IRAQ Waste Management
Hazardous Waste Management
IRAQ Waste Management
Hazardous Waste
This category of waste needs special attention. Dangerous substances will affect directly health and safety of population and all sorts of living bodies, both animal and vegetal. Improper or mismanagement of hazardous waste will on a medium or long term basis lead to irreversible impacts.
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Hazardous Waste
Efficient treatments must be given to Hazardous waste, to prevent
dissemination of hazardous substances in the environment.
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Why raise hazardous waste management standards?
To reduce risks of inadequate controls on hazardous wastes including: • Health impacts for those living near uncontrolled dumps, and for waste workers • Environmental damage from dumped waste eg groundwater pollution, contaminated land • Operational problems at waste treatment facilities where incoming wastes are not controlled • Trend to „export‟ waste to other regions or countries if proper facilities not available
For economic reasons
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History and status
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Evolution of hazardous waste management
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Evolution of hazardous waste management
- The last century has seen countries around the world starting managing increasing quantities of hazardous waste produced, individually or in cooperation with other countries - Hazardous Waste management systems are mandated by specific legislation - Certainly, if systems are to be effective, well written and thorough legislation must be implemented in support of all phases of national waste management
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Vital components Institutional arrangements
)
LEGISLATION
FACILITIES
ENFORCEMENT
SUPPORT SERVICES
Stakeholders
Source: David C Wilson 1993
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Elements for control
WASTE GENERATOR
DEFINITION OR CLASSIFICATION OF WASTE
1 2 5 5
*
TRANSPORTATION
FACILITIES
Source: David C Wilson 1999
Regulatory Tools for Control
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Elements of legislation Generator
Responsibilities Controls
Recycling
Transport
Storage
Treatment
Disposal
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The context: All countries generate hazardous waste
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Developed world lessons • Hazardous waste management and movements need to be controlled • Legislative and enforcement measures must be developed but risks increase that waste will go to less controlled parts of the world • Public communication is important
• Waste minimisation should be addressed at an early stage - waste minimisation reduces the size (and hence cost) of treatment facilities needed
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World lesson: Guiding principles
• Self-sufficiency Principle • Proximity Principle
• Least Transboundary Movement Principle • Polluter Pays Principle • Principle of Sovereignty
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Regulatory approaches
First questions IRAQ Waste Management
First questions
Regulation: • For what purpose? • Of what? • Of whom?
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Why regulate? • for environmental safety • for market stability in disposal • to raise revenue • for social/political policy • as treaty obligation
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Whom regulate?
Regulations impacts on: • waste generators • waste operators • waste transporters • Waste dealers
Enabling regulations necessitates: • government agency
• inspectorates
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Components of legislation : Definitions
A clear legal definition is a crucial part of legislation Need definitions of: • waste materials • hazards posed • waste operations disposal recovery recycling • waste facilities: storage, treatment and disposal No single international definition of what constitutes hazardous waste
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Components of legislation : Responsibilities
Legislation must clearly set out the responsibilities placed on the different parties involved in generating and handling hazardous wastes, and overseeing the practices
• waste generators - large industry and small scale industries • operators of waste handling and treatment facilities • government agencies - to enforce controls
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Components of legislation : Controls
• emissions and discharge limits • transport controls • constructions standards • restrictions on the location of facilities • operating standards • reduction targets
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Regulation of waste facilities Facilities include: • storage depots • treatment plants • transfer stations • disposal • recycling facilities facilities Requirements might include: • planning permits • site specific factors
• waste management licence • design & construction standards • operating conditions, including: • acceptable waste types • emission and discharge standards • self monitoring • reporting
• Inspection and enforcement
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Transboundary movement control
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The Problem • Movements of waste from industrialised to industrialising countries of hazardous wastes for „treatment‟ or „disposal‟ • Hazardous waste disposal cost in industrialised countries is high
• Regulations becoming stricter • Disposal costs in developing economies were low, few regulations, low standards • No legal framework to control „dumping‟
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The Solution
1987 - Preliminary guidelines (the Cairo Guidelines) for the environmentally sound management of hazardous wastes were adopted by UNEP 1989 - Adoption of the Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and their Disposal 1992 - Entry into force of the Basel Convention
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Objectives of the Basel Convention
To protect human health and the environment against adverse effects of hazardous wastes • Reduction of transboundary movements of hazardous wastes • Minimization of generation - quantity and degree of hazard
• Promotion of environmentally sound management of hazardous wastes
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Definition
Under the Basel Convention, hazardous wastes are: • Wastes that belong to any category listed in Annex I unless they do not possess any of the characteristics contained in Annex III Art. 1 (1) (a) • Wastes that belong to any category listed in Annex II re other wastes, Art. 1 (2)
• Wastes defined as hazardous by national legislation Art. 1 (1) (b) Annex VIII (and IX) further defines which wastes are (not) considered hazardous under the Convention
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Main elements of the Convention
Control regime for the transboundary movements of hazardous wastes
Environmentally Sound Management of hazardous wastes
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Control regime for transboundary movement of hazardous waste 1
Responsibility to notify
Prior written consent procedure
Re-import obligations
Prohibitions and restrictions
Definition and control of illegal traffic
Documentation and notification
Contract between exporter and disposer
Insurance/financial guarantees
International transport regulations
Environmentally sound management of wastes
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Control regime for transboundary movements of hazardous waste Prohibitions and restrictions
No movements to non-Parties (unless Art. 11)
No export to States with import prohibition
No export to States without systems of environmentally sound management
No export for disposal to the area of 60o South latitude (ie Antarctica)
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Protocol on liability and compensation
Objective: to provide for a comprehensive regime for liability as well as adequate and prompt compensation for damage resulting from the transboundary movements of hazardous wastes
Assigns responsibilities to all the actors taking part in a transboundary movement, with the obligation to compensate
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Protocol on liability and compensation
The scope: Covers each phase of a transboundary movement, including: - the point where the wastes are loaded onto the means of transport - the international transit - the final destination - the final disposal
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Protocol on liability and compensation What kind of damage is covered by the Protocol?
- loss of life or personal injury - loss of or damage to property - loss of income directly deriving from an economic interest deriving from the use of the environment - costs of reinstatement of the environment - costs of preventive measures
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Assistance to States
• Technical guidelines
• Regional Centerss
• Model national legislation
• Training and seminars
• Waste characterization • Manual to assist implementation
For the future: • Criteria for environmentally sound management of hazardous wastes • Improvement of existing technologies • Development of new technologies • Raising public awareness
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Hazardous waste Handling and storage
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Hazardous waste compatibility
Compatibility = the ability of two or more materials to exist in close association with each other without the formation of harmful chemical or physical reactions
Need compatibility between:
•
waste & container
•
wastes stored together
•
wastes stored close to each other
•
wastes & environment
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Storage site design criteria
Protection from climate
Good ventilation
Limit height of stacked containers
Eye wash station
Provide drainage system or elevate
Adsorbent material for spills
Re-packaging area
Comply with regulations
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Storage site design criteria
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Hazardous waste storage
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Storage site design criteria
Minimise risk of explosion or unplanned releases
Keep incompatible wastes separate
Not < 15m from site boundary (where possible)
Away from foot & vehicular traffic
.
• Impermeable base material • Leak and spill containment
Source: David C Wilson
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Marking and labelling
Source: U.S. DEPARTMENT OF TRANSPORTATION, Research & Special Programs Administration, 2000
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Labels All containers must be clearly marked with waste type and hazard Labels should be:
• • • • •
Made of good quality materials Durable Weather resistant Well located Recognisable and legible in day and night time • Give information about handling precautions and prohibitions • At least 100mm on each side
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Record keeping and inspection Inspection:
To ensure proper handling and storage
To check integrity of storage
Record keeping:
To provide a record of waste generation and movement
To inform a subsequent disposal option
To serve as “chain of custody” document
To comply with regulations
To ensure duty of care
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Laboratory
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Preliminary Acceptation Before accepting waste on the treatment plant : • Check the exact properties of the waste • Check the ability of the plant to receive the waste • Assess compliance with treatment and emissions • Establish the treatment procedure and resulting cost
• Help preparing the contract
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Reception Before trucks are unloaded : • Compare actual content of the delivery truck with samples pre-accepted • Gives the OK for unloading • Direct the truck to the right reception area depending on characteristics
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Reception control
SAMPLING
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General Key element of the plant operation • Daily operations ( acceptance, storage, treatment) • Monitoring of all operations, organize the correct sampling of all streams coming in or going out, preparation of annual reports for the administration • Insure compliance of emissions • Research and development for new capacities, new customers, develop recovery processes
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General Key equipments • pH meter • Spectrophotometer for “rapid” presence checking (metals, cyanides, phenols…) • X Fluorescence elements measurements • ICP • Gas Chromatography • TOC meter
• Calorific value analysis • Oven
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Reception Pre-treatment
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Reception Pre-treatment ADMINISTRATIVE RECEPTION
UNPACKING
Weighing
Interim Storage
Other destination
UNPAKING FOR DIRECT TREATMENT
TO TREATMENT
Basic acceptation scheme
IDENTIFICATION / SORTING
MATERIAL RECOVERY
LIQUID UNPACKING
STORAGES
SOLIDS / PASTEUSE UNPACKING
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Simplified orientation of treatment process Phisical charaacteristics
l
Organique / minéral ?
Minéral
Organics
Critères : pH, PCI faible
Calorific value
Recoverables ?
Yes
recoverable
No
yes
No Aqueux
High metal content , acid, soda,.. potential for « high tech » recovery : electrochemistry, resins, …)
pH, metals, TOC, phénol
High CV without contaminants (hydrocarbons), solvents without halogens,
No
yesi
CV, pH, métal content, % sédiment, biodegradability PCVCI, pH, métaux, % sédiment, PCB, halogènes…
Material Recovery
Minéral Physico-Chimical
simplified orientation scheme for liquid waste
Energy recovery
Biological treatment Evapo-incineration
Incineration
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Simplified orientation of treatment process Physical Characteristics
Solid
Organic / minéral ?
Minéral
Organic
Very low CV
CV
Recoverables ?
Recoverables ?
Yes
No
High metal content, silica,.. + compatibility with pre-treatment (washing, magnetic separation, cryogenic separation,…)
Leacheability, Mechanical resistance
Material Recovery
Landfilling directly or after stabilization
Simplified scheme for solids treatment
Yes i High plastic content (PEHD) + compatibility pre-treatment (washing)
Material or energy Recovery
No
Pre-treatment, Flash point odors, metals, halogens, ph
Pre-treatment + incinération
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Transit Pre-treatment Intermediate storage
Protected storage of incoming waste
Container pressing
Emptying of incoming containers Shredder in a separate building
Basic pre-treatment scheme
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Treatment
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Treatment
The purpose of the treatment is either to destroy the hazardousness of the waste or to recover molecules , chemicals or “products” All operations must comply with regulations and “standards” concerning emissions health and safety. The treatment processes must be adapted to the physico-chemical characteristics of the waste and the technical performances achievable by the different processes
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Treatment •
Physical
•
Chemical
•
Physical and chemical
•
Biological
•
Thermal :destructive, thermo-metallurgy, “pyrolysis”
Most treatments leave residues for disposal
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Physical Treatment
Manual separation - removes selected wastes by visual inspection
Sorting by categories
Neutralisation
Sedimentation Precipitation - removes from liquid phase, water treatment
Centrifuging - removes water content
Filtration
Solvent extraction
Adsorption
Soil purification
Sludge drying
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Shredding
1-Outlet 2-Choc Absorber d 3-hydraulic Motor 4-knifes 5-hoper 6-Tooth like guide
7-Frame
:shredder
(source SID)
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Shredding
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Physico-chemical treatment
Flocculation precipitation: aggregates fine constituents or chemicals in solution
Neutralization
Detoxification
Solvent extraction: uses immiscible solvent to dissolve organic material in aqueous solution
Solvent recycling
Desorption - separates volatile components from liquid by passing through gas stream
Ion exchange - exchange with dissolved ionic species through contact with resin
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Physico-chemical treatment Typical lay out
Chemical addition
Flocculation
Sedimentation
Source: Guyer, Howard H Industrial processes and waste stream management, Wiley
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Biological treatment
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Advantages of biological waste treatment
• Cost Effective for huge quantities of waste water, since the pollution is biodegradable • Tolerant to changes in waste composition these may result in a short period of inactivity, but do not halt the process
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Scope of treatment application • Wastewater treatment is the most widely used application of biological treatment e.g. for industries such as paper manufacture and recycling, food processing, tanneries and the pharmaceutical industry, and for landfill leachate Also: • In-situ bio-remediation of contaminated soil • Slurry-phase treatment • Land treatment • Co-composting
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In-situ bio-remediation
• Enables treatment without excavation and removal of contaminated material • An aerobic process • Enhances natural biodegradation • Influenced by hydro-geological factors
• Can reduce contamination to acceptable levels in relatively short time e.g. 1-2 years
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Thermal treatment
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Thermal treatment Thermal treatment of waste:
Incineration : destruction of hazardous molecules
allows energy recovery, materials recycling
Pyrolysis
Gasification allows recovery of useful materials
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Thermal treatment Thermal treatment of waste: legal obligations:
•
Combustion temperature ( 850 or 1100°C)
•
Post combustion chamber with residence time 2 seconds at above temperature
•
Energy recovery
•
Gas cleaning
•
Emission limit values
•
Residues to be treated according to local legislation
•
Gas treatment residues “hazardous”
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Incineration Reception pit
solids To shredder
Packed Waste Transfer pumps
Liquids Bulk
Dedicated storages for bulk and unpacked waste
Direct injection for reacting waste
Typical feeding arrangement
Rotary Kiln
Dedicated Injectors
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Incineration
To the heat recovery boiler
Solids feed hopper
Refractory Lining
Post combustion burner Main Burner
Dedicated liquid injectors
Rotary Kiln and post combustion courtesy SarpIndustries
Bottom ash water cooled extraction
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Fluidized bed combustion
Bubbling fluidised bed Circulating fluidised bed Source: Guyer, Howard H Industrial processes and waste stream management, Wiley
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Example of flue gas cleaning technology
Source: Indaver
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Incineration Treated gas to stack Reactor Inlet Gas
Reagent after treatment
Gas Cleaning: Bag filter with chemical injection
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Incineration Gas outlet to stack Packing
Gas Inlet
atomization Soda injection
Water injection
De-concentrating drain
Drain
Drops collector
Acid column Gas Cleaning WET PROCESS Courtesy Sarp Industries
Basic column
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Incineration Water Turbine
Inlet gas 300°C / 400°C
Soda water Atomiser
Treated gas 200 to 250°C Gas from boiler 300 to 400°C
Exit gas 200 / 250°C
ashes
Ashes
Gas cooling with or without chemical injection courtesy Sarp inustries
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Emissions Emissions from incineration Continuous monitoring for:
HCl, CO, dust, SO2, HF, TOC, Nox, O2 Monthly measurement for: 9 heavy metals Twice a year (soon to be semi continuous): PCDD/PCDF ALSO monitored: wastewater and solid residues
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Landfilling
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Types of landfills
It is now quite everywhere recognized three different types of landfills • Hazardous waste ( class1) to receive hazardous waste • Municipal waste (non hazardous) the recent “landfill” ban restricting acceptance to “pre-treated waste” • Inert landfills mainly for “stable” construction and demolition waste
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Components of a “State of the art landfill design”
Well chosen, properly designed site
Bottom liner - to protect soil and groundwater
Leachate collection and treatment - to prevent contamination of groundwater
Landfill gas collection and flaring or energy generation ( if appropriate )
Provisions for Final cover, after care
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Components of a “State of the art landfill design”
Compaction (fire prevention, odour prevention)
Waste control at entrance
Daily coverage of the “active part of the landfill
Maintenance of drains, flare..
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Landfilling
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Landfilling
Waste Geotextile Draining layer
Collecting pipe Geotextile (protection) Geomembrane (PEHD) Water tight material
Standard design
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Landfilling
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Stabilisation and solidification of hazardous wastes
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Stabilisation and Solidification Converts waste into insoluble rock-like materials
Stabilisation - treats waste to minimise migration
Solidification - uses cement-based process
Encapsulation - encloses waste within casing or layer of inert substance
Recommended for inorganic hazardous wastes
A pre-treatment step prior to landfill disposal
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Solidification
Types of binders used: • Cement-based • Portland cement, cement kiln dust
• Lime/limestone/quicklime • Lime/fly ash, lime kiln dust • Lime/ other natural and artificial pozzolana based systems
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Wastes typically treated by Stabilisation / Solidification
• Air pollution control residues • Metal sludge wastes • Dredging sludge • Filter press cake • Tannery wastes • Contaminated soils • Lagoon sludge Plus other PREDOMINANTLY inorganic wastes - all are likely to contain some organics
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Treated waste specification • 28 day strength from any 1 day of production will not be less than 700 kPa. No individual sample to have strength less than 350kPa • Permeability at 28 days less than 1x10-7 m/s
• No supernatant after S/S waste standing 24 hours • Leaching properties: defined by legislation typically includes concentration limits in the leacate on pH, TOC, Total cyanide, total phenol, ammonia Heavy metals (Zn, Hg, Cr), total metal limit and total organic or organo-metallic pesticides