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Position 
Paper 
Distinction 
Portable 
– 
Industrial 
– 
Automotive 
Batteries 
1. The 
Battery 
Directive: 
actual 
situation 
The 
battery 
directive1 
distinguishes 
following 
types 
of 
batteries: 
• Portable 
battery 
or 
accumulator’ 
means 
any 
battery, 
button 
cell, 
battery 
pack 
or 
accumulator 
that: 
o is 
sealed; 
and 
o can 
be 
hand-­‐carried; 
and 
o is 
neither 
an 
industrial 
battery 
or 
accumulator 
nor 
an 
automotive 
battery 
or 
accumulator. 
• Industrial 
battery 
or 
accumulator’ 
means 
any 
battery 
or 
accumulator 
designed 
for 
exclusively 
industrial 
or 
professional 
uses 
or 
used 
in 
any 
type 
of 
electric 
vehicle. 
• Automotive 
battery 
or 
accumulator’ 
means 
any 
battery 
or 
accumulator 
used 
for 
automotive 
starter, 
lighting 
or 
ignition 
power. 
This 
distinction 
is 
important, 
as 
it 
is 
decisive 
to 
determine 
the 
liabilities 
and 
responsibilities, 
as 
well 
operational 
as 
financial, 
of 
all 
concerned 
actors. 
In 
particular, 
the 
significance 
of 
the 
classification 
of 
the 
batteries 
is 
undisputable 
for 
the 
calculation 
of 
the 
collection 
target, 
as 
this 
only 
applies 
to 
portable 
batteries. 
After 
several 
years 
of 
experience 
in 
the 
Member 
States, 
it 
seems 
that 
there 
is 
particularly 
a 
problem 
to 
distinguish 
industrial 
from 
portable 
batteries. 
2. Current 
application 
of 
the 
definitions 
For 
the 
batteries 
put 
on 
the 
market, 
the 
decision 
on 
the 
classification 
is 
taken 
by 
the 
producers, 
based 
upon 
a 
decision 
tree 
that 
is 
explicitly 
or 
tacitly 
approved 
by 
the 
Member 
State 
and 
that 
takes 
into 
account 
the 
criteria 
described 
in 
the 
battery 
directive. 
The 
decision 
trees 
used 
in 
the 
different 
Member 
States 
are 
similar, 
with 
to 
a 
larger 
or 
smaller 
extent 
some 
interpretative 
guidance 
for 
the 
producers 
on 
the 
different 
criteria. 
1 
Directive 
2006/66/EC 
of 
the 
European 
Parliament 
and 
of 
the 
Council 
of 
6 
September 
2006 
on 
batteries 
and 
accumulators 
and 
waste 
batteries 
and 
accumulators 
and 
repealing 
Directive 
91/157/EEC 
– 
Article 
3, 
3°-­‐5°-­‐6°
For 
the 
collected 
batteries, 
the 
operational 
actors, 
e.g. 
sorting 
or 
recycling 
facilities, 
take 
the 
decision 
on 
the 
classification. 
As 
one 
of 
the 
criteria 
to 
distinguish 
industrial 
batteries 
from 
portable 
batteries 
is 
the 
intended 
use 
of 
these 
batteries 
(“designed 
for 
exclusively 
industrial 
or 
professional 
uses”), 
and 
it 
is 
impossible 
for 
these 
operational 
actors 
to 
know 
2 
the 
use 
of 
the 
collected 
battery, 
they 
use 
other 
criteria, 
like: 
• Weight 
(varying 
per 
country 
from 
1kg 
to 
5 
kg) 
• Collection 
point 
(industrial 
collection 
points 
or 
consumer 
collection 
points) 
• Pro 
rata 
(proportion 
industrial 
– 
portable 
batteries 
is 
the 
same 
for 
collection 
as 
for 
POM) 
• Sample 
• … 
• A 
mix 
of 
these 
criteria 
3. Issues 
concerning 
the 
criteria 
The 
producers 
can 
relatively 
easily 
apply 
the 
definitions 
of 
the 
battery 
directive, 
as 
they 
know 
in 
most 
cases 
the 
intended 
use 
of 
the 
batteries 
they 
put 
on 
the 
market. 
It 
is 
however 
much 
more 
difficult 
for 
the 
operational 
actors 
to 
apply 
these 
definitions, 
as 
they 
only 
receive 
the 
waste 
batteries 
and 
battery 
packs, 
without 
knowing 
the 
applications 
they 
were 
used 
in. 
They 
are 
obliged 
to 
use 
a 
set 
of 
criteria 
(see 
above) 
that 
differs 
from 
country 
to 
country. 
The 
different 
interpretations 
in 
the 
Members 
States 
for 
the 
classification 
of 
the 
waste 
batteries 
into 
industrial 
and 
portable 
waste 
batteries 
have 
a 
serious 
impact 
on 
the 
reported 
collection 
rates. 
As 
a 
consequence, 
these 
differences 
make 
it 
very 
difficult 
to 
compare 
the 
figures 
of 
the 
Member 
States. 
Furthermore, 
experience 
shows 
that 
the 
application 
of 
inappropriate 
criteria 
to 
distinguish 
the 
collected 
batteries 
leads 
to 
unrealistic 
collection 
rates 
in 
some 
Member 
States. 
Besides 
the 
collection 
rates, 
the 
interpretation 
also 
influences 
the 
financing 
of 
the 
collection 
schemes 
in 
the 
Member 
States 
where 
multiple 
compliance 
organizations 
coexist.
3 
4. Eucobat 
proposal 
The 
main 
criterion 
to 
distinguish 
portable 
batteries 
from 
industrial 
batteries 
in 
the 
definitions 
of 
the 
battery 
directive 
is 
of 
intentional 
kind 
(“designed 
for 
exclusively 
industrial 
or 
professional 
uses”), 
which 
cannot 
be 
determined 
when 
the 
batteries 
are 
collected. 
A 
full 
coherence 
in 
the 
classification 
of 
the 
batteries 
put 
on 
the 
market 
and 
the 
collected 
batteries 
can 
for 
this 
reason 
only 
be 
achieved 
by 
a 
fundamental 
review 
of 
these 
definitions. 
We 
are 
convinced 
that 
this 
will 
be 
necessary 
on 
the 
moment 
of 
the 
recast 
of 
the 
battery 
directive 
and 
we 
will 
discuss 
this 
point 
within 
Eucobat 
and 
will 
formulate 
a 
proposal. 
An 
intermediate 
solution, 
standing 
the 
current 
definitions, 
is 
required 
to 
ensure 
the 
comparability 
of 
the 
reported 
figures 
of 
the 
Member 
States, 
with 
a 
clear 
guidance 
that 
is 
easily 
applicable 
for 
the 
producers 
and 
for 
the 
operational 
actors. 
As 
indicated, 
the 
producers 
can 
relatively 
easily 
apply 
the 
current 
definitions 
for 
the 
batteries 
they 
put 
on 
the 
market, 
using 
the 
existing 
decision 
trees. 
On 
the 
other 
hand, 
clear 
interpretation 
guidance 
is 
required 
for 
the 
operational 
actors 
for 
the 
collected 
batteries, 
in 
order 
to 
ensure 
that 
these 
operational 
actors 
classify 
the 
batteries 
in 
the 
same 
way 
as 
declared 
by 
the 
producers. 
In 
order 
to 
distinguish 
portable 
batteries 
from 
industrial 
waste 
batteries, 
the 
experience 
of 
the 
compliance 
schemes 
indicates 
that 
a 
weight 
limit 
of 
3 
kg 
corresponds 
to 
a 
certain 
reality 
and 
could 
be 
used 
as 
a 
first 
criterion. 
This 
appears 
clearly 
from 
a 
sample 
in 
three 
countries 
on 
a 
typical 
general 
household 
mix 
of 
waste 
batteries 
collected 
by 
the 
compliance 
organisations 
in 
those 
countries. 
The 
figures 
indicate 
that 
a 
large 
majority 
of 
the 
collected 
batteries 
from 
households 
have 
a 
weight 
till 
3 
kg. 
6a. Definitions P-I-A: Sampling 
Definitions P-I-A: Sampling 
Weight&per&ba7ery& 
(kg)& Number&Ba7eries Total&&Weight 
0,00&W&1,00& 43% 17% 
1,01&W&2,00& 16% 15% 
2,01&W&3,00& 27% 35% 
3,01&W&4,00& 5% 8% 
4,01&W&5,00& 2% 4% 
5,01&W&…& 6% 21% 
6a. Definitions 87%& 67%& 
P-I-A: Sampling 
(kg)' Number'Ba,eries Total''Weight 
100% 100% 
Belgium& 
Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 
0,00&W&1,00& 96,6%& 
1,01&W&2,00& 1,2%& 
2,01&W&3,00& 
3,01&W&4,00& 2,1%& 
4,01&W&5,00& 
5,01&W&…& 
100,0%& 
97,8%& 
Germany& 
0,00';'1,00' 43% 17% 
1,01';'2,00' 16% 15% 
2,01';'3,00' 27% 35% 
3,01';'4,00' 5% 8% 
4,01';'5,00' 2% 4% 
5,01';'…' 6% 21% 
87%' 67%' 
Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 
0,00&W&1,00& 
1,01&W&2,00& 99,9%& 
2,01&W&3,00& 
3,01&W&4,00& 
4,01&W&5,00& 0,1%& 
5,01&W&…& 
100,0%& 
Netherlands& 
ba7ery& 
Number&Ba7eries Total&&Weight 
43% 17% 
16% 15% 
27% 35% 
5% 8% 
2% 4% 
6% 21% 
100% 100% 
87%& 67%& 
Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 
0,00&W&1,00& 96,6%& 
1,01&W&2,00& 1,2%& 
2,01&W&3,00& 
3,01&W&4,00& 2,1%& 
4,01&W&5,00& 
5,01&W&…& 
100,0%& 
97,8%& 
Germany& 
Weight'per'ba,ery' 
Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 
0,00&W&1,00& 
1,01&W&2,00& 99,9%& 
2,01&W&3,00& 
3,01&W&4,00& 
4,01&W&5,00& 0,1%& 
5,01&W&…& 
100,0%& 
Netherlands& 
100% 100% 
Belgium' 
Weight'per'ba,ery'(kg)! Number'of'ba,eries! Total'Weight! 
0,00';'1,00' 96,6%' 
1,01';'2,00' 1,2%' 
2,01';'3,00' 
3,01';'4,00' 2,1%' 
4,01';'5,00' 
5,01';'…' 
100,0%' 
97,8%' 
Germany' 
Weight'per'ba,ery'(kg)! Number'of'ba,eries! Total'Weight! 
0,00';'1,00' 
1,01';'2,00' 99,9%' 
2,01';'3,00' 
3,01';'4,00' 
4,01';'5,00' 0,1%' 
5,01';'…' 
100,0%' 
Netherlands'
4 
However, 
this 
weight 
criterion 
is 
not 
absolute, 
as 
some 
batteries 
of 
more 
than 
3 
kg 
that 
are 
typically 
used 
by 
consumers 
and 
that 
can 
be 
separated 
based 
upon 
the 
collection 
channel, 
should 
be 
considered 
as 
portable. 
In 
order 
to 
ensure 
that 
the 
collected 
batteries 
are 
classified 
in 
the 
same 
way 
as 
the 
batteries 
put 
on 
the 
market 
declared 
by 
the 
producers, 
Eucobat 
proposes 
that 
the 
batteries 
above 
3 
kg 
that 
cannot 
be 
used 
by 
private 
households 
are 
considered 
industrial 
batteries. 
5. About 
Eucobat 
Eucobat 
aisbl 
is 
the 
European 
association 
of 
national 
collection 
schemes 
for 
batteries. 
They 
assure 
that 
all 
waste 
batteries 
are 
collected 
and 
recycled 
in 
an 
ecological 
sound 
way, 
and 
contribute 
this 
way 
to 
a 
better 
environment. 
Eucobat 
aisbl 
October 
2013

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Distinction Portable-Industrial-Automotive - Eucobat Position

  • 1. Position Paper Distinction Portable – Industrial – Automotive Batteries 1. The Battery Directive: actual situation The battery directive1 distinguishes following types of batteries: • Portable battery or accumulator’ means any battery, button cell, battery pack or accumulator that: o is sealed; and o can be hand-­‐carried; and o is neither an industrial battery or accumulator nor an automotive battery or accumulator. • Industrial battery or accumulator’ means any battery or accumulator designed for exclusively industrial or professional uses or used in any type of electric vehicle. • Automotive battery or accumulator’ means any battery or accumulator used for automotive starter, lighting or ignition power. This distinction is important, as it is decisive to determine the liabilities and responsibilities, as well operational as financial, of all concerned actors. In particular, the significance of the classification of the batteries is undisputable for the calculation of the collection target, as this only applies to portable batteries. After several years of experience in the Member States, it seems that there is particularly a problem to distinguish industrial from portable batteries. 2. Current application of the definitions For the batteries put on the market, the decision on the classification is taken by the producers, based upon a decision tree that is explicitly or tacitly approved by the Member State and that takes into account the criteria described in the battery directive. The decision trees used in the different Member States are similar, with to a larger or smaller extent some interpretative guidance for the producers on the different criteria. 1 Directive 2006/66/EC of the European Parliament and of the Council of 6 September 2006 on batteries and accumulators and waste batteries and accumulators and repealing Directive 91/157/EEC – Article 3, 3°-­‐5°-­‐6°
  • 2. For the collected batteries, the operational actors, e.g. sorting or recycling facilities, take the decision on the classification. As one of the criteria to distinguish industrial batteries from portable batteries is the intended use of these batteries (“designed for exclusively industrial or professional uses”), and it is impossible for these operational actors to know 2 the use of the collected battery, they use other criteria, like: • Weight (varying per country from 1kg to 5 kg) • Collection point (industrial collection points or consumer collection points) • Pro rata (proportion industrial – portable batteries is the same for collection as for POM) • Sample • … • A mix of these criteria 3. Issues concerning the criteria The producers can relatively easily apply the definitions of the battery directive, as they know in most cases the intended use of the batteries they put on the market. It is however much more difficult for the operational actors to apply these definitions, as they only receive the waste batteries and battery packs, without knowing the applications they were used in. They are obliged to use a set of criteria (see above) that differs from country to country. The different interpretations in the Members States for the classification of the waste batteries into industrial and portable waste batteries have a serious impact on the reported collection rates. As a consequence, these differences make it very difficult to compare the figures of the Member States. Furthermore, experience shows that the application of inappropriate criteria to distinguish the collected batteries leads to unrealistic collection rates in some Member States. Besides the collection rates, the interpretation also influences the financing of the collection schemes in the Member States where multiple compliance organizations coexist.
  • 3. 3 4. Eucobat proposal The main criterion to distinguish portable batteries from industrial batteries in the definitions of the battery directive is of intentional kind (“designed for exclusively industrial or professional uses”), which cannot be determined when the batteries are collected. A full coherence in the classification of the batteries put on the market and the collected batteries can for this reason only be achieved by a fundamental review of these definitions. We are convinced that this will be necessary on the moment of the recast of the battery directive and we will discuss this point within Eucobat and will formulate a proposal. An intermediate solution, standing the current definitions, is required to ensure the comparability of the reported figures of the Member States, with a clear guidance that is easily applicable for the producers and for the operational actors. As indicated, the producers can relatively easily apply the current definitions for the batteries they put on the market, using the existing decision trees. On the other hand, clear interpretation guidance is required for the operational actors for the collected batteries, in order to ensure that these operational actors classify the batteries in the same way as declared by the producers. In order to distinguish portable batteries from industrial waste batteries, the experience of the compliance schemes indicates that a weight limit of 3 kg corresponds to a certain reality and could be used as a first criterion. This appears clearly from a sample in three countries on a typical general household mix of waste batteries collected by the compliance organisations in those countries. The figures indicate that a large majority of the collected batteries from households have a weight till 3 kg. 6a. Definitions P-I-A: Sampling Definitions P-I-A: Sampling Weight&per&ba7ery& (kg)& Number&Ba7eries Total&&Weight 0,00&W&1,00& 43% 17% 1,01&W&2,00& 16% 15% 2,01&W&3,00& 27% 35% 3,01&W&4,00& 5% 8% 4,01&W&5,00& 2% 4% 5,01&W&…& 6% 21% 6a. Definitions 87%& 67%& P-I-A: Sampling (kg)' Number'Ba,eries Total''Weight 100% 100% Belgium& Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 0,00&W&1,00& 96,6%& 1,01&W&2,00& 1,2%& 2,01&W&3,00& 3,01&W&4,00& 2,1%& 4,01&W&5,00& 5,01&W&…& 100,0%& 97,8%& Germany& 0,00';'1,00' 43% 17% 1,01';'2,00' 16% 15% 2,01';'3,00' 27% 35% 3,01';'4,00' 5% 8% 4,01';'5,00' 2% 4% 5,01';'…' 6% 21% 87%' 67%' Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 0,00&W&1,00& 1,01&W&2,00& 99,9%& 2,01&W&3,00& 3,01&W&4,00& 4,01&W&5,00& 0,1%& 5,01&W&…& 100,0%& Netherlands& ba7ery& Number&Ba7eries Total&&Weight 43% 17% 16% 15% 27% 35% 5% 8% 2% 4% 6% 21% 100% 100% 87%& 67%& Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 0,00&W&1,00& 96,6%& 1,01&W&2,00& 1,2%& 2,01&W&3,00& 3,01&W&4,00& 2,1%& 4,01&W&5,00& 5,01&W&…& 100,0%& 97,8%& Germany& Weight'per'ba,ery' Weight&per&ba7ery&(kg)' Number&of&ba7eries' Total&Weight' 0,00&W&1,00& 1,01&W&2,00& 99,9%& 2,01&W&3,00& 3,01&W&4,00& 4,01&W&5,00& 0,1%& 5,01&W&…& 100,0%& Netherlands& 100% 100% Belgium' Weight'per'ba,ery'(kg)! Number'of'ba,eries! Total'Weight! 0,00';'1,00' 96,6%' 1,01';'2,00' 1,2%' 2,01';'3,00' 3,01';'4,00' 2,1%' 4,01';'5,00' 5,01';'…' 100,0%' 97,8%' Germany' Weight'per'ba,ery'(kg)! Number'of'ba,eries! Total'Weight! 0,00';'1,00' 1,01';'2,00' 99,9%' 2,01';'3,00' 3,01';'4,00' 4,01';'5,00' 0,1%' 5,01';'…' 100,0%' Netherlands'
  • 4. 4 However, this weight criterion is not absolute, as some batteries of more than 3 kg that are typically used by consumers and that can be separated based upon the collection channel, should be considered as portable. In order to ensure that the collected batteries are classified in the same way as the batteries put on the market declared by the producers, Eucobat proposes that the batteries above 3 kg that cannot be used by private households are considered industrial batteries. 5. About Eucobat Eucobat aisbl is the European association of national collection schemes for batteries. They assure that all waste batteries are collected and recycled in an ecological sound way, and contribute this way to a better environment. Eucobat aisbl October 2013