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Natural Attenuation of BTEX Compounds: Model Development and Field‐Scale Application
Author(s) -
Lu Guoping,
Clement T. Prabhakar,
Zheng Chunmiao,
Wiedemeier Todd H.
Publication year - 1999
Publication title -
groundwater
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.84
H-Index - 94
eISSN - 1745-6584
pISSN - 0017-467X
DOI - 10.1111/j.1745-6584.1999.tb01163.x
Subject(s) - btex , aquifer , environmental chemistry , chemistry , hydraulic conductivity , nitrate , sulfate , xylene , environmental science , environmental engineering , benzene , groundwater , soil science , geology , geotechnical engineering , organic chemistry , soil water
Benzene, toluene, ethyl benzene and xylene (BTEX) dissolved into ground water and migrated from a light nonaqueous phase liquid (LNAPL) source in a sandy aquifer near a petroleum, oil, and lubricants (POL) facility at Hill Air Force Base (AFB), Utah. Field observations indicated that microbially mediated BTEX degradation using multiple terminal electron‐accepting processes including aerobic respiration, denitrification, Fe(III) reduction, sulfate reduction, and methanogenesis has occurred in the aquifer. To study the transport and transformation of dissolved BTEX compounds under natural conditions, a reactive flow and transport model incorporating biochemical multispecies interactions and BTEX was developed. The BTEX, oxygen, nitrate, Fe(II), sulfate, and methane plumes calculated by the model agree reasonably well with field observations. The first‐order biodegrada‐tion rate constants, estimated based on model calibration are 0.051, 0.031, 0.005, 0.004, and 0.002 day −1 for aerobic respiration, denitrification, Fe(III), sulfate reduction, and methanogenesis, respectively. The results of a sensitivity analysis show that the saturated aquifer thickness, hydraulic conductivity, and reaction rate constants are the most critical parameters controlling the natural attenuation of BTEX at this site. The hydraulic conductivity and aquifer thickness were found to be the key factors affecting the restoration of oxygen, nitrate, and sulfate after their interaction with the BTEX plume. The multispecies reactive transport modeling effort, describing BTEX degradation mediated by multiple electron‐accepting processes, represents one of the few attempts to date to quantify a complete sequence of natural attenuation processes with a detailed field data set. Because the case study is representative of many petroleum‐product contaminated sites, the results and insights obtained from this study are of general interest and relevance to other fuel‐hydrocarbon natural attenuation sites