Water Management Infrastructure

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This project was made possible by the very generous support of an anonymous donor and

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Pulling together a project of this size takes a lot of work. The help of Jayme Nelson, Katherine Hill and Kathryn Wagner from Inside Education was invaluable. We couldn’t have done it without you. Thank you!

Project Team

AC Atienza, Brendan Bate, Shannon Smithwick, Steff Stephansson, Kaleigh Watson, Andrew Wilson.

July 2024 photograph of the Site C dam in British Columbia before filling started
Site C Dam, July 2024. Source: Daily Hive.

Dams and other water infrastructure (see here for more discussion) are a broad class of projects that play vital roles in modern society, providing benefits ranging from hydroelectric power, flood control, water supply security and on to recreational services.   These projects can be the classic “grey” infrastructure of dams but also the “green” infrastructure of nature-based solutions such as created wetlands.   Some examples of such projects are listed below:

  • Dams
  • Berms, dykes, levees, embankments
  • Drinking water distribution systems
  • Sewer and waste-water treatment systems
  • Bioswales, green-roofs, wetlands
Photograph of an urban bioswale or rain-garden - an example of a nature-based solution to urban stormwater management.
Bioswale. Source: Meristem Design.

The community and ecosystem pros and cons of such projects depend on the type of project, how it is implemented and the nature of the problem it is intended to address.   There is no “one-size-fits-all” solution and there may be several ways to achieve a desired outcome.   And, different stakeholder groups are likely to have strong and very different opinions on the merits or otherwise of a given project.

The following article is a high-level overview of some of the issues of such infrastructure-focussed water management approaches.   We will also explore some of the challenges and opportunities in balancing development and conservation.   This article will not address water distribution, water treatment or wastewater management.

The role of dams

Dams serve multiple roles, each critical to the development and maintenance of human societies. They provide essential services including holding water for domestic, agriculture and industrial use, generating hydroelectric power, and recreation.   While dams serve multiple functions, their operation and design is optimised to prioritise a very small number of services as some services may conflict with others.   For example, a flood-control dam needs the reservoir to be kept relatively empty to preserve space to capture flood run off.   On the other hand, a hydro-power dam works best when the reservoir is kept full to give the greatest possible pressure on the turbines and to cater for years of lower flows.   It is not possible to optimally operate the same dam for both purposes simultaneously.

For example:

  • The new Springbank Dam [1] upstream of Calgary on the Elbow River is a flood control structure and slightly unusual in that the reservoir is intended to remain dry unless a flood event is happening. It is not able to generate electricity.
  • “Site C” [2], in British Columbia, is designed as a run-of-the-river hydro-power project and needs to keep the reservoir levels high. When operated for power generation, it will have limited flood control ability.
  • The Ghost Dam [3], upstream of Calgary on the Bow River, is designed as a hydro-power dam. It is operated as such most of the year but, for a few months during the peak flood-risk period, the reservoir level is lowered to prioritise flood control over power generation [4].
  • The St Mary Dam [5], Canada’s largest irrigation dam, is designed and operated primarily as a water supply dam for irrigation but also generates power and provides recreation opportunities.

All these dams are (or, where still under construction, will be) central to regional development and growth and highlight the importance of water infrastructure in supporting modern societies.

Other water management infrastructure

As noted above, dams are only one type of water management infrastructure.   Others include flood barriers such as berms (also called dykes/dikes/levees), diversion channels or channelised rivers.   Such structures are designed to manage floods up to a certain size.   If the flood exceeds that design size, the protection they offer is severely compromised.

On a small scale, “dugouts” are used on farms to store run-off for later use.  They can also offer an environment favourable to plants and wildlife but need careful planning and management [6].   Similarly, the work of organisations such as Ducks Unlimited to restore wetlands can help to restore natural water bodies and improve water quality.

Communities and the socioeconomic impacts of dams

The construction of dams can have profound positive and negative socioeconomic effects on local communities.   In a nutshell: it’s complicated!

Positives

Dams may bring benefits such as flood control, groundwater recharge, recreation opportunities, electricity, and a more secure water supply for communities, agriculture, and industry.   Developed water resource infrastructure tends to encourage economic growth and community prosperity by providing a reliable water supply [7].   However, the picture is complicated with research suggesting the size of the dam is linked to whether or not areas near to the dam benefit or not – larger dams tend to primarily economically benefit more distant populations [8].

Negatives

  • Population displacement
    Dams require space, and sometimes that space, is already occupied, especially if the dam requires a lot of space. Consequently, communities are displaced (e.g. 1.3 million people were moved to enable construction of the Three Gorges Dam [9]) and those displaced may struggle to adapt to the loss of their ancestral lands or to find new comparable land.
  • Cultural disruptions
    The dam and reservoir may bury or submerge historical and cultural sites (e.g. submergence of historical sites [10]). The loss of these heritage sites may have profound long-term impacts on communities’ culture and social practices.
  • Damaged social cohesion
    Displaced populations may face challenges in adapting to new environments, accessing resources, and maintaining social cohesion. Further, downstream communities may experience changes in water availability, water quality, and sediment transport, affecting their livelihoods and well-being.  Dams can also lead to loss of livelihoods (economic displacement) as previous means of earning a livelihood may no longer be possible (e.g. a farmer whose land has been flooded).   These negative effects tend to disproportionately affect already-vulnerable communities in the neighbourhood of the dam [11].
  • Loss of human food sources
    Dams block migrating fish which can cause the collapse of fisheries which provided economic and nutritional sustenance to communities dependent on those fisheries [12]. Another problem is that of naturally occurring methylmercury.  This toxin can bio-accumulate (concentrate in organisms higher up the food chain) and then contaminates the wildlife in the reservoirs and downstream of the dams.   This is an existing problem in Canada [13] and one that is expected to grow as new hydropower dams are commissioned [14].
  • Long-term costs
    One of the long-term challenges with water management infrastructure is the maintenance budget. The structures require maintenance and, possibly, upgrades to continue to operate to the expected standard and that work costs money the protected communities may not be able to afford.   Failure to do necessary maintenance may ultimately lead to unfortunate results (e.g. Sainte-Marthe-sur-le-Lac in Quebec [15], dykes in southern BC [16], [17]).
     
    A longer-term issue is the life-span of the structure.   As mentioned above, structures are designed and built to deliver services at a certain level.   Over time, those services may no longer be wanted or the level (e.g. flood protection) may no longer be adequate.   The necessary upgrades to return the structure to the desired level of safety and service may be more expensive than simply removing them [18].   Of course, removing structures that have been in place a long time is likely to be contentious [19] especially if there has been significant development which relies on the presence of those structures [20].

Environmental and ecosystem effects of dams

Habitat alteration and loss

Dams alter natural river ecosystems in significant ways, with far-reaching consequences for biodiversity and ecosystem services.   The fragmentation, or breaking up, of rivers by dams disrupts the natural flow regime, impedes sediment transport, and alters habitats [21].   These changes can degrade aquatic and riparian ecosystems, leading to the loss of species diversity, changes in species composition, and habitat degradation [22].   Additionally, dams can impede fish migration, disrupt nutrient cycling, and exacerbate water quality issues such as eutrophication and sedimentation.   These environmental impacts have implications for ecosystem resilience, food security, and the provision of ecosystem services.

Water quality and flow

Altering the natural flow of water bodies can impact water quality by changing how sediment such as sand is moved by the flow of water and reducing the flow of nutrients. Stagnant or still water behind dykes can lead to lower oxygen levels, affecting fish and other aquatic life. Additionally, the disruption of natural flooding cycles, which replenish nutrients in floodplains, can impact the health of these ecosystems [23].

Greenhouse gases

An effect of dams which is not always appreciated is the potential for the reservoirs to emit carbon-dioxide and methane from the breakdown of plant matter.   New research [24] suggests that, on a global scale, reservoirs are a significant source of these gases although the extent varies according to their proximity to the equator.   Reservoirs in the tropics and subtropics produce more of the gasses than reservoirs in the higher latitudes.   This is a particular concern as it is estimated that 65-75% of new hydropower reservoirs will be built in the topics and sub-tropics in coming decades.  

“Safe” versus “Safer” or the infrastructure risk/protection paradox

A common reason for building a dam or a dyke is to provide community protection against flooding (e.g. the Springbank Dam [1]).   However, unfortunately, the construction of flood protection can result in higher, not lower, risk over time.   Obviously, there is the new risk of dam or dyke failure (e.g. Derna dam failure [25], USA overview [26]) but properly-designed, properly-maintained and properly-operated infrastructure should not present a significant risk of failure.

Growth in risk from new development

However, the bigger issue comes from people’s perception of being “safe”.   When we develop infrastructure to protect communities against flooding, a consequence becomes the building of new neighbourhoods and other developments in areas previously known as flood prone that are now seen as “safe” from floods.   This means that while the probability of flooding may be reduced, the value of the houses and buildings as well as the number of people vulnerable to flooding increases if there was to be a failure of the water management infrastructure. This increases the risk of damage occurred and increases the costs of actions like rehousing people affected in comparison to if the infrastructure hadn’t been built (e.g. British Columbia’s Sumas Prairie [27]).   The core mistake is in thinking in absolute terms:  that infrastructure makes one “safe”.   The truth is that infrastructure should make one “safer” but there is always a remaining level of risk.   This is most easily seen with dykes:  they are built and designed to manage storms up to a certain size.   The protection they offer against a bigger-than-designed-for storm is greatly reduced as the water simply flows over the top of the dykes and, should the dykes fail, the failure may make the damage worse than if the dykes hadn’t been there in the first place.

Growth in risk from climate change

Another source of “new” risk is the effects of a changing climate on storm frequency and intensity.   A structure is designed to a “service level” of protection against extreme water events of a certain size.   For example, a new structure might be designed to protect an area against, say, a storm with a 1:200 chance of happening.   This means that a bigger storm, say 1:300, will not be protected against but the builders of the structure are prepared to accept the consequences of a storm that rare.

However, climate change is increasing both the intensity and the frequency of severe storms.   Which means, in effect, that a storm in Canada which currently occurs with a 1:50 frequency is expected to become a 1:10 event by the late 2000’s [28] under the RCP8.5 emissions scenario.

The result of this is that, over time, the “service level” protection provided by the new structures declines.   And that communities who had thought they were protected against a, say, 1:50 event will only have a fraction of that protection.

A (very brief) description of RCP scenarios: RCPs or Representative Concentration Pathways are climate change scenarios which have been adopted globally to project future greenhouse gas concentrations.   These “pathways” describe future greenhouse gas (GHG) (e.g. Carbon-dioxide) concentrations and are used to make predictions of our future climate at various dates in the future.   RCP 8.5 is the most extreme (i.e. most GHG) scenario and assumes that the world’s GHG emissions will continue to increase in the 2000’s.   See here for more information.

Two graphs showing the predicted changing return periods of future 24-hour precipitation extremes under RCP2.6 and RCP8.5. In all cases, current extreme events become more common in the future.
Future precipitation return periods. Source: Canada's Changing Climate Report 2019, Chapter 4.

Use caution and think carefully

Dams and dykes are vitally important tools in community protection against flooding and dam reservoirs provide valuable water management capabilities.   However, communities protected by such structures need to be cautious and deliberate about permitting further development in the protected areas.

Conclusion

Water management infrastructure can and does bring both benefits and costs to communities and ecosystems.   Trying to balance those benefits and costs is not simple [29].   Communities need to involve all stakeholders in the necessary discussions to choose the most appropriate and long-term sustainable solution.   Ensuring the resilience and health of both human and natural communities requires ongoing effort and collaboration by all stakeholders.

Call to action

Have a look around your community and see how much water management infrastructure you can find. 

  • How much do you know about it?
  • What does it do and how does it do it?
  • Why was it built?
  • Is any of it dedicated to flood control? To drought mitigation?  
  • Is it “grey” or “green” infrastructure?
  • What size storm can it handle?
  • Who manages it?

Potential education approaches to teaching children about infrastructure

  • Build a model dam or dyke in a tank or on the ground and see how it behaves with differently sized “floods” from a bucket or a hose.
  • If the school property or nearby property permits, study a local wetland.  To take it further, undertake a wetland restoration project and study the effects of that on biodiversity.
  • Site visits to local water management infrastructure such as a storm pond or dam with an expert to explain what is being seen.
  • Site visit to reservoirs constructed for fish and wildlife habitat.
  • Site visit to structures constructed and maintained for recreation and cultural purposes.

Sources:

  1. Government of Alberta,  n.d., Springbank Off-stream Reservoir.  https://www.alberta.ca/springbank-off-stream-reservoir.  Accessed 20247-03-15.
  2. BC Hydro, n.d., Site C Clean Energy Project.  https://www.bchydro.com/energy-in-bc/projects/site_c.html.  Accessed 2024-03-15.
  3. TransAlta, n.d., Ghost.  https://transalta.com/about-us/our-operations/facilities/ghost/.  Accessed 2024-03-15.
  4. Government of Alberta, 2022, Bow River – TransAlta agreement : Alberta Environment and Parks and TransAlta five-year water services agreement extension.  https://open.alberta.ca/publications/bow-river-transalta-agreement-fact-sheet.  Accessed 2024-03-15.
  5. APEGA, n.d., Irrigation Transforms Southern Alberta.  https://discoverapega.ca/stories/irrigation-transforms-southern-alberta/.  Accessed 2024-03-15.
  6. Government of Alberta, n.d., Understanding Prairie Dugouts.  https://www1.agric.gov.ab.ca/$Department/deptdocs.nsf/all/agdex15866/$FILE/716_B01_module2.pdf.  Accessed 2024-06-25.
  7. United Nations, 2024, The United Nations World Water Development Report 2024: Water for Prosperity and Peace.  https://www.unesco.org/reports/wwdr/en/2024.  Accessed 2024-03-27.
  8. Fa, P, Cho, M.S, et al, 2022, Recently constructed hydropower dams were associated with reduced economic production, population, and greenness in nearby areas.  https://www.pnas.org/doi/10.1073/pnas.2108038119.  Accessed 2024-03-21.
  9. Wee, S., 2012, Thousands being moved from China’s Three Gorges – again.  https://www.reuters.com/article/idUSBRE87L0ZX/.  Accessed 2024-03-15.
  10. Cox, S., 2016, ‘Gone Forever’: Archaeologist Warns Site C Threatens First Nations Historic Sites.  https://thetyee.ca/News/2016/01/09/Site-C-Threatens-Historic-Sites/.  Accessed 2024-03-15.
  11. Mavhura, E., 2020, Dam-induced displacement and resettlement: Reflections from Tokwe-Mukorsi flood disaster, Zimbabwe.  https://doi.org/10.1016/j.ijdrr.2019.101407.  Accessed 2024-03-21.
  12. Cafasso, S., 2020, Hydropower dams threaten fish habitats worldwide.  https://sustainability.stanford.edu/news/hydropower-dams-threaten-fish-habitats-worldwide.  Accessed 2024-03-21.
  13. Austen, I., 2016, Canada’s Big Dams Produce Clean Energy, and High Levels of Mercury.  https://espp.fas.harvard.edu/news/canada%E2%80%99s-big-dams-produce-clean-energy-and-high-levels-mercury.  Accessed 2024-03-21.
  14. Calder, R.S.D, Schartup, A.T., et al, 2016, Future Impacts of Hydroelectric Power Development on Methylmercury Exposures of Canadian Indigenous Communities.  https://pubs.acs.org/doi/abs/10.1021/acs.est.6b04447.  Accessed 2024-03-21.
  15. Lowrie, M., 2023, Residents of Quebec town still struggle with aftermath of 2019 dike break, flooding.  https://www.cbc.ca/news/canada/montreal/residents-sainte-marthe-struggle-flooding-1.6827357.  Accessed 2024-03-28.
  16. Parfitt, B., 2023, Failure to act means failing dikes.  https://www.policynote.ca/dikesfoi/.  Accessed 2024-03-28.
  17. Owen, B., 2023, B.C. aware of dike problems before destructive flooding in 2021, documents show.  https://vancouversun.com/news/local-news/b-c-aware-of-dike-problems-before-destructive-flooding-in-2021-documents-show.  Accessed 2024-03-28.
  18. Massachusetts Department of Fish and Game, Division of Ecological Restoration, 2015, Economic & Community Benefits from Stream Barrier Removal Projects in Massachusetts.  https://extension.unh.edu/sites/default/files/migrated_unmanaged_files/Resource006641_Rep9683.pdf.  Accessed 2024-03-28.
  19. Baumhardt, A., 2023, Feds consider removing Snake River dams in leaked agreement with plaintiffs in lawsuit.  https://washingtonstatestandard.com/2023/11/30/feds-consider-removing-snake-river-dams-in-leaked-agreement-with-plaintiffs-in-lawsuit/.  Accessed 2024-03-28.
  20. Donovan, M., 2020, Breaching tradition: Salt marshes replacing Nova Scotia’s dikes.  https://www.cbc.ca/news/canada/nova-scotia/nova-scotia-dikes-sea-walls-salt-marshes-1.5454709.  Accessed 2024-04-03.
  21. World Wildlife Fund, 2004, Rivers at Risk: Dams and the future of freshwater ecosystems.  https://wwf.panda.org/wwf_news/?13716/Rivers-at-Risk-Dams-and-the-future-of-freshwater-ecosystems.  Accessed 2024-03-21.
  22. International Rivers, n.d., Environmental Impacts of Dams.  https://archive.internationalrivers.org/environmental-impacts-of-dams.  Accessed 2024-03-21.
  23. González Macé, O., Steinauer, K., et al, 2016, Flood-Induced Changes in Soil Microbial Functions as Modified by Plant Diversity.  https://journals.plos.org/plosone/article?id=10.1371/journal.pone.0166349.  Accessed 2024-04-03.
  24. Harrison, J.A., Prairie, Y.T., et al, 2021, Year-2020 Global Distribution and Pathways of Reservoir Methane and Carbon Dioxide Emissions According to the Greenhouse Gas From Reservoirs (G-res) Model.  https://agupubs.onlinelibrary.wiley.com/doi/full/10.1029/2020GB006888.  Accessed 2024-03-21.
  25. CNN, 2023, Aging dams and missed warnings: A lethal mix of factors caused Africa’s deadliest flood disaster.  https://www.cnn.com/2023/09/14/middleeast/lethal-factors-leading-to-libya-floods-intl/index.html.  Accessed 2024-03-27.
  26. Association of State Dam Safety Officials, n.d., Dam Failures and Incidents.  https://damsafety.org/dam-failures.  Accessed 2024-03-27.
  27. CBC, 2021, Before-and-after satellite images show flood devastation in B.C.’s Sumas Prairie.  https://www.cbc.ca/news/canada/british-columbia/bc-floods-sumas-prairie-before-after-images-1.6258803.  Accessed 2024-03-27.
  28. Government of Canada, 2019, Canada’s Changing Climate Report.  https://changingclimate.ca/CCCR2019/.  Accessed 2024-03-27.
  29. Parshley, L., 2018, The Costs and Benefits of Hydropower.  https://www.smithsonianmag.com/innovation/costs-and-benefits-hydropower-180967691/.  Accessed 2024-03-28.

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Photograph of WaterPortal Board Member Ross Douglas

Ross Douglas

Board Member

Ross has extensive executive experience in Operations, Governance, Information Technology and Strategy at the board and senior management level including Mancal Corporation, Mancal Energy, Highridge Exploration and Atlantis Resources. He has worked in Oil and Gas, Coal, Commercial Real Estate, Portfolio Management, Recreation, Retail and Water and Wastewater Treatment. His experience is also geographically diverse having overseen operations in Canada, the United States, United Kingdom and Northern Ireland. Additionally, he has been on the board of companies with operations in Argentina, Azerbaijan, Barbados, Kazakhstan, and Russia. He has served on numerous Public, Private and Not for Profit Boards across a number of industries.

Ross has been active on several industry Boards and committees including the Canadian Association of Petroleum Producers (CAPP) and The Schulich School of Engineering Industry Advisory Council at the Schulich School of Engineering.

Photograph of WaterPortal Board Member Brian Mergelas

Brian Mergelas, PhD, ICD.D

Board Member

Brian is a seasoned Cleantech entrepreneur with a proven history of successfully bringing complex water technologies to the market.   With over 25 years of experience, he has led various organizations to achieve significant milestones in the industry. 

Having started as the founding CEO of the Pressure Pipe Inspection Company (PPIC) and later taking the helm at the Water Technology Acceleration Project (WaterTAP), Brian’s entrepreneurial spirit has been instrumental in driving innovation and growth within the sector. 

He is an active investor in the cleantech sector and has served on many boards including the Ontario Clean Water Agency. 

Actively engaged in industry associations like AWWA, WEF, IWA, and ASCE, Brian enjoys collaborating with fellow professionals to promote advancements in the field. 

Brian holds an undergraduate degree and a PhD in Physics from Queen’s University, which has provided him with a solid technical foundation.   As a member of the Institute of Corporate Directors, he brings valuable insights to corporate governance.