HR: 0800h
AN: H51B-0459 [Abstracts]
TI: Fate of 3-tert-Butyl-4-hydroxyanisole, 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8- hexamethylcyclopenta(g)-2-benzopyrane and chlorpyrifos in a Conventional Wastewater Treatement Plant
AU: * Thomas, S M
EM: sheeba.thomas@utsa.edu
AF: University of Texas at San Antonio, Department of Earth and Environmental Science, One
UTSA Circle, San Antonio, TX 78249, United States
AU: Bodour, A
EM: adria.bodour@utsa.edu
AF: University of Texas at San Antonio, Department of Earth and Environmental Science, One
UTSA Circle, San Antonio, TX 78249, United States
AU: Inniss, E C
EM: innisse@missouri.edu
AF: University of Missouri-Columbia, Department of Civil & Environmental Engineering,E2509
Lafferre Hall, Columbia, MO 65211, United States
AU: Murray, K E
EM: kyle.murray@utsa.edu
AF: University of Texas at San Antonio, Department of Earth and Environmental Science, One
UTSA Circle, San Antonio, TX 78249, United States
AB:
Emerging contaminants (ECs) are a major concern in the environment, particularly those found in waters.
Wastewater treatment plants (WWTPs) play a key role in reducing the concentrations in the environment because
compounds may be transformed under either aerobic or anaerobic conditions or may sorb to wastewater
sludges and therefore be removed from waters. If these ECs are not contained or treated then effluent
discharged from the WWTP and to a receiving stream may contain hazardous levels of these contaminants.
Reported here is a study of the fate of three emerging contaminants (ECs): 3-tert-Butyl-4-hydroxyanisole (BHA),
1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethylcyclopenta(g)-2-benzopyrane (HHCB) and chlorpyrifos. Experiments
were conducted on a laboratory scale by emulating conditions of a conventional WWTP in San Antonio, TX. The
goal of the research was to determine general characteristics for both sorption (to wastewater sludges) and
degradation.
The sorption experiments were performed by exposing the sludge to a variety of initial concentration of ECs for 24
hours. After exposure these three ECs were extracted and analyzed using gas chromatography followed by flame
ionization detector (GC/FID). Sorption experiments indicated that HHCB and chlorpyrifos are more hydrophobic
than BHA and, therefore, would be mostly contained in the sludges.
The degradation rates for these ECs were also considered for both aerobic and anaerobic conditions using
different bench-scale reactor setups for 21 days. The differences between the reactor setups included volume of
reactor, amount of sludge, mode of supply of nutrients and acclimatization of sludge to the ECs. One sludge was
first acclimated to EC concentrations and then used in the experiment. The acclimated reactor had reaction rate
constants approximately double that of the non-acclimated sludge reactor setups and followed first order reaction
kinetics. Aerobic degradation occurred more readily for all three compounds than anaerobic degradation.
These experiments supported the hypothesis that the WWTPs do capture and transform most of these
compounds and, therefore, limit their reach to the effluent. However it cannot be supported that the compounds in
the sludge phase are degraded to very low concentrations. Because of the changing dynamics of the sludge
phase with time, further work needs to be conducted on the influence of time on sorption coefficients and,
subsequently the effect of these temporal changes on degradation of these compounds.
DE: 0416 Biogeophysics
DE: 0496 Water quality
DE: 1806 Chemistry of fresh water
DE: 1831 Groundwater quality
DE: 1835 Hydrogeophysics
SC: Hydrology [H]
MN: 2007 Fall Meeting