FUND FOR RESEARCH INTO INDUSTRIAL DEVELOPMENT, GROWTH
& EQUITY
Global Review of Eco-Labels: Implications for South
Africa
PHASE ONE REPORT
4. Specific Analysis of the EU Experience with
Eco-Labelling
This chapter provides a more detailed review and assessment of
the implications of the EU scheme for South Africa that that
provided in chapter 2, noting in particular the potential impact of
the scheme on the competitiveness of South African products within
the EU market. (Note: It had been anticipated that this chapter
would use the recent FRIDGE study on non-tariff barriers as a point
of departure, but unfortunately this study was not made available
to the consultants during the course of Phase I. This report will
be used in Phase II of the study).
4.1 Environment and the EU
The legal basis for the EU's environmental policy is found in
the Treaty on European Union, articles 100a, and
100r to 130t. Although the Treaty leaves scope
for member states to introduce more stringent environmental
measures than agreed upon at Union level, the express intention of
EU policy is to:
- Preserve, protect and improve the quality of the
environment;
- Ensure a prudent and rational use of natural resources;
- Protect human health; and
- Promote measures at international level to deal with regional
or international environmental problems.
The EU's environmental policy has evolved since the 1970s, where
environmental legislation was left predominantly up to the
individual countries in Europe. Environmental policy was concerned
principally with setting limits on emissions of specific
pollutants, such as discharges into water systems and air
emissions. By the 1990s these strategies broadened somewhat, and
related to the regulation of consumption of natural resources,
covering many environmentally sensitive activities. Individual
member states were granted a certain amount of flexibility with
regard to the implementation of such directives.
A EU Community Action Program, entitled Towards
Sustainability, was devised for the period 1992-2000. It
marked a significant shift for policy development, as it
complemented legislation with the use of market-based instruments.
The program also sought to integrate environmental considerations
into a broad range of policy areas, its intention being to develop
partnerships with shared responsibilities between government,
business and consumers. The five key sectors that were targeted
were industry, energy, transport, agriculture and tourism.
Key instruments of the EU's environmental policy include the
following:
- Environmental Impact Assessments (EIAs): Directive that lays
down the systematic procedure to be followed in the assessment of
potential environmental damage of individual projects, and
requiring public consultation in the process.
- Free Access to Information on Environmental Pollution:
Directive that requires national authorities to make information on
the environment available to all interested parties on request,
without such party having to prove a direct interest.
- Eco-Labelling for Environmentally Friendly Products: regulation
that enables a manufacturer or importer of a product to apply for
an eco-label to the relevant Competent Body, which may be granted
after a thorough assessment of the product.
- Eco-Audit: A voluntary environmental auditing scheme that is
co-ordinated by Member States. It requires participating companies
to incorporate environmental protection standards into their
production processes.
- The LIFE Regulation. This programme is designed to provide
financial incentives for EU priority projects in the environmental
field.
4.2 History of the EU Eco-Labelling Schemes
Experiences with the growth of eco-labelling in the EU have been
varied. The German national eco-label, the Blue Angel, is the
oldest of all eco-labels, having been founded in 1977. It has
achieved wide-spread success in its home country, with a total of
over 3.500 products having obtained the relevant certification. It
also covers over 80 product lines from 11 product categories, which
is by far the widest product range of all the European eco-labels.
Its only exclusion is food and pharmaceuticals. As such, it has
achieved significant consumer uptake and awareness in the home
market. The mark is entirely voluntary and has increased
environmental awareness of both producers and consumers. Uptake of
the Blue Angel is predominantly by German applicants, although a
significant number (approximately 15% of the total) of foreign
produced products have obtained the eco-label.
The European Union eco-label is in many instances similar to
Germany's Blue Angel, having been introduced 15 years later, in
1992. This follows the increasingly close co-operation and the
systematic alignment of the policies of the European Union member
countries. As intra-regional trade barriers within the Union were
removed, the individual markets effectively grew into a single
market of some 340 million consumers. It no longer made sense to
only have the numerous different National eco-labels, rather, a
common EU-wide eco-label was called for.
Initially, the uptake of the EU label was very slow, due to the
fact that progress was slow in developing ecological criteria for
various product groups. A year after the establishment of the EU
eco-label, ecological criteria had only been drawn up for one
product category, namely dishwashers (1 company awarded label by
1992). A year thereafter, only a further 3 product categories were
established (paper kitchen rolls, soil improvers and toilet
paper).
To date, Denmark has the largest number of companies
that are using the EU eco-label (22), closely followed by France
(20). Italy (18), Spain (13) Greece (9) and Sweden (8) have a fair
number, although in the wider context, this numbers are indeed very
low. It is interesting to note that the uptake of the EU eco-label
by German (2) and Dutch (2) applicants still lags far behind.
However, this can probably be explained that both these countries
have well-known and successful National eco-labelling programs,
which themselves have achieved wide-scale national (and even
Europe-wide) recognition. The strength of this label is certainly
its European dimension, though. Since it can be used throughout the
EU, it eliminates costly and redundant multiple applications.
4.3 Eco-Labelling and Government
Procurement
In the EU, the first directives on public procurement were
adopted in the 1970s, and were aimed at increasing transparency and
non-discrimination in the tendering procedures of the Member
States. The specification of technical characteristics of goods and
services to be procured by public institutions and governments are
an integral part of any tendering process. Such specifications may
include quality characteristics, performance, packaging, safety
aspects, marking and labelling. These "technical specifications"
thus include environmental characteristics that are used to
determine environmentally preferable products.
According to a 1999 OECD document on trade issues and the
"greening" of public procurement, environmental criteria may in
future become increasingly important co-determinants for government
procurement exercises. Since "greener" goods for public procurement
purposes have been mostly defined by their use or disposal
characteristics, rather than production characteristics (e.g.
stipulating maximum allowable energy consumption levels), they
should not give rise to any serious trade effects.
Currently, where procuring authorities have been attracted to
eco-labels, they appear to be more inclined to adopt certain of the
label's ecological criteria, rather than relying on the labels
themselves. The use of eco-labels to designate environmentally
preferable products for public procurement is not (yet)
particularly widespread. There is concern, though, that this
situation may change in the near future, and eco-labels becoming
part of the public procurement process (especially as more and more
eco-label product categories are drawn up). This could favour
domestic firms over foreign enterprises, and larger firms over
SMEs, in the process.
EU public procurement rules require the use of European
standards, or in their absence, national standards. Only under
limited circumstances may contracting parties depart from European
standards, for example where the use of European Standards would
necessitate the contracting entity to acquire supplies that are
incompatible with equipment currently in use, at disproportionately
high cost.
4.4 Operation of the EU Flower
4.4.1 Overview of Legislative Arrangements to Implement
the EU Eco-Label
The EU eco-label (also known as the EU Flower, or EU "Daisy")
was established in 1992 by Council Regulation (EEC) No. 880/92 of
23 March 1992. In 2000, this regulation was revised significantly,
with a new Regulation (EC No 1980/2000) significantly extending the
original scope of the scheme. The new Regulation streamlined the
scheme and introduced services into the fold of categories that can
obtain the EU eco-label. It also revised the fee structure for
applicants (announcing a reduction in fees), and increased the
Scheme's transparency through greater stakeholder involvement.
Provision was made for a review of the EU eco-labelling scheme
before September 2005.
Specifically, the new Regulation deals with the objectives of
the EU eco-label, its administrative structures and fees of the
label. Its salient features are:
- Widening the scope to cover services as well as products.
- Reinforced stakeholder participation, in particular in
developing the environmental criteria.
- The creation of the EU Eco-labelling Board, comprising of the
Eco-label Competent Bodies and interest groups, whose main role is
to develop the Eco-label criteria.
- Reduced fees for SMEs and developing countries.
- Introduction of a ceiling on the annual fee.
- Reinforced transparency and methodology.
- Renewed emphasis on the promotion of the scheme.
- Reinforced co-operation and co-ordination with the national
Eco-label schemes.
- More information on the label.
- Possibility for traders and retailers to apply directly for
their own brand products.
- Possibility for non-EU producers to apply directly (to the
Competent Body of their choice, where a product is to be marketed
in more than one country).
4.4.2 Existing Eco-Labelling Product Categories and
Categories under Development
The Working Plan drawn up by the European Union Eco-Labelling
Board foresees that ecological criteria for a further 25-35 product
groups will be developed within the next 3 years. According to the
EU this would form a sufficiently complete and manageable range of
products to attract new stakeholders. The scheme has so far
established ecological criteria for 17 major product groups
(including textiles and footwear, several detergent groups, several
household appliances, several paper products, paints and varnishes
and soil improvers and growing media). The largest number of
applicants are from the textile industry (37), followed by
manufacturers of indoor paints and varnishes (27), and tissue paper
(8). Judging by the progress made so far, and the process involved
(including wide stakeholder consultation), this would appear to be
an overly ambitious target.
All of the existing product categories of the EU eco-label
consist of either household items or office equipment. They include
items of a personal nature (e.g. tissue paper, cleaners for
sanitary equipment), household cleaning agents (laundry and
dishwasher detergents), household equipment (washing machines,
refrigerators) and office equipment (personal computers,
photocopiers). A comprehensive list of all product categories for
which eco-labels have been awarded is provided in Appendix 1.
Product groups for which the ecological criteria are currently
under development, include both household items and services.
|
Product Group
|
Status
|
|
Hard floor coverings
|
Ecological criteria under development
|
|
Vacuum cleaners
|
Ecological criteria under development
|
|
Tourist accommodation
|
Ecological criteria under development
|
|
Furniture
|
Ecological criteria under development
|
|
Tyres
|
Feasibility study completed
|
|
Rubbish bags
|
Study completed
|
|
Converted paper products
|
Study completed, work suspended
|
|
Batteries for consumer Goods
|
Study completed, work suspended
|
According to the Commission Decision 2002/18/EC, which
established the EU eco-label Working Plan, the following new
product groups will initially be considered for the development of
ecological criteria. In most cases they continue to be consumer
goods with much relevance, in addition to them being product
categories where the combined environmental impact may indeed be
significant. Most notably, though, they follow the trend set by the
Germany's Blue Angel in that they increasingly include service
sectors. By expanding and broadening their coverage, the product
categories also appear to be increasingly encroaching on industries
with high international trade volumes, including the automotive
industry, toys and games, and fashion accessories.
|
Table 2 - New Product Groups
Planned for the EU Eco-Label
(as per European
Commission Decision 2002/18/EC of December 2001)
|
|
Printing paper
|
Printed paper products
|
|
Converted paper products, stationary
|
Wallpaper
|
|
Rubbish bags / plastic bags
|
Shopping bags - carrier bags
|
|
Writing implements
|
Telephones
|
|
Copiers
|
Small household electrical equipment
|
|
Fashion accessories
|
Gloves
|
|
Leather products
|
Sports equipment
|
|
Toys and games
|
Packaging
|
|
Do-it-yourself products
|
Air conditioners
|
|
Heating systems
|
Water-heating systems
|
|
Insulation
|
Building components
|
|
Building services
|
Retail services
|
|
Dry cleaners
|
Financial services
|
|
Transportation services
|
Delivery services
|
|
Vehicle repair services
|
Cars
|
|
Kitchenware, household fittings etc.
|
Sanitary products (towels and napkins, etc.)
|
|
Shampoo and soap
|
|
4.4.3 How are the Product Group Criteria
developed?
- The functioning the Eco-label scheme consists of distinct
phases. Preparatory work and the establishment of new criteria
generally lie with one or two so-called "Lead" Competent Bodies,
although the initiative for selecting product groups and individual
products is taken either by the European Commission, or by the
European Union Eco-labelling Board (EUEB). The actual decision
whether to award the label lies with the relevant Competent Body,
as per Article 7 of Regulation 1980/2000 of the European
Parliament.
- The EUEB is the central governing body of the EU eco-label, and
was established pursuant to the above-mentioned directive (EC
1980/2000). It consists of the Competent Bodies, as well as various
stakeholders from industry, environmental NGOs and consumer bodies
(which make up the Consultation Forum). Criticism by EU Member
States and interest groups for greater consistency in the choice of
product groups and development of ecological criteria has lead to
key interest groups (industry, SMEs, retailers, consumer
organisation, trade unions, environmental protection agencies)
being consulted more extensively in the drawing up of a "Working
Plan". The Working Plan spells out the choice of future product
groups, and envisages developing approximately 30 additional
product categories over the next 3 years. As decisive stakeholders
of the EUEB, they are thus invited to continue to play an
increasingly active role in promoting and developing the EU
eco-label.
The following procedure is followed in the development of
criteria for a new product group:
- The Commission provides the European Union Eco-labelling Board
(EUEB) with the mandate to develop the ecological criteria for a
particular product group. An Ad-Hoc Working Group (AHWG) involving
the relevant interested parties (retailers, industry and consumers)
and the Competent Bodies is set up for this purpose within the
EUEB.
- One or two of the Competent Bodies, which make up the EUEB, are
chosen as Lead Competent Bodies to leads this process. The AHWG
drafts the ecological criteria for the proposed eco-label, taking
into account the results of the preparatory work completed by the
Lead Competent Body. These results are obtained from:
- A feasibility and market study: This study is carried out to
collate data on the following aspects: the market structure and the
various types of product groups in the EU market, the opinions of
interested parties, key environmental impacts and key elements
relating to the product's fitness for use, an inventory of
eco-labels, standards, test methods and studies. Consumer
perceptions, functional differences between types of products and
the need for identifying subgroups will also be
assessed.
- A report on the relevant life cycle considerations
- An environmental improvement analysis
- The draft ecological criteria and necessary compliance criteria
are then discussed with the entire EUEB, ensuring
transparency.
- The Commission is informed of the draft criteria and decides
whether the mandate has been fulfilled or whether the work should
continue.
- Once the final draft criteria is ready, it is presented to a
Regulatory Committee of experts from the Member States for its
approval.
- The approved criteria are adopted as a Commission Decision by
the European Commission and published in the L series of the
Official Journal.
Since these procedures are intended to ensure that all the
environmental considerations have been taken into account, and that
all the relevant stakeholders have participated, they can take
several months to complete. The Eco-Label Competent Bodies, which
are considered independent and neutral, have been designated by the
Member States to implement the Community Eco-label scheme at
national level or regional level once the ecological criteria have
been developed.
4.4.4 Harmonisation Activities in the
EU
The removal of technical barriers to trade (TBTs) is an
important pre-condition for the successful functioning of the
European internal market. In 1985, the EU adopted a new approach
towards technical harmonisation of European industry standards in
the different areas covered by EU technical legislation. This new
approach recognises the importance of using harmonised standards as
a guarantee of quality, especially with regard to the essential
safety requirements established by the 'Directives'. Up until 1985,
technical harmonisation activities were based on a case-by-case
approach, frequently containing very detailed specifications with
approval procedures that were difficult to implement. It was the
responsibility of the individual EU Member States to issue
certificates of conformity; often, the results obtained were
unsatisfactory and recognition thereof depended largely on the
confidence that the various national authorities were able to show
in each other.
The new approach formulated in 1985 - the most fundamental
elements of which relate to the essential requirements and
procedures necessary for assessing conformity - has enabled the
previously mentioned difficulties to be overcome. The new EU
legislation is now restricted to the establishment of minimum
requirements that have to be met by the various product groups.
Technical specifications meeting these essential requirements are
thus developed on the basis of the new approach to technical
harmonisation and standardisation set out in the applicable EU
directive (Directive 83/189/EEC). Harmonisation certification
procedures and the associated rules governing their use are set out
in EU Decision 93/465/EEC.
The function of drawing up harmonised standards (that define the
technical specifications needed by manufacturers in this context)
is entrusted to the EU standardisation organisations. These are CEN
(European Committee for Standardisation), CENELEC (European
Committee for Electrotechnical Standardization) and ETSI (European
Telecommunications Standards Institute). While standards are
voluntary, (unlike other essential requirements), products
manufactured in accordance with them are assumed to comply with the
essential requirements of the Directives. National standardisation
authorities (present in the various Member States) are required to
confer the status of a national standard to the adopted harmonised
standards. Also, national standardisation authorities are required
to withdraw any conflicting national standards. The national
standardisation authorities, as well as the Official Journal of the
EC, publish a reference list of harmonised standards. The reference
list to harmonised standards currently contains 18 Directives.
The existence of various national eco-labels in Europe (such as
Germany's Blue Angel, the Nordic countries' Nordic Swan and the
Dutch Stichting Milieukeur) - in parallel to the development and
existence of the EU-wide eco-label, has raised various issues with
regard to their consistency, comparability and compatibility. This
is especially so since the national eco-labels surpass the EU label
in terms of product coverage, uptake and levels of consumer
awareness (particularly in their respective home markets).
In terms of Paragraph 16 of the EU Regulation 1980/2000, which
substantially revised the EU eco-labelling program in 2000,
specific mention is made of co-ordination between the EU eco-label
and the various national programs:
"While existing as well as new eco-label schemes in the
Member States may continue to exist, provision should be made to
ensure co-ordination between the Community eco-label and other
eco-label schemes in the (European) Community, in order to promote
the common objectives of sustainable consumption."
Since the progress towards a single market in the EU, which was
to a significant extent achieved with monetary union early in 2002,
this has increased the need for a common eco-label that prevents
confusion amongst consumers and manufacturers. The underlying idea
behind the creation of the EU eco-label was to ensure consistency
in the application of environmental criteria across Member States.
The EU eco-label, being the result of a common EU policy, is thus
intended to become the environmental reference with regard
to consumer products. As per Paragraph 16 (cited above), this does
not mean that national eco-labels and the EU eco-label cannot
co-exist; however the regulation requests Member States and the
European Commission to ensure co-ordination between the EU
eco-label and other national schemes, particularly in the selection
of product groups and the development and revision of the criteria.
Where a product has been awarded both with a national and the EU
eco-label, both such logos will be displayed side by side
on the product.
4.4.5 Nature of Marketing and Promotional
Activities of the EU Eco-Label
The EU eco-label has not achieved the success in terms of market
penetration as envisaged when it was created in 1992. A general
lack of awareness of the scheme, the prominence of some national
eco-labelling programs and other factors contributed to this. Even
today, the scheme has not been an unqualified success,
notwithstanding the fact that a fair number of product categories
have by now been developed. There certainly has not been a stampede
of manufacturers, retailers and importers applying for the right to
apply the EU eco-label.
However this situation appears to be changing, judging by the
rising levels of awareness (especially throughout the EU) of the
label, and the rapidly increasing number of successful applications
for a EU eco-labels in 2001. During this year, the number of
manufacturers using EU eco-labels doubled to over 100 companies
(103 companies as of May 2002), comprising over 400 products.
According to the EU Eco-Label Secretariat, approximately 17 million
products (with an ex-factory value of 38 million Euros) bearing the
EU eco-label were sold in 2000. This is due to a number of reasons,
including the fact that the range of product categories for which
ecological criteria have been developed have increased, and
marketing efforts and awareness campaigns accelerated.
A comprehensive work plan has been drawn up for the EU
eco-label, enforcing and co-ordinating all the marketing efforts of
the individual EU Eco-Labelling Board (EUEB) stakeholders. During
2000, the budget for marketing activities of the label was
approximately 40% (1 million Euros / R10 million) of the total
budget of approximately 2.5 million Euros. The individual countries
Competent Bodies contribute approximately 70% to the total.
Marketing activities undertaken by the European Commission and
the individual Competent Bodies are undertaken on various levels,
and aim to promote the scheme and significantly enhance both
producer and consumer awareness. In 2000, a total number of 37
persons were working fulltime for the EU eco-label, 7 at the
European commission level, and 30 for the Competent Bodies.
These marketing activities include:
- Publication of the info-kit (15 product fact sheets for
producers, 9 product leaflets for consumers, application guide,
consumer guide, business fact-sheet) aimed at producers and
consumers.
- General Information brochure "The European Eco-Label at a
Glance" in all the official European languages.
- The "Flower News" (every four months).
- Publications in the European Environment Newsletter
- Publications in different magazines.
- Production of different promotional materials, including
posters, pins, shopping bags, T-shirts and mouse pads for the
different promotion activities in the 14 Member States.
- Installation and financing of the eco-label "Helpdesk" which
has the task of answering the inquiries and supports the European
Commission in their promotional activities. While most enquiries to
the Helpdesk have originated inside the EU, numerous information
enquiries were also received from outside the EU, including
South Africa, USA, India, Malaysia, South Korea, Sri
Lanka, Mexico, Pakistan and Indonesia.
- Installation and updating of the website
(http://europa.eu.int/comm/environment/ecolabel) that provides full
information on the EU eco-label. This site currently receives
approximately 60.000 visits a month.
- Presentations at public occasions and special events ("Green
Week", Environmental Award Ceremony etc.)
- Launching and Financing of marketing campaigns in the Member
States (the latest in Greece and Spain).
- The Competent Bodies are in charge of the promotion of the
scheme at the national level. For example, Denmark recently
launched a campaign to promote both the EU eco-label as well as the
Nordic Swan (which enjoys wide coverage in the Nordic countries).
Some Member States provide subsidies to producers to help them
apply for an eco-label. This happens in, for example, the
Netherlands and Catalonia (Spain). Some Competent Bodies have their
own website for the promotion of the scheme.
On 21 December 2001 the European Commission (2002/18/EC)
established the EU eco-label "Working Plan", in which it formally
spelt out its marketing and promotion plan for the upcoming years.
It deals with issues such as increased visibility of the label,
stakeholder involvement, general and co-ordinated marketing
activities, and its targets for levels of consumer awareness across
the EU.
Table 3 - EU Marketing and
Promotion Objectives
|
|
Implementation Measures |
| Marketing
& Promotion
Objectives
|
2002
|
2003
|
2004
|
| Co-ordinate marketing efforts and
develop and implement joint actions |
Form a permanent marketing management group.
EUEB to meet twice a year to discuss marketing, promotion and
strategic development of the scheme (Presidential meetings).
|
Identify the different key target groups and define and
implement a strategy for each.
|
Continue.
|
|
Marketing &
Promotion
Objectives
|
Implementation Measures |
|
2002
|
2003
|
2004
|
|
Annual increase of at least 25% of eco-labelled articles
Achieve a minimum level of visibility in two thirds of the
Member States.
Continuously inform all stakeholders about the eco-label and its
developments. In parallel, seek feedback from stakeholders.
All relevant manufacturers and retailers should be aware of the
eco-label.
More than half of European consumers should recognise the EU
eco-label logo as a label of environmental excellence.
|
Undertake promotion.
In each Member State, identify and focus marketing efforts on
key product groups.
In each Member State, identify and focus marketing efforts on
key product groups.
Update and improve design of the eco-label website.
Organise and co-ordinate the development and distribution of
brochures and other printed material.
Draw up list of events where eco-label should be presented.
Inform potential applicants about application procedures and
costs.
Set up reporting mechanisms to establish annual statistics for
tracing market penetration.
Develop the criterion for a minimum level of visibility of the
eco-label, evaluate in which countries this has been achieved.
|
Undertake promotion
Continue updating website, distributing brochures, attending
events and informing about costs, etc.
Develop a strategy and actions for SME support networks and
strategic partnerships with retailers.
Develop a cost-effective methodology for monitoring consumer
recognition of the EU eco-label logo, and develop cost-effective
actions for progressively increasing this.
|
Undertake promotion
Continue updating website, distributing brochures, attending
events and informing about costs, etc.
Resources devoted to promotion should be at least 50% of those
devoted to product group development.
|
4.5 The EU Product Categories - Implications for
South Africa
In order to gauge the potential implications of the EU
eco-label's product categories on South Africa, it needs to be
estimated what the market access implications for South
African-produced products could be. Since the "coverage" of the EU
eco-label is the European Union, its impact on countries such as
South Africa is only likely to be of consequence where the label
could have an impact on trade relations between South Africa and
the EU. Trade flows between countries have been increasing
significantly over the past decade, and those between the EU and
South Africa are no exception. The following sub-section therefore
provide a general overview of general trade between South Africa
and the EU over the period 1999-2001, and then follows with a more
specific analysis of South Africa's trade performance with the EU
of the EU eco-label equivalent South African manufacturing sectors.
Those EU countries, which have been the destination of South
African-produced products in the equivalent sectors over the
1999-2001 period, are identified and ranked.
4.5.1 Nature of Trade between South Africa and
the EU
The European Union is South Africa's most important trade
partner. In 2001, the EU accounted for approximately 37% of all
exports leaving South Africa, while being the source of 41% of
South Africa's imports. Of the 14 EU Member States, South Africa's
most important export markets (in decreasing order) are the United
Kingdom, Germany, The Netherlands, Belgium, Italy, France and
Spain, which together are the destination of approximately 95% of
all exports to the EU.
An overview of trade between the EU and South Africa is provided
in Appendix 3. Closer analysis of South Africa's exports to the EU
reveals that approximately 25% of these exports consist of coal
(HS27 category) and gold, diamonds, platinum (HS71 category). For
the purpose of this analysis, the category definitions of the HS
(Harmonised Commodity Description and Coding System) were used. The
(HS) of the Customs Co-operation Council (CCC) is used worldwide as
a reference for classifications of external trade statistics and
for customs tariffs. The third largest export category consists of
machinery (including those for household use) and parts thereof, a
category falling under manufactured exports. Motor
vehicles (and parts thereof) contribute approximately 9% of total
exports. Other important manufacturing / industrial sector
categories (as opposed to mining and agriculture) include
electrical motors (HS85), paper and related articles (HS48),
organic (HS29) and inorganic chemicals (HS28), articles of iron or
steel (HS73) and fertilisers (HS31).
Overall, manufactured exports account for over 60% of South
Africa's exports to the EU. Exports to the EU thus play a highly
important role from the perspective of South Africa, since a
relatively large proportion consists of products other than
minerals and agricultural products. Manufactured products typically
have higher value-added than other output. The trade statistics
also indicate that South Africa's exports to the EU grew by 50%
(nominal) between 1999 and 2001, proof that South Africa is making
significant progress in terms of export market penetration. In
terms of the SA/EU Trade Protocol, tariff-based trade barriers will
continue to be downscaled over the next decade, although the
potential clearly exists that technical trade barriers (including
eco-labels) could in future restrict export growth.
4.5.2 Specific Analysis of SA-EU Trade in the EU
Eco-Label Equivalent Sectors
In order to obtain a better impression of the potential impact
that the EU eco-label could have on South Africa, trade between
South Africa and the EU in the product categories for which an EU
eco-label exists was analysed. For this purpose, the statistical HS
codes for the relevant products were determined, and it was found
that in most cases the generic description of the 18 product
categories (for which ecological criteria have been developed)
could be closely matched with one (or more) HS 4-digit codes. In
the case of textile products, which refer to products made of
textiles (i.e. garments), the entire HS63 category (i.e. knitted
and woven clothing) was used for purposes of analysis.
As can be seen in the table, the results show that, with the
exception of "Tissue Products", every eco-label "equivalent"
product category manufactured in South Africa is exported to the
EU. The category with the highest volume of South African exports,
namely "Textile Products", is exported to over half of the EU
Member States, including the UK, Italy, France, Germany and The
Netherlands. It should be noted that the EU eco-label has been
awarded most often within this particular product category, as well
as the fact that French and Italian producers form the largest
group of successful EU eco-label applicants.
For most product categories, the equivalent South
African-manufactured product is exported to at least four or more
EU Member States. In two examples, namely "Light Bulbs" and "Bed
Mattresses", a large proportion of South Africa's total exports of
that product category go to the EU. In the case of "Bed Mattresses"
and "Light Bulbs", the UK is South Africa's single largest export
destination, accounting for 25% and 40% respectively.
Although only a portion is sold to the EU, the total value of
exports of the equivalent product categories for which the EU
eco-label criteria have been defined, amounted to R 6,126 billion
in 2001 (significantly, this is a 50% increase from 1999).
Table 4 - Analysis of Trade Between SA and EU in
EU Eco-Label Equivalent Sectors
| EU Eco-label Product
Categories |
Number of Labelled Products with EU
Eco-label |
Trade: Equivalent HS Chapter
coverage |
Trade: Equivalent HS 4-digit code
coverage |
South Africa's
Worldwide Exports inEquivalent Categories
(R'000) |
EU Importers of Equivalent South
African-producedexports |
| 1999 |
2000 |
2001
|
|
Tissue Paper Products
|
8
|
48
|
4803
|
52,401
|
55,925
|
62,144
|
none to EU
|
|
Textile Products
|
37
|
62-63
|
6200-6310
|
1,027,037
|
1,455,339
|
1,929,412
|
UK, Italy, France, Germany,
Netherlands, Belgium, Ireland, Austria
|
|
Dishwashers
|
1
|
84
|
8422
|
68,587
|
93,701
|
90,025
|
Belgium, UK, Netherlands, Germany
|
|
Soil Improvers
|
7
|
31
|
3101-3105
|
948,362
|
928,382
|
1,078,843
|
France, UK
|
|
Footwear
|
4
|
64
|
6401-6406
|
115,275
|
119,950
|
111,376
|
UK, France, Portugal, Germany,
Netherlands
|
|
Bed Mattresses
|
4
|
94
|
9404
|
32,426
|
29,429
|
39,758
|
UK (note: 25% of world total in
2001)
|
|
Indoor Paints & Varnishes
|
27
|
32
|
3208-3210
|
80,425
|
75,667
|
104,015
|
Netherlands, UK, Greece, France,
Germany
|
|
Laundry Detergents
|
3
|
34
|
3402
|
125,932
|
119,367
|
146,513
|
UK, Netherlands, Portugal, Greece
|
|
Light Bulbs
|
1
|
70
|
7011
|
626
|
2,106
|
3,421
|
UK (note: 40% of world total in
2001)
|
|
Detergents for Dishwashers
|
6
|
34
|
3402
|
125,932
|
119,367
|
146,513
|
UK, Netherlands, Portugal, Greece
|
|
Copying Paper
|
2
|
48
|
4802
|
586,330
|
582,991
|
701,995
|
Belgium, UK, Germany
|
|
Refrigerators
|
2
|
84
|
8418
|
174,101
|
216,003
|
235,649
|
Denmark, Netherlands, UK, Greece
|
|
Hand Dishwashing Detergents
|
1
|
34
|
3402
|
125,932
|
119,367
|
146,513
|
UK, Netherlands, Portugal, Greece
|
|
Televisions
|
0
|
85
|
8528
|
91,670
|
140,695
|
209,395
|
UK, Netherlands, France, Germany
|
|
All Purpose Cleaners and Cleaners for Sanitary Facilities
|
0
|
34
|
3401
|
153,072
|
199,394
|
314,148
|
Belgium, Netherlands, UK, Greece,
France
|
|
Washing Machines
|
0
|
84
|
8450
|
7,075
|
5,655
|
7,525
|
UK
|
|
Portable Computers
|
0
|
84
|
8471
|
296,131
|
364,305
|
454,998
|
|
|
Personal Computers
|
0
|
84
|
8471
|
296,131
|
364,305
|
454,998
|
|
|
TOTAL (excl. double counted categories)
|
4,133,113
|
4,968,606
|
6,126,599
|
|
|
Source: DTI Trade Statistics Database
/ Department of Customs & Excise (2002)
|