Title: EPBA
1Battery collection in Europe Hans
Craen European Portable Battery
Association California Battery Workshop 29
April 2008
/
EPBA
2Content
- Introduction
- European legal framework
- Battery collection in Europe
- Impact assessments
- Conclusions
3Introduction
- 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
4EPBA 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
5Achievements
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
6Introduction
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
7Content
- Introduction
- European legal framework
- Battery collection in Europe
- Impact assessments
- Conclusions
8European 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
9European 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
10European 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
11European 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
12European 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
13European 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
14Content
- Introduction
- European legal framework
- Battery collection in Europe
- Impact assessments
- Conclusions
15Progress of Collection Laws in Europe
Battery collection in Europe
16Typical Collection Recycling System
CONSUMERS
COLLECTION at municipal sites, stores, schools,
etc
17Battery 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
18Battery 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
19Battery 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
20Battery 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
21Battery 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
- -
22Battery 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
23Content
- Introduction
- European legal framework
- Battery collection in Europe
- Impact assessments
- Conclusions
24Impact 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.
25Impact 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.
26Impact 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.
27Content
- 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
29Thank you for your attention Questions?