11 research outputs found
Microbial Reductive Transformation of Pentachloronitrobenzene
Pentachloronitrobenzene (PCNB) is an organochlorine fungicide used either as seed dressing or for soil treatment. Research was conducted to investigate the microbial reductive transformation of PCNB with cultures developed from a contaminated estuarine sediment. The biotransformation of PCNB to pentachloroaniline (PCA) occurred under all electron accepting conditions tested. Sequential dechlorination of PCA to di- and in some cases to mono-chlorinated anilines occurred under fermentative/methanogenic conditions. Based on the use of inhibitors, methanogens were not involved in the sequential dechlorination of PCA. Based on 16S rRNA gene analysis, among five known dechlorinating bacterial groups tested, only Dehalococcoides was detected in the mixed culture. The sequential dechlorination of PCA was simulated using a branched-chain Michaelis-Menten kinetic model. The dechlorination rate (k) of the chlorinated anilines ranged from 0.25 to 1.19 uM/day and the half-saturation coefficient (KC) ranged from 0.11 to 1.72 uM at an incubation temperature of 22C and pH 6.90.1. Incubation at different temperature and pH values resulted in significant differences in the biotransformation rate and extent of PCNB in the fermentative/methanogenic enrichment culture. Incubation at 35C resulted in significantly different product distribution. The effect of temperature on the PCA dechlorination rate was modeled using an Arrhenius relationship. Dechlorination of PCA and methanogenesis were not observed in cultures amended with completely bioavailable iron sources until all Fe3+ was reduced to Fe2+. In contrast, PCA dechlorination took place at the same time with iron reduction in the same mixed, methanogenic culture amended with a less bioavailable iron source (FeOOH). PCA was sequentially dechlorinated to dichloroanilines in cultures amended with low nitrate concentrations, whereas partial dechlorination of PCA to tetrachloroanilines was observed in cultures amended with high initial nitrate concentrations due to the accumulation of reduced nitrogen species (e.g., NO, N2O). A semi-empirical molecular model (MOPAC/AM1) was used to estimate the thermodynamic and electronic properties of all chlorinated aniline congeners. These values were used to predict the sequential PCA dechlorination pathway and compare to experimentally observed dechlorination reactions. The results of this study have significant environmental implications relative to the fate and transport of PCNB, PCA and its dechlorination products in subsurface systems.Ph.D.Committee Chair: Pavlostathis, Spyros G.; Committee Member: Huang, Ching-Hua; Committee Member: Loeffler, Frank E.; Committee Member: Mulholland, James A.; Committee Member: Sobecky, Patricia A.; Committee Member: Yiacoumi, Sotir
Acute and chronic responses of denitrifying culture to diclofenac
Acute and chronic effect as well as biodegradation potential at different sludge retention times (SRTs) of a priority pollutant, diclofenac on denitrification process was assessed. The continuous amendment of the culture for 6 months with 1 mu g/L diclofenac resulted in 30% decrease in gas production. The average diclofenac removal observed in the diclofenac-acclimated culture was less than 15%. Batch tests showed that nitrate was removed in diclofenac free-control reactor at a higher rate compared to diclofenac amended reactor. Although, SRT did not have any progressive effect on diclofenac degradation, the system operated at low SRT was more sensitive to diclofenac and resulted in an increase in N2O emission. Wastewater treatment plants (WWTPs) operated at higher SRTs may tolerate and recover from the adverse effects of such micropollutants. The study can lead to other researchers to understand the fate and effect of other emerging pollutants in the anoxic unit of WWTPs. (C) 2014 Elsevier Ltd. All rights reserved
Optimization of diclofenac quantification from wastewater treatment plant sludge by ultrasonication assisted extraction
A rapid quantification method of diclofenac from sludge samples through ultrasonication assisted extraction and solid phase extraction (SPE) was developed and used for the quantification of diclofenac concentrations in sludge samples with liquid chromatography/tandem mass spectrometry (LC MS/MS). Although the concentration of diclofenac in sludge samples taken from different units of wastewater treatment plants in Istanbul was below the limit of quantification (LOQ; 5 ng/g), an optimized method for sludge samples along with the total mass balances in a wastewater treatment plant can be used to determine the phase with which diclofenac is mostly associated. Hence, the results will provide information on fate and transport of diclofenac, as well as on the necessity of alternative removal processes. In addition, since the optimization procedure is provided in detail, it is possible for other researchers to use this procedure as a starting point for the determination of other emerging pollutants in wastewater sludge samples. (c) 2014 Elsevier B.V. All rights reserved
Influence of quaternary ammonium compounds on the microbial reductive dechlorination of pentachloroaniline
Impact of ultrasonic pre-treatment on domestic sludge digestion performance and microbial community dynamics
Seasonal variation of diclofenac concentration and its relation with wastewater characteristics at two municipal wastewater treatment plants in Turkey
The pharmaceutically active compound diclofenac has been monitored during one year at separate treatment units of two municipal wastewater treatment plants (WWTPs) to evaluate its seasonal variation and the removal efficiency. Conventional wastewater characterization was also performed to assess the possible relationship between conventional parameters and diclofenac. Diclofenac concentrations in the influent and effluent of both WWTPs were detected in the range of 295-1376 and 119-1012 ng/L, respectively. Results indicated that the higher diclofenac removal efficiency was observed in summer season in both WWTPs. Although a consistency in diclofenac removal was observed in WWTP_1, significant fluctuation was observed at WWTP_2 based on seasonal evaluation. The main removal mechanism of diclofenac in the WWTPs was most often biological (55%), followed by UV disinfection (27%). When diclofenac removal was evaluated in terms of the treatment units in WWTPs, a significant increase was achieved at the treatment plant including UV disinfection unit. Based on the statistical analysis, higher correlation was observed between diclofenac and suspended solids concentrations among conventional parameters in the influent whereas the removal of diclofenac was highly correlated with nitrogen removal efficiency. (C) 2014 Elsevier B.V. All rights reserved