Life cycle assessment of the environmental impact of biosurfactant production from oil waste by a diculture of azotobacter vinelandii and pseudomonas sp.

 

Table Of Contents


Chapter ONE

INTRODUCTION

  • 1.1Introduction
  • 1.2Background of Study
  • 1.3Problem Statement
  • 1.4Objective of Study
  • 1.5Limitation of Study
  • 1.6Scope of Study
  • 1.7Significance of Study
  • 1.8Structure of the Research
  • 1.9Definition of Terms

Chapter TWO

LITERATURE REVIEW

  • 2.1Overview of Biosurfactants
  • 2.2Production Methods of Biosurfactants
  • 2.3Environmental Impact of Biosurfactant Production
  • 2.4Role of Azotobacter Vinelandii in Biosurfactant Production
  • 2.5Role of Pseudomonas sp. in Biosurfactant Production
  • 2.6Applications of Biosurfactants
  • 2.7Market Trends of Biosurfactants
  • 2.8Regulations and Policies on Biosurfactants
  • 2.9Challenges in Biosurfactant Production
  • 2.10Future Prospects in Biosurfactant Research

Chapter THREE

RESEARCH METHODOLOGY

  • 3.1Research Design and Methodology
  • 3.2Sampling Techniques
  • 3.3Data Collection Methods
  • 3.4Data Analysis Techniques
  • 3.5Experimental Setup
  • 3.6Variables and Parameters
  • 3.7Quality Control Measures
  • 3.8Ethical Considerations

Chapter FOUR

DATA PRESENTATION AND ANALYSIS

  • 4.1Overview of Research Findings
  • 4.2Analysis of Environmental Impact Assessment
  • 4.3Comparison of Biosurfactant Production Methods
  • 4.4Impact of Azotobacter Vinelandii and Pseudomonas sp. in Production
  • 4.5Cost Analysis of Biosurfactant Production
  • 4.6Sustainability Assessment of Biosurfactant Production
  • 4.7Recommendations for Improvement
  • 4.8Implications for Future Research

Chapter FIVE

SUMMARY, CONCLUSION AND RECOMMENDATIONS

  • 5.1Summary of Findings
  • 5.2Conclusion
  • 5.3Contributions to Knowledge
  • 5.4Practical Implications
  • 5.5Recommendations for Further Research

Project Abstract

<p> During the bioprocess of the biosurfactant production (by the consortium), the volume of CO2 evolved was 28.23 ± 5.08 cm3, which is equivalent to 0.056 ± 0.01g CO2 per 100 ml of broth. In terms of gCO2/1000Kg biosurfactant, this gave a value of 4545 ± 817.93g CO2 in this bioprocess. Following from above, the life cycle impact assessment (LCIA) of biosurfactant production by this consortium, based on global warming potential (GWP) was 0.046 tonnes/1000Kg biosurfactant. Other impact values calculated for acidification and eutrophication potentials were 0.008 tonnes / 1000 Kg and 0.0014 tonnes/1000Kg of biosurfactant. These values were considered insufficient in terms of environmental pollution when compared with the regular methods of surfactants production. In this work also, the consortium of Pseudomonas sp/Azotobacter vinelandii produced 1.22 ± 0.04 mg biosurfactant per 100ml of cell – free broth. However, the individual organisms (Pseudomonas sp. and Azotobacter vinelandii) produced 1.03 ± 0.02 and 0.08 ± 0.001 mg of biosurfactants per 100 ml cell – free broth respectively. The microbial growth kinetics during the production of the biosurfactant by the consortium gave a specific maximum growth (µmax) of 1.306 ± 0.201 hr-1), a saturation constant (Ks) of 0.017 ± 0.007 mg/l, an Inhibition constant (Ki) of 121.83 ± 21.18 mg/land a Death constant (Kd) of 0.017 ± 0.006 mg/l. These values when compared with those of individual organisms shows that using a consortium for the bioprocess is more sustainable. <br></p>

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