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Environmental Project No. 1179, 2007

Mapping of decabromodiphenylether (decaBDE) in other products than electrical and electronical products

Contents

Introduction

Summary and conclusions

Sammenfatning og konklusioner

1 Intrduction and purpose

2 Introduction to decaBDE

• 2.1 Introduction to decaBDE
• 2.2 Regulations

3 Former mappings

• 3.1 Denmark
• 3.2 Nordic countries
• 3.3 EU

4 Method description

• 4.1 Introduction
• 4.2 Strategy
  • 4.2.1 Import as chemical
  • 4.2.2 Import as part of semi-finished produtcs
  • 4.2.3 Import as part of finished goods
  • 4.2.4 Other sources

5 Mapping of decaBDE in Denmark

• 5.1 Import of decaBDE as a chemical
• 5.2 Import as content in semi-finished products
• 5.3 Import as content in finished products
  • 5.3.1 The plastics industry etc.
  • 5.3.2 Means of transport
  • 5.3.3 The furniture industry
  • 5.3.4 Cables and electronic accessories
  • 5.3.5 Furnishing fabrics
  • 5.3.6 Wholesale textiles
  • 5.3.7 Camping
  • 5.3.8 Outdoor life
  • 5.3.9 Glues
  • 5.3.10 Nursing requisites
  • 5.3.11 Commodities for babies and children
  • 5.3.12 Paints and joint sealing compounds
• 5.4 Total statement of decaBDE
  • 5.4.1 Comparison with EU

6 Alternatives

• 6.1 Alternatives to decaBDE – summary of questionnaire responses
• 6.2 Trends in the use of decaBDE

7 Conclusion and summary

• 7.1 Method
• 7.2 Imported amounts of decaBDE to Denmark as chemical or semi-finished products
• 7.3 Imported amounts of decaBDE to Denmark as part of finished products
• 7.4 Alternatives and trends in the use of decaBDE

Appendix A – List of companies

Appendix B – Questionnaire 1, DK

Appendix C – Qustionnaire 2, DK

Bilag D – Questionnaire 2, UK

Introduction

The project ”Mapping of decabromodiphenylether (decaBDE) in other products than electrical and electronical products” was completed during the period May to November 2006. The project was completed for the Danish Environmental Protection Agency in connection with the Agency’s initiatives on the consumer project area.

The project was completed by a cross-functional project group at Eurofins Miljø A/S. MSc Peter Mortensen has acted as project manager and contact with the Danish EPA. Moreover, MSc Jane Pors and BSc Søren Brødsgaard have executed the project.

The purpose of the project was to map the use of decaBDE in products that are not included in the RoHS Directive, including e.g. cables, furniture, and textiles, together with an assessment of which substances or techniques that are used instead. The project is divided into 2 phases. This report describes the result of the first part of the project. A possible second part will include chemical analyses of selected consumer products for decaBDE content.

Summary and conclusions

DecaBDE is not produced in Denmark; however, in theory the compound may access the Danish market through import of the chemical agent as part of semi-finished products or as content in finished products. All three methods are investigated separately.

Information on imported chemical agents and semi-finished products are collected through public registers and contact to trade organization, while information on import of finished products are collected through the same channels supplemented by contact to companies associated in relevant trades. A detailed questionnaire has been sent to approximately 1,000 Danish companies with questions relating to decaBDE content in imported products and knowledge to alternatives, trends, and so on.

The collected information has documented decaBDE import within a number of trades.

5 ton of the compound as chemical agent or part of semi-finished products has been documented. The documented cases have all been import to the plastics industry. The investigation has proven that the major part is re-exported after processing. Import seems connected to isolated specialized contracts and there are no determined indications that decaBDE is used regularly in Danish production.

Data for import of chemical agents or semi-finished products are estimated valid and credible for Danish import from these channels.

As part of finished products decaBDE has been detected in tents, cars, and heat-shrink tubing. Import of decaBDE has not been detected in product groups as upholstered furniture, bedroom articles, cables, furnishing fabrics, glue, nursing articles, baby and children’s articles, paints and joint fillers.

Information on decaBDE import as part of a finished product is subjected to considerable uncertainty. The uncertainty is attached to the selection of product groups, response rate from companies, and the fact that many of the companies in question are unaware of a potential decaBDE content in their products.

It is estimated that the investigation covers so widely that it is unlikely that there are larger product groups using decaBDE that have not been involved. However, the response rate and the lacking knowledge of the products’ content are a larger problem. It is thus a question whether it is possible at this stage to gain an accurate scenario of the import through finished products.

During the project there have been many contacts to companies and centres of excellence. The obtained knowledge as compared to conclusions in formerly published investigations indicates that the greatest uncertainty is attached to the results within the area of imported means of transportation (cars) and upholstered furniture.

The mapping provides information on the fact that decaBDE is generally attempted replaced with other fire-retardant compounds or other methods. It is a general impression from the investigation that there is no demand for products with decaBDE fire-retardant properties in Denmark. In 1999 the Environmental Protection Agency concluded that the use of decaBDE seemed declining. This investigation confirms this assumption.

Sammenfatning og konklusioner

DecaBDE produceres ikke i Danmark, og stoffet kan derfor teoretisk få adgang til det danske marked via import af kemikaliet, som en del af halvfabrikata eller som indhold i færdigvarer. De tre ruter er undersøgt separat.

Oplysninger om importerede kemikalier og halvfabrikata er indsamlet via offentlige registre og kontakt til brancheforeninger mens oplysninger om import af færdigvarer er indsamlet via de samme kanaler suppleret med henvendelse til virksomheder i de relevante brancher. Der er udsendt detaljerede spørgeskemaer til ca. 1000 danske virksomheder med spørgsmål om indhold af decaBDE i importerede produkter samt kendskab til alternativer og trends mv.

De indsamlede oplysninger har dokumenteret import af decaBDE indenfor en række brancher.

Der er påvist import af skønsmæssigt 5 tons af stoffet som kemikalie eller som del af halvfabrikata. I de påviste tilfælde har der været tale om import til plastbranchen. Undersøgelsen har vist, at størstedelen eksporteres igen efter forarbejdning. Importen synes knyttet til enkeltstående specialordrer, og der er ikke fundet indikationer på, at decaBDE bruges regelmæssigt til produktion i Danmark.

Data for import som kemikalie eller som halvfabrikata skønnes at være valide og troværdige for den danske import ad disse ruter.

Som del af færdigvarer er der påvist import af decaBDE i telte, biler og krympeflex. Der er ikke påvist import af decaBDE i produktgrupper som polstermøbler, sengeartikler, kabler, boligtekstiler, lime, sygeplejeartikler, baby- og børneartikler samt malinger og fugemasser.

Oplysningerne om import af decaBDE som en del af en færdigvare er forbundet med betydelig usikkerhed. Usikkerheden knytter sig til udvælgelsen af produktgrupper, svarprocenten fra virksomhederne samt det forhold, at mange af virksomhederne mangler kendskab til et eventuelt indhold af decaBDE i deres produkter.

Det skønnes, at undersøgelsen er så bredt dækkende, at der næppe er større produktgrupper med brug af decaBDE, som ikke er inddraget. Svarprocenten og det manglende kendskab til produkternes indhold er imidlertid et større problem. Det er således et spørgsmål om det på nuværende tidspunkt er muligt at få et præcist billede af importen via færdigvarer.

Der har i løbet af projektet været mange kontakter til virksomheder og videnscentre. Den opnåede viden sammenholdt med konklusionerne i tidligere publicerede undersøgelser indikerer, at den største usikkerhed knytter sig til undersøgelsens resultater indenfor import af transportmidler (biler) og polstermøbler.

Kortlægningen har givet oplysninger om, at decaBDE generelt søges erstattet med andre brandhæmmende stoffer eller metoder, hvor det er muligt. Det er et generelt indtryk fra undersøgelsen, at der ikke er efterspørgsel efter produkter, som er brandhæmmet med decaBDE i Danmark. Miljøstyrelsen konkluderede i 1999, at forbruget af decaBDE syntes at være faldende. Denne undersøgelse bekræfter denne formodning.

1 Introduction and purpose

The Danish EPA has instigated the project ” Mapping of decabromodiphenylether (decaBDE) in other products than electrical and electronical products” in connection with a call for tenders of the project in the consumer project area.

The project’s purpose is described in the tender documents as follows:

”To map the use of decaBDE in products that are not included in the RoHS Directive, including cables, furniture, and textiles, together with an assessment of which substances or techniques that are used instead.”

The Danish EPA background for this project has been a desire to obtain information on the use of decaBDE outside the product groups that are already regulated through the RoHS Directive (Regulation no 1008 of 12.10.2004).

In the tender documents the Danish EPA has set the stage that the project be completed in two phases.

The first phase is a mapping and collection of present knowledge of the use of decabromodiphenylether (decaBDE) in products that are not included in the RoHS Directive, whereas a second phase consists of a completion of chemical analyses of selected product groups with the purpose of procuring deficient knowledge of occurrence and amounts of decaBDE in these product types.

The purpose is clarified in the following manner in the associated description of the project:

1.       A mapping of use of and trend in use of decaBDE in Danish produced and imported products that are not included in the RoHS Directive

2.       An assessment (and description) of present alternatives to decaBDE

3.       As required possible chemical analyses for decaBDE in selected consumer products.

This report describes the result of the abovementioned items 1-2. As mentioned item 3 is completed at a possible later stage.

DecaBDE used as additive to obtain a fire-retardant effect. Thus normally these are concentrations in percentage level in the products. In connection with this investigation this means that concentrations on trace level, due to accidental contamination are uninteresting and thus not included in this mapping.

2 Introduction to decaBDE

• 2.1 Introduction to decaBDE
• 2.2 Regulations

2.1 Introduction to decaBDE

Decabromdiphenylether (decaBDE) is a polybromsubstituted diphenylether (CAS no 1163-19-5).

The substance belongs to the group of brominated flame-retardants. This group of substances have found great use to fire protection of inflammable materials. The substances have in particularly become increasingly popular for fire protection of electronical products where the combination of inflammable materials (often plastics) and heat from the electrical parts form an ignition risk. Furthermore, the substance is used for fire protection of other inflammable materials.

A Danish investigation from 1999 (the Danish EPA 1999) estimated that the annual Danish use of brominated flame-retardants at 300-600 ton. Hereof it was estimated that the group of polybrominated diphenylethere (PBDE), as decaBDE is a part of, accounted for approximately 12%.

Brominated flame-retardants accumulate in nature and thus in the food chain. Some brominated flame-retardants are furthermore, suspected of having negative health effects. DecaBDE is thus e.g. on the EU’s list of substances that are regarded potentially hormone-disrupting. During the recent years the group of brominated flame-retardants, including decaBDE have be subjected to a number of investigations for this reason, and regulations and measures have been introduced with the purpose of limiting the use of the most critical brominated flame-retardants.

2.2 Regulations

According to the RoHS Directive and the associated Danish regulation (Danish Ministry of the Environment 2004a) DecaBDE is banned in electrical and electronical products. However, this ban is invalidated for decaBDE´s at the Commission’s decision from the 13th October 2005 (EU Commission 2005). Denmark has appealed this decision to the European Court of Justice with a view to make the decision void.

The substance is used as brominated flame-retardants in other consumer products than electronical articles. Currently, there is no further regulation of the use of the substance in Denmark.

Sweden has introduced a total ban on use of decaBDE in all products effective January 1, 2007, however, the regulations in the ROHS directive are observed with the provisional exception.

Other examples of brominated diphenylethers are pentabromdiphenylether and octabromdiphenylether that are both banned marketed according to Regulation no 76 of 9 February 2004 (Danish Ministry of the Environment 2004b).

DecaBDE is not manufactured within the EU; however, it is imported as both a chemical, part of semi-finished products, and as content in finished products.

3 Former mappings

• 3.1 Denmark
• 3.2 Nordic countries
• 3.3 EU

3.1 Denmark

In 1999 the Danish EPA carried out a mass flow analysis for brominated flame-retardants in Denmark (the Danish EPA 1999).

The mapping was concerned with all brominated flame-retardants. There was no separate specification for decaBDE as all polybrominated diphenylethere (PBDE) were processed as one item as a group.

The mapping concluded:

• That the total import of PBDE as chemicals or plastic raw material at the time of testing accounted for approximately 1 ton.
• That PBDE is imported to Denmark in a number of finished good. The specification of the total amount was associated with great uncertainty, however, with an estimated total consumption of PDBE of 30-120 tons annually.
• That content of brominated flame-retardants in imported products constituted approximately 90% of the total use of brominated flame-retardants.
• That the PBDE consumption was in decline.

The results of the investigation are summarized in the tables below (table 3.1 and 3.2).

Table 3.1: Import of PBDE as chemicals or plastic raw material in Denmark in 1997 (the Danish EPA 1999)

Table 3.2: Consumption of PBDE in Denmark in 1997 (the Danish EPA 1999)

If products comprised by RoHS and transportation means are disregarded the total consumption of decaBDE was estimated at 1.3 –11 tons per year.

Keep in mind that decaBDE is one of more polybrominated diphenylethers. The above mentioned results thus express the absolute maximum consumption of decaBDE in Denmark at the time of the investigation.

3.2 Nordic countries

During recent years both Norway and Sweden have published investigations regarding use of brominated flame retardants and including decaBDE.

In 2005 the Norwegian Statens Forurensningstilsyn (SFT) published a mass flow analysis for brominated flame retardants (SFT 2003). The investigation was based on data from 2001.

SFT concluded that the total Norwegian consumption of brominated flame retardants was in the range of 400-500 tons per year. Hereof decaBDE comprise 12-25 tons that are exclusively derived from synthetic rubber production (cellular rubber) for isolation of refrigerating installations in houses, ships, and offshore. There is no registered use of decaBDE for other purposes.

In 2004 the chemical inspection (Sweden) published a waste study of decaBDE (Chemical Inspection 2004). The study contained e.g. a review of the environmental and health risks associated with the substance and an estimate over application and applied amounts.

The report states that decaBDE is primarily used in electronical products (approximately 80%). The remaining 20% are distributed on the following product groups:

• Textiles
• Upholstery
• Cables
• Protective clothing
• Products relating to beds
• Cushions
• Hot-melt glue

The total import of decaBDE as chemical or raw material to Sweden in 2003 was estimated at 5.2 tons.

There is no specification over the import of decaBDE in finished goods.

3.3 EU

There are no manufacturers of decaBDE within the EU; however, EU has estimated that a total amount of 7300 tons (2003) is used for production of goods in EU. 80% of this amount is used for production of electronical products, while 20% (1460 tons) is used for a number of other product types.

The United Kingdom accounts for 50% of this last part corresponding to approximately 730 tons. This is due to strict national regulations for fire protection of furniture (EBFRIP 2004).

The same source indicates that 1300 tons decaBDE was imported in 2003 to the EU in finished goods. If it is assumed that these finished goods are distributed equally between the member states according to population this would in the case of Denmark correspond to 17 tons decaBDE imported through finished goods.

4 Method description

• 4.1 Introduction
• 4.2 Strategy
  • 4.2.1 Import as chemical
  • 4.2.2 Import as part of semi-finished produtcs
  • 4.2.3 Import as part of finished goods
  • 4.2.4 Other sources

4.1 Introduction

The mapping of the consumption decaBDE in Denmark has been completed in accordance to the Danish EPA’s paradigm for mass flow analyses (the Danish EPA 2000).  The mapping covers according to the project description only the 2 initial parts of the paradigm (1.1– 2.3) and 4.1. The volume of waste products will thus not be included in the analysis.

The newest possible data has been searched for in connection with this survey. This means that the contacted manufacturers and suppliers have delivered data from 2005. The public registers have delivered data from 2004 and 2005 respectively depending on the latest update.

The mapping is based on the mapping work that is available from e.g. the other Nordic countries. The result is moreover, compared with data from the Danish EPA’s mass flow analyses for brominated flame retardants from 1997 (the Danish EPA 1999).

The used sources are described in details in the following sections.

4.2 Strategy

DecaBDE is not manufactured in Denmark and thus the substance may enter the Danish market in three different ways. The figure below illustrates that correspondingly there may be export of decaBDE abroad.

Figur 4.1.: DecaBDE import and export to and from Denmark

The three import ways where treated separately in the survey and are described one by one in the following.

4.2.1 Import as chemical

Import of pure chemicals, including brominated flame-retardants must be reported to the Denmark's Statistics Office (Foreign Trade). The reporting is performed through the 2 following channels:

1. Via Intrastat that describes Denmark’s trade flow with the EU. Companies with an annual EU-import above 1.6 million DKK are obligated to report their import to Intrastat (EU 2004).
   
2. Via the Danish Customs and Tax Authorities. If the import takes place from a country outside the EU the reporting will be automatic through the imported goods’ customs clearance documents contrary to Intrastat. There is no lower threshold limit for when the goods are included (LBK 2005).

Information from the two mentioned sources is gathered at the Denmark's Statistics Office (Foreign Trade) to one specification titled: Foreign Trade Distributed on Goods and Countries.

Import and export of goods distributed on KN-product number are listed on this specification (Customs tariff). The specification also specifies import and export countries. The customs tariff is used to map the import of decaBDE as chemical. DecaBDE is listen on the specification under customs tariff no 2909.30.38: Bromine derivates of aromatic ethers, except pentabrominediphenylether (penta-BDE), tetrabromine(pentabrominephenoxy)-benzene, and tribrominephenoxy.

In this mapping it is assumed that the imported amounts under the mentioned customs tariff are comprised of decaBDE. Another alternative could be octaBDE, however, as octaBDE together with pentaBDE have been banned since 2004, it is most likely that the reported amounts are comprised of decaBDE and no other substance.

4.2.2 Import as part of semi-finished produtcs

DecaBDE may also enter the country as a component in semi-finished products (plastic raw material), if so it will be evident from the import register. This opportunity is thus been investigated partly through contacts to the trade association for plastic manufacturers partly at contact to the Danish Product Register.

Labelling obligatory substances and materials must be reported to the Product Register at import. DecaBDE is not included of this labelling obligation duty, however, nevertheless it may still be reported if the substance is included in a labelling obligated product or material. Reporting of decaBDE to the product register was mapped through the SPIN-database (SPIN 2006).

4.2.3 Import as part of finished goods

4.2.3.1 Gross list of product types

The information collection was initiated with examination of potential applications of decaBDE in products that are not included in the RoHS directive.

The following sources are primarily used for disclosing potential products with decaBDE content.

• Internet
• Published reports
• Search in product register (SPIN database)
• Common knowledge to chemical/technical products

The Internet was used to search information on potential application of decaBDE. The information was searched through websites for decaBDE manufacturers and for the European trade association from manufacturers of brominated flame-retardants (EBFRIP).

A number of published reports (including recent year’s Nordic reports), the Danish EPA’s own mapping projects and chemical-technical reference were reviewed for information on product types that may contain decaBDE.

Based on the above-mentioned sources a gross list of product types that potentially might contain decaBDE were identified. Table 4.1 shows the product groups that the test identified as interesting.

Table 4.1: Product types with potential decaBDE presence

4.2.3.2 Collection of information

The gross list was used by means of the NACE code system to select Danish companies within the identified product areas. The selection was performed through a database that is published by the Danish Grocery Industry’s information agency (KOB).

In order to limit the amount of companies all one-man businesses were discarded.

The table below shows the number of companies in the selected product groups (table 4.2.).

Table 4.2: Number of companies that have received a questionnaire in connection with the investigation

Moreover, 2 Danish suppliers/manufacturers of paints and joint fillers were contacted.

A questionnaire was sent to all companies in June 2006 containing questions on potential content of decaBDE in the goods that the companies market. The questionnaire is enclosed in appendix B. The auto industry was given customized questionnaire that is enclosed as appendices C and D (English version).

After the response deadline’s expiry in July 2006 all non-respondents were contacted by phone. In that connection the response deadline was extended with further 3 weeks.

The average response rate for all categories was 18.5% after the initial deadline. The telephone contact and extended response deadline resulted in further 1.5% response.

Appendix A contains a list of the single companies that were contacted in connection with this investigation.

With the responses of the additional questions in mind and the clarification of conditions in the industry a number of companies within the selected product areas were contacted directly.

4.2.4 Other sources

The analytical laboratory Eurofins Gfa GmBH in Hamburg was contacted in connection with the testing. This laboratory has offered analyses for brominated flame-retardants for many years. The analyses are primarily carried out in environmental samples (sludge, sediment etc.), however, during recent years the analyses have been performed on consumer products.

The laboratory was asked about:

• Number of analyses for decaBDE in consumer products over the past 2 years
• Number and result of analyses of products outside the RoHS directive’s area

During the last 2 years the laboratory has analysed to the extent of 50 consumer products for decaBDE content. The major part has been electronical products.

Several non-electronical products contained traces of decaBDE. The content presumably originates from other applied flame-retardants (impurities).

The laboratory database only contains one non-electronical product with a content of decaBDE above 1%. The actual example was seating foam for chairs with a content of 7.4 in percentage.

During the completion of this report Eurofins GfA GmbH analysed a sample of a polystyrene isolation plate from the German market. The analysis indicated a decaBDE content of 11 weight percentage. The contact to the Danish manufacture of polystyrene isolation plates indicated that this type of material formerly was added flame-retardant agents, however, Danish manufactured polystyrene isolation plates are not added flame retardant agents anymore. The manufacturer cannot dismiss that German construction companies takes flame-retardant polystyrene plates with them to Denmark in connection with concrete construction assignments, but this was considered to be of an insignificant extent.

5 Mapping of decaBDE in Denmark

• 5.1 Import of decaBDE as a chemical
• 5.2 Import as content in semi-finished products
• 5.3 Import as content in finished products
  • 5.3.1 The plastics industry etc.
  • 5.3.2 Means of transport
  • 5.3.3 The furniture industry
  • 5.3.4 Cables and electronic accessories
  • 5.3.5 Furnishing fabrics
  • 5.3.6 Wholesale textiles
  • 5.3.7 Camping
  • 5.3.8 Outdoor life
  • 5.3.9 Glues
  • 5.3.10 Nursing requisites
  • 5.3.11 Commodities for babies and children
  • 5.3.12 Paints and joint sealing compounds
• 5.4 Total statement of decaBDE
  • 5.4.1 Comparison with EU

5.1 Import of decaBDE as a chemical

From Statistics Denmark 2006 it appears that under customs tariff 2909.30.38 covering imports of bromine derivates of aromatic esters, including decaBDE, 2 tons were imported in 2005. As earlier mentioned, it is likely that these imports were imports of decaBDE.

Furthermore, it appears from statistics that the materials were imported from Sweden. It has not been possible to track the importing company, for which reason it is not possible to determine whether the material was used for products covered by the RoHS Directive or was re-exported. It is therefore assumed that the 2 tons are in fact products covered by this mapping and that consumption of the products has taken place in Denmark.

Through a contact in the plastics industry the project group got in touch with a company that imported 3 tons of decaBDE from the Netherlands in 2005. This material was used for the production of a master batch. After production, the master batch was re-exported to Germany where it has not been possible to trace the use. This amount is not included in the calculation of the total Danish consumption, as the entire amount was re-exported.

Furthermore, the company informs that the import in question and the following re-export of the master batch with decaBDE was an isolated order in 2005 based on some special competitive circumstances abroad. The company has not been met with any demand for master batch with decaBDE in Denmark. The same answer is given by a number of other Danish suppliers of raw materials for the plastics industry.

5.2 Import as content in semi-finished products

From the SPIN database it appears that 300 kg of decaBDE was imported in 2004 via products that are subject to a duty of notification. No amounts are stated for 2005.

Neither products nor importers appear from the part of the SPIN database that is open to the public. Through the Danish EPA, however, contacts were established with such companies. The two companies responsible for the above-mentioned notification have informed that:

• 250 kg decaBDE was imported as fire-retardant in casting resins for mounting in transformers – i.e. use for electronic and electrical products covered by the RoHS Directive
• 50 kg decaBDE was imported as a component in epoxy paint for a special job in England. It has not been possible to obtain further information. The whole amount was re-exported.

5.3 Import as content in finished products

5.3.1 The plastics industry etc.

5.3.1.1 Plastic raw materials

The group of suppliers of plastic raw materials was identified by reference to www.krak.dk.

Table 5.1: Result of the questionnaire survey for the product group Plastic Raw Materials

As it appears from the above, none of the respondents has used decaBDE the last year. This confirms the general information from the plastics industry that there is no demand in Denmark for master batch with decaBDE content. Note, however, that the supplier of plastic raw materials mentioned earlier who made the import of the 3 tons of decaBDE for the master batch did not respond to the questionnaire.

Two businesses inform that they use flame-retardants in their products, but not decaBDE. Alternatives include aluminium hydroxide and tris(1-chloro-2-propyl)phosphate.

5.3.1.2 Stadium seats

Internet search has revealed that decaBDE can be used for fire protection of seats for sports centres and stadiums.

Therefore, two Danish importers of this type of products were contacted by telephone. These two importers cover more than 50% of the market in Denmark.

Both inform that fire protected seats are not produced in Denmark and that, so far, none of the two companies have supplied fire protected seats to Danish stadiums.

One of the suppliers informed that the latest tenders for projects on public stadiums include requirements for use of fire protected seats and that; consequently, this type of seats will presumably be installed in future. More concise information on the nature of fire protection of such future seats was not available.

5.3.2 Means of transport

This group consists of importers and manufacturers of cars, trucks, buses, and trains. The NACE codes for this group are 15.10.10., 60.21.00 and 51.47.30. At the request of several of the respondents, the questionnaire used for this group was also sent in an English version with a view to obtaining information from the foreign manufacturer.

Table 5.2: Result of the questionnaire survey for the product group Means of Transport

One importer of cars from the East says that decaBDE is used in wire lugs for the electric system in the marque of cars that he imports. The amount used for one individual car is of the order of 1-5 gram. The car marque in question is a common marque on the Danish market. The marque covers many types of cars for private as well as business purposes and is therefore representative of the Danish fleet of cars.

Information was received from a supplier of one make of cars (Western European) that with certainty their cars do not contain decaBDE. Thus, the same content in all makes of cars marketed in Denmark cannot be presupposed.

In 1999 the Danish EPA stated that Northern European car manufacturers are supposed to have completely substituted poly brominated diphenyl ethers, including decaBDE, while cars with decaBDE are still imported from the East and the USA to Europe. On the assumption that at present this conclusion is correct for all cars manufactured in Europe and that the average amount of decaBDE in cars from other countries (primarily the East and USA) is 3 gram per car analogous to the details in this survey, this gives an average annual import of 240 kilos (table 5.3). In this table an estimate of the uncertainty of this number is stated in brackets. The uncertainty is estimated on the basis of the concentration interval stated (1-5 gram per car), the number of imported cars of the make in question and the total import of cars to Denmark from the East and the USA (2005), respectively.

Table 5.3: Annual import of decaBDE in cars

Several of the respondents are not sure, though, whether there is decaBDE in the cars they market. The Danish EPA (1999) states that a number of manufacturers use decaBDE for fire protection in parts of the car cabins. Verification of this has not been possible in this survey. In the affirmative case, however, the amounts in one car will be considerably larger than 1-5 gram and, as a consequence, the above-mentioned figures for consumption in Denmark are underestimated, if cars with decaBDE in cabin parts are still being imported.

A number of the responds received mention that since, at present, the use of decaBDE is not subject to any restrictions, suppliers make no demands on their sub-suppliers as regards the use of decaBDE.

One car manufacturer states that they primarily seek to use materials that already possess natural fire retardant qualities rather than add fire retardant materials.

5.3.3 The furniture industry

5.3.3.1 Upholstered furniture

Upholstered furniture is one of the product groups most often referred to, when it comes to the use of decaBDE in other than electronic products. The reason is that among others England and Ireland have specific rules laying down procedures for fire protection of this type of furniture.

Table 5.4 shows the result of an enquiry made among potential Danish manufacturers and suppliers of upholstered furniture. The NACE code system does not have a specific category for upholstered furniture alone, so the questionnaire was sent to a number of manufacturers and importers of furniture that do not include upholstered furniture in their assortment. The NACE codes for the businesses in this group are 36.11.00., 36.11.20., 36.15.00., 51.47.05. and 51.47.10.

Table 5.4 Result of the questionnaire survey for the product group Upholstered Furniture

The response rate is very low, which of course affects the validity of data negatively. In order to obtain supplementary information three Danish manufacturers of upholstered furniture were contacted by telephone. One has the furniture manufactured in Denmark, whereas the other two have the furniture manufactured in Eastern Europe and Asia.

Two of the three companies state that they definitely do not market FR treated (FR; Flame Retardant) upholsteries in Denmark. Both businesses produce FR treated upholstered furniture for sale in England. In one case the furniture is shipped directly from the foreign manufacturer to England without passing through Denmark. The other case is a special product not for sale in Denmark.

The third manufacturer informs that the production takes place in Eastern Europe and that FR treated furniture is imported to Denmark. E.g. Belgian companies carry out the FR treatment of textiles and cushions. In spite of repeated reminders it was not possible to obtain information on the type of FR treatment or on amounts imported. Presumably, decaBDE is still used for fire protection in furniture textiles in a number of countries, and therefore Danish imports of decaBDE in upholstered furniture cannot be ruled out. A calculation of amounts, however, is not possible.

One consultant, who has a long and detailed knowledge of the Danish furniture industry, claims that he is not aware of any cases of use of decaBDE in Danish furniture.

EUROPUR, the European trade association of foam manufacturers, has been contacted. EUROPUR has no knowledge of any use of decaBDE in PU (polyurethane) foam in Europe.

5.3.4 Cables and electronic accessories

5.3.4.1 Power cables

Cables used for alternating current of more than 1000 volts and direct current of more than 1500 volts are excepted from the regulations of the RoHS Directive and thereby covered by this survey.

Danish manufacturers and suppliers of cables were identified by means of contacts within the industry, references to guides and references to wholesale catalogues. A total of 1 manufacturer and 8 importers of cables were contacted. Sources within the industry have stated that the 9 businesses contacted cover more than 90% of the Danish market.

Table 5.5: Result of the questionnaire survey for the product group Cables

One Danish manufacturer of cables of this type was contacted by telephone. This manufacturer informed that brominated flame-retardants are used in no cables produced in Denmark, at all.

5.3.4.2 Heat shrinkable material

Information was found on the Internet that decaBDE can be used for fire protection of heat shrinkable material (flexible polymer material shrinkable by means of heat - used for e.g. insulation of live joints). A few multinational companies produce most heat shrinkable materials.

Heat shrinkable material is covered by the RoHS Directive, in so far as it is used for/mounted in connection with electric installations, but not if it is sold separately e.g. for other electrical purposes. Therefore it was chosen to include heat shrinkable material in this survey.

Such products are sold in all small and large electronics stores and in many hobby shops. As there are numerous retail shops in Denmark that sell heat shrinkable materials, and as the number of manufacturers worldwide is limited, enquiries about sale of decaBDE-containing products were made to the manufacturers instead of the retailers. Thus the three largest suppliers to the Danish market were approached.

Table 5.6 below summarizes the result.

Table 5.6: Result of the questionnaire survey for the product group Heat Shrinkable Material

Import of decaBDE was identified through the one manufacturer that responded. The material in question was a special product; of which the total annual amount sold was barely 200 m heat shrinkable material. The content of decaBDE was stated to be barely 10 percent by weight.

On this basis, the annual amount of decaBDE imported by this manufacturer can be calculated to be less than 1 kg. If we assume that the other manufacturers of heat shrinkable materials use the same amount of decaBDE, this implies a total annual import of less than 5 kg.

Table 5.7: Annual import of decaBDE in heat shrinkable products

*: the estimate results from an assumption of the same relative share of decaBDE in imported products.

5.3.5 Furnishing fabrics

Flame retardants can be used in a number of furnishing fabrics, such as carpets and curtains. The group covers wholesale and manufacturing of all textiles for the home, except clothing. Fixed and movable carpets, curtains, cushions, tablecloths, bed linen etc. are all included under this group. The NACE codes for the group are 17.40.20., 17.51.00., and 17.40.90.

Table 5.8: Result of the questionnaire survey for the product group Furnishing Fabrics

The completed questionnaires and telephone contact to selected companies in the group of respondents gave the following information on the product group:

There are no general requirements regarding fireproofing of furnishing fabrics in Denmark apart from mattress covers.

None of the manufacturers or dealers mentions use of decaBDE. One respondent describes use of another brominated flame-retardant, and others use inorganic flame-retardants. According to the questionnaires we have received, a number of manufacturers/dealers use materials with inherent flame retardant qualities, such as the polyester fabric Trevira CS with integrated metal compounds.

Brominated flame-retardants are not used in carpets manufactured in Denmark.

5.3.6 Wholesale textiles

Furnishing fabrics are also available through dealers registered as “wholesale textiles”. This group also covers textiles sold for later use in clothing, upholstery etc. However, the group cannot be split up further under the NACE code 51.41.00. Thus, the products include textiles sold directly as well as textiles sold for further manufacture.

Table 5.9: Result of the questionnaire survey for the product group Wholesale Textiles

The completed questionnaires together with telephone contacts to selected businesses in the group gave a good deal of information about the product group.

As was the case with the previous product group, there are no general European requirements regarding fire applying to this product group. However, a few countries, e.g. England, have specific rules regarding fire protection.

One answer indicates the use of halogenated flame-retardants, but not decaBDE. This manufacturer, though, works at phasing out this type of flame-retardants. Several manufacturers report using materials such as Trevira CS, Duraflam, and Duracote. The fire retardant qualities of the two last-mentioned products are based on organic and inorganic phosphorus compounds, including ammonium phosphates.

Dealers of large textiles for sports centres, such as nets, room dividers etc., were contacted by telephone. This product group is not subject to any fire requirements, but one type of material frequently used for room dividers is a material with inherent flame-retardant qualities. None of the respondents acknowledge having used decaBDE.

5.3.7 Camping

To investigate the product group Camping, wholesale businesses selling sports items and/or camping equipment were contacted. The NACE code of this group is 51.40.10 and this covers manufacturers/importers of sunblinds, other types of sunscreens, Venetian blinds, tents etc. Excepted are businesses that could be immediately identified as irrelevant in this connection, such as sail makers, rope makers and flag factories.

Table 5.10: Result of the questionnaire survey for the product group Camping

The completed questionnaires together with telephone calls to selected companies from the group gave the following information on the product group:

Large party tents within this group are subject to requirements for fire safety, but no one uses decaBDE for the purpose. Many of the products within this group use PVC canvas that is inherently fire retardant due to the large content of chlorine. The content of plasticizers in plasticized PVC may necessitate extra fire protection.

A large Danish manufacturer/importer informs that treatment with flame-retardants have become more common in camping tents. This manufacturer uses decaBDE as flame-retardant, thereby accounting for the only confirmative answer in the group. Production takes place in China. The majority of the imported tents are re-exported. Part of the import goes to England. The business has provided information on expected sales for 2007 as data for the investigation.

Table 5.11 shows the actual figures that are based on information on the consumption of decaBDE. The figures in brackets show the estimate range for the consumption of decaBDE in tents in Denmark. The estimate is based on the information received from the one importer about the average content of decaBDE in tents and from Statistics Denmark: Im- and exports January-December 2005.

To convert imports of synthetic tents from tons to number of tents, the project group has based their calculation on an assumption that an average tent weighs 15 kg. Based on this assumption, annual imports will amount to 160.000 tents. This seen in combination with the actual data leaves a maximum import of 190 kg to Denmark via tents. According to market information and data from Statistics Denmark a large part is being re-exported, leaving the share of decaBDE for use in Denmark at less than 190 kg, as seen in table 5.11 below.

Table 5.11: Annual imports of decaBDE in tents

Regardless of the uncertainties of this estimation, the amounts accessing Denmark through imports of tents are still limited.

5.3.8 Outdoor life

To include all tents, the group Outdoor Life is also covered. The NACE code for this group is 51.47.35. and it includes tarpaulins and camping and sports equipment. Excepted from the group are businesses manufacturing or dealing in equipment for golf, riding, horse racing, and yachting

Table 5.12: Result of the questionnaire survey for the product group Outdoor Life

Together with the questionnaire responses, a few businesses in the group were contacted. No respondents had stated a use of decaBDE or other flame-retardants. Awnings were stated as containing no fire retardants, and tarpaulins, in general, were made of PVC, which has natural fire retardant qualities.

5.3.9 Glues

A source (Kemikalieinspektionen 2004) has stated that hot melt glues may contain decaBDE. The NACE code for this group is 24.62.00 and comprises glue factories.

Table 5.13: Result of the questionnaire survey for the product group Glues

Subsequent contact to Kemikalieinspektionen confirms that decaBDE is no longer used in hot melt glues. Thus, the project group considers glues to be completely decaBDE free.

5.3.10 Nursing requisites

Requisites to be used by sick, weak or disabled consumers need more safety in case of fire. Products such as cushion seats/wheelchair cushions, mattresses, duvets/pillows and bed linen are available with flame-retardants for this particular consumer group.

The products constitute a grey zone when it comes to legislation on medical equipment. The products are only subject to the Order (BEK no 1268 of 12/12/2005) when marketed directly as equipment for disabled persons. The buyers on the market, however, demand fire protection of these products.

Countries like England, France, the Netherlands, and Belgium also step up their focus on fire safety in order to satisfy more players on the market.

No information was found regarding any use of decaBDE in this type of products.

One supplier states that duvets/pillows are fire protected by means of Trevira CS, cotton/linen fire protected by means of Pyrovatex, and that smoking aprons are made of glassfibre material. Pyrovatex is based on inorganic phosphorous compounds (Environmental guidance for work clothing). Other actors inform that they use Fyrol FR2 (tris-(1,3-dichloro-2-propyl)phosphate) for fire protection of textiles.

5.3.11 Commodities for babies and children

Consumer products intended for children and babies were investigated, particularly car seats, bicycle trailers, prams, and push chairs.

The largest actors on the market within the four product groups were contacted by telephone.

The calls revealed that no flame-retardants are added to neither bicycle trailers, prams, pushchairs, nor car seats in Denmark.

5.3.12 Paints and joint sealing compounds

As earlier paints have been said to contain PBDE (Table 3.2), three actors on the market were contacted, two of who practically cover the market for fire protecting paints and joint sealing compounds. Both state that flame retardant substances are not added to their products. Instead, their products swell or expand when exposed to heat (structural fire protection).

5.4 Total statement of decaBDE

All facts demonstrated in this investigation are gathered and shown in table 5.14.

Table 5.14: Summary of the findings with regard to annual imports of decaBDE (2005)

1 Covers a group of chemicals including decaBDE; most likely it is decaBDE. Use of the chemical is unknown

2 Stated as an isolated export order

3 Stated as an isolated export order

4 Annual imports to Denmark can be estimated at < 5 kg

When decaBDE is imported as a chemical or as semi-finished products we often speak of single, isolated orders. Nothing indicates a regular use of decaBDE in Denmark. Isolated cases, however, will most likely happen every year in an amount estimated at less than 5 tons. Apparently, most of the material is being re-exported, leaving only a small amount for consumption in Denmark.

Imports of cars constitute the major uncertainty, as only two car manufacturers have submitted detailed answers, one of which uses decaBDE. Other car manufacturers could perhaps be using decaBDE in man-made materials or fabrics for the cabin, as indicated in other investigations. As the total potential amount from such materials by far exceeds the other amounts, cars constitute a field that should be studied more closely in order to throw light on the actual present use of decaBDE.

Three large actors, of whom only one has submitted information for this project, dominate the market for heat shrinkable material. If their use of decaBDE is representative of the other manufacturers, the total consumption of decaBDE in Denmark within this product group will amount to less than 5 kg.

One tent importer and dealer using flame-retardants as surface treatment of the tents have been identified. This does not exclude the possibility that other importers use flame-retardants, but the contact to the other large importers on the market has shown that they do not use fire retardant additives. I any case, within this product group the total import is therefore limited and will hardly exceed 50 kg as net consumption (imports minus exports) for Denmark.

No use of decaBDE has been demonstrated within the product group Upholstery Furniture. The investigation has shown that furniture with fire retardants are still being imported to Denmark to a certain degree, but knowledge about decaBDE as a flame retardant component is very insufficient. There is reason to assume that furniture with content decaBDE is being imported to Denmark, because the component is still being used worldwide for the purpose, and because hardly any special products are being made only for the Danish market.

Foreign laboratory analyses have demonstrated use of decaBDE in polystyrene boards. Insulation boards of polystyrene produced in Denmark do not contain decaBDE, and nothing indicates any import of decaBDE through these materials.

5.4.1 Comparison with EU

As mentioned earlier, the total import through finished products to EU has been calculated to be 1300 tons corresponding to 17 tons for Denmark when distributed proportionally by number of inhabitants. As it appears from the previous sections, it has not been possible by this survey to demonstrate imports of this volume.

However, it is doubtful whether the European data can be applied proportionally within the individual countries, the reason being, partly, national regulations as known from England and Ireland and, partly, national differences in the use of fire protective products. That national differences can be considerable appears from the fact that is has not been possible for this investigation to demonstrate the same consumption of decaBDE for cellular rubber as was demonstrated in a Norwegian investigation (SFT 2003).

6 Alternatives

• 6.1 Alternatives to decaBDE – summary of questionnaire responses
• 6.2 Trends in the use of decaBDE

Due to presumably negative health and environmental impacts at brominated flame-retardants (including decaBDE) usable alternatives have been searched for systematically over the recent years. In this connection detailed catalogues containing alternative have been prepared – e.g. the Chemical Inspection
(Kemikalieinspektionen) 2005 and the Danish EPA 1999.

In principle a reduction in the application of decaBDE may be in one of the following ways:

1.       Substitution of decaBDE with another and less problematic connection without changing the material that needs protection (substance substitution).

2.       Change to another material that does not require flame protection or use of other less problematic flame retardant chemicals (material substitution)

3.       Substitution of the product with another product or another technology that does not presuppose use of decaBDE (design changes)

There are a number of alternatives for decaBDE available today and the previously mentioned reference contains besides a listing of possible alternatives also concrete examples of the three principles mentioned above.

The alternative selection depends on a number of factors. Besides the alternative’s health and environmental properties the ”right” choice is also determined from a number of factors linked to the production and properties at he finished product. The Danish EPA 1999 summarized these significant properties in the headings listed in table 6.1.

Table 6.1: Basic significant conditions when selecting alternatives to decaBDE (The Danish EPA 1999)

As mentioned the Danish EPA 1999 and the Chemical Inspection (Kemikalieinspektionen) 2005 contain comprehensive lists over alternatives to decaBDE in a number of different materials and product types. The reader is thus referred to these lists for inspiration to possible alternatives for concrete materials/products.

In connection with the completed questionnaire study the participant were asked of their knowledge to potential alternatives to decaBDE in their products just as trends in use of decaBDE were asked for.

The same question was sought answered at direct contact in the project stages and especially in the three cases if actual use of decaBDE that was identified.

6.1 Alternatives to decaBDE – summary of questionnaire responses

It is practically identical feedback from the contacted companies that decaBDE is sought replaced with other flame retardant substances or methods if possible.

The following substances and substance groups are represented in case of decaBDE substitution with other substances:

• Metal hydroxides – e.g. magnesium hydroxide
• Metal hydrates – e.g. aluminium trihydrate
• Organic phosphorus compounds – e.g. tris(1-chloro-2-propyl)phosphate
• Inorganic phosphorus compounds – e.g. ammonium phosphates
• Other brominated flame-retardants – e.g. ethane-1,2-bis(pentabromphenyl)
• Metal compounds – e.g. silver (in woven or as nanotechnology)

The use of brominated flame-retardants within paints and joint fillers has been substituted by structural flame-retardant properties, where the flame-retardant effect is obtained by the materials increasing in extent effect at heat impact, thus avoiding or delaying the heat impact of the protected parts.

In other situations the potentially inflammable materials have been substituted with non-flammable materials e.g. use of woven glass fibre materials smoke aprons for senior citizens and disabled persons.

6.2 Trends in the use of decaBDE

The completed mapping has only demonstrated limited or sporadic use of decaBDE in Denmark.

There has only been a determined total import under 300 kg decaBDE as part of finished goods in the present mapping and 5 tons as chemical/semi-finished products. The Danish EPA (Miljøstyrelsen) 1999 has a registered use of 30-120 tons per year for polybrominated diphenylethers. The two mappings have applied different method of assessment and can thus not be immediately compared – however, there is reason to assume that the total use of PBDE and thus decaBDE has decreased since the mapping in the late 1990s. The Danish EPA (Miljøstyrelsen) 1999 concludes that the use of decaBDE seems to have decreased since the late 1990s. Present mapping confirms this assumption.

It is a general assumption from contacts with companies and trade organizations that there is no demand for products that have been flame-retardant treated with decaBDE in Denmark and that the companies seek to substitute decaBDE with other substances or methods if possible.

There is thus no reason to assume that the use of decaBDE will increase in Denmark in the future unless new product types with decaBDE content are introduced.

7 Conclusion and summary

• 7.1 Method
• 7.2 Imported amounts of decaBDE to Denmark as chemical or semi-finished products
• 7.3 Imported amounts of decaBDE to Denmark as part of finished products
• 7.4 Alternatives and trends in the use of decaBDE

This report presents the result of the project ”Mapping of decabromodiphenylether (decaBDE) in other products than electrical and electronical products”. The project is part of the Danish EPA’s continuous initiatives on the consumer product area.

The project was purposed to map the use of decaBDE in products that are not covered by the RoHS Directive and give an assessment of trends and alternatives to use of decaBDE in this type of products.

The project’s initial phase is mapping and collection of present knowledge on use of decaBDE in products that are not covered by the RoHS Directive, while a potential second phase will consist of a number of chemical analyses of selected product groups with the purpose to procure missing knowledge occurrence and amounts of decaBDE in these product types.

DecaBDE is used as an additive to obtain a flame-retardant effect. Normally this would mean concentrations in percentage levels in the products. In connection with this project this means that concentrations on trace levels due to unintentional contaminations are uninteresting and thus not included in this mapping.

7.1 Method

The mapping of the use of decaBDE in Denmark has been completed in accordance to the Danish EPA’s paradigm for mass flow analyses (item 1.1-2.3 and 4.1).

DecaBDE is not produced in Denmark and the substance may thus theoretically enter the Danish market through import of the chemical or as part of semi-finished products or finished goods. The three routes are investigated separately. The information on imported chemicals and semi-finished products are collected through public registers and contact to trade associations, while the information of finished goods are collected through identical channels added inquiry to companies in the relevant trades. A detailed questionnaire containing questions on decaBDE content in imported products and knowledge of alternatives and trends has been sent to approximately 1000 Danish companies.

The total response rate is approximately 20% from the contacted companies. Naturally the low response rate has an impact on the validity of the results – not least due to the few ”findings” of decaBDE in the material.

Furthermore, the project group has found that most importers of finished goods know very little of potential decaBDE content in the imported goods. It is thus likely that there are false negative responses in the material.

7.2 Imported amounts of decaBDE to Denmark as chemical or semi-finished products

The collected information has documented import of decaBDE within several trades.

There is a determined import of estimated 5 tons as chemical or part of semi-finished products. The determined cases have been import to the plastic industry. The investigation has shown that the major part is reexported following processing. The import seems connected to single special orders and there are no indicators that decaBDE is used regularly in Danish production.

The collected information on import of decaBDE as chemical and semi-finished product is assessed to provide a credible image of this import to Denmark. It is, however, notable that the investigation documented import of 3 tons chemical that was not registered in the public registers.

7.3 Imported amounts of decaBDE to Denmark as part of finished products

There is a determined import of decaBDE in finished products as tents, cars, and heat-shrink tubes. The use for tents is estimated to 32 kg (23-110 kg), while the heat-shrink tubes are estimated at less than 5 kg per year.

The estimated import for cars is 240 kg per year (18-1000 kg) that originates from flame retardant connectors. Besides the uncertainty that is attached to the estimate for these components, the estimate for cars is connected with uncertainty due to potential use of decaBDE for the interior of the car. This investigation has not been able to determine a considerable use for this purpose as former investigations have.

There is no determined import of decaBDE in the product groups upholstery, bedding articles, cables, furnishing textiles, glues, health articles, baby and children’s articles, and paints and joint fillers.

The investigation of the import of finished products is connected with considerable uncertainty. The uncertainty is connected with the selection of product groups, response rates from companies, and the companies’ knowledge of potential decaBDE content in their products.

It is assessed that the selection of product groups in this investigation is adequately comprehensive to the fact that it is unlikely that there are product groups with considerable use of decaBDE that are not represented.

As mentioned the average response rate was approximately 20%. Naturally the remaining 80% represents a certain uncertainty, and there is no doubt that this group contains companies that import finished products with decaBDE content.

The third source of uncertainty is the companies’ actual knowledge to potential decaBDE content. As the substance is not regulated many importers’ knowledge is presently insufficient. A number of the contacted companies have made a huge effort to clarify whether decaBDE is part of their products in connection with the questionnaire. However, there are also companies that refer to the fact that the substance is not regulated for which reason detailed knowledge is not necessary.

During the course of the project there have been many contacts to companies and centres of excellence. The obtained knowledge as related to the conclusions in the formerly published Nordic mappings indicates that the greatest uncertainty is connected to the investigation’s results within import of transportation means (cars) and upholstery.

7.4 Alternatives and trends in the use of decaBDE

Companies and trade associations inform that decaBDE is sought substituted with other flame-retardant substances or methods if possible. It is a general impression from the investigation that there is no demand for products that are flame-retardant treated with decaBDE in Denmark.

A wide variety of methods and substances are used to substitute decaBDE and the investigation has determined use of structural flame retardant properties as well as substitution with substances that are regarded less problematic in terms of health and environment relations.

The completed mapping has only limited and sporadically mentioned use of decaBDE as chemical and semi-finished products in Denmark just as the import through finished products seems limited to no more than a few tons a year.

As it appears from the above mentioned the estimated use is connected with great uncertainty and the question is whether it is possible to obtain a precise estimate of the total use in Denmark. When the investigation’s results are joined the result is that use of decaBDE for flame-retardant purposes is limited in Denmark. In 1999 the Danish EPA (Miljøstyrelsen) concluded that the use of decaBDE seems to be decreasing. This investigation confirms this assumption. Thus there seems to be a clear tendency towards a minor use of decaBDE.

There is no reason to assume that the use of decaBDE will increase in Denmark over the coming years unless new product types with decaBDE content are introduced.

References

Bekendtgørelse om begrænsning af import og salg af elektrisk og elektroniks udstyr, der indeholder visse farlige stoffer (BEK nr. 1008 af 12.10.2004).

Danmarks Statistik 2006, Udenrigshandelen fordelt på varer og lande, januar-december 2005, Danmarks Statistik, 2006.

EBFRIP 2004: European Brominated Flame Retardant Industry Panel – refereret i Kemikalieinspektionen 2004.

EU 2004: Kommissionens forordning (EF) nr. 1982/2004 af 18. november 2004 om gennemførelse af Europa-Parlamentets og Rådets forordning (EF) nr. 638/2004 om statistikker over varehandelen mellem medlemsstaterne og om ophævelse af Kommissionens forordning (EF) nr. 1901/2000 og (EØF) nr. 3590/92.

EU kommissionen 2005: 2005/717/17/EC af 13. oktober 2005.

Kemikalieinspektionen 2004: Dekabromdifenyleter (dekaBDE) – underlag til et nationellt förbud. Stockholm 2004.

Kemikalieinspektionen 1/2005: Survey and technical assessment of alternatives to decabromodiphehyl ether (decaBDE) in plastics. Stockholm 2005

LBK 2005: Bekendtgørelse af toldloven, Lovbekendtgørelse nr. 867 af 13/09/2005, Folketinget, 2005.

Miljøstyrelsen 2000. Paradigme for massestrømanalyser (Paradigm for mass flow analyses), Miljøprojekt nr. 577, Miljøstyrelsen 2000

Miljøministeriet 2004a: Bekendtgørelse nr. 1008 af 12.. oktober 2004 om begrænsning af import og salg af elektrisk og elektronisk udstyr, der indeholder visse farlige stoffer.

Miljøministeriet 2004b: Bekendtgørelse nr. 76 af 9. februar 2004 om begrænsning af import, salg og anvendelse af penta- og octabromdiphenylether.

Miljøstyrelsen 1999: Brominated Flame Retardants. Substance Flow Analysis and Assessment of Alternatives.

Miljøvejledning for arbejdsbeklædning med værneegenskaber. Udkast nr. 03 af 2005-03-10. Udarbejdet af HHK, IPU

SFT 2003: Bruken af bromerte flammehemmere i produkter. Statens Forurensningstilsyn, Oslo 2003.

SPIN 2006: Substances in Preparations in Nordic Countries, Arbejdstilsynet, Register for stoffer og materialer, 2006

Appendix A – List of companies

List of the companies to which the questionnaire was sent and/or that the project group has been in telephone contact with.

Auto importers

Plastic raw material supplier

Upholstery

Furnishing fabrics

Wholesale textiles

Outdoor

Outdoor activities

Glue factories

Cables

Miscellaneous

Appendix B – Questionnaire 1, DK

Below questionnaire was sent to the following product groups:

Plastics raw material suppliers, Upholstery, Furnishing fabrics, Wholesale textiles, Outdoor life, Outdoor activities, Glue factories, and Cables.

Appendix C – Questionnaire 2, UK

Below questionnaire was sent to the following product groups:

Auto importer

Bilag D – Questionnaire 2, UK

Below questionnaire is the English version of the questionnaire in appendix C. The questionnaire was sent to auto importers.

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Version 1.0 August 2007, © Danish Environmental Protection Agency