natgillin/translations-raw huggingface dataset:
Lisaks peaks veereostuse minimeerimiseks olema jäätmete ladustamine igasse suublasse kooskõlas Euroopa Parlamendi ja nõukogu 23.oktoobri 2000.aasta direktiiviga 2000/60/EÜ, millega kehtestatakse ühenduse veepoliitika alane tegevusraamistik .
In addition, for the purposes of minimising water pollution, the discharge of waste into any receiving body of water should comply with Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy.
Lisaks sellele tuleks hiivahoidlate tsüaniidi ja tsüaniidühendite kontsentratsioone teatavat liiki kaevandustes nende kahjuliku ja mürgise mõju tõttu alandada madalaima võimaliku tasemeni, kasutades parimat olemasolevat tehnikat.
Furthermore, concentrations in tailings ponds of cyanide and cyanide compounds from certain extractive industries should, in view of their harmful and toxic effects, be reduced to the lowest possible levels, using best available techniques.
Kontsentratsioonide jaoks tuleks vastavalt ja igal juhul kooskõlas käesoleva direktiivi erinõuetega kehtestada maksimummäärad, et selliseid mõjusid vältida.
Maximum concentration thresholds should be set accordingly and, in any case, in line with the specific requirements of this Directive to prevent such effects.
Lisaks peaks veereostuse minimeerimiseks olema jäätmete ladustamine igasse suublasse keelatud, välja arvatud juhul, kui eelnevalt on tõendatud, et tegevus on kooskõlas Euroopa Parlamendi ja nõukogu 23. oktoobri 2000. aasta direktiiviga 2000/60/EÜ, millega kehtestatakse ühenduse veepoliitika tegevusraamistik .
In addition, for the purposes of minimising water pollution, the discharge of waste into any receiving body of water should be prohibited unless it is demonstrated a priori to comply with Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy.
Lisaks sellele tuleks hiivahoidlate tsüaniidi ja tsüaniidühendite sisaldust teatavat liiki kaevandustes nende kahjuliku ja mürgise mõju tõttu alandada madalaima võimaliku tasemeni, kasutades parimat olemasolevat tehnikat.
Furthermore, concentrations in tailings ponds of cyanide and cyanide compounds from certain extractive industries should, in view of their harmful and toxic effects, be reduced to the lowest possible levels, using best available techniques.
Change needed for coherence with Article 13, paragraph 4.
Change needed for coherence with Article 13, paragraph 4.
The Directive allows direct discharges of waste from the extractive industries to continental, coastal and marine waters.
The Directive allows direct discharges of waste from the extractive industries to continental, coastal and marine waters.
However, these must be explicitly prohibited in line with obligations from the Treaty (e.g. prevention of damage at source); from existing Community environmental legislation (e.g. the Waste and the Water Framework Directives); and from Annex II to the OSPAR Convention.
However, these must be explicitly prohibited in line with obligations from the Treaty (e.g. prevention of damage at source); from existing Community environmental legislation (e.g. the Waste and the Water Framework Directives); and from Annex II to the OSPAR Convention.
Further, compliance with the Water Framework Directive should not be ensured a posteriori but a priori by preventing "deterioration".
Further, compliance with the Water Framework Directive should not be ensured a posteriori but a priori by preventing "deterioration".
PÕHJENDUS 26
RECITAL 26
26) Kaevandustööstuse jäätmeid vastuvõtva jäätmehoidla käitaja peaks olema kohustatud esitama liikmesriikide poolt kindlaksmääratavas korras rahalise tagatise või muu samaväärse tagatise, et tagada kõikide loast tulenevate kohustuste täitmine, sealhulgas nende kohustuste täitmine, mis on seotud sulgemise ja hoidla järelhooldusega.
(26) The operator of a waste facility servicing the extractive industries should be required to lodge a financial guarantee or equivalent in accordance with procedures to be decided by the Member States ensuring that all the obligations flowing from the permit will be fulfilled, including those relating to the closure and after-closure of the site.
Rahaline tagatis peaks olema piisav, et maksta hoidla korrastamise eest, mille teeb kvalifitseeritud ja sõltumatu kolmas isik.
The financial guarantee should be sufficient to cover the cost of rehabilitation of the site by a suitably qualified and independent third party.
Selline tagatis tuleb esitada enne, kui jäätmeid hakatakse jäätmehoidlasse ladustama, ning tagatise suurust tuleb korrapäraselt kohandada.
It is also necessary for such a guarantee to be provided prior to the commencement of deposition operations in the waste facility and to be periodically adjusted.
Lisaks on kooskõlas põhimõttega “saastaja maksab” ning vastavalt Euroopa Parlamendi ja nõukogu 21.aprilli 2004.aasta direktiivile 2004/35/EÜ keskkonnavastutusest keskkonnakahjustuste ärahoidmise ja parandamise kohta oluline selgitada, et kaevandustööstuse jäätmeid vastuvõtva jäätmehoidla käitaja vastutab asjakohaselt oma tegevusest tuleneva keskkonnakahju eest või sellise kahju tekkimise ohu eest.
In addition, in accordance with the polluter pays principle and with Directive 2004/35/EC of the European Parliament and of the Council of 21 April 2004 on environmental liability with regard to the prevention and remedying of environmental damage, it is important to clarify that an operator of a waste facility servicing the extractive industries is subject to appropriate liability in respect of environmental damage caused by its operations or the imminent threat of such damage.
26) Kaevandustööstuse jäätmeid vastu võtva jäätmehoidla käitaja peaks olema kohustatud esitama liikmesriikide poolt kindlaks määratavas korras rahalise tagatise või muu samaväärse tagatise, et tagada kõikide loast tulenevate kohustuste täitmine, sealhulgas nende kohustuste täitmine, mis on seotud sulgemise ja hoidla järelhooldusega.
(26) The operator of a waste facility servicing the extractive industries should be required to lodge a financial guarantee or equivalent in accordance with procedures to be decided by the Member States ensuring that all the obligations flowing from the permit will be fulfilled, including those relating to the closure and after-closure of the site.
Rahaline tagatis peaks olema piisav, et maksta jäätmehoidlaga seotud maa-ala korrastamise eest, mida teeb kvalifitseeritud ja sõltumatu kolmas isik.
The financial guarantee should be sufficient to cover the cost of rehabilitation of the land affected by a waste facility by a suitably qualified and independent third party.
Lisaks on kooskõlas põhimõttega “saastaja maksab” ning vastavalt Euroopa Parlamendi ja nõukogu 21. aprilli 2004. aasta direktiivile 2004/35/EÜ keskkonnavastutusest keskkonnakahjustuste ärahoidmise ja parandamise kohta oluline selgitada, et kaevandustööstuse jäätmeid vastu võtva jäätmehoidla käitaja vastutab asjakohaselt oma tegevusest tuleneva keskkonnakahju eest või sellise kahju tekkimise ohu eest.
In addition, in accordance with the polluter pays principle and with Directive 2004/35/EC of the European Parliament and of the Council of 21 April 2004 on environmental liability with regard to the prevention and remedying of environmental damage, it is important to clarify that an operator of a waste facility servicing the extractive industries is subject to appropriate liability in respect of environmental damage caused by its operations or the imminent threat of such damage.
PÕHJENDUS 31
RECITAL 31
31) On vajalik, et liikmesriigid tagavad nende territooriumil asuvate selliste suletud jäätmehoidlate inventeerimise , mis põhjustavad tõsist negatiivset mõju keskkonnale või mis võivad keskpika või lühikese aja jooksul kujutada tõsist ohtu inimeste tervisele või keskkonnale .
(31) It is necessary for Member States to ensure that an inventory of closed waste facilities located on their territory which cause serious negative environmental impacts or have the potential of becoming in the medium or short term a serious threat to human health or the environment is carried out.
31) On vajalik, et liikmesriigid tagavad nende territooriumil asuvate selliste suletud tegevuskohtade inventeerimise , kuna need tegevuskohad on sageli väga keskkonnaohtlikud.
(31) It is necessary for Member States to ensure that an inventory of closed sites located on their territory is drawn up, since these sites often pose a very high environmental risk.
Liikmesriikidel ja ühendusel on kohustus taastada mahajäetud tegevuskohad, mis võivad keskkonnale tõsiseks ohuks olla.
The Member States and the Community have a responsibility for rehabilitating abandoned sites likely to cause serious negative environmental impacts.
Seetõttu peab olema võimalik kasutada tõukefonde ja teisi asjakohaseid ühenduse rahastamisviise, et teostada inventeerimist ja rakendada meetmeid selliste hoidlate puhastamiseks.
It should therefore be possible to use Structural Funds and other relevant Community funding in order to draw up inventories and implement measures to clean up such facilities.
PÕHJENDUS 37 A (uus)
RECITAL 37 A (new)
37a) Arvestades käesoleva direktiivi tähtsust keskkonna puhul, on soovitav, et uued liituvad liikmesriigid võtaksid seda arvesse juba ühinemiseelses etapis ja rakendaksid pidevalt pärast liitumist.
(37a) In view of the significance of this Directive for environmental protection, it is desirable that newly joining Member States should already take it into account during the pre-accession phase and should apply it consistently from the date of their accession,
This insertion is desirable in connection with the accession of Romania and Bulgaria in 2007 and the planned investment in gold mining at Verespatak (Rosia Montana) in Romania.
This insertion is desirable in connection with the accession of Romania and Bulgaria in 2007 and the planned investment in gold mining at Verespatak (Rosia Montana) in Romania.
ARTIKLI 1 LÕIGE 1 A (uus)
ARTICLE 1, PARAGRAPH 1 A (new)
EÜ asutamislepingu artikli 6 järjekindlaks kohaldamiseks tuleb ühenduse poliitika ja abinõude rakendamisse säästva arengu edendamiseks lisada keskkonnakaitsenõuded.
With a view to the consistent application of Article 6 of the Treaty, environmental protection requirements must be integrated into the implementation of Community policies and activities with a view to promoting sustainable development.
ARTIKLI 2 LÕIKE 3 ESIMENE LÕIK
ARTICLE 2, PARAGRAPH 3, SUBPARAGRAPH 1
Maavarade uuringute, kaevandamise, rikastamise ja ladustamise ning karjääride töö tulemusena tekkinud püsijäätmed ja saastumata pinnas ning turba kaevandamise, rikastamise ja ladustamise tulemusena tekkinud jäätmed ei kuulu artiklite 7 ja 8, artikli 11 lõigete 1 ja 3, artikli 12, artikli 13 lõike5 ning artiklite 14 ja 16 kohaldamisalasse, välja arvatud juhul, kui neid jäätmeid ladustatakse A kategooria jäätmehoidlas .
Inert waste and unpolluted soil resulting from the prospecting, extraction, treatment and storage of mineral resources and the working of quarries and waste resulting from the extraction, treatment and storage of peat shall not be subject to Articles 7, 8, 11(1) and (3), 12, 13(5), 14 and 16, unless deposited in a Category A waste facility.
Maavarade uuringute, kaevandamise, rikastamise ja ladustamise ning karjääride töö tulemusena tekkinud püsijäätmed ei kuulu artikli 11 lõike 1, artikli 13 lõike 5 ja artikli 16 kohaldamisalasse.
Inert waste resulting from the prospecting, extraction, treatment and storage of mineral resources and the working of quarries shall not be subject to Articles 11(1) , 13(5), and 16 .
This amendment brings back the idea expressed in the first reading that this type of waste should be dealt with in a limited number of Articles, but not in the sense that they should all be seen as equal, given that they have very different potential effects.
This amendment brings back the idea expressed in the first reading that this type of waste should be dealt with in a limited number of Articles, but not in the sense that they should all be seen as equal, given that they have very different potential effects.
There is no reason for inert waste to be chemically 'dangerous' i.e. directly poisonous or toxic.
There is no reason for inert waste to be chemically 'dangerous' i.e. directly poisonous or toxic.
However, this type of waste can affect people's health in the same way as it affected freshwater species of flora and fauna, even to the extent of being fatal.
However, this type of waste can affect people's health in the same way as it affected freshwater species of flora and fauna, even to the extent of being fatal.
The nature of its impact is principally determined by the volume produced, and non-dangerous inert waste constitutes the largest part of the total waste produced in the EU.
The nature of its impact is principally determined by the volume produced, and non-dangerous inert waste constitutes the largest part of the total waste produced in the EU.
For this reason, this waste should be subject to Articles 7 (application for and authorisation of waste facilities), 8 (public participation), 11(3) (stability of the waste facility), 12 (closure and subsequent maintenance of waste facilities), and 14 (financial guarantees for the reclamation of waste facilities and the ground affected after closure).
For this reason, this waste should be subject to Articles 7 (application for and authorisation of waste facilities), 8 (public participation), 11(3) (stability of the waste facility), 12 (closure and subsequent maintenance of waste facilities), and 14 (financial guarantees for the reclamation of waste facilities and the ground affected after closure).
ARTIKLI 2 LÕIKE 3 TEINE LÕIK
ARTICLE 2, PARAGRAPH 3, SUBPARAGRAPH 2
Pädev asutus võib leevendada nõudeid, mis esitatakse maavarade, välja arvatud nafta ja vee väljaaurustumisel tekkinud maavarad (peale kipsi ja anhüdriidi) , uuringute tulemusena tekkinud tavajäätmete ladustamisele ning saastumata pinnase ja turba kaevandamisest, rikastamisest ja ladustamisest tulenevatele jäätmetele, kui leitakse, et artikli 4 nõuded on täidetud, või selliste nõuete kohaldamisest loobuda.
The competent authority may reduce or waive the requirements for the deposit of non-hazardous waste generated from the prospecting of mineral resources, except oil and evaporites other than gypsum and anhydrite , as well as for the deposit of unpolluted soil and of waste resulting from the extraction, treatment and storage of peat as long as it is satisfied that the requirements of Article 4 are met.
Pädev asutus võib leevendada nõudeid, mis esitatakse maavarade, välja arvatud nafta ja vee väljaaurustumisel tekkinud maavarad, uuringute tulemusena tekkinud tavajäätmete ladustamisele ning turba kaevandamisest, rikastamisest ja ladustamisest tulenevatele jäätmetele, kui leitakse, et artikli 4 nõuded on täidetud, või selliste nõuete kohaldamisest loobuda.
The competent authority may reduce or waive the requirements for the deposit of non-hazardous waste generated from the prospecting of mineral resources, except oil and evaporites, as well as for the deposit of waste resulting from the extraction, treatment and storage of peat , as long as it is satisfied that the requirements of Article 4 are met.
Eelnimetatu ei kehti juhul, kui neid jäätmeid ladustatakse A kategooria hoidlas.
In all cases, this is u nless these wastes are deposited in a Category A facility.
Amounts of prospective waste are small compared with actual mining/quarrying operations, but they can undoubtedly impact the soil/water around boreholes if not disposed of properly.
Amounts of prospective waste are small compared with actual mining/quarrying operations, but they can undoubtedly impact the soil/water around boreholes if not disposed of properly.
This is why non-hazardous prospective waste must be regulated, in particular if it is deposited in a Category A facility.
This is why non-hazardous prospective waste must be regulated, in particular if it is deposited in a Category A facility.
Waste from the extraction of gypsum and other evaporites can be non-inert, which means that it dissolves in water and releases substances that can impact on freshwater ecosystems: this contradicts the objectives of the Water Framework Directive. .
Waste from the extraction of gypsum and other evaporites can be non-inert, which means that it dissolves in water and releases substances that can impact on freshwater ecosystems: this contradicts the objectives of the Water Framework Directive. .
Unpolluted soil will often undergo fermentation processes, some of which can produce acidic leachates.
Unpolluted soil will often undergo fermentation processes, some of which can produce acidic leachates .
In all cases waste must be regulated, especially if it is deposited in a Category A facility
In all cases waste must be regulated, especially if it is deposited in a Category A facility.
ARTIKLI 2 LÕIKE 3 KOLMAS LÕIK
ARTICLE 2, PARAGRAPH 3, SUBPARAGRAPH 3
Liikmesriigid võivad leevendada artikli 11 lõike 3, artikli 12 lõigete 5 ja 6, artikli 13 lõike 5 ning artiklite 14 ja 16 nõudeid mitteohtlikele tavajäätmetele, välja arvatud juhul, kui neid jäätmeid ladustatakse A kategooria jäätmehoidlas, või selliste nõuete kohaldamisest loobuda.
Member States may reduce or waive the requirements of Articles 11(3), 12(5) and (6), 13(5), 14 and 16 for non-hazardous non-inert waste, unless deposited in a Category A waste facility.
In addition, this waste – being “non-inert” - dissolves in water and could alter the chemistry of the aquatic environment, for example, by promoting the release of “hazardous” substances .
In addition, this waste – being “non-inert” - dissolves in water and could alter the chemistry of the aquatic environment, for example, by promoting the release of “hazardous” substances .
ARTIKLI 3 PUNKT 11
ARTICLE 3, POINT 11
11) tamm – inseneriehitis vee ja jäätmete hoidmiseks või säilitamiseks hiivahoidlas;
11) ‘dam’ means an engineered structure designed to retain or confine water and waste within a pond;
11) tamm – inseneriehitis vee või jäätmete hoidmiseks või säilitamiseks hiivahoidlas;
11) 'dam' means an engineered structure designed to retain or confine water or waste within a pond;
If the waste in a dam is drained, or supernatant water decanted to leave dry waste in the impoundment, the structure is still a dam, even in the absence of free water.
If the waste in a dam is drained, or supernatant water decanted to leave dry waste in the impoundment, the structure is still a dam, even in the absence of free water.
(First reading Amendment 19).
(First reading Amendment 19).
ARTIKLI 3 PUNKT 15
ARTICLE 3, POINT 15
15) jäätmehoidla – iga ala, mis on mõeldud tahkel, vedelal, lahuse või suspensiooni kujul olevate kaevandamisjäätmete kogumiseks või ladustamiseks järgmisteks ajavahemikeks:
15) "waste facility" means any area designated for the accumulation or deposit of extractive waste, whether in a solid or liquid state or in solution or suspension, for the following time ‑periods:
15) jäätmehoidla – iga ala, mis on mõeldud tahkel, vedelal, lahuse või suspensiooni kujul olevate kaevandamisjäätmete kogumiseks või ladustamiseks, mis hõlmab ka tamme või muid struktuure, mille eesmärk on hoida, säilitada, piirata või muul viisil toetada sellist hoidlat, ning samuti, kuid mitte ainult, puistanguid ja hiivahoidlaid, aga ei hõlma kaeveõõsi, millesse jäätmed paigutatakse pärast kaevandamist ala taastamise ja ehituse eesmärgil;
15) "waste facility" means any area designated for the accumulation or deposit of extractive waste, whether in a solid or liquid state or in solution or suspension, and being deemed to include any dam or other structure serving to contain, retain, confine or otherwise support such a facility, and also to include, but not be limited to, heaps and ponds, but excluding excavation voids into which waste is replaced, after extraction of the mineral, for rehabilitation and construction purposes;
- määratlemata ajaks A kategooria jäätmehoidlate ja jäätmekavas kirjeldatud ohtlike jäätmete hoidlate puhul;
- no time-period for Category A waste facilities and facilities for waste characterised as hazardous in the waste management plan;
- rohkem kui kuus kuud ootamatult tekkinud ohtlike jäätmete hoidlate puhul;
- a period of more than six months for facilities for hazardous waste generated unexpectedly;
- rohkem kui aasta mittepüsivate tavajäätmete hoidlate puhul;
- a period of more than one year for facilities for non-hazardous non-inert waste;
- rohkem kui kolm aastat saastumata pinnase, uuringute tulemusel tekkivate tavajäätmete, turba kaevandamisel, rikastamisel ja ladustamisel tekkivate jäätmete ning püsijäätmete hoidlate puhul.
- a period of more than three years for facilities for unpolluted soil, non-hazardous prospecting waste, waste resulting from the extraction, treatment and storage of peat and inert waste.
Sellised hoidlad hõlmavad ka tamme või muid struktuure, mille eesmärk on hoida, säilitada, piirata või muul viisil toetada sellist hoidlat, ning samuti, kuid mitte ainult, puistanguid ja hiivahoidlaid, aga ei hõlma kaeveõõsi, millesse jäätmeid paigutatakse pärast kaevandamist ala taastamise ja ehituse eesmärgil;
Such facilities are deemed to include any dam or other structure serving to contain, retain, confine or otherwise support such a facility, and also to include, but not be limited to, heaps and ponds, but excluding excavation voids into which waste is replaced, after extraction of the mineral, for rehabilitation and construction purposes;
Liikmesriigid tagavad, et käitaja koostab jäätmekava kaevandamisjäätmete minimeerimiseks, töötlemiseks, taaskasutuseks ja kõrvaldamiseks.
Member States shall ensure that the operator draws up a waste management plan for the minimisation, treatment, recovery and disposal of extractive waste.
Liikmesriigid tagavad, et käitaja koostab jäätmekava kaevandamisjäätmete minimeerimiseks, töötlemiseks, taaskasutuseks ja kõrvaldamiseks , võttes arvesse säästva arengu põhimõtet .
Member States shall ensure that the operator draws up a waste management plan for the minimisation, treatment, recovery and disposal of extractive waste , taking account of the principle of sustainable development .
The waste management plan should also take account of the so-called principle of sustainability.
The waste management plan should also take account of the so-called principle of sustainability.
ARTIKLI 5 LÕIKE 2 PUNKTI A ALAPUNKT I
ARTICLE 5, PARAGRAPH 2, POINT (A) (I)
i) jäätmekäitlust projekteerimisjärgus ning kaevandamis- ja rikastamismeetodi valikul;
(i) waste management in the design phase and in the choice of the method used for mineral extraction and treatment;
i) jäätmekäitluse viise projekteerimisjärgus ning kaevandamis- ja rikastamismeetodi valikul;
(i) waste management options in the design phase and in the choice of the method used for mineral extraction and treatment;
ARTIKLI 5 LÕIKE 2 PUNKT C
ARTICLE 5, PARAGRAPH 2, POINT (C)
c) tagada lähemas ja pikemas perspektiivis kaevandamisjäätmete ohutu kõrvaldamine, võttes eelkõige projekteerimisjärgus arvesse jäätmehoidla haldamist selle tegevuse ajal ja pärast selle sulgemist ning valides projekti, mis nõuab vähest ning võimaluse korral mitte mingisugust suletud jäätmehoidla järelevalvet, kontrolli ja haldamist .
(c) to ensure short and long-term safe disposal of the extractive waste, in particular by considering, during the design phase, management during the operation and after‑closure of a waste facility and by choosing a design which requires minimal and, if possible, ultimately no monitoring, control and management of the closed waste facility.