Abstract
Biodegradation of pyridine by a novel bacterial strain, Rhizobium sp. NJUST18, was studied in batch experiments over a wide concentration range (from 100 to 1,000 mg l−1). Pyridine inhibited both growth of Rhizobium sp. NJUST18 and biodegradation of pyridine. The Haldane model could be fitted to the growth kinetics data well with the kinetic constants μ* = 0.1473 h−1, K s = 793.97 mg l−1, K i = 268.60 mg l−1 and S m = 461.80 mg l−1. The true μ max, calculated from μ*, was found to be 0.0332 h−1. Yield coefficient Y X/S depended on S i and reached a maximum of 0.51 g g−1 at S i of 600 mg l−1. V max was calculated by fitting the pyridine consumption data with the Gompertz model. V max increased with initial pyridine concentration up to 14.809 mg l−1 h−1. The q S values, calculated from \(V_{ \hbox{max} }\), were fitted with the Haldane equation, yielding q Smax = 0.1212 g g−1 h−1 and q* = 0.3874 g g−1 h−1 at S m′ = 507.83 mg l−1, K s′ = 558.03 mg l−1, and K i′ = 462.15 mg l−1. Inhibition constants for growth and degradation rate value were in the same range. Compared with other pyridine degraders, μ max and S m obtained for Rhizobium sp. NJUST18 were relatively high. High K i and K i′ values and extremely high K s and K s′ values indicated that NJUST18 was able to grow on pyridine within a wide concentration range, especially at relatively high concentrations.
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Abbreviations
- K :
-
Fitting parameter of the Gompertz model (h−1)
- K i :
-
Inhibition coefficient for Haldane’s growth kinetics (mg l−1)
- K s :
-
Half saturation coefficient for Haldane’s growth kinetics (mg l−1)
- K i′:
-
Inhibition coefficient for Haldane’s degradation kinetics (mg l−1)
- K s′:
-
Half saturation coefficient for Haldane’s degradation kinetics (mg l−1)
- q S :
-
Specific degradation rate (g g−1 h−1)
- q S*:
-
Apparent maximum specific degradation rate (g g−1 h−1)
- q Smax :
-
True maximum specific degradation rate (g g−1 h−1)
- S s :
-
Pyridine concentration (mg l−1)
- S c :
-
Pyridine consumed (mg l−1)
- S i :
-
Initial pyridine concentration (mg l−1)
- S m :
-
Pyridine concentration at which μ = μ max (mg l−1)
- S m′:
-
Pyridine concentration at which q S = q Smax (mg l−1)
- t :
-
Time of incubation (h)
- t opt :
-
Time of maximum pyridine degradation rate (h)
- V max :
-
Maximum volumetric rate of pyridine degradation (mg l−1 h−1)
- X :
-
Concentration of biomass (mg l−1)
- X opt :
-
Concentration of biomass at t opt (mg l−1)
- Y X/S :
-
Yield coefficient [g biomass (g substrate)−1]
- α, β :
-
Fitting parameter of the Gompertz model (mg l−1)
- μ :
-
Specific growth rate (h−1)
- μ*:
-
Apparent maximum specific growth rate (h−1)
- μ max :
-
True maximum specific growth rate (h−1)
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Acknowldgments
This research is financed by Major Project of Water Pollution Control and Management Technology of P. R. China (No. 2012ZX07101-003-001), National Natural Science Foundation of China (No. 51208258, 51378261 and 51348007), Natural Science Foundation of Jiangsu Province (No. BK2011717), Research Fund for the Doctoral Program of Higher Education of China (20123219120009), Environmental Protection Scientific Research Project of Jiangsu Province (201103), Fundamental Research Funds for the Central Universities (No.30920130122007) and Zijing Intelligent Program (No. 2013-ZJ-02-19).
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Shen, J., Zhang, X., Chen, D. et al. Kinetics study of pyridine biodegradation by a novel bacterial strain, Rhizobium sp. NJUST18. Bioprocess Biosyst Eng 37, 1185–1192 (2014). https://doi.org/10.1007/s00449-013-1089-x
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DOI: https://doi.org/10.1007/s00449-013-1089-x