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PNNL-13501 - Pacific Northwest National Laboratory

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the stepwise reduction can be observed. Figure 1 shows<br />

spectra at various times for the reduction of 0.01M<br />

Mn(VII) to Mn(VI) with 0.005M formate. The Mn(VI)<br />

concentration reaches a maximum around 15 minutes<br />

before it begins decreases as it disproportionates to<br />

Mn(VII) and Mn(V). The Mn(VII) concentration<br />

increases with time as shown in Figure 2 because the<br />

formate had been entirely consumed in the initial<br />

oxidation. The Mn(V) reacts with Mn(VI) producing<br />

more Mn(VII) and Mn(IV) which precipitates from<br />

solution.<br />

Absorbance<br />

1.4<br />

1.2<br />

1<br />

0.8<br />

0.6<br />

0.4<br />

0.2<br />

0<br />

Formate Reduction of Mn(VII) to Mn(VI)<br />

250 450 650<br />

Wavelength (nm)<br />

0.167 min<br />

432 FY 2000 <strong>Laboratory</strong> Directed Research and Development Annual Report<br />

1 min<br />

2 min<br />

3 min<br />

5 min<br />

9 min<br />

Figure 1. Spectral change on reduction of Mn(VII) to<br />

Mn(VI) with formate<br />

Absorbance<br />

0.7<br />

0.6<br />

0.5<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

Mn(VI) reacts to give Mn(VII)<br />

0<br />

250 450<br />

Wavelength (nm)<br />

650<br />

85 min<br />

211 min<br />

1303 min<br />

1713 min<br />

2691 min<br />

3137 min<br />

Figure 2. Spectral change as Mn(VI) disproportionates to<br />

Mn(VII)<br />

Using extinction coefficients calculated from Mn(VII)<br />

and Mn(VI) solutions of known concentrations,<br />

concentrations at various reaction times can be<br />

determined and used to examine the kinetics of the<br />

reactions. The reaction kinetics is very complex, with<br />

many concurrent and competing reactions. To compare<br />

the rates of reactions of the various reductants, reactions<br />

were carried out under the same conditions, and the initial<br />

rate of Mn(VII) disappearance was calculated under<br />

psuedo-first-order conditions. The analysis revealed that<br />

formate reacts 40 times faster than glycolate and glycine,<br />

which react at similar rates. Oxalate and nitrite did not<br />

react with permanganate under the conditions studied.<br />

Reactions were allowed to go to completion and the final<br />

products analyzed. Permanganate oxidation of formate<br />

yields carbonate. Both glycolate and glycine yield<br />

oxalate on oxidation, and glycine also yields ammonia.<br />

The permanganate (Mn(VII) is reduced to Mn(IV) which<br />

precipitates from solution. The pH of the solution is<br />

higher then the isoelectric point of manganese dioxide, so<br />

hydroxide is consumed by deprotanation of the<br />

precipitated solids. The dark brown/black solids are<br />

dense and settle to the bottom of the reaction vessel,<br />

resulting in a clear supernatant solution.<br />

Summary and Conclusions<br />

Permanganate reacts rapidly with organic compounds<br />

present in radioactive wastes resulting in a manganese<br />

dioxide precipitate that removes radioactive elements<br />

from solution. The amount of complexant destruction<br />

will be low when significant concentration of formate is<br />

present, since formate reacts much faster. Permanganate<br />

does not react directly with oxalate or nitrite under typical<br />

treatment conditions. A reduction in total organic carbon<br />

will be seen for the oxidation of formate to carbonate, but<br />

glycolate and glycine oxidation yields oxalate, which<br />

would still be included in the total organic carbon<br />

analysis.

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