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See all EU institutions and bodiesKey messages: EU legislation has led to less waste in the EU going to landfills, as well as measures to prevent and treat landfill leachate (LFL). LFL remains a significant environmental threat due to the presence of toxic pollutants that can contaminate groundwater, surface waters and soil if not adequately monitored and controlled. Data on contaminants in LFL is scarce due to limited monitoring requirements. The collection, treatment and monitoring of LFL presents technical and logistical challenges for landfill operators. Existing wastewater treatment plants may not be able to adequately treat such waste streams. Further efforts are needed to reduce waste landfilling, for which a reduction of waste generation is essential.
Rate of waste landfilled (excluding major mineral wastes), 2010-2020
Landfill leachate (LFL) is the liquid that has seeped through solid waste in a landfill, extracting soluble dissolved or suspended materials in the process. When leachate escapes from landfills it can contaminate groundwater, surface waters and soil with toxic organic and inorganic pollutants; these include heavy metals and ammonia nitrogen compounds, as well as emerging pollutants such as pharmaceuticals, plasticisers and Per- and polyfluoroalkyl substances (PFAS). Therefore, ensuring adequate measures are in place to monitor, prevent and treat LFL is essential for protecting human health and the environment.
Managing LFL releases to the environment
The EU Landfill Directive 1999/31/EC sets out strict operational requirements for landfill sites, including provisions for effective sealing systems and the collection and treatment of LFL. Prior to the implementation of this directive, landfilling in the EU was not consistently regulated across Member States. The legislation has resulted in significant improvements in the way landfills (and specifically LFL) are managed. Landfilled waste decreased by 27.5%, from 173 million tonnes to 125 million tonnes between 2010 and 2020. Over the same period, the share of waste generated (excluding major mineral waste) that is being landfilled in the EU has declined from 23% to 16% as shown on the Figure. However, leachate generation remains a problem. The collection and treatment of leachate also continues to be a major management issue facing landfill operators. This issue is likely to continue for decades to come.
Brennan et al. (2016) used historic landfill data, combined with leachate characterisation data (e.g. total nitrogen, chemical oxygen demand and total metals) to determine the impacts of a number of EU Directives (Landfill Directive, Waste Framework Directive 2008/98/EC, Urban Wastewater Treatment Directive 91/271/EEC and the Water Framework Directive 2000/60/EC) on landfill leachate management, composition and treatability in Ireland. The study indicated that there was a reduction in the volume of leachate produced per tonne of waste landfilled in Ireland since the Landfill Directive was enforced, but the concentration of pollutants in leachate has increased.
Challenges in collecting and treating LFL
The collection and treatment of LFL presents technical and logistical challenges for landfill operators. As it is often not possible to treat LFL on site, it is becoming common practice to transfer leachate to wastewater treatment plants (WWTPs) and co-treat LFLs with domestic sewage. To date, there has been limited investigation into the environmental impacts of co-treatment of landfill leachate and municipal wastewater in WWTPs. Studies have been largely limited to laboratory-scale batch experiments. This lack of data is a concern for WWTP managers, as wastewater effluent is subject to increasingly stringent legislation in the EU, for example under the proposal for a revised Urban Waste Water Treatment Directive. This has raised questions regarding how LFLs will be managed going forward and the implications for future environmental and human health impacts.
Though the EU Landfill Directive mandates Member States to establish a monitoring regime for landfills, more specific requirements for monitoring the quantities and concentrations of pollutants in leachates are needed to ensure comprehensive oversight. There is a lack of regulatory requirements in the EU to monitor the volumes and/or concentrations of contaminants that are present within leachates. As a result, data on contaminants in LFL is scarce and is usually available from academic studies of specific landfill facilities for a specific time period. Therefore, there is currently no reliable way to assess the magnitude of risk posed by LFL to the environment and human health.
Possible solutions
Preventing landfill leachate is important for mitigating environmental contamination and promoting sustainable waste management practices. Waste prevention, and proactive waste diversion strategies, such as recycling, reduce the volume of waste disposed in the landfills, thereby decreasing leachate generation. In addition to the updates to Waste Framework Directive and Landfill Directive, the new Circular Economy Action Plan, also underscore the importance of reducing landfilling and promoting sustainable waste management practices, thereby indirectly targeting leachate prevention.
On the other hand, several new technologies and processes to treat LFL are being developed which can be adopted and deployed in conventional WWTPs. For example, floccular activated sludge has evolved to granular sludge processes; shortcut denitrification processes can potentially lower the oxygen and carbon requirement for nitrogen removal; membrane processes can provide higher effluent quality; more advanced aeration methods enhance energy efficiency, instrumentation and control; and automation capabilities have increased. Several projects in the EU have focused on treating landfill leachates, including the CLEANLEACHATE project, which explored a treatment system for the removal of refractory organic substances and ammonium by oxidation processes without chemical additives in LFLs; and the OXFLOC project, which aimed to reduce treatment costs of industrial wastewater in Europe and has been tested with LFL. In addition, while generally not specific to landfilling activities, the ‘Best Available Techniques Reference Documents’ (BREFs) developed to support the Industrial Emissions Directive 2010/75/EU implementation is also a useful source of available technical solutions for treating effluents. For example, the BREF on common waste water treatment techniques in the chemical sector is of particular relevance.
References and footnotes
- ↵EEA, 2004, Landfill leachate (https://www.eea.europa.eu/help/glossary/eea-glossary/landfill-leachate).
- ↵Masoner, J. R., et al., 2014, ‘Contaminants of emerging concern in fresh leachate from landfills in the conterminous United States’, Environmental Science: Processes & Impacts 16 (10), pp. 2335-2354 (https://pubs.rsc.org/en/content/articlelanding/2014/em/c4em00124a/unauth).
- ↵El‐Saadony, M. T., et al., 2023, ‘Hazardous wastes and management strategies of landfill leachates: A comprehensive review’, Environmental Technology and Innovation 31, p. 103150 (https://www.sciencedirect.com/science/article/pii/S2352186423001463).
- ↵EWA, 2017, ‘Leachate from landfills: Volume and environmental impact from landfills reduced through EU environmental legislation - but legacy effects remain’, European Water Association (https://www.ewa-online.eu/article-3-leachate-from-landfills.html).
- ↵Koda, E., et al., 2017, ‘Levels of organic pollution indicators in groundwater at the old landfill and waste management site’, Applied Sciences 7 (6), p. 638 (https://www.mdpi.com/2076-3417/7/6/638).
- a b cEU, 1999, Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste (OJ L 182, 16.7.1999, pp. 1–19).
- ↵The latest data available is for 2020, so the COVID-19 pandemic may have influenced the outcome.
- ↵Brennan, R.B., et al., 2017, ‘Treatment of landfill leachate in municipal wastewater treatment plants and impacts on effluent ammonium concentrations’, Journal of Environmental Management 188 (1), pp. 64-72 (https://www.sciencedirect.com/science/article/abs/pii/S0301479716309471).
- ↵Brennan, R. B., et al., 2016, ‘Management of landfill leachate: The legacy of European Union Directives’, Waste Management 55, pp. 355-363 (https://www.sciencedirect.com/science/article/abs/pii/S0956053X15301598).
- a bEU, 2008, Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives (Text with EEA relevance) (OJ L 312, 22.11.2008, pp. 3–30).
- ↵EU, 1991, Council Directive 91/271/EEC of 21 May 1991 concerning urban waste-water treatment (OJ L 135, 30.5.1991).
- ↵EU, 2000, Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for community action in the field of water policy, (OJ L 327, 22.12.2000, pp. 1-73.).
- ↵EC, 2020, COMMUNICATION FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS A new Circular Economy Action Plan For a cleaner and more competitive Europe (COM/2020/98 final), (https://eur-lex.europa.eu/resource.html?uri=cellar:9903b325-6388-11ea-b735-01aa75ed71a1.0017.02/DOC_1&format=PDF),).
- ↵EU, 2010, Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control) (recast) (Text with EEA relevance) (OJ L 334, 17.12.2010, pp. 17–119).