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PNNL-13501 - Pacific Northwest National Laboratory

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The additions of Ti(III), Ni(II), palladium catalyst, and<br />

EDTA resulted in small to large decreases in the rate of<br />

trichloroethylene dechlorination, possibly indicating<br />

adsorption of these metals or complexes blocked access<br />

by trichloroethylene. The addition of AQDS (electron<br />

shuttle) resulted in a small but insignificant increase in the<br />

trichloroethylene dechlorination rate (Figure 4).<br />

conc (µmol/L)<br />

10<br />

8<br />

6<br />

4<br />

initial: 1.1 ppm TCE in DI water<br />

TCE<br />

Summary and Conclusions<br />

Fe(II) and Mn(II) additions to partially reduced sediment<br />

resulted in a significant increase in trichloroethylene<br />

dechlorination. Trichloroethylene dechlorination with the<br />

Fe(II) addition was more efficient than Mn(II). The additions<br />

of Ti(III), Ni(II), Palladium catalyst, and EDTA did<br />

not enhance the rate of trichloroethylene dechlorination<br />

by the partially reduced sediment. Because the addition<br />

of an electron shuttle (AQDS) had only a slight positive<br />

effect, the rate of trichloroethylene degradation is not<br />

limited by electron transfer, so the addition of an<br />

additional electron donor rather than a catalyst is likely<br />

more efficient. While an Fe(II) addition is thought to be<br />

more cost-efficient than the use of reduced sediment<br />

alone, amending the redox treatment at the field scale<br />

involves additional coupled hydraulic and geochemical<br />

considerations. Because both Mn(II) and Fe(II) adsorb<br />

strongly to natural sediments, engineered small pulse<br />

injections with a high ionic strength or low pH would be<br />

needed at the field scale to result in a dispersed addition<br />

of adsorbed Fe(II) or Mn(II), as indicated by reactive<br />

transport modeling, and could be tested in experimental<br />

systems.<br />

References<br />

AQDS addition: 16.5 h<br />

2<br />

0<br />

acetylene<br />

control: half life 24.8 h<br />

0 5 10 time (h) 15 20 25<br />

Figure 4. Trichloroethylene dechlorination to acetylene in<br />

the presence of reduced natural sediment with the addition<br />

of an aqueous electron shuttle (AQDS), which resulted in a<br />

small increase in the dechlorination rate<br />

Curtis G and M Reinhard. 1994. “Reductive<br />

dehalogenation of hexachloroethane, carbon tetrachloride,<br />

and bromoform by anthrahydroquinone disulfonate and<br />

humic acid.” Env. Sci. Tech. 28:2393-2401.<br />

Heron G, TH Christensen, and J Tjell. 1994. “Oxidation<br />

capacity of aquifer sediments.” Environ. Sci. Technol.<br />

28:153-158.<br />

Li T and J Farrell. 2000. “Reductive dechlorination of<br />

trichloroethene and carbon tetrachloride using iron and<br />

palladized-iron cathodes.” Environmental Science and<br />

Technology 34(1):173-179.<br />

Roberts A, L Totten, W Arnold, D Burris, and<br />

T Campbell. 1996. “Reductive elimination of chlorinated<br />

ethylenes by zero-valent metals.” Environ. Sci. Technol.<br />

30(8):2654-2659.<br />

Scherer M, B Balko, and P Tratnyek. 1999. “The role of<br />

oxides in reduction reactions at the metal-water<br />

interface.” In kinetics and mechanisms of reactions at the<br />

mineral/water interface, eds. D Sparks and T Grundl,<br />

ACS Symposium Series #715, American Chemical<br />

Society, Atlanta, Georgia, p 301-322.<br />

Stucki JW, DC Golden, and CB Roth. 1984.<br />

“Preparation and handling of dithionite-reduced smectite<br />

suspensions.” Clays and Clay Minerals 32(3):191-197.<br />

Su C and RW Puls. 1999. “Kinetics of trichloroethene<br />

reduction by zerovalent iron and tin: Pretreatment effect,<br />

apparent activation energy, and intermediate products.”<br />

Environmental Science and Technology, 33(1):163-168.<br />

Szecsody JE, JS Fruchter, DS Sklarew, and JC Evans.<br />

2000a. In situ redox manipulation of subsurface<br />

sediments from Fort Lewis, Washington: Iron reduction<br />

and TCE dechlorination mechanisms. <strong>PNNL</strong>-13178,<br />

<strong>Pacific</strong> <strong>Northwest</strong> <strong>National</strong> <strong>Laboratory</strong>, Richland,<br />

Washington.<br />

Szecsody J, M Williams, J Fruchter, V Vermeul, and<br />

J Evans. 2000b. “Influence of sediment reduction on<br />

TCE degradation, remediation of chlorinated and<br />

recalcitrant compounds.” book chapter, ed. G<br />

Wickramanayake, Chemical Oxidation and Reactive<br />

Barriers, p. 369-376.<br />

Wehrli B. 1992. “Redox reactions of metal ions at<br />

mineral surfaces.” In aquatic chemical kinetics, ed.<br />

W Stumm, Wiley Interscience, New York.<br />

Publication<br />

Szecsody J, M Williams, J Fruchter, and V Vermeul.<br />

2000. “In Situ Reduction of Aquifer Sediments for<br />

Remediation: 1. Iron Reduction Mechanism.”<br />

Environmental Science and Technology (submitted).<br />

Earth System Science 253

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