Skip navigation
  • Home
  • Browse
    • Communities
      & Collections
    • Browse Items by:
    • Publication Date
    • Author
    • Title
    • Subject
    • Department
  • Sign on to:
    • My MacSphere
    • Receive email
      updates
    • Edit Profile


McMaster University Home Page
  1. MacSphere
  2. Open Access Dissertations and Theses Community
  3. Open Access Dissertations and Theses
Please use this identifier to cite or link to this item: http://hdl.handle.net/11375/31634
Full metadata record
DC FieldValueLanguage
dc.contributor.advisorAwolayo, Adedapo-
dc.contributor.authorUnokiwedi, Ogugua-
dc.date.accessioned2025-05-06T17:15:27Z-
dc.date.available2025-05-06T17:15:27Z-
dc.date.issued2025-
dc.identifier.urihttp://hdl.handle.net/11375/31634-
dc.description.abstractThe sustainability of nuclear energy critically depends on the secure management of high-level radioactive waste. Underground multi-barrier waste isolation systems, also known as deep geological repositories (DGRs), are considered the most viable solution for safe and efficient nuclear waste disposal. Significant uncertainties, however, remain regarding the long-term bio-physicochemical evolution of the near-field and its influence on waste isolation performance. In particular, Microbial-Influenced Corrosion (MIC) of copper-coated canisters, driven by the presence of sulphate-reducing bacteria, poses a sparsely constrained threat to repository integrity. This thesis presents an integrative synthesis of existing literature regarding DGR design concepts, near-field components, and evolution. In addition, it presents a process-based reactive transport model simulating MIC mechanisms in a Canadian DGR (crystalline rock). The model integrates microbial population kinetics, sulphate reduction pathways, sulphide generation, copper canister corrosion, and the eventual radionuclide release. A parametric sensitivity analysis was also conducted to evaluate the effect of key reactive transport parameters on sulphide generation and transport. The findings reveal that diffusive transport and microbial sulphate reduction rates are dominant drivers of copper corrosion, with elevated parameter combinations leading to canister failure at approximately 420,000 years. Post-failure simulations, considering pessimistic scenarios with negligible radionuclide inhibition in the host rock, predict rapid release of key radionuclides (notably 135Cs and 129I), governed by their solubility limits and solid phase fractions. This study highlights the importance of coupling biological and geochemical interactions in long-term DGR safety assessments, resulting in the development of a robust and comprehensive safety assessment frameworks for ensuring the long-term safety and integrity of nuclear waste disposal systems.en_US
dc.language.isoenen_US
dc.subjectNuclear waste managementen_US
dc.subjectradionuclide migrationen_US
dc.subjectdeep geological repositoryen_US
dc.subjectsulphate reducing bacterialen_US
dc.subjectcanister corrosionen_US
dc.subjectmicrobial-influenced corrosionen_US
dc.titleINVESTIGATION OF THE NEAR-FIELD EVOLUTION IN DEEP GEOLOGICAL REPOSITORIES AND ITS IMPLICATIONS FOR LONG-TERM NUCLEAR WASTE DISPOSALen_US
dc.typeThesisen_US
dc.contributor.departmentCivil Engineeringen_US
dc.description.degreetypeThesisen_US
dc.description.degreeMaster of Applied Science (MASc)en_US
dc.description.layabstractThe safe management of radioactive waste generated from nuclear energy operations is a major challenge for long-term sustainability. One promising solution is to place this waste deep underground in specially designed isolation systems, where multiple layers of natural and engineered barriers help to keep the waste away from the environment. This research focuses on investigating the processes that occur within the disposal system and how they affect disposal performance. A key risk to the disposal system is the potential for bacteria to produce harmful chemicals that could corrode the metal containers holding the waste. With the use of a numerical modelling framework, this study explores how these bacteria, under certain conditions, might create substances that damage the copper container and eventually allow radioactive materials to escape. The results show that if certain conditions are met, such as faster chemical reaction rates or easier movement of substances through the ground, container failure could occur hundreds of thousands of years after burial. Following copper failure, certain radioactive elements could be released more quickly than expected. This study emphasizes the importance of understanding the interactions between biological and chemical systems deep underground, helping scientists and engineers design safer systems to protect people and the environment from radioactive exposure.en_US
Appears in Collections:Open Access Dissertations and Theses

Files in This Item:
File Description SizeFormat 
unokiwedi_ogugua_p_finalsubmission2025april_masc.pdf
Embargoed until: 2026-04-25
6.13 MBAdobe PDFView/Open
Show simple item record Statistics


Items in MacSphere are protected by copyright, with all rights reserved, unless otherwise indicated.

Sherman Centre for Digital Scholarship     McMaster University Libraries
©2022 McMaster University, 1280 Main Street West, Hamilton, Ontario L8S 4L8 | 905-525-9140 | Contact Us | Terms of Use & Privacy Policy | Feedback

Report Accessibility Issue