SlideShare a Scribd company logo
CHAPTER 3
Physical Treatment Technologies
Ravi Damera and Alok Bhandari
REMEDIATION TECHNOLOGIES FOR SOILS
AND GROUNDWATER
American Society of Civil Engineers
1801 Alexander Bell Drive
Reston, Virginia, 20191-4400
Copyright © 2007 by the American Society of Civil Engineers. All Rights Reserved.
ISBN 13: 978-0-7844-0894-0 ISBN 10: 0-7844-0894-7
Manufactured in the United States of America.
INTRODUCTION
Physical treatment technologies take advantage of physicochemical
properties of the contaminant and the affected media to remediate soil
and groundwater.
PHYSICOCHEMICAL PROPERTIES
in this context include:
for CONTAMINANT
 density,
 solubility,
 viscosity,
 volatility
for MEDIA (that can be exploited during site remediation)
 physical state (solid, liquid or gas),
 its bulk density,
 moisture content,
 permeability,
 porosity,
 particle size distribution
 ability to conduct heat or electric current
Most conventional physical treatment technologies:
 free product recovery,
 pump and treat,
 soil vapor extraction,
 air sparging,
 groundwater circulation wells,
 multi-phase extraction,
 induced fracturing,
 soil heating
1. FREE PRODUCT RECOVERY
Free product, also known as free phase
contamination, refers to concentrated contaminants
that are not miscible with groundwater and
therefore form a separate layer.
Free phase product recovery is often applied in
combination with other treatment processes such
as soil vapour extraction (SVE), dual phase
extraction, ex-situ treatments and bioremediation. It
is rarely undertaken alone except in the least
sensitive environmental settings. Depending on
physical properties, product can be recovered as a
liquid or vapour and the recovery could be
enhanced by steam injection or surfactant flushing.
1. FREE PRODUCT RECOVERY
Light non-aqueous phase liquids (LNAPL):
these contaminants are less dense than
water and float on the water table surface.
Dense non-aqueous phase liquid (DNAPL): these
contaminants are denser than water and sink to the
bottom of water table and rest on impermeable
surfaces such as clays and bedrock.
There are two types of free product:
Contaminants
Free product recovery is applicable to all chemicals,
common free product contaminants are:
•Light non-aqueous Phase liquids (LNAPL)
•Diesel range organics (DRO)
•Petroleum range organics (PRO)
•Kerosene
•Dense non-aqueous phase liquid (DNAPL)
•Creosote
•Chlorinated solvents
•Coal tars
•Polychlorinated biphenyls (PCBs)
The design phase for a free product recovery system is often initiated by seeking
answers to the following questions (EPA 1996a):
• What is the spatial distribution of the free product in the subsurface?
• What is the expected mass of free product in the contaminated zone?
• What mass/volume of the free product is recoverable?
• How quickly/easily can the free product be recovered?
Widely used approaches to recover free product from subsurface contaminant pools
include skimming systems, recovery with water table depression, soil
vapor/groundwater extraction, and dual phase (liquid and vapor) recovery and
separation. The selection of a particular approach is often guided by site conditions,
specific remedial objectives or design constraints. Skimming systems (Figure 3.1) are used
for short-term remedial actions where the free phase is removed from a well or trench
without recovering groundwater. These systems work effectively to remove free product
exits from permeable subsurface zones such as utility bedding or buried underground open
structures. Skimming systems may be passive such as filter canisters or absorbent bailers
or active such as belt skimmers, pneumatic pumps or floaters.
Table 3.1 summarizes key properties of the fluid and geologic media that affect subsurface migration and free
product recovery
Figure 3.1
Skimming system for
LNAPL free product
recovery includes an
interceptor trench and
a recovery well.
Recovery of free phase DNAPLs is complicated by the fact that these
products sink to the bottom of the aquifer. Chemical flooding methods
such as enhanced dissolution and physical mobilization are often
used to flush the free product out of soil pores before recovery using
extraction wells. Enhanced dissolution methods utilize cosolvents or
solubilizing surfactants to increase the solubility of the DNAPL. Physical
mobilization of DNAPL by reducing interfacial tension is accomplished
through mobilizing surfactants or miscible alcohol floods.
2. PUMP-AND-TREAT
Pump-and-treat is the most
widely used remediation
technology. Pump-and-treat has
been used both as a stand-alone
treatment system and in
conjunction with
complementary technologies.
Conventional pump-and-treat
methods focus on the extraction
of contaminated groundwater to
the surface for subsequent
treatment. Such systems have
been used in about 75% of
Superfund clean up actions
where groundwater was
contaminated (NRC, 1994). The
treated groundwater may be re-
injected into the subsurface or
discharged into a receiving
PUMP-AND-TREAT
Once groundwater is extracted, a variety of physical, chemical and biological processes can be
used to treat the contaminated water. These processes include adsorption, volatilization,
precipitation, oxidation-reduction, and biotransformation. However, the effective extraction
of contaminated groundwater at the site requires that the contaminant sources be identified,
located, and controlled. Wherever possible, source removal should be implemented to
prevent further contamination. A thorough study of the site should include assessing the type
and extent of contamination and a three-dimensional characterization of the subsurface
including hydraulic conductivity, particle size distribution and the sorption potential of aquifer
material
Pump-and-treat systems are severely limited by the extensive contaminant tailing and
rebound problems often associated with the technology. Tailing represents the progressively
slow decline in aqueous contaminant concentration in the extracted water with pumping
duration (Figure 3.4). Tailing of contaminants results in long treatment times. At longer
treatment periods, larger and larger volumes of water have to be extracted to remove the
smaller and smaller concentrations of pollutant. At several sites, pump-and-treat systems
would have to run for hundreds of years before contaminant concentrations have receded
to acceptable cleanup levels.
Contaminant rebound refers to the momentary increase in aqueous contaminant
concentration observed when a well is re-started after a period of no pumping. Rebound is
also known to occur when pumps are restarted after a treatment system appears to have
achieved the cleanup standard. The reasons for tailing and rebound during pump-and-treat
operations often relate to mass-transfer limitations from aquifer surfaces and NAPL pools.
Other factors may include precipitate dissolution in case of inorganic solutes, contaminant
diffusion into low permeability media, and variations in groundwater velocity (EPA 1996b).
Figure 3.4 Tailing and rebound behavior typically observed in pump-and-treat
systems (Cohen et al., 1994).
REFERENCES:
■ 1. Remediation technologies for soils and groundwater / sponsored by
Remediation Technologies for Soils and Groundwater Task committee of the
Environmental Council, Environmental and Water Resources Institute (EWRI) of
the American Society of Civil Engineers ; edited by Alok Bhandari ... [et al.].
■ 2. How To Effectively Recover Free Product At Leaking Underground Storage
Tank Sites. A Guide For State Regulators, EPA 510-R-96-001, September 1996
■ 3. https://www.vertasefli.co.uk/our-solutions/expertise/free-product-
recovery

More Related Content

Similar to Chapter 3.pptx

Landremediationcanhelptorestorelandto 140619022629-phpapp01
Landremediationcanhelptorestorelandto 140619022629-phpapp01Landremediationcanhelptorestorelandto 140619022629-phpapp01
Landremediationcanhelptorestorelandto 140619022629-phpapp01
madhu rani
 
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational ResourcesOn-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
ricardo0hodges91
 
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational ResourcesOn-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
ovalnotary8042
 
Design of 210 Mld Sewage Treatment Plant
Design of 210 Mld Sewage Treatment PlantDesign of 210 Mld Sewage Treatment Plant
Design of 210 Mld Sewage Treatment Plant
ARUN KUMAR
 
Unit 5 SHWM.pptx
Unit 5 SHWM.pptxUnit 5 SHWM.pptx
Unit 5 SHWM.pptx
NaveenRathore25
 
1. Please explain the reaction mechanism and kinetics for the treatme.pdf
1. Please explain the reaction mechanism and kinetics for the treatme.pdf1. Please explain the reaction mechanism and kinetics for the treatme.pdf
1. Please explain the reaction mechanism and kinetics for the treatme.pdf
aratextails30
 
Domestic Waste water treatment
 Domestic Waste water treatment   Domestic Waste water treatment
Domestic Waste water treatment
Ghassan Hadi
 
Successful ISCR-Enhanced Bioremediation - Summer 2010
Successful ISCR-Enhanced Bioremediation - Summer 2010Successful ISCR-Enhanced Bioremediation - Summer 2010
Successful ISCR-Enhanced Bioremediation - Summer 2010
James Peale
 
waste disposal and processing
waste disposal and processingwaste disposal and processing
waste disposal and processing
Kanika Saxena
 
8. Trickling filters.pptx
8. Trickling filters.pptx8. Trickling filters.pptx
8. Trickling filters.pptx
Zhiwaroramari
 
L11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptx
L11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptxL11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptx
L11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptx
PRACHI DESSAI
 
Air and water pollution environment studies.pdf
Air and water pollution environment studies.pdfAir and water pollution environment studies.pdf
Air and water pollution environment studies.pdf
archanaagarwal35
 
Recycling Earths Rapidly Shrinking Resources_Published
Recycling Earths Rapidly Shrinking Resources_PublishedRecycling Earths Rapidly Shrinking Resources_Published
Recycling Earths Rapidly Shrinking Resources_Published
Nate Maguire
 
Wwtp presentation asim
Wwtp presentation asimWwtp presentation asim
Wwtp presentation asim
AsimDin2
 
Article four (recovered) one plus
Article four (recovered) one plusArticle four (recovered) one plus
Article four (recovered) one plus
Dr Robert Craig PhD
 
Biological treatments of water
Biological treatments of waterBiological treatments of water
Biological treatments of water
Mozakkir Azad
 
Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12
Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12
Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12
Terrance (Terry) Keep
 
Constructed wetland
Constructed wetlandConstructed wetland
Constructed wetland
Ankit Jain
 
A045040110
A045040110A045040110
A045040110
IJERA Editor
 
A045040110
A045040110A045040110
A045040110
IJERA Editor
 

Similar to Chapter 3.pptx (20)

Landremediationcanhelptorestorelandto 140619022629-phpapp01
Landremediationcanhelptorestorelandto 140619022629-phpapp01Landremediationcanhelptorestorelandto 140619022629-phpapp01
Landremediationcanhelptorestorelandto 140619022629-phpapp01
 
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational ResourcesOn-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
 
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational ResourcesOn-Site Sewage Treatment Alternatives | Publications and Educational Resources
On-Site Sewage Treatment Alternatives | Publications and Educational Resources
 
Design of 210 Mld Sewage Treatment Plant
Design of 210 Mld Sewage Treatment PlantDesign of 210 Mld Sewage Treatment Plant
Design of 210 Mld Sewage Treatment Plant
 
Unit 5 SHWM.pptx
Unit 5 SHWM.pptxUnit 5 SHWM.pptx
Unit 5 SHWM.pptx
 
1. Please explain the reaction mechanism and kinetics for the treatme.pdf
1. Please explain the reaction mechanism and kinetics for the treatme.pdf1. Please explain the reaction mechanism and kinetics for the treatme.pdf
1. Please explain the reaction mechanism and kinetics for the treatme.pdf
 
Domestic Waste water treatment
 Domestic Waste water treatment   Domestic Waste water treatment
Domestic Waste water treatment
 
Successful ISCR-Enhanced Bioremediation - Summer 2010
Successful ISCR-Enhanced Bioremediation - Summer 2010Successful ISCR-Enhanced Bioremediation - Summer 2010
Successful ISCR-Enhanced Bioremediation - Summer 2010
 
waste disposal and processing
waste disposal and processingwaste disposal and processing
waste disposal and processing
 
8. Trickling filters.pptx
8. Trickling filters.pptx8. Trickling filters.pptx
8. Trickling filters.pptx
 
L11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptx
L11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptxL11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptx
L11 -SECONDARY TREATMENT OF SEWAGE - TRICKLING FILTERS.pptx
 
Air and water pollution environment studies.pdf
Air and water pollution environment studies.pdfAir and water pollution environment studies.pdf
Air and water pollution environment studies.pdf
 
Recycling Earths Rapidly Shrinking Resources_Published
Recycling Earths Rapidly Shrinking Resources_PublishedRecycling Earths Rapidly Shrinking Resources_Published
Recycling Earths Rapidly Shrinking Resources_Published
 
Wwtp presentation asim
Wwtp presentation asimWwtp presentation asim
Wwtp presentation asim
 
Article four (recovered) one plus
Article four (recovered) one plusArticle four (recovered) one plus
Article four (recovered) one plus
 
Biological treatments of water
Biological treatments of waterBiological treatments of water
Biological treatments of water
 
Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12
Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12
Florida DEP Indirect Potable & Direct Potable Reuse presentation 10 sep12
 
Constructed wetland
Constructed wetlandConstructed wetland
Constructed wetland
 
A045040110
A045040110A045040110
A045040110
 
A045040110
A045040110A045040110
A045040110
 

Recently uploaded

Essentials of Automations: The Art of Triggers and Actions in FME
Essentials of Automations: The Art of Triggers and Actions in FMEEssentials of Automations: The Art of Triggers and Actions in FME
Essentials of Automations: The Art of Triggers and Actions in FME
Safe Software
 
GenAI Pilot Implementation in the organizations
GenAI Pilot Implementation in the organizationsGenAI Pilot Implementation in the organizations
GenAI Pilot Implementation in the organizations
kumardaparthi1024
 
Cosa hanno in comune un mattoncino Lego e la backdoor XZ?
Cosa hanno in comune un mattoncino Lego e la backdoor XZ?Cosa hanno in comune un mattoncino Lego e la backdoor XZ?
Cosa hanno in comune un mattoncino Lego e la backdoor XZ?
Speck&Tech
 
Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!
Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!
Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!
SOFTTECHHUB
 
GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...
GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...
GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...
Neo4j
 
GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024
GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024
GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024
Neo4j
 
Introduction to CHERI technology - Cybersecurity
Introduction to CHERI technology - CybersecurityIntroduction to CHERI technology - Cybersecurity
Introduction to CHERI technology - Cybersecurity
mikeeftimakis1
 
Video Streaming: Then, Now, and in the Future
Video Streaming: Then, Now, and in the FutureVideo Streaming: Then, Now, and in the Future
Video Streaming: Then, Now, and in the Future
Alpen-Adria-Universität
 
Infrastructure Challenges in Scaling RAG with Custom AI models
Infrastructure Challenges in Scaling RAG with Custom AI modelsInfrastructure Challenges in Scaling RAG with Custom AI models
Infrastructure Challenges in Scaling RAG with Custom AI models
Zilliz
 
20240605 QFM017 Machine Intelligence Reading List May 2024
20240605 QFM017 Machine Intelligence Reading List May 202420240605 QFM017 Machine Intelligence Reading List May 2024
20240605 QFM017 Machine Intelligence Reading List May 2024
Matthew Sinclair
 
20240609 QFM020 Irresponsible AI Reading List May 2024
20240609 QFM020 Irresponsible AI Reading List May 202420240609 QFM020 Irresponsible AI Reading List May 2024
20240609 QFM020 Irresponsible AI Reading List May 2024
Matthew Sinclair
 
Communications Mining Series - Zero to Hero - Session 1
Communications Mining Series - Zero to Hero - Session 1Communications Mining Series - Zero to Hero - Session 1
Communications Mining Series - Zero to Hero - Session 1
DianaGray10
 
Removing Uninteresting Bytes in Software Fuzzing
Removing Uninteresting Bytes in Software FuzzingRemoving Uninteresting Bytes in Software Fuzzing
Removing Uninteresting Bytes in Software Fuzzing
Aftab Hussain
 
GraphRAG for Life Science to increase LLM accuracy
GraphRAG for Life Science to increase LLM accuracyGraphRAG for Life Science to increase LLM accuracy
GraphRAG for Life Science to increase LLM accuracy
Tomaz Bratanic
 
How to use Firebase Data Connect For Flutter
How to use Firebase Data Connect For FlutterHow to use Firebase Data Connect For Flutter
How to use Firebase Data Connect For Flutter
Daiki Mogmet Ito
 
Best 20 SEO Techniques To Improve Website Visibility In SERP
Best 20 SEO Techniques To Improve Website Visibility In SERPBest 20 SEO Techniques To Improve Website Visibility In SERP
Best 20 SEO Techniques To Improve Website Visibility In SERP
Pixlogix Infotech
 
Driving Business Innovation: Latest Generative AI Advancements & Success Story
Driving Business Innovation: Latest Generative AI Advancements & Success StoryDriving Business Innovation: Latest Generative AI Advancements & Success Story
Driving Business Innovation: Latest Generative AI Advancements & Success Story
Safe Software
 
Building Production Ready Search Pipelines with Spark and Milvus
Building Production Ready Search Pipelines with Spark and MilvusBuilding Production Ready Search Pipelines with Spark and Milvus
Building Production Ready Search Pipelines with Spark and Milvus
Zilliz
 
Artificial Intelligence for XMLDevelopment
Artificial Intelligence for XMLDevelopmentArtificial Intelligence for XMLDevelopment
Artificial Intelligence for XMLDevelopment
Octavian Nadolu
 
How to Get CNIC Information System with Paksim Ga.pptx
How to Get CNIC Information System with Paksim Ga.pptxHow to Get CNIC Information System with Paksim Ga.pptx
How to Get CNIC Information System with Paksim Ga.pptx
danishmna97
 

Recently uploaded (20)

Essentials of Automations: The Art of Triggers and Actions in FME
Essentials of Automations: The Art of Triggers and Actions in FMEEssentials of Automations: The Art of Triggers and Actions in FME
Essentials of Automations: The Art of Triggers and Actions in FME
 
GenAI Pilot Implementation in the organizations
GenAI Pilot Implementation in the organizationsGenAI Pilot Implementation in the organizations
GenAI Pilot Implementation in the organizations
 
Cosa hanno in comune un mattoncino Lego e la backdoor XZ?
Cosa hanno in comune un mattoncino Lego e la backdoor XZ?Cosa hanno in comune un mattoncino Lego e la backdoor XZ?
Cosa hanno in comune un mattoncino Lego e la backdoor XZ?
 
Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!
Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!
Goodbye Windows 11: Make Way for Nitrux Linux 3.5.0!
 
GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...
GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...
GraphSummit Singapore | Enhancing Changi Airport Group's Passenger Experience...
 
GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024
GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024
GraphSummit Singapore | Neo4j Product Vision & Roadmap - Q2 2024
 
Introduction to CHERI technology - Cybersecurity
Introduction to CHERI technology - CybersecurityIntroduction to CHERI technology - Cybersecurity
Introduction to CHERI technology - Cybersecurity
 
Video Streaming: Then, Now, and in the Future
Video Streaming: Then, Now, and in the FutureVideo Streaming: Then, Now, and in the Future
Video Streaming: Then, Now, and in the Future
 
Infrastructure Challenges in Scaling RAG with Custom AI models
Infrastructure Challenges in Scaling RAG with Custom AI modelsInfrastructure Challenges in Scaling RAG with Custom AI models
Infrastructure Challenges in Scaling RAG with Custom AI models
 
20240605 QFM017 Machine Intelligence Reading List May 2024
20240605 QFM017 Machine Intelligence Reading List May 202420240605 QFM017 Machine Intelligence Reading List May 2024
20240605 QFM017 Machine Intelligence Reading List May 2024
 
20240609 QFM020 Irresponsible AI Reading List May 2024
20240609 QFM020 Irresponsible AI Reading List May 202420240609 QFM020 Irresponsible AI Reading List May 2024
20240609 QFM020 Irresponsible AI Reading List May 2024
 
Communications Mining Series - Zero to Hero - Session 1
Communications Mining Series - Zero to Hero - Session 1Communications Mining Series - Zero to Hero - Session 1
Communications Mining Series - Zero to Hero - Session 1
 
Removing Uninteresting Bytes in Software Fuzzing
Removing Uninteresting Bytes in Software FuzzingRemoving Uninteresting Bytes in Software Fuzzing
Removing Uninteresting Bytes in Software Fuzzing
 
GraphRAG for Life Science to increase LLM accuracy
GraphRAG for Life Science to increase LLM accuracyGraphRAG for Life Science to increase LLM accuracy
GraphRAG for Life Science to increase LLM accuracy
 
How to use Firebase Data Connect For Flutter
How to use Firebase Data Connect For FlutterHow to use Firebase Data Connect For Flutter
How to use Firebase Data Connect For Flutter
 
Best 20 SEO Techniques To Improve Website Visibility In SERP
Best 20 SEO Techniques To Improve Website Visibility In SERPBest 20 SEO Techniques To Improve Website Visibility In SERP
Best 20 SEO Techniques To Improve Website Visibility In SERP
 
Driving Business Innovation: Latest Generative AI Advancements & Success Story
Driving Business Innovation: Latest Generative AI Advancements & Success StoryDriving Business Innovation: Latest Generative AI Advancements & Success Story
Driving Business Innovation: Latest Generative AI Advancements & Success Story
 
Building Production Ready Search Pipelines with Spark and Milvus
Building Production Ready Search Pipelines with Spark and MilvusBuilding Production Ready Search Pipelines with Spark and Milvus
Building Production Ready Search Pipelines with Spark and Milvus
 
Artificial Intelligence for XMLDevelopment
Artificial Intelligence for XMLDevelopmentArtificial Intelligence for XMLDevelopment
Artificial Intelligence for XMLDevelopment
 
How to Get CNIC Information System with Paksim Ga.pptx
How to Get CNIC Information System with Paksim Ga.pptxHow to Get CNIC Information System with Paksim Ga.pptx
How to Get CNIC Information System with Paksim Ga.pptx
 

Chapter 3.pptx

  • 1. CHAPTER 3 Physical Treatment Technologies Ravi Damera and Alok Bhandari REMEDIATION TECHNOLOGIES FOR SOILS AND GROUNDWATER American Society of Civil Engineers 1801 Alexander Bell Drive Reston, Virginia, 20191-4400 Copyright © 2007 by the American Society of Civil Engineers. All Rights Reserved. ISBN 13: 978-0-7844-0894-0 ISBN 10: 0-7844-0894-7 Manufactured in the United States of America.
  • 2. INTRODUCTION Physical treatment technologies take advantage of physicochemical properties of the contaminant and the affected media to remediate soil and groundwater. PHYSICOCHEMICAL PROPERTIES in this context include: for CONTAMINANT  density,  solubility,  viscosity,  volatility for MEDIA (that can be exploited during site remediation)  physical state (solid, liquid or gas),  its bulk density,  moisture content,  permeability,  porosity,  particle size distribution  ability to conduct heat or electric current Most conventional physical treatment technologies:  free product recovery,  pump and treat,  soil vapor extraction,  air sparging,  groundwater circulation wells,  multi-phase extraction,  induced fracturing,  soil heating
  • 3. 1. FREE PRODUCT RECOVERY Free product, also known as free phase contamination, refers to concentrated contaminants that are not miscible with groundwater and therefore form a separate layer. Free phase product recovery is often applied in combination with other treatment processes such as soil vapour extraction (SVE), dual phase extraction, ex-situ treatments and bioremediation. It is rarely undertaken alone except in the least sensitive environmental settings. Depending on physical properties, product can be recovered as a liquid or vapour and the recovery could be enhanced by steam injection or surfactant flushing.
  • 4. 1. FREE PRODUCT RECOVERY Light non-aqueous phase liquids (LNAPL): these contaminants are less dense than water and float on the water table surface. Dense non-aqueous phase liquid (DNAPL): these contaminants are denser than water and sink to the bottom of water table and rest on impermeable surfaces such as clays and bedrock. There are two types of free product: Contaminants Free product recovery is applicable to all chemicals, common free product contaminants are: •Light non-aqueous Phase liquids (LNAPL) •Diesel range organics (DRO) •Petroleum range organics (PRO) •Kerosene •Dense non-aqueous phase liquid (DNAPL) •Creosote •Chlorinated solvents •Coal tars •Polychlorinated biphenyls (PCBs)
  • 5. The design phase for a free product recovery system is often initiated by seeking answers to the following questions (EPA 1996a): • What is the spatial distribution of the free product in the subsurface? • What is the expected mass of free product in the contaminated zone? • What mass/volume of the free product is recoverable? • How quickly/easily can the free product be recovered? Widely used approaches to recover free product from subsurface contaminant pools include skimming systems, recovery with water table depression, soil vapor/groundwater extraction, and dual phase (liquid and vapor) recovery and separation. The selection of a particular approach is often guided by site conditions, specific remedial objectives or design constraints. Skimming systems (Figure 3.1) are used for short-term remedial actions where the free phase is removed from a well or trench without recovering groundwater. These systems work effectively to remove free product exits from permeable subsurface zones such as utility bedding or buried underground open structures. Skimming systems may be passive such as filter canisters or absorbent bailers or active such as belt skimmers, pneumatic pumps or floaters.
  • 6. Table 3.1 summarizes key properties of the fluid and geologic media that affect subsurface migration and free product recovery
  • 7. Figure 3.1 Skimming system for LNAPL free product recovery includes an interceptor trench and a recovery well.
  • 8. Recovery of free phase DNAPLs is complicated by the fact that these products sink to the bottom of the aquifer. Chemical flooding methods such as enhanced dissolution and physical mobilization are often used to flush the free product out of soil pores before recovery using extraction wells. Enhanced dissolution methods utilize cosolvents or solubilizing surfactants to increase the solubility of the DNAPL. Physical mobilization of DNAPL by reducing interfacial tension is accomplished through mobilizing surfactants or miscible alcohol floods.
  • 9. 2. PUMP-AND-TREAT Pump-and-treat is the most widely used remediation technology. Pump-and-treat has been used both as a stand-alone treatment system and in conjunction with complementary technologies. Conventional pump-and-treat methods focus on the extraction of contaminated groundwater to the surface for subsequent treatment. Such systems have been used in about 75% of Superfund clean up actions where groundwater was contaminated (NRC, 1994). The treated groundwater may be re- injected into the subsurface or discharged into a receiving
  • 10. PUMP-AND-TREAT Once groundwater is extracted, a variety of physical, chemical and biological processes can be used to treat the contaminated water. These processes include adsorption, volatilization, precipitation, oxidation-reduction, and biotransformation. However, the effective extraction of contaminated groundwater at the site requires that the contaminant sources be identified, located, and controlled. Wherever possible, source removal should be implemented to prevent further contamination. A thorough study of the site should include assessing the type and extent of contamination and a three-dimensional characterization of the subsurface including hydraulic conductivity, particle size distribution and the sorption potential of aquifer material
  • 11. Pump-and-treat systems are severely limited by the extensive contaminant tailing and rebound problems often associated with the technology. Tailing represents the progressively slow decline in aqueous contaminant concentration in the extracted water with pumping duration (Figure 3.4). Tailing of contaminants results in long treatment times. At longer treatment periods, larger and larger volumes of water have to be extracted to remove the smaller and smaller concentrations of pollutant. At several sites, pump-and-treat systems would have to run for hundreds of years before contaminant concentrations have receded to acceptable cleanup levels. Contaminant rebound refers to the momentary increase in aqueous contaminant concentration observed when a well is re-started after a period of no pumping. Rebound is also known to occur when pumps are restarted after a treatment system appears to have achieved the cleanup standard. The reasons for tailing and rebound during pump-and-treat operations often relate to mass-transfer limitations from aquifer surfaces and NAPL pools. Other factors may include precipitate dissolution in case of inorganic solutes, contaminant diffusion into low permeability media, and variations in groundwater velocity (EPA 1996b).
  • 12. Figure 3.4 Tailing and rebound behavior typically observed in pump-and-treat systems (Cohen et al., 1994).
  • 13.
  • 14.
  • 15. REFERENCES: ■ 1. Remediation technologies for soils and groundwater / sponsored by Remediation Technologies for Soils and Groundwater Task committee of the Environmental Council, Environmental and Water Resources Institute (EWRI) of the American Society of Civil Engineers ; edited by Alok Bhandari ... [et al.]. ■ 2. How To Effectively Recover Free Product At Leaking Underground Storage Tank Sites. A Guide For State Regulators, EPA 510-R-96-001, September 1996 ■ 3. https://www.vertasefli.co.uk/our-solutions/expertise/free-product- recovery