Multimedia Chemical Fate Model for Environmental Dredging Fabian F. Sanchez 1 ; Louis J. Thibodeaux 2 ; Kalliat T. Valsaraj 3 ; and Danny D. Reible 4 Abstract: Dredging the bed-sediment of rivers, lakes, estuaries, and harbors is a process of remediating contaminated sites. Whether used alone or in conjunction with in situ capping or natural recovery, its application results in the loss of contaminants to the surroundings. A steady-state multimedia box model has been developed consisting of a dredge element that initiates chemical release in a flowing stream and an algorithm for residue transport to air, water, and sediment, both with and without silt curtain containment. The model quantifies these losses and, commencing with the original in-place contaminant mass, determines the quantity targeted for dredging and the quantity ‘‘delivered to shore.’’The latter is a measure of the efficiency of the dredging operation. The model was developed from experience gained studying the effectiveness of environmental dredging at three sites: Bayou Bonfouca Slidell, La., Grasse River Massena, N.Y., and Manistique Harbor Manistique, Mich.. This paper describes the multimedia model theory and algorithm development and demonstrates its use in the application to the Bayou Bonfouca Superfund site, which was dredged for removal of creosote waste containing 16 polyaromatic hydrocarbons. DOI: 10.1061/ASCE1090-025X20026:2120 CE Database keywords: Multimedia; Dredging; Models; Chemicals; Sediment; Contamination; Environmental impacts. Introduction Toxic and hazardous materials exist in the sediment on the bottom of rivers, lakes, and estuaries in the United States. This accumu- lation of contaminants in surface waters represents a long-term source of contamination to aquatic life. Direct human contact with contaminated sediments is also a concern if they are present in a shallow water environment used for recreational purposes. For contaminated sediments, remediation technologies can be grouped into four categories: interim control, in situ management, sediment removal and transportation, and ex situ management NRC 1998. Interim control is a means of reducing risk of human exposure by implementing preventive measures warning signs, fencing, swimming and fishing advisories, and so on. In situ management deals with the contaminated sediment on-site, where the technologies are for containment and treatment. A form of containment is capping, which is the process of placing a layer of clean sediment such as sand over the contaminated bed. An- other form of in situ management is monitored natural attenua- tion, which entails allowing natural processes to reduce the con- taminant concentration and/or bioavailability. The two removal technologies involve relocation and handling of the contaminated sediment. Sediment removal is accomplished using dredges or earth-moving equipment. Ex situ management is accomplished by placing the dredged material in landfills, con- fined disposal facilities, or confined aquatic disposal facilities on or near the contaminated sites. Alternative and more aggressive ex situ treatment technologies such as incineration are site spe- cific, and their implementation depends on the cost and environ- mental friendliness of the operation and other factors. Of all the remediation technologies available, the U.S. Envi- ronmental Protection Agency USEPAmandates that most of the sites designated for cleanup consider dredging. In fact, ‘‘dredging has become the default remedy for contaminated sediments’’ GEC 2000. Environmental dredging operations remove sedi- ments with some known contamination as effectively as possible. An effective method would include complete removal of the de- sired sediment with as little environmental risk and consequence as possible Hayes 1992. Anticipating extensive use of environmental dredging, it is im- portant to be able to determine the effectiveness of the operation. The General Electric Company GECrecently compiled a report on its effectiveness in controlling risks. The report reviewed major sediment remediation projects in the United States, their objectives, the technologies being employed, and the capabilities and limitations of those technologies GEC 2000. The primary conclusions drawn from the 54 sites reviewed were 1environ- mental dredging has not reduced surface sediment concentrations to acceptable levels, being higher in some cases that is, Manis- tique Harbor, Mich.; 2dredging has not been shown to lead to quantifiable reductions in fish contaminant levels; 3dredging projects are costly and take a long time to complete; 4dredging resuspends and releases contaminants into the water column; and 5dredging technology and experience in large rivers are limited. From a chemodynamic standpoint, the main disadvantage to dredging is the resuspension of sediment in the water column. Sediment resuspension leads to contaminant releases in the water column and other environmental media air, soil, and sediment. 1 Gordon A. and Mary Cain Dept. of Chemical Engineering, Louisiana State Univ., Baton Rouge, LA 70803. 2 Gordon A. and Mary Cain Dept. of Chemical Engineering and South/ Southwest Hazardous Substance Research Center, Louisiana State Univ., Baton Rouge, LA 70803. 3 Gordon A. and Mary Cain Dept. of Chemical Engineering, Louisiana State Univ., Baton Rouge, LA 70803. 4 Gordon A. and Mary Cain Dept. of Chemical Engineering, Louisiana State Univ., Baton Rouge, LA 70803. Note. Discussion open until September 1, 2002. Separate discussions must be submitted for individual papers. To extend the closing date by one month, a written request must be filed with the ASCE Managing Editor. The manuscript for this paper was submitted for review and pos- sible publication on February 9, 2001; approved on December 26, 2001. This paper is part of the Practice Periodical of Hazardous, Toxic, and Radioactive Waste Management, Vol. 6, No. 2, April 1, 2002. ©ASCE, ISSN 1090-025X/2002/2-120–128/$8.00+$.50 per page. 120 / PRACTICE PERIODICAL OF HAZARDOUS, TOXIC, AND RADIOACTIVE WASTE MANAGEMENT / APRIL 2002