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20 DEVELOPING A REMEDIATION STRATEGY FOR CONTAMINATED SEDIMENTS: SELECTING REMOVAL, TREATMENT, DISPOSAL, AND RE-USE ALTERNATIVES Stanislaus J. Zagula, Chemical Engineer Eberhard W. Beitinger, Senior Project Engineer Woodward-Clyde Consultants Chicago, Illinois 60603 INTRODUCTION The need to develop cost-effective strategies to assess and remediate contaminated sediment has come to the forefront of the regulated communities in both the public and private sector as the United States Environmental Protection Agency (USEPA) changes the focus of its water pollution control efforts from point source discharges to non-point sources. Contaminated sediment, a primary non- point source of pollution, has been identified as one of the largest potential risks to water quality and the aquatic environment.1 The concern over contaminated sediments stems from their tendency to adsorb and accumulate toxic metals and organic chemicals which make their way into streams, lakes, rivers, and harbors from a variety of sources. These contaminants may then be introduced into food chains, ingested or absorbed through dermal contact, or released into the water column during mixing and resuspension of the sediment. In the Great Lakes regions alone, contaminated sediments have been identified as a problem in 42 of 43 Areas of Concern (AOCs). Nationally, nearly 25 percent of National Priority List sites have been found to contain contaminated sediments and over 20 percent of Superfund Records of Decision address potential sediment contamination.2 In addition, approximately 390 million cubic yards of sediment, some of which are potentially contaminated, are dredged annually from waterways within the United States to maintain shipping channels and for flood control.3 By enforcement of existing statutes, such as the Clean Water Act (CWA), the Toxic Substances Control Act (TSCA), the Resource Conservation and Recovery Act (RCRA), and the Comprehensive Environmental Response, Compensation, and Liabilities Act (CERCLA or Superfund), the USEPA is addressing the cleanup of contaminated sediments through Consent Orders and Remedial Action Plans. Proposed water quality programs, such as the Great Lakes Water Quality Guidelines (Great Lakes Initiative) and international water quality agreements also address issues related to non-point source pollution, including contaminated sediments. Developing an integrated approach to contaminated sediment removal, transport, treatment, disposal, and re-use, coupled with an understanding of sediment characterization and assessment, will be fundamental to the successful implementation of cost-effective remediation plans for contaminated sediments. NATURE AND EXTENT OF CONTAMINATED SEDIMENT Sediments can be defined as the fine, medium, and coarse grain mineral and organic particles that are found at the bottom of lakes, rivers, bays, estuaries, and oceans. A large portion of these particles are comprised of eroded soil which was transported and/or deposited by water or wind. Other important components of sediment include organic matter, iron oxides, sulfides, carbonates, and the interstitial water in equilibrium with the sediment. The organic matter consists of humus, plant and animal detritus, and other organic material which settles to the bottom of a body of water, providing substrate for a variety of benthic organisms (worms, amphipods, bivalves, etc.) at the base of the aquatic food chain. In addition to the naturally deposited mineral and organic material and associated benthic organisms, the sediment may contain larger vegetative, plant, and woody material, trash, and debris. Sediments are very heterogenous materials, however, they can be characterized by selected chemical and physical properties, such as grain size distribution, water content, percent organic matter, and 48th Purdue Industrial Waste Conference Proceedings, 1993 Lewis Publishers, Chelsea, Michigan 48118. Printed in U.S.A. 199
Object Description
Purdue Identification Number | ETRIWC199320 |
Title | Developing a remediation strategy for contaminated sediments : selecting removal, treatment, disposal, and re-use alternatives |
Author |
Zagula, Stanislaus J. Beitinger, Eberhard W. |
Date of Original | 1993 |
Conference Title | Proceedings of the 48th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,21159 |
Extent of Original | p. 199-214 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Date Digitized | 2009-11-03 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 199 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | 20 DEVELOPING A REMEDIATION STRATEGY FOR CONTAMINATED SEDIMENTS: SELECTING REMOVAL, TREATMENT, DISPOSAL, AND RE-USE ALTERNATIVES Stanislaus J. Zagula, Chemical Engineer Eberhard W. Beitinger, Senior Project Engineer Woodward-Clyde Consultants Chicago, Illinois 60603 INTRODUCTION The need to develop cost-effective strategies to assess and remediate contaminated sediment has come to the forefront of the regulated communities in both the public and private sector as the United States Environmental Protection Agency (USEPA) changes the focus of its water pollution control efforts from point source discharges to non-point sources. Contaminated sediment, a primary non- point source of pollution, has been identified as one of the largest potential risks to water quality and the aquatic environment.1 The concern over contaminated sediments stems from their tendency to adsorb and accumulate toxic metals and organic chemicals which make their way into streams, lakes, rivers, and harbors from a variety of sources. These contaminants may then be introduced into food chains, ingested or absorbed through dermal contact, or released into the water column during mixing and resuspension of the sediment. In the Great Lakes regions alone, contaminated sediments have been identified as a problem in 42 of 43 Areas of Concern (AOCs). Nationally, nearly 25 percent of National Priority List sites have been found to contain contaminated sediments and over 20 percent of Superfund Records of Decision address potential sediment contamination.2 In addition, approximately 390 million cubic yards of sediment, some of which are potentially contaminated, are dredged annually from waterways within the United States to maintain shipping channels and for flood control.3 By enforcement of existing statutes, such as the Clean Water Act (CWA), the Toxic Substances Control Act (TSCA), the Resource Conservation and Recovery Act (RCRA), and the Comprehensive Environmental Response, Compensation, and Liabilities Act (CERCLA or Superfund), the USEPA is addressing the cleanup of contaminated sediments through Consent Orders and Remedial Action Plans. Proposed water quality programs, such as the Great Lakes Water Quality Guidelines (Great Lakes Initiative) and international water quality agreements also address issues related to non-point source pollution, including contaminated sediments. Developing an integrated approach to contaminated sediment removal, transport, treatment, disposal, and re-use, coupled with an understanding of sediment characterization and assessment, will be fundamental to the successful implementation of cost-effective remediation plans for contaminated sediments. NATURE AND EXTENT OF CONTAMINATED SEDIMENT Sediments can be defined as the fine, medium, and coarse grain mineral and organic particles that are found at the bottom of lakes, rivers, bays, estuaries, and oceans. A large portion of these particles are comprised of eroded soil which was transported and/or deposited by water or wind. Other important components of sediment include organic matter, iron oxides, sulfides, carbonates, and the interstitial water in equilibrium with the sediment. The organic matter consists of humus, plant and animal detritus, and other organic material which settles to the bottom of a body of water, providing substrate for a variety of benthic organisms (worms, amphipods, bivalves, etc.) at the base of the aquatic food chain. In addition to the naturally deposited mineral and organic material and associated benthic organisms, the sediment may contain larger vegetative, plant, and woody material, trash, and debris. Sediments are very heterogenous materials, however, they can be characterized by selected chemical and physical properties, such as grain size distribution, water content, percent organic matter, and 48th Purdue Industrial Waste Conference Proceedings, 1993 Lewis Publishers, Chelsea, Michigan 48118. Printed in U.S.A. 199 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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