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Topic:
<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
<strong>Labelling</strong>

<br />


<br />

Overview

<br />


<br />

<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
technical
regulations
provide
a
vehicle
<strong>for</strong>
promoting
energy
efficiency,
as
<br />

well
as
credible
solutions
<strong>for</strong>
monitoring,
measuring,
verifying
<strong>and</strong>
reporting
greenhouse
<br />

gas
emissions
<strong>and</strong>
their
trading.
While
energy
efficiency
st<strong>and</strong>ards
are
widespread
<br />

around
the
world,
there
are
great
variations
in
the
technical
specifications,
the
testing
<br />

procedures
<strong>and</strong>
modalities
of
en<strong>for</strong>cement
across
countries.
<br />


<br />

Consumer
in<strong>for</strong>mation
that
can
influence
purchasing
decisions
is
an
essential
component
<br />

of
market
trans<strong>for</strong>mation.
Energy‐in<strong>for</strong>mation
labels
are
required
by
all
OECD
<strong>and</strong>
EU
<br />

member
countries,
<strong>and</strong>
by
a
growing
number
of
non‐OECD
countries.
In
addition,
<br />

voluntary
seal‐of‐approval
labels
can
be
selectively
awarded
<strong>for</strong>
products
that
meet
strict
<br />

environmental
requirements
<br />


<br />

In
addition
to
schemes
that
look
at
energy,
labelling
schemes
that
address
carbon
<br />

efficiency
by
looking
at
the
full
life
cycle
of
traded
goods
are
at
an
early
phase
of
<br />

development.
The
role
of
carbon
labelling
schemes
is
likely
to
grow
in
the
future,
<br />

providing
consumers
with
the
option
of
decreasing
their
personal
carbon
footprints.
<br />

These
schemes
provide
positive
product
differentiation
<strong>and</strong>
market
opportunities.
<br />


<br />

<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
labels
focusing
on
carbon
content
deal
directly
with
the
controversial
<br />

issue
of
process
<strong>and</strong>
production
methods
(PPMs).
Although
there
seems
to
be
a
growing
<br />

acceptance
of
the
use
of
PPMs
<strong>for</strong>
specific
<strong>and</strong>
defined
purposes—such
as
protecting
<br />

exhaustible
natural
resources,
<strong>and</strong>
human
health
<strong>and</strong>
safety—there
is
also
concern
<br />

among
developing
countries
in
particular
that
they
be
abused
<strong>for</strong>
protectionist
purposes.
<br />

Developing
countries
would
like
to
keep
“non‐product
related”
PPMs
in
particular
out
of
<br />

the
WTO,
that
is
to
say,
cases
in
which
there
is
no
way
to
distinguish
how
a
final
product
<br />

was
produced
based
on
the
characteristics
of
the
final
product.
For
example,
it
is
not
<br />

possible
to
tell
when
examining
a
computer
whether
it
was
produced
in
a
factory
<br />

powered
by
wind,
hydro
or
coal
power.
<br />


<br />

From
a
trade
policy
perspective,
st<strong>and</strong>ards
<strong>and</strong>
labels
as
such
represent
non‐tariff
<br />

measures
<strong>and</strong>
are
potential
obstacles
to
market
entry.
Many
producers
are
concerned
<br />

that
labelling
<strong>and</strong>
st<strong>and</strong>ards
may
become
barriers
to
market
access.
They
see
the
rise
in
<br />

such
non‐tariff
barriers
as
potential
obstacles
to
market
entry
<strong>and</strong>
a
vehicle
<strong>for</strong>
green
<br />

protectionism.

<br />


<br />

The
WTO
establishes
a
number
of
conditions
that
will
be
relevant
to
national
<strong>and</strong>
<br />

regional
ef<strong>for</strong>ts
to
promote
energy
efficiency.
In
addition,
WTO
rules
require
st<strong>and</strong>ards
<br />

<strong>and</strong>
technical
regulations
to
be
based
on
international
st<strong>and</strong>ards
where
they
exist.
<br />


<br />


Related
WTO
agreements

<br />


<br />

GATT
<br />


<br />

WTO
Agreement
on
Technical
Barriers
to
Trade
<br />


<br />

WTO
Agreement
on
Sanitary
<strong>and</strong>
Phytosanitary
<strong>St<strong>and</strong>ards</strong>
<br />


Further
reading

<br />


<br />

Appleton,
A.
(1997).
Environmental
labelling
programmes:
Trade
law
implications.
<br />

London:
Kluwer
Law
<strong>International</strong>.
<br />


<br />

Bernasconi‐Osterwalder,
N.,
Magraw,
D.,
Oliva,
M.J.,
Orellana,
M.
<strong>and</strong>
Tuerk,
E.
(2005).
<br />

Environment
<strong>and</strong>
trade:
A
guide
to
WTO
jurisprudence.
London:
Center
<strong>for</strong>
<strong>International</strong>
<br />

Environmental
Law
(CIEL)
<strong>and</strong>
Earthscan
<br />

www.ciel.org/Publications/Environment_<strong>and</strong>_Trade2006.pdf.


<br />


<br />

Charnovitz,
S.
(2002).
The
law
of
environmental
PPMs
in
the
World
Trade
Organization:
<br />

Debunking
the
myth
of
illegality.
Yale
Journal
of
<strong>International</strong>
Law,
27(1):
59–110.
<br />


<br />

CLASP.
(2007).
<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
labeling
guidebook.
Washington,
D.C.:
Collaborative
<br />

Labeling
<strong>and</strong>
Appliance
<strong>St<strong>and</strong>ards</strong>
Program.
<br />


<br />

Gaines,
S.E.
2(002).
Processes
<strong>and</strong>
production
methods:
How
to
produce
sound
policy
<strong>for</strong>
<br />

environmental
PPM‐based
trade
measures?
Columbia
Journal
of
Environmental
Law,
<br />

27(2):
383–432.
<br />


<br />

Howse,
R.
<strong>and</strong>
Regan,
D.
(2000).
The
product/process
distinction:
An
illusory
basis
<strong>for</strong>
<br />

disciplining
‘unilateralism’
in
trade
policy.
European
Journal
of
<strong>International</strong>
Law,
11(2):
<br />

249–290.
<br />


<br />

Howse,
R.,
van
Bork,
P.
<strong>and</strong>
Hebebr<strong>and</strong>,
C.
(2006).
WTO
disciplines
<strong>and</strong>
biofuels:
<br />

Opportunities
<strong>and</strong>
constraints
in
the
creation
of
a
global
marketplace.
Washington
D.C.:
<br />

<strong>International</strong>
Food
&
Agriculture
Trade
Policy
Council.
<br />

www.agritrade.org/Publications/DiscussionPapers/WTO_Disciplines_Biofuels.pdf.


<br />


<br />

<strong>International</strong>
Energy
Agency
(IEA).
(2003).
Cool
appliances:
Policy
strategies
<strong>for</strong>
energyefficient
homes.
Paris:
IEA.
<br />


<br />

IEA.
(2006).
Light’s
labour’s
lost:
Policies
<strong>for</strong>
energy‐efficient
lighting.
Paris:
IEA.
<br />


<br />

IEA.
(2007a).
Mind
the
gap:
Quantifying
principal‐agent
programs
in
energy
efficiency.
<br />

Paris:
IEA.
<br />


<br />

IEA.
(2007b).
Experience
with
energy
efficiency
regulations
<strong>for</strong>
electrical
equipment.
<br />

In<strong>for</strong>mation
Paper.
Paris:
IEA.
<br />


<br />

Organisation
<strong>for</strong>
Economic
Co‐operation
<strong>and</strong>
Development
(OECD).
(1997).
Processes
<strong>and</strong>
<br />

production
methods
(PPMs):
Conceptual
framework
<strong>and</strong>
considerations
on
use
of
PPMbased
trade
measures.
OCDE/GD(97)137.
Paris:
OECD.
<br />


Potts,
J.
(2008).
The
legality
of
PPMs
under
the
GATT:
Challenges
<strong>and</strong>
opportunities
<strong>for</strong>
<br />

sustainable
trade
policy.
Winnipeg:
<strong>International</strong>
<strong>Institute</strong>
<strong>for</strong>
<strong>Sustainable</strong>
Development.
<br />

www.iisd.org/pdf/2008/ppms_gatt.pdf.


<br />


<br />

Waide,
P.
(2008).
Market
trans<strong>for</strong>mation
initiatives
from
around
the
world.
Presented
at
<br />

the
ACEEE
Market
Trans<strong>for</strong>mation
Symposium,
March
30–April
1,
2008.
Washington,
<br />

D.C.
<br />


<br />


Sub‐topic:
<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
labelling
–
Energy
st<strong>and</strong>ards
<strong>and</strong>
labels
<br />


<br />

Overview

<br />


<br />

Climate
change
policy
aims
to
set
countries
onto
a
path
towards
an
efficient,
low‐carbon
<br />

energy
future.
According
to
the
World
Energy
Outlook
<strong>and</strong>
other
studies,
energy
<br />

efficiency
improvements
provide
one
of
the
most
cost‐effective
ways
to
reduce
energy
<br />

bills
<strong>and</strong>
greenhouse
gas
emissions,
lower
the
cost
of
energy
services
<strong>and</strong>
diminish
<br />

energy
import
dependence.
This
potential
is
particularly
important
<strong>for</strong>
developing
<br />

countries
with
high
energy‐import
bills.
<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
labelling
are
some
of
the
most
<br />

important
tools
to
increase
efficiency,
<strong>and</strong>
WTO
rules
set
out
the
parameters
<strong>for</strong>
<br />

st<strong>and</strong>ards
<strong>and</strong>
labelling.

<br />


<br />

For
the
time
being,
energy
efficient
end‐use
technologies
are
still
relatively
underutilized
<br />

because
of
numerous
market
barriers.
Governments
are
increasingly
recognizing
the
<br />

need
to
overcome
these
barriers
through
direct
policy
measures.
The
most
widely
<br />

deployed
policies
are
m<strong>and</strong>atory
minimum
energy
per<strong>for</strong>mance
st<strong>and</strong>ards
(MEPS)
<strong>and</strong>
<br />

energy
labelling,
both
of
which
have
been
highly
effective
in
improving
equipment
<br />

energy
per<strong>for</strong>mance.
<br />


<br />

As
the
large
majority
of
energy‐using
equipment
is
traded
internationally,
these
policies
<br />

have
implications
<strong>for</strong>
the
nature
<strong>and</strong>
cost
of
international
trade.
Different
regional
<strong>and</strong>
<br />

national
st<strong>and</strong>ards
<strong>for</strong>
testing
<strong>and</strong>
con<strong>for</strong>mity
assessment
procedures,
as
well
as
import
<br />

tariff
regimes,
add
to
the
cost
of
trading
energy‐efficient
products.
<br />


<br />

Testing
<strong>and</strong>
con<strong>for</strong>mity
assessment
procedures
are
complex
<strong>and</strong>
reflect
both
historic
<strong>and</strong>
<br />

user
difference
across
nations.
Any
multilateral
decision
to
develop
internationallyagreed
criteria
<strong>for</strong>
relatively
energy‐efficient
goods,
based
on
comparable
test
<br />

procedures,
would
need
to
be
justified
by
the
expectation
that
the
net
benefits
of
<br />

increased
trade
in
goods
outweigh
the
inconvenience
of
harmonization.
Future
energy
<br />

st<strong>and</strong>ards
<strong>and</strong>
labelling
schemes
would
need
to
balance
the
need
<strong>for</strong>
accurate
<strong>and</strong>
useful
<br />

data
with
the
need
to
be
simple,
transparent,
<strong>and</strong>
involve
sufficiently
low
transaction
<br />

costs
to
include
small
countries
<strong>and</strong>
players.
<br />


Key
issues

<br />


<br />

The
development
<strong>and</strong>
dissemination
of
new
<strong>and</strong>
efficient
energy
technologies
provides
<br />

one
important
element
in
the
levelling
off
of
the
current
energy
growth
trends,
<br />

contributing
to
the
reduction
of
emissions
from
energy
use.
<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
technical
<br />

regulations
provide
a
vehicle
<strong>for</strong>
promoting
energy
efficiency.
According
to
the
<br />

<strong>International</strong>
Energy
Agency,
accelerated
energy
efficiency
improvement
is
credited
with
<br />

78
per
cent
of
the
emissions
reduction
savings
potential
by
2030,
making
it
critical
<strong>for</strong>
a
<br />

future
climate
regime
to
harness
that
potential.

<br />


<br />

Trade
in
energy‐efficient
products
<br />


<br />

Given
that
the
vast
majority
of
energy‐using
equipment
<strong>and</strong>
consumer
products
are
<br />

traded
globally,
an
important
question
is
how
markets
can
be
made
to
work
better
<strong>for</strong>
<br />

the
scaling
up
of
energy
efficiency.
A
global
trade‐led
market
trans<strong>for</strong>mation
ef<strong>for</strong>t
<br />

would
require
exp<strong>and</strong>ing
markets
<strong>for</strong>
more
advanced
technologies,
while
eliminating
<br />

outdated
equipment.
M<strong>and</strong>atory
minimum
energy
per<strong>for</strong>mance
st<strong>and</strong>ards
(MEPS)
aim
to
<br />

push
up
the
efficiency
level
of
new
products
entering
the
market.
Governments
can
take
<br />

these
a
step
further
by
phasing
out
older
technologies
<strong>and</strong>
products
that
use
more
<br />

energy
<strong>and</strong>
produce
more
greenhouse
gas
emissions.
Examples
include
replacing
<br />

inc<strong>and</strong>escent
light
bulbs
with
more
energy‐efficient
compact
fluorescent
lamps,
which
<br />

use
only
about
20
per
cent
of
the
power
to
produce
the
same
amount
of
light
<strong>and</strong>
last
<br />

longer.
Energy
in<strong>for</strong>mation
labels
can
help
consumers
made
climate‐friendly
purchasing
<br />

decisions.
<br />


<br />

Energy
per<strong>for</strong>mance
st<strong>and</strong>ards
<br />


<br />

Several
countries
have
taken
steps
aimed
at
directing
energy‐per<strong>for</strong>mance
st<strong>and</strong>ards
<strong>for</strong>
<br />

a
range
of
consumer
appliances.
M<strong>and</strong>atory
minimum
energy‐per<strong>for</strong>mance
st<strong>and</strong>ards
<br />

(MEPS)
have
been
introduced
in
most
OECD
countries,
but
also
in
many
developing
<br />

countries.
In
2006,
57
countries
representing
80
per
cent
of
the
world’s
population
had
<br />

energy‐efficiency
st<strong>and</strong>ards
<strong>and</strong>
labelling
programs
in
place.

<br />


<br />

Minimum
energy‐per<strong>for</strong>mance
requirements
have
taken
various
<strong>for</strong>ms
in
different
<br />

countries,
with
MEPS
often
coupled
with
more
stringent
st<strong>and</strong>ards
or
by
more
<br />

restrictive,
voluntary
agreements
between
government
<strong>and</strong>
industry.
<br />


<br />

<strong>Labelling</strong>
<br />


<br />

Consumer
in<strong>for</strong>mation
that
can
influence
purchasing
decisions
is
an
essential
component
<br />

of
market
trans<strong>for</strong>mation.
Most
countries
that
regulate
MEPS
also
require
energyin<strong>for</strong>mation
labels
to
be
displayed
on
the
same
products.
Energy‐in<strong>for</strong>mation
labels
are
<br />

required
by
all
OECD
<strong>and</strong>
EU
member
countries,
<strong>and</strong>
by
a
growing
number
of
non‐OECD
<br />

countries.





<br />

The
main
piece
of
in<strong>for</strong>mation
provided
by
a
m<strong>and</strong>atory
energy‐in<strong>for</strong>mation
label
is
the
<br />

appliance’s
estimated
energy
consumption
in
kWh/year,
or
per
operating
cycle
derived
<br />

from
st<strong>and</strong>ard
tests.
The
label
typically
shows
the
product
group
type
<strong>and</strong>
size
category
<br />

within
which
the
model
should
be
compared,
as
well
as
the
energy
consumption
of
the
<br />

most
<strong>and</strong>
least
energy
efficient
models
within
the
product
group
<strong>for</strong>
comparison.
<br />

Increasingly
popular
are
the
use
of
visual
aids,
such
as
the
EU’s
colour‐coded
<br />

per<strong>for</strong>mance
scale
from
G
(lowest
efficiency)
to
A
(Highest
efficiency),
to
increase
quick
<br />

comparison
between
different
appliances
<strong>and</strong>
to
identify
the
most
efficient
models.
<br />


<br />

In
addition,
voluntary
seal‐of‐approval
labels
can
be
selectively
awarded
<strong>for</strong>
products
<br />

that
meet
strict
environmental
requirements.
Ecological
or
environmental
labelling
<br />

schemes
(“eco‐labels”)
often
augment
energy‐efficiency
criteria
with
other
product
<br />

per<strong>for</strong>mance
criteria,
such
as
<strong>for</strong>
noise,
water
use
or
product
durability,
specifications
<br />

relating
to
the
composition
of
the
product
or
the
product’s
re‐use,
recycling
<strong>and</strong>
disposal
<br />

characteristics.
<br />


<br />

Harmonizing
st<strong>and</strong>ards
<strong>and</strong>
labels
internationally

<br />


<br />

While
energy‐efficiency
st<strong>and</strong>ards
are
widespread
around
the
world,
there
are
great
<br />

variations
in
the
technical
specifications,
the
testing
procedures
<strong>and</strong>
modalities
of
<br />

en<strong>for</strong>cement
across
countries.
Such
differences
are
recognized
in
the
climate
<br />

Convention,
which
notes
in
its
preamble
that
"
environmental
st<strong>and</strong>ards
[…]
should
<br />

reflect
the
environmental
<strong>and</strong>
developmental
context
to
which
they
apply,
<strong>and</strong>
that
<br />

st<strong>and</strong>ards
applied
by
some
countries
may
be
inappropriate
<strong>and</strong>
of
unwarranted
<br />

economic
<strong>and</strong>
social
cost
to
other
countries,
in
particular
developing
countries."

<br />


<br />

An
ef<strong>for</strong>t
towards
harmonization
of
energy
efficiency
st<strong>and</strong>ards
would
generate
greater
<br />

coherence
at
the
international
level.
Whether
that
can
be
achieved
under
the
UNFCCC
<br />

umbrella
or
through
other
<strong>for</strong>ums,
such
as
the
<strong>International</strong>
<strong>St<strong>and</strong>ards</strong>
Organisation
<br />

(ISO),
requires
further
consideration.
Overall,
views
diverge
on
the
desirability
<strong>and</strong>
need
<br />

<strong>for</strong>
harmonization
of
energy
st<strong>and</strong>ards
at
the
international
level.
Some
argue
that
this
is
<br />

a
sphere
<strong>for</strong>
“regulatory
competition”
where
consumers
play
an
arbitration
function.
<br />

Others
point
out
that
in
aligning
processes
<strong>for</strong>
setting
<strong>and</strong>
testing
st<strong>and</strong>ards,
policymakers
should
take
care
not
to
threaten
legitimate
functional
distinctions
<strong>and</strong>
the
<br />

integrity
of
st<strong>and</strong>ards
<strong>and</strong>
labelling
schemes.
<br />


<br />

<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
labels
as
non‐tariff
barriers
<br />


<br />

From
a
trade
policy
perspective,
st<strong>and</strong>ards
<strong>and</strong>
labels
represent
non‐tariff
measures
<strong>and</strong>,
<br />

as
such,
are
potential
obstacles
to
market
entry.
Different
efficiency
st<strong>and</strong>ards
<strong>and</strong>
<br />

labels,
as
well
as
test
procedures,
are
reported
to
be
the
most
frequent
concern
of
the
<br />

WTO
under
the
Agreement
on
Technical
Barriers
to
Trade.
WTO
rules,
through
<br />

disciplines
on
areas
such
as
subsidies,
border
measures
<strong>and</strong>
technical
requirements,



there<strong>for</strong>e
have
implications
<strong>for</strong>
the
options
available
to
countries
in
implementing
<br />

climate
measures
<strong>and</strong>
promoting
the
use
of
energy‐efficient
products.

<br />


<br />

However,
st<strong>and</strong>ards
<strong>and</strong>
labelling
schemes
also
provide
opportunities
<strong>for</strong>
positive
<br />

product
differentiation
<strong>and</strong>
market
opportunities.
In
general,
WTO
rules
require
<br />

st<strong>and</strong>ards
<strong>and</strong>
technical
regulations
to
be
based
on
international
st<strong>and</strong>ards
where
they
<br />

exist.

<br />


<br />






Sub‐topic:
<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
labelling
–
Carbon
labels

<br />


<br />

Overview

<br />


<br />

The
carbon
embedded
in
internationally
traded
goods—its
measurement,
as
well
as
<br />

different
ways
of
communicating
the
climate
impact—is
a
rapidly
emerging
factor
<br />

expected
to
significantly
influence
consumer
behaviour
in
major
markets
across
the
<br />

globe.
Changing
consumption
patterns
will
be
important
within
the
wide
spectrum
of
<br />

measures
needed
to
address
climate
change.
New,
mainly
private‐sector
driven
carbon
<br />

labelling
schemes
raise
a
number
of
issues,
however.
They
will
affect
a
wide
range
of
<br />

stakeholders,
including
producers
<strong>and</strong>
consumers,
the
public
<strong>and</strong>
private
sector,
<strong>and</strong>
<br />

developing
<strong>and</strong>
developed
countries,
along
all
levels
of
globally‐distributed
value
chains.
<br />

So
far,
public
scrutiny
<strong>and</strong>
debate
around
carbon
labelling
has
been
limited.

<br />


<br />

While
the
intergovernmental
processes
under
the
UNFCCC
<strong>and</strong>
the
Doha
Round
are
<br />

advancing
at
a
slow
pace,
carbon
labelling
schemes
as
well
as
initiatives
to
measure
<br />

carbon
<strong>and</strong>
address
carbon
hotspots
within
the
value
chains
of
globally
traded
goods,
<br />

both
agricultural
<strong>and</strong>
industrial,
are
moving
ahead.
The
measurement
of
the
carbon
<br />

embedded
within
individual
products
is
rapidly
becoming
more
sophisticated—<strong>and</strong>
is
<br />

certainly
costly.
Early
experiments,
which
largely
singled
out
the
“carbon
hotspot”
airfreighting
of
fresh
fruits
<strong>and</strong>
flowers
entailed
<strong>and</strong>
communicated
this
through
airplane
<br />

stickers,
have
been
largely
discredited.
Newer
initiatives
seek
to
underst<strong>and</strong>
the
full
<br />

lifecycle
of
any
given
good.
However,
drawing
the
boundaries
<strong>for</strong>
such
lifecycle
analysis
<br />

becomes
close
to
impossible.
And
yet,
simplifications
must
be
made
to
render
any
<br />

scheme
workable,
<strong>and</strong>
costs
bearable—especially
<strong>for</strong>
smaller
producers.

<br />


<br />

For
developing
country
players
to
be
able
to
participate
in
the
schemes,
technical
<br />

assistance
<strong>and</strong>
support
targeting
smaller
producers
in
particular
would
be
needed.
<br />

Transparency
is
important
to
allay
fears
that
the
schemes
are
just
the
newest
in
a
<br />

seemingly
never‐ending
stream
of
developed
country
non‐tariff
barriers
used
as
green
<br />

protectionism.
Depending
on
how
carbon‐labelling
schemes
are
developed,
they
could
<br />

well
provide
new
market
opportunities
<strong>and</strong>
niches
<strong>for</strong>
developing
countries
based
on
<br />

carbon
efficiency.

<br />


<br />

Meanwhile,
<strong>for</strong>
consumers
to
trust
new
carbon
labels,
they
must
be
developed
in
an
<br />

open
<strong>and</strong>
transparent
manner,
with
clarity
around
what
greenhouse
gas
emissions
they
<br />

account
<strong>for</strong>,
<strong>and</strong>
which
ones
they
do
not—how
they
interact
with
other
social
<strong>and</strong>
<br />

environmental
st<strong>and</strong>ards,
<strong>and</strong>
how
they
affect
development
opportunities
in
developing
<br />

countries.
However,
they
must
also
be
simple
to
underst<strong>and</strong>
in
order
to
be
relevant.
<br />


Key
issues

<br />


<br />

The
food
miles
debate
<br />


<br />

Simply
put,
food
miles
are
the
distance
that
food
travels
from
the
field
where
it
was
<br />

grown
to
the
plate
where
it
is
consumed.
The
objective
in
measuring
these
distances
is
to
<br />

determine
the
environmental
impact
based
on
the
carbon
emitted
during
transport,
<br />

whether
by
air,
sea,
lorry
or
car.
Most
bulk
products
are
shipped
by
sea;
fresh
produce,
<br />

however,
needs
to
reach
the
consumer
quickly
<strong>and</strong>
airfreight
is
the
only
option.
The
<br />

carbon
emissions
associated
with
air‐freighted
products
are
high—177
times
greater
<br />

than
<strong>for</strong>
products
being
shipped
by
sea.
This
means
that
mangos
from
Brazil,
<br />

strawberries
from
Kenya
<strong>and</strong>
asparagus
from
Mexico
being
sent
to
European
<br />

supermarkets
have
a
significant
environmental
impact
based
on
the
miles
they
have
<br />

travelled
to
reach
their
final
destination.
Among
all
food
products
transported
<br />

internationally,
the
most
miles
are
clocked
by
such
out‐of‐season
fruits
<strong>and</strong>
vegetables
<br />

arriving
from
distant
countries.
<br />


<br />

For
many
governments,
supermarkets,
<strong>and</strong>
even
some
environmental
advocates,
the
<br />

simple
solution
to
reducing
the
carbon
miles
generated
by
food
travel
is
to
buy
locally.
In
<br />

supermarkets
throughout
Europe,
fresh
produce
from
abroad
is
being
labelled
with
a
<br />

sticker
depicting
an
airplane
to
alert
consumers
that
it
was
imported
via
air
freight.
The
<br />

policy
behind
this
labelling
is
to
encourage
consumers
to
purchase
local
products
<strong>and</strong>
<br />

also
to
provide
incentives
to
the
company
itself
to
source
as
much
food
locally
as
<br />

possible,
to
grow
local
supply
networks
<strong>and</strong>
to
offset
carbon
emissions
from
air‐freighted
<br />

products.

<br />


<br />

Problems
with
food
miles
<br />


<br />

In
most
countries,
even
food
produced
nationally
travels
extensively
be<strong>for</strong>e
getting
to
<br />

retailers.
While
these
trips
are
made
by
lorry
as
opposed
to
airplane,
the
carbon
emitted
<br />

during
cross‐country
tours
is
not
negligible.
Add
in
the
cars
used
by
most
consumers
to
<br />

get
from
their
homes
to
the
market,
<strong>and</strong>
the
carbon
footprint
is
on
par
with
that
of
airfreighted
products.

<br />


<br />

Another
major
challenge
with
buying
local
is
that
transport
is
only
part
of
the
equation.
<br />

Agricultural
methods
used
in
producing
food,
the
types
of
processing
manufacturers
use,
<br />

<strong>and</strong>
storage
methods
also
play
an
important
role.
Studies
have
shown,
<strong>for</strong>
instance,
that
<br />

lamb
grown
in
the
U.K.
<strong>and</strong>
sold
locally
has
a
greater
carbon
footprint
than
lamb
grown
<br />

in
New
Zeal<strong>and</strong>,
11,000
miles
away.
This
is
because
New
Zeal<strong>and</strong>
uses
more
energyefficient
<strong>and</strong>
environmentally‐friendly
methods
<strong>for</strong>
raising
its
lamb
than
the
U.K.
does.

<br />


<br />

Beyond
the
environmental
aspects
of
food
miles,
there
are
social
implications
to
be
<br />

considered.
Development
advocates
say
it
does
not
make
sense
to
halt
air‐freighted
<br />

products
<strong>and</strong>
encourage
local
food
production,
as
this
would
hurt
the
poorest
suppliers



in
least‐developed
<strong>and</strong>
developing
countries
that
rely
heavily
on
revenue
from
exported
<br />

products.
Growing
fresh
produce
provides
a
crucial
source
of
income
<strong>for</strong>
the
poorest
of
<br />

the
poor
in
these
already
vulnerable
countries,
<strong>and</strong>
countless
livelihoods
would
be
at
<br />

stake.
The
fresh
fruit
<strong>and</strong>
vegetable
trade
with
the
U.K.,
<strong>for</strong>
instance,
generates
US$400
<br />

million,
which
supports
one
million
people
living
in
Africa.
If
developed
countries
were
to
<br />

buy
only
locally,
the
development
implications
would
be
significant.

<br />


<br />

Carbon
lifecycle
analysis
<br />


<br />

The
failure
of
the
“food
miles”
concept
to
account
<strong>for</strong>
social
implications
has
caused
<br />

many
in
the
trade
<strong>and</strong>
development
community
to
critique
the
concept.
So
too
have
<br />

some
environmentalists
that
believe
the
idea
is
too
simplistic
in
its
focus
on
carbon
<br />

emitted
solely
during
transport.
These
critics
are
instead
calling
<strong>for</strong>
a
full
life‐cycle
<br />

analysis
(LCA)
of
the
carbon
footprint;
that
is,
measuring
the
carbon
emissions
from
the
<br />

field
to
the
plate
by
accounting
<strong>for</strong>
agricultural
methods,
processing,
energy,
soil,
<br />

distribution
<strong>and</strong>
everything
in
between.
The
full
life
cycle
is
a
kind
of
cradle‐to‐grave
<br />

approach
<strong>for</strong>
determining
the
carbon
impact
of
foodstuffs.
As
this
calculation
is
based
<br />

not
only
on
miles
travelled
but
on
carbon
emitted
during
the
entire
production
process,
<br />

it
is
less
likely
to
discriminate
against
developing
country
exports
the
way
food
miles
<br />

schemes
have
done.

<br />


<br />

Some
companies
<strong>and</strong>
supermarket
chains
have
started
implementing
carbon
labelling
<br />

programs
based
on
LCA,
<strong>and</strong>
are
moving
from
agricultural
products
(with
simple
value
<br />

chains)
to
also
include
more
complex
industrial
products.

<br />


<br />

<strong>Labelling</strong>
st<strong>and</strong>ards
that
ensure
consistency
<strong>and</strong>
comparability
among
products
carrying
<br />

the
tag
are
being
created
by
the
Carbon
Trust,
a
private
company
established
by
the
U.K.
<br />

government
to
help
Britain
move
towards
a
low
carbon
economy.
The
Carbon
Trust
is
<br />

working
to
develop
an
agreed
method
to
measure
the
embodied
greenhouse
gases
<br />

among
a
wide
range
of
products.
Once
calculated,
the
label
will
show
the
amount
of
<br />

carbon
in
grams
much
like
the
nutrition
label
provides
the
amount
of
sodium
or
fat
in
<br />

foods.

<br />


<br />

The
st<strong>and</strong>ards
<strong>and</strong>
the
labels
are
still
in
their
trial
stages.
Once
the
st<strong>and</strong>ard
is
in
place,
<br />

manufacturers
can
voluntarily
sign
up
to
have
their
products
carry
the
label.
The
process
<br />

of
certification
<strong>and</strong>
monitoring
will
be
h<strong>and</strong>led
by
independent
companies
to
ensure
that
<br />

manufactures
are
adhering
to
the
st<strong>and</strong>ards.
<br />


<br />

Private
sector
st<strong>and</strong>ards
<strong>and</strong>
the
WTO
<br />


<br />

Carbon
labelling
schemes
developed
thus
far
have
all
been
initiated
by
the
private
sector.
<br />

Within
the
WTO
Committee
on
Sanitary
<strong>and</strong>
Phytosanitary
<strong>St<strong>and</strong>ards</strong>
(SPS),
debate
is
<br />

ongoing
on
these
types
of
st<strong>and</strong>ards,
which
some
Members
consider
to
be
the
new



frontier
of
protectionism.
As
actual
trade
tariffs
come
down,
these
types
of
non‐tariff
<br />

barriers
take
their
place.
<br />


<br />

A
number
of
developing
countries,
in
particular,
have
been
highly
critical
of
the
use
of
<br />

private
sector
st<strong>and</strong>ards,
arguing
that
they
reduce
the
efficacy
of
the
SPS
regime
by
<br />

creating
higher
st<strong>and</strong>ards
outside
of
government
control.
These
countries
stress
that
the
<br />

st<strong>and</strong>ards
are
arbitrary
<strong>and</strong>
end
up
penalizing
developing
countries
<strong>and</strong>
small
farmers
<br />

exporting
to
the
North
since
they
lack
capacity
<strong>and</strong>
funding
to
comply.
Many
developing
<br />

countries
argue
that
governments
should
to
take
responsibility
<strong>for</strong>
st<strong>and</strong>ards
set
by
<br />

private‐sector
actors
within
their
boundaries.
Others,
especially
developed
countries,
say
<br />

that
private
sector
st<strong>and</strong>ards
fall
outside
the
remit
of
the
WTO
<strong>and</strong>
its
SPS
Agreement.
<br />

Under
the
Agreement
on
Technical
Barriers
to
Trade
(TBT),
which
would
appear
to
apply
<br />

more
directly
to
carbon
labelling
initiatives,
private
sector
labelling
schemes
are
covered
<br />

in
addition
to
public
labelling
schemes.
However,
there
is
no
ongoing
debate
on
the
topic
<br />

within
the
TBT
Committee.
<br />


Sub‐topic:
<strong>St<strong>and</strong>ards</strong>
<strong>and</strong>
labelling
–
PPMs
<br />


<br />

Overview

<br />


<br />

Discussions
<strong>and</strong>
developments
at
the
trade
<strong>and</strong>
climate
change
interface
touch
directly
<br />

on
the
issue
of
how
the
WTO
deals
with
process
<strong>and</strong>
production
methods
(PPMs).
One
of
<br />

the
key
principles
underpinning
the
WTO
is
that
Members
cannot
discriminate
among
<br />

“like”
products,
no
matter
in
which
Member
nation
they
are
produced.
In
order
to
make
<br />

distinctions
regarding
the
carbon
impact
of
a
product,
they
way
it
was
produced
is
key.
<br />

However,
this
is
not
always
obvious
just
by
looking
at
the
final
product
itself—is
it
“like”
<br />

or
“unlike”
a
similar
product
<strong>for</strong>
which
massive
amounts
of
greenhouse
gases
were
<br />

released
during
production?

<br />


<br />

Taking
PPMs
into
consideration
implies
looking
beyond
the
borders
of
countries
at
<br />

production
issues.
Many
countries—especially
developing
ones—feel
this
unjustly
<br />

impinges
on
sovereignty.
They
feel
concerned
especially
because
most
PPM‐based
<br />

st<strong>and</strong>ards
<strong>and</strong>
labels
are
imposed
by
rich
developed
countries
<strong>and</strong>
have
the
potential
<br />

negatively
affect
the
exports
of
developing
countries.
The
issue
is
relevant
not
only
<strong>for</strong>
<br />

carbon
st<strong>and</strong>ards
<strong>and</strong>
labelling
initiatives,
but
also
within
the
Doha
Round
negotiations
<br />

on
the
liberalization
of
environmental
goods
<strong>and</strong>
services,
including
climate‐friendly
<br />

goods.
<br />


<br />

WTO
jurisprudence
does,
however,
seem
to
imply
that
the
use
of
PPMs
is
legal,
as
long
<br />

as
the
country
restricting
imports
based
on
PPMs
has
made
ef<strong>for</strong>ts
to
ensure
that
the
<br />

restrictions
are
fair,
transparent
<strong>and</strong>
based
on
a
cooperative
approach.
As
such,
an
<br />

importing
country
is
not
imposing
its
own
st<strong>and</strong>ards
<strong>and</strong>
norms
on
other
countries,
but
<br />

rather
making
sure
that
products
entering
its
own
territory
con<strong>for</strong>m
to
such
norms.
Here,
<br />

it
would
appear
to
be
important
that
the
way
the
exporter
chooses
to
con<strong>for</strong>m
with
the
<br />

norms
is
not
restricted,
but
that
the
exporter
can
embark
on
its
own
path
to
achieve
the
<br />

same
goals.
For
example,
process‐related
greenhouse
gas
restrictions
can
be
achieved
in
<br />

a
wide
variety
of
ways.
This
is
recognized
under
the
UNFCCC,
which
allows
countries
to
<br />

choose
themselves
what
policies
<strong>and</strong>
measures
to
use
to
achieve
climate
goals.
<br />


Key
issues
<br />


<br />

Competitiveness
<strong>and</strong>
border
adjustments
<br />


<br />

Beyond
being
directly
applicable
to
carbon
labelling
schemes
<strong>and</strong>
certain
climate
<strong>and</strong>
<br />

energy‐related
st<strong>and</strong>ards,
PPMs
also
play
a
role
in
other
climate
measures
countries
are
<br />

contemplating
to
tackle
climate
change.
As
some
countries
take
on
stricter
climate
<br />

targets
than
others,
they
will
implement
a
wide
range
of
policies
<strong>and</strong>
measures
to
<br />

implement
these
targets.
These
policies
will
often
make
production
in
these
countries
<br />

more
expensive
due
to
higher
energy
prices,
requirements
to
buy
carbon
credits
under
<br />

emissions
trading
schemes,
<strong>and</strong>
so
<strong>for</strong>th.
Countries
are
there<strong>for</strong>e
concerned
that
by
<br />

taking
on
climate
change
commitments,
they
will
put
their
industries—at
least
the
<br />

energy
<strong>and</strong>
carbon‐intensive
ones—at
a
disadvantage.
<br />


<br />

For
this
reason,
they
are
looking
to
take
measures
to
ensure
that
their
exports
are
not
<br />

penalized
on
the
global
markets,
<strong>and</strong>
to
avoid
“leakage,”
that
is,
relocation
of
<br />

greenhouse
gas
intensive
industries
to
slacker
jurisdictions
with
associated
higher
overall
<br />

greenhouse
gas
emissions.
They
are
looking
at
different
options,
such
as
different
types
<br />

of
border
adjustments
that
would
level
the
carbon
playing
field.
Such
adjustments
would
<br />

have
to
directly
factor
in
PPMs.
<br />


<br />

Current
discussions
on
“embedded”
carbon
also
relate
directly
to
PPMs.
This
refers
to
<br />

the
fact
that
carbon
emissions
related
to
the
production
of
a
good
are
accounted
<strong>for</strong>
in
<br />

the
country
of
manufacture,
not
consumption,
in
national
carbon
inventories
under
the
<br />

UNFCCC.
Some
have
argued
that
carbon
accounting
systems
should
be
revised
on
this
<br />

point,
though
any
practical
ef<strong>for</strong>t
to
move
in
this
direction
remains
daunting.

<br />


<br />

Certification
schemes

<br />


<br />

Closely
linked
to
carbon
labelling
schemes,
schemes
certifying
traded
goods
from
a
<br />

carbon
vantage
point
<strong>and</strong>
taking
on‐board
additional
sustainability
criteria
are
on
the
<br />

rise.
For
example,
the
EU
is
planning
a
certification
scheme
<strong>for</strong>
biofuels
that
will
set
<br />

sustainability
requirements
beyond
carbon
impact,
including
secondary
impacts
on
l<strong>and</strong>
<br />

use
<strong>and</strong>
biodiversity,
<strong>and</strong>
requiring
producers
to
be
parties
to
a
number
of
international
<br />

agreements
on
environmental
<strong>and</strong>
labour
issues
(the
latter
in
particular
being
a
longst<strong>and</strong>ing
controversial
issue
<strong>for</strong>
developing
countries,
<strong>and</strong>
a
major
reason
they
have
<br />

tended
to
oppose
bringing
PPMs
within
the
WTO).
Major
producer
countries
have
<br />

already
threatened
to
challenge
this
scheme
at
the
WTO.
If
this
were
to
happen,
the
<br />

systemic
implications
of
a
ruling
would
be
wide
ranging.

<br />


<br />

Meanwhile,
a
number
of
private
sector
certification
schemes
on
biofuels
are
already
up
<br />

<strong>and</strong>
running,
<strong>and</strong>
many
companies
from
countries
opposed
to
official
biofuels
<br />

certification
schemes
have
signed
on
<strong>and</strong>
helped
develop
them.
Indeed,
one
of
the
<br />

problems
appears
to
be
the
proliferation
of
different
<strong>and</strong>
partially
overlapping
schemes,



which
will
be
difficult
especially
<strong>for</strong>
smaller
producers
<strong>and</strong>
countries
to
navigate,
<br />

influence
<strong>and</strong>
make
use
of.

<br />


<br />

Discrimination
<strong>and</strong>
inclusiveness
<br />


<br />

Developing
countries
have
opposed
the
use
of
process
<strong>and</strong>
production
methods
on
the
<br />

basis
that
it
would
create
a
de
facto
trade
barrier
<strong>for</strong>
them,
since
it
is
only
the
wealthier
<br />

countries
that
would
have
high
st<strong>and</strong>ards
<strong>and</strong>
complex
PPM‐based
labelling
schemes,
<br />

<strong>and</strong>
only
they
have
the
financial
<strong>and</strong>
technical
resources
to
comply
with
them.
<br />


<br />

However,
in
some
cases
developing
countries
might
actually
have
an
advantage
in
terms
<br />

of
producing
cleaner
goods
through
cleaner
processes—<strong>and</strong>
the
possibility
to
capture
<br />

new
markets.
However,
in
order
to
make
use
of
any
such
opportunities,
developing
<br />

countries
need
to
be
involved
in
st<strong>and</strong>ard‐setting
<strong>and</strong>
labelling
processes.
In
this
regard,
<br />

technical
assistance
could
be
provided
both
under
the
WTO
<strong>and</strong>
UNFCCC.

<br />

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