Response Surface Method for the Optimization of Pseudomonas sp. strain DrY135 Growth on Acrylamide as a Nitrogen Source

Authors

  • Garba Uba Department of Science Laboratory Technology, College of Science and Technology, Jigawa State Polytechnic, Dutse, PMB 7040, Nigeria.
  • Motharasan Manogaran Malaysia Genome and Vaccine Institute (MGVI) National Institute of Biotechnolgy Malaysia (NIBM) Jalan Bangi, 43000 Kajang, Selangor, Malaysia.
  • Motharasan Manogaran Malaysia Genome and Vaccine Institute (MGVI) National Institute of Biotechnolgy Malaysia (NIBM) Jalan Bangi, 43000 Kajang, Selangor, Malaysia.
  • Hafeez Muhammad Yakasai Department of Biochemistry, Faculty of Basic Medical Sciences, College of Health Sciences, Bayero University Kano, Nigeria.
  • Nur Adeela Yasid Department of Biochemistry, Faculty of Biotechnology and Biomolecular Sciences, Universiti Putra Malaysia, 43400 UPM Serdang, Selangor, D.E, Malaysia.
  • Mohd Yunus Shukor Department of Biochemistry, Faculty of Biotechnology and Biomolecular Sciences, Universiti Putra Malaysia, 43400 UPM Serdang, Selangor, D.E, Malaysia.

DOI:

https://doi.org/10.54987/bessm.v6i2.745

Keywords:

Acrylamide, Pseudomonas sp., Box Behnken, Bioremediation, RSM

Abstract

Acrylamide pollution and contamination can come from a variety of sources and is an emerging toxic pollutant that need remediation. A molybdenum-reducing bacteria that had been previously isolated and demonstrated the ability to degrade amides was further studied of its critical parameters contributing to optimum growth on acrylamide. The Box-Behnken design was utilized in optimizing the three previously identified significant components (pH, incubation time and acrylamide concentration). ANOVA, the pertubation's plot, and several other diagnostic plots were utilized in the analysis of the significant factors or parameters that contributed. The model was supported by the diagnostic plots including the half-normal, Cook's distance, leverage vs runs,  residual vs runs, Box-Cox, DFFITS, and DFBETAS. Conditions that were predicted to be optimal were found and analyzed in order to find the optimal growth given the factors that were used and to determine the optimal concentration, which was 1 g/L. The solutions for finding the optimal growth predicted a growth maximum of 12.055 Log CFU/mL (95 percent confidence interval (C.I.) from 11.550 to 12.593), and verification using experimental results resulted in a growth of 12.908 Log CFU/mL (12.744 to 13.072) with the results being close to the predicted values but was significantly higher than the predicted data. The second numerical optimization was for predicting the highest acrylamide concentration tolerable for growth and the solution shows a predicted a growth maximum of 12.055 Log CFU/mL (95 percent confidence interval from 11.550 to 12.593). This solution was  experimentally verified resulting in a growth of 12.195 Log CFU/mL (95 percent confidence interval from 11.806 to 12.584) with the actual results being in accordance with the predicted values. The results of the RSM exercise showed that growth on acrylamide may be optimized more effectively with RSM than with OFAT, which indicates that RSM is more useful than OFAT in this regard.

References

Mottram, DS, Wedzicha BL, Dobson AT. Acrylamide is formed in the Maillard reaction. Nature. 2002;419:448-9.

Zamora R, Delgado RM, Hidalgo FJ. Strecker aldehydes and ?-keto acids, produced by carbonyl-amine reactions, contribute to the formation of acrylamide. Food Chem. 2011;128(2):465-70.

Shukor MY, Gusmanizar N, Azmi NA, Hamid M, Ramli J, Shamaan NA, et al. Isolation and characterization of an acrylamide-degrading Bacillus cereus. J Enviromental Biol. 2009;30(1):57-64.

Spencer P, Schaumburg HH. Nervous system degeneration produced by acrylamide monomer. Environ Health Perspect. 1975 Jun 1;11:129-33.

Sega GA, Valdivia Alcota RP, Tancongco CP, Brimer PA. Acrylamide binding to the DNA and protamine of spermiogenic stages in the mouse and its relationship to genetic damage. Mutat Res Mutagen Relat Subj. 1989 Aug 1;216(4):221-30.

Tyl RW, Friedman MA. Effects of acrylamide on rodent reproductive performance. Reprod Toxicol. 2003 Jan 1;17(1):1-13.

Yang HJ, Lee SH, Jin Y, Choi JH, Han CH, Lee MH. Genotoxicity and toxicological effects of acrylamide on reproductive system in male rats. J Vet Sci. 2005 Jun;6(2):103-9.

Backer LC, Dearfield KL, Erexson GL, Campbell JA, Westbrook?Collins B, Allen JW. The effects of acrylamide on mouse germ-line and somatic cell chromosomes. Environ Mol Mutagen. 1989;13(3):218-26.

Hagmar L, Törnqvist M, Nordander C, Rosén I, Bruze M, Kautiainen A, et al. Health effects of occupational exposure to acrylamide using hemoglobin adducts as biomarkers of internal dose. Scand J Work Environ Health. 2001;27(4):219-26.

Igisu H, Goto I, Kawamura Y, Kato M, Izumi K. Acrylamide encephaloneuropathy due to well water pollution. J Neurol Neurosurg Psychiatry. 1975;38(6):581-4.

Eikmann T, Herr C. How dangerous is actually acrylamide exposure for the population. Umweltmed Forsch Prax. 2002;7(6):307-8.

Pruser KN, Flynn NE. Acrylamide in health and disease. Front Biosci - Sch. 2011;3 S(1):41-51.

Pennisi M, Malaguarnera G, Puglisi V, Vinciguerra L, Vacante M, Malaguarnera M. Neurotoxicity of acrylamide in exposed workers. Int J Environ Res Public Health. 2013;10(9):3843-54.

Rahim MBH, Syed MA, Shukor MY. Isolation and characterization of an acrylamide-degrading yeast Rhodotorula sp . strain MBH23 KCTC 11960BP. J Basic Microbiol. 2012;52(5):573-81.

Wakaizumi M, Yamamoto H, Fujimoto N, Ozeki K. Acrylamide degradation by filamentous fungi used in food and beverage industries. J Biosci Bioeng. 2009;108(5):391-3.

Wampler DA, Ensign SA. Photoheterotrophic metabolism of acrylamide by a newly isolated strain of Rhodopseudomonas palustris. Appl Environ Microbiol. 2005;71(10):5850-7.

Buranasilp K, Charoenpanich J. Biodegradation of acrylamide by Enterobacter aerogenes isolated from wastewater in Thailand. J Environ Sci. 2011;23(3):396-403.

Charoenpanich J, Tani A. Proteome analysis of acrylamide-induced proteins in a novel acrylamide-degrader Enterobacter aerogenes by 2D electrophoresis and MALDI-TOF-MS. Chiang Mai Univ J Nat Sci. 2014;13(1):11-22.

Gusmanizar N, Shukor Y, Ramli J, Syed MA. Isolation and characterization of an acrylamide-degrading Burkholderia sp. strain DR.Y27. J Ris Kim. 2015 Feb 11;2(1):34.

Yu F, Fu R, Xie Y, Chen W. Isolation and characterization of polyacrylamide-degrading bacteria from dewatered sludge. Int J Environ Res Public Health. 2015;12(4):4214-30.

Bedade DK, Singhal RS. Biodegradation of acrylamide by a novel isolate, Cupriavidus oxalaticus ICTDB921: Identification and characterization of the acrylamidase produced. Bioresour Technol. 2018 Aug 1;261:122-32.

Aisami A, Gusmanizar N. Characterization of an acrylamide-degrading bacterium isolated from hydrocarbon sludge. Bioremediation Sci Technol Res. 2019 Dec 28;7(2):15-9.

Othman AR, Rahim MBHA. Modelling the Growth Inhibition Kinetics of Rhodotorula sp. strain MBH23 (KCTC 11960BP) on Acrylamide. Bioremediation Sci Technol Res. 2019 Dec 28;7(2):20-5.

Rusnam, Gusmanizar N. An Acrylamide-degrading Bacterial Consortium Isolated from Volcanic Soil. J Biochem Microbiol Biotechnol. 2021 Dec 31;9(2):19-24.

Rusnam, Gusmanizar N. Characterization of An Acrylamide-degrading Bacterium Isolated from Volcanic Soil. J Environ Bioremediation Toxicol. 2022 Aug 5;5(1):32-7.

Khuri IA, Mukhopadhyay S. Response surface methodology. Adv Rev WIREs Comput Stat John Wiley Sons Inc. 2010;2:128-49.

Karamba KI, Ahmad SA, Zulkharnain A, Syed MA, Khalil KA, Shamaan NA, et al. Optimisation of biodegradation conditions for cyanide removal by Serratia marcescens strain AQ07 using one-factor-at-a-time technique and response surface methodology. Rendiconti Lincei. 2016 Sep;27(3):533-45.

Annadurai G, Ling LY, Lee J fwu. Statistical optimization of medium components and growth conditions by response surface methodology to enhance phenol degradation by Pseudomonas putida. J Hazard Mater. 2008;151:171-8.

Ibrahim S, Shukor MY, Khalil KA, Halmi MIE, Syed MA, Ahmad SA. Application of response surface methodology for optimising caffeine-degrading parameters by Leifsonia sp. strain SIU. J Environ Biol. 2015 Sep;36(5):1215-21.

Ahmad WA, Zakaria ZA, Zakaria Z, Surif S. Hexavalent Chromium Reduction at Different Growth Phases of Acinetobacter haemolyticus. 2009;26(7):1275-8.

Anderson MJ, Whitcomb PJ. RSM simplified: optimizing processes using response surface methods for design of experiments. 2nd ed. Boca Raton, FL, USA.: Productivity Press; 2016.

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Published

2022-12-31

How to Cite

Uba, G., Manogaran, M., Manogaran, M., Yakasai, H. M., Yasid, N. A., & Shukor, M. Y. (2022). Response Surface Method for the Optimization of Pseudomonas sp. strain DrY135 Growth on Acrylamide as a Nitrogen Source. Bulletin of Environmental Science and Sustainable Management (e-ISSN 2716-5353), 6(2), 23–34. https://doi.org/10.54987/bessm.v6i2.745

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