Successful design and operation of a bioremediation process for soil contaminated with crude petroleum requires an in-depth understanding of the type of microorganisms involved, the specific reaction they perform, the factors that affect their performance, and their bioremediation kinetics. This paper attempts to develop the kinetic model for the pH being one of the major environmental factors that influence the bioavailability of contaminants, the availability of other nutrients, the activity of biological processes and hence the overall bioremediation kinetics of crude-petroleum contaminated soil. The pH model have been developed at the chemical and mathematical level with the basic assumptions that i) all side chains necessary for catalysis are in the correct protonation state; ii) an enzyme can exist in three degrees of protonation; iii) only one form of the enzyme is capable of binding substrate and catalyzing the reaction; and iv) the substrate is in great enough excess such that the equilibrium constant for the protonation of the free enzyme is the same as for the enzyme-substrate complex. The resulting model equations enable to obtain values of the equilibrium constants (K1 and K2) which are significant in determination of the optimal pH for bioremediation reaction rate.
| Published in | American Journal of Chemical Engineering (Volume 1, Issue 1) |
| DOI | 10.11648/j.ajche.20130101.12 |
| Page(s) | 6-10 |
| Creative Commons |
This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited. |
| Copyright |
Copyright © The Author(s), 2024. Published by Science Publishing Group |
Bioremediation, Crude-Petroleum, Kinetic Model, pH
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APA Style
G. A. O. Ajoku, M. K. Oduola. (2013). Kinetic Model of pH effect on Bioremediation of Crude Petroleum Contaminated Soil. 1. Model Development. American Journal of Chemical Engineering, 1(1), 6-10. https://doi.org/10.11648/j.ajche.20130101.12
ACS Style
G. A. O. Ajoku; M. K. Oduola. Kinetic Model of pH effect on Bioremediation of Crude Petroleum Contaminated Soil. 1. Model Development. Am. J. Chem. Eng. 2013, 1(1), 6-10. doi: 10.11648/j.ajche.20130101.12
AMA Style
G. A. O. Ajoku, M. K. Oduola. Kinetic Model of pH effect on Bioremediation of Crude Petroleum Contaminated Soil. 1. Model Development. Am J Chem Eng. 2013;1(1):6-10. doi: 10.11648/j.ajche.20130101.12
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Download@article{10.11648/j.ajche.20130101.12,
author = {G. A. O. Ajoku and M. K. Oduola},
title = {Kinetic Model of pH effect on Bioremediation of Crude Petroleum Contaminated Soil. 1. Model Development},
journal = {American Journal of Chemical Engineering},
volume = {1},
number = {1},
pages = {6-10},
doi = {10.11648/j.ajche.20130101.12},
url = {https://doi.org/10.11648/j.ajche.20130101.12},
eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ajche.20130101.12},
abstract = {Successful design and operation of a bioremediation process for soil contaminated with crude petroleum requires an in-depth understanding of the type of microorganisms involved, the specific reaction they perform, the factors that affect their performance, and their bioremediation kinetics. This paper attempts to develop the kinetic model for the pH being one of the major environmental factors that influence the bioavailability of contaminants, the availability of other nutrients, the activity of biological processes and hence the overall bioremediation kinetics of crude-petroleum contaminated soil. The pH model have been developed at the chemical and mathematical level with the basic assumptions that i) all side chains necessary for catalysis are in the correct protonation state; ii) an enzyme can exist in three degrees of protonation; iii) only one form of the enzyme is capable of binding substrate and catalyzing the reaction; and iv) the substrate is in great enough excess such that the equilibrium constant for the protonation of the free enzyme is the same as for the enzyme-substrate complex. The resulting model equations enable to obtain values of the equilibrium constants (K1 and K2) which are significant in determination of the optimal pH for bioremediation reaction rate.},
year = {2013}
}
TY - JOUR T1 - Kinetic Model of pH effect on Bioremediation of Crude Petroleum Contaminated Soil. 1. Model Development AU - G. A. O. Ajoku AU - M. K. Oduola Y1 - 2013/06/10 PY - 2013 N1 - https://doi.org/10.11648/j.ajche.20130101.12 DO - 10.11648/j.ajche.20130101.12 T2 - American Journal of Chemical Engineering JF - American Journal of Chemical Engineering JO - American Journal of Chemical Engineering SP - 6 EP - 10 PB - Science Publishing Group SN - 2330-8613 UR - https://doi.org/10.11648/j.ajche.20130101.12 AB - Successful design and operation of a bioremediation process for soil contaminated with crude petroleum requires an in-depth understanding of the type of microorganisms involved, the specific reaction they perform, the factors that affect their performance, and their bioremediation kinetics. This paper attempts to develop the kinetic model for the pH being one of the major environmental factors that influence the bioavailability of contaminants, the availability of other nutrients, the activity of biological processes and hence the overall bioremediation kinetics of crude-petroleum contaminated soil. The pH model have been developed at the chemical and mathematical level with the basic assumptions that i) all side chains necessary for catalysis are in the correct protonation state; ii) an enzyme can exist in three degrees of protonation; iii) only one form of the enzyme is capable of binding substrate and catalyzing the reaction; and iv) the substrate is in great enough excess such that the equilibrium constant for the protonation of the free enzyme is the same as for the enzyme-substrate complex. The resulting model equations enable to obtain values of the equilibrium constants (K1 and K2) which are significant in determination of the optimal pH for bioremediation reaction rate. VL - 1 IS - 1 ER -
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