharged with the tailings slurry to the tailings pond;
opravi se popis snovi in pripravkov, ki se uporabljajo pri predelavi in se nato skupaj z jalovino v obliki mulja odvedejo v usedalni bazen jalovine;
for each substance and preparation, the yearly quantities used in the process shall be estimated out for each year of the planned duration of operation;
za vsako snov in pripravek se za vsako leto načrtovanega trajanja obratovanja ocenijo letne količine, ki se uporabijo v procesu;
for each substance and preparation, it shall be determined whether it is a dangerous substance or preparation within the meaning of Council Directive 67/548/EEC [4] and of Directive 1999/45/EC of the European Parliament and of the Council [5];
za vsako snov in pripravek se ugotovi, ali gre za nevarno snov ali pripravek v smislu Direktive Sveta 67/548/EGS [4] in Direktive 1999/45/ES Evropskega parlamenta in Sveta [5];
for each year of planned operation, the yearly increase in stored water (ΔQi) within the tailings pond shall be calculated under steady state conditions according to the formula set out in Annex I;
za vsako leto načrtovanega obratovanja se izračuna letno povečanje skladiščene vode (ΔQi) v usedalnih bazenih jalovine v stabilnih pogojih v skladu z enačbo iz Priloge I;
for each dangerous substance or preparation identified in accordance with point (c), the maximum yearly concentration (C max) in the aqueous phase shall be estimated according to the formula set out in Annex II.
za vsako nevarno snov ali pripravek, ugotovljen v skladu s točko (c), se oceni največja letna koncentracija (C max) v vodni fazi v skladu s formulo iz Priloge II.
If, on the basis of the estimation of the maximum yearly concentrations (C max), the aqueous phase is considered to be ‘dangerous’ within the meaning of Directives 1999/45/EC or 67/548/EEC, the facility shall be classified as a Category A facility.
Če se na podlagi ocene največjih letnih koncentracij (C max) šteje, da je vodna faza „nevarna“ v smislu Direktive 1999/45/ES ali Direktive 67/548/EGS, spada objekt v kategorijo A.
For operating tailings ponds, the classification of the facility shall be based on the methodology set out in paragraph 2, or on direct chemical analysis of the water and solids contained in the facility.
Za delujoče usedalne bazene jalovine klasifikacija objekta temelji na metodologiji iz odstavka 2 ali na neposredni kemični analizi vode in trdnih snovi, ki so prisotne v objektu.
If the aqueous phase and its contents have to be considered as dangerous preparation within the meaning of Directive 1999/45/EC or 67/548/EEC, the facility shall be classified as a Category A facility.
Če se morajo vodna faza in njena vsebina šteti za nevaren pripravek v smislu Direktive 1999/45/ES ali Direktive 67/548/EGS, spada objekt v kategorijo A.
For heap leaching facilities, where metals are extracted from ore heaps by percolating leach solutions, Member States shall undertake a screening for dangerous substances at closure based on an inventory of used leach chemicals and the residual concentrations of these leach chemicals in the drainage after washing has been finalised.
Za objekte za izluževanje, kjer se kovine pridobivajo iz jalovišč rude s filtriranjem izluženih raztopin, države članice ob zaprtju opravijo pregled nevarnih snovi, ki temelji na popisu uporabljenih kemikalij za izluževanje in koncentracijah ostankov teh kemikalij v drenažni vodi po zaključku izpiranja.
If these leachates have to be considered as dangerous preparation within the meaning of Directives 1999/45/EC or 67/548/EEC, the facility shall be classified as a Category A facility.
Če se morajo te izcedne vode šteti za nevaren pripravek v smislu Direktive 1999/45/ES ali Direktive 67/548/EGS, spada objekt v kategorijo A.
Article 7 and 8 of this Decision shall not apply to waste facilities containing inert waste or unpolluted soil only.
Člena 7 in 8 te odločbe se ne uporabljata za objekte za ravnanje z odpadki, ki vsebujejo samo inertne odpadke ali neonesnažena tla.
A review of the classification shall be carried out by the competent authority within the meaning of Directive 2006/21/EC where the permit is substantially modified or the operational conditions have changed significantly.
Pregled klasifikacije mora opraviti pristojni organ v skladu z Direktivo 2006/21/ES, kadar se je dovoljenje bistveno spremenilo ali so pogoji obratovanja bistveno drugačni.
That review shall be carried out at the latest at the end of the operational period of the facility.
Pregled se opravi najpozneje ob koncu obratovanja objekta.
Formula for the calculation of the average yearly increase in stored water within the tailings pond ΔQ as referred in Article 8 paragraph 2
Enačba za izračun povprečnega letnega povečanja skladiščene vode v usedalnem bazenu jalovine ΔQ iz člena 8(2)
ΔQi (ΔΜi/D) * P, where:
ΔQi (ΔΜi/D) * P, pri čemer je:
ΔQi yearly increase of stored water in the tailing pond (m3/year) during the year ‘i’
ΔQi letno povečanje skladiščene vode v usedalnem bazenu jalovine (v m3/leto) v letu „i“,
ΔΜi yearly mass of tailings discharged to pond (tonnes dry weight/year) during the year ‘i’
ΔΜi letna masa jalovine, ki se odvede v usedalni bazen (v tonah suhe teže/leto) v letu „i“,
D average dry bulk density of the deposited tailings (tonnes/m3)
D povprečna specifična masa odložene jalovine v suhem stanju (v tonah/m3),
P average porosity of the sedimented tailings (m3/m3) defined as the ratio of the volume of voids to the total volume of sedimented tailings
P povprečna poroznost usedlin jalovine (v m3/m3), opredeljena kot razmerje med prostornino odkopanega prostora in skupno prostornino usedlin jalovine.
If exact data are not available, default values of 1,4 tonnes/m3 for the dry bulk density and 0,5 m3/m3 for the porosity should be used.
Če točni podatki niso na voljo, je treba uporabiti privzete vrednosti v višini 1,4 tone/m3 za specifično maso v suhem stanju in 0,5 m3/m3 za poroznost.
Estimation of the maximum concentration in the aqueous phase C max as referred in Article 8 paragraph 2
Ocena največje koncentracije v vodni fazi C max iz člena 8(2)
C max = the maximum of the following value: Si/ΔQi, where:
C max = največja vrednost naslednjega: Si/ΔQi, pri čemer je:
Si = yearly mass of each substance and preparation as identified under Article 8(2)(c), discharged into the pond during the year ‘i’.
Si = letna masa vsake snovi in pripravka, kot sta opredeljena v členu 8(2)(c), ki se odvede v usedalni bazen v letu „i“.
amending Decision 2007/589/EC as regards the inclusion of monitoring and reporting guidelines for emissions and tonne-kilometre data from aviation activities
o spremembi Odločbe 2007/589/ES glede vključitve smernic za spremljanje in sporočanje emisij in podatkov o tonskih kilometrih iz letalskih dejavnosti
(notified under document number C(2009) 2887)
(notificirano pod dokumentarno številko C(2009) 2887)
Having regard to Directive 2003/87/EC of the European Parliament and of the Council of 13 October 2003 establishing a scheme for greenhouse gas emission allowance trading within the Community and amending Council Directive 96/61/EC [1], and in particular Article 14(1) thereof,
ob upoštevanju Direktive 2003/87/ES Evropskega parlamenta in Sveta z dne 13. oktobra 2003 o vzpostavitvi sistema za trgovanje s pravicami do emisije toplogrednih plinov v Skupnosti in o spremembi Direktive Sveta 96/61/ES [1] ter zlasti člena 14(1) Direktive,