Authors: de Lary de Latour, L; Guérin, V; Gatellier, C; Piat, C

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DOI https://doi.org/10.36487/ACG_repo/2215_90

Cite As:
de Lary de Latour, L, Guérin, V, Gatellier, C & Piat, C 2022, 'Implementing phytostabilisation for tailings deposits remediation: project design and feedback from case studies in France', in AB Fourie, M Tibbett & G Boggs (eds), Mine Closure 2022: Proceedings of the 15th International Conference on Mine Closure, Australian Centre for Geomechanics, Perth, pp. 1219-1230, https://doi.org/10.36487/ACG_repo/2215_90

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Abstract:
Due to economic and environmental reasons, French mines closed down in the 19th and 20th centuries. In 2012, a legacy of more than 2000 metallic mine waste deposits was identified in the framework of an inventory resulting from the European Directive on the management of wastes from extractive industries. The dispersion of solid particles, especially tailings due to their fine grain size, can contribute risks to the environment and specifically to surface water through transport and leaching. Waste deposits with bare surfaces can result in significant transfers of sediments through hydraulic erosion. In this context, phytostabilisation strategies are valuable remediation options to mitigate the risk of transfer. However, only a few full-scale phytostabilisation implementations have yet been completed in France. This paper deals with the deployment of phytostabilisation to remediate legacy tailings deposits in the French context, focusing on operational aspects and feedback from several case studies (former Ag-Pb mines from Massif Central and Sn and Au mines from the Pays-de-la-Loire region). Phytostabilisation relies on the use of plants and amendments to reduce mobility of pollutants in soil and transfers trough environment. In the French context, the aim is to reduce, to an acceptable level, transfers from waste deposits to the surrounding environment, particularly due to surface erosion and, to a lesser extent, leaching. Conventional approaches to confining mining waste are mainly based on water management, landform design and covering the soil with subsequent revegetation. With this approach, plants are used to stabilise the soil layer that has been deposited above the tailings. Thus, plants do not directly stabilise mine tailings, as is the case with phytostabilisation strategies. From case studies, we show that evaluating the benefits of phytostabilisation requires using appropriate new criteria for the cost-benefits analysis in order to capture the ecosystem services that control the stabilisation process (ecosystem services such as soil creation, water regulation, erosion reduction). Costs are expected to be lower because it tends to minimise intervention. Furthermore, long-term perspectives, technology readiness, constraints due to access and site immobilisation, costs of remediation and maintenance and social perception are key criteria that also require appropriate evaluation. As biological organisms, plants have inherently variable responses that must be considered in project management. Thus, based on case studies, strategies have been developed to tackle uncertainties by implementing laboratory and pilot tests. A phytostabilisation project needs a sound understanding of site functionality that can be synthetised on a conceptual site model. Based on a case study, we show that design at a detailed scale can optimise phytostabilisation solutions. Evaluation of pollutant fluxes enables prioritisation of actions on zones with critical transfers. Identification of stable (no transfers) zones due to spontaneous vegetation minimises intervention, costs and ecological impact. To complement phytostabilisation, other solutions are necessary to reduce erosion on critical zones or adapt the technology to site constraints (e.g. soil cover, fascines, areas for rainwater infiltration). Perspectives for long-term site evolution are then discussed in terms of the solutions implemented (conventional or phytostabilisation). Return of experience still needs to be gathered in the years to come in order to improve management by phytostabilisation.

Keywords: phytostabilisation, tailings, mine waste, erosion, ecosystem services.

References:
Barthe, P, Eder, P, Saveyn, HGM, Orveillon, G & Garbarino E 2018, European Commission, Joint Research Centre, 2018, Best available techniques (BAT) reference document for the management of waste from extractive industries: in accordance with Directive 2006/21/EC, European Union, Luxembourg,
Bellenfant, G, Guezennec, AG, Bodenan, F, D’Hugues, P & Cassard, D 2013, 'Reprocessing of mining waste: combining environmental management and metal recovery?', in M Tibbett, AB Fourie & C Digby (eds), Mine Closure 2013: Proceedings of the Eighth International Seminar on Mine Closure, Australian Centre for Geomechanics, Cornwall, pp. 571-582,
Courtin-Nomade, A, Waltzing, T & Evrard, C 2016, ‘Arsenic and lead mobility: from tailing materials to the aqueous compartment’, Applied Geochemistry, no. 64, pp. 10–21.
European Union 2006, Directive 2006/21/EC of the European Parliament and of the Council of 15 March 2006 on the management of waste from extractive industries and amending Directive 2004/35/EC, Statement by the European Parliament, the Council and the Commission, Luxembourg,
GEODERIS 2012, Inventaire des dépôts issus des exploitations minières selon l’article 20 de la directive 2006/21/CE. Synthèse des résultats (Inventory of deposits from extractive industries, article 20 of 2006/21/CE Directive), RAPPORT N2012/009DE12NAT2120
Hasselt, IRH 2006, ‘Phytostabilisation Difpolmine, Diffuse pollution from mine activity’, Final Report, Budapest University, European program LIFE 02 ENV/F/000291,
ITRC 2009, ‘Phytotechnology Technical and Regulatory Guidance and Decision Trees’, revised, PHYTO-3, Washington, D.C.: Interstate Technology & Regulatory Council, Phytotechnologies Team, Tech Reg Update.
Larcheveque, M, Derochers, A, Bussiere, B & Cimon, D 2014, ‘Planting trees in soils above non-acid-generating wastes of a boreal gold mine’, Ecoscience, vol. 21, no. 3–4, pp. 217‒231.
Ministry in Charge of Environment 2017, Méthodologie nationale de gestion des sites et sols pollués (French methodology for polluted soils management), DGPR
Mertz, S 2021, Devenir de contaminants métalliques (Pb, Zn) depuis un dépôt minier ancien: développement d’un modèle de transport réactif (Fate of metal contaminants (Pb, Zn) from an old mine deposit: development of a reactive transport model), PhD thesis, University of Orléans, Orléans.
Nandillon, R 2019, Phytostabilisation des éléments métalliques d’un technosol minier végétalisé par le genre Salix assisté par du biochar (Phytostabilization of the metallic elements of a mining technosol vegetated by Salix assisted by biochar), PhD thesis, University of Orléans, Orléans.
Piramid 2003, The Passive Remediation of Acidic and/or Metaliferous Mine Drainage and Similar Wastewater, University of Newcastle Upon Tyne, Newcastle Upon Tyne.
Sheoran, V, Sheoran, A & Poonia, P 2013, ‘Phytostabilisation of metalliferous mine waste’, Journal of Industrial Pollution Control, vol. 29, no. 2, pp. 183–192.




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