Select Committee on Environment, Food and Rural Affairs Eighth Report


APPENDIX: VISIT TO DENMARK

The Committee undertook a three-day visit to Denmark in March 2003 to learn about the Danish approach to waste management, because Denmark is often held up as an example of a country with a successful sustainable waste management system for all kinds of waste.

Danish Environmental Protection Agency

The Committee spoke to Christian Fischer, Head of the Household Waste Division and Lene Bjerg Kristensen from the Copenhagen EPA.

STATISTICS

Of all waste produced in Denmark in 2001, 63% was recycled, 25% was incinerated with energy recovery, 10% was landfilled and 1% went for special treatment. However, recycling of construction and demolition waste accounts for a large part of the recycling figure. When household waste alone is considered, 30% was recycled, almost 60% was incinerated and just over 10% was landfilled. Mr Fischer told the Committee that, except for paper and glass, Denmark does not usually source recycled materials from households as they are too dirty and contaminated with other materials. He said that recycling rates were much higher in other sectors.

HISTORY - REASONS FOR CHANGE

Until the 1980s, Denmark still relied heavily on landfill. The shift from landfill was precipitated by concerns over groundwater pollution, particularly because all of Denmark's drinking water comes from groundwater. There was also little remaining space to site new landfills and the country relied heavily on imported fuel and was eager to find alternative energy sources.

However, we were told that one of the reasons Denmark could adapt to a new system was that there was already a basic infrastructure that could deal with all kind of waste, that is, incineration with energy recovery, landfill and disposal of hazardous waste. This infrastructure needed to be in place before they could adapt to changed priorities.

POWERFUL LOCAL GOVERNMENT

The Danish waste model is based on the premise that waste management is a public sector task[93] and depends on a combination of legislation and taxation. The national government formulates nation-wide waste plans and is responsible for national legislation and economic instruments. Municipal and regional councils are in charge of the practical administration of waste management. They must ensure there is sufficient capacity to deal with all the waste that is produced. This is possible because municipalities direct waste from all sources to the treatment or disposal site of their choice and waste producers must comply. For commercial waste, the waste producer hands the waste to an approved carrier (there are a number of approved carriers in each municipality so there is a degree of choice), and the carrier then transfers the waste to an approved treatment plant (there is no choice of treatment plant). Both the carrier and the treatment plant must submit information to the Environment Protection Agency

Since 1992, all landfill sites have had to be owned by municipal authorities (except that some industries may operate landfill sites solely for their own use). Most incinerators are owned by municipalities or groups of municipalities. This public ownership and the fact that municipalities control where and how waste is disposed of (recycling is mainly privately run) mean that there is effectively no competition between landfill sites or incinerators. There is currently a debate about whether the waste sector should be liberalised. Industry would prefer to send its waste to the cheapest plant and not necessarily the one chosen by the municipality. Some industry figures are in favour of liberalisation as a matter of principle and say they would accept higher waste management costs provided there was competition.

There are a number of laws which promote the waste hierarchy. Waste that can be recycled or burnt is banned from landfill. The paper and glass fractions of household waste must be collected separately for recycling (collection may be either via kerbside schemes or through local bring sites and other waste fractions are also often collected). Construction and demolition waste must be separated into separate fractions at source, in order that as much as possible may be recycled.

GRADUATED WASTE TAX

The EPA attributed much of Denmark's success in moving waste up the hierarchy to its graduated waste tax, which is highest for waste going to landfill at 375 Danish krona per tonne (DKK/t), lower for incineration with energy recovery (all waste incinerators in Denmark recover energy) at 330 DKK/t and zero rated for recycling. The tax is on top of any fee charged by operators of the waste management facility.

The difference in that tax on landfill and incineration is such that some companies 'mine' combustible waste that was landfilled before the ban and incinerate it, in order to claim the rebated landfill tax.

Revenue from the waste tax was 1.1 billion DKK in 2001. There is some discussion about how this revenue should be used; at present 75 million DKK goes to support recycling and the development of clean technologies and the rest goes into the waste budget.

WASTE AND ENERGY POLICIES COORDINATED

Since the 1960s, there have been district-heating systems in many Danish towns, including Copenhagen. These were originally based on oil, but the fuel crisis of the 1970s promoted a switch to coal, gas and alternative fuels including waste. Any new incineration plant requires the approval of the Energy Agency and since the mid-1990s it has required that incineration produce electricity as well as heat. Waste incinerators currently provide 10% of Denmark's heat supply and 3% of its electricity. The Environmental Protection Agency checks that sufficient waste is available for each plant, but equally looks to ensure there is no over-capacity lest there be less motivation for recycling. As a result, incineration capacity relative to total waste arisings is stable, even though new incinerators are being built or existing ones expanded to cope with increases in the amount of waste produced. Planning permission for new incinerators is a matter for the local councils rather than the EPA. The whole process (from seeking permission to coming online) usually lasts between four and six years, including appeals, for a new incinerator. 60% of the plants already meet the requirements of the European Union Waste Incineration Directive.

Incineration

The Committee visited Vestforbrænding, a waste treatment company owned by 21 municipalities. It treats the waste of 800,000 inhabitants in 22 municipalities (the 21 co-owners and one other). The company's main business is incineration: 65% of the waste it deals it is burnt. However is also recycles 30%, landfills 4% and 1% goes to specialist hazardous waste treatment. In 2001, the waste incineration produced 1,066,000 MWh in district heating and 108,000 MWh of electricity production. The waste burnt replaces about 165,000t of fuel oil. The company charges industries a fee of 200DKK/t for handling the waste (the waste tax is added to this charge but goes direct to national government). This fee covers the nets costs of treatment once the income from heat and power generation has been deducted. The company expects its cost to decrease as it moves from five lines to two and accordingly expects to drop its fees to about 100DKK/t excluding tax.

Environmental performance is monitored by the Environmental Protection Agency and emissions are controlled. For example, dust is removed by an electrostatic filter, oxides of nitrogen are reduced to nitrogen gas using ammonia and dioxins are bound using lime and active carbon. Where possible, waste products are sold on as raw materials to other companies, but at present the fly ash and flue gas cleaners are exported to Norway for landfill. However the company and the EPA are working on ways to stabilise or recycle this waste as well. We were told that, although fifteen or twenty years ago there were "tough discussions" with people living close to the plant, the incinerator is accepted now. The EPA told us that this was largely because the incinerators were local, so people accepted that it was their waste that was being treated and that useful products - district heating and electricity - were generated.

For a new plant, it takes about seven or eight years between permission first being sought and operation. This includes two years discussing alternatives, two years to obtain the necessary planning permission and licensing and three or four years building the plant.

Recycling - household waste

The Committee visited a municipal recycling centre and a block of flats whose residents voluntarily separate their domestic waste.

There is some kerbside collection of fractions such as paper and glass and some municipalities are experimenting with source separation and collection of a greater range of recyclable waste types, but the majority of recycling for household waste relies on individuals taking their waste to bottle and paper banks or 'bring sites' for other fractions.

The recycling centre in the municipality of Herlev handles about a third of all the waste in that municipality. It is a 'bring site', where householders and small businesses can take the recyclable fractions of their waste free of charge. It will accept 27 different types of waste and in 2002 the centre processed more than 20,000 tons of waste, delivered in the course of 170,000 visits. 77% of this waste was recycled. About 50% of the waste received is from smaller construction projects in private households or carried out by the building industry. The recycling centre also receives household hazardous waste, such as paint, batteries and household chemicals. The amount of hazardous waste received has been stable at 74 tons per year for the last few years.

The Committee also visited a residential housing block in the Nørrebro district of Copenhagen, where a pilot project on source separation is being conducted. Nørrebro has 30,000 inhabitants and, before the waste sorting project began, sent 15,000t of waste per year for incineration. Now a quarter of the inhabitants take part in the project and those people have cut the amount of waste they send for incineration by half.

The project takes place in residential housing blocks, which in Nørrebro are built around a central courtyard. A 'waste station' is built in the courtyard which houses containers for different types of waste: paper and magazines; glass; food scraps for compost; cardboard; aluminium and other metal. Only non-meat food scraps can be composted, and there is an on-site closed composter. The resulting compost is often used for the courtyard gardens. In addition to the collection points for waste for recycling, composting and disposal, residents can deposit bulky waste (e.g. refrigerators, furniture, electronic equipment) and dangerous or hard-to-handle waste (such as batteries, anything containing mercury, and PVC plastics). There is also an 'exchange corner' where items that could be re-used, such as clothes, shoes, toys can be left. Residents can help themselves to these items and the remainder are periodically collected by charities such as the Red Cross. Finally, there is a 'garbage' bin for the remainder of the waste. The content of this bin are collected by a waste management company and delivered to an incinerator.

The scheme is voluntary, and its success appeared to rely heavily on the caretaker of the apartments, who, in addition to carrying out repairs in the (rented) apartments and managing the garden, also helps residents recycle by advising them on what kinds of waste go into each container and encouraging them to separate their waste. There is an overall saving to the landlord because only the waste sent to the incinerator is subject to the waste tax, but this saving is not very significant for the tenants.

Recycling - construction and demolition waste

About a quarter of Danish waste, or 3.1 million tonnes, comes from construction and demolition. Denmark achieves very high rates of recycling (about 90%) of waste from this sector, partly because there is a tax on waste that is not recycled. The government has also reached agreements with the Danish Contractors' Association about selective demolition, for example. We were told that although a high proportion of construction waste is recycled, the amount recycled is equivalent to only 5% (in 1995) of the raw materials used.

The Committee visited a construction site to see source separation of construction and demolition waste and a company, RGS90, that accepts such waste, treats it and sells it on as a replacement for aggregates, among other things.

At the construction site, there were a number of lorry containers, one for each fraction of waste and, as it arose, the builders put each item of waste into the appropriate container. The containers are taken away several times a week.

RGS90 was originally an aggregates supplier, and moved into recycling construction and demolition waste into replacement aggregates when Denmark's waste tax was raised. This private company occupies a 100 hectare site on the outskirts of Copenhagen and handles between 10% and 15% of all Denmark's waste.

Construction waste is delivered to the site, sorted, and treated if necessary, in order to produce high quality aggregates replacements. The company charges a higher fee for accepting unsorted waste because only a lower-grade product can be made. Since developing the aggregates recycling business the company has expanded into higher technology, value added activities such as soil remediation, PVC recycling and transformation of sewage sludge into a rockwool substitute.

Composting

In Denmark, household waste, including organic waste, is usually sent for incineration, although there are some moves towards composting and biogasification. 'Green' waste, that is, plant material from parks and gardens is composted. The Committee visited the Solum group, which runs large scale composting facilities. Green waste is accepted, sorted, shredded and composted in either windrow or mattress systems for three years. The company charges waste producers to accept the waste and then sells the compost. We were told that the sale of the compost alone did not generate enough income to maintain the company and that the gate fees were therefore essential. The company produces composts of different grades, suitable for different purposes.

The Danish government has said that it would like to increase the proportion of household organic waste that is collected. Biogasification, i.e. anaerobic digestion to produce methane, is the government's preferred route, in order to recover both energy and nutrients from the waste.

Both the EPA and private companies such as the Solum group are conducting research on ways of minimising the human and animal health risks posed by composting animal by-products.

Landfill

In Denmark, landfill is regarded as the last resort for waste, and is only to be used for waste which cannot be re-used, recycled or incinerated. Landfilled wastes include asbestos, non-recyclable PVC, impregnated wood, contaminated soil, residues from car shredding and the bottom ash from municipal incinerators. In the past, the flue gas cleaning residues were also landfilled, but since 1999, these have been sent to Norway. In addition, mixed waste is stored in separate landfill cells during periods when the incinerators are not operating. This waste is later 'mined' back out and incinerated.

The Committee visited a landfill site owned jointly by two municipal waste treatment companies; Vestforbrænding and Amagerforbrænding. The site was built by the two companies on land reclaimed from the sea specifically for that purpose. A site below sea level was seen as less environmentally damaging because leachate from the landfill site would not leak out into groundwater. (Instead, sea water percolates slowly into the landfill and is pumped out and treated, a system which is easier to control than normal leaching.)

The rate of landfilling waste has slowed over the lifetime of the site, which in turn means that it had more remaining capacity than first anticipated and that it will stay open for longer.



93   Biodegradable municipal waste management in Europe. Part 1: Strategies and Instruments. European Environment Agency Topic Report 15/2001. January 2002, p.33. Back


 
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