Technical Papers
Sep 25, 2015

Herbicide-Impacted Sediment Remediation. I: Delineation and Treatability Study

Publication: Journal of Hazardous, Toxic, and Radioactive Waste
Volume 20, Issue 2

Abstract

This paper is the first in a series on the Tyco Fire Products LP Sediment Removal Project (Marinette, Wisconsin) describing the dredging, stabilization and solidification (S/S) treatment, and nonhazardous disposal of arsenic-impacted sediments. Arsenic (As) impacts were associated primarily with the release of monomethyl arsonic acid (MMA) [CH3AsO(OH)2] and dimethyl arsinic acid (DMA) [(CH3)2AsO(OH)] derived from historic herbicide manufacturing and storage activities. Two main sediment horizons were affected: an upper soft sediment [soft dredged material (DM)] and an underlying semiconsolidated material (SCM) layer. One soft DM surrogate had a total As content of 6,295mg/kg; toxicity characteristic leaching procedure (TCLP) As of 34.6mg/L, moisture contents (MCs) between 169 and 200%; and a loss on ignition of 15.4. Two types of SCMs were evaluated. One was a very sandy nonplastic sediment with a total As content of 1,066mg/kg and TCLP As of 32mg/L. The other was TCLP As compliant but was more water sensitive, with a total As content of 884mg/kg and MC of 81%. A treatability study was conducted to determine the S/S treatments, using no more than two reagents simultaneously, that would yield a product meeting all disposal criteria (TCLP As <5mg/L, pass paint filter test, and maintain a pH between 2 and 12) within 3 days, and be moreover workable. More than 200 mix designs were performed. The conventional approach to immobilizing inorganic arsenic with traditional pozzolans (lime, cement, cement kiln dust, lime kiln dust) led to a doubling of the TCLP As values into the 70mg/L range. The inclusion of ferric iron was decisive, and combinations of ferric sulfate (wet and dry for As immobilization) with limited quantities of portland cement sufficient to achieve solidification were found to perform the best.

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Acknowledgments

CH2M HILL (Jeff Danko, Project Manager) completed this work for Tyco International, Inc., (Princeton, New Jersey) under the direction and management of Messrs. Joseph Janeczek, PE, and Larry Wilson, with regulatory oversight provided by U.S. EPA Region V and the Wisconsin Department of Natural Resources (WDNR). Sevenson Environmental Services (Niagara Falls, New York) was the general contractor responsible for all dredging and sediment treatment. All S/S mix design work (reported here) was completed by the CH2M HILL Applied Sciences Laboratory (Corvallis, Oregon). Dr. Jonathan Blount (formerly of CH2M HILL) is thanked for his assistance in developing Fig. 3 and supporting narrative. Any opinions, findings, and conclusions expressed in this publication are those of the authors and do not necessarily reflect the views of Tyco, CH2M HILL, U.S. EPA, or WDNR.

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Information & Authors

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Published In

Go to Journal of Hazardous, Toxic, and Radioactive Waste
Journal of Hazardous, Toxic, and Radioactive Waste
Volume 20Issue 2April 2016

History

Received: Nov 16, 2014
Accepted: Jul 14, 2015
Published online: Sep 25, 2015
Discussion open until: Feb 25, 2016
Published in print: Apr 1, 2016

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Authors

Affiliations

Dennis G. Grubb, M.ASCE [email protected]
Vice President, Phoenix Services LLC, 348 W State St., Suite 301, Kennett Square, PA 19348; formerly, Senior Principal Technologist, CH2M HILL, 1717 Arch St., Suite 4400, Philadelphia, PA 19103 (corresponding author). E-mail: [email protected]
Heather L. Ziegelbauer
Project Manager, CH2M HILL, 135 South 84th St., Suite 400, Milwaukee, WI 53214.
Dusty R. V. Berggren
Associate Engineer, CH2M HILL, 1100 NE Circle Blvd., Suite 300, Corvallis, OR 97330.
Jeffrey Danko
Senior Project Manager, CH2M HILL, 135 South 84th St., Suite 400, Milwaukee, WI 53214.

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