Memorandum submitted by Department for
Environment, Food and Rural Affairs
1. INTRODUCTIONTHE
ROLE OF
DEFRA AND
OTHER PUBLIC
AUTHORITIES IN
RELATION TO
ENVIRONMENTAL LABELLING
1.1 Defra has a number of direct interests
in the subject of environmental labelling.
At a general policy level, we are
interested in the use of information and labelling as part of
a wider potential toolkit for helping to reduce the environmental
impacts of products and services.
We have formal responsibilities in
relation to some particular labelling regimesfor example,
the EU ecolabelling scheme and the EU energy labelling regime,
which are established by legal instruments at EU level.
We are responsible (with the agreement
of the Devolved Administrations) for implementing the standards
for the production of organic food and feed which are set out
in EU law.
1.2 Other Government Departments also have
formal responsibilities for rating and labelling regimes which
cover a significant environmental issues, for example:
The Department for Transport in relation
to the labelling of new cars to show their CO2 emissions.
Communities and Local Government
in relation to the energy efficiency of homes (the Energy Performance
Certificate included in Home Information Packs).
1.3 The Health and Safety Executive has
responsibilities in relation to the regulatory regime for the
classification and labelling of hazardous chemicals. This alerts
users to hazards to the environment and human health, and provides
instructions for the safe use of the chemical.
1.4 The Food Standards Agency leads within
Government on the regulation of horizontal labelling requirements
which are harmonised at EU level. Food labelling rules aim to
ensure that consumers can make safer, healthier, and more informed
choices, and to promote free trade within the EU.
1.5 At a broader level, the Department for
Business, Enterprise and Regulatory Reform (BERR) has responsibilities
for consumer protection, and the legislation on unfair commercial
practices, which BERR is currently introducing, is capable of
applying to labelling claims which mislead consumers. (The new
legislation on unfair commercial practices will replace existing
legislation on trade descriptions and, so far as business-to-consumer
advertising is concerned, existing legislation on misleading advertising.)
However, this framework extends across a potentially very wide
range of issues, of which environmental claims is only one.
2. GENERAL BACKGROUNDINFORMATION
AND LABELLING
AS A
TOOL FOR
ENVIRONMENTAL IMPROVEMENT
2.1 This memorandum goes on to offer factual
material and comment on the specific topics which the Committee
has highlighted as its principal lines of inquiry.
2.2 However, Defra would like to offer first
some wider background about the issues and developments surrounding
environmental labelling. The subject has evolved considerably
over the last 15 years or so:
In the early 1990s the general thinking
was dominated by assumptions that good information about products
would directly create consumer demand for greener products and
"pull" them through the supply chain. Debate was concerned
mainly with high-level award schemes (such as the EU Ecolabel,
introduced in 1992) and the quality of self-declared "green
claims" which businesses made about their products.
By the late 1990s, however, thinking
in many quarters was moving away from this model. The drivers
of consumer choice were appreciated as being much more complex
and the role of product information was seen more in terms of
it working alongside a number of other tools to induce the supply
chain to raise the environmental performance of products. The
UK was in the forefront of this shift in thinking. For example,
the consultation paper "Consumer Products and the Environment"
(DETR, 1999) set out a new picture of product policy tools, and
how information and labelling might fit into it. This was explored
further by the Advisory Committee on Consumer Products and the
Environment (ACCPE) which contributed many helpful insights on
the topic in its first two reports (DETR, 2000 and 2002).[1]
At the same time, views on what became known as "integrated
product policy" (IPP) were taking shape at EU level.[2]
More recently, our evidence base
about consumer choice and behaviour change has become more sophisticatedsee
for example the research done in the lead-up to the UK Sustainable
Development Strategy, Securing the Future (2005)[3]and
is still evolving. This work has confirmed the weakness of consumer
information as a driver for pro-environmental behaviour change,
unless used in conjunction with other measures.
In another recent development, the
European Commission ran an expert working group to take an in-depth
look at how product information could be made to work positively
for environmental improvement. The report, Making Product Information
Work for the Environment (2006)[4]
is intended as in input to the Commission's Action Plan for Sustainable
Consumption and Production (SCP) in the EU, due in 2008. Its recommendations
involve looking at the whole process of generating and using information
in the supply chain, as well as the forms in which it can most
helpfully be communicatedincluding, in the right circumstances,
the use of labels.
2.3 The 2006 report, to which Defra made
a significant contribution, represents the most up-to-date policy
analysis of environmental product information. The report received
broad support at a meeting of EU stakeholders and member state
representatives in June 2006. The analysis part of the document
(p 5-21) could therefore be a useful input to the Committee's
inquiry.
3. BACKGROUND
ON THE
VARIOUS TYPES
OF ENVIRONMENTAL
LABELLING
3.1 Environmental labels, claims and declarations
come in very varied forms and there is no simple way of categorising
them all. But the International Organization for Standardisation
(ISO) has produced technical classifications and standards which
capture much of the field.
ISO 14024 is for what are known as
"Type I" claimsdeclarations which meet criteria
set by third parties (not by a manufacturer or retailer themselves)
and based on life-cycle impacts. These are award-type labels,
like the EU Ecolabel and national ecolabelling schemes, requiring
compliance with the criteria to be verified by a third party.
In theory, products bearing a Type I label should be of a fairly
high environmental standard, though in practice this depends on
how the criteria for a particular scheme are set and on the effectiveness
of the management of the scheme.
ISO 14021 covers "Type II"
claims, which are manufacturers' or retailers' own labels and
declarations, sometimes called "green claims". These
can be useful, but there is a wide range of quality. Defra and
BERR have issued advice about the making of green claims (principally
in The Green Claims Code, in collaboration with the Confederation
of British Industry, the British Retail Consortium and other bodies)
to help businesses present the environmental credentials of their
products accurately and appropriately, especially in on-pack advertising.
ISO 14025 is for "Type III"
claims, which give quantified information about products based
on life-cycle impacts. Type III claimssometimes known as
Environmental Product Declarations (EPDs) or eco-profilesconsist
of quantified information about key impacts, such as energy in
use. The idea is to allow products to be compared on a like-for-like
basis. They have mainly been used in the business-to-business
market (though the feature of rating and comparability can also
be seen in regimes like energy labelling, which are not technically
"Type III" claims).
3.2 Various other schemes or symbols overlap
with environmental labels in some way. For example, there are
ethical schemes which have links with certain environmental factors
or which include some environmental requirement (like the Fairtrade
scheme); and there are informative symbols, such as the Mobius
loop.
3.3 Defra's explanatory leaflet, A Shopper's
Guide to Green Labelssubmitted with this memorandum[5]summarises
the characteristics of many of the major labelling schemes seen
in the UK, and illustrates their logos.
3.4 The Shopper's Guide looks at
the different types of labels in less formal categories and may
be a more helpful way of looking at what the labels are trying
to achieve. (Some schemes fit into more than one of the following
categories, and the categories themselves are not mutually exclusive.)
Ecolabels[6]voluntary
"award" schemes, which may cover a wide range of products,
such as the voluntary EU Ecolabel scheme, or regional or national
schemes such as the Scandinavian Nordic Swan, or the German Blue
Angel. There are over 20 such schemes around the world, and more
are in the pipeline, including proposals for schemes in Africa
and Asia (see Section 9).
Energy labels, which focus on the
energy-in-use impacts of productsespecially the EU energy
label, which is mandatory for certain domestic products such as
washing machines, refrigerators and lightbulbs. Other labels focusing
on energy efficiency and reduced CO2 have recently been developed
in the UK which echo the energy label's colour-coded ratings,
such as the UK's fuel efficiency and CO2 label for cars. Other
examples of energy labels include the "Energy Saving Recommended"
label for a wide range of energy efficient products in the UK
market (also a form of "award" label) and the "Energy
Star" scheme which appears in Europe and America on a wide
range of office products.
Sector-specific labels, which apply
to one kind of product, like timber or textiles. The international
Forest Stewardship Council (FSC) scheme (also a form of ecolabel
award) is the most well-known of these, but there are many different
schemes for products as diverse as flowers and textiles.
Organic labelling. The word "organic"
can only be used to describe food, feed or livestock if the relevant
EU standards are complied with. At present the use of the organic
logo prescribed by the EU standards is optional, but its use will
be compulsory after 2008 when a food or feed product is sold as
organic. The logos of the bodies like the Soil Association, which
have been approved by Defra to certify organic produce, may accompany
the EU logo. Some of these bodies also certify non-food products
like textiles, wood products and cosmetics, which are not covered
by EU law on organic production.
Food labelsthere are many
schemes, for many different types of food, which have an environmental
dimension. One of the better known examples is the Marine Stewardship
Council (MSC) scheme, but several other schemes also operate just
in the fish and seafood sector alone. Some suppliers' "own
brand" labels, covering a range of foods, may also be linked
to environmental criteria.
Social and "wider world"
labels primarily address specific ethical (and sometimes environmental)
issues associated with the places where products are sourced,
such as Fairtrade and Rainforest Alliance (which is why Fairtrade
is occasionally mentioned in this memorandum even though it is
not primarily an environmental label). These can cover crops such
as bananas, coffee, timber, as well as products like footballs
and activities like tourism.
Green claims (the "Type II"
labels of the ISO classification above). This covers a multitude
of labels, declarations and claims which are self-declared on
the initiative of the producer. They are not generally associated
with any third-party regime. They are however subject to consumer
protection regimes on trades descriptions and misleading advertising.
3.5 There are variations and hybrids of
these categoriesand some other kinds of labels as well.
For example, a few companies have their own quite specific "schemes"
behind their self-declared labelling, such as Philips' "Green
Flagship". Within the last year or so, initiatives using
the term "carbon labelling" have started to appearsee
Section 5.8.
3.6 Even the more systematised schemes vary
in quite basic aspects, such as the strictness of their standards
(eg, whether aiming for a very high standard or a reasonably good
standard). They also vary considerably in their visibility in
the marketplace.
4. THE SCOPE
AND COVERAGE
OF LABELLING
Products requiring labelling. The Sub-committee
would like to investigate which products are currently subject
to environmental labelling, both compulsory and voluntary, and
whether further products or sectors should be included under an
environmental labelling scheme.
Compulsory schemes
4.1 The EU Energy Label is the longest-established
mandatory scheme operating in the UK market. It covers most of
the more significant energy-using consumer products in the home.
4.2 A similar approach of comparable performance
"ratings", presented on a colour-coded scale, is used
in the Energy Performance Certificates (EPC) element of Home Information
Packs (HIPs).
4.3 The approach is also used in the UK
Fuel Economy Label. The label has been agreed voluntarily by all
the companies selling new cars in the UK, but it is in effect
a standardised way of presenting consumers with legally required
information on fuel and emissions.
4.4 The approaches now followed for homes
and cars can be traced back to recommendations made by ACCPE in
2000, around the idea of a "family" of labels for major
consumer products contributing to carbon emissions in their use
phase.[7]
4.5 The Chemicals (Hazard Information and
Packaging for Supply) Regulations 2002, implement the existing
European Directives on the classification and labelling of hazardous
chemicals, a long-established and widely understood system. The
Regulations require hazards to the environment and human health
to be communicated to the user (both consumer and professional)
via agreed symbols and warning phrases. The existing system
is due to be replaced by the forthcoming European Regulation based
on the United Nations Globally Harmonised System of Classification
and Labelling of Chemicals (GHS).
4.6 The crossed-out "wheelie bin"
symbol is a mandatory mark that manufacturers are required to
apply to products which fall within the 10 categories of electrical
and electronic equipment (EEE) covered by the WEEE directiveto
indicate to consumers that the EEE should not be disposed of as
general waste to landfill. End-users are strongly encouraged to
separate such WEEE from their general waste.
4.7 The Eco-design for Energy-Using Products
(EuP) directive will require a new approach when it is implemented
for various types of productby requiring environmental
criteria to be met before the product can receive the CE Mark
it needs in order to appear in the market. In this way environmental
criteria will be incorporated into a non-environmental label.
Mandatory food labelling in the UK
4.8 As the Sub-Committee has flagged up
a particular interest in food labelling, here is a summary picture:
The labelling of most food in the
UK is governed by the provisions of the Food Safety Act 1990 and
the Food Labelling Regulations 1996. These implement EU Directive
2000/13/EC on the labelling, presentation and advertising of foodstuffs.
Additional labelling requirements
are contained in over 40 horizontal and vertical pieces of legislation
(for example, GM labelling, wine, beef and EU marketing standards).
These rules aim to ensure that consumers
are properly informed about the nature and substance of the foods
they buy, protected from false or misleading descriptions, and
that industry has a clear regulatory framework which does not
restrict product innovation or inhibit the free movement of goods
within the EU.
The European Commission is reviewing
the General Food Labelling and Nutrition Labelling legislation.
A draft proposal is expected in by end of 2007, at which point
the Food Standards Agency will conduct a full public consultation.
Voluntary environmental labels
4.9 As noted in the Section 3 above, there
is a very wide range of voluntary environmental labelling approaches
covering products and services, including food.
4.10 The most visible voluntary schemes
operating in the UK are featured in The Shopper's Guide to
Green Labels. It would be hard to agree a meaningful and comprehensive
list of the many other schemes of varying standards operating
in the UK, but Defra publishes an on-line list of many of the
less familiar schemes in its Directory of Green Labels.[8]
4.11 For some types of products, such as
timber and textiles, there are several schemes which highlight
different aspects of sourcing or production, depending on what
messages the supplier wishes to communicate.
4.12 Although participation in these schemes
is voluntary on the part of business, there are a few which actually
operate within a legal framework. For example, organic food labelling
schemes are not mandatory, but the use of the word "organic"
is controlled by law. And while business participation in the
EU Ecolabel scheme is voluntary, all Member States are required
by law to establish a Competent Body to run it in their countries,
and are also required to promote it.[9]
The case for trying to cover further products
or sectors in an environmental labelling scheme
4.13 "Better labelling" is often
advocated as a solution to reducing the environmental impact of
products, and the idea has stimulated a host of labelling schemes
around the world. But labelling is certainly not the only means
of effecting change, as noted in Section 2 above. Nor is labelling
necessarily the best means of effecting change, especially if
pursued in isolation.
4.14 It is quite instructive to look at
some of the more successful examples of labelling schemes, in
terms of recognition and take-up. The experience of cases like
FSC, organic labels and Fairtrade, for example, suggests that
market interest is stronger where there is a clear, specific issue
which can be readily identified with certain productseg
(in the three examples just mentioned) sustainable sources of
timber; food grown without artificial chemical fertilisers and
pesticides; and equitable treatment of suppliers in developing
countries.
4.15 By contrast, award schemes which aim
to cover a complex mixture of environmental issues across a product's
life-cycle have often found it much harder to make headway in
the market. (The exceptions in the European market have been the
"Blue Angel" label in Germany and the "Nordic Swan"
in Scandinavia, which have achieved reasonable recognition in
their regional markets.)
4.16 Over many years the Government has
consistently held the view that it would not be worthwhile to
set up a new publicly-owned, multi-criteria award label for the
national market. This was also the firm view of ACCPE, when it
was asked to consider this question in depth.[10]
4.17 The UK has however continued to support
the official EU Ecolabel scheme, working hard to make the existing
scheme effective and, increasingly, to advocate reforms which
would help to streamline the scheme and get it working closer
to the market. The European Commission expects to publish its
formal proposals for revision by the end of 2007.
4.18 There are many types of products for
which there are no ready-made third-party "schemes"
which a company can participate in. With that in mind, Defra offers
information to businesses about alternative marketing approachesin
an on-line guide called Pitching Green.[11]
4.19 Labelling schemes that aim to make
a virtue of high environmental standards in farming, such as the
"LEAF Marque" label, can help raise farmers' environmental
performance as well as improving consumer choice. These schemes
have the potential to make a positive contribution to environmental
goals, if they were adopted more widely and covered the range
of environmental issues. However, uptake of these schemes is currently
low and Defra is investigating how it might be increased, for
example through more explicit government recognition of these
standards. Defra is also considering the possibility of developing
some form of generic standard for an integrated farm management
and environmental management scheme, which would allow consumers
to know more about the environmental provenance of food products
and improve recognition in the market place.
5. THE ISSUES
BEST COVERED
BY ENVIRONMENTAL
LABELLING
What should be shown under a labelling system.
The Sub-committee would like to assess which criteria should
be illustrated by an environmental label, and how overlaps between
different concerns could be adequately dealt with.
The Sub-committee would also be interested in
investigating how environmental labels could best convey information
accurately and usefully to the consumer.
Given the EAC's recent focus on climate change
and related issues, the Sub-committee would be particularly interested
to hear about the development and merit of labels which demonstrate
the carbon footprint of a productie the carbon emitted
during its production, storage and transportation.
Types of criteria
5.1 In general environmental labelling tends
to address three main kinds of environmental issue:
measurable impacts connected with
energy and resource use;
the sustainability of supply, particularly
the implications for biodiversity; and
the presence or absence of substances
which may be held to constitute a problem.
5.2 However, as noted in Sections 3 and
4 above, the market is often interested in other aspects of the
product, combining social and environmental factors. A good example
of this is the FSC labelling scheme for timber productsand
arguably this combination is one of the scheme's real strengths
in the market.
Communicating with consumers
5.3 Labelling is a flexible instrument,
and there are no hard-and-fast rules about the best way of conveying
information usefully and accurately to the consumer. Even though
the internet can now provide far more detailed information about
products, on-product labelling remains highly popular as a conveyor
of key messages of all kinds.
5.4 Environmental labels have two main functions
vis-a"-vis consumers:
they informwhere plain factual
information is provided, perhaps because this is required by law,
or because consumers are thought very likely to expect it.
they influence, directly or indirectlythis
might be promotional (aimed at trying to encourage the consumer
to buy the product); or advisory (for example, saying how the
product is best used or disposed of).
5.5 Some labels combine the twofor
example, in "warning" mode, where a label provides essential
safety information about the composition of a product and tries
to influence consumers to use it safely, because the product may
be dangerous to the consumer or to the environment if used incorrectly.
As such, labels are covered by legislation preventing or requiring
certain features.
5.6 All these aspects may be covered by
legal requirements about what information must be put on the labels
of certain types of products (especially factual labelling), and
laws prohibiting certain kinds of statements (for example, misrepresentation
when promoting products).
5.7 Labels which aim to influence are more
complex. Another consideration is that labelling schemes (or types
of labels) which aim to influence the consumer are themselves
also brands or "products". Like brands, they can:
create a unique selling point, which
advertising tries to sell to consumers (what marketers term "mind
share branding"the use of the FSC logo on tissue paper,
for example); or
be valued not so much for what they
do, as for how they make consumers feel about themselves (what
marketers term "identity brands").
Carbon footprinting and labelling
5.8 Carbon footprintingand how it
can be used in the marketis an area of fast-growing interest.
It is important, however, to distinguish between the measurement
of the carbon footprint (or, more properly, the "embodied"
greenhouse gas emissions in products across their life cycle)
and the various uses to which that information can be putof
which product labelling is only one of the possibilities.
5.9 A vital first step is to get a commonly
accepted method for doing the measurement. That is why Defra is
supporting and helping to fund BSI British Standards (BSI) to
develop a Publicly Available Specification (PAS) that will give
businesses a standard methodology for assessing the "embodied
emissions" in their products.[12]
The Carbon Trust is also supporting that work and the steering
group arrangements to take it forward as quickly as possible.
5.10 Once there is a common measurement
standard, there are various uses which companies can make of the
information about their products. Footprinting information could
be used:
to help companies reduce impacts
through changes in product design or process management;
to help companies reduce impacts
through supply chain managementthe choice of materials
or the standards demanded from their suppliers;
to communicate to groups of stakeholders
the steps being taken to reduce impactseg, through company
reporting or other corporate materials; and
to communicate to individual consumers
at the point of salethrough product labelling or other
advertising material.
5.11 All of these possible uses have potential
value. Communication to end-consumers is the one which throws
up most challenges. There are issues about how in practice a business
can provide information that is meaningful and generally helpful
to consumers, does not give any misleading messages, and actually
empowers consumers to take useful action.
5.12 The pilot scheme which the Carbon Trust
is currently running (the Carbon Reduction Label) should help
to tease out some of the issues about how communication to consumers
could be made to work in practice.
5.13 Defra's main concerns in this field
are:
to get a method of measurement for
"embodied" emissions which the whole of the market can
use with confidence;
to encourage businesses to act on
this information to reduce the climate change footprint of their
products;
to keep in view, nonetheless, that
the range of environmental impacts varies for different products,
and that the climate change impact is but one aspect; and
to ensure that whatever kinds of
product information are eventually provided to consumers are going
to be fair, reliable, helpful and genuinely useful to them.
6. THE CASE
FOR RATIONALISING
ENVIRONMENTAL LABELS
The case for rationalising environmental labels.
The Sub-committee would like to assess whether concerns over
the proliferation of environmental labels are justified, and the
extent to which consumers are able to cope and engage with the
many different labels on the market.
The Sub-committee would also like to investigate
whether there is a case for rationalising the system of environmental
labelling, or for calling for certain labels to be given priority
when displayed on products.
6.1 Existing labelling schemes cover many
different issues, including some overlap between certain schemes.
But having a wide range of different labels on the market is not
necessarily a disadvantage.
6.2 "Rationalisation" is difficult
to consider when there is no fully comprehensive model of labelling
which covers all aspects of sustainability. In fact, the striving
for balance between different factors may mean that the more issues
a scheme covers, the less effective it is as a label.
6.3 Although the number of labelling schemes
can seem confusing, some have become well known by consumers,
who are able to differentiate between them in the same way as
between the many different brands and retailers. Suppliers are
likely to continue to want a range of labels to reinforce a variety
of key messages about their products. And retailers in particular
can aim to make their own brand a desirable environmental and
social label.
6.4 There are several important sectors
in which well-known standards or labels do not address all of
the issues which matter to buyers, or where there is no good labelling
scheme, or where existing labels do not meet market needs in other
ways. So there is room for initiative in the market to consider
new labels which address issues not covered by others. This helps
fresh approaches to be tried out and can help inform wider debate.
6.5 Even where separate labelling schemes
cover similar territory, a degree of choice can help business.
The first-rate schemes obviously help to encourage better environmental
standards, and stimulate other organisations to create better
schemes. At present it seems likely that there will continue to
be a core range of good green labels in the market.
6.6 There was a helpful discussion of some
of these issues in a report by the Cabinet Office Performance
and Innovation Unit in 2000,[13]
which looked across a range of social, health and environmental
issues in the trading system, and included a look at some of the
issues raised by labelling. Among the conclusions were that "labelling
can often be left to the market to deliver, responding to consumer
and producer demand for schemes. Voluntary approaches have a number
of advantages including greater flexibility and capacity to reward
market leadership through setting high standards. Government still
has a role to play in terms of guarding against misleading claims,
promoting adherence to best practice (eg to avoid the creation
of de facto trade barriers) and in promoting mutual recognition
of schemes." These points were reflected in subsequent inter-departmental
work on common principles to apply in policy towards labelling
schemes.[14]
6.7 Defra's approach towards promoting voluntary
schemes is to encourage businesses to use the best of them, and
to help consumers to recognise those schemes through initiatives
like The Shopper's Guide to Green Labels, which shows the
main types of green labelling schemes operating in the UK, and
its Green Labelling News.[15]
We have also been working to encourage cooperation and convergence
of approach (and therefore less proliferation) in the field of
formal "Type I" award labels, particularly in the EU
market.
7. THE IMPACT
OF ENVIRONMENTAL
LABELLING ON
CONSUMER BEHAVIOUR
The impact of environmental labelling on consumer
behaviour. The Sub-committee would be interested in assessing
how easily consumers understand environmental labels, and whether
environmental labelling has a significant impact on human behaviour;
not only whether it can reinforce and assist existing positive
environmental behaviour, but also whether it can cause behavioural
change.
The Sub-committee would like to assess whether
concerns over the proliferation of environmental labels are justified,
and the extent to which consumers are able to cope and engage
with the many different labels on the market.
7.1 Surveys normally find that consumers
say they want more or better labelling, and would use it to guide
their choices. However, other evidence suggests that environmental
labelling in itself actually has limited impact on consumer choice
at present. This is partly because of the complex factors behind
choice and behaviour (referred to in the introduction to this
memorandum). But sometimes it is simply because consumers are
unsure about specific aspects of labelling. For example, a very
recent study by ANEC, the European body representing the consumer
voice in standardisation, said that new "A+" and "A++"
Energy Label ratings were confusing to consumersin what
is one of the most familiar areas of green product labelling,
and one with clear factual backing.
7.2 Whether labels cause consumers to switch
from one brand to another is not known with any precision. It
appears that environmental labels are held by consumers to be
more important in some areas (eg, cleaning products, paint and
textiles) than others. And also that there are different headline
issues for consumers for different types of product (eg, no peat
for soil improvers; recycled paper for kitchen roll).
8. THE REGULATION
OF ENVIRONMENTAL
LABELLING
The regulation of environmental labelling.
The Sub-committee would like to examine the ways in which
environmental labels are calculated, assessed and awarded, and
would also like to investigate the current regulation to which
these labels are subjected.
The Sub-committee would welcome assessments of
whether current levels of regulation are adequate, or whether
further regulation, be it wider in scope or stricter in demand,
is required.
8.1 As noted above, the UK has legal requirements
about the accuracy of claims made about products. Defra keeps
The Green Claims Code and other guidance to manufacturers
and retailers under review, and occasionally meets the ASA and
other bodies to discuss this.
8.2 It is worth noting that the European
Commission has raised the possibility of strengthening the application
of rules on misleading advertising to green product information.[16]
How standards for labels are set and labels are
awarded
8.3 This varies with the scheme. Type I
ecolabel award labels normally set their criteria after consultation
with interested parties and circulation of drafts, which is intended
to be a transparent process; applicants then have to obtain some
kind of independent verification to prove that they comply with
the scheme's requirements. Type III `profile' labels typically
set their criteria through some form of sectoral collaboration.
Type II labels and declarations are by definition self-declared.
And the criteria for legally-backed schemes (such as the EU energy
label) are agreed as part of a legislative process.
Regulation of voluntary labelling schemes in the
market
8.4 Most green labelling schemes start as
industry or sector initiatives, or are independent. Many schemes
are run by private organisations and some are international. There
is little scope for Government to control these, beyond the legal
framework to deter inaccurate, unfair or unhelpful claims. Governments
are also wary about intervening beyond thatin their own
fields many independent labelling schemes have a valuable profile,
with strong promotional strategies for focusing public attention
on key areas of environmental concern.
9. EXPORTS FROM
DEVELOPING COUNTRIES
Exports from developing countries. The
Sub-committee would also like to investigate the impact of environmental
labelling on exports from developing countries, and in particular
whether labelling of this kind could have a detrimental impact
on the trade opportunities available to these countries.
9.1 Environmental labelling has sometimes
been seen as a threat to developing countries, and debate about
ecolabelling in the 1990s frequently questioned whether it was
a Technical Barrier to Trade (see also section 10).
9.2 It tends now to be seen more as an opportunity.
The development of an African eco-labelling scheme was one of
the activities identified in the African 10-Year Framework Programme
on Sustainable Consumption and Production. The African Union Commission
is currently working with the Economic Commission for Africa and
the United Nations Environment Programme (UNEP) to develop an
ecolabelling scheme for Africa, to exploit the global market for
greener products, to increase access for its products and contribute
to poverty reduction.
9.3 UNEP also held the first Steering Committee
meeting this summer for its project on enabling ecolabelling opportunities
for developing countries, which will be formally launched in December
this year. The project supports the implementation of ecolabels
in developing countries, and aims at developing a roadmap in the
direction of mutual recognition of ecolabelling schemes. The countries
involved include Brazil, China, India, Kenya, Mexico, and South
Africa, as well as representatives of the European Commission.
9.4 At the opening session, the Chair of
the Global Ecolabelling Network expressed his appreciation for
the project "in reversing the misperception of ecolabels
as trade barriers and transforming them into an accessible tool
for enhancing trade opportunities of developing countries".
9.5 Other kinds of labelling, especially
"wider world" labels such as Fairtrade and Rainforest
Alliance, have built relatively strong support by focusing on
the impacts of products on the communities and environments in
the areas where they are produced. For example, Unilever announced
in May that it would certify its tea producers in East Africa
to Rainforest Alliance Standards as the first move in a plan to
source its entire tea supply sustainably.
9.6 There is a legitimate concern, however,
that labelling which focuses exclusively on the issue of "food
miles" may be damaging to developing economies (eg, as in
debates about the environmental downside of green beans air-freighted
from Africa, as against the social and economic upside for the
producing country.) The concept of "food miles" has
gained wide currency, but is often unhelpful if taken in isolation:
as one study has put it, "a single indicator based on total
food kilometres is an inadequate indicator of sustainability".[17]
It can also be misleading in terms of the total environmental
impacts of a productfor example, a focus on overseas transportation
ignores the climate impact from other stages of the production
cycle, such as cultivation, preparation, refrigeration, and transport
within the UK. As an illustration of this, one recent study has
found Kenyan cut flowers to be five times less carbon-intensive
than flowers imported from the Netherlands.[18]
Defra's work in developing a robust standard for measuring all
the embodied greenhouse gases in products (see Section 5 above)
is intended to enable a more balanced view of this complex subject.
10. INTERNATIONAL
LABELLING
International labelling. Finally, the
Sub-committee would be interested in assessing the feasibility
of an international environmental labelling system, and the extent
to which this would be compatible with the rules on trade set
out by the WTO.
10.1 The EU Ecolabel is the largest scheme
in the world in terms of the number of countries which formally
operate it. The scheme is already watched with interest around
the world and can also be awarded outside to products from outside
the EU (Defra has awarded it to companies in Asia, North America
and Australia), so the scheme has the potential to be a much more
influential player on the world stage.
10.2 Several international voluntary organisations
exist to coordinate information about each type of labelling system
and to promote good practice, but they have no regulatory powers.
These include the Global Ecolabelling Network (GEN), for Type
I labels; and GEDnet (the Global Type III Environmental Product
Declarations Network) for Type III labels. These bodies do not
have formal powers to coordinate labels, and do not "own"
the labels, some of which are subject to owners' copyright and
other restrictions, and are effectively products or brands in
their own right.
10.3 GEN has been working for some time
on proposals for an International Coordinated Ecolabelling System
(GENICES). The intention is to develop a coordinated system, not
a replacement international system. Proposals include the development
of 12 harmonised or core criteria. As noted in Section 9, UNEP's
project on enabling ecolabelling opportunities for developing
countries aims at establishing a roadmap in the direction of mutual
recognition of ecolabelling schemes.
10.4 A big new international scheme is therefore
not on the cards in the foreseeable future, but international
cooperation is likely to increase, and indeed international cooperation
in other areas of labelling will promote this in environmental
labelling. For example, the European Commission is proposing to
align the current EU system of classification of chemicals to
the United Nations Globally Harmonised System (GHS)see
Section 4.5 aboveintegrating the internationally accepted
classification and labelling system in new EU legislation.
10.5 The GHS, which is currently under negotiation,
is expected to boost trade and competitiveness, and this is also
one of the potential benefits of harmonised labelling schemes.
International cooperation is in the interests of all stakeholders,
but is perhaps particularly important for multinational companies,
which need to know the environmental standards that they are expected
to meet and stay ahead of in many different markets around the
world. The development of labelling schemes therefore needs to
take account of the global supply chain of a great many products,
and hence to meet international industry requirements as well
as those at a national level. Defra's work to develop a methodology
on the measurement of embodied greenhouse gas emissions, with
its potential to form the basis for agreement of future international
standards, is an example of keeping this international perspective
in view.
11. CONCLUSIONS
11.1 A wide and very diverse range of environmental
labels currently appears on food and other products and services
in the UK.
11.2 Most labelling schemes cover the environmental
impacts for one kind of product, such as timber; or focus on one
major environmental impact, like energy. A few schemes, like the
EU Ecolabel, cover a range of environmental impacts for a wide
range of product groups.
11.3 The key issue underlying such initiatives
is the difference that the scheme is intended to make. The environmental
benefits of voluntary green labels vary. Most provide a high environmental
standard for producers to aim at, and there is evidence that this
is important to manufacturers and retailers. If producers communicate
a product's green credentials to consumers, the label may also
help to raise awareness about environmental issues, and may change
consumer behaviour in some cases by building up allegiance.
11.4 However, environmental labelling in
itself appears to have limited impact on consumer choice at present.
Defra feels that the environmental impacts of products need to
be addressed in many other ways as well, as part of an overall
strategy for improving key types of product.
At a cross-cutting level, this involves
for example promoting the development and use of standards and
sound methodologies for assessing impacts (as for example Defra
is currently doing in relation to the carbon footprint of products).
At a sectoral level it involves engagement
with industry to encourage good practice to reduce the environmental
footprint of its activities (as for example with various Defra
programmes in relation to the food sector, and further consideration
being given to the development of integrated farm management).
And at a product level it may more
detailed engagement with the supply chain to agree specific improvements
to the performance of products placed on the market (as for example
with Defra's work on key energy-using products like domestic lightbulbs).
Defra is continuing to develop its strategy
for raising the environmental performance of products and is planning
to report on progress in Spring 2008.[19]
11.5 Defra does not regard the number of
existing labelling schemes in itself as a major problem for consumers,
because the development of such schemes has been mainly led by
the market for a specific purpose, indeed sometimes with encouragement
from Government for that purpose. A degree of choice between labels
can help the many different interests in a very diverse market,
and has resulted in some excellent schemes. Although there is
now a large range of labels, the leading few are becoming better
known to consumers, and their purpose seems generally understood.
As with "brands" generally, promotion of different schemes
is a matter for the label owners, but Defra can and does help
by focusing the attention of domestic consumers and professional
purchasers on the best schemes.
1 October 2007
1 See Chapter 3, http://www.defra.gov.uk/environment/consumerprod/accpe/report01/index.htm
and Chapter 4, http://www.defra.gov.uk/environment/consumerprod/accpe/report02/pdf/accpe<mv1.2>-<mv-1.2>report02.pdf. Back
2
See http://ec.europa.eu/environment/ipp/home.htm Back
3
A note at http://www.sustainable-development.gov.uk/what/priority/pdf/change-behaviour-model.pdf
gives further references to relevant material. Back
4
Available at http://ec.europa.eu/environment/ipp/pdf/20070115<mv1.2>-<mv-1.2>report.pdf Back
5
Can also be viewed on-line at http://www.defra.gov.uk/environment/consumerprod/shopguide/index.htm Back
6
In some countries outside the EU (especially in the USA) "ecolabel"
is frequently used to refer to the generality of environmental
labelling. Back
7
ACCPE's thinking is set out at http://www.defra.gov.uk/environment/consumerprod/accpe/report01/05.htm6 Back
8
http://www.defra.gov.uk/environment/consumerprod/glc/pdf/greenlabels-index.pdf Back
9
The Competent Body in the UK is the Secretary of State for the
Environment, Food and Rural Affairs. Back
10
http://www.defra.gov.uk/environment/consumerprod/accpe/report01/05.htm3.1 Back
11
http://www.defra.gov.uk/environment/consumerprod/glc/pdf/pitching-green.pdf Back
12
For further details see http://www.bsi-global.com/PAS2050 Back
13
Rights of Exchange, at http://www.cabinetoffice.gov.uk/strategy/downloads/su/trade/rights.pdf Back
14
See http://www.berr.gov.uk/files/file8162.pdf Back
15
http://www.defra.gov.uk/environment/consumerprod/glc/gnews.htm Back
16
See p 13 of the Commission's consultation document on an
EU SCP Action Plan (July 2007) http://ec.europa.eu/enterprise/environment/sip.pdf Back
17
Watkiss (2005). Back
18
Williams (2007), Comparative Study of Cut Roses for the British
Market Produced in Kenya and the Netherlands. Back
19
See Waste Strategy for England 2007, p 58, http://www.defra.gov.uk/environment/waste/strategy/strategy07/pdf/waste07-strategy.pdf Back
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