ДИРЕКТИВА СОВЕТА N 1999/31/ЕС ПО ПОЛИГОНАМ ЗАХОРОНЕНИЯ ОТХОДОВ. Директива. Европейский Союз. 26.04.99 1999/31/ЕС

Фрагмент документа "ДИРЕКТИВА СОВЕТА N 1999/31/ЕС ПО ПОЛИГОНАМ ЗАХОРОНЕНИЯ ОТХОДОВ".

Предыдущий фрагмент <<< ...  Оглавление  ... >>> Следующий фрагмент

Полный текст документа

COUNCIL DIRECTIVE No. 1999/31/EC
                       ON THE LANDFILL OF WASTE

                       (Luxembourg, 26.IV.1999)

     The Council of the European Union,
     Having  regard to the Treaty establishing the European Community,
and in particular Article 130s (1) thereof,
     Having regard to the proposal from the Commission <*>,
--------------------------------
     <*> OJ C 156, 24.5.1997, p. 10.

     Having regard to the opinion of the Economic and Social Committee
<*>,
--------------------------------
     <*> OJ C 355, 21.11.1997, p. 4.

     Acting in accordance with the procedure laid down in Article 189c
of the Treaty <*>,
--------------------------------
     <*>  Opinion of the European Parliament of 19 February 1998 (OJ С
80,  16.3.1998,  p. 196), Council common position of 4 June 1998 (OJ С
333,  30.10.1998,  p. 15) and Decision of the European Parliament of 3
February 1999 (OJ С 150, 28.5.1999, p. 78)

     (1)  Whereas  the  Council  resolution of 7 May 1990 <*> on waste
policy  welcomes  and  supports  the  Community  strategy document and
invites  the  Commission  to  propose  criteria  and standards for the
disposal of waste by landfill;
--------------------------------
     <*> OJ C 122, 18.5.1990, p. 2.

     (2)  Whereas  the  Council resolution of 9 December 1996 on waste
policy  considers  that,  in  the  future,  only  safe  and controlled
landfill activities should be carried out throughout the Community;
     (3)  Whereas  the  prevention,  recycling  and  recovery of waste
should  be  encouraged  as  should  the use of recovered materials and
energy  so  as to safeguard natural resources and obviate wasteful use
of land;
     (4)  Whereas  further consideration should be given to the issues
of  incineration  of  municipal  and  non-hazardous waste, composting,
biomethanisation, and the processing of dredging sludges;
     (5)  Whereas  under  the polluter pays principle it is necessary,
inter  alia,  to  take  into  account  any  damage  to the environment
produced by a landfill;
     (6)  Whereas,  like  any  other type of waste treatment, landfill
should  be  adequately  monitored  and  managed  to  prevent or reduce
potential  adverse  effects  on  the  environment  and  risks to human
health;
     (7) Whereas it is necessary to take appropriate measures to avoid
the  abandonment,  dumping or uncontrolled disposal of waste; whereas,
accordingly,  it  must  be  possible  to  monitor  landfill sites with
respect  to  the  substances  contained  in the waste deposited there,
whereas  such  substances  should,  as  far as possible, react only in
foreseeable ways;
     (8)  Whereas  both  the  quantity  and  hazardous nature of waste
intended for landfill should be reduced where appropriate; whereas the
handling  of  waste  should  be facilitated and its recovery enhanced;
whereas  the use of treatment processes should therefore be encouraged
to  ensure  that  landfill  is  compatible with the objectives of this
Directive; whereas sorting is included in the definition of treatment;
     (9)  Whereas Member States should be able to apply the principles
of  proximity  and self-sufficiency for the elimination of their waste
at  Community and national level, in accordance with Council Directive
75/442/EEC of 15 July 1975 on waste <*> whereas the objectives of this
Directive  must  be pursued and clarified through the establishment of
an  adequate,  integrated  network  of disposal plants based on a high
level of environmental protection;
--------------------------------
     <*>  OJ  L  194,  25.7.1975,  p. 39. Directive as last amended by
Commission Decision 96/350/EC (OJ L 135, 6.6.1996, p. 32).

     (10)  Whereas  disparities  between  technical  standards for the
disposal  of  waste by landfill and the lower costs associated with it
might  give rise to increased disposal of waste in facilities with low
standards  of  environmental  protection and thus create a potentially
serious  threat  to  the environment, owing to transport of waste over
unnecessarily  long  distances  as  well  as to inappropriate disposal
practices;
     (11)  Whereas  it  is  therefore  necessary to lay down technical
standards  for  the  landfill  of waste at Community level in order to
protect,  preserve  and  improve the quality of the environment in the
Community;
     (12) Whereas it is necessary to indicate clearly the requirements
with   which   landfill   sites   must  comply  as  regards  location,
conditioning,   management,   control,   closure  and  preventive  and
protective  measures to be taken against any threat to the environment
in  the  short  as  well  as  in  the  long-term perspective, and more
especially   against   the   pollution   of  groundwater  by  leachate
infiltration into the soil;
     (13)  Whereas  in view of the foregoing it is necessary to define
clearly  the  classes  of  landfill  to be considered and the types of
waste to be accepted in the various classes of landfill;
     (14)  Whereas  sites for temporary storage of waste should comply
with the relevant requirements of Directive 75/442/EEC;
     (15)  Whereas  the  recovery,  in  accordance  with Directive 75/
442/EEC,  of  inert  or non-hazardous waste which is suitable, through
their  use  in  redevelopment/restoration  and filling-in work, or for
construction purposes may not constitute a landfilling activity;
     (16) Whereas measures should be taken to reduce the production of
methane  gas  from  landfills,  inter  alia, in order to reduce global
warming,  through the reduction of the landfill of biodegradable waste
and the requirements to introduce landfill gas control;
     (17)  Whereas  the  measures  taken  to  reduce  the  landfill of
biodegradable  waste  should  also  aim  at  encouraging  the separate
collection  of  biodegradable  waste, sorting in general, recovery and
recycling;
     (18)  Whereas, because of the particular features of the landfill
method  of  waste  disposal,  it  is necessary to introduce a specific
permit  procedure  for  all classes of landfill in accordance with the
general   licensing   requirements   already  set  down  in  Directive
75/442/EEC   and   the  general  requirements  of  Directive  96/61/EC
concerning integrated pollution prevention and control <*> whereas the
landfill  site`s compliance with such a permit must be verified in the
course of an inspection by the competent authority before the start of
disposal operations;
--------------------------------
     <*> OJ L 257, 10.10.1996, p. 26.

     (19)  Whereas,  in  each case, checks should be made to establish
whether  the  waste  may  be  placed  in  the landfill for which it is
intended, in particular as regards hazardous waste;
     (20)  Whereas, in order to prevent threats to the environment, it
is  necessary to introduce a uniform waste acceptance procedure on the
basis  of  a  classification  procedure  for  waste  acceptable in the
different categories of landfill, including in particular standardised
limit values; whereas to that end a consistent and standardised system
of  waste  characterisation, sampling and analysis must be established
in  time  to  facilitate implementation of this Directive; whereas the
acceptance criteria must be particularly specific with regard to inert
waste;
     (21)  Whereas,  pending  the  establishment  of  such  methods of
analysis or of the limit values necessary for characterisation, Member
States  may  for  the  purposes  of this Directive maintain or draw up
national  lists  of  waste  which  is  acceptable  or unacceptable for
landfill, or define criteria, including limit values, similar to those
laid down in this Directive for the uniform acceptance procedure;
     (22)  Whereas  for  certain  hazardous  waste  to  be accepted in
landfills  for  non-hazardous  waste  acceptance  criteria  should  be
developed by the technical committee;
     (23)  Whereas  it  is  necessary  to  establish common monitoring
procedures during the operation and after-care phases of a landfill in
order  to  indentify  any possible adverse environmental effect of the
landfill and take the appropriate corrective measures;
     (24)  Whereas  it  is necessary to define when and how a landfill
should  be  closed  and  the  obligations  and  responsibility  of the
operator on the site during the after-care period;
     (25)  Whereas  landfill  sites that have been closed prior to the
date  of  transposition of this Directive should not be subject to its
provisions on closure procedure;
     (26)  Whereas  the  future  conditions  of  operation of existing
landfills should be regulated in order to take the necessary measures,
within  a  specified  period  of  time,  for  their adaptation to this
Directive on the basis of a site-conditioning plan;
     (27)  Whereas  for  operators  of  existing  landfills having, in
compliance  with binding national rules equivalent to those of Article
14  of this Directive, already submitted the documentation referred to
in  Article 14 (a) of this Directive prior to its entry into force and
for which the competent authority authorised the continuation of their
operation, there is no need to resubmit this documentation nor for the
competent authority to deliver a new authorisation;
     (28)  Whereas  the operator should make adequate provision by way
of a financial security or any other equivalent to ensure that all the
obligations  flowing  from  the  permit are fulfilled, including those
relating to the closure procedure and after-care of the site;
     (29)  Whereas  measures  should be taken to ensure that the price
charged  for waste disposal in a landfill cover all the costs involved
in  the  setting up and operation of the facility, including as far as
possible  the  financial  security  or  its  equivalent which the site
operator  must  provide,  and  the  estimated cost of closing the site
including the necessary after-care;
     (30)  Whereas,  when  a  competent  authority  considers  that  a
landfill  is  unlikely to cause a hazard to the environment for longer
than a certain period, the estimated costs to be included in the price
to be charged by an operator may be limited to that period;
     (31)  Whereas it is necessary to ensure the proper application of
the  provisions  implementing this Directive throughout the Community,
and  to  ensure  that  the training and knowledge acquired by landfill
operators and staff afford them the necessary skills;
     (32)  Whereas  the Commission must establish a standard procedure
for  the  acceptance  of waste and set up a standard classification of
waste  acceptable  in  a  landfill  in  accordance  with the committee
procedure laid down in Article 18 of Directive 75/442/EEC;
     (33)  Whereas  adaptation  of  the  Annexes  to this Directive to
scientific  and  technical  progress  and  the  standardisation of the
monitoring,  sampling  and  analysis methods must be adopted under the
same committee procedure;
     (34)  Whereas  the Member States must send regular reports to the
Commission  on  the implementation of this Directive paying particular
attention  to  the  national  strategies  to be set up in pursuance of
Article  5; whereas on the basis of these reports the Commission shall
report to the European Parliament and the Council;
     has adopted this Directive

Фрагмент документа "ДИРЕКТИВА СОВЕТА N 1999/31/ЕС ПО ПОЛИГОНАМ ЗАХОРОНЕНИЯ ОТХОДОВ".

Предыдущий фрагмент <<< ...  Оглавление  ... >>> Следующий фрагмент

Полный текст документа