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Hazardous Waste
Management:Overview
Waste Management
Definition of Hazardous Waste
A solid or liquid wastes which because of its
quantity, concentration or physical, chemical
or infectious characteristics, may:
1. Cause increase in mortality or severe
illness,
2. Pose a substantial potential hazard to
human health or environment, when
improperly treated, stored, transported or
disposed
Definition of Hazardous Waste
Characteristics of Hazardous Waste
Ignitability (flash point >60oC)
Corrosivity (pH <2 or >12.5)
Reactivity (unstable materials or
material that cause violent reaction
when in contact with another material)
Toxicity (Leachate Test)
Nature of Hazardous Waste Management
Hazardous Waste field is interdisciplinary
Requires professionals with diverse
background working together to solve the
complex issue of hazardous waste
management
Environmental Impact and Risk Assessment
Treatment, Storage and Disposal
Waste Minimization, Recycling and Reduction
Management and Cost
Past Disposal Practice
 Soil Spreading
 Pits/Ponds/Lagoons
 Sanitary Landfills
 Drum Storage Areas
 Underground Storage
Tanks
 Midnight Dumping
 Uncontrolled Incineration
Waste Generation Rates By Industry

Chemical Products

Electronics

Petroleum & Coal Products

Primary Metals

Transportation Equipment

All Other Industries
Typical Hazardous Waste Types

25%

70%

Inorganic Liquid

Organic Liquid

Sludge
Why the need for HWTC?
Protect public health and the environment
Reduce impact of hazardous waste on
surface water and ground water
Provide the means to enhance:
Waste minimization at various industrial
operations, and
Waste recycling
Objectives of HWTC
1. Avoid and minimize environmental
and health pollution risks associated
with the generation, storage,
collection, transport, handling,
recycling, and disposal of hazardous
wastes
2. Ensure the movement and disposal
practice of hazardous wastes is
always controlled and environmentally
safe, flexible, and economically
sustainable for local conditions
Technical Feasibility
 Can the wastes be
separated at source to
avoid co-mingling and
analyzed before shipping
to the facility?
 What characteristics are
the separated wastes
likely to have?
 What quantity of the
wastes should be
considered as
wastewater?
Market and Economic Feasibility
 Is there a local market for the products of
recycling?
 Is there an international market for the
products of recycling?
 What scale of disposal fees is to be expected
for each category of waste?
 What rate of return would a Private Sector
investor expect for providing and operating a
Hazardous Waste Recycling Facility?
Materials Disposed in HWTC
Liquid organic waste
Oily sludge and residue
from petroleum industry
Spent oil and catalysts
Contaminated soil
Liquid heavy metals
Acidic and basic solids
and liquids
Liquid ammonia and
urea
Off-Specification
products
Estimation of Hazardous Wastes
Quantities??
Hazardous Waste Inventory:
Estimate the total waste stream quantity
Deduct the portion of these wastes that are
being recycled or processed at the generator’s
own facilities
Deduct any co-mingled wastes that are
impossible to separate in a cost-effective
manner
Estimation of Hazardous Wastes
Quantities (cont.)
Deduct waste quantities being disposed
without permit
Prepare an integrated treatment system for
the remainder with add-on facilities for growth
and improvement in anticipation of reducing
any unauthorized disposal
Propose action as necessary for treatment
and disposal facilities for the co-mingled and
improperly disposed wastes
HWTC Design Approach
1. A flexible modular design will provide the

Project Authority with the opportunity to
attract private sector investments and
will minimize capital cost in the long-term

–
–
–

Focus initially on the major polluters
Provide HWTC to treat part of the waste
Initiate and monitor
HWTC Design Approach (cont.)
2.

Due to the nature of the hazardous
wastes and their potential to change
characteristics and properties over
time, the HWTC needs to be properly
designed and equipped with facilities
that are capable of safely meeting the
needs of handling and disposing the
hazardous waste
Description of the HWTC
Liquid Waste Treatment
Facility
Land Farming Facility
Class I Hazardous
Waste Landfill
Class II Regular Waste
Landfill
Solidification and
Stabilization Unit
Incinerator
Important Points
 The priorities of hazardous Waste
management in decreasing order of
importance:
 Minimization/Prevention
 Treatment/Remediation
 Disposal
Liquid Waste Treatment Facility
Separate tank farm
storage for acidic and
basic waste as well as
drum storage area
Neutralization reactors
Sludge storage reactor
Standby neutralization
reactors to be used
during maintenance
Activated Carbon Column
Liquid Phase Adsorption Treatment System
Industrial Wastewater Treatment
Chemical Oxidation
In general the objective of chemical oxidation
is to detoxify waste by adding an oxidizing
agent to chemically transform waste
components
Chemical oxidation is a well established
technology that is capable of destroying a
wide range of organic molecules, including
chlorinated VOCs, phenols and inorganics
such as cyanide
Process Description
Chemical Oxidation is based on the delivery
of oxidants to contaminated media in order to
either destroy the contaminants by
converting them to innocuous compounds
commonly found in nature
The oxidants applied are typically hydrogen
peroxide (H2O2), potassium permanganate
(KMnO2), ozone (O3)
Process Description
Land Farming Facility
Land farming is the
preferred technology for
the treatment of oily
sludge and hydrocarbon
contaminated soils,
which constitute the
main component of
hazardous organic
wastes to be treated at
the HWTC
Base Liner Detail
WASTE
FILTER SOIL
GEOMEMBRANE
SUBSOIL

GRAVEL W/
PERFORATED PIPE
Land Farming Facility (cont’d)
Compounds to be treated at the land
Farming Facility:
 Volatile Organic Compounds (VOCs):
benzene, ethylbenzene, toluene, xylenes;
 Semi-Volatile Organic Compounds
(SVOCs): phenols, creosol, naphthalene,
phennathrene, benzo(a)pyrene, flourrene,
anthracene, chrysene; and
 Heavy Metals: chromium, cyanides, lead
and nickel
Aerobic Biodegradation
HYDROCARBON
PRODUCT

ORGANIC
POLLUTANT + MICROORGANISMS + NUTRIENTS + OXYGEN

CARBON DIOXIDE + WATER + BIOMASS
Microorganisms
• Regarding the natural breakdown of
hydrocarbon products, bacteria are the
main microorganism in the
bioremediation process
• Bacteria act as decomposers and utilize
hydrocarbon product as a source of
energy
Nutrients
 Nutrients enhance the biodegradation
process by supplying essential
elements required for optimal microbial
growth and maintenance
 Nutrients can be supplied in the field
through the application of manure or
fertilizer
 C:N:P = (100-300):10:1
Requirements for Biodegradation
 Proper nutrient balance
 Temperature
15 – 30 oC
 Acceptable pH
5.5 - 8.5
 Moisture content of 60% - 80% of field
capacity
 Oxygen concentration
 Presence of toxic heavy metals
REMOVAL EFFICIENCY (%)

AVERAGE NAPTHALENE

Naphthalene Removal Efficiency
100

80

60

40

20

0
0

100

200

300

400

TIME (hours)
Non-Acclimatized

Acclimatized

Control
Bio-piles
Soil Composting
Hazardous Waste Landfill







Class I Landfill
should include:
Double liner
Leachate collection
Leachate detection
system
Surface water
control mechanism
Impermeable cover
system
Hazardous Waste Landfill
Hazardous Waste Landfill
Liner System
Regular Waste Landfill






Class II Landfill
should include:
Single liner
Leachate collection
Surface water
control mechanism
Impermeable cover
system
Regular Waste Landfill
Solidification and Stabilization
The solidification and
stabilization facility
(SSF) will be designed
to inactivate and
immobilize
contaminants prior to
landfilling
Solidification and Stabilization
The following waste will be
processed by SSF plant
prior to landfilling:
 Mercury contaminated solid
wastes;
 Solid miscellaneous
inorganic sulfur;
 Semi-solid hazardous
waste; and
 Sludge from Liquid
Hazardous Waste
Treatment
Solidification and Stabilization
S/S reduces the mobility of hazardous
substances and contaminants in the
environment through both physical and
chemical means
S/S seeks to trap or immobilize
contaminants within their host medium (i.e.
soil, sand and binding agent)
Leachability testing is usually performed to
measure the immobilization of contaminants
from the stabilized matrix
Solidification and Stabilization
• General binding and
sorbent materials:
Cement
 Pozzolans
 Lime
 Silicates
 Organically Modified
Clays

High Temperature Thermal
Desorption
HTTD is a technology in
which wastes are heated
to 320 to 560 oC
Produce final
contaminant
concentration level
below 5 mg/kg
Incinerator
Structure to house the
furnace
Tipping floor where the
Hazardous Waste is
disposed
Storage pit to store the
Hazardous Waste
delivered
Charging system
Furnace
Air pollution control
Ash handling system
HWTC Control Philosophy
Provide a Supervisory Control and Data
Acquisition (SCADA). The SCADA
system will provide two levels of control:
Level 1 control operates equipment
directly and bypasses all interlocks.
Level 2 is initiated directly by computer
programming. Level 2 controls,
operates equipment and processes
remotely.
Typical Control System
Environmental Monitoring
 Air

Quality
 Groundwater
Quality
 Surface Water
Quality
 Dust and Noise
Environmental Monitoring
 Selection

of the
parameters of
concern
 Sampling
methodology
 Quality
assurance
/quality control
plan
Project Approach
Task 1: Review of Existing Data
Task 2: Discussion with Project
Authority
Task 3: Development and Finalization of
HWTF Design
Task 4: Prepare Final Design Drawings
and Design Basis Memorandum
Project Approach (cont.)
Task 5: Design of Liquid Hazardous
Waste Treatment Facility
Task 6: Class I and II Landfills Design
Task 7: Land Framing Facility Design
Task 8: Solidification and Stabilization
Facility Design
Project Approach (cont.)
Task 9: HWTC Construction
Task 10: Facility Commissioning and
Operation
Task 11: Facility Handing Over
Conclusions
1. Key to proper design of HWTC is
system flexibility to adjust to
hazardous waste quantities and
properties over time
2. Enforcement of environmental law
and regulations
Leachate Treatment Using
Wetlands
Department of Environmental Engineering
Beijing University of Chemical Technology
December 2003
Wetlands
 Wetland is define as land having the water
table at, near or above the land surface or
which is saturated for long enough period to
promote wetland or aquatic processes as
indicated by hydric soils, hydrophilic
vegetation, and various kinds of biological
activity which are adapted to the wet
environment.
Treatment Mechanisms in a
Wetland System
Type of Engineered wetlands
Constructed wetland systems are classified
into
two general types:
 Horizontal Flow System (HFS)



Surface Flow (SF)
Sub-surface Flow (SSF)

 Vertical Flow System (VFS).
Horizontal Flow Wetland System
Surface Flow Wetland System
Subsurface Flow Wetland System
Field Monitoring
Field Monitoring
MW-4

Pump

Pond #2

Monitoring wells

MW-2

DC
BA

MW-1
MW-3
MW-5

Peat Filter

FSW-1 SW-1
SW-2

FSW-2

Pond #1
SW-4

Manhole

W-1

SW-3

FSW-3
W-2
Field Monitoring
18
16
14
12
10
8
6
4
2
97-6

97-5

97-4

97-3

97-2

97-1

96-8

96-7

96-6

96-5

96-3

96-2

0
96-1

Concentration (mg/L)

Boron Concentration

Monitoring Event

Pond

MW-A

MW-B

MW-C

MW-D

SW
Conclusions
 Boron adsorption was directly related to organic
content
 Peat filter was effective in treating landfill
leachate
 The adsorption capacity of the peat can be
significantly enhanced by lime addition

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Hazardous waste-management

  • 2. Definition of Hazardous Waste A solid or liquid wastes which because of its quantity, concentration or physical, chemical or infectious characteristics, may: 1. Cause increase in mortality or severe illness, 2. Pose a substantial potential hazard to human health or environment, when improperly treated, stored, transported or disposed
  • 4. Characteristics of Hazardous Waste Ignitability (flash point >60oC) Corrosivity (pH <2 or >12.5) Reactivity (unstable materials or material that cause violent reaction when in contact with another material) Toxicity (Leachate Test)
  • 5. Nature of Hazardous Waste Management Hazardous Waste field is interdisciplinary Requires professionals with diverse background working together to solve the complex issue of hazardous waste management Environmental Impact and Risk Assessment Treatment, Storage and Disposal Waste Minimization, Recycling and Reduction Management and Cost
  • 6. Past Disposal Practice  Soil Spreading  Pits/Ponds/Lagoons  Sanitary Landfills  Drum Storage Areas  Underground Storage Tanks  Midnight Dumping  Uncontrolled Incineration
  • 7. Waste Generation Rates By Industry Chemical Products Electronics Petroleum & Coal Products Primary Metals Transportation Equipment All Other Industries
  • 8. Typical Hazardous Waste Types 25% 70% Inorganic Liquid Organic Liquid Sludge
  • 9. Why the need for HWTC? Protect public health and the environment Reduce impact of hazardous waste on surface water and ground water Provide the means to enhance: Waste minimization at various industrial operations, and Waste recycling
  • 10. Objectives of HWTC 1. Avoid and minimize environmental and health pollution risks associated with the generation, storage, collection, transport, handling, recycling, and disposal of hazardous wastes 2. Ensure the movement and disposal practice of hazardous wastes is always controlled and environmentally safe, flexible, and economically sustainable for local conditions
  • 11. Technical Feasibility  Can the wastes be separated at source to avoid co-mingling and analyzed before shipping to the facility?  What characteristics are the separated wastes likely to have?  What quantity of the wastes should be considered as wastewater?
  • 12. Market and Economic Feasibility  Is there a local market for the products of recycling?  Is there an international market for the products of recycling?  What scale of disposal fees is to be expected for each category of waste?  What rate of return would a Private Sector investor expect for providing and operating a Hazardous Waste Recycling Facility?
  • 13. Materials Disposed in HWTC Liquid organic waste Oily sludge and residue from petroleum industry Spent oil and catalysts Contaminated soil Liquid heavy metals Acidic and basic solids and liquids Liquid ammonia and urea Off-Specification products
  • 14. Estimation of Hazardous Wastes Quantities?? Hazardous Waste Inventory: Estimate the total waste stream quantity Deduct the portion of these wastes that are being recycled or processed at the generator’s own facilities Deduct any co-mingled wastes that are impossible to separate in a cost-effective manner
  • 15. Estimation of Hazardous Wastes Quantities (cont.) Deduct waste quantities being disposed without permit Prepare an integrated treatment system for the remainder with add-on facilities for growth and improvement in anticipation of reducing any unauthorized disposal Propose action as necessary for treatment and disposal facilities for the co-mingled and improperly disposed wastes
  • 16. HWTC Design Approach 1. A flexible modular design will provide the Project Authority with the opportunity to attract private sector investments and will minimize capital cost in the long-term – – – Focus initially on the major polluters Provide HWTC to treat part of the waste Initiate and monitor
  • 17. HWTC Design Approach (cont.) 2. Due to the nature of the hazardous wastes and their potential to change characteristics and properties over time, the HWTC needs to be properly designed and equipped with facilities that are capable of safely meeting the needs of handling and disposing the hazardous waste
  • 18. Description of the HWTC Liquid Waste Treatment Facility Land Farming Facility Class I Hazardous Waste Landfill Class II Regular Waste Landfill Solidification and Stabilization Unit Incinerator
  • 19.
  • 20. Important Points  The priorities of hazardous Waste management in decreasing order of importance:  Minimization/Prevention  Treatment/Remediation  Disposal
  • 21. Liquid Waste Treatment Facility Separate tank farm storage for acidic and basic waste as well as drum storage area Neutralization reactors Sludge storage reactor Standby neutralization reactors to be used during maintenance
  • 22.
  • 24. Liquid Phase Adsorption Treatment System
  • 26. Chemical Oxidation In general the objective of chemical oxidation is to detoxify waste by adding an oxidizing agent to chemically transform waste components Chemical oxidation is a well established technology that is capable of destroying a wide range of organic molecules, including chlorinated VOCs, phenols and inorganics such as cyanide
  • 27. Process Description Chemical Oxidation is based on the delivery of oxidants to contaminated media in order to either destroy the contaminants by converting them to innocuous compounds commonly found in nature The oxidants applied are typically hydrogen peroxide (H2O2), potassium permanganate (KMnO2), ozone (O3)
  • 29. Land Farming Facility Land farming is the preferred technology for the treatment of oily sludge and hydrocarbon contaminated soils, which constitute the main component of hazardous organic wastes to be treated at the HWTC
  • 30. Base Liner Detail WASTE FILTER SOIL GEOMEMBRANE SUBSOIL GRAVEL W/ PERFORATED PIPE
  • 31. Land Farming Facility (cont’d) Compounds to be treated at the land Farming Facility:  Volatile Organic Compounds (VOCs): benzene, ethylbenzene, toluene, xylenes;  Semi-Volatile Organic Compounds (SVOCs): phenols, creosol, naphthalene, phennathrene, benzo(a)pyrene, flourrene, anthracene, chrysene; and  Heavy Metals: chromium, cyanides, lead and nickel
  • 32.
  • 33. Aerobic Biodegradation HYDROCARBON PRODUCT ORGANIC POLLUTANT + MICROORGANISMS + NUTRIENTS + OXYGEN CARBON DIOXIDE + WATER + BIOMASS
  • 34. Microorganisms • Regarding the natural breakdown of hydrocarbon products, bacteria are the main microorganism in the bioremediation process • Bacteria act as decomposers and utilize hydrocarbon product as a source of energy
  • 35. Nutrients  Nutrients enhance the biodegradation process by supplying essential elements required for optimal microbial growth and maintenance  Nutrients can be supplied in the field through the application of manure or fertilizer  C:N:P = (100-300):10:1
  • 36. Requirements for Biodegradation  Proper nutrient balance  Temperature 15 – 30 oC  Acceptable pH 5.5 - 8.5  Moisture content of 60% - 80% of field capacity  Oxygen concentration  Presence of toxic heavy metals
  • 37. REMOVAL EFFICIENCY (%) AVERAGE NAPTHALENE Naphthalene Removal Efficiency 100 80 60 40 20 0 0 100 200 300 400 TIME (hours) Non-Acclimatized Acclimatized Control
  • 40. Hazardous Waste Landfill      Class I Landfill should include: Double liner Leachate collection Leachate detection system Surface water control mechanism Impermeable cover system
  • 41.
  • 44. Regular Waste Landfill     Class II Landfill should include: Single liner Leachate collection Surface water control mechanism Impermeable cover system
  • 46. Solidification and Stabilization The solidification and stabilization facility (SSF) will be designed to inactivate and immobilize contaminants prior to landfilling
  • 47. Solidification and Stabilization The following waste will be processed by SSF plant prior to landfilling:  Mercury contaminated solid wastes;  Solid miscellaneous inorganic sulfur;  Semi-solid hazardous waste; and  Sludge from Liquid Hazardous Waste Treatment
  • 48. Solidification and Stabilization S/S reduces the mobility of hazardous substances and contaminants in the environment through both physical and chemical means S/S seeks to trap or immobilize contaminants within their host medium (i.e. soil, sand and binding agent) Leachability testing is usually performed to measure the immobilization of contaminants from the stabilized matrix
  • 49. Solidification and Stabilization • General binding and sorbent materials: Cement  Pozzolans  Lime  Silicates  Organically Modified Clays 
  • 50.
  • 51. High Temperature Thermal Desorption HTTD is a technology in which wastes are heated to 320 to 560 oC Produce final contaminant concentration level below 5 mg/kg
  • 52. Incinerator Structure to house the furnace Tipping floor where the Hazardous Waste is disposed Storage pit to store the Hazardous Waste delivered Charging system Furnace Air pollution control Ash handling system
  • 53. HWTC Control Philosophy Provide a Supervisory Control and Data Acquisition (SCADA). The SCADA system will provide two levels of control: Level 1 control operates equipment directly and bypasses all interlocks. Level 2 is initiated directly by computer programming. Level 2 controls, operates equipment and processes remotely.
  • 55. Environmental Monitoring  Air Quality  Groundwater Quality  Surface Water Quality  Dust and Noise
  • 56. Environmental Monitoring  Selection of the parameters of concern  Sampling methodology  Quality assurance /quality control plan
  • 57. Project Approach Task 1: Review of Existing Data Task 2: Discussion with Project Authority Task 3: Development and Finalization of HWTF Design Task 4: Prepare Final Design Drawings and Design Basis Memorandum
  • 58. Project Approach (cont.) Task 5: Design of Liquid Hazardous Waste Treatment Facility Task 6: Class I and II Landfills Design Task 7: Land Framing Facility Design Task 8: Solidification and Stabilization Facility Design
  • 59. Project Approach (cont.) Task 9: HWTC Construction Task 10: Facility Commissioning and Operation Task 11: Facility Handing Over
  • 60. Conclusions 1. Key to proper design of HWTC is system flexibility to adjust to hazardous waste quantities and properties over time 2. Enforcement of environmental law and regulations
  • 61. Leachate Treatment Using Wetlands Department of Environmental Engineering Beijing University of Chemical Technology December 2003
  • 62. Wetlands  Wetland is define as land having the water table at, near or above the land surface or which is saturated for long enough period to promote wetland or aquatic processes as indicated by hydric soils, hydrophilic vegetation, and various kinds of biological activity which are adapted to the wet environment.
  • 63. Treatment Mechanisms in a Wetland System
  • 64. Type of Engineered wetlands Constructed wetland systems are classified into two general types:  Horizontal Flow System (HFS)   Surface Flow (SF) Sub-surface Flow (SSF)  Vertical Flow System (VFS).
  • 69. Field Monitoring MW-4 Pump Pond #2 Monitoring wells MW-2 DC BA MW-1 MW-3 MW-5 Peat Filter FSW-1 SW-1 SW-2 FSW-2 Pond #1 SW-4 Manhole W-1 SW-3 FSW-3 W-2
  • 71. Conclusions  Boron adsorption was directly related to organic content  Peat filter was effective in treating landfill leachate  The adsorption capacity of the peat can be significantly enhanced by lime addition

Editor's Notes

  1. &lt;number&gt;
  2. &lt;number&gt; The naphthalene removal efficiency increased steadily in both the columns containing acclimatized MOs and those containing non-acclimatized MOs, to eventually attain 100% and 95%, respectively. The acclimatized columns attained their maximum naphthalene removal efficiency in 33% less time than the non-acclimatized columns. In the control column, which was biologically inhibited using sodium azide, the naphthalene removal was due to adsorption to the sand. The control column’s adsorption capacity never was exhausted which is why the naphthalene removal remained constant at 47% for the duration of this study. .
  3. &lt;number&gt;
  4. &lt;number&gt;
  5. &lt;number&gt;
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