Concepts for the environmentally sound management of surplus mercury Sven Hagemann GRS.

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Presentation transcript:

Concepts for the environmentally sound management of surplus mercury Sven Hagemann GRS

National/ regional mercury supply What is Surplus Mercury? 2 Need to manage surplus mercury  storage  disposal National / regional demand for products & proceses National/ regional surplus Elemental Hg & Hg compounds like calomel

3 How Much Surplus Mercury Will Have to be Managed in South/ South East and East Asia? (Concorde 2009) Main assumptions: VCM production: decrease of consumption after 2015 Zinc smelting: strong increase of Hg recovery between now an 2030 Alternative scenario: 7,500 t (reduced supply for ASM) Regional surplus 5,500 t ( ) Possibly national surpluses ? ?  Management options for surplus mercury?  AIT/RRCAP study (2010)

Important Sources of Surplus mercury 4 Export Non –ferrous metal production (zinc, gold) Decommis- sioning of mercury cells (chlor alkali) End of life products Contaminated sites Oil & gas industry Elemental mercury Mercury compounds Mercury contaminated material Mercury containing products Primary waste type

What is Environmentally Sound Manage of Wastes? Taking all practicable steps to ensure that hazardous wastes or other wastes are managed in a manner which will  protect human health and  the environment against the adverse effects which may result from such wastes (Basel Convention, Article 2.8) 5

Polluter-pays principle: producer to bear all storage/ disposal cost Practised Surplus Mercury Management Options 6 Elemental mercury Mercury compounds like calomel (mercurous chloride) Stabilization Removal from the market (storage) Aboveground storage in warehouses (up to 40 years or more) Removal from the biosphere (disposal) Permanent storage in underground mines Possible interim step (up to a few years) Temporary storage Surplus mercury

Management Options for Mercury Wastes 7 Waste contaminated with mercury (e.g. soil, debris) Waste containing mercury (e.g. end of life products) Stabilization Permanent storage in underground mines Specially engineered landfill Temporary storage Use Extraction Stabilization ?

8 Surplus mercury Elemental Hg Specially engineered landfills Deep well injection Underground storage (final disposal) of elem. Hg Stabilized mercury waste (e.g. mercury sulphide)/ Removal from the market Mercury compounds e.g. calomel Underground storage (final disposal) of Hg compounds Range of Removal Strategies –in Use and Under Investigation Removal from the biosphere (final disposal) Aboveground warehouse storage (not time-limited) Underground storage (final disposal) of stabil. Hg Temporary storage of elemental Hg Temporary storage of Hg compounds Temporary storage of stabilized Hg Waste containing or contaminated with Hg

9 Potential elements of environmentally sound management of surplus mercury Safe Disposal Effective CollectionEarly Stabilization Remove mercury from the market Obligation to deliver/ store surplus mercury Temporarily store elemental mercury Avoid transport and storage of elemental mercury Stabilize mercury Temporarily store stabilized mercury and mercury compounds Isolate mercury from the biosphere Underground storage Specially engineered landfills? Deep injection?

Brief overview on storage and disposal concepts 10 Aboveground storage in warehouses (up to 40 years or more) Permanent storage in underground mines Specially engineered landfill Deep well injection Temporary storage

Long-term Management and Storage of Elemental Mercury in Warehouses 11 Concept Placement of containers in aboveground warehouses Technical safety measures: flooring, containers, fire protection Organizational safety measures Monitoring, inspection, security Implementation and options USA: several facilities in use Global options: locations with distance to sensible areas (population, water basins) and low risk of environmental hazards

Underground Storage (Disposal) of Stabilized Mercury and Mercury Compounds Concept: Placement of containers in an underground mine Sealing of mine and permanent isolation of mercury from the biosphere: >10,000 years Passive long-term safety through multibarrier system (geological + technical barriers) Implementation and options Some European countries Global options: Existing underground mines (salt, metal ore, other) with suitable geology 12

Specially Engineered Landfill I Complete isolation of wastes from the biosphere through combination of a geological barrier and a bottom liner system during the operational phase combination of a geological barrier and a top liner during the closure and post-closure phase For a defined time period, a landfill site can be engineered to be environmentally safe 13

Specially Engineered Landfill II Complete isolation from the biosphere by: Before operation: Protection of groundwater: geological system + bottom liner After closure: top liner Operation and management Landfill gas control Drainage and leachate control Waste acceptance criteria Environmental Monitoring 14

Specially Engineered Landfill III Final resort, only if other efforts to avoid or eliminate Hg contamination failed May be operated for mono-disposal: only one waste stream Co-disposal: many wastestreams including municipal waste (more complex, not recommended) -Only after stabilization/ solidification -Only if waste acceptance criteria are met (e.g. leaching limit) -In some countries not allowed for waste with high Hg content 15

Specially engineered landfills III Opportunities and challenges 16 Opportunities Well established concept, already present in many developing countries Relatively low costs Challenges Safety may only predicted for some tens of years Mercury sulfide not thermodynamically stable in above ground landfills (oxidation, formation of elemental mercury) Present landfills may become future source of releases

Deep Well Injection of waste I 17 Injection of liquid or liquified waste into deep geological formations Formations shall have no connection to higher groundwater levels > y. Use of existing wells depleted oil/ gas deposits Salt caverns Newly drilled wells

Deep Well Injection of waste II 18 Typically used in the oil/gas industry, e.g. for Hg contaminated sludges Examples: Thailand, Croatia In few countries used to dispose waste from other sources (chemical industy, CO 2 )

Deep Well Injection of waste III Opportunities and challenges 19 Opportunities Well known concept in the oil & gas industry for waste from this sector Challenges Typically not used for waste from other sources Requires careful well construction and sealing to avoid contamination of higher groundwater levels during or after operation No control after injection, retrieval technically impossible

Temporary storage 20 Temporary holding of waste before waste is collected stored elsewhere disposed Interim/ preliminary storage: by the owner/ producer Storage: by waste management company (private/ state) before waste is submitted for treatment, final disposal, recycling or recovery