PNNL-13501 - Pacific Northwest National Laboratory
PNNL-13501 - Pacific Northwest National Laboratory
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 />
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Szecsody JE, JS Fruchter, DS Sklarew, and JC Evans.<br />
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and TCE dechlorination mechanisms. <strong>PNNL</strong>-13178,<br />
<strong>Pacific</strong> <strong>Northwest</strong> <strong>National</strong> <strong>Laboratory</strong>, Richland,<br />
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J Evans. 2000b. “Influence of sediment reduction on<br />
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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