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Canada’s Plan for Used Nuclear Fuel: How the Decisions Get Made

August 2026 6 min read

Every kilowatt hour Canada has generated from nuclear power since the 1960s has left behind a physical residue: ceramic uranium fuel pellets sealed in metal tubes, bundled together, and removed from the reactor once they can no longer sustain an efficient chain reaction. Those bundles are still highly radioactive when they come out. For decades the answer has been to cool them in water pools at the reactor site, then transfer them to dry storage containers on the same property. That approach is safe, licensed, and monitored, but it is not permanent. It depends on institutions continuing to exist and continuing to pay attention, which is a difficult assumption to carry across the tens of thousands of years the material remains hazardous.

Canada’s chosen answer is a deep geological repository, and after more than a decade of community engagement the country now has a proposed location in northwestern Ontario, in the Ignace area, advanced jointly with Wabigoon Lake Ojibway Nation. Nothing is built yet. What follows is a long regulatory process that will determine whether the concept survives contact with impact assessment, licensing, and continued local consent.

How Canada Classifies Radioactive Waste

Not all radioactive waste is the same, and the policy debate often blurs categories that have very different handling requirements. Canada uses four broad classes.

Class Typical material Management approach
Low level Mops, protective clothing, contaminated soils, laboratory materials Near surface disposal or engineered storage facilities
Intermediate level Reactor components, resins, filters Shielded storage, with deeper disposal under consideration
High level Used reactor fuel bundles Interim storage at reactor sites, then deep geological disposal
Uranium mine and mill tailings Residues from milling uranium ore Engineered tailings facilities with long term monitoring

Only the third category is at issue in the repository project. About three million used fuel bundles are currently in storage in Canada, and that inventory grows as reactors continue to operate. The material accounts for a small fraction of the total volume of radioactive waste in the country but the overwhelming majority of the radioactivity.

Who Holds the Responsibility

Three actors matter most, and they play distinct roles that are easy to conflate.

Provinces have a narrower role here than they do in most resource files, because nuclear energy falls under federal jurisdiction. That is a meaningful contrast with sectors where oversight is layered across both levels of government, as it is in the environmental oversight system that applies to the oil sands.

How the Site Was Chosen

The siting process was designed to be community driven rather than imposed, which is a direct response to the failure of earlier top down attempts in several countries. The sequence ran roughly as follows.

  1. Communities volunteered to learn more, with no obligation to continue. More than twenty expressed initial interest.
  2. Preliminary screening removed sites with obvious geological or logistical disqualifiers.
  3. Field studies followed in remaining areas, including borehole drilling to characterize rock formations at depth.
  4. The field narrowed over successive rounds as communities withdrew or were set aside on technical grounds.
  5. Willingness was tested through municipal votes and Indigenous community processes before a preferred site was named.

A parallel project illustrates why the consent step is not a formality. A proposed repository for low and intermediate level waste at the Bruce site in Ontario was abandoned after Saugeen Ojibway Nation voted against it. The proponent withdrew the project rather than proceed.

The Engineering Concept

A deep geological repository relies on redundant barriers rather than any single line of defence. Fuel is contained in a solid ceramic form to begin with. Bundles are placed in steel containers coated in copper, which resists corrosion in the chemically stable conditions found deep underground. Containers are surrounded by compacted bentonite clay, which swells when wet and limits water movement. All of this sits several hundred metres down in stable rock that has been isolated from surface water systems for very long periods. The design intent is that even if one barrier degrades, the others continue to perform.

Retrievability is part of the concept. Adaptive Phased Management includes a period during which fuel could be recovered if a better technology emerges or if monitoring reveals a problem.

What Still Has to Happen

Site selection is a milestone, not an authorization. A repository of this kind is a designated project under federal impact assessment law, which means it faces a full review by the Impact Assessment Agency of Canada covering environmental, health, social, and economic effects, alongside effects on Indigenous rights. That regime has itself been reshaped by litigation, as covered in our look at the Impact Assessment Act after the Supreme Court reference.

Licensing under the CNSC proceeds in stages, each requiring its own public hearing and its own safety case:

Transportation is a separate approval track and a separate source of public concern, since fuel would move from reactor sites in Ontario, Quebec, and New Brunswick to a single inland location. Packages used for this purpose are certified against impact, fire, and immersion tests before they carry anything.

What to Watch

Three things will tell you how the project is really going. First, whether continued consent holds through the assessment years, particularly as detailed effects become concrete rather than conceptual. Second, whether the geological characterization at depth confirms what preliminary drilling suggested, since an unfavourable finding at the licensing stage would be far more consequential than one found early. Third, whether the funding trust keeps pace with cost estimates, because the obligation runs for generations and underfunded closure liabilities are a recurring problem across resource sectors, a pattern visible in how reclamation standards work after extraction ends.

The honest summary is that Canada has made a decision of principle and identified a place, and has now entered the phase where that decision gets tested against evidence and against the people who would live with it.

References

  1. Government of Canada. Nuclear Fuel Waste Act. Justice Laws Website.
  2. Government of Canada. Nuclear Safety and Control Act. Justice Laws Website.
  3. Canadian Nuclear Safety Commission. Regulating Nuclear Safety in Canada.
  4. Impact Assessment Agency of Canada. Federal Impact Assessment Process.
  5. Nuclear Waste Management Organization. Adaptive Phased Management and Site Selection.

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