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Handbook of Solvents - George Wypych - ChemTech - Ventech!

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1600 Hanadi S. Rifai, Charles J. Newell, Todd H. Wiedemeier<br />

Figure 23.1.6. Conceptual model <strong>of</strong> Type 1 environment<br />

for chlorinated solvent plumes. [From T.H.<br />

Wiedemeier, H. S. Rifai, C. J. Newell and J.T. Wilson,<br />

Natural Attenuation <strong>of</strong> Fuels and Chlorinated <strong>Solvents</strong><br />

in the Subsurface, after reference 88. Copyright<br />

© 1999 John Wiley & Sons, Inc. Reprinted by permission<br />

<strong>of</strong> John Wiley & Sons, Inc.]<br />

carbons, landfill leachate, or other<br />

anthropogenic carbon because these<br />

organics exert a tremendous electron-acceptor<br />

demand on the system. This condition is<br />

referred to as a Type 1 environment. In a<br />

Type 1 environment, anthropogenic carbon<br />

is fermented to produce hydrogen which<br />

drives halorespiration.<br />

The geochemistry <strong>of</strong> groundwater in a<br />

Type 1 environment is typified by strongly<br />

reducing conditions. This environment is<br />

characterized by very low concentrations <strong>of</strong><br />

dissolved oxygen, nitrate, and sulfate and elevated<br />

concentrations <strong>of</strong> Fe(II) and methane<br />

in the source zone (Figure 23.1.6). The presence<br />

<strong>of</strong> methane is almost always observed<br />

and confirms that fermentation has been occurring<br />

at the site, generating hydrogen. If<br />

measured, hydrogen concentrations are typically<br />

greater than 1 nanomolar. Importantly,<br />

a Type 1 environment results in the rapid and<br />

extensive degradation <strong>of</strong> the more<br />

highlychlorinated solvents such as PCE,<br />

TCE, and DCE: PCE → TCE → DCE → VC<br />

→ Ethene → Ethane<br />

In this type <strong>of</strong> plume, cis-1,2-DCE and<br />

VC degrade more slowly than TCE; thus,<br />

they tend to accumulate and form longer<br />

plumes (Figure 23.1.6a). In Figure 23.1.6b,<br />

the PCE declines to zero and is replaced, in<br />

sequence, by a peak in TCE concentrations,<br />

followed by a peak in cis-1,2-DCE, VC, and<br />

ethene. Fermentation constituents (BOD and<br />

acetate) and inorganics are shown in Figure<br />

23.1.6c and 23.1.6d. Figure 23.1.6d illustrates how the fermentation substrate (represented<br />

by BOD) extends beyond the source before being consumed. Both panels show long chloride<br />

and methane plumes extending far downgradient from the plume area, because chloride<br />

is conservative and methane cannot be biodegraded in an anaerobic environment. The acetate<br />

curve indicates where active primary fermentation is occurring; declining acetate concentrations<br />

are due to consumption by methanogens in the plume area.<br />

23.1.5.2.2 Type 2<br />

The classification system <strong>of</strong> Wiedemeier et a1. 107 recognized that anaerobic conditions may<br />

also result from the fermentation <strong>of</strong> naturally-occurring organic material in the groundwater<br />

that flows through chlorinated solvent source zones. This Type 2 environment occurs in<br />

hydrogeologic settings that have inherently high organic carbon concentrations, such as<br />

coastal or stream/river deposits with high concentrations <strong>of</strong> organics, shallow aquifers with

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