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Incineration

Eliminating waste by incineration

  • Hazardous waste
  • Waste
  • Final waste disposal
  • End of life

Incineration is the process of burning waste material in a controlled facility in order to reduce the volume and the toxicity of waste. It is a complex process which requires careful management to ensure it does not generate irreversible impacts on the environment and human health through the emanation of toxic gases. (1)

Why is this important?

When waste cannot be recycled, repaired, or reused, last option is to neutralise it and dispose of it safely.

In most humanitarian settings, environmentally friendly options for the end-of-life process of waste are limited and present numerous environmental and health challenges (see factsheet on final waste disposal in humanitarian settings).

Unlike landfilling, which requires a large fenced, controlled sanitary field, with regulations and trained staff, incineration demands much less space and significantly reduces the volume of waste.

However, inadequate combustion of waste can generate serious environmental (e.g. air, soil, food contamination) and health risks (e.g. cancer, cardiovascular problems, negative effects on reproductive systems) due to the emission of ‘forever’ chemicals (e.g. dioxins, furans and particulate matter) which can travel long distances and persist in the environment.(2) Such hazards occur when the temperature is not high enough, and the combustion is incomplete.

When incineration is the only available option, minimising the associated risks is essential to upholding the “do no harm” principle.

What are the solutions?

The primary solution is always to reduce the amount of waste produced and discarded. For the remaining waste, incineration can be considered as an option. Incineration is most commonly used for infectious, medical, or hazardous waste (exceptions include e-waste which can be recycled/repurposed, and wet organic waste which does not burn easily) as a way to reduce the risks of contamination of the environment or of people. In the case of perished drugs, incineration is used as a way to eliminate the risk of them being resold on the black market.

Incineration differs from open-air burning in that it occurs in a controlled facility, where high temperatures are achieved and emissions can be partially reduced. Incinerators must be situated away from residential and cultivated areas. Four types of incinerators are used in humanitarian settings:

  • The drum reducer, barely better than open-air burning, and not promoted here;
  • The DeMontfort Incinerator, a double-chamber small scale incinerator available in kit and relatively easy to build anywhere, able to reach 850°C;
  • Semi-industrial incinerators are more robust and long–lasting, but more expensive;
  • Industrial sites, such as cement kilns or similar factories, sometimes accept to burn waste in their very high temperature furnaces.

To avoid irreversible effects on the environment, the incineration of waste needs to reach a minimum temperature of at least 850°C for a minimum of 2 seconds (3) and at least 900°C for medical waste.(4) While this is very difficult to verify, it is critical to aim for this standard to avoid irreversible effects on the environment and human health.

  • Point of attention

    Incineration should not divert efforts away from the priorities of reducing, reusing, and recycling waste.(10)

    Incineration is dangerous and toxic. Even in best condition with catalytic filters in high income countries, a municipal waste incinerator produces almost 5 times more polycyclic aromatic hydrocarbons (PAH), a major toxic pollutant, than a coal factory.(11) The waste-to-energy principle is questioned, arguing that in the US, waste incinerators emit almost twice as much CO2e per Kwh produced than coal electricity plants.(12)

Key figures

850°C

Waste needs to be burnt at 850 °C for at least 2 seconds to avoid irreversible health and environmental damage.

2,500

There are more than 2,500 cement factories around the world. (9)

1,000 – 2,000 USD

A De Monfort incinerator costs approx. 1000-2000 USD.

500 – 700 m

A buffer zone of approx. 500 to 750 m around the incinerator facility is required. (6).

1 ton

of municipal waste incinerated corresponds to 0.7 to 1.2 ton of CO2 .(13)

Key actions

  • # 1 Reduce waste as a priority

    Keep reducing the quantity of waste produced and disposed of. Even the best incineration produces greenhouse gas emissions and toxic pollutants. Follow the Waste Management principles.

  • # 2 Ban open air or drum burning of waste

    Open burning of waste is particularly harmful as it releases pollutants such as dioxins, furans, or particulate matter also called ‘forever chemicals’ which remain in the environment and have significant long-term negative effects on the environment and human health.(1)

  • #3 Explore local legislation and existing infrastructure

    Although not always enforced, national legislation on final waste disposal must be respected. Look for existing legally approved facilities, which are certified for transport and disposal of hazardous and non-hazardous wastes.

  • #4 Collaborate with other humanitarian organisations

    Pooling resources with other humanitarian organisations present in the country might be particularly beneficial from a logistical and financial perspective. Some organisations might have already assessed and partnered with cement kilns or might have built/purchased an incinerator which your organisation can benefit from. HULO (14)  and the WREC project might support you in developing joint initiatives on waste management.

  • #5 Choose the appropriate facility and assess its processes

    Get expert advice to help you choose the appropriate disposal technique. If the available incineration option does not reach environmental standards (i.e.: combustion for at least 2 seconds at 850°C), landfilling might be a preferred option. Check if other organisations have assessed the facilities, and would be willing to share their findings. Make regular visits.

  • #6 Set up the partnership

    Set up a contract with the facility, including rights to visit. Partnerships might include a fee which would need to be anticipated in budgets.

  • #7 Consider upgrading the facility

    When existing incinerators do not meet environmental standards, consider evaluating options to provide technical and financial support to upgrade an existing facility. This is in general more sustainable than building or purchasing a new one.  Set a clear timeframe and safely store the waste in the meantime. Collaborate with other key actors, such as UN agencies or international NGOs. Ensure that sufficient budget is allocated for ongoing maintenance, including fuel and human resources.

To consider

  • Potential co-benefits

    • Energy use reduction: Energy use can be reduced when waste is used as a fuel in cement kilns.
  • Success conditions

    • Compliance: Infrastructure and protocols must be strictly checked and ensured to be legally compliant.
    • Distance: A reasonable distance must be maintained between the project site and the incineration facility.
    • Transportation: Transportation must be effectively planned and managed.
    • Storage: Adequate storage must be ensured for waste.
    • Maintenance and staffing: Incinerators must be well maintained, with trained staff and financial resources allocated to meet environmental standards.
    • Exit strategy: An exit strategy must be developed to ensure the facility can continue operating after the end of the intervention.
    • Budget: Sufficient budget must be planned for maintenance and operating costs.
  • Prerequisites & specificities

    • Combustion temperature: A minimum temperature of 850°C must be reached for at least 2 seconds during combustion.
    • Regular assessment: The facility must be visited and assessed regularly with expert support.
    • Collaborative efforts: Mutualised efforts between actors, such as partnerships with cement factories or joint incinerator building/purchase, should be made to reduce costs.
  • Potential risks

    • Temperature and fume quality: The temperature achieved in incinerators and the toxicity of fumes may be difficult to accurately assess.

Success stories

Waste-to-energy plants in Sweden incinerate waste and make energy

Sweden only landfills 1% of its waste. After thorough sorting, 50% of Swedish municipal waste primarily consisting of biomass, plastics, and paper—is incinerated and converted into energy, such as electricity or heating.

Tools and good practices

  • DeMonfort Incinerator guidelines, 2004

    Managing Health Care Waste Disposal: guidelines on how to construct, use, maintain a waste disposal unit.

    Read here
  • MSF Pacemaker guide on waste management and green logistic, 2024

    Médecins Sans Frontières developped and published in 2024 the ‘PACE MAKER-100 Logistical solutions for meeting climate and environmental commitments’, with a section page 242 on how to choose an incinerator.

    Read here
  • UNEP Guidelines for medical waste incineration, 2012

    The Environmental Council of Zambia (ECZ) and Ministry of Health (MoH), supported by UNEP and other actors, developed specifications to ensure adequate incineration of medical waste.

    Read here
  • Path Guidebook to choose the best small-scale incinerator, 2010

    This guidebook is intended to be a practical guide for selecting, purchasing, installing, operating, and maintaining small-scale incinerators in low-resource settings.

    Read here
  • Advantages and disadvantages of waste incineration

    A video from Waterpedia Environmental Learning Series.

    Read here

To go further

  • International Solid Waste Association (ISWA), The white book on energy from waste recovery, 2023

    The Working Group on Energy Recovery (WGER) published this guidance on energy-from-waste (instead of waste-to-energy or incineration).

    Explore more
  • GIZ, Guidelines on pre- and co-processing of waste in cement production, 2020

    Guidance on necessary conditions for pre- and co-processing of waste. It is addressed to public and private stakeholders and decision-makers from the waste and co-processing sector. It provides suggestions about possible steps as well as practical examples.

    Read here
  • Global Alliance for Incineration Alternative (GAIA), Facts about “waste-to-energy” incinerators, 2018

    Facts published by GAIA showing the dark side of incineration and criticising waste-to-energy practices.

    Explore here
  • UNEP, Beyond an age of waste, 2024

    This report is addressed to policymakers, governments, industry and international organisations, and provides information and recommendations to reduce waste worldwide, including reusing waste as a resource.

    Read more
  • International Panel on Climate Change (IPCC), Emissions from waste incineration, 2003

    An IPCC study about emissions generated by waste incineration practices.

    Find out more
  • Review on pollutants emitted by incineration in rotary kilns in China, 2019

    Analysis and review of different studies concerning waste incineration in cement kilns in China and other countries.

    Learn more
  • Waste incinerators undermine clean energy goals, 2023

    Study in the United States showing that waste incineration is not a viable option to clean the air quality.

    Read here
  • The role of incinerators in reducing greenhouse gas emissions, 2024 (in French)

    An article discussing the European regulations driving the modernisation of waste incineration facilities.

    Explore here
  • Plasma gasification versus incineration of plastic waste: Energy, economic and environmental analysis, 2022

    Study about the promising technology of plasma gasification to eliminate plastics, instead of incineration: less polluting, producing more energy, and economically viable.

    Explore more

Last updated 19 August 2024.

Share your success stories, suggestions, and comments with us! contact@climateactionaccelerator.org

Sources

(1) United Nations Environment Programme, ‘Global Waste Management Outlook 2024: Beyond an age of waste’, Turning rubbish into a resource, 2024, Available here (accessed 20 August 2024).

(2) UN Environment Programme, ‘Stokholm Convention on Persistent Organic Pollutants’, 2019, Available here, (accessed 20 August 2024).

(3) Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions, ‘Integrated pollution prevention and control’, EUR-Lex, 2010, Available here, (accessed 20 August 2024).

(4) SPHERE Handbook, Standard 6: Wash in healthcare settings, 2018, Available here, (accessed 20 August 2024).

(5) Making Medical Injections Safer, ‘The incinerator guidebook’, 2010, Available here, (accessed 20 August 2024).

(6) Batterman, ‘Findings on an Assessment of Small-scale Incinerators for Health-care Waste’, World Health Organisation, 2004, Available here, (accessed 20 August 2024).

(7) World Cement, ‘The cement industry in emerging countries’, 2018, Available here, (accessed 20 August 2024).

(8) Médecins Sans Frontières France, ‘Pace Maker’, 2024, Available here , (accessed 20 August 2024).

(9) CN Cemnet, ‘The Global Cement Report – Online Database of Cement Plants’, Available here, (accessed 20 August 2024).

(10) Gaia, ‘International Zero Waste Cities Conference,’ Available here, (accessed 20 August 2024).

(11) T. Hsu, M. C. Liu, P. C. Hung, S H. Chang, M. B. Chang,‘PAH emissions from coal combustion and waste incineration’, ScienceDirect, 2016, Available here, (accessed 20 August 2024).

(12) Tangri, Waste incinerators undermine clean energy goals’, PLOS Climate, 2023, Available here, (accessed 20 August 2024).

(13) Johnke, ‘Emissions from waste incineration’, IPCC, Available here, (accessed 20 August 2024).

(14) Hulo, ‘Joint Initiatives’, Available here, (accessed 20 August 2024).

Cover photo: Karsten Füllhaas/Unsplash