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EPBA

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Title: EPBA


1
Battery collection in Europe Hans
Craen European Portable Battery
Association California Battery Workshop 29
April 2008
/
EPBA
2
Content
  • Introduction
  • European legal framework
  • Battery collection in Europe
  • Impact assessments
  • Conclusions

3
Introduction
  • EPBA is the leading organisation in Europe
    representing the interests of
  • primary and rechargeable portable battery
    manufacturers
  • those industries using portable batteries in
    their products
  • and distributors of portable batteries active
    within the European Union
  • EPBA enjoys excellent cooperation (regular
    trilateral exchanges and events) with its
    counterparts in
  • USA - with the National Electrical Manufacturers
    Association and the Portable Rechargeable Battery
    Association
  • Japan - with the Battery Association of Japan

4
EPBA Key-Activities
Introduction
  • Lobbying at EU level in the framework of the
    Battery Directive
  • Support to European countries in the setting up
    of Compliance Organisations
  • Preparing the transposition and implementation of
    the Battery Directive
  • Monitoring of and responding to other European
    legislation impacting the battery industry (e.g.
    WEEE ROHS, REACH, LVD,)
  • Monitoring of and responding to the UN
    legislation regarding transport of dangerous goods

5
Achievements
Introduction
  • Pioneered voluntary programme for the removal of
    mercury from alkaline and zinc batteries
    completed 1993,
  • Developed alternative zero and low mercury
    containing batteries, lithium and zinc air
    types, to replace mercury oxide batteries
    containing 30 mercury circa 1985,
  • Developed technology to recycle mercury free
    batteries in metals industry 1991 - 2000,
  • Developed nickel metal hydride and lithium ion
    rechargeable batteries as alternatives to nickel
    cadmium circa 94 98

6
Introduction
European Portable Battery Association
(EPBA) Interfaces with EU international bodies
Set up by members
20 National Battery Associations (NBA)
Interface with national Governments
14 Collection and Recycling Organisations (CRO)
Compliance with producer responsibility
7
Content
  • Introduction
  • European legal framework
  • Battery collection in Europe
  • Impact assessments
  • Conclusions

8
European legal framework
EU Battery Legislation
Amendment to battery Directive
New Battery Directive Published
First EU battery Directive
Technical adaptation to battery Directive
New Battery Directive Implemented
1991
1993
1998
2006
2008
9
European legal framework
  • First Battery Directive (91/157)
  • Main objective of Directive was to harmonise
    existing national legislation on collection of
    batteries
  • ? Should be seen in context of Waste Directive
    (1975)
  • Ban of Alkaline Manganese batteries containing
    gt0,025 Hg
  • Separate collection for batteries containing
  • - gt 25 mg Hg
  • - gt 0,025 Cd
  • - gt 0,4 Pb
  • Marking requirements for batteries above
    indicated limits
  • - Crossed-out dustbin
  • - Chemical symbol
  • Collected batteries could be recycled or disposed
    to land fill

10
European legal framework
  • Amendment to Battery Directive (93/86)
  • This Directive set detailed marking arrangements
  • Scope batteries containing Hg, Pb and Cd
  • Specifications on size and placement

11
European legal framework
  • Technical adaptation of Battery Directive
    (98/101)
  • Technical adaptation was result of industrys
    recommendations
  • ? Industrys mercury elimination programme
  • Ban of all batteries gt5ppm Hg
  • ? This limit is based on analytical threshold
  • ? lt5ppm Hg No Hg added but present as
    background level in materials used
    in batteries
  • Exemption for button cells containing up to 2 Hg

12
European legal framework
  • New Battery Directive (2006/66)
  • Scope all batteries (portable, automotive,
    industrial)
  • Substance ban
  • - Mercury gt 5ppm for all batteries
  • ? exemption for button cells with no more
    than 2 Hg by weight
  • - Cadmium gt 20ppm for portable batteries
  • ? exemption for
  • 1. emergency and alarm systems (incl.
    emergency lighting) 2.
    medical equipment
  • 3. cordless power tools
  • Collection targets for portable batteries
  • - By September 2012 minimum 25 of sales by
    weight
  • - By September 2016 minimum 45 of sales by
    weight

13
European legal framework
  • New Battery Directive (2006/66)
  • Marking (1) Crossed-out dustbin
  • (2) Chemical symbol
  • (3) Capacity marking on portable and automotive
    batteries
  • Financing No visible fee to end-users
  • ? visible fee on invoice level will be
    possible
  • Specific recycling targets - recycle 65 of
    contents of lead acid batteries, - recycle 75
    of contents of nickel cadmium batteries, -
    recycle 50 of contents of other batteries on
    average.

Member States have until 26 September 2008 to
transpose the new Directive into national law
14
Content
  • Introduction
  • European legal framework
  • Battery collection in Europe
  • Impact assessments
  • Conclusions

15
Progress of Collection Laws in Europe
Battery collection in Europe
16
Typical Collection Recycling System
CONSUMERS
COLLECTION at municipal sites, stores, schools,
etc
17
Battery collection in Europe
  • The involvement of industry is essential to
    ensure that a workable collection scheme can be
    set up

This expertise and know how have to be taken into
account in the full process in order to achieve
  • ? Most suitable solution
  • ? Ensuring high level of efficiency

18
Battery collection in Europe
  • Considerations based on the European experience
  • The current experience in Europe shows the
    complexity of collecting portable batteries
  • The actual results in collecting batteries vary
    from one country to another
  • Some elements are essential for collecting
    portable batteries but impossible to control

19
Battery collection in Europe
The current experience in Europe shows the
complexity of collecting portable batteries
  • This is not fully reflected in the European
    Directive
  • ? e.g. definition of producer
  • Complexity, costs and environmental burdens of
    battery collection, sorting, transportation and
    recycling are often underestimated
  • Battery collection requires not only the
    involvement of producers but also of
  • ? government
  • ? distributors
  • ? consumers

20
Battery collection in Europe
The actual results in collecting batteries vary
from one country to another
  • A one size fits all solution is not possible
  • The existing collection schemes in the European
    countries are not identical national
    specificities have to be taken into account
  • In some countries progress in collection results
    is very slow or even declining
  • 100 collection rate for portable batteries can
    never be achieved

21
Battery collection in Europe
The actual results in collecting batteries vary
from one country to another (Contd)
  • Different factors have an influence on the
    collection results
  • - Legislative framework
  • - Consumer awareness
  • - Apropriate financial schemes
  • - Geography
  • - Government involvement
  • - Social conditions
  • -

22
Battery collection in Europe
Some elements are essential for collecting
portable batteries but impossible to control
  • Consumer involvement is essential for achieving
    results
  • Consumer involvement is difficult to regulate for
    a product such as portable batteries small,easy
    to store away, easy to throw away
  • Ensuring consumer awairness is a long and gradual
    process
  • ? Other European waste legislation (WEEE,
    packaging, ELV,) which has been issued over the
    past years is helping raising the awairness among
    consumers

23
Content
  • Introduction
  • European legal framework
  • Battery collection in Europe
  • Impact assessments
  • Conclusions

24
Impact Assessments
  • Three recent studies have put into question the
    environmental benefits of collecting and
    recycling both hazardous and non-hazardous
    batteries.
  • Environmental and economic impact assessments
    have been carried out in 2000, 2005 and 2006 for
    the Governments of France and UK.

25
Impact Assessments
  • UK Government, Department of Industry study Nov.
    2000 and French Environment Ministry study,
    April. 2006
  • Prohibition of batteries containing mercury and
    cadmium can be justified since there are
    alternatives which do not present the same high
    level of risks to the environment.
  • There are clear environmental benefits from
    collecting and recycling batteries containing Hg,
    Cd and Pb because of the toxicity of these
    metals, compared to land filling them.
  • Transportation of waste batteries causes damage
    to the environment from global warming, resource
    depletion, smog and acidification. The extent of
    these negative effects is closely related to the
    distances the collected batteries have to be
    transported. It is therefore better for the
    environment to minimise these distances.
  • It is better to recycle collected batteries than
    to land fill them.
  • There is no benefit for the environment from
    collecting alkaline batteries separately from
    other household waste.

26
Impact Assessments
  • UK Government, Department of Environment study,
    10/2006
  • Increasing collection and recycling of batteries
    is beneficial to the environment, due to the
    recovery of metals. However, this is achieved at
    high cost, almost 400 million compared against
    60 million for land fill.
  • The benefit of reducing greenhouse gas emissions
    by 6000 t per year is small and costs 2550/t
    which compares with a greenhouse gas trading
    price today of around 9/t.
  • Disposing batteries containing mercury, cadmium
    and lead in land fill sites or by incineration
    causes pollution of the environment. It is
    therefore better to collect and recycle batteries
    containing these metals.
  • Likelihood of batteries such as alkaline that do
    not contain hazardous materials to pollute the
    environment through disposal in land fill sites
    is very small.

27
Content
  • Introduction
  • European legal framework
  • Battery collection in Europe
  • Impact assessments
  • Conclusions

28
  • The European legislative framework has evolved
    over a long period of time
  • Every national collection system has its own
    characteristics even when based on the same
    European legislation
  • Achieving results in battery collection is
  • ? difficult (100 collection rate not
    possible)
  • ? time dependent process
  • Recent studies put into question the green
    option of collecting certain type of batteries

29
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