SRCosmos:

Order of appearence	Full citation	SRCosmos Link
1	Grubb DG, Wazne M, Jagupilla SC, Malasavage NE, (2010). “Arsenic immobilization using slag fines,” Protection & Restoration of the Environment X, Corfu, Greece, July 5-9, pp.8.
2	Dragun J, Chekiri K, (2005). Elements in North American Soils, 2nd Edition, Amherst Scientific Publishers, Amherst, MA, p. 274.
3	Dermatas D, Braida W, Christodoulatos C, Strigul N, Paniko N, Los M, Larson S, (2004a). Solubility, Sorption And Soil Respiration Effects Of Tungsten And Tungsten Alloys, Environmental Forensics, Taylor and Francis, 5(1), March, 5-13.
4	Dermatas D, Dutko P, Dadachov M, (2004b) “Geoenvironmental Site Characterization: Lead Contaminated Firing Range Case Studies”, Proc. 5th International Conference on Case Studies in Geotechnical Engineering, New York, NY, pp.11.
5	Dermatas D, Menounou N, Dutko P, Dadachov M, Arienti P, Tsaneva V, (2004c) Lead and Copper Contamination in Small Arms Firing Ranges, Global NEST Journal, Greece, 6(2), pp. 143-150.
6	Dermatas D, Shen G, Chrysochoou M, Grubb DG, Menounou N, Dutko P, (2006) Pb speciation versus TCLP release in army firing range soils, Journal of Hazardous Materials, 136(1) 34-46.
7	Moon DH, Dermatas D, Grubb DG, (2006) “The effectiveness of quicklime-based stabilization/solidification on lead (Pb) contaminated soils,” Environmental Geotechnics (5th ICEG), H.R. Thomas (ed.), Thomas Telford Publishing, London, Vol. 1, pp. 221-228.
8	Grubb DG, Moon DH, Reilly T, Chrysochoou M, Dermatas D, O-Connor G, (2009) Leaching Behavior of Lead (Pb) and Tungsten (W) Contaminated Soils Stabilized with Type I/II Portland Cement, Silica Fume Cement and Cement Kiln Dust, Global NEST Journal, Greece, 11(3), pp. 267-282.
9	Karachalios A, Wazne M, Bentacur NJ, Jagupilla SC, Christodoulatos C, Braida W, O-Connor G, (2010) “Immobilization of Cu, Pb, and W in Mixed Munitions Firing Range Contaminated Soils by Various Amendments,” GeoFlorida 2010: Advances in Analysis, Modeling and Design, Geotechnical Special Publication No. 199, D. Fratta, A.J. Puppala, and B. Muhunthan (eds.), ASCE, pp. 10.
10	Chrysochoou M, Dermatas D, Grubb DG, (2007) Phosphate application to firing range soils for Pb immobilization: The unclear role of phosphate, Journal of Hazardous Materials, 144(1-2), 1-14.
11	Koutsospyros A, Braida W, Christodoulatos C, Dermatas D, Strigul N, 2006) Tungsten: from environmental obscurity to scrutiny, Journal of Hazardous Materials, Elsevier, 136(1), pp 1-19.
12	Sansalone JJ, Buchberger SG, Al-Abed SR, (1996) Fractionation of heavy metals in pavement runoff, Science of the Total Environment, 189/190, 371-378.
13	Kayhanian M, Singh A, Suverkropp C, Borroum S, (2003) Impact of annual average daily traffic on highway runoff pollutant concentrations, ASCE J. Env. Engrg., November, 129(11), pp. 975-990.
14	OSHA (1994) Method ID-213, Tungsten and Cobalt in Workplace Atmospheres (ICP Analysis), United States Department of Labor, Occupational Safety and Health Administration, Washington, DC (accessed 2/27/10, via www.osha.gov).
15	Materials Data Inc. (2006) Jade Version 7.5, California, USA.
16	Rietveld HM, (1969) A profile refinement method for nuclear and magnetic structures, J. Appl. Crystallogr., 2, 65–71.
17	International Centre for Diffraction Data (ICDD) (2004) Powder Diffraction File, PDF-2 Database Release.
18	Inorganic Crystal Structure Database (ICSD) (2009) Fachinformationszentrum, Karlsruhe, Germany.
19	Moon DH, Grubb DG, Reilly TL, (2009) Stabilization/solidification of selenium-impacted soils using Portland cement and cement kiln dust, Journal of Hazardous Materials, 168(2-3), 944-951.
20	Dermatas D, Dadachov M, Dutko P, Menounou N, Arienti P, Shen G, (2004) Weathering of Lead in Fort Irwin Firing Range Soils, Global Nest Journal, Greece, 6(2), pp 171-179.

Keywords
Abstract	The metals immobilization potential of freshly crushed (blast furnace and steel) slag fines was evaluated, where each media resembled USCS SP type soil with <5% passing the No. 200 (0.075 mm) sieve. Because of their granular nature, hardness, mineralogy and residual lime content, these media are quite reactive. Accordingly, their metals (immobilization) potential was evaluated using aqueous metal solutions (Cd, Cu, Pb, Ni, W, Se(IV), Se(IV), Zn) having target doses equivalent to 100 mg/kg to 100,000 mg/kg to the slag fines. After 30 days of mellowing, all samples were tested for pH, totals, toxicity characteristic leaching procedure (TCLP) and synthetic precipitation leaching procedure (SPLP) leaching behavior.
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Name	Affiliation	Home page	e-mail	Total pubs
Grubb DG	CETCO, Environmental Technology & Sustainable Geotechnics, 900 Northbrook Drive, Suite 320, Trevose, PA, USA, 19053		dennis.grubb@cetco.com	10
Jagupilla SCK	Department of Civil, Environmental and Ocean Engineering, Stevens Institute of Technology, Hoboken, NJ – 07030, USA			5
Wazne M	Center for Environmental Systems, Stevens Institute of Technology, Hoboken, NJ 07030, USA		mwazne@stevens.edu	16