Melgund Recreation, Arts and Culture
Public Comments Archive

19.2.3.3 NOISE, VIBRATION AND LIGHT

Detailed Technical Assessment Report • Ref: REC-S105-5ERH

Section Synopsis

Pages: 219-221

Section 19.2.3.3 of the Initial Project Description for the Deep Geological Repository (DGR) outlines the anticipated impacts of noise, vibration, and light during construction and operation. The document identifies land clearing, blasting, and rail spur use as primary sources of disturbance. While acknowledging that these activities will alter baseline conditions, the NWMO asserts that through the application of established mitigation measures and adherence to provincial and federal guidelines (e.g., NPC-300, DFO blasting guidelines), the residual risks to the environment and human receptors will be negligible. Notably, the report admits that site-specific modelling for these factors has not yet been completed, yet it maintains a 'high confidence' rating in the effectiveness of proposed mitigations due to the project's remote location.

Community Assessment Narrative

The text exhibits a common tension found in preliminary environmental assessments: the assertion of 'negligible risk' prior to the execution of quantitative modelling. The proponent relies heavily on the 'remote location' (10-12 km from residents) as a primary buffer, which may be valid for human receptors but does not necessarily account for the sensitivities of migratory birds or Species at Risk (SAR) mentioned in the pathways of change. There is a potential logical gap where the document claims 'high confidence' in mitigation effectiveness while simultaneously stating that modelling results are required to 'inform site-specific mitigation.' This suggests that the current mitigation strategies are generic rather than tailored to the unique acoustic and seismic environment of the DGR site. Furthermore, the reliance on regulatory compliance (NPC-300) as a proxy for environmental health may overlook non-human biological sensitivities to vibration and light, which often require lower thresholds than human-centric standards.

Corrective Measures & Recommendations

The proponent must conduct comprehensive seasonal baseline acoustic and light monitoring prior to the finalization of the Environmental Impact Statement. This is critical because sound propagation in northern environments can be significantly enhanced by atmospheric inversions and snow cover, which may carry noise further than the 10-12 km buffer suggests. Detailed modelling should include 'worst-case' scenarios for blasting and rail operations to ensure that the 'negligible risk' claim is mathematically supported. Additionally, the NWMO should develop a site-specific 'Dark Sky' lighting strategy. Given the remote location, the introduction of artificial light can have disproportionate effects on nocturnal wildlife and migratory birds; simply stating the location is remote does not mitigate the attraction or disorientation effects of light on SAR. Furthermore, the proponent should establish a 'Quietude' baseline in consultation with the Wabigoon Lake Ojibway Nation (WLON). For many Indigenous communities, the value of the land is tied to the absence of industrial noise, which is a higher standard than the provincial NPC-300 human-health limits. Finally, vibration monitoring must include specific sensors near fish-bearing watercourses to validate DFO guideline compliance in real-time during the construction phase, as the geological transmission of blasting energy in Canadian Shield rock can be highly unpredictable.

On 16 February, 2026 the Impact Assessment Agency of Canada (IAAC), with input from the Canadian Nuclear Safety Commission (CNSC), published a Summary of Issues (SOI) for the proposed Deep Geological Repository (DGR) for Canada’s Used Nuclear Fuel Project, put forward by the Nuclear Waste Management Organization (NWMO). The SOI identifies the key issues that IAAC considers relevant to the federal integrated impact assessment process for the project. NWMO’s response to the SOI will assist IAAC in determining whether an impact assessment is required under section 16 of the Impact Assessment Act. If an impact assessment is required, the issues outlined in the SOI—together with NWMO’s response—will help shape the scope of the assessment and inform the continued development and finalization of the Integrated Tailored Impact Statement Guidelines and associated plans.

Alignments to IAAC Summary (SOI)

Based on a cross-reference of Melgund Township’s assessment of the proponent’s Initial Project Description against the IAAC’s February 16, 2026, Summary of Issues (SOI), there is strong alignment regarding the potential impacts of physical disturbances, though the community’s analysis identifies specific methodological flaws not explicitly detailed in the federal summary. The IAAC SOI explicitly validates the community’s concerns under the section Health, social and economic conditions, specifically within the "Health effects" category, which lists concerns regarding "changes in air, water, food quality, noise, light, stress." Furthermore, Annex A of the SOI reinforces this by noting a request for "monitoring of effects during construction and operations on... blasting." This confirms that the federal agency considers Noise, Vibration, and Light (NVL) to be material issues requiring assessment, contradicting the proponent’s preliminary assertion that these risks are negligible enough to be screened out prior to detailed modeling.

However, Melgund Township’s findings highlight a critical gap in the process that the IAAC SOI touches upon only broadly. While the IAAC SOI notes concerns regarding "limited, inaccurate, or missing baseline data" under Current use of lands and resources, the community’s analysis specifically identifies that the proponent has assigned a "negligible" risk rating and "high confidence" level before conducting the necessary site-specific modeling. This supports the IAAC’s "Project description" issue in Annex A, which questions "how uncertainty, risk, and the effectiveness of proposed mitigation measures are characterized." The community’s finding that "sensitive receptors" are currently defined too narrowly (excluding seasonal land users) provides the necessary detail to substantiate the IAAC’s broad concern regarding "Socio-economic impacts to land use" and "Impacts to harvesting and travel."

Finally, the community’s observation that human-centric noise thresholds may bias assessments for wildlife directly supports the IAAC’s key issue under Terrestrial Wildlife and their Habitat. The SOI requests "more information on levels of disturbance, displacement, or harm." Melgund Township’s analysis clarifies that a "negligible" rating for humans does not equate to negligible impact for fauna. This validates the IAAC’s concern that the current information is insufficient to determine impacts on Species at risk, particularly regarding "indirect pathways of effects" such as sensory disturbance from light and noise.

Recommendations

To address the identified gaps in data and methodology, the working group recommends that the proponent be required to complete and publicly disclose preliminary noise, vibration, and light modeling prior to the finalization of the Environmental Impact Statement guidelines. This recommendation directly addresses the IAAC’s concern regarding "Uncertainty related to project effects" and the "Health effects" associated with noise and light. By shifting the modeling to an earlier phase in the assessment, the proponent can replace "anticipated" outcomes with empirical evidence, thereby resolving the discrepancy between their "high confidence" assertions and the lack of baseline data flagged in the SOI.

Furthermore, the working group recommends a formal expansion of the definition of "sensitive receptors" to include seasonal camps, traditional harvesting areas, and migratory corridors within the 10km buffer zone, developed in consultation with local stakeholders. This action is necessary to satisfy the IAAC’s requirement to assess "Socio-economic impacts to land use" and "Impacts to harvesting and travel." This expanded definition should inform a tiered mitigation strategy that establishes specific thresholds for wildlife, ensuring that the "Species at risk" concerns identified in the SOI are managed based on ecological sensitivity rather than standard residential noise by-laws.

Key Claims

Project activities will generate noise, vibration, and light that change baseline conditions.
Mitigation strategies are well-established and supported by industry experience and regulatory guidance.
Residual effects on noise, vibration, and light are expected to be low in degree and negligible in likelihood.
The remote location of the project (10-12 km from communities) ensures noise levels remain well below applicable limits.
High confidence exists in the effectiveness of mitigation and oversight measures despite pending modelling.

Underlying Assumptions

Regulatory compliance with human-centric noise guidelines (NPC-300) is sufficient to protect all Valued Components, including wildlife.
The physical distance from human receptors is the primary determinant of impact significance.
Generic industry mitigation measures will be effective in the specific geological and atmospheric conditions of the Ignace site.
Future modelling will confirm the current preliminary assessment of 'negligible risk'.
The impact of light pollution is minimized solely by the site's remoteness, ignoring the sensitivity of dark-sky environments.

Critical Observations & Gaps

Analysis Table
Issue Identified Implication Information Required
Vibration modelling is pending, yet risk is already classified as negligible. Blasting vibration could impact the structural integrity of nearby aquatic habitats or sensitive geological features. Site-specific seismic propagation studies in the local bedrock.
The document defers specific wildlife risk screening to other sections without providing integrated thresholds here. Light and noise may disrupt the migratory patterns or nesting success of SAR birds. Species-specific noise and light sensitivity thresholds.
Reliance on provincial noise standards which do not account for cultural or spiritual values of silence. The 'quietude' of the area, valued for traditional land use, may be permanently altered. Consultation with Indigenous groups to define acceptable 'acoustic character' for the area.
Predictive conclusions are made in the absence of baseline modelling. Stakeholders may perceive the 'negligible risk' conclusion as premature. A commitment to update the risk screening once modelling results are available.

Working Group Recommendations

Human Environment (People)

Assess the specific noise and vibration impacts of the 'rail spur' and 'access road' traffic on the quality of life for residents in Dyment and Borups Corners.

The text identifies 'use of access roads and the rail spur' as sources of noise and vibration. Given that Dyment/Borups Corners are situated along the primary transportation corridor (Hwy 17) likely to connect to these access points, the community will experience these effects disproportionately compared to the 'remote' site itself. The Board must ensure the assessment covers the transportation corridor impacts on local well-being, not just the static site impacts.
HEP-062
Environment

Request a specific baseline study of 'Dark Sky' quality and ambient soundscapes within the unorganized territory to quantify the current 'remote' conditions.

The text relies on the 'remote location' to mitigate light and noise emissions. However, for Melgund, this 'remoteness' is not just a buffer; it is a critical environmental asset (silence and darkness). Without a quantified baseline of the current dark sky and quiet levels, the Proponent cannot accurately measure the 'degree of adverse effects.' Establishing this baseline is crucial to proving that even 'minimal' industrial light or noise constitutes a significant degradation of the unorganized territory's character.
ENV-039
Environment

Reject the 'Negligible Risk' and 'High Confidence' ratings for Noise, Vibration, and Light until the Proponent completes and submits the site-specific modelling admitted to be missing in Section 19.2.3.3.2.

The Initial Project Description admits that 'Noise, vibration, and light modelling have not yet been completed,' yet simultaneously assigns a 'negligible' risk rating with 'high confidence.' For the Melgund community, which relies on the pristine natural environment, accepting a conclusion without supporting data is a strategic risk. The Board must demand that the Proponent demonstrate—through data, not assumptions—that the 'remote location' is sufficient to mitigate impacts. This ensures the regulatory process remains evidence-based and prevents the Proponent from bypassing rigorous assessment of potential nuisances that could degrade the local environment.
ENV-040
Human Environment (People)

Challenge the Proponent's definition of 'sensitive receptors' and 'nearest community' to explicitly include residents and seasonal dwellings within the unorganized territory of Melgund (Dyment/Borups Corners).

The Proponent's submission cites the project's location as 'about 10 km from the nearest community' and '12 km from closest WLON resident' as the primary justification for claiming negligible effects. This definition appears to overlook the unorganized territory of Melgund, which may have residents, seasonal camps, or land users closer to the site or along the access routes. By formally requesting the inclusion of Melgund as a distinct receptor group, the Board ensures that the unique socio-economic and health impacts on its residents are not dismissed simply because they fall outside the municipal boundaries of Ignace. This is an opportunity to ensure the Impact Statement reflects the true human geography of the area.
HEP-063

Understanding the Impacts of Nuclear Waste on our Community

This digital archive houses the public comments submitted to the Impact Assessment Agency of Canada regarding Project 88774: The Nuclear Waste Management Organization Deep Geological Repository (DGR) for Canada's Used Nuclear Fuel Project. The impact assessment is led jointly by the Impact Assessment Agency of Canada and the Canadian Nuclear Safety Commission. This archive preserves community perspectives, concerns, and observations shared during the assessment process, particularly in relation to Melgund Township, Northwestern Ontario and the communities of Dyment and Borups Corners who are the closest and most impacted of all in the process.