Jay Clausen
Amec Foster Wheeler
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Soil & Sediment Contamination | 2004
Hiroshi Yamamoto; Matthew C. Morley; Gerald E. Speitel; Jay Clausen
Several areas of the Massachusetts Military Reservation (MMR) have soils with significant levels of high explosives (HE) contamination because of a long history of training and range activities (such as open burning, open detonation, disposal, and artillery and mortar firing). Site-specific transport and attenuation mechanisms were assessed in sandy soils for three contaminants of concern: the nitramine hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX), and the nitroaromatics 2,4-dinitrotolune (2,4-DNT) and 2,4,6-trinitrotoluene (TNT). For all three contaminants, linear distribution coefficients (Kd) were dependent on the fraction of organic carbon in soil. The nitroaromatics sorbed much more strongly than RDX in both soils. Over 120 hours, the desorption rate of RDX from field contaminated surface soil was much slower than its sorption rate, with the desorption Kd (1.5 L/kg) much higher than Kd for sorption (0.37 L/kg). Desorption of 2,4-DNT was negligible over 120 hours. Thus, applying sorption-derived Kd values for transport modeling may significantly overestimate the flux of explosives from MMR soils. Based on multiple component column transport tests, RDX will be the most mobile of these contaminants in MMR soils. In saturated columns packed with uncontaminated soil, RDX broke through rapidly, whereas the nitroaromatics were significantly attenuated by irreversible sorption or abiotic transformations.
Soil & Sediment Contamination | 2004
Jay Clausen; Marilyn Hoyt; Elizabeth Wessling; Bryce Stearns; Bosco Ramirez; Nic Korte
The use of sodium bisulfate for field preservation of soil samples collected for the analysis of volatile organics (VOCs) can result in the formation of acetone. The work was performed at Camp Edwards, Massachusetts, as part of a multi-year investigation of the effects of training activities on the local environment. Preservation with sodium bisulfate was initiated in 1999 under regulatory mandate. The frequency of acetone detection and the quantities reported increased immediately thereafter. Correlation of duplicate sample results and a side-by-side comparison of six sample handling methods involving two analytical laboratories suggest the interaction of sodium bisulfate with naturally occurring organic matter in samples from Camp Edwards cause the formation of acetone. The data also indicate that a higher content of natural organic matter results in a greater production of acetone, and more acetone is formed the longer the sodium bisulfate is in contact with the soil.
Environmental Pollution | 2004
Jay Clausen; Joe Robb; Diane Curry; Nic Korte
Bombing and gunnery ranges | 2006
Jay Clausen; Nic Korte; Mary Dodson; Joe Robb; Shirley Rieven
This Digital Resource was created in Microsoft Word and Adobe Acrobat | 2012
Jay Clausen; Thomas Georgian; Julie Richardson; Anthony J. Bednar; Nancy Perron; Andrew Bray; Patricia Tuminello; Larry Penfold; Diane Anderson; Gordon Gooch
Archive | 2011
Jay Clausen; Benjamin C. Bostick; Anthony J. Bednar; Jing Sun; Joshua D. Landis
Archive | 2013
Jay Clausen; Thomas Georgian; Anthony J. Bednar; Nancy Perron; Andrew Bray; Patricia Tuminello; Gordon Gooch; Nathan Mulherin; Arthur B. Gelvin; Marc Beede
Archive | 2012
Jay Clausen; Julie Richardson; Nic Korte; Nancy Perron; Susan Taylor; Anthony J. Bednar; Patricia Tuminello; William T Jones; Shawna Tazik; Michael R. Walsh
This Digital Resource was created in Microsoft Word and Adobe Acrobat | 2007
Jay Clausen; Nic Korte; Benjamin C. Bostick; Benjamin Rice; Matthew Walsh; Andrew Nelson
This Digital Resource was created in Microsoft Word and Adobe Acrobat | 2013
Jay Clausen; Thomas Georgian; Anthony J. Bednar