A Hybrid Future for Halifax, NS, Canada: Integrating Decentralized Wastewater System for Resiliency

A stark reminder that even with modern, expensive treatment plants, Halifax’s system remains dangerously vulnerable. Halifax’s wastewater system remains vulnerable because large flows depend on a centralized network of trunk sewers and pump stations. Climate change increases this risk: extreme rainfall drives higher wet-weather volumes, while sea-level rise, high tides, and storm surge raise backflow pressure, reduce outfall drainage, and worsen urban flooding during storms that already stress sewers.

This report proposes a hybrid centralized–decentralized portfolio centered on district-scale Membrane Bioreactors (MBRs) supported by complementary measures. Satellite MBRs paired with sewer separation are targeted to redevelopment districts; green infrastructure and targeted interception reduce peak inflows in older high-density areas; and vortex separators improve solids capture at terminal CSO outfalls. While multiple interventions are included, the primary focus of this report is the MBR (Membrane Bioreactor system) technology strategy, because it provides the most direct mechanism to reduce reliance on conveyance bottlenecks by intercepting and treating district flows and buffering peaks through equalization. MBRs provide “load shedding” by treating roughly 20–30% of the runoff, and it also reduces the peak flow during heavy rainfalls through the storage function, thereby reducing the reliance on critical transportation nodes. The report will therefore present MBR in detail, including its technical pathway (screening/equalization, biological treatment, membrane filtration, and reuse or controlled discharge), a refined site-selection map identifying a feasible redevelopment district and its relationship to trunk constraints and flood exposure, and expected performance outcomes. 

Halifax Water Treatment: The Fragility of Centralization

In July 2022, a mechanical failure at the Duffus Street Wastewater Pumping Station forced Halifax Water into a crisis. Millions of liters of screened but untreated wastewater were discharged directly into the Halifax Harbour for several days. As emergency repairs were underway, residents were advised to avoid any water-based activities along the city’s iconic waterfront.

Figure 1. Duffus Street Pump Station Service Area
Source: Halifax Harbour – Wastewater System Update

Risk of A Single Point of Failure

The crisis caused by Duffus Street Pump was not an isolated stroke of bad luck. Instead,  it was a symptom of a fundamental structural flaw. Currently, Halifax’s wastewater system relies on a highly centralized network of pump stations and trunk infrastructure. While efficient under normal conditions, this design creates a “Single Point of Failure.” As shown in Figure 2, the Duffus Street station acts as a bottleneck for a vast service area (highlighted in pink). When this critical component fails, the system lacks the redundancy to reroute or store large-scale flows, leaving 13 Combined Sewer Overflows Discharge Points as the only relief valve.

Figure 2. Map of the Water Treatment System in Halifax

The Looming Web of Challenges

Figure 3. Main Water Challenges and Strategies in Halifax

Halifax is being pushed to its limits by a “perfect storm” of external pressures. Population growth is increasing the base load, while climate change introduces two catastrophic variables: intense rainfall and sea level rise (SLR). During heavy storms, more inflow leads to massive inflation of wastewater volume, triggering WWTP capacity stress and Combined Sewer Overflows (CSOs). Simultaneously, sea level rise creates a “backflow” effect, where rising tides physically obstruct the gravity-based outfalls. These pressures create a compounding cycle of infrastructure damage and urban flooding that the current centralized system was never designed to withstand. To address this systemic fragility, Halifax must get rid of its heavy reliance on a single treatment plant. 

Strategies for Moving Toward a Climate-Decoupled System

Halifax’s current wastewater system functions as a largely all-flow centralized network, where a high proportion of wastewater flows linearly through combined sewers to major pump stations, and finally to the treatment facility. Therefore, the primary driver of risk within the Halifax Water system is centralization. In this structure, the Duffus Street Wastewater Pumping Station becomes a practical single point of failure, because the system has limited redundancy and limited ability to reroute or temporarily hold large volumes of flow when constraints arise.

When a bottleneck occurs at any point, especially during intense rainfall, wet-weather inflows can exceed the capacity of the collection and conveyance infrastructure. In those conditions, the system relies on Combined Sewer Overflows (CSOs) as a protective relief mechanism. As a result, untreated or partially treated combined wastewater/stormwater can be discharged to Halifax Harbour to prevent upstream surcharging, basement backups, and broader system damage. In Halifax’s combined sewer area, this risk pathway is reinforced during extreme events, where high inflow volumes quickly concentrate at major pumping and trunk conveyance nodes.

Figure 4. Decentralized & Centralized Infrastructure Diagram

To mitigate this vulnerability, our intervention proposes a hybrid centralized–decentralized system. Rather than replacing the central WWTF, the strategy adds district-scale satellite treatment (MBR units) to intercept and treat a portion of local sanitary flow, reducing dependence on a single conveyance corridor. The approach also integrates distributed storage/equalization for peak shaving and green infrastructure to reduce runoff and wet-weather inflow. Together, these physical and natural infrastructure elements strengthen mid-stream resilience, lower peak loading on the central grid, and reduce the likelihood and consequences of CSO discharges to Halifax Harbour.

Intervention 1 Membrane Bioreactors (MBR)

Our intervention uses a district-based zoning logic that matches solutions to Halifax’s different urban conditions. In the core redevelopment districts, we propose district-scale MBR satellite treatment paired with sewer separation, so new growth does not add stormwater-driven load to the combined system, and a portion of sanitary flow can be treated locally. In older high-density neighborhoods where combined sewers and wet-weather surcharging are most problematic, we prioritize green infrastructure and targeted interception (runoff reduction, inflow control, and localized diversion) to reduce peak wet-weather volumes that trigger overflows. In the terminal discharge areas along the waterfront, we propose adding hydrodynamic vortex separators to improve solids capture and screening performance during overflow conditions before discharge to the harbour. These measures are intended to work as a coordinated portfolio rather than isolated projects. 

MBR (Membrane Bioreactor system) technology is a modular design for decentralized, small district-scale water recycling projects(Figure 5). A district-scale membrane bioreactor (MBR) can reduce single-point failure consequences in Halifax when it is implemented as part of a hybrid centralized–decentralized system. In the current centralized configuration, large volumes of wastewater must pass through particularly major pump stations and trunk sewers before reaching the central treatment plant. By intercepting and treating a portion of local sanitary flow upstream, a district MBR provides load shedding: if the MBR treats approximately 20–30% of local dry-weather sanitary flow, that volume no longer depends on a single pump station or trunk corridor. During a pump station failure or capacity constraint, less flow arrives at the bottleneck, which increases the time available before surcharge or emergency discharge occurs and reduces the likelihood that the system must rely on overflow pathways. In addition, pairing the MBR with equalization and storage enables peak shaving during storm events, smoothing inflows so that downstream conveyance and treatment are less likely to be exceeded. 

Figure 5. MBR (Membrane Bioreactor system)
Source: Membrane Bioreactors (MBR): A Deep Dive into the Future of Wastewater Treatment

A district-scale MBR is best located in a redevelopment district, campus, or major commercial/business zone. Places with high wastewater generation, high drainage pressure during storms, and enough public control over land, such as parks, parking structures, and civic parcels, to deliver an underground facility with reliable access. 

MBRs are compact, but the footprint depends on the design flow (m³/day) and whether the system is containerized or built as a small underground vault. A common packaged benchmark is that a single 40ft container MBR may treat roughly 30–100 m³/day, while district-scale systems are typically multiple modules plus tanks. Planning-level footprint estimates often scale with capacity: ~1,000 m³/day (≈1 MLD) may require on the order of ~480 m² of core process area (plus circulation and ancillary space), and ~5,000 m³/day (≈5 MLD) on the order of ~2,400 m² core area. In dense districts, MBR and equalization storage can be placed in an underground vault beneath a park or parking structure, with access hatches, ventilation, and a small above-grade control. 

Packaged MBR systems are often estimated at ~$7–$20/gallon-per-day of capacity, so an underground 0.2–0.5 MGD district MBR could cost roughly $1.4M–$10M for the packaged plant portion, before Halifax-specific adders such as an underground vault, equalization storage, controls, and reuse piping. In capacity terms, 0.2 MGD ≈ 757 m³/day and 0.5 MGD ≈ 1,893 m³/day. Using a planning assumption of 75–90 gallons/person/day, a 0.2 MGD facility could serve roughly 2,200–2,700 people, while 0.5 MGD could serve 5,600–6,700 people, which is equivalent to approximately 37–107 acres (0.2 MGD) or 93–267 acres (0.5 MGD) at dense urban densities. For our proposed sites, by filtering out flood zones and focusing on commercial districts, parks, and redevelopment areas, we identified these two locations as the most suitable for MBR implementation (Figure 6). The blue shaded area represents the 0.2 MGD service catchment, and the green shaded area represents the expanded 0.5 MGD catchment, increasing localized treatment and reducing reliance on trunk sewers and critical pump stations, especially during wet-weather stress events.

Figure 6. Physical Intervention Location

The relationship between MBR (Membrane Bioreactor) and sea level rise (SLR) mainly lies in “adaptation” rather than “mitigation”. As the combination of SLR with high tide levels and storm surges will raise the water level within the port, causing “tide-lock” at the estuary and backflow pressure. This makes it more difficult for the external discharge outlets that rely on gravity discharge to release water, thereby exacerbating the risks of pipe overloading, internal flooding, and overflow. Deploying area-level MBR can intercept and treat part of the dry weather domestic sewage base flow upstream of the system, reducing the total flow that must pass through low-lying, tide-influenced sections and external discharge outlets at the source.

By placing the MBR as the satellite processing unit in the upstream area, it can reduce this risk through three mechanisms: First, the MBR intercepts and treats a portion of domestic sewage base flow at the source, reducing the volume that needs to pass through the main trunk pipes and outflowing pipes affected by tides; Second, if the MBR is equipped with a storage/ equalization tank, it can store and staggerly treat during the “storm peak + high tide” overlapping period, reducing the system’s forced overflow during the most vulnerable period; Third, the effluent quality of the MBR is high, facilitating on-site non-drinking reuse or adopting controllable/pressurized discharge schemes, thereby further reducing the reliance on tidal gravity discharge.

However, MBR cannot directly lower the sea level or eliminate the combined sewer overflow or leakage problems of the old water supply network alone. It can only reduce the impact of SLR on drainage and overflow through “reduction + storage + reuse & controlled discharge”, and still needs to be implemented in conjunction with measures such as pipe network repair, separation, and prevention of backflow at outflow points.

Intervention 2 Physical Measures – A MBR Support System

Figure 7. MBR Support System
  • Green Infrastructure
    • Location: High-density corridors such as Spring Garden Road and the Dalhousie University area
    • Function: Promotes infiltration and temporary storage of stormwater, reducing peak surface runoff and alleviating localized flooding.
  • Separated Sewer System
    • Location: Redevelopment areas centered on Cogswell District
    • Function: Separates stormwater from sanitary sewage, ensuring only wastewater is conveyed to treatment facilities.
  • Modern Screens & Vortex Separators
    • Location: CSO outfalls discharging into Halifax Harbour (DC1–DC13)
    • Function: Removes coarse solids, floatables, and sediments through mechanical and hydrodynamic separation during overflow events.
  • Decentralized Block-scale Water Systems
    • Location: High-density mixed-use redevelopment clusters such as the Cogswell District and adjacent waterfront developments.
    • Function: Implements building/block-scale systems that separate blackwater and greywater, enabling on-site treatment, resource recovery (water, energy, nutrients), and reuse through integrated treatment units and shared.
Figure 8. Proportional representation of the space requirements for decentralized wastewater treatment in a typical city block
Source: Nature Water

Impact Evaluation

While Canada maintains high standards in water management, Halifax’s current reliance on a regionalized and centralized infrastructure has created a systemic vulnerability. Our evaluation shows that a shift toward managed decentralization is a necessity for climate adaptation.

Decoupling from Sea Level Rise

It is important to identify the relationship between wastewater discharge and rising tides around Halifax Harbour. Halifax now relies on gravity discharge. As the sea level rises, a backflow pressure will effectively paralyze the outfalls and force sewage to back up into the streets or overflow into the Harbour. Different from traditional systems, MBRs produce high-quality and portable effluent. The treated water can be forcibly discharged via high-pressure pumps, defying the tidal backflow, or diverted for non-potable municipal reuse. Thus, this mechanism prevents wastewater treatment from being affected by SLR.

Enhance Systemic Redundancy

By deploying decentralized units, we eliminate the Single Point of Failure that has historically crippled the network. They ensure that a failure at a central pump station, like the 2022 Duffus Street event, does not lead to a city-wide environmental disaster. With the help of digital monitoring, smart zones are created to improve water use efficiency and provide real-time data to prevent capacity shocks during intense rainfall.

Limitations and Residual Risk

While our intervention offers a robust shield, we must acknowledge its strategic boundaries: (1) Decentralization cannot instantly reverse decades of infrastructure aging or pipe seepage in non-target zones. (2) Transitioning to a hybrid model introduces operational complexity and requires a specialized workforce to maintain those distributed assets.

Conclusion

Our proposal moves beyond theoretical planning to offer a multi-layered, physical strategy designed to address Halifax’s wastewater crisis at its geographic and mechanical roots. Instead of relying on a singular, overburdened backbone, we have outlined a Hybrid Infrastructure Model that prioritizes redundancy and climate adaptation. By treating wastewater at the source, decentralized units provide immediate hydraulic relief to the central system and eliminate the risk of single-point failure. To optimize vital MBRs, we integrated multiple physical measures to realize synergy and thus improve the overall performance.

Reference

  1. Containerised/packaged plants | the MBR site. (n.d.-d). https://www.thembrsite.com/containerised-packaged-plants
  2. Garrido-Baserba, M., Sedlak, D.L., Molinos-Senante, M. et al. Using water and wastewater decentralization to enhance the resilience and sustainability of cities. Nat Water 2, 953–974 (2024). https://doi.org/10.1038/s44221-024-00303-9
  3. Gebhard J. Weiß, Vortex separator: Proposal of a dimensioning method, Water Science and Technology, Volume 36, Issues 8–9,1997,Pages 201-206,ISSN 0273-1223, https://doi.org/10.1016/S0273-1223(97)00598-2.
  4. Hurley, G. V. (2025, June 19). Commentary: Halifax harbour: Time for a smarter, more resilient sewage treatment strategy. PNI Atlantic. https://www.saltwire.com/opinion/commentary-halifax-harbour-time-for-a-smarter-more-resilient-sewage-treatment-strategy
  5. Sandy, E. (2024, December 5). Membrane bioreactors: Coming to the rescue of wastewater facilities struck by disaster. IWS. https://integratedwaterservices.com/membrane-bioreactors-coming-to-the-rescue-of-wastewater-facilities-struck-by-disaster/

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