Abstract:SummaryIt is conventional to describe the relationship between the specific rate of microbial growth and the concentration of the inhibitory substrate in terms of the Andrews-Edwards equation. A novel method for establishing the constants of this equation is presented. The equation is transformed to a polynomial and the empirical data are approximated by a quadratic polynomial. The results obtained for the biodegradation of phenol in a mixed culture (activated sludge) are discussed.
“…The growth kinetic parameters derived were: H , , ,~~ = 0.365 h-', K, = 10.948 x kg/m3, and Ki = 1 13.00 x kg/m3. These numerical values are very close to those reported in literature for mixed cultures growing on phe- no1 (D'Adamo et al, 1984;Szetela and Winnicki, 1981;Pawlowsky and Howell, 1973). The double-substrate limiting kinetics used in the biofilm model assumes that phenol and oxygen are limiting substrates.…”
Section: Evaluation Of Biokinetie Parameterssupporting
Experiments on phenol biodegradation by a mixed culture in a drafttube, three-phase fluidized-bed biofilm reactor (DTFBR) at the steady state were performed. The characteristics of biofilms developed in the DTFBR were identified. A steady state biofilm model was proposed that considers the simultaneous diffusion and reaction of oxygen and phenol within the biofilm and the external mass transfer resistance between the biofilm and the completely mixed bulk liquid phase. The proposed model assumes a double-substrate limiting mechanism for microbial growth kinetics, and Haldane and Monod type expressions were used to characterize the dependence of microbial specific growth rate on phenol and oxygen, respectively. The experimental results were used to test the validity of the proposed model.
“…The growth kinetic parameters derived were: H , , ,~~ = 0.365 h-', K, = 10.948 x kg/m3, and Ki = 1 13.00 x kg/m3. These numerical values are very close to those reported in literature for mixed cultures growing on phe- no1 (D'Adamo et al, 1984;Szetela and Winnicki, 1981;Pawlowsky and Howell, 1973). The double-substrate limiting kinetics used in the biofilm model assumes that phenol and oxygen are limiting substrates.…”
Section: Evaluation Of Biokinetie Parameterssupporting
Experiments on phenol biodegradation by a mixed culture in a drafttube, three-phase fluidized-bed biofilm reactor (DTFBR) at the steady state were performed. The characteristics of biofilms developed in the DTFBR were identified. A steady state biofilm model was proposed that considers the simultaneous diffusion and reaction of oxygen and phenol within the biofilm and the external mass transfer resistance between the biofilm and the completely mixed bulk liquid phase. The proposed model assumes a double-substrate limiting mechanism for microbial growth kinetics, and Haldane and Monod type expressions were used to characterize the dependence of microbial specific growth rate on phenol and oxygen, respectively. The experimental results were used to test the validity of the proposed model.
“…Figures 1 and 3 indicate that as phenol pulse frequency increased there was a corresponding decrease in phenol removal rates. In parallel, with increasing phenol pulse frequency, there was an initial delay in batch growth, as depicted in Analytical integration of eq 4 termined values of gm, Ks, and are tabulated in Tables II and III for the first and second set of consecutive experiments, respectively. The values of KB did not change appreciably (KB values ranged 3.6-9.9 mg/L in both sets of experiments with an average value of 8.03 ± 0.85 in the first set and 7.01 ± 0.54 in the second set) with increasing phenol pulse frequency in both studies, and they are about the same for both studies.…”
Section: Mmsmentioning
confidence: 99%
“…They fitted the biodegradation data to the Haldane equation and to its modified forms classified by Edwards (3) and reported average values for pm, Kg, and for the Haldane equation as 0.26 h-1, 25.4 mg/L, and 173.0 mg/L, respectively. Szetela and Winnicki (4) reported values of the Haldane equation constants, pm, Kg, and as 0.33 hr1, 19.2 mg/L, and 229.0 mg/L, respectively, for phenol.…”
“…Phenol biodegradation by bacteria is generally inhibited by phenol itself. The Haldane and Monod equations have frequently been used to describe this degradation in pure or mixed cultures (Allsop et al 1993;Beyenal et al 1997;D'Adamo et al 1984;Hill and Robinson 1975;Lallai et al 1988;Pawlowsky and Howell 1973;Sokol 1987;Sokol and Howell 1981;Szetela and Winnicki 1981;Tang and Fan 1987;Yang and Humphrey 1975;).…”
The kinetics of phenol biodegradation by mixed culture in a batch reactor was investigated over a wide range of initial phenol concentrations (40-350 mg L -1 ). The temperature (30°C), the stirring velocity (200 rpm), mineral salt supplementation, namely NaH 2 PO 4 (3 g L -1 ), KH 2 PO 4 (3 g L -1 ), MgSO 4 (0.1 g L -1 ), (NH 4 ) 2 SO 4 (1 g L -1 ), as well as the initial pH (8) were kept constant. All experiments were carried out at a given initial bacterial concentration of 0.08 g L -1 (based on the optical density determination, 0.079). Irrespective of the culture conditions, total phenol degradation was recorded for a culture time ranging from 15.6 to 49.0 h. In addition, the optimal value of the maximum specific growth rate was observed for 125 mg L -1 of phenol. These results show the relevance of the specific microbial consortium used. The Luong equation accurately matched growth kinetics and enabled the relation between the maximum specific growth rates (μ m ) and the initial phenol concentration (S o ) to be described. It could also be used to deduce the substrate saturation coefficient (K s ) and the maximum substrate concentration (S m ) above which growth ceases. The kinetic constants of the Luong equation for phenol were m m ¼ 1:04 h À1 ; K s ¼ 153:2 mg L À1 ; S m ¼ 540 mg L À1 and n ¼ 0:9, respectively.
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