Carbon Tetrachloride Degradation Results for 200-ZP-1 Operable Unit

Bagwell, Christopher E.; Wang, Guohui; Saunders, Danielle L. (ORCID:0000000170600915); Heal, Katherine R.; Kugler, Alex J.; Torgeson, Joshua M.; Brooks, Shelby M.; Escobedo Avalos, Nancy M. (ORCID:0000000180734642); Robinson, Judith L.

doi:10.2172/3684050

DOE OSTI · 3684050

Carbon Tetrachloride Degradation Results for 200-ZP-1 Operable Unit

Bagwell, Christopher E.·Wang, Guohui·Saunders, Danielle L. (ORCID:0000000170600915)·Heal, Katherine R.·Kugler, Alex J.·Torgeson, Joshua M.·Brooks, Shelby M.·Escobedo Avalos, Nancy M. (ORCID:0000000180734642)·Robinson, Judith L.

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Abstract

Carbon tetrachloride (CT) contamination in the 200-ZP-1 Operable Unit (OU) at the Hanford Site originated from large-volume discharges to the subsurface during plutonium production operations between 1955 and 1973. Contamination migrated through more than 70 meters of unsaturated sediment to reach the underlying unconfined aquifer, where it persists as a large and complex groundwater plume. The 200-ZP-1 OU Record of Decision (ROD) requires that groundwater CT concentrations be reduced to 3.4 µg/L within 125 years. Current groundwater modeling projections estimate that the existing pump-and-treat, even when combined with monitored natural attenuation (specifically hydrolysis), will not achieve this target within the designated timeframe. A fundamental contributor to this shortfall is the extremely slow rate of CT hydrolysis under Hanford aquifer conditions, which has been estimated to have a half-life of 630 years. If faster-acting biotic and abiotic degradation processes are operating within the aquifer, their contribution to CT mass reduction could have a meaningful impact. However, site-specific measurements of these processes and their rates have not previously been performed. This report documents the results of a two-phase laboratory investigation designed to characterize and quantify the capacity of site-specific 200-ZP-1 OU sediments and groundwater to support natural attenuation of CT through biotic and abiotic pathways. In this context, degradation capacity is defined as the intrinsic potential of the subsurface matrix to transform CT under optimized, controlled conditions. System capacity is evaluated in two ways: (1) as rate-limited capacity, which establishes the maximum kinetic velocity of CT transformation and is measured using half-lives and first order rate constants; and (2) as mass limited capacity, which defines the total contaminant mass the batch experimental system can degrade before reactants are exhausted, representing the maximum amount of contaminant the microbial community and reactive mineral phases can transform under the experimental conditions.

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Bagwell, Christopher E., Wang, Guohui, Saunders, Danielle L. (ORCID:0000000170600915), Heal, Katherine R., Kugler, Alex J., Torgeson, Joshua M., Brooks, Shelby M., Escobedo Avalos, Nancy M. (ORCID:0000000180734642), Robinson, Judith L.. 2026-08-31. Carbon Tetrachloride Degradation Results for 200-ZP-1 Operable Unit. https://doi.org/10.2172/3684050

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