PHYTOCHEMICAL ANALYSIS OF CLEOME VISCOSA.

 

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 Phytochemicals
  • 2.2Importance of Phytochemical Analysis
  • 2.3Cleome Viscosa: Botanical Description
  • 2.4Phytochemical Components of Cleome Viscosa
  • 2.5Previous Studies on Cleome Viscosa
  • 2.6Methods of Phytochemical Analysis
  • 2.7Techniques for Phytochemical Extraction
  • 2.8Analytical Instruments for Phytochemical Analysis
  • 2.9Significance of Phytochemical Analysis
  • 2.10Future Trends in Phytochemical Research

Chapter THREE

RESEARCH METHODOLOGY

  • 3.1Research Design
  • 3.2Sampling Methods
  • 3.3Data Collection Procedures
  • 3.4Data Analysis Techniques
  • 3.5Experimental Setup
  • 3.6Variables and Controls
  • 3.7Ethical Considerations
  • 3.8Reliability and Validity

Chapter FOUR

DATA PRESENTATION AND ANALYSIS

  • 4.1Phytochemical Analysis Results
  • 4.2Comparison with Previous Studies
  • 4.3Interpretation of Findings
  • 4.4Discussion on Phytochemical Components
  • 4.5Implications of Results
  • 4.6Limitations of the Study
  • 4.7Recommendations for Further Research
  • 4.8Practical Applications of Findings

Chapter FIVE

SUMMARY, CONCLUSION AND RECOMMENDATIONS

  • 5.1Summary of Findings
  • 5.2Conclusion
  • 5.3Implications for the Field
  • 5.4Contributions to Knowledge
  • 5.5Recommendations

Project Abstract

<p> </p><p><strong>A</strong><strong>B</strong><strong>S</strong><strong>T</strong><strong>R</strong><strong>A</strong><strong>C</strong><strong>T</strong></p><p>This study is undertaken to measure the variation of terrestrial gamma radiation and the</p><p>activity concentrations of U-238, Th-232 and K-40 in soil of Northern part of Zamfara State (Nigeria), and assess the potential health hazards associated with the exposures to the natural radiation in the area with respect to geological formations. Inspector AlertTM Nuclear Radiation Monitor and HPGe gamma ray spectrometer were used for TGRD and laboratory analyses respectively. The measured TGRD rates ranged from 20.00 to 61.43 nGy/h, with mean value of 31.99 nGy/h. The mean (range) activity concentrations of U-238, Th-232 and K-40 in the soil samples were 19.43 ± 2.23 (8.82 ± 0.95 to 44.22 ± 5.78) Bq/kg, 23.26 ± 8.43 (11.02 ± 1.03 to 43.96 ± 2.15) Bq/kg and 268.62 ± 39.03 (57.45 ± 2.88 to 527.36 ± 12.38) Bq/kg respectively. These results were compared with the world average values for specific activities (i.e. 33, 45 and 420 Bq/kg) for U-238, Th-232 and K-40 respectively, and were found to be less than the worldwide average. The highest TGRD rate and activity concentrations of U-238, Th-232 and K-40 were recorded in an area underlain by Older Granite formation, which are enriched with high contents of radioactive materials. The radiological hazards to the public in the studied area was assessed by estimating mean values of radium equivalent activity, external hazard index, and activity utilization index for the soil samples were found to be 71.674± 7.099 Bq/kg, 0.1936± 0.0192, and 0.4688± 0.0448 respectively.In addition, the mean values of absorbed gamma dose rates, annual outdoors effective dose rates, and excess lifetime cancer risk for both TGRD rate measurements and spectrometric analyses were found to be 31.99 nGy/h, 0.0393 mSv/y and 137.6x10-6, and 33.467</p><br> <br><p></p>

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