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This Project is funded by the European Union
SWIM and Horizon 2020 Support Mechanism
Working for a Sustainable Mediterranean, Caring for our Future
Presented by:
Dr. Ahmed Gaber, Professor of Chemical Engineering, Cairo University
and Chairman, Chemonics Egypt Consulting
Leachate Management Training Program
June 25th-29th, 2018, Beirut, Lebanon
Landfill Basics
Lecture
1
Outline
1.Introduction
2.Principles
3.Processes
4.Design considerations
5.Emerging technologies in landfills
Introduction: Hierarchy of integrated waste management
• Even with the implementation of waste
reduction, recycling, material recovery and
transformation technologies, disposal of solid
waste in a landfill remains an important
component of solid waste management
strategies.
• It is not always economical to recycle/recover
all waste under all conditions.
• Safe and reliable long-term disposal of solid
waste is one of the most essential components
of solid waste management.
• The landfill is the most economical form of solid
waste disposal that minimises adverse
environmental effects, associated risks and
inconveniences; allowing the waste to
decompose under controlled conditions.
Introduction: Service Provision Plans (SPPs) and the need for
final disposal
Transfer station
SPP1
Cleaning, collection
and transportation of
MSW
Transfer of collected,
mixed MSW in small
vehicles to large
vehicles
Final disposal –
Sanitary landfill
Final disposal of
mixed MSW in
sanitary landfill
Alternative:
Bioreactor landfill
G3
Collection of
mixed MSW
Street
cleaning
G1
Service Provision Plan (SPP) 1: Collection of mixed MSW  G1 (Transfer Station)  G3 (Sanitary Landfill
for the disposal of mixed MSW)
Introduction: Service Provision Plans (SPPs) and the need for
final disposal
Transfer station
SPP
2
Cleaning, collection
and transportation
of MSW
Transfer of
collected, mixed
MSW in small
vehicles to large
vehicles
Centralised
treatment facility
Collection
of mixed
MSW
Street
cleaning
G1
Service Provision Plan (SPP) 2: Collection of mixed MSW  G1 (Transfer Station)  G2 (Centralised Treatment Facility) 
G3 (Sanitary Landfill for the final disposal of the rejects fraction of the MSW)
Final disposal –
Sanitary landfill
Final disposal of
reject fraction of
MSW in sanitary
landfill
Sorting of
recyclables and
processing the
Organic Fraction
(OF) of MSW
Output depends
on the employed
technology and
may include;
recyclables,
compost, Refuse
Derived Fuel
(RDF), electrical
energy…etc.
G2 G3
Introduction: Service Provision Plans (SPPs) and the need for
final disposal
Dirty Material
Recycling
Facility (MRF)
SPP
3
Cleaning,
collection and
transportation of
MSW
Sorting of mixed
MSW and transfer
of OFMSW in
large vehicles
Centralised
treatment facility
Collection
of mixed
MSW
Street
cleaning
G1
Service Provision Plan (SPP) 3: Collection of mixed MSW  G1 (Dirty MRF)  G2 (Centralised Treatment Facility)  G3
(Sanitary Landfill for the final disposal of the rejects fraction of the MSW)
Final disposal –
Sanitary landfill
Final disposal of
reject fraction of
MSW in sanitary
landfill
Processing of
OFMSW
Output depends
on the employed
technology and
may include;
compost,
electrical
energy…etc.
G2 G3
Recyclables and
RDF separated
Introduction: Service Provision Plans (SPPs) and the need for
final disposal
Clean Material
Recycling Facility
(MRF)
SPP
4
Cleaning, collection
and transportation
of MSW
Processing of
source-separated
MSW and transfer
of OFMSW in
large vehicles
Centralised
treatment facility
Collection
of source-
separated
MSW
Street
cleaning G1
Service Provision Plan (SPP) 4: Collection of source-separated MSW  G1 (Clean MRF)  G2 (Centralised Treatment
Facility)  G3 (Sanitary Landfill for the final disposal of the rejects fraction of the MSW)
Final disposal –
Sanitary landfill
Final disposal of
reject fraction of
MSW in sanitary
landfill
Processing of
OFMSW
Output depends
on the employed
technology and
may include;
compost,
electrical
energy…etc.
G2 G3
Recyclables and
RDF separated
Introduction: Landfills and their classification
• A landfill is any form of waste disposal land, ranging from an uncontrolled rubbish
dump to a full containment site engineered with high standards to protect the
environment.
• Landfilling practices in developing countries differ from that of developed
countries; which, follow advanced landfilling practices such as sanitary landfills as
opposed to open dumping practices.
Cross section of a typical engineered landfill
Source: http://waste.snu.ac.kr
Two main types of landfills
• Sanitary landfills: For Municipal
Solid Waste (MSW) i.e. waste
from residential and commercial
areas.
• Secure landfills: For hazardous
waste.
Introduction: Evolution of landfills (definitions adapted from
the World Bank technical paper No. 26)
• Open dumping: Uncontrolled dump causing hazards to humans and
the environment
• Unsanitary landfill/controlled landfill: Dump with covering of waste
• Fence
• Daily cover
• Control of insects pests and scavenging…etc.
• First generation sanitary landfill/Engineered landfill: Controlled landfill
and engineered measures to limit impact
• Leachate liner and treatment
• Landfill fuel gas (LFG) collection and reuse…etc.
• Second generation sanitary landfill/Sanitary landfill: Engineered
landfill in addition to landfill gas extraction, groundwater monitoring,
water treatment facility and highly trained staff…etc. This may also
include:
• Multi-barrier concept for leachate and gas management
• After care and environmental monitoring…etc.
Source: Haubrichs, Sanitary landfill Design, waste and water
environmental engineering
Introduction: Landfills and their minimum requirements
• Sanitary landfill implementation, therefore, requires careful site selection,
preparation and management.
• There are four minimum requirements to be considered:
• Full or partial hydrological isolation (usually using liners)
• Formal engineering preparation
• Permanent control
• Planned waste emplacement and covering
• These issues are discussed by addressing
• Landfill principles
• Landfill process
Landfill Principles (source: Municipal solid waste management, unit 4: waste disposal)
Purpose: To bury or alter the chemical composition of the waste so as not to pose
any threat to public and environmental health.
Landfills are NOT homogeneous and are made up of cells. Cells are discrete volumes
of waste, kept isolated from adjacent waste cells using suitable barriers.
Landfilling most commonly relies on containment rather than treatment (for control)
of waste. If executed appropriately, it can be safer and cheaper than incineration.
An environmentally sound landfill comprises appropriate liners for the protection of
groundwater, run-off controls, leachate collection and treatment, monitoring wells
and appropriate final cover design (Phelps, 1995)
Landfill Principles
Source: Haubrichs, Sanitary landfill Design, waste and water environmental engineering
Landfill Principles: life cycle and costs
• Planning phase: Involves preliminary hydro-geological and geo-technical site
investigations a s a basis for actual design.
• Construction phase: Involves earthworks, road and facility construction and
preparation (liners and drains) of the fill area.
• Operation phase (5-20 years): This phase has a high intensity of traffic work at
the front of the fill, operation of environmental installations and completion of
finished sections.
• Completed phase (20-100 years): Involves the termination of the actual filling to
the time when the environmental installations no longer need to be operated. At
this time, emissions may have decreased to a level that need no further
treatment and can be directly discharged to the surrounding.
• Final storage phase: The landfill is integrated into the surroundings for other
purposes and no longer needs special attention.
Source: https://foresternetwork.com/wp-content/uploads/ms1611_26.jpg
Landfill Processes: Site selection process
• Appropriate location e.g. far from airports, flood plains
• Land availability
• Soil conditions and topography
• Geological conditions e.g. unstable areas, seismic activity
• Hydrologic conditions e.g. surface and ground water
• Climatic conditions e.g. rainfall and wind
• Environmental and ecological conditions e.g. endangered species..etc.
• Minimise haul distance
• Large enough site to accommodate the SW needs of the service area
• Compatible with local SWM programmes
• Minimise adverse effects on surrounding area and property value
• Minimise impacts on traffic flow
• Minimise potential for fire, spill, accidents e.g. outside flood zones
• Public input and concerns
• Potential use after closur
Site selection considerations include
Site selection process and consideration require a working plan or a series of plans outlining
the development and descriptions of site location, operation, engineering and site
restorations.
Landfill Processes: Settling process
Primary consolidation
•Short-term
deformation stage
with substantial
settling.
•It results from the
weight of the waste
layers and the
movement of
trucks, bulldozers
and mechanical
compactors.
•Aerobic degradation
processes occur
during this stage.
Secondary
compression
•Rate of settling is
much lower than
primary
consolidation.
•Settling occurs due
to compression
which can't be
enhanced.
Decomposition
•During this process,
organic material is
converted into gas
and leachate.
•The settling rate
increases compared
to secondary
compression and
continues until the
OFMSW has
degraded.
•The settling rate
gradually decreases
with the passage of
time.
Source: Municipal solid waste management, unit 4: waste disposal
Landfill Processes: Microbial degradation process
Source: Municipal solid waste management, unit 4: waste disposal)
This process is the most important biological process occurring in a landfill. These
processes induce changes in the chemical and physical environment within the
waste body which determine the quality of leachate and both the quality and
quantity of landfill gas (LG).
Assuming that landfills mostly receive organic wastes, microbial processes will
dominate the stabilisation of the waste and will thus govern LG generation and
leachate composition.
After waste disposal in the landfill, the predominant part of the waste degradation
becomes anaerobic, where, bacterial will degrade the solid organic carbon eventually
to produce carbon dioxide and methane. This process can be enhanced using:
• Adding partly composted waste
• Recirculating leachate
Design considerations
• The design should be acceptable to the public (hide/keep distance).
• The shape of the area has major impacts on the design of the landfill.
• Appropriate gas collection systems and leachate management systems should be
employed
• Limit negative environmental impacts by limiting the transport of pollutants by
constructing liners and waste covers.
• Additional facilities may be included such as fences, rainwater drainage ditches,
leachate and LFG treatment facilities, groundwater monitoring wells…etc.
Design considerations Landfills = Containment
Passive Barrier
+
Active Barrier
Passive Barrier: Protects the bottom/side layer (in contact with the soil)
• Geological barrier formed with natural material that is found in-situ or brought in
• Material with low permeability
• Must not be sollicitated
Active Barrier: Protects the top layer (in contact with the waste)
• Synthetic membrane (liners)
• Drainage and leachate collection systems
Design considerations: Liner systems
Two categories of liners:
• Natural liners: These refer to compacted clay or shale, bitumen or soil sealants.
• They are generally less permeable, resistant to chemical attach and have good
sorption properties.
• They generally do not act as true containment barriers, since leachate can
migrate through them.
• Synthetic (geo-membrane) liners: these are typically made up of high or medium
density polyethylene.
• Are generally less permeable, easy to install, relatively strong and have good
deformation characteristics.
• They can expand and shrink depending on temperature and age.
Note:
• Both types of liners are often combined to enhance the overall efficiency of the
containment system.
• Some leachate collection systems include impermeable liner and granular material.
Source: Seoul National University; Design, operation and management of solid waste
landfills; Laboratory of waste management and resource recirculation
Design considerations: Standards for liner systems
Bottom lining systems for municipal waste landfills from different regulations and
recommendations
Source: Seoul National University Laboratory of waste management and resource recirculation;
Design, operation and management of solid waste landfills
Design considerations: Landfill gas and Leachate
• LFG and leachate resulting from the degradation of the OFMSW are considered a
major hazard associated with landfills and can contaminate soils, water and air.
• Factors that affect the production of LFG and leachate include:
• Nature of the waste i.e. the content of biodegradable material.
• Moisture content since most microorganisms require a minimum of 12%
moisture for growth.
• pH: The bacteria producing methane gas will only grow around a neutral pH.
• Particle size and density which affect the surface area and volume which in
turn affect moisture absorption and rate of degradation.
• Temperature which affects the .optimum operating conditions for different
types of bacteria
• Note: In the past, it was believed that in a closed landfill, leachate was only generated by
the percolation of precipitation. However, leachate will be generated irrespective of
whether there is precipitation or not.
Design considerations: Landfill Gas Collection System
• Methane gas is emitted to the atmosphere from natural wet lands, rice paddy
fields, gas and oil wells, landfills…etc.
• Among the emission sources, landfills are the most dominant anthropogenic
source.
Gas GWP Lifetime
(years)
CO2 1 Variable
CH4 21 12
N2O 310 120
PCFs 140 6,300
HCFs 6,500 9,200
SF6 23,900 3,200
Source: Seoul National University Laboratory of waste management and resource recirculation;
Design, operation and management of solid waste landfills
Design considerations: Landfill Gas Extraction Wells
Source: Seoul National University Laboratory of waste management and resource recirculation;
Design, operation and management of solid waste landfills
Equilateral triangular distribution for vertical gas extraction wells
Design considerations: Leachate Collection System
Source: Seoul National University Laboratory of waste management and resource recirculation;
Design, operation and management of solid waste landfills
Design considerations: Leachate Collection System
Source: Seoul National University Laboratory of waste management and resource recirculation;
Design, operation and management of solid waste landfills
Source: CH2MHILL; Understanding leachate generation
and management
Design considerations: Covers
Source: Seoul National University Laboratory of waste management and resource recirculation;
Design, operation and management of solid waste landfills
Two types of covers:
Protects against:
• The scattering of waste
• Odours
• Insect pests and animals
• Rainwater drainage
• Accessibility
• Aesthetic
Daily/intermediate cover
Protects against:
• Rainwater drainage
• Gaseous contaminants
• Vegetation (erosion,
aesthetics)
• LFG control (fire)
• Insect pests and animals
Final cover
*Intermediate cover needs better accessibility of heavy equipment
Design considerations: Covers
*Intermediate cover needs better accessibility of heavy equipment
Source: Seoul National University Laboratory of waste management and resource recirculation;
Design, operation and management of solid waste landfills
Emerging Technologies in Landfills: Selected cases (Source: Seoul National
University; Design, operation and management of solid waste landfills; Laboratory of waste management and resource recirculation)
Landfill classifications
Emerging Technologies in Landfills: Selected cases
Bio-reactor landfill (anaerobic bioreactor)
Source: Don Davies Stantec Consulting Ltd.; 2010; Sustainable landfill biocell
Emerging Technologies in Landfills: Selected cases
Bio-reactor landfill (forced aeration)
Source: Don Davies Stantec Consulting Ltd.; 2010; Sustainable landfill biocell
Emerging Technologies in Landfills: Selected cases (Source: Seoul National
University; Design, operation and management of solid waste landfills; Laboratory of waste management and resource recirculation)
Closed landfill – steel cover
Emerging Technologies in Landfills: Selected cases (Source: Seoul National
University; Design, operation and management of solid waste landfills; Laboratory of waste management and resource recirculation)
Offshore disposal sites

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EU-Funded Landfill Basics Lecture

  • 1. This Project is funded by the European Union SWIM and Horizon 2020 Support Mechanism Working for a Sustainable Mediterranean, Caring for our Future Presented by: Dr. Ahmed Gaber, Professor of Chemical Engineering, Cairo University and Chairman, Chemonics Egypt Consulting Leachate Management Training Program June 25th-29th, 2018, Beirut, Lebanon Landfill Basics Lecture 1
  • 3. Introduction: Hierarchy of integrated waste management • Even with the implementation of waste reduction, recycling, material recovery and transformation technologies, disposal of solid waste in a landfill remains an important component of solid waste management strategies. • It is not always economical to recycle/recover all waste under all conditions. • Safe and reliable long-term disposal of solid waste is one of the most essential components of solid waste management. • The landfill is the most economical form of solid waste disposal that minimises adverse environmental effects, associated risks and inconveniences; allowing the waste to decompose under controlled conditions.
  • 4. Introduction: Service Provision Plans (SPPs) and the need for final disposal Transfer station SPP1 Cleaning, collection and transportation of MSW Transfer of collected, mixed MSW in small vehicles to large vehicles Final disposal – Sanitary landfill Final disposal of mixed MSW in sanitary landfill Alternative: Bioreactor landfill G3 Collection of mixed MSW Street cleaning G1 Service Provision Plan (SPP) 1: Collection of mixed MSW  G1 (Transfer Station)  G3 (Sanitary Landfill for the disposal of mixed MSW)
  • 5. Introduction: Service Provision Plans (SPPs) and the need for final disposal Transfer station SPP 2 Cleaning, collection and transportation of MSW Transfer of collected, mixed MSW in small vehicles to large vehicles Centralised treatment facility Collection of mixed MSW Street cleaning G1 Service Provision Plan (SPP) 2: Collection of mixed MSW  G1 (Transfer Station)  G2 (Centralised Treatment Facility)  G3 (Sanitary Landfill for the final disposal of the rejects fraction of the MSW) Final disposal – Sanitary landfill Final disposal of reject fraction of MSW in sanitary landfill Sorting of recyclables and processing the Organic Fraction (OF) of MSW Output depends on the employed technology and may include; recyclables, compost, Refuse Derived Fuel (RDF), electrical energy…etc. G2 G3
  • 6. Introduction: Service Provision Plans (SPPs) and the need for final disposal Dirty Material Recycling Facility (MRF) SPP 3 Cleaning, collection and transportation of MSW Sorting of mixed MSW and transfer of OFMSW in large vehicles Centralised treatment facility Collection of mixed MSW Street cleaning G1 Service Provision Plan (SPP) 3: Collection of mixed MSW  G1 (Dirty MRF)  G2 (Centralised Treatment Facility)  G3 (Sanitary Landfill for the final disposal of the rejects fraction of the MSW) Final disposal – Sanitary landfill Final disposal of reject fraction of MSW in sanitary landfill Processing of OFMSW Output depends on the employed technology and may include; compost, electrical energy…etc. G2 G3 Recyclables and RDF separated
  • 7. Introduction: Service Provision Plans (SPPs) and the need for final disposal Clean Material Recycling Facility (MRF) SPP 4 Cleaning, collection and transportation of MSW Processing of source-separated MSW and transfer of OFMSW in large vehicles Centralised treatment facility Collection of source- separated MSW Street cleaning G1 Service Provision Plan (SPP) 4: Collection of source-separated MSW  G1 (Clean MRF)  G2 (Centralised Treatment Facility)  G3 (Sanitary Landfill for the final disposal of the rejects fraction of the MSW) Final disposal – Sanitary landfill Final disposal of reject fraction of MSW in sanitary landfill Processing of OFMSW Output depends on the employed technology and may include; compost, electrical energy…etc. G2 G3 Recyclables and RDF separated
  • 8. Introduction: Landfills and their classification • A landfill is any form of waste disposal land, ranging from an uncontrolled rubbish dump to a full containment site engineered with high standards to protect the environment. • Landfilling practices in developing countries differ from that of developed countries; which, follow advanced landfilling practices such as sanitary landfills as opposed to open dumping practices. Cross section of a typical engineered landfill Source: http://waste.snu.ac.kr Two main types of landfills • Sanitary landfills: For Municipal Solid Waste (MSW) i.e. waste from residential and commercial areas. • Secure landfills: For hazardous waste.
  • 9. Introduction: Evolution of landfills (definitions adapted from the World Bank technical paper No. 26) • Open dumping: Uncontrolled dump causing hazards to humans and the environment • Unsanitary landfill/controlled landfill: Dump with covering of waste • Fence • Daily cover • Control of insects pests and scavenging…etc. • First generation sanitary landfill/Engineered landfill: Controlled landfill and engineered measures to limit impact • Leachate liner and treatment • Landfill fuel gas (LFG) collection and reuse…etc. • Second generation sanitary landfill/Sanitary landfill: Engineered landfill in addition to landfill gas extraction, groundwater monitoring, water treatment facility and highly trained staff…etc. This may also include: • Multi-barrier concept for leachate and gas management • After care and environmental monitoring…etc. Source: Haubrichs, Sanitary landfill Design, waste and water environmental engineering
  • 10. Introduction: Landfills and their minimum requirements • Sanitary landfill implementation, therefore, requires careful site selection, preparation and management. • There are four minimum requirements to be considered: • Full or partial hydrological isolation (usually using liners) • Formal engineering preparation • Permanent control • Planned waste emplacement and covering • These issues are discussed by addressing • Landfill principles • Landfill process
  • 11. Landfill Principles (source: Municipal solid waste management, unit 4: waste disposal) Purpose: To bury or alter the chemical composition of the waste so as not to pose any threat to public and environmental health. Landfills are NOT homogeneous and are made up of cells. Cells are discrete volumes of waste, kept isolated from adjacent waste cells using suitable barriers. Landfilling most commonly relies on containment rather than treatment (for control) of waste. If executed appropriately, it can be safer and cheaper than incineration. An environmentally sound landfill comprises appropriate liners for the protection of groundwater, run-off controls, leachate collection and treatment, monitoring wells and appropriate final cover design (Phelps, 1995)
  • 12. Landfill Principles Source: Haubrichs, Sanitary landfill Design, waste and water environmental engineering
  • 13. Landfill Principles: life cycle and costs • Planning phase: Involves preliminary hydro-geological and geo-technical site investigations a s a basis for actual design. • Construction phase: Involves earthworks, road and facility construction and preparation (liners and drains) of the fill area. • Operation phase (5-20 years): This phase has a high intensity of traffic work at the front of the fill, operation of environmental installations and completion of finished sections. • Completed phase (20-100 years): Involves the termination of the actual filling to the time when the environmental installations no longer need to be operated. At this time, emissions may have decreased to a level that need no further treatment and can be directly discharged to the surrounding. • Final storage phase: The landfill is integrated into the surroundings for other purposes and no longer needs special attention. Source: https://foresternetwork.com/wp-content/uploads/ms1611_26.jpg
  • 14. Landfill Processes: Site selection process • Appropriate location e.g. far from airports, flood plains • Land availability • Soil conditions and topography • Geological conditions e.g. unstable areas, seismic activity • Hydrologic conditions e.g. surface and ground water • Climatic conditions e.g. rainfall and wind • Environmental and ecological conditions e.g. endangered species..etc. • Minimise haul distance • Large enough site to accommodate the SW needs of the service area • Compatible with local SWM programmes • Minimise adverse effects on surrounding area and property value • Minimise impacts on traffic flow • Minimise potential for fire, spill, accidents e.g. outside flood zones • Public input and concerns • Potential use after closur Site selection considerations include Site selection process and consideration require a working plan or a series of plans outlining the development and descriptions of site location, operation, engineering and site restorations.
  • 15. Landfill Processes: Settling process Primary consolidation •Short-term deformation stage with substantial settling. •It results from the weight of the waste layers and the movement of trucks, bulldozers and mechanical compactors. •Aerobic degradation processes occur during this stage. Secondary compression •Rate of settling is much lower than primary consolidation. •Settling occurs due to compression which can't be enhanced. Decomposition •During this process, organic material is converted into gas and leachate. •The settling rate increases compared to secondary compression and continues until the OFMSW has degraded. •The settling rate gradually decreases with the passage of time. Source: Municipal solid waste management, unit 4: waste disposal
  • 16. Landfill Processes: Microbial degradation process Source: Municipal solid waste management, unit 4: waste disposal) This process is the most important biological process occurring in a landfill. These processes induce changes in the chemical and physical environment within the waste body which determine the quality of leachate and both the quality and quantity of landfill gas (LG). Assuming that landfills mostly receive organic wastes, microbial processes will dominate the stabilisation of the waste and will thus govern LG generation and leachate composition. After waste disposal in the landfill, the predominant part of the waste degradation becomes anaerobic, where, bacterial will degrade the solid organic carbon eventually to produce carbon dioxide and methane. This process can be enhanced using: • Adding partly composted waste • Recirculating leachate
  • 17. Design considerations • The design should be acceptable to the public (hide/keep distance). • The shape of the area has major impacts on the design of the landfill. • Appropriate gas collection systems and leachate management systems should be employed • Limit negative environmental impacts by limiting the transport of pollutants by constructing liners and waste covers. • Additional facilities may be included such as fences, rainwater drainage ditches, leachate and LFG treatment facilities, groundwater monitoring wells…etc.
  • 18. Design considerations Landfills = Containment Passive Barrier + Active Barrier Passive Barrier: Protects the bottom/side layer (in contact with the soil) • Geological barrier formed with natural material that is found in-situ or brought in • Material with low permeability • Must not be sollicitated Active Barrier: Protects the top layer (in contact with the waste) • Synthetic membrane (liners) • Drainage and leachate collection systems
  • 19. Design considerations: Liner systems Two categories of liners: • Natural liners: These refer to compacted clay or shale, bitumen or soil sealants. • They are generally less permeable, resistant to chemical attach and have good sorption properties. • They generally do not act as true containment barriers, since leachate can migrate through them. • Synthetic (geo-membrane) liners: these are typically made up of high or medium density polyethylene. • Are generally less permeable, easy to install, relatively strong and have good deformation characteristics. • They can expand and shrink depending on temperature and age. Note: • Both types of liners are often combined to enhance the overall efficiency of the containment system. • Some leachate collection systems include impermeable liner and granular material. Source: Seoul National University; Design, operation and management of solid waste landfills; Laboratory of waste management and resource recirculation
  • 20. Design considerations: Standards for liner systems Bottom lining systems for municipal waste landfills from different regulations and recommendations Source: Seoul National University Laboratory of waste management and resource recirculation; Design, operation and management of solid waste landfills
  • 21. Design considerations: Landfill gas and Leachate • LFG and leachate resulting from the degradation of the OFMSW are considered a major hazard associated with landfills and can contaminate soils, water and air. • Factors that affect the production of LFG and leachate include: • Nature of the waste i.e. the content of biodegradable material. • Moisture content since most microorganisms require a minimum of 12% moisture for growth. • pH: The bacteria producing methane gas will only grow around a neutral pH. • Particle size and density which affect the surface area and volume which in turn affect moisture absorption and rate of degradation. • Temperature which affects the .optimum operating conditions for different types of bacteria • Note: In the past, it was believed that in a closed landfill, leachate was only generated by the percolation of precipitation. However, leachate will be generated irrespective of whether there is precipitation or not.
  • 22. Design considerations: Landfill Gas Collection System • Methane gas is emitted to the atmosphere from natural wet lands, rice paddy fields, gas and oil wells, landfills…etc. • Among the emission sources, landfills are the most dominant anthropogenic source. Gas GWP Lifetime (years) CO2 1 Variable CH4 21 12 N2O 310 120 PCFs 140 6,300 HCFs 6,500 9,200 SF6 23,900 3,200 Source: Seoul National University Laboratory of waste management and resource recirculation; Design, operation and management of solid waste landfills
  • 23. Design considerations: Landfill Gas Extraction Wells Source: Seoul National University Laboratory of waste management and resource recirculation; Design, operation and management of solid waste landfills Equilateral triangular distribution for vertical gas extraction wells
  • 24. Design considerations: Leachate Collection System Source: Seoul National University Laboratory of waste management and resource recirculation; Design, operation and management of solid waste landfills
  • 25. Design considerations: Leachate Collection System Source: Seoul National University Laboratory of waste management and resource recirculation; Design, operation and management of solid waste landfills Source: CH2MHILL; Understanding leachate generation and management
  • 26. Design considerations: Covers Source: Seoul National University Laboratory of waste management and resource recirculation; Design, operation and management of solid waste landfills Two types of covers: Protects against: • The scattering of waste • Odours • Insect pests and animals • Rainwater drainage • Accessibility • Aesthetic Daily/intermediate cover Protects against: • Rainwater drainage • Gaseous contaminants • Vegetation (erosion, aesthetics) • LFG control (fire) • Insect pests and animals Final cover *Intermediate cover needs better accessibility of heavy equipment
  • 27. Design considerations: Covers *Intermediate cover needs better accessibility of heavy equipment Source: Seoul National University Laboratory of waste management and resource recirculation; Design, operation and management of solid waste landfills
  • 28. Emerging Technologies in Landfills: Selected cases (Source: Seoul National University; Design, operation and management of solid waste landfills; Laboratory of waste management and resource recirculation) Landfill classifications
  • 29. Emerging Technologies in Landfills: Selected cases Bio-reactor landfill (anaerobic bioreactor) Source: Don Davies Stantec Consulting Ltd.; 2010; Sustainable landfill biocell
  • 30. Emerging Technologies in Landfills: Selected cases Bio-reactor landfill (forced aeration) Source: Don Davies Stantec Consulting Ltd.; 2010; Sustainable landfill biocell
  • 31. Emerging Technologies in Landfills: Selected cases (Source: Seoul National University; Design, operation and management of solid waste landfills; Laboratory of waste management and resource recirculation) Closed landfill – steel cover
  • 32. Emerging Technologies in Landfills: Selected cases (Source: Seoul National University; Design, operation and management of solid waste landfills; Laboratory of waste management and resource recirculation) Offshore disposal sites