Legislation and Technical Aspects of Regulations on Waste Containing Mercury in Europe and Germany Thomas Brasser, GRS Latin America Mercury Storage Project.

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Presentation transcript:

Legislation and Technical Aspects of Regulations on Waste Containing Mercury in Europe and Germany Thomas Brasser, GRS Latin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Who is GRS (‚Plant & Reactor Safety Ltd.‘) Non-profit, independent expert and research organisation Assess and improve safety of technical facilities Focus on nuclear safety and waste management Customers: Ministries and authorities, European Commission Technical support of BMU conc. safety of chemicals, e.g. Hg About 400 employees, offices in several European countries International co-operations ISO 9001:2000 certified Latin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009 [For details see: Th. Brasser, GRS

22 October 2008: Adoption of Regulation (EC) No 1102/2008 on banning of exports of metallic mercury *) and safe storage by EU legislator One of the key elements for implementation of EU mercury strategy adopted in 2005, as well as Council Conclusions of June 2005 and December 2008 on the need for international action on mercury Basic aim of regulation to prevent surplus mercury **) from re-entering global market Storage Obligation for Metallic Mercury (1) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009 *) as well as certain mercury compounds and mixtures **) mainly resulting from closure of mercury-cell facilities in the chlor-alkali industry

Amount at stake estimated at up to 13,000 tonnes of metallic mercury Remaining (and declining) EU demand for mercury at legal uses up to 580 tonnes/year Export ban complemented by storage obligation Storage Obligation for Metallic Mercury (2) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Storage obligation covers metallic mercury from 4 major sources: - no longer used in chlor-alkali industry - gained from cleaning of natural gas - gained from non-ferrous mining and smelting operations - extracted from cinnabar ore in the EU Other, smaller sources deliberately not covered to maintain supply for remaining legal uses, e.g. - dental amalgam - some types of batteries - energy saving light bulbs - electronic equipment Storage Obligation for Metallic Mercury (3) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Temporary or permanently in salt mines *) or in deep underground hard rock formations **) Temporary only in above-ground facilities ***) („temporary“ not defined, but normally more than 1 year) Purpose of allowing temporary storage is not to jeopardize efforts to find alternative solutions to storage, e.g. solidification Storage Obligation for Metallic Mercury (4) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009 *) adapted for the disposal of metallic mercury **) providing a level of safety and confinement equivalent to that of salt mines ***) dedicated to and equipped for the temporary storage of metallic mercury Regulation allows only few storage options:

Council Directive 1999/31/EC of 26 April 1999 on the landfill *) of waste Key piece of EU legislation in the field of waste disposal Stringent operational and technical requirements to prevent possible negative effects on the environment Not to be operated without appropriate permit by competent authority General EU Rules for Waste Storage (1) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009 *) notion „landfill“ = very broad, covers sites for waste disposal onto or into land

Council Directive 1999/31/EC on the landfill of waste (cont.) Application for permit must contain all relevant information - type and quantity of waste - capacity of the site - geological and hydrogeological characteristics - proposed measures for pollution control - monitoring and control plan - plan for closure and after-care of the site - financial security provided by applicant - environmental impact assessment (acc. to local conditions) Permit only to be granted if authority is satisfied with all elements Liquid waste not to be accepted in a landfill, but now derogation for metallic mercury General EU Rules for Waste Storage (2) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

2003/33/EC: Council Decision of 19 December 2002 establishing criteria and procedures for the acceptance of waste at landfills Complement and particularizing of the landfill directive by detailed technical requirements Criteria for waste acceptable at landfills dedicated to hazardous waste *) Criteria for underground storage, including specific considerations for salt mines Long-term safety assessment required for underground storage All provisions of landfill directive as well as of criteria and procedures apply to a storage facility of metallic mercury General EU Rules for Waste Storage (3) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009 *) Metallic mercury as well as waste containing mercury is classified as hazardous waste under EU legislation

Council Decision 2003/33/EC establishing criteria and procedures for the acceptance of waste at landfills Criteria for underground storage - A site-specific safety assessment as defined in Annex A Importance of geological barrier - Ultimate objective of underground storage = Isolation of wastes from the biosphere - Wastes + geological barrier + cavities + engineered structures + technical aspects must fulfill the corresponding requirements EU Criteria for Underground Disposal (1) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Council Decision 2003/33/EC establishing criteria and procedures for the acceptance of waste at landfills The site-specific assessment of risk requires the identification of: - The hazard (deposited wastes) - The receptors (biosphere and possibly groundwater) - The pathways by which substances from the wastes may reach the biosphere - The assessment of impact of substances that may reach the biosphere EU Criteria for Underground Disposal (2) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Council Decision 2003/33/EC establishing criteria and procedures for the acceptance of waste at landfills An integrated performance assessment analysis, including: - Geological assessment - Geomechanical assessment - Hydrogeological assessment - Geochemical assessment - Biosphere impact assessment - Assessment of the operational phase - Long-term assessment - Assessment of the impact of all the surface facilities at the site EU Criteria for Underground Disposal (3) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

EU Legislation on Mercury Storage Export Ban with Storage Obligation (2008) Landfill Directive (1999) Criteria & Procedures (2003) refers to giving details in affects on Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Development of specific criteria, tailor made to the characteristics of metallic mercury Some of existing criteria are likely to be unsuitable for a liquid substance like metallic mercury Development of specific provisions for the containment of the substance European Commission is about to launch a study that will deliver basic elements of such criteria Study will also look into state-of-the-art of solidification or other means of pre-treatment of metallic mercury before storage Additional criteria scheduled to be adopted in 2010 by means of a Commission decision (  available in March 2011, storage obligation) Further Legislative Steps (EU) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Why Salt Rock ? Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009 Unique rock properties, esp. plastic behaviour Enables complete inclusion of waste disposed off Former drift in a salt mine

Concept of Underground Disposal in Salt Rock Th. Brasser, GRS Disposal-Site Latin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009 Disposal-Site a. Layered Salt b. Salt Dome

PropertiesRock SaltClay / Claystone Crystalline (e.g. Granite) Thermal Conductivity+-+/- Hydraulic Conductivity+++/- Mechanical Strength+/- + Deformation Behavior++/-- Stability of Cavities+-+/- In-situ-Stress+-- Solubility-++ Sorption Capability-++/- Host Rock Properties - Comparison Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Host-Rock Specific Aspects Th. Brasser, GRS Rock salt: Complete and permanent isolation of waste from biosphere by total inclusion in host rock; host rock = essential barrier Plastic-clayey sediments: Barrier effect by geosphere and technical resp. geotechnical measures Crytalline rocks / consolidated sediments (fractured): System of technical barriers essential for enclosure of waste Latin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Waste content Waste form Canister Backfill Sealing Host rock Overburden Technical Barriers Geological Barriers Waste Isolation Barrier System (1) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Shaft sealing Drift sealing Borehole sealing Backfill Waste & Canister Overburden Host rock Waste Isolation Barrier System (2) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Repository Host rock Overburden Biosphere Well Underground Disposal System & Scenario Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Experiences since 1972 (Herfa-Neurode in operation) Host rock = rock salt Exclusive usage of still existing or abandoned mines Broad spectrum of hazardous wastes Operated commercially (‚polluter pays‘) Operated cost covering and profitable Underground Disposal Sites Experiences and Practice in Germany Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Technical Instructions on Waste (1991) – Underground disposal of hazardous waste, site specific proof of long- term safety is mandatory, waste specific requirements and exclusion criteria Landfill Ordinance – DepV (2002) – Instructions on the maintenance of long-term safety records within the context of site-related safety assessments for mines in salt rock (currently under revision) German Regulations on Underground Disposal Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

What is the behavior of metallic Mercury in contact with air and brines ? How much is the solubility of metallic Mercury influenced by impurities ? Does the conversion of metallic Mercury in Hg-sulfides hold advantages ?  significant in case of waste not isolated totally Important Questions Concerning Mercury Th. Brasser, GRS Scientific Knowledge on Mercury Which of the existing criteria are likely to be unsuitable for liquid Hg ? Which specific provisions for the containment are necessary and how does it effect the system ? Demand of Regulations Latin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

ANNEX Supplementing informations Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Regulation (EC) No 1102/2008 on banning of exports and safe storage of metallic mercury Mercury releases are recognized as a global threat Necessity to reduce the risk of exposure to mercury for humans and the environment The export of metallic mercury, … from the Community should be banned in order to significantly reduce the global mercury supply The safe storage within the Community of this mercury should be ensured The safety assessment required for underground storage (Decision 2003/33/EC) should be complemented by specific requirements and should also be made applicable to non-underground storage Preamble to 1102/2008 (1) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Regulation (EC) No 1102/2008 on banning of exports and safe storage of metallic mercury The storage conditions in a salt mine or in deep underground, hard rock formations, …, should notably meet the principles of protection of groundwater against mercury, prevention of vapor emissions of mercury, impermeability to gas and liquids of the surroundings and - in case of permanent storage - of firmly encapsulating the wastes at the end of the mines' deformation process The above-ground storage conditions should notably meet the principles of reversibility of storage, protection of mercury against meteoric water, impermeability towards soils and prevention of vapor emissions of mercury The above-ground storage of metallic mercury should be considered as a temporary solution Preamble to 1102/2008 (2) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Regulation (EC) No 1102/2008 on banning of exports and safe storage of metallic mercury (Art.1-1) Export of metallic mercury prohibited from 15 March 2011 (Art.1-3) Mixing of metallic mercury prohibited from 15 March 2011 (Art.2) Metallic mercury (no longer used / gained from operations) considered as waste and to be disposed of from 15 March 2011 Actual EU Regulation on Mercury (1) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Regulation (EC) No 1102/2008 on banning of exports and safe storage of metallic mercury (Art.3) Metallic mercury (as waste) to be stored in salt mines or in deep underground, hard rock formations (providing equivalent level of safety) (Art.8) By 1 January 2010 examination of - Need for extending the export ban to other mercury compounds - Need for import ban - Consideration of research on safe disposal options Actual EU Regulation on Mercury (2) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Annex 2: Instructions on the maintenance of long-term safety records General: Objective = complete and permanent sealing of waste from biosphere No impairment of the biosphere – proof by long-term safety record Salt rock in adequate spread and thickness = barrier rock Further geological barriers = additional protection (not compulsory) Penetrations of geological barrier (e.g. shafts) must be sealed (acc. to latest state of the art) German Ordinance on Landfills (1) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Annex 2: Instructions on the maintenance of long-term safety records Long-term safety: Based on - Safety Concept - Record of Geotechnical Stability - Safety Record for the Operational Phase Comprises entire system: ‚Waste - Underground Mine - Rock Body‘ Due regard for scheduled and non-scheduled incidents (scenarios) Proof of complete enclosure dispenses from model calculations on pollutant disseminations in the overburden German Ordinance on Landfills (2) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Annex 2: Instructions on the maintenance of long-term safety records Required Basic Informations: Geological conditions Informations about the drifts Hydrogeological conditions Emplacement of waste German Ordinance on Landfills (3) Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

PropertiesRock SaltClay / Claystone Crystalline (e.g. Granite) Thermal Conductivityhighlowmedium Hydraulic Conductivitynearly impermeablevery low - low very low (without joints) - permeable (jointed) Mechanical Strengthmediumlow - mediumhigh Deformation Behaviorviscous (creep)plastic - brittlebrittle Stability of Cavitiesself-stabilitytimbering necessary high (without joints) - low (intensively jointed) In-situ-Stresslithostatic isotropicanisotropic Solubilityhighvery low Sorption Capabilityvery lowvery highmedium - high Host Rock Properties - Comparison (Detail) Th. Brasser, GRS Source: BGR Latin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Metallic Hg is stable under the conditions of repositories in salt formations The high vapor pressure of metallic Hg poses high demands on the handling and ventilation Contact with brines: Solubility of Hg(0) is low, but higher Hg concentrations must be expected due to impurities with higher solubilities Conversion into Hg-sulfides is feasible. The benefit is dependant on the form and mass of impurities Specific waste acceptance criteria need to be determined Containment is important Conclusions on Mercury Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Regulation (EC) No 1102/2008 of the European Parliament and of the Council of 22 October 2008 on the banning of exports of metallic mercury and certain mercury compounds and mixtures and the safe storage of metallic mercury - lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2008:304:0075:0079:EN: PDF Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste - lex.europa.eu/smartapi/cgi/sga_doc?smartapi!celexapi!prod!CELEXnumdoc &lg=EN&numdoc=31999L0031&model=guichett 2003/33/EC: Council Decision of 19 December 2002 establishing criteria and procedures for the acceptance of waste at landfills pursuant to Article 16 of and Annex II to Directive 1999/31/EC - lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2003:011:0027:0049:EN: PDF Citations (1) - EU Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009

Technical Instructions on Waste (TA Abfall) - (in German) Act for Promoting Closed Substance Cycle Waste Management and Ensuring Environmentally Compatible Waste Disposal - Ordinance on Landfills and Long-Term Storage Facilities (Landfill Ordinance – DepV) - Annex 2: Instructions on the maintenance of long-term safety records within the context of site-related safety assessments for mines in salt rock - Contact: Dr. Thomas Brasser Gesellschaft fuer Anlagen- und Reaktorsicherheit (GRS) mbH Theodor-Heuss-Strasse Braunschweig, Germany Phone: , Fax: , Citations (2) - DE Th. Brasser, GRSLatin America Mercury Storage Project Inception Workshop - Montevideo, Uruguay, April 22-23, 2009