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Growing Green Cities - A Practical Guide to Urban Forestry in Canada
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Page 1
Growing Green Cities: A Practical
Guide to Urban Forestry in Canada
Bardekjian, A. & Puric-Mladenovic, D. (2025). Growing Green Cities: A Practical Guide
to Urban Forestry in Canada. Tree Canada. Retrieved from Tree Canada: https://
treecanada.ca/urban-forestry-guide
Context1.0
Definition of Urban Forests (https://treecanada.ca/urban-forestry-guide/definition-of-
urban-forests/)
1.1
History of Urban Forests in Canada (https://treecanada.ca/urban-forestry-guide/
history-of-urban-forests-in-canada/)
1.2
Ecological Services2.0
Benefits of Urban Forests (https://treecanada.ca/urban-forestry-guide/benefits-of-
urban-forests/)
2.1
Trees and Urban Heat Island (UHI) (https://treecanada.ca/urban-forestry-guide/trees-
and-urban-heat-island-uhi/)
2.2
Air Quality and Climate Change (https://treecanada.ca/urban-forestry-guide/air-
quality-and-climate-change/)
2.3
Stormwater Management (https://treecanada.ca/urban-forestry-guide/stormwater-
management/)
2.4
Inventory and Monitoring3.0
Economic Value and Appraisal of Trees (https://treecanada.ca/urban-forestry-guide/
economic-value-and-appraisal-of-trees/)
3.1
Individual Tree and Woodlot Inventory, and the Tree Inspection Cycle (https://
treecanada.ca/urban-forestry-guide/individual-tree-and-woodlot-inventory-and-the-tree-
inspection-cycle/)
3.2
GIS, Remote Sensing and Other Technologies (https://treecanada.ca/urban-forestry-
guide/gis-remote-sensing-and-other-technologies/)
3.3
Datasets (https://treecanada.ca/urban-forestry-guide/datasets/)3.4
Management4.0
Urban Forest Management Planning (https://treecanada.ca/urban-forestry-guide/
urban-forest-management-planning/)
4.1
Tree Maintenance (https://treecanada.ca/urban-forestry-guide/tree-maintenance/)4.2
Hydro Lines and Corridors (https://treecanada.ca/urban-forestry-guide/hydro-lines-and-
corridors/)
4.3
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Definition of Urban Forests
Tree Selection and Planting (https://treecanada.ca/urban-forestry-guide/tree-selection-
and-planting/)
4.4
Hard Surface Planting (https://treecanada.ca/urban-forestry-guide/hard-surface-
planting/)
4.5
Urban Woodlot and Park Management (https://treecanada.ca/urban-forestry-guide/
urban-woodlot-and-park-management/)
4.6
Emergency Preparedness (https://treecanada.ca/urban-forestry-guide/emergency-
preparedness/)
4.7
Legislation and Protections5.0
Enabling Legislation, Municipal By-laws and Regulations (https://treecanada.ca/
urban-forestry-guide/enabling-legislation-municipal-by-laws-and-regulations/)
5.1
Tree Protection During Construction and Conflict with Building Foundations
(https://treecanada.ca/urban-forestry-guide/tree-protection-during-construction-and-
conflict-with-building-foundations/)
5.2
Urban Forest Stresses6.0
Abiotic Stresses (https://treecanada.ca/urban-forestry-guide/abiotic-stresses/)6.1
Insects and Diseases (https://treecanada.ca/urban-forestry-guide/insects-and-
diseases/)
6.2
Invasive Plant Species (https://treecanada.ca/urban-forestry-guide/invasive-plant-
species/)
6.3
Fire and the Urban-Rural Interface (https://treecanada.ca/urban-forestry-guide/fire-
and-the-urban-rural-interface/)
6.4
Social Considerations7.0
Equity Considerations in Urban Forestry (https://treecanada.ca/urban-forestry-guide/
equity-considerations-in-urban-forestry/)
7.1
Awareness and Community Stewardship (https://treecanada.ca/urban-forestry-guide/
awareness-and-community-stewardship/)
7.2
Indigenous Collaboration and Integration of ITK (https://treecanada.ca/urban-
forestry-guide/indigenous-collaboration-and-integration-of-itk/)
7.3
Education and Professional Development (https://treecanada.ca/urban-forestry-
guide/education-and-professional-development/)
7.4
Additional Resources8.0
Additional Resources (https://treecanada.ca/urban-forestry-guide/additional-resources/)8.1
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What comes to mind when thinking of an urban forest? Street trees? Trees in
containers on sidewalks? Forests in ravines? Backyard trees on lot lines? In fact,
urban forests encompass all those things and more.
Since the mid-20th century, urban areas in Canada have experienced signi�cant
growth and increased population density, which has brought many environmental,
ecological, and social problems to the surface. These have underscored the
importance of developing greener cities and heightened the need for the
conservation and management of urban trees. Over time, urban greening attention
has moved from a tree-by-tree management approach to one that recognizes the
importance of all trees in urban areas (Konijnendijk et al., 2004). Terms like "urban
forest," "urban forestry," and "urban tree canopy" have emerged, and their de�nitions
have developed over time. While these three terms are related and often used
interchangeably, it is important to recognize the differences between them.
Key Terms in Urban Forestry
There are several detailed de�nitions of urban forest and forestry that have been
used in Canada. In general, the urban forest is de�ned as a collection of all trees,
woody plants, and vegetation within urban areas (Jorgensen, 1974). Broadly
speaking, urban forestry is a specialized yet multidisciplinary branch of forestry
Highlights
Key definitions
Explanation of urban forests, urban forestry, and urban canopy.
Evolution of definitions
How the understanding of urban forests, forestry, and urban areas has changed
over time.
Urban forestry as a practice
Management, planning, planting, maintenance, and protection of urban forests.
Urban forestry resources in Canada
Available resources.
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focusing on forest and tree management techniques and practices that range from
planning, planting, maintaining, and protecting trees to public engagement and
education (Deneke, 1993). Urban tree canopy is a two-dimensional expression of an
urban forest and a measure of the extent of tree canopies that shade the ground
(CSLA, 2024; Vogt, 2020). Easily mappable using modern spatial technologies, the
urban tree canopy is often used as a simple and general measure of urban forests,
enabling urban forest quanti�cation, comparison, and monitoring over space and
time (Tree Canada, 2019).
The approach to thinking of trees in urban areas as a forest was prompted by the
loss of American elms (Ulmus americana) due to the impacts of Dutch Elm Disease
(DED) in North American cities in the 1960s. DED, a vascular wilt fungus, killed most
American elms in urban areas and devastated the tree canopy cover in many Eastern
American and Canadian communities. The sudden loss of tree canopy left streets
and neighbourhoods without su�cient canopy cover and shade, leading to a
signi�cant public outcry for conserving and managing urban trees. The movement
mobilized forestry professionals and scientists to recognize and value urban forests
as critical natural resources in urban areas. Society had started to recognize that
urban forests were critical for providing diverse environmental and social bene�ts
and making urban areas livable.
Subsequently, the importance of all trees growing in urban areas was recognized, and
the terms "urban forest" and “urban forestry” were coined. The terms were de�ned in
1965 by Dr. Eric Jorgensen at the Faculty of Forestry, University of Toronto, Canada.
Dr. Jorgensen �rst de�ned the term "urban forestry" as “a specialized branch of
forestry and [it] has in its objectives the cultivation and management of trees for their
present and potential contribution to the physiological, sociological, and economic
well-being of urban society. These contributions include the overall ameliorating
effect of trees on their environment, as well as their recreational and general amenity
value." (Jorgensen, 1974). He also believed that urban forestry extends beyond "the
city trees or single street management, but rather the tree management in the entire
area in�uenced by the urban population." (Jorgensen, 1974).
Definitions Over Time
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Dr. Jorgensen’s original de�nition of urban forestry was enhanced and developed
over time. In 1993 at the �rst Canadian Urban Forest Conference, Frederick Deneke
expanded on the term, stating: "Urban forestry is the sustained planning, planting,
protection, maintenance, and care of trees, forests, greenspace, and related
resources in and around cities and communities for economic, environmental, social,
and public health bene�ts for people. The de�nition includes retaining trees and
forest cover as urban populations expand into surrounding rural areas and restoring
critical parts of the urban environment after construction. Expansion at the urban/
rural interface raises environmental and public health safety concerns, as well as
opportunities to create educational and environmental links between urban people
and nature. In addition, urban and community forestry includes the development of
citizen involvement and support for investments in long-term ongoing tree planting,
protection, and care programs."
Over the years, with growing knowledge and a better understanding of the
signi�cance and value of the urban forest, more foresters and professionals began
working in the �eld of urban forestry, and urban forest de�nitions started to surface
in professional documents and acts in Canada. For example, the Ontario
Government's Professional Foresters Act of 2000 de�nes urban forests as "tree-
dominated vegetation and related features found within an urban area, and includes
woodlots, plantations, shade trees, �elds in various stages of succession, wetland
and riparian areas." In 2021, the Act's urban forest de�nition was enhanced, and the
term "urban woodland" was added to include urban natural areas such as "woodlands
found in an urban environment, including those in riparian areas, ravines and
wetlands" (Professional Foresters Act, 2000).
Along with the de�nition of urban forests and urban forestry, the importance of
strategic and planned urban forests and their management became apparent.
Kenney (2003) pioneered the idea of strategic urban forest management planning
and emphasized the importance of strategically managing all urban forest
components and associated biotic and abiotic elements across a wide range of
urban areas, from large to small communities, and in the areas between them. As
such, strategic management of urban forests across a range of urban spaces, such
as streets, parks, cemeteries, arboretums, private properties, and natural forest
fragments, was implemented. All urban forest elements were recognized as the
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backbone of green infrastructure, and the contribution of urban forest to connecting
urban and rural green areas and its contribution to improving the urban environment
(GIOC 2015; NRCan and Canadian Forest Service, 2022).
Building on Kenney’s (2003) idea of the importance of strategic urban forest
management and recognizing the ecological and social importance of urban trees
within and outside the boundary of urban areas, the 2019-2024 Canadian Urban
Forest Strategy (CUFS) de�nes urban forests more comprehensively as the "trees,
forests, greenspace and related abiotic, biotic and cultural components in areas
extending from the urban core to the urban-rural fringe" (Tree Canada, 2019).
Additionally, the CUFS de�nition of urban forestry also includes "the sustained
planning, planting, protection, maintenance, management and care of trees, forests,
greenspace along with related resources in and around cities as well as communities
for economic, environmental, social, and public health bene�ts for people." It also
recognized "techniques associated with retaining trees in the context of
densi�cation, forest cover in the context of urban expansion into surrounding rural
areas, and greening critical parts of the urban environment after development and
urbanization." The CUFS acknowledges that "As the geographic and social
distinctions between urban and rural become less clear, urbanization raises
environmental and public health and safety concerns, thereby creating a need for
educational and environmental links between urban people and nature. Urban
forestry is multidisciplinary and multifaceted, comprised of many actors in research,
policy, practice, and community engagement. Urban forestry includes the
development of citizen involvement and support for investments in long-term on-
going tree planting, protection, and care programs."
Defining Urban Areas
While de�nitions of urban forests use the term “urban” to describe the bounds of the
urban forest, this raises the question of how to de�ne the term "urban." In Canada, the
de�nition of urban areas has evolved over the years. In the 1931 Canadian Census,
an urban population is de�ned as a "population residing inside boundaries of
incorporated cities, towns, and villages, regardless of size." After 1951, however,
urban areas in Canada began to be de�ned by their population size and, later, by
population density. The 1971 Canadian Census, based on population count and
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density at the time, stated, "An urban area has a minimum population concentration
of 1,000 persons and a population density of at least 400 persons per square
kilometre." In 2008, Statistics Canada recognized that there are two classes of
populated areas in Canada: urban areas and rural areas, and they further de�ne urban
population speci�cally as "all population living in the urban cores, secondary urban
cores and urban fringes of census metropolitan areas" (Statistics Canada, 2008).
Consequently, as the de�nitions of urban areas and urban population have evolved
spatially and structurally, the de�nition of urban forest also advanced to include trees
and associated vegetation found in areas deemed metropolises, cities, towns or
villages, and areas impacted by the urban population. It has also been recognized
that urban forests and urbanization are interdependent and that urban forests extend
beyond the city limits and are not constrained to municipal borders (Tree Canada,
2019). Urban areas and their populations bene�t from the forests and woodlands
outside urban boundaries. These forests and trees, between urban and rural areas,
within the zone of urban in�uence often termed peri-urban forests (FAO, n.d.;
Salbitano et al., 2016), provide recreational opportunities for urban dwellers, support
biodiversity conservation, and, although outside urban areas, contribute to regulating
urban climate and hydrology, improve air and water quality, and provide aesthetic and
cultural value. However, the pressures from urbanization, development, and the urban
population negatively impact forests and the natural environment in peri-urban areas,
often resulting in fragmented forest patches and forests that are permanently lost or
altered due to development (Puric-Mladenovic, Kenney & Csillag, 2000).
Understanding and recognizing the interdependence of urban and peri-urban areas,
as well as the similarities and connections between peri-urban and urban forests, is
critical for strategic urban forest management and planning (Kenney & Rosen, 2003;
Konijnendijk et al., 2004; Salbitano et al., 2016).
Resources
Canadian Society of Landscape Architects (CSLA). (2024). De�ning the Urban Canopy.
https://www.csla-aapc.ca/mission-areas/de�ning-urban-canopy
Green Infrastructure Ontario Coalition (GIOC). (2015). Ontario's urban forests: Call to action.
Canadian
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https://greeninfrastructureontario.org/app/uploads/2016/06/
GIO_Urban_Forest_Call_to_Action_Sept15Print.pdf
Kenney, W. A., & Rosen, M. R. (2003). Urban Forestry Trends in Canada. Food and Agriculture Organization
of the United Nations.
https://www.fao.org/4/XII/0752-B1.htm
Natural Resources Canada. (2024). What's an Urban Forest? Natural Resources Canada.
https://natural-resources.canada.ca/simply-science/whats-urban-forest/25985
National Capital Commission. (n.d.). Tree canopy assessment for the National Capital Region: A climate
change perspective [PDF]. Retrieved January 12, 2025, from
https://ncc-website-2.s3.amazonaws.com/documents/FINAL_Tree_Canopy_Assessment_EN.pdf
Natural Resources Canada, Canadian Forest Service. (2022). Think tank on a pan-Canadian strategy on
urban forests: Synopsis of discussion.
https://www.csla-aapc.ca/sites/csla-aapc.ca/�les/CFS-Urban_Forest_summary_EN%20_small.pdf
Professional Foresters Act, 2000, S.O. 2000, c. 18.
https://www.ontario.ca/laws/statute/00p18
Statistics Canada. (2008). Urban area (UA).
https://www12.statcan.gc.ca/census-recensement/2006/ref/dict/geo049-eng.cfm
Tree Canada. (2019) Canadian Urban Forest Strategy: 2019-2024, 15 pp.
https://treecanada.ca/wp-content/uploads/2018/10/TC-CUFS-2019-2024-Eng-1.pdf
Cities4Forests. (2023). Learning Guide: Urban Forests for Healthier Cities, 48 pp. Retrieved from
https://cities4forests.com/resource/urban-forests-for-healthier-cities-policy-planning-regulations-and-
institutional-arrangements/
Food and Agriculture Organization of the United Nations (FAO). (n.d.). Urban and peri-urban forestry.
https://www.fao.org/forestry-fao/urbanforestry/87025/en/
Salbitano, F., Borelli, S., Conigliaro, M., & Chen, Y. (2016). Guidelines on Urban and Peri-urban Forestry.
Food and Agriculture Organization of the United Nations.
https://openknowledge.fao.org/server/api/core/bitstreams/9c27d98b-8071-4ee7-8fc4-e0b430f8a8dc/
content#:~:text=Urban%20forests%20can%20be%20de�ned,and%20trees%20in%20derelict%20corners
Allegretto, G., Kendal, D., & Flies, E. J. (2022). A Systematic Review of the Relationship Between Urban
Forest Quality and Socioeconomic Status or Race. Urban Forestry & Urban Greening, 74, 127664.
https://doi.org/10.1016/j.ufug.2022.127664
Non-Canadian
Further Reading
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Andresen, J. W. (1977). Urban Forestry Legislation in Ontario. The Forestry Chronicle, 53(5), 291–293.
https://doi.org/10.5558/tfc53291-5
Artibise, A. F. J. (1988). Canada as an Urban Nation. Daedalus, 117(4), 237–264.
https://www.jstor.org/stable/20025203
Barker, E., & Kenney, W. (2012). Urban Forest Management in Small Ontario Municipalities. The Forestry
Chronicle, 88(02), 118-123.
https://doi.org/10.5558/tfc2012-027
Dean, J. (2005). "Said tree is a veritable nuisance": Ottawa's Street Trees 1869-1939. Urban History
Review, 34(1), 46-57.
https://doi.org/10.7202/1016046ar
Deneke, F. (1993). Urban forestry in North America: Towards a global ecosystem perspective. In G. Blouin
& R. Comeau (Eds.), Proceedings of the First Canadian Urban Forests Conference May 30–June 2, 1993
(pp. 4-8). Winnipeg, MB.
Gerhold, H.D. (2007). Origins of Urban Forestry. In: Kuser, J.E. (eds) Urban and Community Forestry in the
Northeast.
https://doi.org/10.1007/978-1-4020-4289-8_1
Hauer, R. (2005). Urban Forestry and Urban Forest Capacity: De�ning Capacity and Models of Capacity
Building (thesis).
https://www.researchgate.net/
publication/35641908_Urban_forestry_and_urban_forest_capacity_de�ning_capacity_and_models_of_c
apacity_building
Jorgensen, E. (1974). Towards an Urban Forestry Concept. Proceedings of the 10 Commonwealth
Forestry Conference. Ottawa: Forestry Service.
Kenney, W. A. (2003). A Strategy for Canada's Urban Forests. The Forestry Chronicle, 79(4), 785-789.
https://doi.org/10.5558/tfc79785-4
Konijnendijk, C., & Randrup, T. (2004). Urban Forestry. In Burley J., Evans J., Youngquist J.A (Eds.),
Encyclopedia of Forest Sciences (pp.471-478) Oxford: Elsevier.
https://www.researchgate.net/publication/280562809_Urban_Forestry
Konijnendijk, C., Sadio, S., Randrup, T., & Schipperijn, J. (2004). Urban and peri-urban forestry in a
development context—strategy and implementation. Journal of Arboriculture, 30(5), 269–275.
https://doi.org/10.48044/jauf.2004.032
McGahan, P . (1986). Introduction (pp. 9). In Urban Sociology in Canada, 403 pp. Toronto: Butterworth &
Co.
Puric-Mladenovic, D., Kenney, W. A. and Csillag, F. (2000). Land development pressure on peri-urban
forests: A case study in the Regional Municipality of York. The Forestry Chronicle, 76(2): 247-250.
https://doi.org/10.5558/tfc76247-2
Vogt, J. (2020). Urban Forests as Social-Ecological Systems. In M. I. Goldstein & D. A. DellaSala (Eds.),
th
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Encyclopedia of the World's Biomes (pp. 58-70). Oxford: Elsevier.
https://doi.org/10.1016/B978-0-12-409548-9.12405-4.
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History of Urban Forests in Canada
The history of urban forests and forestry in Canada and the relationships between
people and urban trees are deeply rooted in the natural environment and diverse
cultural values of Canadians. Land and forest stewardship that is based on a deep
respect for the natural world and harmony with nature has been practiced by
Indigenous peoples who have been stewarding the land and waters for millennia
(Artelle et al., 2019). Canadian cities and towns have been established on the
traditional ancestral territories of First Nations, Inuit, and Métis people, whose rights
assert their authority to exercise their own jurisprudence and decision-making on
these lands (Reo et al., 2017; Artelle et al., 2019; Dietz et al., 2021; Moola et al.,
2024).
However, these rights were not recognized by English and French colonizers, who
brought their European land use values and drastically changed the land and forest.
They stripped Indigenous people of their land, resources, rights, knowledge,
governance, and their way of land stewardship (Youdelis et al., 2021; Mansuy et al.,
2023; Townsend and Roth, 2023). European settlers perceived the land primarily as a
Highlights
Land colonization
Deforestation, land use change, and permanent settlements.
Evolving practice
Urban forestry has evolved from pest control to addressing broader issues such as
green infrastructure, asset management, and natural climate solutions.
Public interest and stewardship
Growing environmental and social concerns have increased public interest in urban
forests, leading to greater community involvement and stewardship.
Ongoing development
Urban forestry in Canada evolves to meet new challenges and opportunities as
urban areas continue to grow.
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resource for extraction and an opportunity for short-term pro�t. This mindset led to
rapid changes and degradation of the forests and lands. What was once a lush
landscape, rich with forests and wetlands, was permanently changed due to
deforestation, resource extraction, and the establishment of permanent settlements,
villages, towns, and farms.
European settlers established permanent villages and towns, introducing various new
land use practices, including farms, residential areas, permanent roads, railways,
parks, cemeteries, and industrial zones, to name a few. These changes in land use,
coupled with a century of intensive deforestation and degradation, resulted in
environmental problems such as erosion and stream sedimentation within a few
decades of settlement (e.g. In Ontario by the late 1800s). Driven by the economic
cost that environmental degradation and deforestation caused, the �rst government-
led conservation movement started in Ontario at the turn of the 20 century. Trees,
once seen solely as timber value and revenue, were recognized as being important
for stabilizing soils, sheltering homes from winds, providing shade, stopping stream
sedimentation, and providing food and beauty around homes and settlements. Due
to poor environmental conditions in urban areas, city dwellers began to yearn for
more green spaces and escape to natural surroundings outside the cities. This
prompted the creation of some of the �rst parks within or in proximity to urban
centres, such as Stanley Park in Vancouver, BC (1888), High Park in Toronto, ON
(1873), Mont-Royal Park in Montreal, QC (1876), and Point Pleasant Park in Halifax,
NS (1866). These early urban parks are now iconic and indispensable to the urban
fabric of these cities.
The creation of natural and manicured parks, urban tree plantings, and the practice of
European-style gardening and beauti�cation spread across towns and villages and
expanded over time. Urban trees were planted and enjoyed for their shade, exotic
properties, and beauty. As such, groups dedicated to ‘urban greening’ started to form
in cities, such as the Toronto Parks, Forestry and Recreation group established in
1884 under the name "Committee on public walks and gardens", and the "Vancouver
Park Board" in 1886. For Ottawa, the �rst municipal response related to urban trees
was a bylaw passed in 1869 (Dean, 2005).
In the early 1900s, a devastating fungal pathogen called Dutch Elm Disease (DED)
th
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reached Canada and decimated American elms (Ulmus americana), one of the most
popular urban trees. Thus, the urban tree canopy of many cities in eastern Canada, at
the time dominated by elms, was lost. Following the DED outbreak and tree canopy
loss across eastern parts of the country, the public and decision-makers started to
realize the gap left by the loss of many trees in their communities. The severity of
canopy loss from one single pathogen also highlighted the risk of narrow tree
selection and the vulnerability of overplanting one singular tree species. It also
highlighted the need to strategically manage urban trees and parks to prevent such
catastrophes in the future.
In the 1960s, this vulnerability was recognized by a forward-thinking forest
pathologist named Dr. Erik Jorgensen, who was conducting research on tree
diseases, including DED, at the University of Toronto. Prevention and tree-protection
measures had been one of the main focuses of his work for nearly a decade. In the
1950s, he estimated that ninety percent of the trees on the University of Toronto St.
George campus were American elms (Ulmus americana) vulnerable to DED (Dean,
2009). As a researcher, he witnessed the devastation that DED caused while
recognizing that the problem could have been mitigated by proper tree management
and care. Dr. Jorgensen and Brigadier J. F. Westhead lobbied municipal politicians
and representatives to create a united front against DED, establishing the Dutch Elm
Disease Control Committee for Metro Toronto in 1962.
Eventually, the loss of elms and tree canopy in urban areas was so signi�cant that Dr.
Jorgenson coined the term "urban forestry" in 1974 and pioneered the �rst urban
forestry program at the University of Toronto. Once de�ned, urban forests became
more recognized and urban tree management and similar departments were created
in larger cities, such as Toronto in 1965 and Montreal in 1977 (Jorgensen, 1974;
Desbiens, 1998). While these departments were under various names, such as parks
and recreation, they started to practice ‘urban forestry’ and related activities. In many
cities, these departments have since been re-named and are now urban forestry
departments, while some cities still practice ‘urban forestry’ under various municipal
departments (Puric-Mladenovic & Bardekjian, 2023) or agencies within a city. For
example, urban forests and trees in Ottawa are managed by several bodies, including
the National Capital Commission, the Federal Ministry of Transportation, Hydro
Ottawa, Planning, Infrastructure and Economic Development Department, and the
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Public Works and Environmental Services Department, to name a few (Bider, 2024).
In the mid-1970s, with the expansion of urban forestry across larger municipalities,
the Dutch Elm Disease Control Committee of Toronto (piloted by Dr. Jorgensen)
expanded into the Ontario Shade Tree Council, a province-wide network with a
broader mandate of managing trees in the urban area (Dean, 2009). About the same
time, the �rst federal urban forestry program called 'A Forest for Man’ started. While it
only lasted until 1979, the movement continued with the �rst International
Conference on Urban Forests that same year, which was held at Laval University
(Rosen & Tree Canada, 2015).
In the next couple of decades, while many municipalities across Canada had
developed urban forestry or urban forestry-related departments, there was still a lack
of cohesion across provincial and national scales. To address this gap, an NGO
called Tree Canada was established in 1992 (Tree Canada, 2024). Being the only
national NGO with an urban forestry portfolio, Tree Canada partnered with the
Ontario Shade Tree Council as well as professionals pioneering urban forestry in
Canada to organize the �rst Canadian Urban Forest Conference (CUFC) in 1993 in
Winnipeg, Manitoba. Tree Canada continued to organize bi-annual conferences,
allowing professionals from across Canada to gather and share new innovations and
knowledge regarding urban forestry practices, policies, and research (Tree Canada,
2024; Tree Canada, 1993). As an outcome of the 5th Canadian Urban Forest
Conference in 2003, the Canadian Urban Forest Network (CUFN) Listserv for urban
forestry was formed and the Canadian Urban Forest Network was established as a
result (CANUFNET, 2024; CUFN, n.d.).
Urban forestry in Canada continued to evolve from the 1990s to the early 2000s.
Another urban forest vulnerability wake-up call came in the early 2000s due to the
impact of the Emerald Ash Borer (EAB) and the loss of ash trees across Ontario and
Quebec. Once again, the loss of urban trees prompted increased interest in the
conservation of trees, resulting in another jump in urban forestry programs across
municipalities. In addition, urban forests and urban forestry were integrated for the
�rst time into Canada's National Forest Strategy for 2003-2008 (NFSC, 2003). Since
2010, urban forestry as a �eld has grown across Canada, and about 50% of
municipalities with a population greater than 3,000 are funding some form of urban
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forestry or urban greening department (Puric-Mladenovic & Bardekjian, 2023).
As new environmental and social issues arise in urban areas across Canada, public
interest in urban forest conservation and community stewardship of trees is
increasing. The goals and values of urban forestry are continually evolving. What
initially started as a response to pest control has expanded to include various
aspects of urban trees, their value, and management. New topics have emerged,
such as green infrastructure, asset management involving trees, and natural climate
solutions. Urban forestry in Canada has a rich history, and it continues to develop
alongside the growth and intensi�cation of urban areas as well as public awareness
about trees and urban forests.
Resources
Andresen, J. W., & Swaigen, J. (1978). Urban tree and forest legislation in Ontario (No. 0-X–282). Canadian
Forestry Service.
Artelle, K. A., Zurba, M., Bhattacharyya, J., Chan, D. E., Brown, K., Housty, J., et al. (2019). Supporting
resurgent indigenous-led governance: a nascent mechanism for just and effective conservation.
Biological Conservation, 240:108284.
https://doi.org/10.1016/j.biocon.2019.108284
Canadian Society of Landscape Architecture. (n.d.). Urban Canopy Resources.
https://www.csla-aapc.ca/mission-areas/urban-canopy-resources
Canadian Urban Forest Network (CANUFNET). (2024). Canadian Urban Forest Network (CUFN) Listserv.
http://list.web.net/lists/listinfo/canufnet
Canadian Urban Forest Network (CUFN). (n.d.). Canadian Urban Forest Network – Canada's largest
network of urban forestry professionals.
https://treecanada.ca/research-engagement/canadian-urban-forest-network/
Dean, J. (2009). Seeing trees, thinking forests: Urban Forestry at the University of Toronto in the 1960s. In
A. A. MacEachern & W. J. Turkel, Method and meaning in Canadian environmental history.
Desbiens, E. (1988). Urban Forestry in Quebec. Journal of Agriculture, 14(1), 24-26. DOI
https://doi.org/10.48044/jauf.1988.007
Dietz, S., Beazley, K. F., Lemieux, C. J., St Clair, C., Coristine, L., Higgs, E., et al. (2021). Emerging issues for
protected and conserved areas in Canada. Facets 6, 1892–1921.
https://doi.org/10.1139/facets-2021-0072
Sources
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Jorgensen, E. (1974). Towards an Urban Forestry Concept. Proceedings of the 10th Commonwealth
Forestry Conference. Ottawa, Canada; Forestry Service.
Mansuy, N., Staley, D., Alook, S., Parlee, B., Thomson, A., Littlechild, D. B., et al. (2023). Indigenous
protected and conserved areas (IPCAs): Canada's new path forward for biological and cultural
conservation and indigenous well-being. Facets 8, 1–16.
https://doi.org/10.1139/facets-2022-0118
Moola, F., Jolly, H., Borah, J. and Roth, R. (2024). The potential for Indigenous-led conservation in
urbanized landscapes in Canada. Frontiers in Human Dynamics, 6, 1340379.
https://doi.org/10.3389/fhumd.2024.1340379
National Forest Strategy Coalition (NFSC). (2003). National Forest Strategy 2003-2008 – a sustainable
forest, the Canadian commitment. 27pp.
https://cfs.nrcan.gc.ca/pubwarehouse/pdfs/23638_e.pdf
Ontario Urban Forest Council (OUFC). (2023). History of OUFC - Ontario Urban Forest Council (OUFC).
https://oufc.org/index.php/history-of-oufc/
Puric-Mladenovic, D. and Bardekjian, A. (2023). Canada's Urban Forest Footprint: Mapping the Extent and
Intensity of Urban Forestry Activities. Forests in Settled & Urban Landscapes applied science and
research lab. Daniels Faculty, University of Toronto. John H. Daniels Faculty of Architecture, Landscape
and Design, University of Toronto.
Reo, N. J., Whyte, K. P ., McGregor, D., Smith, M. A., and Jenkins, J. F. (2017). Factors that support
indigenous involvement in multi-actor environmental stewardship. AlterNative 13, 58–68.
https://doi.org/10.1177/1177180117701028
Rosen, M. & Tree Canada. (2015). A brief historical perspective of urban forests in Canada. In Urban
Forest Series: Vol. Volume I (pp. 27–32).
http://treecanada.ca/wp-content/uploads/2017/10/Article-2-EN-2015-Historical-Perspective-Urban-
Forests.pdf
Townsend, J., and Roth, R. (2023). Indigenous and decolonial futures: indigenous protected and
conserved areas as potential pathways of reconciliation. Frontiers in Human Dynamics, 5, 970.
https://doi.org/10.3389/fhumd.2023.1286970
Tree Canada. (2024). Who we are - Tree Canada. Tree Canada.
https://treecanada.ca/about-us/who-we-are/
Tree Canada. (1993). Proceedings of the First Canadian Urban Forest Conference – May 30-June 2, 1993.
Canadian Forestry Association: Ottawa.
Youdelis, M., Townsend, J., Bhattacharyya, J., Moola, F., and Fobister, J. B. (2021). Decolonial
conservation: establishing indigenous protected areas for future generations in the face of extractive
capitalism. Journal of Political Ecology, 28:4716.
https://doi.org/10.2458/jpe.4716
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Benefits of Urban Forests
Urban trees, individually or collectively as urban forests, provide diverse ecological
services, some of which can be monetized and provide economic value to society.
Ecological services of urban forests, in general, include regulating, provisioning,
supporting, and cultural services (Filho et al., 2020). Urban forest regulating services
have the ability to moderate the environment via climate regulation, �ood control, air
pollution removal, and carbon storage. Provisioning services provide tangible
products such as food, water, wood, and medicinal plants (Visentin, 2019).
Supporting services are natural processes that sustain life, including nutrient cycling,
soil creation, biodiversity, habitat, oxygen production, photosynthesis, biomass
production, erosion control, and the water cycle (Przewoźna, 2022). For example,
urban forests support biodiversity through pollination and seed dispersal, and
provide wildlife habitats for birds, mammals, and invertebrate species (FAOUN, 2022;
Pickett et al., 2016). Cultural services of urban forests bene�t humans when they
directly or indirectly interact with trees. Compared to regulating, provisioning, and
supporting services, cultural services are often harder to quantify and monetize, yet
they improve the quality of human life by providing aesthetic, recreational, and
restorative values (NWF, n.d.). The practice of urban forestry, which includes
management and planning associated with maintaining and protecting urban forests
Highlights
Ecological and economic value
Urban forests regulate climate, improve air quality, support biodiversity, and provide
economic bene�ts.
Climate and urban sustainability
Canadian cities are expanding urban forests to combat climate change, enhance
health, and improve livability.
Quantifying urban forest benefits
Canadian municipalities use a range of tools to assess urban forest structure, map
ecological services, and guide decision-making.
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and green spaces, also supports a steady �ow of ecological services to society (Tree
Canada, 2019; Salmond et al., 2016). It also provides economic bene�ts in terms of
job creation, reduced infrastructure maintenance, and other direct and indirect
bene�ts (Filho et al., 2020).
Climate & Urban Sustainability
With rising concerns about climate instability and government commitments to
environmental sustainability and biodiversity conservation, urban forests and urban
green spaces are being recognized as natural climate solutions and integral tools for
improving the quality of life in urban areas. With nearly 75% of Canadians living in
urban/metropolitan areas (StatCan, 2022), integrated land use planning and urban
forest management efforts are required to maintain the quality of urban life and city
livability in the face of climate change and environmental challenges.
As the negative impacts of climate change, urban sprawl, and intensi�ed
development continue to grow, public awareness of environmental issues is also on
the rise. Many people recognize the importance of urban forests and the ecological
services they provide. As a result, urban forestry has become a prominent topic in
discussions related to municipal policy and decision-making across Canada.
Recognizing these challenges and the need to increase urban forest cover to obtain
the bene�ts that trees provide, Canadian cities have set some of the most ambitious
urban forest canopy goals. For example, many major Canadian cities, including
Vancouver, Halifax, Montreal, Ottawa, and Winnipeg, have pledged to increase urban
tree canopy cover by more than 25% by 2030 (CCI, 2021), and Toronto has set an
ambitious 40% target by 2050. For example, with over 11.5 million trees and around
1,500 urban parks and green spaces, Toronto has been integrating urban forest into
urban land use fabric with an aim to become one of the most forested cities in
Canada (City of Toronto, 2024; City of Toronto, n.d.).
The bene�ts of urban forests across various land uses and green spaces are far-
reaching in Toronto. According to multiple health indicators, notably cardiovascular
and respiratory health (StatCan, 2019), Toronto is one of the healthiest cities in
Canada. Other Canadian cities, such as Ottawa, Winnipeg, and Metro Vancouver, are
also developing and implementing management, operations, maintenance, and
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protection strategies to manage urban green spaces and receive the full bene�ts of
urban forests and green spaces. Ecological services provided by urban forests and
green spaces have been shown to vastly improve the quality of life in urban areas by
also improving mental health and promoting social cohesion (Tree Canada, 2019).
Epidemiological studies have shown that even brief experiences in natural settings
can reduce neural activity in the subgenual prefrontal cortex, indicating a reduction in
feelings of stress and anxiety (Bratman et al., 2015). When congruent experiments
were conducted in urban areas lacking nature, the same effects were not observed
(Bratman et al., 2015). Medical studies highlight urban naturalized areas and green
space as essential for enhancing mental health in urban environments (Astell-Burt &
Feng, 2019; Rugel, Carpiano, Henderson & Brauer, 2019). A direct link has also been
drawn between tree canopy cover and social capital, where urban neighbourhoods
with more tree cover have more social networks and a greater sense of cohesion,
and also further bene�t from improved mental health (Holtan, Dieterlan & Sullivan,
2014).
When access to treed green spaces is available, Canadians tend to use them,
increasing the likelihood of social interaction while encouraging diverse recreation
activities across all demographic spectrums (Koley, Kuo & Sullivan, 1997). Proximity
and availability of green space within urban areas encourage physical activity, which
further bene�ts the mental health of urban residents while improving general
indicators of physical health (FAOUN, 2022). Greener urban areas have shown a
positive association with better cardiovascular health, lower blood pressure, reduced
incidences of obesity, asthma and diabetes, and improved memory and attention
span (Richardson et al., 2013; Pretty et al., 2006; Kim, Lee & Ramos, 2021; Tree
Canada, 2024; Kardan et al., 2015).
In addition, urban trees are also crucial bio�lters because they capture atmospheric
pollutants and particulates in city air, keep the air cleaner, and reduce the severity of
respiratory-related conditions and illnesses (Wolf et al., 2020). Urban trees in Canada
are responsible for sequestering and neutralizing around 2.5 million metric tonnes of
atmospheric carbon every year (Steenberg et al., 2023). Trees can reduce ambient
temperatures by 2-5 degrees Celsius in urbanized areas, combating negative health
outcomes related to high temperatures in summer months (NRCan, 2016).
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Quantifying Urban Forest Benefits
Urban areas with extensive and diverse green spaces and strong urban forestry
practices bene�t from increased urban forest ecological services (FAOUN, 2022).
Overall, urban forests across cities in Canada provide various bene�ts, and many
municipalities have quanti�ed and mapped urban forest services (i-Tree, 2024; Town
of Oakville, 2016). Urban forest inventory and monitoring are a foundational step
toward quantifying urban forests and the bene�ts they provide. Depending on the
method and tools used, it is possible to estimate and quantify urban forest services
and track them over time by utilizing urban canopy mapping, tree species
measurements, and tree health data.
One such tool used for estimating ecological services is i-TreeEco, developed by the
USDA Forest Service. i-Tree provides forestry analysis tools at the level of individual
trees to entire stands, bene�ts assessment tools, and a database to support
quantifying forest structure and guide decision-making (i-Tree, n.d.). i-Tree has been
used across over 20 municipalities in Canada to estimate ecological services (i-Tree,
n.d.).
Resources
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Holtan, M., Dieterlen, S., and Sullivan, W. (2014). Social Life Under Cover: Tree Canopy and Social Capital
in Baltimore, Maryland. Environment and Behavior, 47, 1-24.
https://journals.sagepub.com/doi/full/10.1177/0013916513518064
Kim, J., Lee, S., and Ramos, W. (2021). Investigating the Relationship Between Accessibility of Green
Space and Adult Obesity Rates: A Secondary Data Analysis in the United States. Journal of Preventative
Medicine and Public Health, 54(3),208-217.
https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8190549/
Livesly, S.J., McPherson, E.G. & Calfapietra, C. (2016). The Urban Forest and Ecosystem Services:
Impacts on Urban Water, Heat, and Pollution Cycles at the Tree, Street, and City Scale. Journal of
Environmental Quality, 45(1), 119-124.
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Nesbitt, L., Hotte, N., Barron, S., Cowan, J., Sheppard, S.R.J. (2017). The social and economic value of
cultural ecosystem services provided by urban forests in North America: A review and suggestions for
future research. Urban Forestry & Urban Greening, 25, 103-111.
https://doi.org/10.1016/j.ufug.2017.05.005
ParaSpace. (2021). Urban Forests – What are they and how do they bene�t us?
https://www.paraspaceinc.com/blog/urban-forests
Pickett, S.T.A., M.L. Cadenasso, D.L. Childers, M.J. McDonnell, and W. Zhou. 2016. Evolution and future of
urban ecological science: ecology in, of, and for the city. Ecosystem Health and Sustainability 2(7),
e01229.
https://doi.org/10.1002/ehs2.1229
Pretty, J., Peacock, J., Sellens, M., & Gri�n, M. (2005). The mental and physical health outcomes of green
exercise. International Journal of Environmental Health Research, 15(5), 319–337.
https://doi.org/10.1080/09603120500155963
Przewoźna, P ., Mączka, K., Mielewczyk, M. et al. (2022). Ranking ecosystem services delivered by trees in
urban and rural areas. Ambio, 51(9),2043-2057.
https://doi.org/10.1007%2Fs13280-022-01722-2
Richardson, E. A., Pearce, J., Mitchell, R., ans Kingham, S. (2013). Role of physical activity in the
relationship between urban green space and health. Public Health, 127(4),318-324.
https://doi.org/10.1016/j.puhe.2013.01.004
Rollins, R. (2008). City of Nanaimo Urban Forest Study – City Trees and You: Results of Public Opinion
Survey. City of Nanaimo.
https://www.nanaimo.ca/docs/services/home-and-property/urbanforeststudy.pdf
Rugel, E. J., Carpiano, R. M., Henderson, S. B., & Brauer, M. (2019). Exposure to natural space, sense of
community belonging, and adverse mental health outcomes across an urban region. Environmental
Research, 171, 365–377.
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Salmond, J.A., Tadaki, M., Vardoulakis, S. et al. (2016). Health and climate related ecosystem services
provided by street trees in the urban environment. Environmental Health, 15(Suppl 1), S36.
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Statistics Canada. (2019). Canadian Community Health Survey: Public use microdata �le, 2015/2016
https://www150.statcan.gc.ca/n1/daily-quotidien/190107/dq190107b-eng.htm
Statistics Canada. (2022). Canada's large urban centres continue to grow and spread.
https://www150.statcan.gc.ca/n1/daily-quotidien/220209/dq220209b-eng.htm
Steenberg, J.W.N., Ristow, M., Duinker, P .N. et al. (2023). A national assessment of urban forest carbon
storage and sequestration in Canada. Carbon Balance and Management,18(11).
https://doi.org/10.1186/s13021-023-00230-4
van den Bosch, M. (2017). Impacts of urban forests on physical and mental health and wellbeing. In:
Ferrini, F., Konijnendijk van den Bosch, C. C. & Alessio, F. (eds). Routledge handbook of urban forestry.
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physical-mental-health-wellbeing-matilda-van-den-bosch
Visentin, J. (2019). Urban Food Forestry (UFF), its Role in Canadian Urban Forestry Management Plans,
and Integration into Thunder Bay, Ontario. Thesis submitted to Lakehead University.
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Wolf, K.L., Lam, S.T., McKeen, J.K., et al. (2020). Urban Trees and Human Health: A Scoping Review.
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Bosch, C. C. & Alessio, F. (eds). Routledge handbook of urban forestry. Routledge: New York. 65-81.
Chapter 5. ISBN 9781315627106.
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forestry-metro-nature-kathleen-wolf
Ziter, C.D., Pedersen, E.J., Kucharik, C.J., and Turner, M.G. (2019). Scale-dependent interactions between
tree canopy cover and impervious surfaces reduce daytime urban heat during summer. Proceedings of
the National Academy of Sciences, 116(15) 7575-7580,
https://doi.org/10.1073/pnas.1817561116
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Trees and Urban Heat Island (UHI)
One of the many bene�ts of the urban forest is its ability to ameliorate urban
microclimate, cool large or small areas, and bene�t human health. Cities tend to have
higher ambient air temperatures than rural areas due to the high heat absorption
capacity of various building materials (GoC, 2022). Concrete, asphalt, and cement
absorb sunlight and trap heat much more effectively than trees, parks, and �elds,
leading to higher air temperatures in built-up areas (USEPA, 2024). Cities also
produce their own heat, which is released by vehicles, air conditioners, and
machinery (Climate Atlas of Canada, n.d.). Trees and green spaces can improve
urban climate, reduce surface and air temperatures, cool the environment, improve
the comfort of citizens by providing shade, and mitigate the effects of urban heat
islands through evapotranspirative cooling (Yin et al., 2024; Schwaab et al., 2021).
The combined effects of evapotranspiration and shading can reduce summer
temperatures by 1–5°C (USEPA, 2008).
The urban heat island effect in cities across the globe is ampli�ed by climate
warming. Urban forests and green infrastructure are recognized as nature-based
solutions and natural capital investments for addressing climate change impacts
Highlights
Urban Heat Island (UHI) effect
Urban areas experience higher temperatures than rural areas.
Urban forests
Trees and green spaces help cool cities by reducing air temperatures, absorbing
sunlight, and providing shade.
Impact of urban greenery
Cities with more trees see greater temperature reductions than those with fewer
trees.
Health and cost benefits
Cooler cities experience fewer heat-related illnesses and lower energy costs.
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(IFC, 2024). Canada, like many other urbanized countries, is facing challenges related
to climate change and the urban heat island effect. These issues include the impacts
of heat on human health, infrastructure, biodiversity, and wildlife. Urban areas in
British Columbia and Quebec have experienced extreme heat, leading to an increase
in heat-related illnesses and mortality during heat waves in recent years (Poitras et
al., 2018; Beugin et al., 2023). The extent and distribution of urban tree canopy in
Canadian cities can signi�cantly bene�t both human and environmental health,
especially during the summer months. As a result, urban trees and green spaces are
becoming increasingly valuable as climate change continues to drive extreme
weather events, such as heat waves and temperature �uctuations (Health Canada,
2020).
UHI: Trees and Air Cooling
Many studies have documented across the globe that during the summer peak, air
temperature in large cities with heat-absorbing surfaces and lack of green space
could be as much as 10-15°C hotter than surrounding areas, while at night, the
difference can be up to 12°C (Joint Research Centre, 2022; Mentaschi et al., 2022).
This higher air temperature across urban areas is referred to as the urban heat island
effect (UHIE). The UHIE phenomenon also impacts many cities across Canada. For
example, it reached the highest daytime value of 7.25°C for Vancouver and the
highest nighttime UHI intensity at 4.36°C for Toronto (Duan, Agrawal, Sanchez-
Azofeifa, and Welegedara, 2024). When gray infrastructure absorbs heat from the
sun, this heat is retained and slowly released even after the sun goes down, which
keeps city temperatures higher during the night (USEPA, 2024).
Urban forests, trees, and urban greenery can help reduce UHIE by cooling city air
temperatures through sunlight absorption, evapotranspiration, and interception of
particulate matter. Evapotranspiration, the process that adds water to the air through
evaporation from plants and surrounding soil, can reduce ambient air temperatures
by 1-5°C (USEPA, 2024). Studies have found that greener urban areas are cooler on
average than less-green urban areas, with urban forests having daytime temperatures
about 1.5°C cooler than surrounding areas during summer months (Knight et al.,
2021). Additionally, by intercepting greenhouse gases and particulate matter
associated with air pollution from dust, car exhaust, and wild�res, urban trees use
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their leaves and needles to �lter the air and reduce ground-level temperature by
offsetting greenhouse gas emissions and reducing smog in cities (Knight et al.,
2021).
Urban tree canopies provide much-needed shade and can reduce the amount of
sunlight absorbed by gray infrastructure like buildings and roads (SFI, 2024). They
help decrease the severity of this UHI effect by intercepting sunlight before it reaches
buildings and roads. Additionally, the shade provided by urban trees can help
decrease cooling-related energy costs by up to 7% in summer months by reducing
the amount of sunlight absorbed by building exteriors, reducing cooling energy costs
(Nowak, 2017). In addition to urban forests, green roof technologies can reduce roof
surface temperature by up to 20°C, further asserting the bene�ts of vegetation and
green spaces (USEPA, 2024).
Canadian municipalities such as Kingston, Vancouver, and Surrey have successfully
implemented diverse urban forestry initiatives to combat high temperatures and
climate change. For example, Kingston’s urban forest has helped to combat the
urban heat island effect by improving thermal comfort and reducing energy
consumption associated with cooling (Guilbault, 2016). The City of Vancouver
analyzed local climate zones to optimize tree planting locations, ensuring that urban
trees contribute effectively to maintaining outdoor thermal comfort (Aminipouri et al.,
2019); this approach highlights the value of local and site-speci�c urban forest
planning strategies. Additionally, the City of Surrey has engaged residents in urban
heat readiness by developing a conversation guide emphasizing the role of urban
trees in mitigating heat waves and improving community resilience (City of Surrey,
2021). These are some examples of novel approaches to utilizing urban forestry as a
tool to combat climate change and enhance human health in urban areas in Canada.
UHI: Human Health
As the climate changes in Canada, the role of trees in cooling urban areas and
supporting human health becomes increasingly important. Urban forests serve as a
crucial climate change mitigation measure. With rising summertime temperatures,
the ability of trees to cool the air and provide shade is an essential resource for
public health in Canada.
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Heat waves and excessive temperatures yearly contribute to many illnesses and
deaths in Canadian cities; these high temperatures can induce heat cramps,
respiratory di�culties, heat stroke, and even heat-related mortality (GoC, 2020; Chen
et al., 2016). By increasing daytime temperatures and reducing nighttime cooling, the
urban heat island effect is responsible for over 45 deaths in Canada annually
(StatCan, 2024). Young children under the age of 5, older people over the age of 65,
people with chronic illnesses, homeless people, and low-income, low canopy cover
communities are particularly at risk when it comes to heat-related illnesses and
mortality (Climate Atlas of Canada, n.d.; Whittingham et al., 2022).
Urban trees can reduce the severity of these health hazards through air cooling and
shade provision, and the City of Toronto became the �rst Canadian municipality to
develop a policy speci�cally related to urban trees and heat. In collaboration with
many city departments and NGOs such as Parks, Forestry and Recreation, Child
Services, Tree Canada, and LEAF, Toronto Public Health formed an interdisciplinary
team to develop the �rst Shade Policy in Canada (City of Toronto, 2007, 2010). This
initiative, led by the Toronto Cancer Prevention Coalition between 2005-2015, is the
�rst of its kind. It represents an important step towards preparing for a warmer
climate with increased frequency and duration of extreme heat events.
The Toronto Cancer Prevention Coalition's shade policy initiative is a testament to the
importance of shade in protecting against skin cancer. Integrating shaded areas,
especially where the shade is created by trees, into urban parks, streets, schools, and
facilities draws an important connection between urban forestry, urban planning, and
public health (Sivarajah, Thomas & Smith, 2020). This policy o�cially recognized the
value of shade trees in cities, especially large trees with dense canopies, in providing
shade and lowering air temperatures, and created a policy framework to incorporate
shade provision into planning, bylaws, and climate change and energy action plans
(City of Toronto, 2010).
Resources
Canadian Institute for Climate Choices (CICC). (2021). Growing Forests in a City – Urban Tree Study.
Canadian
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https://climatechoices.ca/wp-content/uploads/2021/05/Urban-Trees-study_May11b.pdf
City of Surrey. (2021). Urban heat ready: A conversation guide for Surrey residents.
https://www.surrey.ca/
Climate Atlas of Canada. (n.d.) Urban Heat Island Effect. Prairie Climate Centre.
https://climateatlas.ca/urban-heat-island-effect
Climate Atlas of Canada. (n.d.) Forests and Climate Change. Prairie Climate Centre.
https://climateatlas.ca/urban-forests-and-climate-change
Government of Canada (GoC). (2020). Climate Change and Health - Adaptation Bulletin.
https://www.canada.ca/en/health-canada/services/environmental-workplace-health/reports-
publications/climate-change-health/climate-change-health-adaptation-bulletin-number-1-
november-2009-revised-december-2010-health-canada-2009.html
Government of Canada (GoC). (2022). Urban heat islands tools and resources.
https://www.canada.ca/en/health-canada/services/climate-change-health/urban-heat-islands-tools-
resources.html
Health Canada. (2020). Reducing Urban Heat Islands to Protect Health in Canada: An Introduction for
Public Health Professionals.
https://www.canada.ca/content/dam/hc-sc/documents/services/health/publications/healthy-living/
reducing-urban-heat-islands-protect-health-canada/Reducing-Urban-Heat-EN.pdf
HealthyPlan. (n.d.). HealthyPlan City – Explore Equity in Your City.
https://healthyplan.city/en
Natural Resources Canada. (2020). The State of Canada’s Forests. Annual Report 2019. Canadian Forest
Service, Ottawa. 80 p.
https://publications.gc.ca/site/eng/9.505771/publication.html
Toronto Public Health. (2014). Partners in Action - Shade Policy for the City of Toronto [video].
https://www.youtube.com/watch?v=Jg1jD6E43Z4
Wang, Y., & Akbari, H. (2016). The effects of street tree planting on Urban Heat Island mitigation in
Montreal. Sustainable Cities and Society, 27, 122–128.
https://doi.org/10.1016/j.scs.2016.04.013
United States Environmental Protection Agency (USEPA). (2008). Reducing urban heat islands:
Compendium of strategies [Draft].
https://www.epa.gov/heat-islands/heat-island-compendium.
United States Environmental Protection Agency (USEPA). (2024). Learn About Heat Islands.
https://www.epa.gov/heatislands/learn-about-heat-islands
United States Environmental Protection Agency (USEPA). (2024). Using Trees and Vegetation to Reduce
Non-Canadian
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Heat Islands.
https://www.epa.gov/heatislands/using-trees-and-vegetation-reduce-heat-islands
USDA Northwest Climate Hub. (n.d.). Northwest Urban Forests and Climate Change. United States
Department of Agriculture.
https://www.climatehubs.usda.gov/hubs/northwest/topic/northwest-urban-forests-and-climate-
change
Joint Research Centre. (2022). Cities are often 10-15 °C hotter than their rural surroundings. European
Commission.
https://joint-research-centre.ec.europa.eu/jrc-news-and-updates/cities-are-often-10-15-degc-hotter-
their-rural-surroundings-2022-07-25_en
Aminipouri, M., Rayner, D., Lindberg, F., Thorsson, S., Knudby, A. J., Zickfeld, K., Middel, A., & Krayenhoff, E.
S. (2019). Urban tree planting to maintain outdoor thermal comfort under climate change: The case of
Vancouver’s local climate zones. Building and Environment, 158, 226–236.
https://doi.org/10.1016/j.buildenv.2019.05.022
Beugin, D., Clark, D., Miller, S., Ness, R., Pelai, R. and Wale, J. (2023). The case for adapting to extreme
heat: Costs of the 2021 B.C heat wave. Canadian Climate Institute.
https://climateinstitute.ca/wp-content/uploads/2023/06/The-case-for-adapting-to-extreme-heat-costs-
of-the-BC-heat-wave.pdf
Boudreault, J., Lavigne, É., Campagna, C & Chebana, F. (2024). Estimating the heat-related mortality and
morbidity burden in the province of Quebec, Canada. Environmental Research, 257,119347.
https://doi.org/10.1016/j.envres.2024.119347
Chen, H., Wang, J., Li, Q., Yagouti, A., Lavigne, E., Foty, R., ... Copes, R. (2016). Assessment of the effect of
cold and hot temperatures on mortality in Ontario, Canada: a population-based study. CMAJ Open, 4(1),
E48.
http://www.cmajopen.ca/content/4/1/E48.abstract
City of Vancouver. (n.d.). VanPlay Strategic Bold Moves, Equity Tool: Initiative Zones.
https://vancouver.ca/�les/cov/vanplay-strategic-bold-moves-equity-chapter.pdf
City of Toronto. (2007). Policy for the Provision of Shade at Parks, Forestry and Recreation Sites.
https://www.toronto.ca/legdocs/mmis/2008/pe/bgrd/background�le-10540.pdf
Duan, Y., Agrawal, S., Sanchez-Azofeifa, A., and Welegedara, N. (2024). Urban Heat Island Effect in
Canada: Insights from Five Major Cities [pre-print].
http://dx.doi.org/10.2139/ssrn.4965331
Evergreen. (2022). Feeling the heat? Here’s how cities are �ghting the Urban Heat Island effect.
https://www.evergreen.ca/stories/feeling-the-heat-heres-how-cities-are-�ghting-the-urban-heat-island-
effect/
Further Reading
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Evergreen. (2024). AI for the Resilient City.
https://www.evergreen.ca/impacts/ai-for-the-resilient-city/
Graham, D. A., Vanos, J. K., Kenny, N. A. and Brown, R. D. (2016). The relationship between
neighbourhood tree canopy cover and heat-related ambulance calls during extreme heat events in
Toronto, Canada. Urban Forestry & Urban Greening, 20, 180-186.
https://doi.org/10.1016/j.ufug.2016.08.005
Guilbault, S. (2016). KINGSTON: Using the urban forest to mitigate the urban heat island effect (pp. 59–62).
The Institute for Catastrophic Loss Reduction.
https://www.iclr.org/wp-content/uploads/PDFS/11_Kingston.pdf
Han, L., Heblich, S.,Timmins, C., and Zylberberg, Y. (2023), Cool Cities: The Value of Green Infrastructure.
NBER Working Paper 32063.
https://cepr.org/voxeu/columns/cool-cities-value-urban-trees
Health Canada. (2020). Reducing Urban Heat Islands to Protect Health in Canada: An Introduction for
Public Health Professionals.
https://www.canada.ca/content/dam/hc-sc/documents/services/health/publications/healthy-living/
reducing-urban-heat-islands-protect-health-canada/Reducing-Urban-Heat-EN.pdf
International Finance Corporation, Cool Coalition, UN Environment Program. (2024). Cooler Finance
Mobilizing Investment for the Developing World’s Sustainable Cooling Needs [Final Report].
https://www.ifc.org/content/dam/ifc/doc/2024/cooler-�nance-report.pdf
Knight, T., Price, S., Bowler, D. et al. How effective is ‘greening’ of urban areas in reducing human
exposure to ground-level ozone concentrations, UV exposure and the ‘urban heat island effect’? An
updated systematic review. Environmental Evidence 10, 12 (2021).
https://doi.org/10.1186/s13750-021-00226-y
Mentaschi, L., Duveiller Bogdan, G.H.E., Zulian, G., Corban, C., Pesaresi, M., Maes, J., Stocchino, A. and
Feyen, L. (2021). Global long-term mapping of surface temperature shows intensi�ed intra-city urban
heat island extremes. Global Environmental Change, 72, 102441.
https://doi.org/10.1016/j.gloenvcha.2021.102441.
Nowak, D. J. (2017). Urban Trees Save Billions of Dollars Through Reduced Energy Costs. United States
Department of Agriculture Forest Service. Northern Research Station, NY.
https://research.fs.usda.gov/nrs/news/highlights/urban-trees-save-billions-dollars-through-reduced-
energy-costs
Poitras, A., Austin, S., Barrow, E., Campagna, C., Chaumont, D., Gosselin, P . and Yagouti, A. (2018).
Extreme heat waves in Québec. Climate Data.
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Sivarajah, S., Thomas, S. C. & Smith, S. M. (2020). Evaluating the ultraviolet protection factors of urban
broadleaf and conifer trees in public spaces. Urban Forestry & Urban Greening, 51, 126679.
https://doi.org/10.1016/j.ufug.2020.126679
Schwaab, J., Meier, R., Mussetti, G. et al. The role of urban trees in reducing land surface temperatures in
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European cities. Nature Communications, 12, 6763 (2021).
https://doi.org/10.1038/s41467-021-26768-w
Standards Council of Canada (SCC). (2022). Urban Heat Island Mapping Workshop: What We Heard.
Government of Canada.
https://scc-ccn.ca/system/
�les/2024-05/20221206_uhi_what_we_heard_report_�nal_en_2023-04-04.pdf
Statistics Canada (StatCan). (2024). Extreme heat events were associated with elevated risk of dying in
Canada's largest cities from 2000 to 2020. Health Reports, June 2024.
https://www150.statcan.gc.ca/n1/daily-quotidien/240619/dq240619b-eng.htm
Toronto Cancer Prevention Coalition, Toronto Public Health, City of Toronto. (2010). Shade Guidelines.
https://www.toronto.ca/wp-content/uploads/2019/08/8ecf-
AODA_Shade_Guidelines_2010_Final_Report-002.pdf
Whittingham, E., Vabi, V., Lalloo S. and Hak, S. (2022). Canada's Urban Forests: Bringing the Canopy to All.
Nature Canada.
https://naturecanada.ca/wp-content/uploads/2022/09/Nature-Canada-Report-Tree-Equity.pdf
Yin, Y., Li, S., Xing, X., Zhou, X., Kang, Y., Hu, Q., & Li, Y. (2024). Cooling Bene�ts of Urban Tree Canopy: A
Systematic Review. Sustainability, 16(12), 4955.
https://doi.org/10.3390/su16124955
Ziter, C.D., Pedersen, E.J., Kucharik, C.J., and Turner, M.G. (2019). Scale-dependent interactions between
tree canopy cover and impervious surfaces reduce daytime urban heat during summer. Proceedings of
the National Academy of Sciences, 116(15) 7575-7580,
https://doi.org/10.1073/pnas.1817561116
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Air Quality and Climate Change
Urban forests, providing multiple ecosystem services, offer a natural and sustainable
solution for improving the environmental quality of urban areas through air
puri�cation, temperature regulation, and carbon sequestration. Trees, individually and
collectively as part of urban forests, play a crucial role in enhancing air quality by
�ltering pollutants such as nitrogen dioxide (NO) and sulphur dioxide (SO ). By
absorbing these pollutants, trees metabolize and convert them into less harmful
substances. They also trap particulate matter (PM) on their leaves, needles, and bark,
effectively reducing their concentrations in the air. Research by Nowak et al. (2018)
has shown that urban forests in Canada remove substantial amounts of air
pollutants annually, leading to signi�cant improvements in air quality and co-
bene�ting public health. An urban tree can absorb anywhere between 10 and 40 kg of
CO each year and can intercept up to 4.5 kg of pollutants such as NO , SO , dust,
soot, and smoke (EcoTree, 2024; Vallet, 2005; Greener Seasons, 2022).
Urban forests play a crucial role in helping communities deal with the impacts of
Highlights
Urban forests and air quality
Trees purify the air by trapping and �ltering pollutants like nitrogen, sulphur, and
carbon dioxide.
Carbon sequestration
Urban trees help offset signi�cant greenhouse gas emissions through carbon
dioxide sequestration.
Management and planning
Proper management, urban planning, and careful tree species selection are
essential to maximizing air quality and climate bene�ts.
Targeted planting areas
Tree planting in heat-prone, high-tra�c, and low-canopy areas should be prioritized
to improve air quality.
2 2
2 2 2
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climate change. In addition to their air-purifying functions, trees aid in mitigating the
urban heat island (UHI) effect, which exacerbates air pollution levels. Trees cool
down urban areas by providing shade and releasing moisture through transpiration,
thereby reducing ground-level ozone formation (McDonald et al., 2016). These
cooling bene�ts are signi�cant as cities face warmer summers and more frequent
and intense heat waves. Furthermore, the cooling effect of trees can result in lower
energy usage in buildings, indirectly reducing greenhouse gas emissions. For
instance, research conducted in Montreal demonstrated that planting more trees
along streets could signi�cantly reduce the UHI effect, leading to lower temperatures
and improved thermal comfort (Wang & Akbari, 2016).
Urban forests also contribute signi�cantly to climate change mitigation by
sequestering carbon dioxide (CO2) from the atmosphere and acting as carbon sinks.
Canadian urban forests already store signi�cant amounts of carbon (Pasher et al.,
2014; McGovern & Pasher, 2016; Steenberg et al., 2023). Moreover, urban forests, as
a natural climate solution, have the potential to sequester and store more carbon if
the existing trees are managed effectively and new trees are planted strategically
(Drever et al., 2021).
Carbon credit projects across Canada have promoted sustainable forest
management, carbon sequestration, and biodiversity conservation. However, urban
forest carbon credit programs are less prevalent in urban areas than in rural and
boreal forest initiatives in Canada. In urban forests, due to limited space for tree
growth, soil compaction, and pollution, which impact tree longevity, tree mortality,
and ongoing carbon maintenance, urban forest carbon sequestration and storage
present unique challenges. Urban forests have a relatively small biomass for carbon
sequestration compared to rural forests. Additionally, the diverse ownership of urban
forests and the high cost of investments associated with certi�cation further
complicate the process of generating substantial carbon offset credits from urban
trees. However, the importance of carbon sequestration has been recognized, and
urban forest carbon programs offer an opportunity to enhance urban sustainability
and contribute to climate change mitigation. The Sustainable Forestry Initiative's
Urban and Community Forest Sustainability Standard and the Forest Stewardship
Council (FSC) Certi�cation standard can assist municipalities in developing
frameworks that incorporate carbon storage into their urban forest management
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plans (SFI, 2024; FSC, n.d.). The City of Mississauga attained FSC® certi�cation for
its woodlands in 2024. In Canada, there are also localized, voluntary, and self-
evaluated carbon offset programs for urban forests. These programs promote tree
preservation and planting and carbon credits on a voluntary basis (University of
Toronto, 2019).
Mitigation and Management Strategies
Maximizing these bene�ts requires effective urban forest management of the
existing trees and strategic planning and implementation of tree planting. One critical
component of planning future urban forests is appropriate tree species selection, as
different species vary in their ability to contribute to air pollution removal and
withstand changing climate conditions. Using climate analogues and vulnerability
metrics to inform tree species selection ensures that urban forests remain resilient
under future climate scenarios (Esperon-Rodriguez et al., 2022). Furthermore,
integration of urban forest management into municipal climate policies can enhance
the effectiveness of climate adaptation strategies. Aligning municipal climate change
and urban forestry policies in Canadian cities can lead to more cohesive and robust
adaptation frameworks that bene�t both urban forest and climate change mitigation
(Cheng et al., 2021).
Several Canadian municipalities have successfully implemented urban forestry
initiatives to combat air quality issues and climate change. In Kingston, the impact of
urban forests was critical in mitigating the UHI effect, improving thermal comfort,
and reducing energy consumption for cooling (Guilbault, 2016). In Vancouver, local
climate zones have been analyzed to optimize tree planting locations, ensuring that
urban trees contribute effectively to maintaining outdoor thermal comfort
(Aminipouri et al., 2019). This approach highlights the importance of local and site-
speci�c strategies in urban forest planning. Moreover, the City of Surrey has
developed a conversation guide to engage residents in urban heat readiness,
emphasizing the role of urban trees in mitigating heatwaves and improving
community resilience (City of Surrey, 2021).
Municipalities and industry professionals consider several vital recommendations to
maximize the bene�ts of urban forests, including those related to air quality.
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Sustaining healthy large-stature trees and promoting a diverse mix of long-lived and
low-maintenance tree species enhances resilience against pests, diseases, and thus
climate change while providing a more comprehensive range of ecosystem services
(Wood & Dupras, 2021). Moreover, identifying priority areas for tree planting, such as
heat-prone neighbourhoods and high-tra�c areas, can maximize air quality
improvements and thermal comfort (Chan et al., 2007). Additionally, implementing
more e�cient tree care, such as watering during droughts, can support the health of
trees and enhance their role in mitigating climate change effects. These efforts can
be supported by involving local communities in urban forestry initiatives through
education and participation programs; engaged residents are more likely to support
and care for urban trees, which can supplement municipal tree care efforts and
ensure urban forestry's long-term success and sustainability (Bourque et al., 2021).
Finally, regular monitoring and maintenance programs are essential to ensure healthy
and functional urban forests. Urban forests are indispensable assets for Canadian
cities, offering signi�cant bene�ts for improving air quality and mitigating climate
change. By strategically managing and expanding urban tree cover, municipalities
and industry professionals can enhance urban resilience, improve urban
environments, and create more livable and resilient cities (Cheng et al., 2024).
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Further Readings
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moderating summer surface temperatures in a large city. Urban Ecosystems, 20(1), 141–156.
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https://www.greenerseasons.ca/tree_facts.html#bene�ts
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Stormwater Management
Urbanization and intensive land development have signi�cantly changed the
permeability of urban landscapes and impacted their natural hydrological cycles and
processes. Cities are becoming more vulnerable to heavy rainfall events that result in
rapid runoff and �ooding (Kaykhosravi et al., 2020). With fewer natural forests and
less natural vegetation, any reduction in tree canopy cover results in increased runoff
and urban areas becoming more prone to �ooding. Urban forests, with adequate
canopy cover, structure, and composition, have the potential to improve urban
hydrology and reduce runoff (Berland et al., 2018; Kuehler, Hathaway & Tirpak, 2017;
Xiao, McPherson, Simpson & Ustin, 1998). However, to effectively manage urban
forests for improving hydrology, many cities and towns globally lack appropriate
areas for future tree planting. Canadian urban areas are no exception when it comes
to these issues of urbanization, hydrology, and tree canopy.
Trees, individually and collectively as urban forests, play a crucial role in stormwater
management. Strategically conserved, managed, and enhanced urban forests can
provide a sustainable solution for Canadian municipalities experiencing
environmental challenges. Urban trees and their canopies manage stormwater
through evapotranspiration and by physically intercepting rainfall via leaves,
Highlights
Stormwater runoff and urbanization
Impermeable surfaces in cities cause excessive stormwater runoff, increasing
�ood risks and infrastructure damage.
Role of urban forests
Trees help restore natural water cycles by intercepting rainfall, stabilizing soil, and
improving water absorption.
Stormwater management strategies
Expanding and improving urban tree canopy cover and soft surfaces is an effective
way to reduce runoff and manage stormwater.
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branches, and tree trunks, thus reducing the volume of water that reaches the ground
(Carlyle-Moses et al., 2020; Dowtin et al., 2023). However, interception and
evapotranspiration are determined by morphological characteristics of tree species,
tree size and stature, leaf area density, branching structure, and whether trees are
planted in groups or individually (Berland et al., 2018; Kuehler, Hathaway & Tirpak,
2017; Xiao, McPherson, Simpson & Ustin, 1998).
Additionally, tree roots stabilize the soil, improve soil structure and organic content,
and increase the soil’s ability to absorb and �lter water. This reduces the load on
stormwater management infrastructure, streams, and ponds, and lessens �ood risks
while mitigating erosion and sedimentation in waterways (United States
Environmental Protection Agency, 2023). Urban trees also improve overall water
quality (The Mersey Forest, 2014) by reducing runoff and toxic chemicals like metals,
fuels, solvents, and other pollutants (USEPA, 2013). Urban forests with hydrological
functions help protect properties and gray urban infrastructure by reducing �ooding
and runoff during extreme weather events, which provides signi�cant economic
bene�ts (Nesbitt et al., 2017).
Many Canadian cities have created green development standards to incorporate
trees and integrate urban forests into land use planning (see City of Toronto, 2023b;
City of Mississauga, 2012; The Town of Halton Hills, 2019). By preserving and
managing urban trees, municipalities reduce overall runoff from rainfall and increase
soil absorption capacity, thus creating a more resilient urban environment, urban
forest, and natural ecosystem (City of Mississauga, 2023; Ministry of Municipal
Affairs, 2023).
Implementation Strategies
One of the most effective strategies for managing stormwater and reducing runoff is
to increase both the coverage and quality of tree canopy. This can be accomplished
by strategically planting trees in areas such as streets, parks, private properties, and
various types of land use. To further enhance the advantages of urban forests, it is
recommended to combine tree canopy conservation and planting with other forms of
green infrastructure, such as rain gardens, green roofs, and permeable pavements.
This integrated approach can signi�cantly improve stormwater management and
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maximize the bene�ts provided by urban forests (Carlyle-Moses et al., 2020; USEPA,
2024).
More recently in Canada, various levels of government have been encouraging urban
tree planting to increase canopy cover and improve urban environmental conditions,
as well as to improve stormwater management (Green Infrastructure Ontario
Coalition, 2016; City of Toronto, 2023a; City of Toronto, 2023b). To that effect, many
Canadian municipalities have set goals or guidelines for stormwater management
that utilize urban forests and increase tree canopy cover. For example, as per
Toronto’s Green Standard Requirements, the City of Toronto aims to minimize runoff
to at least 50 percent of its annual rainfall and, for some sites, retain at least 5 mm of
rainfall (through rainwater reuse, on-site in�ltration, and evapotranspiration) from
each rainfall event (City of Toronto, 2017). Aside from the various ecosystem
services urban forests provide, urban trees also enable the saving of resources for
managing gray infrastructure. The City of Surrey, for example, saved $4.8 million/year
on stormwater infrastructure due to the presence of trees (City of Surrey & Urban
Systems, 2023). Some municipalities, such as the City of Mississauga and the City of
Kitchener, have implemented stormwater fees to encourage private landowners to
reduce the hard surface on their properties. The fees are based on a percentage of
impervious surfaces to encourage property owners to use green infrastructure and
permeable surfaces to reduce localized runoff (Environmental Commissioner of
Ontario, 2016).
Resources
Canadian Standards Association Group. (2022). The Municipal How to Guide for CSA Community Water
Standards. In CSA Community Water Standards.
https://www.csagroup.org/wp-content/uploads/CSAGroup-Municipal-WaterStandards-How-To-
Guide.pdf
Clean Air Partnership (CAP). (2019). Sample Green Development Standards Metrics and Comparison
Tables.
https://council.cleanairpartnership.org/wp-content/uploads/2019/10/CAP-Green-Development-
Metrics-Low-Rise-Residential-and-Comparison-Scan.pdf
Depave Paradise. (2025). Projects – Check the calendar below to �nd Depave Paradise events near you.
Canadian National
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Green Communities Canada. (2017a). Soak It Up! Toolkit: 16 Actions Your Municipality Can Take to Reduce
Runoff and Runoff Pollution (2 ed.). Rain Community Solutions.
https://raincommunitysolutions.ca/wp-content/uploads/2017/07/GCC-SoakItUp-Toolkit-2017.pdf
Green Communities Canada. (2017b). Stormwater Scorecard: What Canadian communities are doing to
reduce stormwater runoff and runoff pollution. Rain Community Solutions.
https://raincommunitysolutions.ca/wp-content/uploads/2017/07/GCC-StormwaterSC-June17.pdf
Green Municipal Fund. (n.d.). Helping municipalities create a sustainable and prosperous future.
https://greenmunicipalfund.ca/
Horizon Advisors, Rous, T., Camacho, L., Batarseh, R., Asadollahi, A., & Preston, S. (2019). Bene�ts of
adopting natural infrastructure: A comparison of natural and grey infrastructure solutions.
https://awc-wpac.ca/wp-content/uploads/2019/08/Adopting-Natural_Infrastructure.pdf
Tree Canada (2024). Canadian Urban Forest Network.
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City of Calgary. (2023). City of Calgary Stormwater Management Strategy. Alberta Low Impact
Development Partnership (ALIDP).
https://alidp.org/initiatives/policy-and-planning/cocswm-strategy
Province of Alberta. (1999). Stormwater Management Guidelines for the Province of Alberta - Open
Government.
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City of Surrey & Urban Systems. (2023). Urban Forest Management Strategy.
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strategy.pdf
City of Vancouver. (n.d.). Citywide Integrated Rainwater Management Plan.
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plan.aspx
City of Victoria. (n.d.). Stormwater Management.
https://www.victoria.ca/home-property/utilities/stormwater-management
nd
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Change.
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https://saintjohn.ca/sites/default/�les/2020-11/
Storm%20Drainage%20Design%20Criteria%20Manual%20March%207-2016%20-%20English.pdf
Government of New Brunswick. (2021). Integrated Watershed Management Plan for the Shediac Bay
Watershed (2021-2031).
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shediacbay_watershed_management_plan.html
OPUS International Consultants (Canada) Limited. (2017). Village of New Maryland Storm Water
Management Master Plan.
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Report-V2-15-02-2017-with-drawings.pdf
The City of Saint John. (n.d.). Stormwater and drainage.
https://saintjohn.ca/en/water-and-sewer/stormwater-and-drainage
Town of Hampton. (2019). Stormwater Management Guidelines.
https://hampton.ca/documents/stormwater-management-guidelines/
Government of Newfoundland and Labrador. (2024). Water Resources Management. Environment and
Climate Change.
https://www.gov.nl.ca/ecc/waterres/
Town of Torbay & Progressive Engineering & Consulting Incorporated (PEC). (2019). Town of Torbay –
Stormwater Management Plan.
https://torbay.ca/site/uploads/2019/09/2018-021-Torbay-Stormwater-Management-Plan-Final-without-
appendices.pdf
Government of Northwest Territories. (n.d.). Water stewardship in the NWT. Environment and Climate
Change.
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New Brunswick
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Government of Nova Scotia. (n.d.). Nova Scotia Surface water. Environment and Climate Change.
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City of Mississauga. (2012). Green Development Standards - Going Green in Mississauga.
https://www.mississauga.ca/wp-content/uploads/2020/07/16135257/Green-Standards-Development-
Standards-2012.pdf
City of Mississauga. (2023). Build Beautiful: Stormwater Master Plan.
https://www.mississauga.ca/publication/build-beautiful-stormwater-master-plan/
City of Toronto. (2017). Toronto Green Streets Technical Guidelines (GSTG).
https://www.toronto.ca/ext/digital_comm/pdfs/transportation-services/green-streets-technical-
guidelines-document-v2-17-11-08.pdf
City of Toronto. (2023a). Stormwater management programs & projects.
https://www.toronto.ca/services-payments/water-environment/managing-rain-melted-snow/what-the-
city-is-doing-stormwater-management-projects/other-stormwater-management-projects/
City of Toronto. (2023b). Toronto Green Standard.
https://www.toronto.ca/city-government/planning-development/o�cial-plan-guidelines/toronto-green-
standard/
Environmental Commissioner of Ontario (ECO). (2016). Urban stormwater fees: How to pay for what we
need.
https://www.auditor.on.ca/en/content/reporttopics/envreports/env16/Urban-Stormwater-Fees.pdf
Government of Ontario. (2003). Stormwater Management Planning and Design Manual.
https://www.ontario.ca/document/stormwater-management-planning-and-design-manual-0
Green Infrastructure Ontario Coalition. (2016). Ontario’s urban forests call to action.
https://greeninfrastructureontario.org/app/uploads/2016/07/
GIO_Urban_Forest_Call_to_Action_Sept15Print.pdf
Lake Simcoe Region Conservation Authority (LSRCA) (2022). Technical guidelines for stormwater
management submissions.
https://www.lsrca.on.ca/wp-content/uploads/2023/06/Technical-Guidelines-for-Stormwater-
Management-Submissions.pdf
Niagara Peninsula Conservation Authority, & AECOM. (2010). Niagara Peninsula Conservation Authority
Stormwater Management Guidelines.
https://npca.ca/images/uploads/common/NPCASWMManual-Guidelines.pdf
The City of Waterloo. (n.d.). Volume 6 - Stormwater management.
https://www.waterloo.ca/en/government/volume-6-stormwater-management.aspx
The Town of Halton Hills. (2019). Green Development Standard.
https://www.haltonhills.ca/en/residents/green-development-standard.aspx
Ontario
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Toronto and Region Conservation Authority (TRCA). (2019). Stormwater Management - Toronto and
Region Conservation Authority (TRCA).
https://trca.ca/conservation/stormwater-management/
Toronto and Region Conservation Authority (TRCA) & Credit Valley Conservation Authority. (2010). Low
Impact Development Stormwater Management Planning and Design Guide.
https://trcaca.s3.ca-central-1.amazonaws.com/app/uploads/2021/10/20091521/LID-SWM-Guide-
v1.0_2010_1_no-appendices.pdf
Town of Caledon & Sustainability Solutions Group (SSG). (2024). Green Development Standard
Guidebook.
https://www.caledon.ca/en/town-services/resources/Energy-Environment/Caledon-GDS-
Guidebook_Final.pdf
Gouvernement du Québec. (n.d.). Rainwater management. Ministère De L’Environnement, De La Lutte
Contre Les Changements Climatiques, De La Faune Et Des Parcs.
https://www.environnement.gouv.qc.ca/eau/pluviales/index-en.htm
Ministry of Municipal Affairs. (2023). Local Government Stormwater Infrastructure - Province of British
Columbia.
https://www2.gov.bc.ca/gov/content/governments/local-governments/infrastructure/water-systems/
stormwater-infrastructure
City of Saskatoon. (n.d.-a). Pathway to a Sustainable Urban Forest: Implementation of the Urban Forest
Management Plan 2022-2031.
https://www.saskatoon.ca/sites/default/�les/
Pathway%20to%20a%20Sustainable%20Urban%20Forest%20-
%20Implementation%20of%20the%20Urban%20Forest%20Management%20Plan%202022-2031_3.pdf
City of Saskatoon. (n.d.-b). Urban Forest Management Plan. In City of Saskatoon – Urban Foresty
Management Plan (pp. 3–45).
https://www.saskatoon.ca/sites/default/�les/urban_forest_management_plan_0.pdf
Government of Saskatchewan. (2015). Stormwater guidelines. Publications Centre.
https://publications.saskatchewan.ca/#/products/113259
Center for Climate and Energy Solutions. (2023). Drought and Climate Change.
https://www.c2es.org/content/drought-and-climate-change/
Quebec
Saskatchewan
Non-Canadian
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Center for Urban Forest Research. (2003). Is all your rain going down the drain? The United States
Department of Agriculture (USDA).
https://www.fs.usda.gov/psw/topics/urban_forestry/products/cufr_392_rain_down_the_drain.pdf
Davey Resource Group & U.S. Environmental Protection Agency. (2013). Stormwater to Street Trees:
Engineering urban forests for stormwater management. U.S. Environmental Protection Agency.
https://www.epa.gov/sites/default/�les/2015-11/documents/stormwater2streettrees.pdf
Global Communications Team. (2019). Biodiversity in cities: How natural asset mapping helps cities
protect livelihoods and address climate change impacts – CityTalk. ICLEI – Local Governments for
Sustainability.
https://talkofthecities.iclei.org/biodiversity-in-cities-how-natural-asset-mapping-helps-cities-protect-
livelihoods-and-address-climate-change-impacts/
The Mersey Forest. (2014). Urban Catchment Forestry: the strategic use of urban trees and woodlands to
reduce �ooding, improve water quality, and bring wider bene�ts.
https://www.merseyforest.org.uk/�les/documents/1310/
Urban%20Catchment%20Forestry%20prospectus%20-%20�nal%20-%20Oct%202014.pdf
United States Environmental Protection Agency (USEPA). (2023a). Using trees and vegetation to reduce
heat islands.
https://www.epa.gov/heatislands/using-trees-and-vegetation-reduce-heat-islands
United States Environmental Protection Agency (USEPA). (2023b). Soak up the rain: Trees help reduce
runoff.
https://www.epa.gov/soakuptherain/soak-rain-trees-help-reduce-runoff
Bartens, J., Day, S. D., Harris, J. R., Dove, J. E., & Wynn, T. M. (2008). Can Urban Tree Roots Improve
In�ltration through Compacted Subsoils for Stormwater Management? Journal of Environmental Quality,
37(6), 2048-2057.
https://doi.org/10.2134/jeq2008.0117
Carlyle-Moses, D. E. (2012). Trees as green infrastructure in our cities.
https://treecanada.ca/wp-content/uploads/2019/12/DCarlyle-Moses-Trees-as-Green-Infrastructure-in-
our-Cities.pdf
Carlyle-Moses, D. E., Livesley, S., Baptista, M. D., Thom, J., & Szota, C. (2020). Urban Trees as Green
Infrastructure for Stormwater Mitigation and Use. In D. F. Levia, D. E. Carlyle-Moses, S. i. Iida, B. Michalzik,
K. Nanko, & A. Tischer (Eds.), Forest-Water Interactions (pp. 397-432). Springer International Publishing.
https://doi.org/10.1007/978-3-030-26086-6_17
Carlyle-Moses, D. E., & Schooling, J. T. (2015). Tree traits and meteorological factors in�uencing the
initiation and rate of stem�ow from isolated deciduous trees. Hydrological Processes, 29(18), 4083-4099.
https://doi.org/10.1002/hyp.10519
Dowtin, A. L., Cregg, B. C., Nowak, D. J., and Levia, D. F. (2023). Towards optimized runoff reduction by
Further Reading
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urban tree cover: A review of key physical tree traits, site conditions, and management strategies.
Landscape and Urban Planning, 239, 104849.
https://doi.org/10.1016/j.landurbplan.2023.104849
Frosi, M. H., Kargar, M., Jutras, P ., Prasher, S. O., & Clark, O. G. (2019). Street Tree Pits as Bioretention
Units: Effects of Soil Organic Matter and Area Permeability on the Volume and Quality of Urban Runoff.
Water, Air, & Soil Pollution, 230(7), 152.
https://doi.org/10.1007/s11270-019-4197-7
Garg, M., CaterinaValeo, Gupta, R., Prasher, S., Sharma, N. R., & Constabel, P . (2018). Integrating natural
and engineered remediation strategies for water quality management within a low-impact development
(LID) approach. Environmental Science and Pollution Research, 25(29), 29304-29313.
https://doi.org/10.1007/s11356-018-2963-5
Green Communities Canada. (2017c). Urban Flooding in Ontario: Towards Collective Impact Solutions.
Rain Community Solutions.
https://raincommunitysolutions.ca/wp-content/uploads/2017/04/GCC-UrbanFloodingMar17.pdf
Green Communities Canada, Living Cities Canada Fund. (2023). Living Cities Canada Fund 2023 Impact
Report.
https://greencommunitiescanada.org/wp-content/uploads/2024/03/LivingCitiesFundImpact2023-
Final.pdf
Kaykhosravi, S., Khan, U. T., & Jadidi, M. A. (2020). The effect of climate change and urbanization on the
demand for low impact development for three Canadian cities. Water, 12(5), 1280.
https://doi.org/10.3390/w12051280
Kirnbauer, M. C., Baetz, B. W., & Kenney, W. A. (2013). Estimating the stormwater attenuation bene�ts
derived from planting four monoculture species of deciduous trees on vacant and underutilized urban
land parcels. Urban Forestry & Urban Greening, 12(3), 401-407.
https://doi.org/10.1016/j.ufug.2013.03.003
Kuehler, E., Hathaway, J., & Tirpak, A. (2017). Quantifying the bene�ts of urban forest systems as a
component of the green infrastructure stormwater treatment network. Ecohydrology, 10(3), e1813.
https://doi.org/10.1002/eco.1813
Nesbitt, L., Hotte, N., Barron, S., Cowan, J., & Sheppard, S. R. J. (2017). The social and economic value of
cultural ecosystem services provided by urban forests in North America: A review and suggestions for
future research. Urban Forestry & Urban Greening, 25, 103-111.
https://doi.org/10.1016/j.ufug.2017.05.005
O'Neill, S. (2018). Measuring Urban Forest Canopy Effects on Stormwater Runoff in Guelph, Ontario.
University of Guelph.
http://hdl.handle.net/10214/12958
Orta-Ortiz, M.S. and Geneletti, D. (2022). What variables matter when designing nature-based solutions
for stormwater management? A review of impacts on ecosystem services. Environmental Impact
Assessment Review, 95, 106802.
https://doi.org/10.1016/j.eiar.2022.106802.
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R. Bean, R. E. P ., J. Voorhees and M. Elliott. (2021). Urban Tree Rainfall Interception Measurement and
Modeling in WinSLAMM, the Source Loading and Management Model. Journal of Water Management
Modeling, 29.
https://doi.org/10.14796/JWMM.C475
Schooling, J. T., & Carlyle-Moses, D. E. (2015). The in�uence of rainfall depth class and deciduous tree
traits on stem�ow production in an urban park. Urban Ecosystems, 18(4), 1261-1284.
https://doi.org/10.1007/s11252-015-0441-0
Van Stan, J. T., Norman, Z., Meghoo, A., Friesen, J., Hildebrandt, A., Côté, J.-F., Underwood, S. J.,
Maldonado, G. (2017). Edge-to-Stem Variability in Wet-Canopy Evaporation from an Urban Tree Row.
Boundary-Layer Meteorology, 165(2), 295-310.
https://doi.org/10.1007/s10546-017-0277-7
Xiao, Q., McPherson, E. G., Simpson J, R. and Ustin, S. L. (1998). Rainfall Interception by Sacramento’s
Urban Forest. Arboriculture & Urban Forestry, 24(4) 235-244.
https://doi.org/10.48044/jauf.1998.028
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Economic Value and Appraisal of Trees
Urban forests provide numerous ecological and social functions that can be
translated into economic value, �nancial bene�ts, and dollar value. Urban trees
increase property values and reduce energy costs through natural cooling; also, treed
and forested urban areas promote tourism and recreation, which can all be
transformed into monetary value (Ewane et al., 2023; Nowak et al., 2017; Wolf et al.,
2020). The economic value of trees can be assessed in several ways depending on
the geography, purpose of the evaluation, and who is performing the evaluation. For
example, trees can be valued for their intrinsic value (e.g., diversity, complexity,
beauty, spiritual signi�cance) or the objective value of the tree in and of itself (AWES,
2021). Alternatively, urban trees can be evaluated in situ, built on the monetary value
they provide based on their ecological services (e.g., stormwater management,
carbon sequestration), or appraised for the cost of replacing them based on their
size, health, and species.
Highlights
Measuring economic value
The bene�ts and ecological services of urban forests can be assessed and
quanti�ed.
Tree appraisal methods
The value of individual urban trees can be determined using specialized
assessment techniques.
Legal and practical significance
Understanding tree value is crucial for tree replacement, legal disputes, urban
planning, infrastructure development, and insurance claims.
Beyond monetary value
Urban trees provide additional bene�ts, such as carbon storage, air quality
improvement, and urban heat reduction.
Tools
Available tools for economic evaluation and appraisal of urban trees.
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Tree Appraisal
In addition to measuring, assessing, and quantifying urban forest bene�ts and
ecological services, tree appraisal is conducted for numerous compelling reasons,
including o�cial and legal valuations of urban trees. Several appraisal methods have
been developed and implemented to estimate the monetary value of trees (Watson,
2002). While tree appraisal results can vary between appraisal methods and
appraisers (Watson, 2002), conducting tree appraisals remains an important way to
convey the signi�cance and value of urban trees (Komen & Hodel, 2015; Purcell, n.d.).
Several methods can be used for estimating tree replacement values, particularly
when estimating the value of a tree for legal disputes, sales, urban planning, and
infrastructure development needs, or insurance claims. Several tree appraisal
methods are used across urban areas, and all of them assess the monetary value of
trees based on several common variables: species characteristics, tree size, health
condition, location, and contribution to the surrounding environment (Doick et al.,
2018). For example, these methods are: the Trunk Formula Method (TFM), often used
for large and irreplaceable trees; the replacement cost method, used for smaller and
replaceable trees; the cost approach, used to evaluate lifetime maintenance and
planting costs for trees; the market approach (comparable sales), to assess the value
of a tree based on market prices of similar trees; the income approach, which
focuses on economic bene�ts of trees such for example energy savings; the capital
asset valuation which estimates a value that a tree contributes to property value;
ecosystem service valuation which assigns tree value based on the environmental
bene�ts it provides such example carbon sequestration and air quality improvement;
and the CTLA Guide for Plant Appraisal, an ISA approach that combines multiple tree
variables such as size, species, and condition into the valuation (Watson, 2002;
Szaller et al., 2019; Doick et al., 2018).
A tree appraisal's purpose is usually guided by speci�c clients' needs and often
considers handling unexpected losses, tort claims (civil claims for compensation for
wrongful acts or injury), insurance claims, tax deductions, real estate assessments,
or proactive planning. Once all relevant tree information is collected, the appraiser
selects an appropriate appraisal method and delivers an objective valuation as a
dollar �gure (Purcell, n.d.; Ponce-Donoso, Vallejos-Barra & Escobedo, 2017; CTLA,
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2020; Grande-Ortiz, Ayuga-Téllez & Contato-Carol, 2012).
The Council of Tree and Landscape Appraisers (CTLA) Guide for Plant Appraisal is
one of the most commonly used tree valuation methods in Canada and the United
States, and is considered an industry standard (Cullen, 2007; Komen and Hodel,
2015). The appraisal process requires collecting site-level information, including tree
measurements and assessment, to obtain all measurable variables effectively. Tree
species characteristics and size, tree condition, damage, scarring, location factors,
and many more criteria determine the value of a tree. Valuing trees and landscape
elements requires specialized training, expertise, and experience. Tree appraisal
material and courses are available through organizations such as the International
Society of Arboriculture (ISA) and ISA Ontario. CTLA methods, endorsed by the ISA
and local arborist organizations, are applicable for tree valuation in legal disputes,
urban planning, environmental impact studies, and insurance claims. For example,
the City of Ottawa, Edmonton, Guelph, and Mississauga use the CTLA approach to
assess and evaluate the value of trees affected by construction and development
projects (City of Guelph, 2019; City of Edmonton, 2024; AECOM, 2022). Smaller
municipalities may lack the resources needed for complete tree inventories;
collaborating with consultants or universities can provide valuable support at the city
level.
Economic Value of Urban Forests – Benefits Provided
Urban trees provide a myriad of ecological services that can be translated into
economic value. For example, tree bene�ts include increased property values (Han et
al., 2024), positive impacts on real estate consumer preference (Farr, 2017),
reduction in energy costs by shading buildings and pavement, and lower ambient
temperatures (McDonald et al., 2024). In 2014, a TD Economics Report found that
urban forests in Halifax, Montreal, Vancouver, and Toronto had a combined value of
$42 billion and provided $330 million per year in environmental bene�ts. Depending
on the city, for each dollar spent on tree maintenance, about $1.88 to $12.70 was
returned in various bene�ts (Alexander & DePratto, 2014). These values are likely to
be lower estimates, as they do not include the value of tourism, recreation, or impact
on property values, human health, and social wellbeing (Farr, 2017). Urban trees
provide services akin to other urban infrastructure by reducing runoff and erosion,
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improving air quality, saving energy, and sequestering carbon, which increases over
time as trees grow (Hotte et al., 2015; Farr, 2017).
Technology such as remote sensing (e.g., multispectral images and LIDAR) and
geographic information systems (e.g., GIS and Google Maps), combined with ground-
based sampling methods (e.g., plot and tree sampling, as well as data collected
through citizen science), play a vital role in estimating the extent, structure, and
composition of urban forests and their bene�ts (Hotte et al., 2015). These
technologies facilitate the mapping of urban canopy extent and the collection of
measurements of urban forests and woodlots in both large and small municipalities.
This spatial and �eld information is then further used to support the ecological and
economic values of trees and the services they provide.
For instance, �eld measurements, along with tools like i-Tree or other tree-relevant
allometric formulas, can be employed to determine the carbon sequestration rates of
urban forests. By utilizing �eld data alongside mapped tree canopy coverage, it
becomes possible to estimate the amount of carbon dioxide sequestered from the
atmosphere by the entire urban tree canopy, by individual trees, and by a unit (e.g., 1
ha) of the urban tree canopy. For example, a study conducted in Canada by Pasher et
al. (2014) estimated that the average carbon sequestration capacity of urban tree
canopies is 2.9 tonnes of CO per hectare per year.
Benefits and Value of Urban Forests – Beyond Money
Estimating the value of an urban forest can be done by appraising forest structural
components such as canopy cover, species composition, and age. The many bene�ts
of urban forests, such as carbon storage, carbon sequestration, air quality
improvement, and the moderation of urban heat island effects (Han et al., 2024), also
create value via co-bene�ts. It has been shown that some of these bene�ts result in
co-bene�ts, such as decreased power usage during a heatwave (McDonald et al.,
2024), and a negative correlation between urban tree canopy cover and mortality and
morbidity rates during heat waves (McDonald et al., 2020). Aside from providing
refuge during summer, proximity to urban forests is positively correlated with shorter
hospital stays for patients recovering from surgeries and better health outcomes for
pregnancies (Ulrich, 1984; Hotte et al., 2015). While more challenging to quantify, the
2
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cultural, spiritual, visual, and sensory values of urban trees are often the aspects
most highly valued by the general public.
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Individual Tree and Woodlot Inventory, and
the Tree Inspection Cycle
The structure, distribution, and composition of an urban tree canopy greatly impact
the bene�ts and services provided by urban green spaces in Canadian cities
(Przewoźna et al., 2022). The foundation of an effective urban forest management
program and the base information supporting ecological service estimates comes
from a detailed tree inventory. A tree inventory is a necessary urban forest
management tool that provides information about trees, such as tree species, health,
size, and location. There are diverse ways in which city authorities, professionals, and
researchers can use tree inventory data. Inventory data can be used to identify and
analyze tree species diversity and distribution, percentage of canopy cover, tree size/
class distribution, functional group distribution, tree health and growth trends, and
more (Nielsen, Delshammer & Ostberg, 2014). Tree inventory data can also be used
to support various efforts such as strategic forest management plans, cost-bene�t
assessments of urban climate/pollution mitigation, creation of invasive species
management plans, risk assessment, examination of social dimensions of urban
forests, and much more (City of Toronto, 2013). Forest managers can also prioritize
Highlights
Importance of tree inventories
Tree inventories are essential for urban forestry and provide valuable data for
foresters, planners, policymakers, and homeowners.
Inventory details
Tree species, health, size, and location.
Data collection methods
Inventories and inspections can be done at various spatial scales, either manually
or remotely.
Citizen science and community involvement
Volunteer-based inventories can be a cost-effective and socially bene�cial way to
start or update a city's tree inventory.
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maintenance efforts and resources by knowing urban forest resources. As such,
keeping an up-to-date inventory of urban trees, supplemented by routine tree
inspection, is fundamental for effective urban forest management.
Sample-Based Inventory
There are several different methods and scopes of tree inventory that a city can
employ. The quickest and most minimal scope of inventory is a sample-based
inventory, which contains information on a small subset of trees from a larger
population. A sample with su�cient data enables urban foresters to extrapolate tree
data across the city to represent an entire urban forest. This type of inventory is
considered a cost-effective way to achieve a statistically valid representation of an
urban forest when the scope of inventory and analysis does not require data on each
tree for speci�c management applications (Sabatini, 2021). Similarly, partial tree
inventories focus on certain areas of concern, such as speci�c tree species, land use
categories, or geographic areas. This type of inventory is taken when dealing with a
pest outbreak and species-speci�c pests and diseases, as with the Emerald Ash
Borer. A partial inventory is also useful when assessing storm damage and when
performing risk assessments (EFUF, 2018).
Individual Tree Inventory
When a more comprehensive analysis of urban trees is required to support tree
management and daily maintenance, tree surveys/inventories at the level of
individual trees may be conducted. Survey methods include direct inspection and
measurement of individual trees to gather a complete record of species, age, size,
health, location, and other qualities (Nielsen, Delshammer & Ostber, 2014; Morales-
Gallegos et al., 2023). While this approach can be labour-intensive and time-
consuming, it supports urban forest management and operations with the most
thorough and accurate tree data. Individual tree inventories may be considered the
most bene�cial inventory method in situations when analyzing tree species diversity
and distribution, tree size/class distribution, and monetary evaluation of individual
trees/species are required, such as for preparing tree planting prescriptions or
creating a baseline inventory for further assessment (Urban Forest Analytics, 2024).
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Tree Inspection
A tree inspection cycle, coupled with an updated tree inventory, is integral for proper
tree maintenance and hazard management. Effective tree monitoring enables the
evaluation of urban forest resources and the development of short and long-term
plans and maintenance, which can provide substantial cost savings while also
mitigating safety and tree hazard issues.
Urban tree inspection, pruning, and removal are necessary components of urban
forestry in Canada [see chapter: Tree Maintenance]. Up-to-date inspection of urban
street tree condition and health, as well as recording previous and scheduled work,
are the basis of effective street tree maintenance and management (City of Toronto,
2013). Regular inspection cycles are also important health and safety tools, where
storm or construction tree damage, canopy dieback, limb damage, pest and disease
presence, routine tree care and tree health decline can be assessed and managed in
a timely manner to prevent hazards and risks to citizens (International Society of
Arboriculture, n.d.).
Tree health indicators at the individual tree level such as trunk damage, crown
dieback, vandalism, pest/disease presence and root damage require on-the-ground
inspection (Morales-Gallegos et al., 2023), while street- or stand-level health
indicators such as crown density, stand age/size, vegetation indices, edaphic (soil-
related) factors and climatic/environmental stressors can be inspected and observed
using satellite imagery, sample inventories, proxy indicators and models (Haq et al.,
2023).
Aerial Urban Forest Inventory
Conversely, when general tree data is required for large areas, many Canadian cities
create tree inventories using aerial photography and GIS (Esri Canada & City of
Guelph, n.d.). By employing satellite imagery and scanning tools, cities can conduct
an inventory of tree cover types and general stand qualities without inspecting each
individual tree [see chapter: GIS, Remote Sensing and Other Spatial Technologies].
This type of inventory can be bene�cial when considering the health and bene�ts of
urban canopy cover, when assessing large areas where �eld surveys may be too
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costly/time-intensive, and when information about individual trees is not necessary
based on the scope of data application (Wood, Norton & Rowland, n.d.; Nielsen,
Delshammer & Ostber, 2014).
Community Science and Participation
When conducting tree inventories, Canadian cities may employ citizens and non-
pro�t organizations to participate in data collection. Recruiting volunteers to record
general observations about tree health in their neighbourhoods, such as cavity decay,
crown dieback, and trunk damage, is a valuable and cost-effective way to build and
maintain tree health inventories without performing constant �eld surveys (Sabatini,
2021). In Canada, community-based stewardship programs such as
Neighbourwoods™ (Kenney & Puric-Mladenovic, 1995) can help community groups
and volunteers contribute to tree inventories, which help inform foresters and
planners about the state of urban forests while also encouraging community
involvement in urban forest stewardship. This program has explicitly been employed
in several municipalities across Ontario and has potential for application across
Canada and beyond. Additionally, Canadian urban tree inventory data can be added to
national and international databases (e.g., CIF Open Urban Forests (2024), i-Tree
(n.d.), Making Nature's City ToolKit (n.d.), etc.), which support concerted
management and planning efforts.
It is important to recognize that many community involvement and volunteer-based
outreach programs only reach a very targeted audience. There is often a lack of
emphasis on place-based landscape design and engagement, which should vary
based on the needs of individual neighbourhoods, communities, and municipalities
(Eisenman et al., 2024). A place-based approach to community engagement in urban
forestry requires understanding the issues, relationships, and needs of community
members in any given place and speci�cally coordinating planning and resources to
improve the quality of life for that community (Improvement Service UK, 2016). When
place-based needs and goals are not well understood, the bene�ts of community
involvement in urban forestry can be inequitably distributed (Kudryavtsev, Stedman &
Krasny, 2012).
For a successful and equitable place-based outreach program, it is necessary to
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allocate funds properly, meaningfully consult with target volunteers, co-develop
participation opportunities with community members, and select performance
outcomes based on place-based needs and goals (Eisenman et al., 2024). People
from all communities should be equally able to engage in urban forestry, so public
participation programs should re�ect their speci�c needs and goals [see chapter:
Equity Considerations in Urban Forestry].
Natural Area/Woodlot Inventory
Contents
•
• Determine the type of inventory that should be used.
• Selecting inventory methods, scale, and sampling plan.
• Ongoing process of tracking changes in
forest communities over time and space.
Effective woodlot, natural parks, and area management rely on accurate knowledge
of plant species composition, community structure, and how healthy its components
are. Woodlot inventories differ from street tree inventories both in their spatial extent
and in that a woodlot will have trees grown from naturally occurring seed, understory
plants, wildlife, and other components not controlled by humans. Woodlot inventories
can range from a basic timber cruise to a detailed inventory including soil, vegetation
community, and wildlife inventory. The management goals for the woodlot generally
determine the type of inventory chosen for a project. However, it is important to keep
in mind that an inventory may bring to light new information (such as the presence of
a species at risk or invasive plants) that might change management goals (Ma et al.,
2021).
The �rst step in understanding what is in a woodlot is a survey of available aerial
images and maps. Depending on when and why they were developed, existing maps
may already delineate the different stand types, roads, and water bodies in a woodlot.
Aerial imagery can be used to create these maps and to judge the accuracy of
outdated or broad-scale maps when newer information is not available (Gougeon,
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2014). Forest resource inventory maps are variably available across Canada and may
be found through provincial open spatial data hubs [see chapter: National and
Provincial Datasets]. LiDAR mapping may also be an option for stand delineation
(Wang et al., 2004).
After getting a basic idea of what stands and other features are present in a woodlot,
a sampling plan can be developed to build a basic inventory. The simplest form of
woodlot inventory sampling is a timber cruise. In this form of inventory, sample
locations (plots of variable size) are selected where surveyors record tree species,
diameter, and growth form, which are then used to estimate the number of each tree
species and the amount of basal area and merchantable timber per hectare. There
are many guides to timber cruising provided by provincial governments and woodlot
associations. However, this kind of inventory does not provide su�cient information
on forest structure, composition, plant diversity, non-tree plant species, soil condition,
forest community, and other aspects of woodlots, which determine their ecological
integrity, combined health, and classi�cation. A more detailed inventory, often based
on �xed area plots and which collects data on species besides trees as well as site
characteristics, can better support tailored management for multiple purposes such
as monitoring, habitat and species-at-risk protection, regeneration success,
recreation, or carbon stock (Day and Puric-Mladenovic, 2012). One such inventory
and monitoring program is the Vegetation Sampling Protocol (VSP) (Puric-
Mladenovic, 2016), which can be adjusted to different spatial scales depending on
landscape and management needs (Puric-Mladenovic & Baird, 2017). VSP is a
sampling protocol that collects multipurpose, detailed information on trees and their
size, but also a full species list, dead wood, and invasive species abundance
(Sherman, 2015). VSP , as a strategic inventory, gathers information that is multi-
functional and standardized (data collection and web-based portal for data entry),
and gives a precise record of spatial extent and location, enabling �eld data to be
transferred into diverse spatial formats and vegetation mapping products. It is also
used for monitoring as it enables resampling and tracking changes in forest
ecosystems over time and space. Detailed protocols such as this can be great
resources when creating detailed inventories and �exible woodlot management
plans.
Resources
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Improvement Service UK. (2016). Place-based Approaches to Joint Planning, Resourcing and Delivery: An
overview of current practice in Scotland.
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report.pdf
Kudryavtsev, A., Stedman, R. C., & Krasny, M. E. (2012). Sense of place in environmental education.
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Ma, B., Hauer, R. J., Östberg, J., Koeser, A. K., Wei, H. and Xu, C. (2021). A global basis of urban tree
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Rosales, D., Saavedra-Romero, L.d.L. (2023). Tree Health Condition in Urban Green Areas Assessed
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Nielsen, A., Ostberg, J., & Delshammar, T. (2014). Review of Urban Tree Inventory Methods Used to
Collect Data at Single-Tree Level. Arboriculture and Urban Forestry 40, 96-111.
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urban and rural areas. Ambio51, 2043–2057.
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GIS, Remote Sensing and Other Technologies
Technologies like Geographic Information Systems (GIS), remote sensing, other web-
based spatial technologies, and relevant software are widely used to support urban
forest management, conservation, and planning. They allow the mapping,
cataloguing, inventory, and monitoring of urban forest characteristics from the scale
of individual trees, woodlots, and urban green spaces to an entire urban tree canopy
(Ward & Johnson, 2007). Besides mapping trees, they also allow mapping of the
urban environment and environmental conditions where urban trees grow. There is a
diversity of GIS and remote sensing technologies in use and development, and a
diversity of spatial and remotely sensed urban forest-related data. Some of the
technologies have been designed for use in urban forestry, and some have been
developed in other professions and adopted by the urban forestry sector (Green
Municipal Fund, n.d.). This chapter brie�y summarizes technologies used in urban
forestry and provides a list of Canada's relevant examples.
Geographic Information Systems (GIS)
Geographic Information Systems (GIS) have played a pivotal role in natural resources
management, and thus urban forestry, for decades. Since the 1980s, particularly in
1990, with spatial technology and software development and growth, GIS has
become a critical tool for urban forest management and decision-making. For
example, GIS enables detailed tree and canopy mapping, analysis, and management
of tree population data. GIS creates spatial tree inventories containing species,
health, size, and more information. Such spatial tree data facilitates more effective
Highlights
Technologies
GIS, remote sensing, LiDAR, and orthoimagery, and how they are used in urban
forestry.
Overview
GIS and remote sensing in urban forestry.
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and adaptive urban forest management and monitoring, critical for informing tree
planting strategies and sustainable and evidence-based urban development.
Additionally, GIS, combined with remote sensing, enables sampling of the entire
urban area, supports timely urban forest monitoring, and detects urban forest decline
and pest infestations, to name a few applications. Furthermore, by integrating urban
forest spatial data with urban planning, GIS supports future urban forest planning
and enhances urban forest conservation in the face of increased urban
intensi�cation and development. Moreover, GIS facilitates using other spatial data
(e.g. Digital Elevation Models, infrastructure mapping, and soil zones) to provide
context about a proposed planting site, potentially protect trees and green areas, and
other urban forestry projects (Kip, 2022).
Numerous commercial and open-source GIS software exist and are utilized in urban
forestry. Commercial GIS programs like ESRI ArcGIS Pro are widely used across
municipalities, governments, and larger NGOs. MapInfo Professional is another
commercial software that has mapping and spatial analysis tools suitable for urban
forest management and land use planning. In the open-source category, QGIS is
certainly one of the most popular GIS platforms. It has a wide range of tools for
mapping, geospatial analysis, and data visualization. GRASS GIS is an advanced
open-source GIS, particularly for use with remotely sensed images. It has powerful
analytical capabilities. Each of these tools enables spatial database creation, data
maintenance, mapmaking, analysis, and reporting. For example, they can be used to
create and maintain databases of individual street trees, facilitate tree health risk and
assessment, track tree removal and work planning, analyze and map woodland and
urban forest characteristics, and more.
Municipalities, provincial governments, and some larger NGOs typically use Esri
software to manage their data, conduct analyses, and share the information with the
public. By taking advantage of web mapping, Canadian municipalities share street
tree inventories with the public. For example, Vancouver, Ottawa, Charlottetown,
Oakville, Winnipeg, and Montreal have their tree inventory data online. GIS in
combination with web mapping also supports speci�c interactive web applications
and other forms of knowledge sharing, reporting, and science communication that
allow the public and other interest groups to view and understand forestry data
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easily. Examples of interactive web applications include Nature Canada's 2022 report
on tree equity and the associated Canadian Map of Adaptation Actions, the City of
Toronto’s Tree Equity Map, and Calgary's urban forest management map.
Mobile and web-based GIS tools and applications are also used to collect urban
forest information and engage the public in data gathering and urban forest
monitoring. These platforms enable citizens, researchers, and the broader public to
contribute to the inventory, monitoring, and management of urban forests and their
biodiversity. For example, iNaturalist has been used to track urban biodiversity and
upload photos and locations of observed plants, wildlife, and insects. The
Neighbourwoods© program has been using mobile GIS applications to support
inventory and monitoring trees on private urban lands by engaging community
groups and graduate students in data collection.
Remote Sensing
Collecting data and sampling the entire urban forest through �eld surveys alone
would be challenging and not economically feasible. Remote sensing is a method of
collecting spatial data across entire study areas without direct contact with the
observed objects, and it plays a crucial role in urban mapping, management,
conservation, and planning. Remote sensing provides critical insight into urban forest
extent, structure, composition, and dynamics by capturing broad-scale, consistent,
and repeatable data. Remote sensing products include multiple spectral imagery of
forestry, such as remote sensing, airborne sensing, drone imagery and LiDAR (Staley,
2022). The advantage of remote sensing is that it frequently enables sampling of the
entire urban forest and provides high-resolution data with diverse derivatives and
multiple applications. For example, high-resolution satellite imagery and LiDAR allow
for precise urban tree canopy cover mapping across entire cities.
Remote sensing technologies with hyperspectral and multispectral sensors help
identify vegetation stress and even speci�c tree species. Remotely sensed images
and their derivative tools also enable consistent monitoring that can help to detect
the effects of environmental and climate changes, phenology change, and green
space loss, and can even be used to evaluate the effectiveness of urban forestry
programs (e.g., tree planting efforts). Through remote sensing technologies, urban
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foresters can evaluate health, distribution, and changes in vegetation, as well as the
impacts of urbanization. Besides providing information about urban forests and
trees, satellite and airborne remote sensing platforms also enable monitoring of
environmental factors such as temperature, urban heat island effects, pollution, and
soil moisture.
Remotely Sensed Images Used in Urban Forestry
Satellite-based remote sensing collects and analyzes data about Earth's surface and
atmosphere using satellite sensors. It enables large-scale, consistent, and repeatable
monitoring of various environmental and urban features (Wulder et al., 2024; Latifovic
et al., 2015).Images from satellite-based remote sensing are free or commercial.
Both free and commercial imagery play complementary roles, with free data offering
broader accessibility and commercial data providing greater detail and precision for
specialized applications.
Free satellite imageries are openly accessible for public use and are widely used for
research, education, and non-commercial purposes. While these datasets are free,
they may have limitations in terms of spatial resolution. For example, Landsat Data
has multispectral imagery with 30m resolution (15m panchromatic) and a temporal
resolution of 16 days. Sentinel-2 (ESA) imagery is high-resolution imagery (10-60m
resolution) with multispectral bands. Like Landsat, it is suitable for urban forestry
and land cover classi�cation, and tree canopy analysis.MODIS (NASA) is imagery
takendaily and has moderate-resolution imagery (250m-1km) applicable for broad-
scale monitoring of vegetation, land cover, and global change, with limited
application to urban forests.
Commercial imagery provides �ner spatial, temporal, and spectral resolution
specialized data products, but they can be cost-prohibitive, especially for large-scale
or long-term projects. Thereare many commercial satellite imageries based on
purchase or subscription, like PlanetScope (Planet) high-resolution imagery, which is
taken daily. Older imagery has a resolution of 5m, while images taken by newer
satellites have a resolution of around 3m. These images do not have a panchromatic
band. They have 4 multispectral bands (Blue, Green, Red, and Near-Infrared).
GeoEye-1 has one panchromatic band with a resolution of 41cm and four
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multispectral bands (Blue, Green, Red, and Near-Infrared) at a resolution of 1.65m.
WorldView Series (Maxar) is high-resolution imagery up to 30cm and provides
multispectral and high-resolution panchromatic images. The multispectral WorldView
satellite images provide data in multiple spectral bands, which are useful for urban
forestry. WorldView-2 imagery has 8 multispectral bands (coastal, blue, green, yellow,
red, red edge, NIR1, NIR2) with a spatial resolution of 1.84m. Its panchromatic band
has a resolution of 0.46m. WorldView-3 images (and WorldView-4 decommissioned
in 2019) have 1.24m resolution for 8 standard multispectral bands, 8 shortwave
infrared (SWIR) bands, and 0.31m resolution for a panchromatic band.
Airborne remote sensing is used to capture high-resolution data about urban
forests. Airborne remote sensing requires aircraft or drones equipped with
multispectral, hyperspectral, or LiDAR sensors. Similar to airborne remote sensing,
UAVs (Unmanned Aerial Vehicles or Drones) are equipped with multispectral
cameras and LiDAR or sensors. This makes airborne and UAV remote sensing
especially valuable for monitoring and mapping urban forests and green spaces,
detecting changes in forest cover, and using their outputs to support urban forest
management and plan for sustainable urban development.
LiDAR (Light Detection and Ranging) uses lasers to generate point clouds
representing the real world as the lasers encounter obstacles such as buildings, tree
branches, and vegetation cover. These point clouds can then be classi�ed by what
they represent in order to generate models of the real world used in these analyses.
These datasets are becoming more available to the general public as their use
increases (Natural Resources Canada, 2023). LiDAR provides detailed 3D topography
and 3D models of tree heights and canopy density. Once processed for practical
uses, this data offers detailed spatial information for speci�c uses, such as canopy
height models to support tree inventory risk assessment and forest structure
assessment. LiDAR analysis of an area can be used to estimate the leaf area and
crown density of individual trees or entire regions, creating more accurate canopy
cover estimates as technology evolves (LidarBC, n.d.). LiDAR is also commonly used
as a tool for forest inventory (Natural Resources Canada, 2024; Ontario Woodlot
Association, n.d.), and there has been an exploration of LIDAR as a tool for �re risk
classi�cation (Burns, 2012) and natural disaster impact assessment (Blackman &
Yuan, 2020).
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Red, Green, and Blue (RGB) are basic spectral bands used to visually view, assess,
and map vegetation in urban areas. Near-infrared (NIR) bands are sensitive to
vegetation health and can be used to distinguish tree canopy from other land uses.
For example, shortwave infrared (SWIR) is useful in detecting moisture content in
vegetation and providing insights into tree health and stress. Depending on the
available spectral bands and imagery used, a combination of spectral bands is
possible to derive various vegetation indices that provide information about the
urban canopy. For example, the Normalized Difference Vegetation Index (NDVI),
widely used to assess vegetation density and health, is derived from NIR and red
bands. Enhanced Vegetation Index (EVI, as a variation of NDVI) might be more
sensitive to mapping dense vegetation. The availability of near-infrared (NIR) and red-
edge bands is particularly valuable for vegetation analysis, canopy mapping, and
detecting tree health in urban forestry applications. For example, Leaf Area Index
(LAI) can be estimated from NIR and �eld survey LAI to create urban forest LAI
across a wider area (Ren et al., 2018; Le Saint et al., 2024) using Lidar data (Alonzo et
al., 2015).
In addition, various airborne or satellite hyperspectral images can be used to map
tree canopy health, detect vegetation stress, or classify vegetation. They can even
identify species and leaf biochemical properties such as chlorophyll content, leaf
area index (LAI), or water content. For example, AVIRIS is an airborne sensor with 224
spectral bands. HyMap has 126 spectral bands, and SpecTIR offers hyperspectral
data across hundreds of bands. The EO-1 satellite, Hyperion, has 220 spectral bands,
while PRISMA, from the Italian Space Agency, delivers 239 bands that can be used to
support and inform environmental monitoring and urban forestry management. While
hyperspectral imagery has high spectral resolution and is complex, it creates a large
volume of data, requiring specialized remote sensing software to manage data and
extract meaningful urban forest information.
Aerial Orthoimagery
Digital Orthophotography (Orthoimagery) is aerial or satellite imagery, typically RGB
and geometrically corrected (orthorecti�ed) to remove distortions caused by terrain,
camera angles, and lens distortion. It is commonly used to visually represent
landscapes and as a base map in GIS. The advantage of orthoimages is that they are
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publicly available and shared by provinces or municipalities, and they can have a pixel
resolution of 16cm and an accuracy of 45cm, which allows for precise identi�cation
of tree locations within urban environments and makes them suitable for mapping
tree locations.
These imagery-based maps are widely used in GIS applications. As high-resolution
imagery, they are overlaid with vector or raster data to provide quick spatial context
and verify spatial data accuracy. Imagery-based maps are image layers that display
satellite or aerial photographs of the Earth's surface. For example, Esri has included a
high-quality aerial imagery-based map that is part of Esri's Living Atlas of the World.
Unlike Esri products, QGIS does not have a native-based map, but with adequate
plugins, it can use Google Maps, Bing Maps, and other services as base maps. For
example, though time-consuming for larger areas, digital orthophotography and base
maps can be used to digitize tree canopy outlines for smaller areas (e.g. parcel).
Tools and Technologies
City of Calgary, Esri. (n.d.). Urban Forest Management – Interactive Map.
https://maps.calgary.ca/TreeSchedule/
Evergreen. (n.d.). AI for the Resilient City – About the Project.
https://www.evergreen.ca/impacts/ai-for-the-resilient-city/
Google Earth. (n.d.). Overview – The World's Most Detailed Globe.
https://www.google.ca/earth/
HealthyPlan. (n.d.). HealthyPlan City – Explore Equity in Your City.
https://healthyplan.city/en
Natural Resources Canada, (n.d.). Registry of Open Data on AWS.
https://registry.opendata.aws/
QGIS Association. (n.d.). QGIS Geographic Information System – Open Access.
http://www.qgis.org
Spatial Data Tools/GIS
Free/public domain technologies and GIS
Paid/membership model technologies and GIS
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ESRI. (2011). ArcGIS Desktop: Release 10.8 - Overview. Redlands, CA: Environmental Systems Research
Institute.
https://www.esri.com/en-us/arcgis/products/arcgis-pro/overview
ESRI. (2023). ArcGIS Solutions – Introduction to Tree Management.
https://doc.arcgis.com/en/arcgis-solutions/latest/reference/introduction-to-tree-management.htm
Note: Valid license for Esri ArcGIS required.
American Forests. (2024). Discover Tree Equity Score.
https://www.treeequityscore.org/
iNaturalist. (2024). A Community for Naturalists – How it Works.
https://www.inaturalist.org/
i-Tree International Database. (n.d.). i-Tree International Database – About.
https://database.itreetools.org/
Open Ottawa. (2024). Tree Inventory.
https://open.ottawa.ca/datasets/tree-inventory/explore
Open Tree Map. (2024). Flexible all-in-one urban tree inventory and ecosystem services calculations tool.
https://opentreemap.github.io/
Texas A&M Forest Service. (2024). Trees Count Mobile App – Download.
https://texasforestinfo.tamu.edu/MobileApps/TreesCount/
Quebio. (n.d.). Arbres publics de Montréal.
https://quebio.ca/en/arbresmtl
International Society of Arboriculture. (2018). Basic Tree Risk Assessment Form.
https://wwv.isa-arbor.com/education/onlineresources/basictreeriskassessmentform
Texas A&M Forest Service. (2024). Tree Risk Mobile App – Download.
https://texasforestinfo.tamu.edu/MobileApps/TreeRisk/
Regent Instruments. (2023). Image Analysis for Plant Science - Products.
https://www.regentinstruments.com/assets/products.html
Tree-Related Tools
Tree Inventory
Tree Risk Assessment
Dendrology tools
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Perdue University. (n.d.). Purdue Plant Doctor.
https://www.purdueplantdoctor.com/
Native Plant Trust. (n.d.). Go Botany Plant ID Tools.
https://gobotany.nativeplanttrust.org/
Virginia Tech. (2024). Virginia Tech Tree ID – App Download. Retrieved from Google Play.
https://play.google.com/store/apps/details?id=org.pottssoftware.agps21&hl=en_CA
Glority LLC. (2024). PictureThis Plant ID app– Botanist in Your Pocket.
https://www.picturethisai.com/
City of Vancouver. (2022). Orthophoto Imagery 2022 - dataset.
https://opendata.vancouver.ca/explore/dataset/orthophoto-imagery-2022/information/
Government of British Columbia. (n.d.). Maps & Orthos.
https://a100.gov.bc.ca/ext/mtec/public/products/mapsheet
McGill Libraries. (n.d.). CanImage – Data Download.
https://www.mcgill.ca/library/�nd/maps/canimage
Ontario Ministry of Natural Resources. (2023). Ontario Imagery Program. Geospatial Ontario
https://geohub.lio.gov.on.ca/pages/ontario-imagery-program
Resources
Canada in a Changing Climate: Advancing our Knowledge for Action. (2024). Map of Adaptation Actions.
https://changingclimate.ca/about-map-of-adaptation/
Green Municipal Fund. (n.d.). Factsheet: Urban forestry technology and tools.
https://greenmunicipalfund.ca/resources/factsheet-urban-forestry-technology-and-tools
Healthy Plan City. (2024). Explore equity in your city – interactive map.
https://healthyplan.city/en
Kip, J. (2022). Assessing Candidate Protected Areas using GIS Technology. Ontario Nature.
https://ontarionature.org/candidate-protected-areas-gis-blog/
LidarBC. (2023). British Columbia is investing in better data.
https://lidar.gov.bc.ca/
Plant and pest/disease identification
Orthoimagery
Canadian
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Natural Resources Canada (NRCan). (2023). New LiDAR Point Clouds product: Canada as you've never
seen it before! Retrieved from Government of Canada.
https://natural-resources.canada.ca/science-and-data/science-and-research/geomatics/topographic-
tools-and-data/whats-new/new-lidar-point-clouds-product-canada-youve-never-seen-it/24861
Natural Resources Canada (NRCan). (2024). Aerial LiDAR and forest inventory monitoring.
https://natural-resources.canada.ca/our-natural-resources/forests/sustainable-forest-management/
measuring-and-reporting/remote-sensing-forestry/aerial-lidar-and-forest-inventory-monitoring/13425
Nature Canada. (2022). Canada's Urban Forests: Bringing the canopy to all (September 2022).
https://naturecanada.ca/wp-content/uploads/2022/09/Nature-Canada-Report-Tree-Equity.pdf
Ontario Woodlot Association. (n.d.). Private Forest Inventory Program.
https://www.ontariowoodlot.com/Forest-Inventory-Program
Standards Council of Canada. (2022). Urban Heat Island Mapping Workshop: What We Heard.
https://scc-ccn.ca/system/
�les/2024-05/20221206_uhi_what_we_heard_report_�nal_en_2023-04-04.pdf
American Forests. (2024). Tools, Research, Reports & Guides.
https://www.americanforests.org/tools-research-reports-and-guides/
Portland Parks & Recreation Urban Forestry. (2024). Street Tree Inventory.
https://pdx.maps.arcgis.com/apps/webappviewer/index.html?
id=b4671f4591144530b1c590731923b182
Alonzo, M., Bookhagen, B., McFadden, J. P ., Sun, A. and Roberts, D. A. (2015). Mapping urban forest leaf
area index with airborne lidar using penetration metrics and allometry. Remote Sensing of Environment,
162, 141-153.
https://doi.org/10.1016/j.rse.2015.02.025.
Blackman, R., & Yuan, F. (2020). Detecting Long-Term Urban Forest Cover Change and Impacts of Natural
Disasters Using High-Resolution Aerial Images and LiDAR Data. Remote Sensing, 12(11), 1820.
https://doi.org/10.3390/rs12111820
Burns, J. (2012). Applications of LIDAR in Wildlife Management: an opportunity in British Columbia.
http://dx.doi.org/10.14288/1.0075533
Latifovic, R., Pouliot, D., and Olthof, I. (2009) North American Land Change System: Canadian
Perspective. 30th Canadian Symposium on Remote Sensing, Lethbridge, Alberta. Retrieved from
Government of Canada
https://natural-resources.canada.ca/maps-tools-and-publications/satellite-imagery-elevation-data-and-
Non-Canadian
Further Reading
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air-photos/characterization-and-monitoring-change-canadas-land-surface/9146
Le Saint, T., Nabucet, J., Hubert-Moy, L., & Adeline, K. (2024). Estimation of Urban Tree Chlorophyll
Content and Leaf Area Index Using Sentinel-2 Images and 3D Radiative Transfer Model Inversion.
Remote Sensing, 16(20), 3867.
https://doi.org/10.3390/rs16203867
Münzinger, M., Prechtel, N. and Behnisch, M. (2022). Mapping the urban forest in detail: From LiDAR
point clouds to 3D tree models. Urban Forestry & Urban Greening 74, 127637.
https://doi.org/10.1016/j.ufug.2022.127637
Nitoslawski, S. and Konijnendijk, C. C. (2022). The Emergence of Smart Urban Forestry: Challenges and
Opportunities in the Digital Age. Arboriculture & Urban Forestry, 48(2), 45-48.
https://doi.org/10.48044/jauf.2022.004
Ren, Z., Du, Y., He, X. et al. Spatiotemporal pattern of urban forest leaf area index in response to rapid
urbanization and urban greening. Journal of Forestry Research, 29, 785–796 (2018).
https://doi.org/10.1007/s11676-017-0480-x
Staley, D. C. (2022). Modern Urban Forestry for Modern Cities: Technology Challenges and Opportunities
for the Remote Sensing of Urban Forests. Arboriculture & Urban Forestry (AUF) 48(2), 147-163.
https://doi.org/10.48044/jauf.2022.012
Ward, K. T. and Johnson, G. R. (2001). Geospatial methods provide timely and comprehensive urban
forest information. Urban Forestry & Urban Greening, 6(1), 15-22.
https://doi.org/10.1016/j.ufug.2006.11.002
Wulder, M., Hermosilla, T., White, J., Bater, C., Hobart, G. and Bronson, S. (2024). Development and
implementation of a stand-level satellite-based forest inventory for Canada. Forestry: An International
Journal of Forest Research. 97.
https://doi.org/10.1093/forestry/cpad065
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Datasets
Federal, provincial, municipal governments, academic institutions, and non-
government organizations produce, maintain, and distribute several urban forest and
urban environment-related datasets covering all or part of Canada. Many of these
available datasets are helpful for urban forestry practitioners as they are
standardized and have long-term update plans, ensuring their availability in the
future. Most of these datasets are available online, publicly accessible, or available
through data-sharing agreements. National and provincial data are listed below, as
well as some individual national datasets made available by non-governmental
organizations. Federal and provincial datasets generally contain remote sensing and
spatial data, geological and soil data, census data, and other large-scale data types.
Municipal datasets often include local landcover data, orthoimagery, and city-level
spatial data. Many municipalities and cities across Canada develop and maintain
open data portals speci�c to their geographic area. Some of these are: In Alberta,
Edmonton, Calgary, Medicine Hat, Red Deer, and Grande Prairie. In British Columbia,
the open data includes Vancouver, Kamloops, Langley, Nanaimo, North Vancouver,
Prince George, Surrey, and the Regional District of North Okanagan. For Manitoba,
there is open data for Winnipeg. In New Brunswick, for Fredericton. Ontario's open
data municipalities include London, Ottawa, Toronto, Windsor, Niagara Falls,
Highlights
Urban forestry datasets
Government and non-government organizations in Canada maintain open-access
urban forest-related datasets.
Types of data
Remote sensing and spatial data, tree inventories, canopy data, geological and soil
data, census data, land-cover data, large-scale and municipal datasets.
Open data
Publicly accessible online data.
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Mississauga, Burlington, York Region, Peel Region, Niagara Region, Guelph, Hamilton,
City of Waterloo, and Waterloo Region. In Quebec, the cities are Montreal, Ville de
Québec/Quebec City, and Sherbrooke. In Saskatchewan, open data is available for
Regina and Saskatoon, New Brunswick for Fredericton, and Prince Edward Island for
Charlottetown.
For further information about any other municipality, visit the municipal site to
determine if an open data portal is maintained by the appropriate governing authority.
Resources
Government of Canada. (n.d.). Open Government Portal – Open Data.
https://search.open.canada.ca/data/
Government of Canada. (n.d.). Open Government Portal – Open Maps.
https://search.open.canada.ca/opendata/?page=1&sort=metadata_modi�ed%20desc&collection=fgp
Statistics Canada. (2024). Data products, 2021 census.
https://www12.statcan.gc.ca/census-recensement/2021/dp-pd/index-eng.cfm
Canadian Institute of Forestry (CIF). (2024). CIF-IFC Urban Forestry Learning Hub – Interactive Map.
https://dsny5wm08q4u8.cloudfront.net
National Forest Information System. (2024). National Terrestrial Ecosystem Monitoring System for
Canada.
https://opendata.n�s.org/mapserver/n�s-change_eng.html
Urban Heat Island Toronto (UHI Toronto). (2020). Toronto Census Metropolitan Area – Land Surface
Temperature.
https://uhitoronto.z13.web.core.windows.net/
Canadian Open Datasets by Government
National/Federal
Canadian Datasets
National
Provincial
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City of Edmonton. (n.d.). City of Edmonton Open Data Portal.
https://data.edmonton.ca/
City of Calgary. (n.d.). City of Calgary Open Data Portal.
https://data.calgary.ca/
City of Medicine Hat. (n.d.). City of Medicine Hat Open Data.
https://www.odata.org/ecosystem/liveservices/City-of-Medicine-Hat-Open-Data-Portal/
City of Red Deer. (n.d.). City of Red Deer Open Data Catalogue.
https://data.reddeer.ca/datasets
City of Grande Prairie. (n.d.). City of Grande Prairie Open Data.
https://opendata.countygp.ab.ca/
Government of Alberta. (n.d.). Open Government Program – Open Data.
https://open.alberta.ca/opendata
Government of Alberta. (n.d.). GeoDiscover Alberta.
https://open.alberta.ca/interact/geodiscover-alberta
City of Kamloops. (n.d.). City of Kamloops Open Data Catalogue.
https://mydata-kamloops.opendata.arcgis.com/
City of Nanaimo. (n.d.). City of Nanaimo Open Data Catalogue.
https://www.nanaimo.ca/open-data-catalogue/
City of North Vancouver. (n.d.). City of North Vancouver Open Data.
https://www.dnv.org/government-administration/open-data-geoweb
City of Prince George. (n.d.). City of Prince George Open Data Catalogue.
https://data-cityofpg.opendata.arcgis.com/
City of Surrey. (n.d.). City of Surrey Open Data.
https://www.surrey.ca/services-payments/online-services/open-data
City of Vancouver. (2024). Open Data Portal.
https://opendata.vancouver.ca/pages/home/
Government of British Columbia. (2024). Geographic Data and Tools.
https://www2.gov.bc.ca/gov/content/data/geographic-data-services
Regional District of North Okanagan. (n.d.). RDNO Maps and Digital Data.
https://www.rdno.ca/maps
Township Langley. (n.d.). Township of Langley Open Data.
Alberta
British Colombia
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https://www.tol.ca/en/connect/open-data.aspx
Government of Manitoba. (n.d.). Data MB – Open Data.
https://geoportal.gov.mb.ca
City of Winnipeg. (2024). City of Winnipeg Open Data Portal.
https://data.winnipeg.ca
Government of New Brunswick. (n.d.). Open Data New Brunswick.
https://gnb.socrata.com
City of Fredericton. (n.d.). City of Fredericton Open Data.
https://data-fredericton.opendata.arcgis.com/
Government of Nova Scotia. (2024). Open Data Portal.
https://data.novascotia.ca
Government of Northwest Territories. (n.d.). NWT Centre for Geomatics.
https://www.geomatics.gov.nt.ca/en
City of Halifax. (n.d.). Halifax Data, Mapping, and Analytics Hub – Open Data.
https://data-hrm.hub.arcgis.com/pages/open-data-catalogue
Canada-Nunavut Geoscience O�ce. (2021). Home – Nunavut Geoscience.
https://nunavutgeoscience.ca/en/
City of Burlington. (n.d.). City of Burlington Open Data.
Manitoba
New Brunswick
Newfoundland & Labrador
Northwest Territories
Nova Scotia
Nunavut
Ontario
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https://www.burlington.ca/en/council-and-city-administration/open-data.aspx
City of Guelph. (n.d.). City of Guelph Open Data.
https://geodatahub-cityofguelph.opendata.arcgis.com/
City of Hamilton. (n.d.). City of Hamilton Open Data.
https://open.hamilton.ca/
City of London. (n.d.). City of London Open Data.
https://opendata.london.ca/
City of Mississauga. (n.d.). City of Mississauga Open Data.
https://data.mississauga.ca/
City of Niagara Falls. (n.d.). City of Niagara Falls Open Data.
https://niagarafalls.ca/services/open/default.aspx
City of Ottawa. (n.d.). City of Ottawa Open Data.
https://open.ottawa.ca/
City of Toronto. (n.d.). City of Toronto Open Data Portal.
https://open.toronto.ca/
City of Waterloo. (n.d.). City of Waterloo Open Data.
https://data.waterloo.ca/
City of Windsor. (n.d.). City of Windsor Open Data Catalogue.
https://opendata.citywindsor.ca/
Government of Ontario. (2024). Ontario GeoHub.
https://geohub.lio.gov.on.ca
Niagara Region. (n.d.). Niagara Region Open Data.
https://niagaraopendata.ca/
Region of Peel. (n.d.). Region of Peel Open Data.
https://data.peelregion.ca/
Region of Waterloo. (n.d.). Region of Waterloo Open Data.
https://www.regionofwaterloo.ca/en/regional-government/open-data.aspx
York Region. (n.d.). York Region Open Data.
https://insights-york.opendata.arcgis.com/
City of Charlottetown. (n.d.). City of Charlottetown Open Data.
https://www.charlottetown.ca/business___development/invest_here/data_and_information_hub
Prince Edward Island Government. (2024). Prince Edward Island Open Data.
https://data.princeedwardisland.ca
Prince Edward Island
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City of Sherbrooke. (n.d.). City of Sherbrooke Open Data.
https://donneesouvertes-sherbrooke.opendata.arcgis.com/
City of Montreal. (n.d.). City of Montreal Open Data Portal.
https://montreal.ca/en/articles/open-data-platform-easy-access-10641
Données Québec. (2024). Québec Open Data.
https://www.donneesquebec.ca
Ville de Québec. (n.d.). Ville de Québec Open Data.
https://www.ville.quebec.qc.ca/services/donnees-services-ouverts/index.aspx
City of Regina. (n.d.). City of Regina Open Data.
https://open.regina.ca/
City of Saskatoon. (n.d.). Open Data – Explore Data Catalogue.
https://data-citysaskatoon.opendata.arcgis.com
City of Saskatoon. (n.d.). City of Saskatoon Open Data.
https://www.saskatoon.ca/services-residents/connect-your-city/open-data
Government of Saskatchewan. (n.d.). Saskatchewan GeoHub.
https://geohub.saskatchewan.ca
Government of Yukon. (2024). GeoYukon - Yukon digital map data viewer.
https://open.yukon.ca/data/datasets/geoyukon-yukon-digital-map-data-viewer
National Centers for Environmental Information. (2024). Monthly Global Climate Report for Annual 2023.
National Oceanic and Atmospheric Administration.
https://www.ncei.noaa.gov/access/monitoring/monthly-report/global/202313
European Space Agency (ESA). (2020). Worldwide Land Cover Mapping.
https://esa-worldcover.org/en
Quebec
Saskatchewan
Yukon
International Datasets
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Urban Forest Management Planning
Diverse urban forest management and tree maintenance practices play a vital role in
keeping urban forests healthy, managing tree hazards, planting trees, and/or
generally sustaining tree canopy in urban areas. However, these practices have often
targeted public trees, focusing on street trees or speci�c management practices
(e.g., pruning). Urban tree maintenance and management have often been
implemented as reactive responses to natural disasters or invasive species impact
rather than as proactive approaches. While the importance of urban forests was
recognized in the 1960s, it took over 50 years to understand how this valuable natural
resource should be managed in its entirety and more strategically.
Strategic urban forest management in Canada emerged in the early 2000s, based on
the idea that the entire urban forest and all its components need to be strategically
managed through a carefully planned process (Kenney, 2003; Kenney et al., 2011).
Such strategic and effective urban forest management ensures that the diverse
Highlights
Strategic urban forest management
For maintaining urban forest health, optimizing urban forest bene�ts, and proactive
management.
Urban forest management planning in Canadian cities
Examples.
Supporting strategies
These plans can be strengthened through natural asset management, urban forest
monitoring, and certi�cations.
Natural Asset Management (NAM)
Stock of natural resources.
Sustainable Forestry Initiative
Urban Forest Standards
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bene�ts urban forests provide are maximized and sustained over time. As critical
components of green infrastructure and urban land uses, urban forests and green
spaces require careful planning and management that is adaptive and sustainable.
Taking a proactive approach to urban forest management ensures that urban forests
are not left unmanaged. It also ensures that an urban forest management plan
addresses foreseen pressures and challenges such as urban development, genetic
diversity of tree species, and tree age distribution. Additionally, it incorporates
measures for unforeseen challenges that could occur due to pest outbreaks, invasive
species impacts, or climate change.
The leading objectives of urban forest management are to optimize the tree canopy
leaf area by planting and maintaining a genetically diverse and site-appropriate mix
of trees and shrubs, which should be achieved cost-effectively while maximizing
public bene�ts and minimizing risks to public safety. Urban forest management
planning begins by assessing the existing state of urban forests using the most
recent data. If tree inventories are not available, new management plans should
include a tree inventory that surveys tree species, size, overall health, and value.
Urban forest inventories are prerequisite for measuring urban forest bene�ts and
developing comprehensive urban forest management plans, and also serve as a base
for developing natural asset management plans (GIOC, 2016). While natural asset
management ideas related to natural areas emerged in 2017, the concept has also
been applied to urban forests overall. Recently, Urban Forest Certi�cation standards
were developed to address the growing need for sustainable management of urban
forests (SFI, 2024). All these approaches contribute to urban forest management and
share many common objectives and components, namely tree inventories.
Strategic Urban Forest Management Planning in Canadian
Cities
Urban forests and all their elements have been recognized as the backbone of green
infrastructure in Canada, and as critical for connecting urban and rural green areas
(GIOC, 2015; NRCan, Canadian Forest Service, 2022). Strategic management
planning emphasizes the importance of managing all urban forest components and
their associated biotic and abiotic elements across a wide range of land uses and
areas, from large to small communities, as well as the areas between them.
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Moreover, the entire urban forest, including trees across a range of urban spaces
such as streets, parks, cemeteries, arboretums, private properties, and natural forest
fragments, is recognized by strategic management planning.
The importance of strategic urban forest management planning was introduced to
Canada by Kenney et al (2011), but the �rst Urban Forest Master Plan was developed
for Prince George in 2003 as a response to the impact of �re that devastated the
area. Following the principles of strategic urban forest management planning, urban
forest strategic management plans were developed by many municipalities, such as
the Town of Oakville (2008), the City of Guelph (2008), Town of Ajax (2011), and
Halifax and the City of Toronto (2013), to name a few. While the development of
urban forest plans in Canada peaked from 2010-14 within more urbanized mixed-
forest regions (Ordóñez Barona, 2024; Puric-Mladenovic & Bardekjian, 2023b), new
urban forest plans are still developing, while the early plans are being updated or
prepared for renewal.
Urban forest management plans or strategies that provide a long-term, strategic
approach to protect, preserve, and enhance the municipal urban forest are typically
approved by city councils. Canadian municipalities are among the global leaders in
terms of urban forest management planning, with over 80 urban municipalities
having urban forest management plans. For example, based on the 2023 study
(Puric-Mladenovic and Bardekjian, 2023b), 89 out of 800 (11%) of the examined
municipalities had an urban forest management strategy and/or urban forest
management plan. Since that time, there has been an increase to 118 (14.7%)
municipalities with urban forest management plans or strategies. For example,
Saskatoon recently released its Urban Forest Management Plan 2022-2031, which
emphasizes the importance of urban forest sustainability (City of Saskatoon, 2022);
the City of Saanich (2024) followed close behind with a 10-year urban forest strategy
published in 2024.
These urban forest management plans, though all aimed at maintaining and
maximizing urban forest canopy and tree bene�ts, differ based on how they approach
implementation, tree maintenance, increasing canopy coverage, diversifying species,
or involving the community (Kenney et al., 2011; Ordóñez & Duinker, 2013). Urban
forest management plans are also crucial for maximizing ecological services and
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resilience by guiding the long-term management of a healthy, biodiverse, resilient
urban forest.
Not all of these plans are created equally; some are detailed plans with set goals and
timelines, while some are more like strategies than plans. For example, the context of
some plans is more like an outline of the importance of urban forests rather than a
management plan. However, they are still valuable for setting the stage for
developing a Strategic Urban Forest Management Plan (SUFMP), which is a long-
term plan (typically 20 or 25 years) with a detailed roadmap of how to achieve the set
long-term vision and goals. SUFMPs are based on measurable objectives that allow
plans to move strategically from a baseline condition to a desired set target while
prioritizing implementation and monitoring the implementation and success of the
plan. These plans are based on understanding the existing state of the urban forest
and then setting measurable objectives, criteria, and indicators, which are all crucial
to developing an actionable management plan. Strategic urban forest management
planning objectives, depending on the region, type of urban area, and state of the
urban forest, can include increasing tree canopy cover, enhancing the longevity and
health of urban forests, diversifying species, or fostering engagement from the
community. Other common goals in SUFMP for urban forests across Canada include
expanding species diversity, improving tree health, managing invasive species,
increasing resilience against climate change and natural disasters, and improving
canopy cover equity.
SUFMP objectives are achieved through detailed operational plans, which might
include reaching speci�c canopy cover percentage targets, plans for invasive species
removal, followed by native species plantings, community stewardship initiatives, or
hazard tree removals, to name a few (Kenney et al., 2011; Ordóñez & Duinker, 2013).
For example, the urban forest plan for the City of Calgary aims to raise canopy cover
to 16% by 2060, protect current forests, and engage the community in forestry
projects (City of Calgary, n.d.), while the plan for the City of Toronto aims to achieve
40% canopy cover by 2050 (City of Toronto, 2023). Strategic goals in SUFMP are
aimed to be achieved through speci�c operational plans that are typically at 4-5 year
intervals. Furthermore, 4-5 year operational plans are implemented through Annual
Operating Plans (AOPs). AOPs involve day-to-day decisions on things like planting,
pruning, and felling trees, controlling pests and diseases, and ensuring optimal water
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and soil conditions. Annual operational planning also involves developing a budget,
delegating roles and responsibilities, and establishing metrics to monitor progress.
As an illustration, a strategic urban forest plan for the City of Calgary involves
operational initiatives of caring for existing trees, planting 3,500 new trees each year,
and prioritizing public safety and legal safeguards to protect new and existing trees
through bylaws (City of Calgary, n.d.).
Natural Asset Management
Natural Asset Management (NAM) is an emerging approach to urban forestry in
Canada where natural features are viewed as any other municipal asset or gray
infrastructure that provides essential services. In this context, urban forests, as a
natural asset, are placed into formal municipal asset management frameworks and
plans. Several Canadian municipalities have implemented NAM strategies to
enhance urban forest management; the Town of Gibsons, BC, was the �rst to
implement NAM and recognize aquifers, forests, and wetlands as green
infrastructures that need management. A monetary value was assigned to these
natural systems, which enabled them to be incorporated into the town’s asset
management plans and ensure their management and sustainable use (Town of
Gibsons, 2018). Another example is the City of Edmonton, which developed an Urban
Forest Asset Management Plan that focuses on the characteristics and conditions of
publicly managed urban forest assets (City of Edmonton, 2021). It also provides a
framework for achieving desired service levels at optimal life cycle costs. The City of
Saskatoon also recently completed an inventory of its natural assets (wetlands, a
portion of the South Saskatchewan River, grasslands, forest/shrublands) and
completed their evaluation to support their own NAM (City of Saskatoon, 2020).
Urban Forest Certification
Forest sustainability and good management certi�cations have existed in Canada for
managed forests and woodlots since 1995. Recently, one of the leading forest
certi�cation programs, the Sustainable Forestry Initiative (SFI), developed a
certi�cation standard for the sustainability of urban forests. The SFI certi�cation
standards for urban forests are grouped into 16 different objectives aimed at
continual improvement of urban forestry programs. The 16 core objectives are:
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fostering community, people, and Indigenous participation; enhancing human health
and well-being; conserving biodiversity; stewarding natural resources such as air,
water, and soil; promoting tree health and vitality; protecting special sites, including
natural areas; implementing climate-smart management; advancing urban forest
planning; ensuring effective management and care of urban forests; preparing for
and responding to disasters; building capacity; utilizing urban wood resources;
strengthening communications; supporting science, research, and technology;
adhering to legal and regulatory standards, including Indigenous rights, and
maintaining transparent reporting (SFI, 2024). Achieving these objectives should be
an end goal for any new SUFMP .
Urban Forests Monitoring
All urban forest management initiatives must be evaluated for their performance
using both pre-determined criteria and adaptive judgments of the effect of
management strategies on urban forests. As such, consistent long-term monitoring
is crucial to supporting and evaluating any urban forest management plan.
Monitoring may take the form of updated street tree inventories, canopy cover equity
mapping and analyses, policy impacts, woodlands and natural areas monitoring,
vegetation monitoring, or public opinion surveys (among a myriad of other
monitoring approaches) (Green Municipal Fund, n.d.). Provisions for continued
monitoring should be included in all steps of management plans.
Resources
Green Infrastructure Ontario Coalition (GIOC). (2016). Urban Forests & Asset Management Planning — A
Primer.
https://greeninfrastructureontario.org/app/uploads/2016/06/UF-Toolkit-Part-2-Asset-Management-
Primer-Final.pdf
Green Municipal Fund. (n.d.). Factsheet: Urban forest planning.
https://greenmunicipalfund.ca/resources/factsheet-urban-forest-planning
Municipal EcoToolkit. (2020). Municipal EcoToolkit – Tools for Maintaining Your Natural Systems.
https://www.municipal-ecotoolkit.ca/
Natural Assets Initiative. (2024). Nature is infrastructure: how to include natural assets in asset
Canadian
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management plans, a guidebook for local governments (1 e). Retrieved from Municipal Finance O�cers’
Association
https://mnai.ca/wp-content/uploads/2024/04/NAI-NAM-guidance-doc-april-2024.pdf
Programme for the Endorsement of Forest Certi�cation (PEFC). (2024). Forest Management Certi�cation.
https://www.pefccanada.org/pefc-standards/forest-management-certi�cation.htm
Puric-Mladenovic, D. and Bardekjian, A. C. (2023a). Canada’s Urban Forestry Footprint.
https://utoronto.maps.arcgis.com/apps/dashboards/21acf59a306d41dd862c4e6ba25a0da0
Puric-Mladenovic, D. and Bardekjian, A. (2023b). Canada's Urban Forest Footprint: Mapping the Extent and
Intensity of Urban Forestry Activities. Forests in Settled & Urban Landscapes applied science and
research lab. Daniels Faculty, University of Toronto. John H. Daniels Faculty of Architecture, Landscape
and Design, University of Toronto.
City of Calgary. (2007a). Calgary, a City of Trees: Parks urban forest strategic plan.
https://www.calgary.ca/content/dam/www/csps/parks/documents/management-plans/urban-
forestry-strategic-plan.pdf
City of Edmonton. (2007b). Policy C531: Natural Area Systems.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PoliciesDirectives/C531.pdf
City of Edmonton. (2012). Urban Forest Management Plan.
https://www.edmonton.ca/public-�les/assets/document?path=PDF/
Urban_Forest_Management_Plan.pdf
City of Edmonton. (2014). City-Wide Natural Area Management Plan – January 2014.
https://www.edmonton.ca/sites/default/�les/public-�les/City-
Wide_Natural_Area_Management_Plan.pdf
City of Edmonton. (2021). Urban Forest Asset Management Plan.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PDF/Urban-Forest-Asset-
Management-Plan.pdf
City of Lethbridge. (2021). City of Lethbridge Urban Forest Management Plan – 2021-2041.
https://getinvolvedlethbridge.ca/8261/widgets/32516/documents/119445
City of Prince George. (2006). Community Forest of Prince George: Management Plan.
https://treecanada.ca/wp-content/uploads/2017/11/City-of-prince-George.pdf
City of Spruce Grove. (2004). Urban Forest Management Plan: Vol. 1.
https://www.sprucegrove.org/media/2062/urban-forest-management-plan.pdf
st
Canadian Urban Forest Management Plans (36)
Alberta
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City of Abbotsford. (2022). Urban Forest Strategy: 2020 – 2045.
https://www.abbotsford.ca/sites/default/
�les/2022-05/2021-22%20Urban%20Forestry%20Strategy.pdf
City of Courtenay. (2019). Courtenay Urban Forest Strategy – 2019-2050.
https://www.courtenay.ca/assets/Departments/
Documents/190710_Courtenay%20UrbanForestStrategy_FINAL-Reduced.pdf
City of Kelowna. (2024). Sustainable urban forest strategy [PDF]. Retrieved January 12, 2025, from
https://hdp-ca-prod-app-kelowna-involved-�les.s3.ca-
central-1.amazonaws.com/8917/2470/9018/2024_Sustainable_Urban_Forest_Strategy.pdf
City of Maple Ridge. (2024). Maple Ridge Urban Forest Management Plan.
https://www.mapleridge.ca/media/�le/�nalufms240723v15with-appendicesreduced�nalpdf-0
City of Nanaimo. (2010). Urban Forest Management Plan.
https://www.nanaimo.ca/docs/services/home-and-property/ufms-edited-2012-1.pdf
City of Penticton. (2024). Urban Forest Management Plan: Our o�cial community tree plan.
https://www.penticton.ca/sites/default/�les/docs/parks-and-recreation/parks/
Penticton%20UFMP%20-%20FINAL%20(August%2022%2C%202024)_compressed.pdf
City of Port Moody. (2023). Urban Forest Management Strategy.
https://www.portmoody.ca/en/recreation-parks-and-environment/resources/Documents/
Port%20Moody%20UFMP .pdf
City of Saanich. (2024). Urban Forest Strategy – 2024-2034.
https://www.saanich.ca/assets/Community/Documents/
Environment/240726_SaanichUFS_8_online.pdf
City of Surrey. (2023). Urban Forest Management Strategy.
https://www.surrey.ca/sites/default/�les/media/documents/surrey-urban-forest-management-
strategy.pdf?utm_source=chatgpt.com
City of Victoria. (2013). Urban Forest Master Plan.
https://www.victoria.ca/media/�le/urban-forest-master-planpdf
District of West Vancouver. (2023). District of West Vancouver Urban Forest Management Plan.
https://westvancouver.ca/media/2180
City of Morden. (2022). Parks And Urban Forestry Master Plan.
https://conservation.mymorden.ca/wp-content/uploads/2022/06/Morden-Masterplan-Document-
DRAFT-2022-02-18_Online-Format.pdf
British Colombia
Manitoba
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City of Winnipeg. (2023). Winnipeg Comprehensive Urban Forest Strategy.
https://engage.winnipeg.ca/10550/widgets/67282/documents/120884
City of Winnipeg. (n.d.). Winnipeg Urban Forest Strategy – Documents.
https://engage.winnipeg.ca/urbanforest/widgets/67282/documents
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City of Thunder Bay. (2011). Urban Forest Management Plan.
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TBay-UF-Final-Print-Version020812.pdf
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Supporting In�ll Housing. Planning and Housing Committee.
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�le-verison=1736714019200
Clean Air Council. (2025). Urban Forest Plans – Ontario.
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LargeParks_Report_Sm_upd4-13-22.pdf
Town of Ajax. (2011). Town of Ajax Urban Forest Management Plan: Comprehensive Report (2011-2015).
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Town of Aurora. (2024). Natural Capital Asset Management Plan (NCAMP).
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Management-Plan-NCAMP .pdf
City of Charlottetown. (2024). City Of Charlottetown Post-Fiona Urban Forest Restoration Strategy.
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Prince Edward Island
Quebec
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Arrondissement de Côte-des-Neiges—Notre-Dame-de-Grâce. (2011). Plan de foresterie urbaine. Nature-
Action Québec.
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compressed.pdf
Habitat. (2022). Plan directeur de foresterie urbaine de la Ville de Rosemère : Portrait, diagnostics et
stratégie de plantation. 76 p.
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_PLAN_DE_FORESTERIE_-_HABITAT.pdf
Ville de Drummondville. (2022). Politique de L’Arbre: Plan D’action En Foresterie Urbaine.
https://www.drummondville.ca/wp-content/uploads/2020/05/VIDR_Plan-action_Politique-
Arbre_05_WEB-medium.pdf
Ville de Gatineau. (2023). Plan de foresterie urbaine (PFU) 2023-2030.
https://www.gatineau.ca/docs/guichet_municipal/arbres/plan_foresterie_urbaine.fr-CA.pdf
Ville de Laval. (2020). Plan de foresterie urbaine.
https://www.laval.ca/Documents/Pages/Fr/citoyens/environnement-recyclage-et-collectes/trame-
verte-bleue-plan-foresterie-urbaine.pdf
Ville de Lévis. (2012). Des Arbres pour Demain – Politique de foresterie urbaine.
https://www.ville.levis.qc.ca/�leadmin/Documents_PDF/politique-foresterie_web_opt.pdf
Ville de Montréal. (2009). Plan de foresterie urbaine de St. Laurent.
https://ville.montreal.qc.ca/pls/portal/docs/page/arrond_sla_fr/media/documents/
plan_foresterie_urb2009.pdf
Ville de Montréal. (2020). Foresterie Urbaine & Équité Environnementale: Recommander Pour Outiller Les
Professionnels De L’aménagement Du Territoire A�n De Rendre La Ville De Montréal Plus Résiliente.
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Ville de Mont-Tremblant. (2024). Plan D’action En Foresterie Urbaine: 2025-2030.
https://www.villedemont-tremblant.qc.ca/public_upload/�les/ville/plans-politiques/
Foresterie2024VF.pdf?v=33641
Ville de Pointe-Claire. (2020). Urban Forestry Policy.
https://www.pointe-claire.ca/content/uploads/2020/01/19-0742_pc_politique_foresterie_en.pdf
Ville de Repentigny. (2021). Politique de Foresterie Urbaine et de Biodiversité.
https://repentigny.ca/sites/default/�les/2021-04/ville_repentigny_politique-foresterie-urbaine-
biodiversite_2016-05.pdf
Ville de Saint-Eustache. (2022). Politique De Foresterie Urbaine.
https://www.saint-eustache.ca/storage/app/media/ville/vie-democratique/politiques-et-codes-
dethique/vse-politique-foresterie-urbaine.pdf
Ville de Québec. (2015). Place aux arbres: Vision de l’arbre 2015-2025.
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https://www.ville.quebec.qc.ca/apropos/plani�cation-orientations/environnement/milieuxnaturels/
docs/vision_arbre_2015_2025.pdf
Ville de Québec. (2010). Plan Directeur des Milieux Naturels et de la Forêt Urbaine – Tome 2: La Forêt
Urbaine.
https://www.ville.quebec.qc.ca/citoyens/propriete/arbres/docs/plan_directeur_foret_urbaine.pdf
City of Prince Albert. (2018). Forestry Management Plan 2018-2038.
https://www.citypa.ca/en/parks-recreation-and-culture/resources/Documents/Forestry-Management-
Plan.pdf
City of Regina. (2000). The Regina Urban Forest Management Strategy.
https://treecanada.ca/wp-content/uploads/2017/11/THE-REGINA-URBAN-FOREST.pdf
City of Saskatoon. (2021). Urban Forest Management Plan.
https://www.saskatoon.ca/sites/default/�les/urban_forest_management_plan_0.pdf
City of Saskatoon. (2022). Pathway to a Sustainable Urban Forest - Implementation of the Urban Forest
Management Plan 2022-2031.
https://www.saskatoon.ca/sites/default/�les/
Pathway%20to%20a%20Sustainable%20Urban%20Forest%20-
%20Implementation%20of%20the%20Urban%20Forest%20Management%20Plan%202022-2031_3.pdf
City of Warman. (2018). Environmental Master Plan.
https://warman.ca/DocumentCenter/View/2210/EMP-Final-Plan
City of Whitehorse. (2021). Urban Forest Strategy 2021-2031: Implementation and action plan.
https://www.whitehorse.vic.gov.au/sites/whitehorse.vic.gov.au/�les/assets/documents/Whitehorse-
Urban-Forest-Strategy-Action-Plan-2021-2031.pdf
Sustainable Forestry Initiative (SFI). (2024). SFI Urban and Community Forest Sustainability Standard.
https://forests.org/wp-content/uploads/SFIUrbanCommunityForestStandard.pdf
Urban Forest Management Plan (UFMP). (n.d.). UFMP Toolkit.
https://ufmptoolkit.net/
USDA Forest Service. (2006). Urban Forestry Manual.
https://urbanforestrysouth.org/resources/library/ttresources/uf-manual-complete/
USDA Forest Service. (2022). Hazard Tree Identi�cation and Mitigation.
Saskatchewan
Yukon
Non-Canadian
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https://www.fs.usda.gov/Internet/FSE_DOCUMENTS/fseprd1006739.pdf
USDA Forest Service. (n.d.). A Guide: Developing a Street and Park Tree Management Plan.
https://www.umass.edu/urbantree/mgtplanguide.pdf
USDA Forest Service. (n.d.). Management Tools.
https://www.fs.usda.gov/forestmanagement/tools.shtml
USDA Forest Service. (n.d.). Urban Tree Risk Management: A Community Guide to Program Design and
Implementation.
https://research.fs.usda.gov/treesearch/11070
Vibrant Cities Lab, USDA Forest Service, American Forests. (n.d.). Step 7 – Planning: Best Practices in
Urban Forestry. Vibrant Cities Lab.
https://vibrantcitieslab.com/toolkit/plan-the-total-program/
Wisconsin Department of Natural Resources. (n.d.). A Technical Guide to Developing Urban Forest
Strategic Plans & Urban Forest Management Plans.
https://dnr.wisconsin.gov/sites/default/�les/topic/UrbanForests/UFPlanningGuide.pdf
City of Saskatoon. (2020). City of Saskatoon Natural Capital Asset Valuation Pilot Project.
https://www.saskatoon.ca/sites/default/�les/documents/ncav-report-�nal.pdf
District of Saanich. (2024). Toward natural asset management in the District of Saanich, British Columbia.
https://www.saanich.ca/assets/Local~Government/Documents/Engineering/AM_DoS-
June2024_NAM-Inventory-report-NAI.pdf
Green Infrastructure Ontario Coalition. (2015). Ontario's urban forests: Call to action.
https://greeninfrastructureontario.org/app/uploads/2016/06/
GIO_Urban_Forest_Call_to_Action_Sept15Print.pdf
Kenney, W. A. (2003). A Strategy for Canada's Urban Forests. The Forestry Chronicle, 79(4), 785-789.
https://doi.org/10.5558/tfc79785-4
Kenney, W. A., van Wassenaer, P . J. E., & Satel, A. L. (2011). Criteria and Indicators for Strategic Urban
Forest Planning and Management. Arboriculture & Urban Forestry, 37(3), 108-117.
https://www.fufc.org/soap/kenney_criteria_and_indicators2011.pdf
Miller, R. W., Hauser, R. J., & Werner, L. P . (2015). Urban Forestry: Planning and Managing Urban
Greenspaces (3 ed.). Long Grove, IL: Waveland Press, Inc.
Natural Resources Canada (NRCan), Canadian Forest Service. (2022). Think tank on a pan-Canadian
strategy on urban forests: Synopsis of discussion.
https://www.csla-aapc.ca/sites/csla-aapc.ca/�les/CFS-Urban_Forest_summary_EN%20_small.pdf
Ordóñez Barona, C. & Duinker, P . N. (2013). An analysis of urban forest management plans in Canada:
Implications for urban forest management. Landscape and Urban Planning, 116, 36-47.
Further Readings
rd
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https://doi.org/10.1016/j.landurbplan.2013.04.007
Ordóñez Barona, C., Jain, A., Heppner, M., St Denis, A., Boyer, D., J., Lane, C., Edwards, Duinker, P . and
Conway, T. (2024). Gaps in the implementation of urban forest management plans across Canadian
cities. Landscape and Urban Planning, 251, 105168.
https://doi.org/10.1016/j.landurbplan.2024.105168.
Ordóñez Barona, C., St Denis, A., Jung, J., Bassett, C. G., Delagrange, S., Duinker, P ., and Conway. T.
(2024). A content analysis of urban forest management plans in Canada: Changes in social-ecological
objectives over time. Landscape and Urban Planning, 251, 105154.
https://doi.org/10.1016/j.landurbplan.2024.105154.
Town of Gibsons. (2018). Advancing Municipal Natural Asset Management: The Town of Gibsons’
experience in �nancial planning & reporting.
https://gibsons.ca/wp-content/uploads/2018/01/GibsonsFinancialPlanningReportJan2018-PRINT.pdf
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Tree Maintenance
Tree maintenance is crucial for ensuring the health and longevity of urban trees,
which can directly support the sustainability of urban forests in Canadian
municipalities. Depending on the geographic region, environmental conditions, tree
age, and species, tree care can include a variety of practices. These include tree
pruning, watering, mulching, fertilizing, cabling, bracing, and identifying and removing
hazard trees. These practices not only enhance tree vitality but also help mitigate the
stresses that urban trees face due to environmental stressors like drought, pests and
pathogens, nutrient de�ciencies, invasive species, and general damage due to
physical stresses like weather or construction activities.
Maintenance Practices
Investment in the maintenance of newly planted and young trees pays off later by
having healthy trees and reducing the cost of their management. Some of the most
common maintenance practices used for young trees are watering, mulching,
pruning to shape the tree for a strong structure, protecting the base of a tree and
trunk from mechanical damage, inspecting for pests or diseases, and soil
improvement like fertilization. Some of the most common practices to maintain older
trees are regular pruning, protection of the root system from soil compaction,
Highlights
Maintenance practices
Ensuring the health and safety of trees and the people around them.
Tree maintenance practices
Pruning, watering, mulching, hazard removal.
Guidelines
Bylaws and handbooks for homeowners and practitioners.
Invasive insects and diseases
Monitoring and treatment.
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supplemental watering during drought conditions, and careful fertilization, which can
enhance tree longevity and vitality (ISA, 2021a).
Tree pruning is one of the most common maintenance practices used to support the
health, structure, and safety of urban managed trees. Pruning practices include
structural pruning of young trees, removal of dead, diseased, or damaged branches,
crown thinning, crown raising, pollarding, or in some cases, crown reduction to
prevent tree con�icts with structure or utility lines. It is best to time pruning during
the dormant season and avoid techniques like topping, which can harm the tree (see
chapter: Hydro Lines and Corridors).
Cabling and bracing are structural support techniques used to stabilize trees with
weak or multiple trunks, large limbs, or those subject to strong winds (Mayne, 1975;
Vandergriff & Clatterbuck, 2005). These methods are particularly useful in urban
settings where tree failure can pose signi�cant risks to public safety and
infrastructure (Purcell, 2017).
In urban growing spaces where natural water sources may be limited or inconsistent,
regular and deep watering is essential for establishing young trees and the
development of their root systems in the �rst few years (2 to 5 years). This is
particularly relevant during drought periods, which are becoming more frequent due
to climate change, and for newly planted trees, which are particularly at risk of drying
out (Steil, 2022; Zuzek, 2018; UMC, 2023).
Mulching complements watering by conserving soil moisture, reducing weed
competition, protecting trees from mechanical damage by mowers and trimmers, but
also improving root development (Sun et al., 2023; Magditsch, 2021; Qu et al., 2019).
Mulching also helps mitigate soil compaction, a common issue in urban
environments that can impede root growth and water in�ltration. Older trees might
also bene�t from mulching, which helps conserve moisture and improve soil health
(ISA, 2021b).
Fertilizing urban trees is a targeted approach to addressing nutrient de�ciencies
often found in city soils. However, it is important to apply fertilizers judiciously, as
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over-fertilization can lead to water pollution and tree health issues (Appleton &
Kauffman, 2021; Maine Forest Service, 2000; Bellis, 2023). In Canada, guidelines for
urban tree fertilization emphasize soil testing and the use of slow-release fertilizers
that match the speci�c needs of the tree species and site conditions (CFIA, 2024).
Identi�cation and removal of hazard trees are critical for urban forest management
practice. Hazard-rating systems, which assess the likelihood of tree failure and the
potential impact on people or property, are employed by many Canadian
municipalities to prioritize tree maintenance efforts (TRCA, 2006). By assessing key
hazard identi�ers such as limb damage, wood decay, and cankers, as well as
situational conditions such as frequent use areas, proximity to infrastructure, and
tree species failure potential, a decision can be made about the size of the hazard
and the urgency with which action, such as pruning or tree removal, should be taken
against the hazard. Taking a proactive approach in hazard tree management helps
manage risks and allocate resources effectively (Gurney & Ward, n.d.; Pokorny et al.,
2003; ISA, n.d.).
In addition to traditional maintenance practices, invasive insects and disease
management is a growing concern in global and Canadian urban forestry (Sweeney
et al., 2019). The spread of pests like the Emerald Ash Borer (Agrilus planipennis) has
led to signi�cant maintenance efforts to retain some trees and reduce tree loss,
requiring municipalities to implement extensive monitoring, treatment, and removal
programs. The City of Montreal, for example, has removed thousands of ash trees
(genus Fraxinus) to manage this invasive pest.
Tree Maintenance and Relevant Guidelines
Canadian municipalities follow national and provincial guidelines for urban tree
maintenance, often supplemented by local bylaws and urban forest management
plans. These frameworks provide a structured approach to tree care, emphasizing
sustainable practices, climate resilience, and community involvement. For instance,
the Canadian Urban Forest Strategy (CUFS) promotes best practices in urban
forestry, including tree maintenance, and recommends that municipalities integrate
urban forest management into broader city planning initiatives (Tree Canada, 2018).
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At the provincial level, organizations like the Ontario Urban Forest Council, the British
Columbia Urban Forest Network, and the Manitoba Urban Forest Council offer
resources and guidance on urban tree care, while municipalities often have their own
arboriculture standards and maintenance protocols. These include regular
inspections, pruning cycles, and emergency response plans for extreme weather
events.
Tree Maintenance and Human Resources
The effectiveness of tree maintenance programs depends on the availability of
skilled professionals, including arborists, urban foresters, and municipal staff trained
in tree care and management (Trees Are Good, n.d.). Continuous education and
training are vital to ensure that the latest techniques and knowledge are applied in
the �eld. In Canada, certi�cation programs such as those offered by the International
Society of Arboriculture (ISA) and other regional bodies are widely recognized and
help maintain high standards in urban tree care.
Moreover, municipalities often collaborate with community groups and volunteers to
support tree maintenance efforts, particularly in the context of tree-planting
initiatives and public awareness campaigns. Canadian municipalities can effectively
maintain and enhance their urban forests by engaging the broader public in tree care
and maintenance, invasive species monitoring, and tree monitoring, contributing to
healthier, more livable cities. For example, educating the public on how to prune and
maintain their private trees contributes to urban forest health and the enhancement
of tree canopy (Johnson et al., 2008; IUFC, n.d.). These partnerships are crucial in
fostering a shared sense of responsibility for the urban forest and ensuring its more
sustainable maintenance.
Resources
Brandt, J.P . (1994). Pruning trees and shrubs (lea�et) Natural Resources Canada. Canadian Forest
Service, Northwest Region, Northern Forestry Centre, Edmonton, Alberta. Forestry Lea�et 27.
Tree Maintenance Resources
Tree Pruning
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https://ostrnrcan-dostrncan.canada.ca/handle/1845/235955
City of Toronto. (2023). Tree Pruning Guidelines.
https://www.toronto.ca/wp-content/uploads/2023/10/9748-tree-pruning-guidelines.pdf
Inland Urban Forest Council (IUFC). (n.d.). A Practical Guide to the Proper Pruning of Trees and Shrubs.
https://www.ontarioca.gov/sites/default/�les/Ontario-Files/Parks-Maintenance/
practical_pruning_guide-single_pgweb.pdf
Bedker, P ., O’Brien, J., & Mielke, M. (1995). How to Prune Trees. United States Department of Agriculture
Forest Service.
https://extapps.dec.ny.gov/docs/lands_forests_pdf/prunetree.pdf
Purcell, L. (2015). Tree Pruning Essentials. Purdue Extension.
https://extension.purdue.edu/extmedia/FNR/FNR-506-W.pdf
Trees Are Good. (n.d.). Pruning Trees [webpage]. International Society of Arboriculture.
https://www.treesaregood.org/treeowner/pruningyourtrees
European Arboriculture Standards. (2022). Tree Cabling/Bracing Standard.
https://instytut-drzewa.pl/wp-content/uploads/2022/12/Tree-Cabling_Bracing.pdf
Mayne, L. (1975). Cabling and Bracing. Arboriculture & Urban Forestry, 1(6) 101-106.
https://doi.org/10.48044/jauf.1975.023
Purcell, L. (2017). Large Tree Cabling and Bracing. Purdue Extension.
https://www.extension.purdue.edu/extmedia/FNR/FNR-550-W.pdf
Vandergiff, D. & Clatterbuck, W. (2005). Cabling, Bracing and Other Support Systems for Trees. University
of Tennessee.
https://utia.tennessee.edu/publications/wp-content/uploads/sites/269/2023/10/SP659.pdf
University of Maryland (UMD). (2023). Watering Trees and Shrubs.
https://extension.umd.edu/resource/watering-trees-and-shrubs/
Zuzek, K. (2018). Watering newly planted trees and shrubs. University of Minnesota.
https://extension.umn.edu/planting-and-growing-guides/watering-newly-planted-trees-and-shrubs
International Society of Arboriculture (ISA). (2021b). Proper Mulching Techniques – Consumer Brochure.
Trees Are Good.
https://www.treesaregood.org/Portals/0/TreesAreGood_Proper%20Mulch%20Tech_0321.pdf
Cabling and Bracing
Watering
Mulching
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Appleton, B. & Kauffman, K. (2021). Fertilizing Landscape Trees and Shrubs.
https://www.pubs.ext.vt.edu/content/dam/pubs_ext_vt_edu/430/430-018/430-018_pdf.pdf
Canadian Food Inspection Agency. (2024). Fertilizers. Government of Canada.
https://inspection.canada.ca/en/plant-health/fertilizers
Maine Forest Service. (2000). Fertilizing Urban Trees.
https://www.maine.gov/dacf/mfs/forest_health/documents/fertilizing_urban_trees.pdf
Pokorny, J., O'Brien, J., Hauer, R., Johnson, G., Albers, J., Bedker, P ., and Mielke, M. (2003). Urban Tree Risk
Management: A Community Guide to Program Design and Implementation. USDA Forest Service
Northeastern Area State and Private Forestry, St. Paul.
https://www.fs.usda.gov/nrs/pubs/na/NA-TP-03-03.pdf
Toronto and Region Conservation Authority (TRCA). (2006). Operational Procedures for Managing Hazard
Trees. Tree Canada.
https://treecanada.ca/wp-content/uploads/2017/11/OPERATIONAL-PROCEDURES-FOR-MANAGING-
HAZARD-TREES.pdf
Trees Are Good. (n.d.a). Managing Hazards and Risks [webpage]. International Society of Arboriculture.
https://www.treesaregood.org/treeowner/treehazards
Gulick, J. (2014). Planning for Urban Forest Resilience: Managing Invasive Pests and Diseases. American
Planning Association.
https://www.treesintrouble.com/wp-content/uploads/2015/08/PAS-Memo-March-April-2014_cr.pdf
International Society of Arboriculture (ISA). (2021c). Insect and Disease Problems – Consumer Brochure.
Trees Are Good.
https://www.treesaregood.org/Portals/0/TreesAreGood_Insect%20Disease%20Problems_0721.pdf
Ontario Ministry of Natural Resources, Ontario Commercial Arborist Association, City of Toronto. (2012).
What you need to know about the management of the Emerald Ash Borer (EAB): Guidelines for hiring tree
care services to manage urban trees. Eastern Ontario Model Forest.
https://www.eomf.on.ca/media/k2/attachments/eab_management.pdf
City of Guelph. (2019). Tree Technical Manual.
https://guelph.ca/wp-content/uploads/Tree-Technical-Manual.pdf
Fertilizing
Hazard Trees
Invasive Species
Maintenance Guides
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Government of Ontario. (n.d.). Maintaining Healthy Urban Trees. Landowner Resource Centre.
http://www.lrconline.com/Extension_Notes_English/pdf/urbntrs.pdf
Green Municipal Fund. (n.d.). Factsheet: Tree maintenance – How to care for trees after planting.
https://greenmunicipalfund.ca/resources/factsheet-tree-maintenance
International Society of Arboriculture (ISA). (2021a). Mature Tree Care – Consumer Brochure. Trees Are
Good.
https://www.treesaregood.org/Portals/0/TreesAreGood_Mature%20Tree%20Care_0721.pdf
Johnson, J., Johnson, G., McDonough, M., Burban, L. and Monear, J. (2008). Tree Owner's Manual for the
Northeastern and Midwestern United States. United States Department of Agriculture Forest Service.
https://www.fs.usda.gov/Internet/FSE_DOCUMENTS/stelprdb5368392.pdf
LEAF - Local Enhancement & Appreciation of Forests. (n.d.). Tree Care – Ongoing Care.
https://www.yourleaf.org/tree-care
Steil, A. (2022). Care of Newly-Planted Trees. Iowa State University.
https://yardandgarden.extension.iastate.edu/how-to/care-newly-planted-trees
Trees Are Good. (n.d.b). Why hire an arborist? [webpage]. International Society of Arboriculture.
https://www.treesaregood.org/treeowner/whyhireanarborist
Bellis, E. (2023). Recommendations to improve the health of Vancouver’s street trees surrounded by
hardscape. University of British Columbia.
https://sustain.ubc.ca/sites/default/�les/2023-058_RecommendationsStreetTreehealth_Bellis.pdf
City of Edmonton. (n.d.). Tree Preservation Guidelines.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PDF/
Tree_Preservation_Guidelines.pdf
City of Saskatoon Parks Branch. (2019). Saskatoon’s Urban Forest – Brochure.
https://www.saskatoon.ca/sites/default/�les/documents/urban_forestry_booklet.pdf
Dixon, C. (2024). Why Maintenance Matters: Stewarding Our Urban Forests. Tree Canada.
https://treecanada.ca/article/why-maintenance-matters-stewarding-our-urban-forests/
Gurney, S. and Ward, G. (n.d.). Natural Areas: Tree Hazard Management Strategy. City of Surrey.
https://www.surrey.ca/sites/default/�les/media/documents/TreeHazardStrategy.pdf
International Society of Arboriculture. (n.d.). Tree Ownership Information. Trees Are Good.
https://www.treesaregood.org/treeowner
Magditsch, D. (2012). Strategic Mulching of Trees in Forested Urban Parkland for Rooting Medium
Amendment [thesis]. Toronto Metropolitan University.
https://doi.org/10.32920/ryerson.14662743.v1
Pleninger, A. & Luley, C. (2012). The ABCs Field Guide to Young and Small Tree Pruning (1 ed.). Urban
Other Sources
st
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Forestry LLC. ISBN 9780976712923
Qu, B., Liu, Y., Sun, X., Li, S., Wang, X., et al. (2019). Effect of various mulches on soil physico— Chemical
properties and tree growth (Sophora japonica) in urban tree pits. PLOS ONE 14(2), e0210777.
https://doi.org/10.1371/journal.pone.0210777
Sun, X., Zhao, J., Wang, G. et al. (2023). Fine root extension in urban forest soil depends on organic
mulching. Agroforestry Systems 97, 235–247.
https://doi.org/10.1007/s10457-022-00801-3
Sweeney, J., Rassati, D., Meurisse, N., Hurley, B., Duan, J., Stauffer C. and Battisti, A. (2019). Special issue
on invasive pests of forests and urban trees: pathways, early detection, and management. Journal of
Pest Science, 92, 1–2.
https://doi.org/10.1007/s10340-018-01073-6
Tree Canada. (2018). Canadian Urban Forest Strategy (2019-2024).
https://treecanada.ca/wp-content/uploads/2018/10/TC-CUFS-2019-2024-Eng-1.pdf
Wisconsin Council on Forestry. (2009). Wisconsin’s Urban Forestry Best Management Practices for
Preventing the Introduction and Spread of Invasive Species.
https://councilonforestry.wi.gov/Documents/InvasiveSpecies/UF-BMP-Manual.pdf
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Hydro Lines and Corridors
Hydro lines and hydro corridors are energy infrastructures within urban areas and
Canadian urban forests. The location of hydro lines in Canada, above or below
ground, depends on when the urban areas were developed and built. Aboveground
hydro lines are found along city streets, sidewalks, and laneways in older
subdivisions or neighbourhoods in Canada. One of the most common �xtures on
Canadian streets is utility poles with hydro lines attached. Due to maintenance
standards, this energy infrastructure interferes with trees and constrains tree canopy
development, growth, and height (Appleton, 2006). In newer developments and
subdivisions, hydro lines are buried underground, where they have the potential to
restrict root growth and tree planting. In both cases, urban trees share limited
growing space with these utility �xtures, restricting how many trees and which
species can be planted under hydro wires. The design, planting, and maintenance of
trees within or near hydro wires always requires careful considerations of factors
such as available growing space, proximity to hydro wires, future risk of tree
interference with electrical infrastructure, compliance with local regulations or utility
guidelines, tree species selection, tree height and canopy spread at maturity, growth
habit, long-term maintenance requirements, tree trimming or pruning, accessibility for
maintenance crews, the potential for breakage during storms or high winds, visual
aesthetics, and community impact (Dupras et al., 2016; Appleton, 2006; Bloniarz,
1992; Browning & Wiant, 1997).
Hydro Lines
In the planning and design phase, landscape and tree planting plans in areas under or
Highlights
Hydro lines and hydro corridors
How they interact with urban trees.
Regulations
Tree selection, planting, and routine maintenance.
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close to hydro lines should consider tree height and canopy spread at maturity. It is
crucial to carefully plan tree planting based on tree size at maturity, growing
conditions (soil, nutrients), and distance from hydro lines to determine which species
are suitable to plant under hydro wires. Choosing the right tree species can reduce
pruning and maintenance intensity, leading to healthier, more aesthetically pleasing
trees along streets and under hydro lines. More importantly, the right tree species can
signi�cantly reduce the risk of power outages and accidental �res, resulting in
economic savings (Bloniarz, 1992). Power companies and many Canadian
municipalities (see Canadian Online Resources section) have a list of recommended
tree species that are suitable to plant adjacent to power lines (Appleton, 2006).
It is standard practice for utility companies across Canada to perform routine tree
maintenance along power lines and corridors (Parent et al., 2019; Perrette et al.,
2021). Utility companies also maintain street trees and park trees that are within
range of hydro lines. To ensure safety and hydro wire clearance,trees under or near
hydro lines are managed on an individual basis. Maintenance around power lines can
only be done by trained and certi�ed professional arborists. Canadian utility
companies often develop and provide various tree resources, including tree pruning
maintenance standards, hazards to watch for, and a list of certi�ed arborists in the
area on their websites (see Canadian Online Resources section). Trees along power
lines are usually pruned at 5-6 years intervals, but some can be as frequent as 3
years (Perrette, Delagrange, & Messier, 2020; Browning & Wiant, 1997; Millet &
Bouchard, 2003; Millet, 2012; Lecigne et al., 2018). A good understanding of tree
species biology can help improve pruning practices, lessen its impact on trees, and
reduce pruning costs (Perrette, Delagrange, & Messier, 2020; Millet, 2012).
Additionally, consistently assessing the overall health of a tree can help determine
the frequency of pruning and its suitability for extensive pruning (Perrette et al.,
2021). This, in turn, can inform maintenance planning to optimize the allocation of
time, human resources, and funding.
Hydro Corridors
In addition to hydro lines, urban areas are often intersected by transmission
corridors, commonly called hydro corridors. Hydro corridors are long and narrow
linear spaces, covered by shrubs and grasses, used by hydro companies for high-
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voltage hydro transmission, which requires very tall transmission towers. These
areas have strict regulations regarding the type of vegetation growing under
transmission lines due to safety concerns. Trees are prohibited under and within a
certain distance from the transmission lines because their height can pose safety
risks. Electricity can easily arc out of transmission lines and jump into the taller tree
branches. As a result, vegetation directly under hydro lines in hydro corridors should
be low. Different hydro companies and municipalities may have different rules, but
most guidelines indicate that woody vegetation over 6 meters is not permitted in
these areas (Hydro Ottawa, 2025).
The hydro corridors themselves can support native plants and provide habitats for
wildlife, insects, and birds. They often act as ecological corridors and serve as a
landscape linkage between urban centers, rural communities, and beyond (Hydro
Ottawa, 2010). There has also been a repurposing of how land under hydro corridors
is used in urban areas, from providing recreational spaces and supporting urban
gardening to strategically enhancing urban biodiversity and improving ecological
connectivity in Canadian cities. For example, the Meadoway 16-kilometre-long hydro
corridor in Toronto has been gradually transformed into a native meadow and will
become a linear urban park when �nished (TRCA, 2022). Hydro corridor lands have
been incorporated into the urban green system to support recreation in Winnipeg
(Sage Creek, 2023) and urban biodiversity restoration in Calgary (City of Calgary,
n.d.). Similar efforts towards restoring hydro corridors and converting them to native
plant communities and wildlife habitats are happening across many Canadian cities,
such as Montreal, Guelph, and Ottawa, to name a few (Hydro Quebec, 2024; Milkweed
Journal, 2016; OSC, 2024).
Resources
City of Calgary. (n.d.). Habitat restoration.
https://www.calgary.ca/parks/wildlife/habitat-restoration.html
Electrical Safety Association. (n.d.). Guidelines for pruning trees around powerlines.
https://esasafe.com/assets/�les/esasafe/pdf/Electrical_Safety_Products/Guidelines/
Tree%20Pruning%20Guideline%20Tagged.pdf
Canadian
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ENMAX Calgary. (n.d.). Trees and power lines.
https://www.enmax.com/outages-and-safety/safety-guidelines/trees-and-power-lines
Hydro Ottawa. (n.d.). Tree Trimming.
https://hydroottawa.com/en/outages-safety/community-safety/tree-trimming
Hydro Ottawa. (2010). Tree Planting Advice.
https://static.hydroottawa.com/documents/publications/safety/tree_planting_advice-EN.pdf
Hydro Ottawa. (2025). Clearances – Trees & Surface Finishing.
https://hydroottawa.com/en/accounts-services/accounts/contractors-developers/clearances
Hydro Québec. (n.d.). Trees and Power Lines – Choosing the right place for a tree.
https://poweroutages.hydroquebec.com/poweroutages/understand-and-prevent/vegetation.html
Hydro Québec. (2022). Hydro-Québec’s Biodiversity Strategy 2022-2026.
https://www.hydroquebec.com/themes/developpement-durable/pdf/hydro-quebec-
s_biodiversity_strategy-2022-2026.pdf
Maritime Electric. (n.d.). Tree Trimming.
https://www.maritimeelectric.com/safety/tree-trimming/tree-trimming/
Maritime Electric. (n.d.). Tree Planting Guide.
https://www.maritimeelectric.com/safety/tree-trimming/tree-planting-guide/
Nova Scotia Power. (n.d.). Vegetation Management.
https://www.nspower.ca/about-us/reliability/tree-management
New Brunswick Power. (n.d.). Tree Maintenance – Your Trees.
https://www.nbpower.com/en/products-services/tree-maintenance/your-trees/
Newfoundland Power. (n.d.). Tree Trimming.
https://www.newfoundlandpower.com/Safety/Electrical-Safety/Tree-Trimming
Toronto and Region Conservation Authority (TRCA). (2022). The Meadoway: A Blueprint for Naturalizing
Infrastructure Corridors. The Meadoway.
https://themeadoway.ca/app/uploads/2022/10/Meadoway-Manual-2022-FA-Web_v2.pdf
Bloniarz, D. (1992). (rep.). Street Trees, Overhead Utility Distribution, and Physical Infrastructure: Design
Implications, Maintenance Costs and Proposed Alternatives. Northeast Center for Urban & Community
Forestry, USDA Forest Service.
https://www.umass.edu/urbantree/mla.pdf
Appleton, B. L. (2006). Designing and implementing utility line arboreta. Arboriculture and Urban Forestry,
Non-Canadian
Further Reading
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32(2), 80-85.
doi.org/10.48044/jauf.2006.011
Bloniarz, D. (1992). (rep.). Street Trees, Overhead Utility Distribution, and Physical Infrastructure: Design
Implications, Maintenance Costs and Proposed Alternatives. Northeast Center for Urban & Community
Forestry, USDA Forest Service.
https://www.umass.edu/urbantree/mla.pdf
Browning, D., & Wiant, H., (1997). The Economic Impacts of Deferring Electric Utility Tree Maintenance.
Arboriculture & Urban Forestry, 23(3), 106-112.
doi.org/10.48044/jauf.1997.017
Dupras, J., Patry, C., Tittler, R., Gonzalez, A., Alam, M., & Messier, C. (2016). Management of vegetation
under electric distribution lines will affect the supply of multiple ecosystem services. Land Use Policy, 51,
66-75.
doi:10.1016/j.landusepol.2015.11.005
Hydro Quebec. (2024). Upgrading the power transmission system between Aqueduc and Saraguay
substations – Green Corridor Partnership.
https://www.hydroquebec.com/aqueduc-saraguay/en/
Kotsopoulos, S., Turnbull, K., Cormack, C., Cartwright, L. A., Hayes, S. M., Ford, B., Shachak, R. and
Watkinson, A. (2024). The Meadoway: native meadow creation in underutilized transmission line
corridors. Botany, 102(10), 421-427.
https://doi.org/10.1139/cjb-2023-0157.
Lecigne, B., Delagrange, S., & Messier, C. (2018). Exploring trees in three dimensions: VoxR, a novel voxel-
based R package dedicated to analysing the complex arrangement of tree crowns, Annals of Botany,
121(4) 589–601,
https://doi.org/10.1093/aob/mcx095
Milkweed Journal. (2016). Native plants turning hydro corridor into wildlife habitat.
https://milkweedjournal.com/2016/05/native-plants-turning-hydro-corridor-into-wildlife-habitat/
Millet, J. (2012). L’architecture des arbres des régions tempérées: son histoire, ses concepts, ses usages.
https://www.researchgate.net/
publication/281590469_L'architecture_des_arbres_des_regions_temperees_son_histoire_ses_concepts
_ses_usages
Millet, J., & Bouchard., A. (2003). Architecture of silver maple and its response to pruning near the power
distribution network. Canadian Journal of Forest Research,33(4), 726-739.
doi.org/10.1139/x02-206
Most, W., & Weissman, S. (2012). Trees and Power Lines: Minimizing Con�icts between Electric Power
Infrastructure and the Urban Forest.
https://escholarship.org/uc/item/8kg6t2jx
Ottawa Stewardship Council. (2024). Hydro Corridors: Cooperation in the Kanata North Hydro Corridor.
https://www.ottawastewardship.org/category/hydro-corridors/
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Parent, J. R., Meyer, T. H., Volin, J. C., Fahey, R. T., & Witharana, C. (2019). An analysis of enhanced tree
trimming effectiveness on reducing power outages. Journal of Environmental Management, 241, 397-406.
doi:10.1016/j.jenvman.2019.04.027
Perrette, G., Delagrange, S., & Messier, C. (2020). Optimizing Reduction Pruning of Trees Under Electrical
Lines: The In�uence of Intensity and Season of Pruning on Epicormic Branch Growth and Wound
Compartmentalization. Arboriculture and Urban Forestry, 46(6), 432-449.
doi:10.48044/jauf.2020.031
Perrette, G., Delagrange, S., Ramirez, J. A., & Messier, C. (2021). Optimizing reduction pruning under
electrical lines: The in�uence of tree vitality before pruning on traumatic responses. Urban Forestry and
Urban Greening, 63.
doi:10.1016/j.ufug.2021.127139
Powell, A. S., & Lindquist, E. S. (2011). Effects of power-line maintenance on forest structure in a
fragmented Urban Forest, Raleigh, NC. Southeastern Naturalist, 10(1), 25-38.
doi:10.1656/058.010.0103
Sage Creek. (2023). The hydro corridor – Sage Creek.
https://sagecreek.qualicocommunities.com/blog/details/the-hydro-corridor/
Santos, N. A., de Freitas, L. C., Fiedler, N. C., & da Silva Leite, E. (2023). Ergonomic Analysis of Pruning
Trees in Con�ict with Power Lines. Floresta, 53(4), 433-443.
doi:10.5380/RF.V53I4.79831
Speak, A. F., & Salbitano, F. (2023). The impact of pruning and mortality on urban tree canopy volume.
Urban Forestry and Urban Greening, 79.
doi:10.1016/j.ufug.2022.127810
Suttle, R., Kane, B., & Bloniarz, D. (2022). Comparing the Structure, Function, Value, and Risk of Managed
and Unmanaged Trees along Rights-of-Way and Streets in Massachusetts. Forests, 13(10).
doi:10.3390/f13101602
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Tree Selection and Planting
Appropriate tree species selection should be based on environmental, ecological,
social, infrastructural, and tree maintenance considerations. For example, tree
selection should ensure an urban forest that is resilient and that can endure
challenging urban environmental conditions, including air and soil pollution, soil
compaction, drought, and road salt. Tree selection and planting are also site-speci�c
and should consider soil properties, moisture availability, wind, frost, and light
exposure (Nowak et al., 2010). Species-speci�c characteristics such as tree growth
rate, shade tolerance, and visual appeal also play a critical role in species selection.
In addition, considering maintenance needs is critical as this can determine long-
term sustainability of urban forests and reduce management costs (Almas &
Conway, 2016; LSRCA, 2018; Nowak, 2000; Conway & Vander Vecht, 2015).
Highlights
Tree species selection must be site-specific and future-focused
Effective selection considers environmental, ecological, and infrastructural factors,
as well as long-term resilience to urban stressors and climate change.
Climate change requires adaptive species planning
Tree selection should anticipate shifting temperature zones and species suitability,
using climate models and phased testing to guide planting decisions.
Diversity builds urban forest resilience
Avoiding over-reliance on a few species helps reduce vulnerability to pests,
diseases, and environmental change, while supporting urban biodiversity.
Proper planning minimizes tree-infrastructure conflicts
Trees must be selected and visualized at mature size to prevent future clashes with
sidewalks, buildings, or utilities, reducing maintenance costs and risks.
Nursery stock quality and planting methods are critical
Tree health at planting, correct handling of root systems, and ongoing care
determine whether trees thrive to maturity and deliver full ecological bene�ts.
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Tree Selection and Sites
Tree species selection should be based on site conditions, location, species
compatibility with local climate and species hardiness zone, tree size, form, and
aesthetic/public appeal. Other factors to consider are tree growth rate, environmental
suitability (soil characteristics, pH, moisture regimes, salt tolerance), and the tree’s
function within the space (shade provision, aesthetic, etc.). Well-considered criteria
for tree species selection can result in secondary bene�ts for the larger urban
forestry program. Some of these bene�ts include reducing long-term maintenance
costs, building an urban forest resilient to climate change, providing manageable
urban forest solutions to neighbourhoods and communities, and maintaining a
diversity of tree species that bene�t wildlife in cities and towns (Almas & Conway,
2016).
In the design and planning stage of tree selection, trees should be visualized at full
functional size. This helps to minimize later con�icts between trees and structures
and reduces maintenance needs that may arise from unexpected issues. Selecting a
tree that is well-suited to the soil conditions, light availability, pedestrian tra�c,
drainage, space, and microclimate of the speci�c site is essential to the tree’s long-
term survival and to public safety (Vibrant Cities Lab, n.d.).
To make the decision process easier, Canadian municipalities often list species that
can thrive in their speci�c urban context based on the tree selection considerations
and their experience (see City of Markham, 2009; City of Kelowna, 2020; City of
Toronto, 2021, 2024; Metro Vancouver, 2017; Ville de Quebec, n.d.).
Climate Change
When selecting tree species, their long-term climatic suitability is increasingly
important for successful planting decisions. As climate change brings warmer
weather to many Canadian cities, individual species’ suitability is expected to change
over time (Khan & Conway, 2020). The composition of urban forests needs to adapt
and shift in anticipation of this trend. Suitable climate conditions for many tree
species are shifting northward much faster than trees can naturally migrate (Metro
Vancouver, 2017). As a result, tree species selection must be based on forethought
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and consideration of changing climate regimes, rising temperatures, and levels of
tolerance that individual tree species have for rising temperatures and shifting
conditions.
To determine a species’ suitability in the context of climate change, a combination of
historical range, current suitable habitat, and climate projection models can be used
as a basis for analysis (LSRCA, 2018). This process helps determine if a species is
retreating northward, continuing to persist, or becoming a new suitable possibility.
Trees and other species that are becoming increasingly unsuited to their location
may experience stunted growth and shorter lifespans. Species that persist in urban
settings tend to have a wider ecological amplitude and climatic range and are likely
to continue to thrive in the future (Das, Ossola & Beaumont, 2024; Liang & Huang,
2023).
For species that may become more suitable as climate change progresses, testing
their survivability in the new environment before widespread implementation by
planting limited amounts can prevent large-scale tree mortality in the future (LSRCA,
2018). These assessments should be updated as more data for different species and
new climatic models become available. Flexibility in modifying planting programs
can help mitigate the risk of implementing new species.
Since urban forest planning is a long-term vision and young trees take years to grow,
active engagement with nurseries can ensure that su�cient planting stock of
speci�c species is available. Coordination with nurseries can also lead to the sharing
of knowledge, which can be a hugely bene�cial source of information in
implementing new planting programs or testing of new tree species (Khan & Conway,
2020; LSRCA, 2018).
Species Diversity and Composition
The diversity of tree species is critical in building and maintaining a resilient urban
forest. Having a large variety of tree species allows an urban forest to better absorb
shocks brought by pests, diseases, and climate change. For instance, the spread of
Emerald Ash Borer put around 20% of Montreal’s urban forest at risk, and thousands
of trees were cut down between 1999-2020 (Canadian Institute for Climate Choices,
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2021). Many of the trees that were impacted were mature with wide-spreading
canopies, which provided various bene�ts like climate regulation, air quality, and
stormwater management bene�ts that a newly planted sapling could not
immediately replace. Ash trees across North American cities were impacted at
similar or worse rates. This highlights the importance of supporting tree diversity to
strengthen urban forest resilience to a changing climate and environmental threats.
In addition to considering urban forest diversity, tree species that are dioecious (male
and female trees), tree species sex and overall tree diversity should be considered
when selecting trees to plant. Historically, male trees have been preferably planted in
urban settings as they are considered less “messy” and do not produce fruits or
seeds (Nowak & Ogren, 2021). While female plants produce fruits and nuts and
provide food for birds and other urban wildlife, they require higher maintenance and
upkeep. As a result, they have not been favoured for planting to avoid fruit cleanup in
high human tra�c areas. Studies have shown how the planting of mostly male trees
across cities in North America has led to increased urban pollen concentrations,
which has been correlated with increased seasonal allergies. Favouring male trees
has a long-term impact on urban forest and tree species composition, as well as
resilience against pests and overall city biodiversity. It also contributes to perceived
tree disservices as overproduction of pollen can impact human health (Katz,
Robinson, Ellis & Nowak, 2024).
Furthermore, urban trees planted along streets, parks, in residential and institutional
areas often include many cultivars selected for their speci�c traits, such as growth
rate, canopy shape, leaf and �ower colour, the absence of fruit, visual appeal, or other
features. The predictability of their growth and other characteristics, and how these
trees eventually grow, make these cultivars desirable for some urban environments
and landscaping. There are hundreds of cultivars, of which some have been planted
more than others. However, cultivars are clones that share identical genetic material,
reduce genetic diversity, and increase vulnerability to pests, diseases, and
environmental stressors. Heavily relying on cultivars can lead to portions of the urban
forest becoming monocultures, but also having monocultures across cities (Avolio,
2023; Sacre, 2020; Lohr, Kendal & Dobbs, 2016).
Tree Planting
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Tree planting material should be inspected for damage and disease before being
purchased from nurseries to ensure successful tree establishment and growth. Some
common issues of tree planting materials are damage to the trunk, broken branches,
or injuries to the root system (International Society of Arboriculture, 2021). The three
common types of nursery trees are ball and burlap, container, and bare root stock.
Each has its advantages and limitations when planting and should be selected based
on the needs of the site or project (International Society of Arboriculture, 2021;
Natural Resources Canada, 2023). The Arbor Day Foundation has a useful guide on
how to plant each type of nursery tree. Planting under speci�c circumstances may
have different requirements, such as when planting under power lines or for hard-
surface planting in intensely urbanized areas.
Depending on how trees are packaged and sold, their planting methods differ. Young
trees often come in containers, as ball and burlap, or as bare root trees. One of the
main concerns for trees that come in containers is root girdling. Root balls should be
loosened on the bottom and sides to ensure no roots grow to choke the plant
(International Society of Arboriculture, 2021a; Tree Canada, 2023). For trees that
come in ball and burlap, it is important to cut away the burlap and wire basket, or the
packaging will slowly strangle the tree as it grows (Tree Canada, 2023). For bare root
stock, the most important thing is to ensure that the root does not dry out prior to
and during the planting process (Virginia Department of Forestry, n.d.). The ultimate
goal of urban tree planting is for the trees to reach maturity and provide maximum
bene�ts, such as carbon sequestration, shade, and biodiversity. Therefore,
monitoring and maintaining young trees so that they continue growing and thriving is
an imperative part of urban forest management.
Resources
Corrigan, S. (2024, August 6). The Ultimate Guide on How to Plant Urban Trees. Citygreen.
https://citygreen.com/ultimate-guide-on-how-to-plant-trees-in-urban-areas/
Credit Valley Conservation. (2020a). How-to: Plant a potted tree or shrub.
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McGrath, D., Munroe, R. & Henry, J. (2019). Ontario Landscape Tree Planting Guide. Landscape Ontario.
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(2023). Tree Improvement in Canada – past, present and future, 2023 and beyond. The Forestry
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canad.pdf
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https://www.ville.quebec.qc.ca/citoyens/environnement/arbres-plantes/essences-arbres/index.aspx
City of Regina. (n.d.). Trees in your yard.
https://www.regina.ca/home-property/tree-yard/trees/
City of Saskatoon Parks Branch. (n.d.). (rep.). Saskatoon’s Urban Forest.
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Bassuk, N., Curtis, D. F., Marranca, B. Z., and Neal, B. (2009). Recommended Urban Trees: Site Assessment
and Tree Selection for Stress Tolerance. Cornell University Department of Horticulture, Ithaca.
http://www.hort.cornell.edu/uhi/outreach/recurbtree/pdfs/~recurbtrees.pdf
Eisenman, T.S., Roman, L. A., Östberg, J., Campbell, L. K., and Svendsen, E. (2024). Beyond the Golden
Shovel: recommendations for a successful urban tree planting initiative. Journal of the American Planning
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Virginia Department of Forestry. (n.d.). Planting trees.
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trees/
Worsley, W. (2022). Urban Tree Manual: The Right Tree in the Right Place for a Resilient Future. UK Forest
Research.
https://cdn.forestresearch.gov.uk/2022/02/7111_fc_urban_tree_manual_v15.pdf
Quebec
Saskatchewan
Non-Canadian
Further Reading
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Almas, A. D. & Conway, T. M. (2016). The role of native species in urban forest planning and practice: A
case study of Carolinian Canada. Urban Forestry & Urban Greening, 17, 54-62.
https://doi.org/10.1016/j.ufug.2016.01.015
Arbor Day Foundation. (n.d.). Tree Planting & Care.
https://www.arborday.org/trees/index-planting.cfm
Avolio, M. L. 2023. The unexplored effects of arti�cial selection on urban tree populations. American
Journal of Botany 110(7), e16187.
https://doi.org/10.1002/ajb2.16187
Canadian Institute for Climate Choices. (2021). Growing Forests in a City.
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Carol-Aristizabal, M., Dupras, J., Messier, C., & Sousa-Silva, R. (2024). Which Tree Species Best Withstand
Urban Stressors? Ask the Experts. Arboriculture & Urban Forestry, 50(1), 57.
https://doi.org/10.48044/jauf.2023.026
City of Guelph. (n.d.). Healthy Landscapes – Plant List Native and Drought-Tolerant Plants Guelph.
https://guelph.ca/wp-content/uploads/droughtTolerant-NativePlants.pdf.
City of Toronto. (2012). Drought Tolerant Landscaping - A Resource for Development.
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landscaping.pdf.
City of Vancouver. (2017). Urban Forest Climate Adaptation Framework for Metro Vancouver: Tree Species
Selection, Planting and Management.
https://metrovancouver.org/services/regional-planning/Documents/urban-forest-climate-adaptation-
framework-tree-species-selection.pdf
Conway, T. M. & Vander Vecht, J. (2015). Growing a diverse urban forest: Species selection decisions by
practitioners planting and supplying trees. Landscape and Urban Planning, 138, 1-10.
doi.org/10.1016/j.landurbplan.2015.01.007
Das, S., Ossola, A., & Beaumont, L. J. (2024). Records of urban occurrences expand estimates of the
climate niches in tree species. Global Ecology and Biogeography, 33, e13809.
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Eisenman, T. S., Roman, L. A., Östberg, J., Campbell, L. K., & Svendsen, E. (2024). Beyond the Golden
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Nowak, D. J., Stein, S. M., Randler, P . B., Green�eld, E. J., Comas, S. J., Carr, M. A., and Alig, R. J. (2010).
Sustaining America’s urban trees and forests: a Forests on the Edge report. General Technical Report
NRS-62. Newtown Square, PA: U.S. Department of Agriculture, Forest Service, Northern Research Station.
27 p.
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Sacre, K. (2020). Diversity in urban tree populations. ARB Magazine, 190, 82-84. The Arboricultural
Association.
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Samaha, J. A. (2019). Finding urban trees for a changing world.
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in drought tolerance in Acer. Urban Forestry & Urban Greening, 14(4), 858-865.
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Sousa-Silva, R., Du�os, M., Ordóñez Barona, C. and Paquette, A. (2023). Keys to better planning and
integrating urban tree planting initiatives. Landscape & Urban Planning, 231, 104649.
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Vibrant Cities Lab. (n.d.). Tree Planting: There’s More to Planting a Tree Than Digging a Hole.
https://vibrantcitieslab.com/toolkit/tree-planting/
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Hard Surface Planting
With increased urbanization, environmental and climate changes, healthy, long-living
urban trees are critical for providing ecological services such as air quality
improvement, stormwater management, and energy conservation. However, these
bene�ts cannot be fully realized when tree growth is limited by inadequate space and
soil (Mullaney, Lucke, & Trueman, 2015a). One of the most persistent challenges in
establishing and maintaining a healthy, resilient, and functional urban forest is the
ongoing battle between tree roots, gray infrastructure, and various hard surface
pavements. Due to the lack of ample growing space, trees are often planted in
restricted soil spaces surrounded by pavement, asphalt, or concrete. As a result, such
trees often have limited soil volume to support their growth, inadequate access to
nutrients, and a lack of oxygen and water to support their basic physiological
functions.
Con�ict with urban structures, limited growing space, and hard surface covering the
root system can lead to root damage and root girdling. This often results in
pavement lifting as roots of large trees try to access nutrients and water (Watson,
Highlights
Urban trees need space
Trees offer key ecological bene�ts but struggle in compact, paved urban areas.
Roots vs. pavement
Limited soil and hard surfaces cause root damage and infrastructure issues.
Pavement limits benefits
Hard surfaces reduce trees’ cooling and ecological functions.
Design matters
Smart planning, soil solutions, and permeable surfaces support healthier trees.
Ongoing care is essential
Long-term maintenance and site-speci�c solutions help trees thrive in cities.
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Hewitt, Custic & Lo, 2014; Mullaney et al., 2015a). Pavement lifting creates safety
hazards for street users, causes concern for property owners and residents, and
signi�cantly impacts the aesthetic value of public spaces (Watson et al., 2014).
Recent studies reveal that surface paving also signi�cantly affects the ability of trees
to provide ecological services. Surrounding hard surfaces in�uences a tree's cooling
effect more than species selection, highlighting the strong impact and restrictions
pavements impose on urban trees' health and ecological functions. This underscores
the strong impact and restrictions that hard surfaces impose on the health of urban
trees and their ecological functions (Konarska et al., 2023).
Planting trees on hard surfaces and as part of new developments can be very
expensive, and without proper forethought, can bring few bene�ts and prove to be a
liability. When tree planting is carefully designed, planned, and implemented, hard-
surface tree issues can be avoided or minimized. Healthy tree growth and survival
can be ensured by selecting appropriate tree species for the growing space available,
using an adequate soil medium to encourage tree root growth, constructing
continuous channels connecting individual planting pits, implementing pervious
paving around trees, and providing su�cient irrigation.
Land use and site planning decisions, combined with poor tree selection and planting
practices, can generate problems down the road. However, past mistakes are
learning opportunities for improving future practices. For example, studies on
permeable paving with deep granular substrates have shown promising results in
mitigating damage to the pavement and tree roots by allowing them to grow at
greater depth. The permeable pavement supplies the soil with su�cient oxygen,
nutrients, and moisture to allow for woody growth at greater depths without
impacting the growth rate (Lucke & Beechman, 2019). Still, depending on the soil type
of the underlying base layer, the effectiveness of permeable pavement may vary
(Mullaney et al., 2015b).
There are solutions to improve the existing trees' growth conditions, allowing them to
extend their life and continue to provide ecological services. Management and
maintenance of trees to support root growth within hardscapes include techniques
such as de-pavement, soil aeration, soil improvements, building bridges over tree
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roots, and establishing root barriers. However, these interventions are often short-
term solutions as tree roots continue to grow, and trees might decline, necessitating
additional interventions. This also underscores the ongoing nature of tree
management and the need for continuous tree care (Watson et al., 2014). There are
less costly and site-speci�c techniques to improve the growing conditions. For
example, planting �ower beds and other vegetation around tree trunks or installing
covers or grates over planting pits can reduce foot tra�c around trees while also
helping to improve soil conditions.
In places where soil volume and quality are lacking, structural soil can be
implemented to ensure healthy root growth. These solutions are often used in highly
urban environments such as parking lots and downtown streets with lots of
pavement and tra�c. This planting solution protects the growing medium from
compaction and is formulated to provide the nutrients needed for tree growth.
Structural soils are expensive to implement, di�cult to maintain, and often provide
limited years of tree growth and performance shorter than a tree's typical lifespan.
However, it is usually the only viable solution in intensely urban areas with heavy
pedestrian tra�c.
Resources
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Mattson, B., Brusse, B., Krahn, A., Voogd, H., & Weerdenburg, R. (2017). (rep.). (A. Heuver & G. Lumis,
Eds.) Canadian Nursery Stock Standard (9th ed., pp. 1–56). Milton, Ontario: Canadian Nursery Landscape
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recommendations. Building and Environment, 225.
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Aryal, B., Steenberg J. W. N., and Duinker, P . N. (2022). The Effects of Residential Street Tree Spacing and
Crown Interactions on Crown Dimensions and Canopy Cover. Arboriculture & Urban Forestry, 47 (5),
183-195.
https://doi.org/10.48044/jauf.2021.017
Booth, D. B., Hartley, D., & Jackson, R. (2002). FOREST COVER, IMPERVIOUS-SURFACE AREA, AND THE
MITIGATION OF STORMWATER IMPACTS 1. Journal of the American Water Resources Association, 38(3),
835-845.
doi:10.1111/j.1752-1688.2002.tb01000.x
Citygreen. (n.d.). Colourful street trees continue to thrive in Rossland, Canada.
https://citygreen.com/case-studies/colourful-street-trees-continue-to-thrive-in-rossland-canada/
de la Mota Daniel, F. J., Day, S. D., Owen, J. S., Stewart, R. D., Steele, M. K., & Sridhar, V. (2018). Porous-
permeable pavements promote growth and establishment and modify root depth distribution of
Platanus × acerifolia (Aiton) Willd. in simulated urban tree pits. Urban Forestry and Urban Greening, 33,
27-36.
doi:10.1016/j.ufug.2018.05.003
Fini, A., Frangi, P ., Comin, S., Vigevani, I., Rettori, A. A., Brunetti, C., . . . Ferrini, F. (2022). Effects of
pavements on established urban trees: Growth, physiology, ecosystem services and disservices.
Landscape and Urban Planning, 226.
doi:10.1016/j.landurbplan.2022.104501
Gooden, B. (2020). Woonerf: A Living Street Concept for Shared City Spaces. Citygreen.
https://citygreen.com/woonerf-street-concept-for-shared-city-spaces/
Herold, N.D., & Koeln, G.T. (2003) Mapping Impervious Surfaces and Forest Canopy Using Classi�cation
and Regression Tree (CART) Analysis. ASPRS 2003 Annual Conference Proceedings, Anchorage, AK, May
2003, 1-7.
https://www.semanticscholar.org/paper/MAPPING-IMPERVIOUS-SURFACES-AND-FOREST-CANOPY-
USING-Herold-Koeln/052154ed604ca3760fa7cadabc087a1078e5a1b3
Konarska, J., Tarvainen, L., Bäcklin, O., Räntfors, M., & Uddling, J. (2023). Surface paving more important
than species in determining the physiology, growth and cooling effects of urban trees. Landscape and
Urban Planning, 240.
doi:10.1016/j.landurbplan.2023.104872
Lucke, T., & Beecham, S. (2019). An in�ltration approach to reducing pavement damage by street trees.
Science of the Total Environment, 671, 94-100.
doi:10.1016/j.scitotenv.2019.03.357
Further Reading
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Mullaney, J., Lucke, T., & Trueman, S. J. (2015). The effect of permeable pavements with an underlying
base layer on the growth and nutrient status of urban trees. Urban Forestry and Urban Greening, 14(1),
19-29.
doi:10.1016/j.ufug.2014.11.007
Mullaney, J., Lucke, T., & Trueman, S. J. (2015). A review of bene�ts and challenges in growing street
trees in paved urban environments. Landscape and Urban Planning, 134, 157-166.
doi:10.1016/j.landurbplan.2014.10.013
Qi, S., Cheng, Z., Hallett, R., Egendorf, S. P ., Reinmann, A. B., & Groffman, P . M. (2024). Feasibility of
constructed soils for tree planting – A pilot study in New York City. Urban Forestry and Urban Greening,
96.
doi:10.1016/j.ufug.2024.128342
Rötzer, T., Moser-Reischl, A., Rahman, M. A., Hartmann, C., Paeth, H., Pauleit, S., & Pretzsch, H. (2021).
Urban tree growth and ecosystem services under extreme drought. Agricultural and Forest Meteorology,
308-309.
doi:10.1016/j.agrformet.2021.108532
Watson, G. W., Hewitt, A. M., Custic, M., & Lo, M. (2014). The Management of Tree Root Systems in Urban
and Suburban Settings II: A Review of Strategies to Mitigate Human Impacts. Arboriculture & Urban
Forestry, 40(5), 249–271.
https://doi.org/10.48044/jauf.2014.025
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Urban Woodlot and Park Management
Natural areas such as woodlots, ravines and other open areas with self-sustained
vegetation make up a signi�cant component of the urban forest and land-use fabric.
They are composed of natural and semi-natural vegetation and managed for their
multiple ecological and social functions. Natural areas are a component of the urban
forest that are managed at a stand (i.e. group of trees) level. They are a vital part of
urban green infrastructure and enable linking urban areas and regional networks (City
of Ottawa, 2022; Ontario Nature, 2014). Due to their position near and within cities,
urban woodlots and natural parks also face multiple anthropogenic challenges
including pollution, contamination, and heavy recreational pressure which leads to
soil compaction and invasive species proliferation. They also tend to have multiple
groups of stakeholders who all carry different needs and management capacities
(Duinker et al., 2017; Miller et al., 2015).
As critical components of the urban forest, urban natural parks and woodlots hold
native diversity and provide wildlife habitat, absorb and �lter rainwater, and provide
outdoor recreation opportunities to city residents. Urban woodlot and park
management involves addressing several common issues, including ensuring safety
via regular tree and risk assessments, mitigating the impacts of recreation such as
Highlights
Woodlots
Self-sustaining urban green spaces that provide wildlife habitats, recreational
opportunities, and ecological bene�ts to urban communities.
Challenges
Pollution, contamination, recreational pressure, soil compaction and invasive
species proliferation.
Woodlot Management Plans
Outline explicit management and conservation strategies, must be goal-oriented
and based on site-speci�c information and data.
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soil compaction and garbage dumping, and monitoring and managing invasive
species to limit their spread and negative effects on plant and wildlife communities.
Efforts also focus on encouraging community use and stewardship by supporting
involvement in tree planting, restoration, and other stewardship efforts and activities,
as well as protecting and restoring ecosystems through ongoing monitoring and
initiatives to strengthen forest health. Because of their many functions, pressures,
and stakeholders, urban woodlots and parks should be managed with multiple goals
in mind. Their management should be based on detailed knowledge and data about
their structure, composition, and health, as well as the pressures of community use
(Duinker et al., 2017).
The management of natural parks and woodlots involves several steps. First,
determining clear management goals is essential to guide all subsequent actions.
These goals may include enhancing biodiversity, promoting recreation and ecological
values, ensuring safety, preserving culture, or storing carbon. Conducting a detailed
and informative inventory that includes the entire vegetation community composition
provides the base data necessary to develop an effective management and
conservation plan. Detailed data collection enables assessing the current state of the
woodlot or park, including its �ora, fauna, soil conditions, water resources, and any
existing human impacts or infrastructure (Tuckett, 2013; Puric-Mladenovic & Baird,
2017). Speci�c management and conservation strategies are developed by following
set objectives and are based on inventory data and identi�ed environmental and
anthropogenic pressures. Management strategies may include controlling invasive
plants, managing trails to reduce soil compaction, planting native species, or
engaging the community in restoration projects.
While similar problems and opportunities might be present across natural areas and
woodlands, individual urban woodlands or patches of natural areas often need to be
evaluated and managed according to their speci�c attributes, policy designation or
role in the local urban ecosystem. For example, some of them might have a higher
density of trails, deer browsing issues, and a decline in tree species. Some could
provide wildlife or species at risk habitat or require �re to manage native biodiversity,
such as High Park in Toronto (High Park Nature. 2019).
In terms of woodlot management activities, cities such as Guelph, Saskatoon,
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Winnipeg, and Halifax have focused management plans to manage the spread of
invasive buckthorn using chemical strategies such as herbicides and physical
methods such as tree cutting (ISC, n.d.). Other examples include municipalities that
have prioritized biodiversity and conservation in these natural remnant woodlots (City
of Toronto, 2019; City of Surrey, 2014; City of Edmonton, 2009). Some other Ontario
municipalities are partnering with academic institutions or allied organizations with
established vegetation monitoring and research to better understand and manage
these natural areas (Puric-Mladenovic, 2015; Puric-Mladenovic & Baird, 2017). Urban
woodlot management comes in many forms and must be based on detailed data,
guided by set goals at an individual woodlot level, and updated regularly based on
community needs and ecological health.
Resources
Alberta Agriculture and Rural Development. (2015). Woodlot Management Guide for Alberta – Bene�cial
Management Practices. Alberta Government.
https://open.alberta.ca/publications/9780773261150
City of Edmonton. (2009). City of Edmonton Natural Connections Biodiversity Action Plan.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PDF/
Edmonton_Biodiversity_Action_Plan_Final.PDF
City of Edmonton. (2014). City-Wide Natural Area Management Plan January 2014.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PDF/City-
Wide_Natural_Area_Management_Plan.pdf
City of Edmonton. (2023). Natural Stand Valuation Guidelines.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PDF/
DRAFT_NaturalStandValuationGuidelines.pdf
B.C. Ministry of Forests, Lands, Natural Resource Operations and Rural Development. (2019). Woodlot
Licence Management Plan Handbook. Government of British Columbia.
https://www2.gov.bc.ca/assets/gov/farming-natural-resources-and-industry/forestry/timber-
teballnures/woodlots/woodlot_mngmt_plan_handbook.pdf
Canadian Provincial
Alberta
British Colombia
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City of Surrey. (2014). City of Surrey Biodiversity Conservation Strategy.
https://www.surrey.ca/sites/default/�les/media/documents/Surrey_BCS_Report.pdf
Ward, D. (n.d.). City of Surrey – Natural Areas: Fauna Management Strategy. City of Surrey Parks,
Recreation and Culture Department.
https://www.surrey.ca/sites/default/�les/media/documents/fauna_management.pdf
Stanley Park Ecology Society. (2024). All Reports - Stanley Park Ecology Society (SPES).
https://stanleyparkecology.ca/ecology/reports-plans/all-reports/#best-practices
B.A. Blackwell & Associates Ltd. (2024). Stanley Park Hemlock Looper Impact and Wild�re Risk
Assessment. City of Vancouver Board of Parks and Recreation.
https://vancouver.ca/�les/cov/stanley-park-hemlock-looper-report.pdf
City of Halifax. (2008). All Chapters – Point Pleasant Park Comprehensive Plan.
https://www.halifax.ca/city-hall/boards-committees-commissions/i-r/point-pleasant-park-advisory-
committee/point-pleasant
Nova Scotia Department of Natural Resources and Renewables. (n.d.). Publications for woodlot owners
[website].
https://novascotia.ca/natr/woodlot/publications.asp
City of Niagara Falls. (n.d.). City of Niagara Falls Woodland Management Plan.
https://niagarafalls.ca/pdf/living/conservation/woodland-management/woodland-management-
plan.pdf
City of Ottawa. (2022). Signi�cant Woodlands Guidelines for Identi�cation, Evaluation, and Impact
Assessment.
https://documents.ottawa.ca/sites/default/�les/signi�cant_woodlands_en.pdf
City of Toronto. (2019). Wild, Connected and Diverse: A Biodiversity Strategy for Toronto.
https://www.toronto.ca/legdocs/mmis/2019/ie/bgrd/background�le-136906.pdf
City of Vaughan. (2024). Woodland Management Strategy.
https://www.vaughan.ca/sites/default/�les/2024-03/Woodland%20Management%20Strategy.pdf
Ministry of Natural Resources. (2012). A Guide to Stewardship Planning for Natural Areas. Government of
Ontario.
https://�les.elfsightcdn.com/02873a1a-8bd7-433b-8910-a4f80f9814b4/50a7d2cc-abb2-43af-
aefe-37a03a0ae412.pdf
Ontario Nature. (2014). Best Practices Guide to Natural Heritage Systems Planning. Natural Heritage
System.
Nova Scotia
Ontario
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https://ontarionature.org/wp-content/uploads/2017/10/nhs-guide-web-1.pdf
Ontario Woodlot Association. (n.d.-a). List of landowner guides [website].
https://www.ontariowoodlot.com/Landowner-Guides
Ontario Woodlot Association. (n.d.-b). A Landowner's Guide to Forest Management Basics.
https://�les.elfsightcdn.com/02873a1a-8bd7-433b-8910-a4f80f9814b4/4c535b6c-
ea56-48bd-8dec-74257c03245e/A-Landowners-Guide-To-Forest-Management-Basics-PRINT_2021.pdf
Postma, Madison.
Assessing The Introduction And Age Of The Acer Platanoides (Norway Maple) Invasion Within Wilket
Creek Ravine In Toronto, Ontario.
Puric-Mladenovic, D. and Baird, K. (2017). Natural areas monitoring in the City of Guelph: Emerald Ash
Borer impact on ash populations in natural areas. Faculty of Forestry, University of Toronto. 76 pp.
https://guelph.ca/wp-content/uploads/VSPGuelphReport_March3_2017.pdf
Rouge National Urban Park. (2024). Park management plan - Rouge National Urban Park. Parks Canada.
https://parks.canada.ca/pn-np/on/rouge/info/gestion-management/gestion-
management-2019#PartB
Canadian Model Forest Network. (n.d.). The Value of a Woodlot Management Plan. Government of
Canada.
https://www.nswooa.ca/uploads/5/9/6/9/59690537/the_value_of_a_woodlot_management_plan.pdf
Carpentier, S., Filotas, E., Handa, I. T., & Messier, C. (2017). Trade-offs between timber production, carbon
stocking and habitat quality when managing woodlots for multiple ecosystem services. Environmental
Conservation, 44(1), 14–23.
https://doi.org/10.1017/S0376892916000357
Duinker, P ., Lehvävirta, S., Busse Nielsen, A., and Toni, S. A. (2017). Chapter 34 – Urban woodlots and
their management. In Ferrini, F., Konijnendijk van den Bosch, C.C., & Fini, A. (Eds.). (2017). Routledge
Handbook of Urban Forestry (1st ed.). Routledge.
https://doi.org/10.4324/9781315627106
Invasive Species Council (ISC). (n.d.). Common Buckthorn (Rhamnus cathartica).
https://www.invasivespeciescentre.ca/invasive-species/meet-the-species/invasive-plants/buckthorn/
Miller, R.W. & Hauer, Richard & Werner, Les. (2015). Urban Forestry Planning and Managing Urban
Greenspaces (third ed.).
O’Brien, J. (2019). Impacts of Urban Forest Structure on Bat Populations in Kitchener, Ontario. Thesis
submitted to Faculty of Forestry, University of Toronto.
http://hdl.handle.net/1807/93330
Prevost, G. (2018). Victoria Park Woodlot Management Plan, Cambridge, ON. Thesis submitted to Faculty
of Forestry, University of Toronto.
Further Reading
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http://hdl.handle.net/1807/81362
Puric-Mladenovic, D. (2016). Vegetation Sampling Protocol (VSP). Forests and Settled Urban Landscapes.
http://forests-settled-urban-landscapes.org/VSP/
Rakika, R. (2020). Observed Differences in Woodland Characteristics of Fenced vs Unfenced Woodlands in
Mississauga, Ontario. Thesis submitted to Faculty of Forestry, University of Toronto.
http://hdl.handle.net/1807/99053
Ricketts-Moncur, G. (2020). Indicators of Natural Cover Quality: Management Applications in the City of
Toronto. Thesis submitted to Faculty of Forestry, University of Toronto.
http://hdl.handle.net/1807/99054
Shakespeare, M. (2020). The Current State of Natural Succession of Pine Plantations at Huron Natural
Area. Thesis submitted to Faculty of Forestry, University of Toronto.
http://hdl.handle.net/1807/99297
Tucket, A. S. (2013). A Plant Ecological Study and Management Plan for Mogale’s Gate Biodiversity Centre,
Gauteng. Thesis submitted to Faculty of Environmental Management, University Of South Africa.
https://core.ac.uk/download/43174396.pdf
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Emergency Preparedness
Emergency preparedness in urban forestry is crucial for protecting trees and
woodlands, as well as the communities that rely on them. As Canadian cities face
increasing threats from natural disasters, including wild�res, �ooding, extreme heat,
and the spread of pests and diseases, it is essential that urban forestry practices not
only focus on routine maintenance but also on preparedness and resilience.
The eastern Canadian ice storm of 1998, the Emerald Ash Borer impact and spread,
the Derecho storm (Ontario, May 21, 2022), Hurricane Juan (Nova Scotia, September
29, 2003), and the BC �res of 2003 starkly illustrated the need for municipalities to
integrate emergency preparedness and disaster management into urban forest
management plans. Emergency preparedness helps minimize damage, ensures
public safety, and allows for the planning and implementation of recovery after an
emergency (Public Safety Canada, 2022a).
Highlights
Increased Risk
Natural disasters such as �oods, extreme weather, high temperatures, �res, pests,
and diseases are increasing in Canada.
Disaster preparedness
Must be built into urban forest management plans to ensure resilience in the face
of disasters and emergencies.
Management and mitigation
Preventative methods like risk assessment and planning, mapping high-risk areas,
monitoring efforts, and proactive maintenance.
Canadian strategies and policies
Emphasize the importance of governance and coordination among different levels
of government and emergency services.
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Incorporating disaster management into urban forest management includes several
key components that are preventive and responsive. Preventive measures involve risk
assessment, planning, and prevention. Risk assessment includes identifying
vulnerabilities and mapping high-risk areas using inventory and monitoring data,
while planning and prevention actions include tree inventories, health monitoring,
proactive tree maintenance (e.g., pruning), and infrastructural protection (e.g.,
managing trees near power lines). Responsive actions involve implementing
response plans and coordinating emergency and recovery efforts. This includes
collaboration with emergency response and land management agencies, public
communication, and post-event assessments (e.g., identifying damaged trees).
Recovery efforts should focus on replanting, restoration, and re�ning strategies to
improve future preparedness (US Forest Service, n.d.; Smart Trees Paci�c, 2013a;
Huff, E. et al., 2020). Comprehensive emergency response plans should also include
preventative and responsive measures that prioritize the safety of workers and the
public during and after emergencies (The Arborist Safe Work Practices (ASWP),
2023).
Management and Mitigation Strategies
Municipalities should allocate adequate resources in their budgets for disaster
preparedness, including funding for specialized training for urban forestry personnel.
Training should cover the safe handling of hazardous situations, such as downed
power lines or unstable trees, and the implementation of health and safety protocols.
Furthermore, regular drills and simulations can help ensure that personnel are well-
prepared to respond swiftly and effectively when disaster strikes (Government of
Canada, 2024b). Cities should also invest in human resources dedicated to disaster
management within the urban forestry sector. This includes roles focused on risk
assessment and emergency planning, and public education on the importance of tree
care in disaster mitigation (Konijnendijk et al., 2021). Collaboration with local
agencies, utilities, and community organizations is also crucial to ensure a uni�ed
response during emergencies.
Canadian strategies and policies also emphasize the importance of governance and
coordination among different levels of government and emergency services. For
instance, the Canadian Wildland Fire Strategy (Canadian Council of Forest Ministers,
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2016) outlines a coordinated approach to wild�re management, while Public Safety
Canada (Public Safety Canada, 2022b) provides guidelines for emergency
management that include urban forestry considerations. Municipalities can also
bene�t from provincial programs like Ontario’s Forest Health Protection Program
(Government of Ontario, n.d.), which supports the management of pest and disease
outbreaks [see chapter: Insects and Diseases].
Integrating disaster management into urban forest management plans is a necessity.
Many municipal urban forest management plans include a section on emergency
preparedness. Municipalities should aim to adopt robust strategies, policies, and
practices so that cities can better protect their urban forests and, by extension, their
communities from the growing risks posed by natural disasters.
Resources
Canadian Council of Forest Ministers. (2016). Canadian Wildland Fire Strategy: A 10-year review and
renewed call to action.
https://cfs.nrcan.gc.ca/pubwarehouse/pdfs/37108.pdf
Government of Canada. (2005). Canadian wildland �re strategy: a vision for an innovative and integrated
approach to managing the risks - a report to the Canadian Council of Forest Ministers, prepared by the
Canadian Wildlife Fire Strategy Assistant Deputy Ministers Task Group: Fo134-1/2005E-PDF. Government
of Canada Publications.
https://publications.gc.ca/site/eng/9.687948/publication.html
Government of Canada. (2024a). National Risk Pro�le: A national emergency preparedness and awareness
tool. Public Safety Canada.
https://www.publicsafety.gc.ca/cnt/rsrcs/pblctns/2023-nrp-pnr/2023-npr-pnr-en.pdf
Government of Canada. (2024b). Health and Safety Program - General elements. Canadian Centre for
Occupational Health and Safety (CCOHS).
https://www.ccohs.ca/oshanswers/hsprograms/basic.html
Hartel, D. (2015). Urban Forests: Building resilience to natural disasters. Urban Forestry South.
https://urbanforestrysouth.org/resources/presentations/2015%20USDN%20Urban%20Forests%20-
%20Resiliency%20and%20Response%20to%20Natural%20Disasters%20-18Feb15%20v1.0.pdf
Hartel, D. (2019). Disaster Recovery Steps to Maintain and Improve Urban Forest Resilience. U.S.
Department of Agriculture, Forest Service.
https://www.fs.usda.gov/nrs/pubs/gtr/gtr-nrs-p-185papers/17-hartel_gtr_nrs-p-185.pdf
Canadian National
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Mihychuk, M. (2018). From The Ashes: Reimagining Fire Safety and Emergency Management in Indigenous
Communities. In 42nd Parliament, 1st session. Standing Committee on Indigenous and Northern Affairs.
https://www.ourcommons.ca/Content/Committee/421/INAN/Reports/RP9990811/inanrp15/inanrp15-
e.pdf
Public Health Agency of Canada. (2023). Creating the Conditions for Resilient Communities: A Public
Health Approach to Emergencies.
https://www.canada.ca/content/dam/phac-aspc/documents/corporate/publications/chief-public-
health-o�cer-reports-state-public-health-canada/state-public-health-canada-2023/report/report.pdf
Public Safety Canada. (2017). An Emergency Management Framework for Canada (3 ed.).
https://www.publicsafety.gc.ca/cnt/rsrcs/pblctns/2017-mrgnc-mngmnt-frmwrk/index-en.aspx
Public Safety Canada. (2022a). Emergency Management Strategy for Canada: Toward a resilient 2030.
https://www.publicsafety.gc.ca/cnt/rsrcs/pblctns/mrgncy-mngmnt-strtgy/index-en.aspx
Public Safety Canada. (2022b). Emergency management.
https://www.publicsafety.gc.ca/cnt/mrgnc-mngmnt/index-en.aspx
Public Safety Canada. (2024). Advancing the Federal-Provincial-Territorial Emergency Management
Strategy: Areas for Action (2024th ed.).
https://www.publicsafety.gc.ca/cnt/rsrcs/pblctns/2024-ems-ctn-rs/ems-ctn-rs-en.pdf
Workplace Safety & Prevention Services. (2023). Arborist Industry Safe Work Practices Guide.
https://www.wsps.ca/resource-hub/guides/arborist-industy-safe-work-practices-guide
City of Edmonton. (2021). Urban Forest Asset Management Plan.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PDF/Urban-Forest-Asset-
Management-Plan.pdf
Temmer, J., Smith, R., & Terton, A. (2017). Building a Climate-Resilient City: Disaster preparedness and
emergency management. Prairie Climate Centre.
https://www.edmonton.ca/public-�les/assets/document?path=PDF/Paper9-pcc-brief-disaster-
mangement-emergency-preparedness.pdf
Town of Banff. (2019). Town of Banff Strategic Plan 2019-2022.
https://banff.ca/DocumentCenter/View/6102/Banff-Strategic-Plan-2019-2022
Town of Banff. (2022). Strengthening Emergency Management and Wild�re Preparedness.
https://banff.ca/DocumentCenter/View/9510/Strengthening-Emergency-Management-and-Wild�re-
Preparedness-Tactics
rd
Canadian Provincial
Alberta
British Columbia
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British Columbia FireSmart. (2022). Community Wild�re Resiliency Plan Instruction Guide. Community
Wild�re Resiliency Plan (pp. 3–60).
https://www.ubcm.ca/sites/default/�les/2022-11/
LGPS_CRI_FCFS%202022CWRPInstruction%20Guide.pdf
British Columbia Firesmart. (2024). British Columbia Community Wild�re Resiliency Plan Instruction Guide.
https://www.ubcm.ca/sites/default/�les/2024-06/
LGPS_CRI_FCFS_2024_CWRP_Instruction_Guide_2024-06.pdf
Government of British Columbia. (2016). BC Wild�re Service Mandate & Strategy - Province of British
Columbia.
https://www2.gov.bc.ca/gov/content/safety/wild�re-status/about-bcws/governance/mandate-
strategy
Town of Gibsons. (2024). Gibsons Takes a Green Step Forward with First-Ever Urban Forest Plan. Town
of Gibsons.
https://gibsons.ca/2024/01/08/gibsons-takes-a-green-step-forward-with-�rst-ever-urban-forest-plan/
Government of Nova Scotia. (2021). Impact of Hurricane Juan on woodlands and parks of central Nova
Scotia.
https://novascotia.ca/natr/forestry/programs/ecosystems/juan/
Burt, J. (2022). Guidelines For a Municipal Forest Fire Emergency Plan. Municipality of Northern Bruce
Peninsula.
https://www.northbrucepeninsula.ca/media/5qniaebz/schedule-e-2022-guidelines-for-forest-�re-
emergency-plan-�nal-1.pdf
City of Guelph. (2024). Urban Forest Management Plan.
https://guelph.ca/plans-and-strategies/urban-forest-management-plan/
City of Kitchener. (2019). It’s a Tree’s Life: Kitchener’s Sustainable Urban Forest Strategy 2019-2028.
https://www.kitchener.ca/en/resourcesGeneral/Documents/INS_PARKS_Urban_Forest_Strategy.pdf
City of Markham. (2017). City of Markham Emergency Response Plan.
https://www.markham.ca/wps/wcm/connect/markham/d4bb8e1c-c668-491c-92a4-03498088719a/
markham-emergency-plan.pdf
City of Toronto. (2021). City of Toronto Emergency Plan.
https://www.toronto.ca/wp-content/uploads/2021/01/9740-Emergency-Plan-2020-Update-2021-01-21-
AODA-Compliance.pdf
Emergency Management Ontario. (2021). Emergency Management Framework for Ontario. Emergency
Management Framework for Ontario (pp. 1–45).
Nova Scotia
Ontario
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https://�les.ontario.ca/books/solgen-emo-emergency-management-framework-2021-
en-2021-12-30.pdf
Government of Ontario. (n.d.). Forest health conditions.
https://www.ontario.ca/page/forest-health-conditions
Town of Oakville. (2020). 2020 Urban Forest Strategic Management Plan.
https://www.oakville.ca/getmedia/fce78d07-771f-4f6a-b65c-fb2d5e7da152/urban-forest-strategic-
management-plan.pdf
International Rainy-Lake of the Woods Watershed Board. (2019). Review of environmental emergency
planning, preparedness and response in the boundary waters of the Rainy-Lake of the Woods Drainage
Basin. International Joint Commission.
https://ijc.org/sites/default/�les/2019-03/RLWWB-EEPPR_in_the_RLOW_basin_March_2019_0.pdf
Smart Trees Paci�c. (2013a). Urban Forestry Emergency Operations Planning Guide for Storm Response.
https://vibrantcitieslab.com/wp-content/uploads/2017/05/Urban-Forestry-Emergency-Operations-
Planning-Guide.pdf
Smart Trees Paci�c. (2013b). Urban Forestry Emergency Operations Planning Guide for Storm Response.
https://smarttreespaci�c.org/past-projects/urbanforestryeop
Sustainable Forestry Initiative. (2022). SFI Urban and Community Forest Sustainability Guidance. SFI
Urban and Community Forest Sustainability Guidance (p. 2).
https://forests.org/wp-content/uploads/Guidance-for-SFI-Urban-and-Community-Forest-Sustainability-
Standard-Second-Draft.pdf
US Forest Service. (n.d.). Emergency Response and Preparedness.
https://www.fs.usda.gov/inside-fs/emergency-response-preparedness
USDA Forest Service. (2013). Urban Forestry Emergency Operations Planning Guide for Storm Response.
Urban Forestry South.
https://urbanforestrysouth.org/resources/library/ttresources/urban-forestry-emergency-operations-
planning-guide-for-storm-response
Huff, E., Johnson, M., Roman, L., Sonti, N., Pregitzer, C., Campbell, L., & McMillen, H. (2020). A Literature
Review of Resilience in Urban Forestry. Arboriculture & Urban Forestry, 46(3), 185–196.
https://doi.org/10.48044/jauf.2020.014
Kenney, W. A., van Wassenaer, P . J. E., & Satel, A. L. (2011). Criteria and Indicators for Strategic Urban
Forest Planning and Management. Arboriculture & Urban Forestry (AUF), 37(3), 108-117. Retrieved from
https://auf.isa-arbor.com/content/isa/37/3/108.full.pdf
Non-Canadian
Further Reading
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Konijnendijk, C., Nesbitt, L., & Wirtz, Z. (2021). Urban Forest governance in the face of Pulse Disturbances
—Canadian Experiences. Arboriculture & Urban Forestry, 47(6), 267–283.
https://doi.org/10.48044/jauf.2021.023
Ordóñez, C., & Duinker, P . (2014). Assessing the vulnerability of urban forests to climate change.
Environmental Reviews, 22(3), 311–321.
https://doi.org/10.1139/er-2013-0078
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Enabling Legislation, Municipal By-laws and
Regulations
Urban areas, though they make up about 1% of the land base in Canada, are home to
over 80% of the population and taxpayers. Urban areas and their populations serve
various national and provincial interests, yet there is no national urban forest
legislation, and existing local-level policies are decentralized. As a result, urban forest
policy in Canada is fragmented among municipalities and exists without signi�cant
involvement from upper levels of government (Kenney 2003; Barker and Kenney
2012). Thus, most urban forest policies are not determined by provincial or national
governments, but by municipalities (Hudson, 2014). With decentralized governance
across three levels of government, urban forest protection and management
decisions are largely made at the municipal level.
Urban forest policies and management are complicated due to the variety of land
ownership in urban areas, the shifts in rights and responsibilities, and the intersection
of land use policies and planning regulations. In response to public pressure, some
municipalities take a proactive approach to protecting trees and urban forests, while
Highlights
Urban forest policy in Canada
Lacking at the provincial and federal levels.
Municipal urban forest management
Complicated and fragmented among municipalities with a wide range of
departments, titles, and responsibilities.
Municipal tree bylaws
Used to guide urban forest management, planning, governance, and legislation.
Public and private tree bylaws
Used to regulate tree-related activities such as maintenance, planting, inspection,
monitoring, and removal.
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others adopt a more reactive stance, prioritizing development over environmental
preservation. Urban tree legislation and bylaws can vary greatly between
municipalities and across geographic areas; these differing bylaws and levels of
management have been captured in a 2018 project that measures the footprint of
urban forestry in Canada (Puric-Mladenovic & Bardekjian, 2023a, b). This tool serves
as a resource for small and large municipalities looking to start new or develop upon
existing urban forestry programs.
Municipal urban forestry programs have a wide variety of management areas and
responsibilities, such as managing street trees, removing hazardous trees, and
planting trees in new subdivisions. There are various policies relating to trees and
urban forests, all of which are adopted by municipalities as tools to aid in protecting
trees and regulating the injury of trees. There are nine major areas of municipal policy
related to trees and urban forests in Canada: (1) policy related to tree permit (e.g.,
tree removal permit, tree harvesting permit, and certi�cate of authorization), (2)
policy related to standards of trees in new subdivisions (e.g., development
speci�cations, landscape screening, shoreline buffer), (3) policy related to tree
planting guidelines, (4) policy related to the choice of tree species (e.g., the list of
recommended/prohibited tree species), (5) policy related to boulevard trees, (6)
policy related to commemorative trees, (7) policy related to protection of heritage
trees and natural heritage, (8) policy related to planting of native trees, and (9) policy
related to planting of shade trees (Puric-Mladenovic & Bardekjian, 2023a).
Municipal Bylaws
Tree bylaws are created by municipalities and implemented within municipal
boundaries. Tree bylaws support safe, sustainable, and legal tree-related activities in
Canada and are often written in accordance with private property laws and city-
curated forest management and land use plans. For example, tree bylaws state
prohibited activities, exemptions, permit requirements, and rule enforcement through
necessary processes, �xed �nes and penalties (City of Guelph, 2010). Tree bylaws,
depending on their implications, are under different provincial acts. Oftentimes,
municipal plans also include provisions for public engagement in tree-related policy
(CEN, n.d.). In British Columbia, the Community Charter acts as an “umbrella
regulation,” and in Ontario, the Municipal Act of 2001 empowers municipalities to
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enact tree bylaws. In Newfoundland, the New Urban and Rural Planning Act is the
enabling legislation that establishes the province’s land use planning system; it
allows the preparation of a range of planning, grant approval, and implementation
documents, and provides public input and appeal processes whereby development
decisions can be subjected to independent review (De Santis, 2020). This Act serves
as an umbrella regulation to manage urban and rural planning (Puric-Mladenovic &
Bardekjian, 2023).
The study by Puric-Mladenovic and Bardekjian (2023b) shows that there is a wide
range of bylaws pertaining to trees in Canadian municipalities. Over one-�fth (22.8%)
of the surveyed municipalities in 2018 had enacted private tree bylaws in response to
the municipal need to regulate the injury and removal of trees. Of the surveyed
municipalities, 18.3% have public/street tree bylaws. As expected, most of the 146
Canadian municipalities that have enacted public tree bylaws are in the more
urbanized provinces, such as Ontario (26%), followed by British Columbia (24%) and
Quebec (17%). Of the 182 municipalities that have private tree bylaws, the majority
are in Quebec (57.7%), followed by British Columbia (22%) and Ontario (13.7%).
A recent study revealed that in Ontario, more populous municipalities tend to have
more tree by-laws, suggesting the in�uence of various factors such as more available
funding, stronger political will, higher capacity for compliance and enforcement, and
increased public pressure (Yung, 2018). Additionally, the study highlighted signi�cant
variation in the types of tree bylaws and policies across municipalities in Ontario.
This variability re�ects a reactive and fragmented approach to tree protection, with
each municipality adopting its own unique strategies and regulations.
Public tree bylaws control activities on public property and city operations, such as
hydro utility practices, landscaping activities, pest management, construction, and
residential, industrial, and commercial development planning (City of Edmonton,
2019). Private tree bylaws regulate tree-related activities on private property, such as
tree-cutting, tree removal, tree topping (removal of large portions of a tree’s crown),
and building practices (Conway et al., 2022). Some municipalities such as Prince
George’s County in Maryland, USA, have tree canopy replacement bylaws, where
several trees must be planted to supplement the removal of large amounts of canopy
or large old trees (Dalke & Hawkins-Nixon, 2012), These “no net loss” or “net gain”
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bylaws help preserve and even increase urban canopy cover while still allowing
regular tree maintenance and removal when necessary.
Municipalities are also increasingly acknowledging the value of woodlands,
biodiversity, wildlife habitats, and ecosystem services through their tree bylaws. For
instance, the City of Peterborough’s Tree Conservation Bylaw (By-Law Number
17-120) explicitly recognizes the environmental, aesthetic, and public health bene�ts
of trees. The bylaw also regulates the destruction and injury of trees on private
property. Similarly, the Town of Orangeville’s Urban Forestry Policy highlights the
environmental, economic, and health bene�ts provided by urban trees (Yung, 2018).
In Quebec, many municipalities have adopted bylaws requiring permits and
certi�cates for tree-related maintenance, which have explicit provisions regarding the
“obligation of obtaining a certi�cate of authorization to fell a tree”. In Ontario, 23.2%
of municipalities (103 out of 444) had speci�c tree policies in 2018. These policies
cover a wide range of disciplines and municipal departments, such as Guidelines for
Trees and Landscaping, Speci�cations for the Planting of Municipal Trees and
Shrubs, and Tree Preservation and Clearing Guidelines for New Developments (Puric-
Mladenovic & Bardekjian, 2023b). However, 74.5% of Ontario municipalities (331 out
of 444) did not have tree bylaws in 2018.
In 2018, in Quebec, 44.2% of municipalities (106 out of 240) had tree bylaws (either
private or public). The tree bylaw has been enacted as part of a zoning bylaw, which
regulates tree cutting and plantation in both urban (e.g., residential areas) and
industrial settings. Such bylaws set out the regulations and guidelines for tree felling
or planting, which require owners to apply for a tree permit or certi�cate of
authorization. In Quebec, a bylaw to stop the spread of Emerald Ash Borer has been
passed in recent years, and about 8% of municipalities (19 out of 240) in Quebec had
such bylaws in 2018.
In Saskatchewan, about 26% of municipalities (6 out of 23) have adopted the Urban
Forestry Bylaw or Urban Tree Policy Rules and Regulations Bylaw. There are
provincial regulations regarding urban trees (e.g., Dutch Elm Disease Regulations in
Saskatchewan), which result in more standardized urban forestry programs (such as
Dutch Elm Management Programs across the province). All of these bylaws and
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regulations are essential to the maintenance and management of urban trees and
forests in Canada.
Resources
Canadian Environmental Network (CEN). (n.d.). - Progressive policy through public participation:
https://www.rcen.ca/en/home
Green Municipal Fund – Factsheet: An urban forestry overview:
https://greenmunicipalfund.ca/resources/factsheet-urban-forestry-overview
Webber, K., Le Geyt, M., O’Neill, M., and Murugesan, V. (2020). Guiding Urban Forestry Policy into the Next
Decade: A Private Tree Protection & Management Practice Guide.
https://council.cleanairpartnership.org/wp-content/uploads/2022/05/Practice-Guide_2020.pdf
City of Calgary. (n.d.). Tree protection bylaw.
https://www.calgary.ca/bylaws/tree-protection.html
City of Edmonton. (2019). Policy number C501A: Integrated pest management.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/PoliciesDirectives/C501A.pdf
City of Edmonton. (2024). City Of Edmonton Bylaw 14600: Community Standards Bylaw.
https://www.edmonton.ca/sites/default/�les/public-�les/assets/Bylaws/C14600.pdf
City of Edmonton. (n.d.). Tree regulations.
https://www.edmonton.ca/city_government/bylaws/tree-regulations
City of Burnaby. (n.d.). City of Burnaby Tree Bylaw Brochure.
https://www.burnaby.ca/sites/default/�les/acquiadam/2022-12/Tree%20Bylaw%20FAQ.pdf
City of Kelowna. (2005). Bylaw #4082: Municipal properties tree bylaw.
https://treecanada.ca/wp-content/uploads/2017/11/SUMMARY-.pdf
City of Vancouver. (2023). Protection Of Trees Bylaw No. 9958.
https://bylaws.vancouver.ca/9958c.PDF
Canadian National
Canadian Provincial
Alberta
British Columbia
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District of North Vancouver. (2012). Bylaw 7671: Protecting trees.
https://dnv-docs.simplicitycms.ca/documents/Bylaw%207671.pdf
District of Saanich. (2024). Urban forest strategy 2024-2034.
https://www.saanich.ca/assets/Community/Documents/
Environment/240726_SaanichUFS_8_online.pdf
City of Winnipeg. (n.d.). Trees and environment.
https://www.winnipeg.ca/services-programs/trees-environment
City of Fredericton. (2020). Bylaw No. L-18: A bylaw for the management of trees within the city of
Fredericton.
https://www.fredericton.ca/en/media/�le/lawnol-18-consolidatedpdf
City of St. John’s. (n.d.). City of St. John’s Landscape Development Policy.
https://www.stjohns.ca/en/building-development/resources/Construction/Landscape-Development-
Policy_Street-Tree-Planting-Standards.pdf
City of Halifax. (2008). Halifax Regional Municipality Bylaw Number T-600: By-law respecting trees on
public lands.
https://www.halifax.ca/sites/default/�les/documents/city-hall/legislation-by-laws/By-LawT-600.pdf
City of Guelph. (2010). Guelph Municipal Code – Tree protection bylaw.
https://guelph.ca/wp-content/uploads/TreeBylaw.pdf
City of Kingston. (n.d.). Tree bylaws and permits.
https://www.cityofkingston.ca/bylaws-and-animal-services/commonly-requested-bylaws/tree-bylaw-
and-permits/
City of Kitchener. (2002). Policy number I-1160: Tree management policy.
https://www.kitchener.ca/en/resourcesGeneral/Documents/INS_OPS_Treemanagementpolicy.pdf
City of London. (2022). Bylaw number C.P .-1555-252: Tree protection bylaw.
Manitoba
New Brunswick
Newfoundland & Labrador
Nova Scotia
Ontario
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https://london.ca/by-laws/consolidated-tree-protection-law
City of Mississauga. (2022). Private Tree Protection Bylaw 0021-2022.
https://www.mississauga.ca/wp-content/uploads/2018/09/30121717/Private-Tree-Protection-By-
law-0021-2022.pdf
Environmental Commissioner of Ontario. (2018). Back to Basics – 2018 Environmental Protection Report,
p.252.
https://www.auditor.on.ca/en/content/reporttopics/envreports/env18/Back-to-Basics.pdf
Filson, F. (2018). Municipal Tree Conservation in Southern Ontario. Thesis submitted to Faculty of Rural
Planning and Development, University of Guelph.
https://atrium.lib.uoguelph.ca/server/api/core/bitstreams/231546b3-f2ad-4c8f-a694-42617be51f34/
content
Government of Ontario. (n.d.). Document 3 - Tree Bylaws in other Ontario Municipalities - Precedent
Review.
https://pub-ottawa.escribemeetings.com/�lestream.ashx?documentid=25503
Government of Ontario. (2024). Forest management policies.
https://www.ontario.ca/page/forest-management-policies
Government of Prince Edward Island. (n.d.). Forest Enhancement Program (FEP): Forestry Services for
Private Forest Land Owners.
https://www.princeedwardisland.ca/en/service/forest-enhancement-program-fep-forestry-services-for-
private-forest-land-owners
Government of Prince Edward Island. (n.d.). Trees and planting.
https://www.princeedwardisland.ca/en/topic/trees-and-planting
Ville de Montréal. (2002). Master Plan Part III Section 5.6: Trees.
http://ville.montreal.qc.ca/portal/page?_pageid=2762,3101464&_dad=portal&_schema=PORTAL
Ville de Pointe-Claire. (2015). Bylaw Number Pc-2825: Bylaw Concerning the Protection of Public Trees.
https://www.pointe-claire.ca/content/uploads/2016/05/PC-2825_Protection_arbres_EN.pdf
City of Saskatoon. (2024). Bylaw no. 9957: The Tree Protection Bylaw.
https://www.saskatoon.ca/sites/default/�les/documents/city-clerk/bylaws/9957.pdf
City of Weyburn. (2018). Bylaw no. 2018-3373: Preservation of city tree policy.
Prince Edward Island
Quebec
Saskatchewan
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https://weyburn.ca/wp-content/uploads/2019/04/2018-3373-Urban-Forestry-Bylaw.pdf
Cities4Forests. (2019). Urban Forests for Healthier Cities: Policy, Planning, Regulations, and Institutional
Arrangements.
https://cities4forests.com/resource/urban-forests-for-healthier-cities-policy-planning-regulations-and-
institutional-arrangements/introduction-to-regulations-for-urban-forests/
Dalke, S. and Hawkins-Nixon, D. (2012). No Net Loss Tree Conservation Regulation and Policy to Maintain
and Expand Street Tree Canopy and Forest as a Land Cover.
https://www.princegeorgescountymd.gov/sites/default/�les/media-document/
SD%2012_%20NO%20NET%20TREE%20LOSS%203V2.pdf
Food and Agriculture Association of the United Nations (2016). Forestry Paper 178 – Guidelines on urban
and peri-urban forestry.
https://openknowledge.fao.org/server/api/core/bitstreams/9c27d98b-8071-4ee7-8fc4-e0b430f8a8dc/
content
Norza, J. (2022). Green Laws and urban forestry — which countries are in the lead? Lampoon Magazine,
29.
https://lampoonmagazine.com/article/2022/01/01/green-laws-urban-forestry/
USDA Forest Service. (2005). Urban Forestry – A Manual for the State Forestry Agencies in the Southern
Region.
https://www.fao.org/uploads/media/
Urban%20forestry%20manual_urban%20forestry%20and%20public%20policy.pdf
Andresen, J. W. (1977). Urban Forestry Legislation in Ontario. The Forestry Chronicle, 53(5), 291-293.
https://doi.org/10.5558/tfc53291-5
Barker, E. J. and Kenney, W. A. (2012). Urban forest management in small Ontario municipalities. The
Forestry Chronicle, 88, 118-123.
https://doi.org/10.5558/tfc2012-027
Conway, T.M., Khatib, J.K., Tetreult, J., & Almas, A.D. (2022). A Private Tree Bylaw’s Contribution to
Maintaining a Diverse Urban Forest: Exploring Homeowners’ Replanting Compliance and the Role of
Construction Activities in Toronto, Canada. Arboriculture & Urban Forestry, 48(1), 9-26.
https://doi.org/10.48044/jauf.2022.002
Conway, T.M. and Urbani, L. (2007). Variations in municipal urban forestry policies: A case study of
Toronto, Canada. Urban Forestry & Urban Greening, 6(3), 181-192.
https://doi.org/10.1016/j.ufug.2007.07.003
Non-Canadian
Further Reading
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De Santis, J. (2020). Impact of Residential Intensi�cation on Urban Forest in the Long Branch
Neighbourhood, Toronto. Thesis submitted to Faculty of Forestry, University of Toronto.
http://hdl.handle.net/1807/99002
Hudson, B. (2014). Institutions, law, and the political ecology of urban forests: A comparative approach.
In: Urban Forests, Trees, and Greenspace - A Political Ecology Perspective. Publisher: Routledge, Editors:
Sandberg, A. L., Bardekijan, A., Butt, S., Pages 61-76.
https://doi.org/10.4324/9781315882901
Kenney, W. A. (2003). A strategy for Canada's urban forests. The Forestry Chronicle, 79, 785-789.
https://doi.org/10.5558/tfc79785-4
Puric-Mladenovic, D. and Bardekjian, A. (2023a). Canada's Urban Forest Footprint: Mapping the Extent and
Intensity of Urban Forestry Activities. Forests in Settled & Urban Landscapes applied science and
research lab. Daniels Faculty, University of Toronto. John H. Daniels Faculty of Architecture, Landscape
and Design, University of Toronto.
http://forests-settled-urban-landscapes.org/UrbanForestryFootprint/
Puric-Mladenovic, D. and Bardekjian, A. C. (2023b). Canada’s Urban Forestry Footprint.
https://utoronto.maps.arcgis.com/apps/dashboards/21acf59a306d41dd862c4e6ba25a0da0
Yung, Y. K. (2018). State of Urban Forest Policy and By-laws across Ontario Municipalities. Thesis
submitted to Faculty of Forestry, University of Toronto.
http://hdl.handle.net/1807/81308
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Tree Protection During Construction and
Conflict with Building Foundations
Tree Protection & Construction
In urban areas, there is often competition between development activities and trees
due to a lack of available growing space. Urban trees are frequently impacted by
infrastructural maintenance, underground utility expansion, or building construction.
When construction is close to or within tree root zones, soil removal, trenching, heavy
machinery, and repeated foot tra�c cause soil compaction and root damage (Despot
Highlights
Construction severely impacts urban trees
Activities like excavation, trenching, and machinery use near trees can cause soil
compaction and root damage, often leading to long-term tree health decline or
death.
Tree damage often shows years later
Signs of decline from construction damage (like canopy dieback or pest
vulnerability) may not appear immediately and can take years to manifest,
especially under added environmental stress like drought.
Proactive tree protection is essential
Pre-construction tree assessments and protection plans (e.g., barriers, bylaws, root
zones) signi�cantly improve tree survival and urban canopy integrity.
Urban trees and infrastructure can conflict
Trees planted too close to buildings can damage foundations and pavements,
particularly when root growth is stimulated by moisture in structural cracks.
Soil type matters
In clay soils, trees near structures can exacerbate soil movement and settlement,
making proper tree species selection and planting distance critical to avoid
damage.
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& Gerhold, 2003). Sometimes, unintended movements by heavy machinery can also
result in mechanical damage to the above-ground tree parts. For example, common
construction activities such as paving, sidewalk (re)installations, excavation,
trenching, and roadway widening involve various machinery that can severely affect
the existing trees (Despot & Gerhold, 2003).
Without adequate protection during construction, trees can be damaged, leading to a
decline in tree health, which can be deadly. In worst cases, these injuries can lead to
functional and structural damages that appear as weak foliage, canopy decline, rot
and decay, or even tree death (Hauer et al., 2020; North et al., 2017). Damage to roots
caused by compaction can impact tree access to water and nutrients, ultimately
compromising its health, longevity, and ability to recover (Fini et al., 2020). In many
cases, tree decline and death can take years to become apparent (Fini et al., 2020). It
has been documented that trees in construction zones experience a higher annual
mortality rate and have worse tree health than trees not impacted by construction
(Hauer et al., 2020; Hilbert et al., 2019). Trees previously exposed to construction
damage are also more vulnerable to other environmental and biological stressors.
For instance, a tree stressed during construction may not exhibit obvious signs of
decline until a period of drought occurs, causing crown defoliation and eventually
other health problems like dieback, limb loss, and increased susceptibility to insects
and disease (Fini et al., 2020). This might appear as a sudden decline, but due to root
reduction from construction impacts, the already-stressed tree has limited access to
water, oxygen, and nutrients and can no longer handle additional environmental
stress. However, the rate of post-construction tree decline depends on many factors
such as the age of trees, tree species, the extent and nature of damage, the health of
the tree prior to construction, and care given after construction is complete (North et
al., 2017; Fini et al., 2020).
Evaluation of green space and trees, as well as implementing strategies to save and
protect urban trees, should be a critical part of urban development. An assessment
should be completed before starting construction to ensure the conservation and
preservation of existing trees and, thus, maintain the urban forest canopy and its
integrity. Studies have shown that investing in tree protection for mature trees
positively impacts the overall tree canopy within urban environments (Benson,
Koeser, & Morgenroth, 2019a). Urban forest studies continuously re�ne tree
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protection recommendations based on emerging root damage and tree health
studies. For example, Benson et al. (2019a) recommend providing a protection zone
15 times the diameter of the tree in question to ensure tree health. Not only do
mature trees add to the aesthetic value of public spaces, but they also provide
ecosystem and infrastructural services that cannot be easily replaced (Hotte et al.,
2015). However, questions always remain about the appropriate extent of the tree
protection zone, and this type of research continues to advance relevant knowledge
(Benson et al., 2019a; City of Toronto, 2016; Matheny & Clark, 1998).
Best management practices to protect trees during construction include
construction-speci�c tree protection bylaws, site plans that ensure adequate space
for tree roots, and tree, soil, and root protection measures. Many large Canadian
municipalities mandate these measures, which are re�ected in protection bylaws,
guidelines, and urban forest management plans (Yung, 2018). Tree-protection plans
often include physical barriers at a certain distance around trees that typically restrict
access to their root zone and stem. These barriers protect the soil around the tree
from compaction and can also prevent damage from machinery. Construction
documents often detail what can and cannot be done within set distances from each
tree (Despot & Gerhold, 2003). Tree protection techniques and guidelines are backed
up by research that tracked tree health for years and decades after construction
(Hauer et al., 2020; Fini et al., 2020). In special situations where additional expertise
is needed, a professional arborist or forester may provide recommendations related
to protecting and preserving trees near construction projects.
Trees and Building Foundations
Many urban trees are planted too close to buildings or other gray infrastructure. This
could be due to lack of space, lack of knowledge of how trees will develop over time,
planning designs that disregard trees as living and growing organisms, or an
inappropriate species or cultivar selection for the given space. As a result, trees often
grow in con�ict with structures and have the potential to cause direct or indirect
damage to urban structures. An example of direct con�ict between a tree and
structure is when a tree trunk or stem grows into a building or a tree root grows into
the pavement (Overkeke, 2008; Day, 1991). When tree roots search for water, air, and
nutrients, they can grow into undesirable places; intruding root growth is often
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prompted by existing cracks in the structures or pavement, which allows moisture to
seep through. This can be avoided by considering the mature size of a tree prior to
planting, including the extent of the root zone, and by selecting the right species for
the space (Overkeke, 2008).
Tree roots can contribute to the settling of substrates under and around building
foundations. Studies show that a combination of clay soil, proximity of trees to
structures, and quality of construction can lead to indirect damage to buildings over
time (Navarro et al., 2009; Overkeke, 2008; Day, 1991; Vorwerk, Cameron, & Keppel,
2015). Clay soil is especially prone to shrinking and expanding, which can lead to
more movement around buildings as they settle and create a space in which tree
roots can develop (Overkeke, 2008; Vorwerk, Cameron, & Keppel, 2015). When trees
are planted too close to the foundation, they can add to the amount of water
extracted from the soil (clay soil in particular) and lead to more root movement over
time. Since the water demands of trees are species-speci�c, the soil type and
species should be considered when creating a planting plan. Planting far away from
buildings or structures is a good preventative measure in areas with clay soil; the
notable exception to this recommendation is for rail tracks and sloped embankments
built on clay soils, where vegetation provides necessary stability (Vorwerk, Cameron,
& Keppel, 2015). Lastly, as structures with shallow foundations are especially prone
to damage, infrastructure solutions such as deeper perimeter foundations are also a
helpful preventative measure (Day, 1991).
Resources
City of Calgary. (2018). Development Guidelines and Standard Speci�cations: Landscape Construction.
https://www.calgary.ca/content/dam/www/pda/pd/documents/urban-development/publications/
landscape-construction.pdf
City of Calgary. (n.d.). Tree Protection Plans.
https://www.calgary.ca/environment/resources/tree-protection-plans.html
Canadian Provincial
Alberta
British Columbia
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City of Burnaby. (n.d.). All about our beautiful trees–how we’re protecting them and what you can do to
help. Trees.
https://www.burnaby.ca/services-and-payments/trees
City of Vancouver. (n.d.). Protection of Trees By-law 9958.
https://vancouver.ca/your-government/protection-of-trees-bylaw.aspx
Esquimalt Parks + Recreation. (n.d.). Avoiding Tree Damage During Construction. Township of Esquimalt.
https://www.esquimalt.ca/sites/default/�les/docs/parks-recreation/
avoiding_tree_damage_during_construction.pdf
City of Halifax. (2012). Halifax Regional Municipality By-Law Number T-600: By-Law Respecting Trees on
Public Lands. Halifax.
https://www.halifax.ca/sites/default/�les/documents/city-hall/legislation-by-laws/By-LawT-600.pdf
City of Halifax. (n.d.-a). Tree Protection Zone and Barrier Construction.
https://www.halifax.ca/home-property/urban-forestry/tree-protection-construction
City of Halifax. (n.d.-b). Trees and Construction.
https://www.halifax.ca/home-property/urban-forestry/tree-protection-construction
City of Ottawa. (2024, February 1). Tree protection (by-law no. 2020-340). Ottawa.
https://ottawa.ca/en/living-ottawa/laws-licences-and-permits/laws/laws-z/tree-protection-law-
no-2020-340
City of Thunder Bay. (2018). Tree Protection. Tree Protection Standards.
https://www.thunderbay.ca/en/city-services/tree-protection-standards.aspx
City of Toronto. (2016). (rep.). Tree Protection Policy and Speci�cations for Construction Near Trees.
Toronto, Ontario. Retrieved August 7, 2024, from
https://www.toronto.ca/data/parks/pdf/trees/tree-protection-specs.pdf
Webber, K., Le Geyt, M., O’Neill, T., Connors, S. & Murugesan, V. (2019). Tree Protection and Tree
Management: A Best Practices and Legislative Review. University of Waterloo.
https://uwaterloo.ca/planning/sites/default/�les/uploads/documents/
treeprotectionandtreemanagement_2019.pdf
City of Pleasanton. (n.d.). Pleasanton, CA Tree Preservation Ordinance. Green Policy.
https://www.greenpolicy360.net/w/Pleasanton,_CA_Tree_Preservation_Ordinance
Nova Scotia
Ontario
Non-Canadian
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City of Seattle. (n.d.). Seattle Department of Construction & Inspections. Trees & Codes.
https://seattle.gov/sdci/codes/codes-we-enforce-(a-z)/trees-and-codes
Dennis, C., & Jacobi, W. R. (2020, August). Protecting Trees During Construction. Colorado State University
Extension.
https://extension.colostate.edu/docs/pubs/garden/07420.pdf
Elmendorf, W. (2022, August 30). A Guide to Preserving Trees in Development Projects. Penn State
Extension.
https://extension.psu.edu/a-guide-to-preserving-trees-in-development-projects
Feeley, C. (2002, May 12). Preventing Construction Damage to Trees. Iowa State University Extension.
https://www.extension.iastate.edu/newsrel/2002/may02/may0203.html
International Society of Arboriculture. (n.d.). Avoiding Tree Damage During Construction. International
Society of Arboriculture. Retrieved August 7, 2024, from
https://dnr.illinois.gov/content/dam/soi/en/web/dnr/conservation/forestry/documents/trees-how-to-
information/avoiding-trees.pdf
Benson, A., Koeser, A., & Morgenroth, J. (2019a). Responses of mature roadside trees to root severance
treatments. Urban Forestry & Urban Greening, 46.
https://doi.org/10.1016/j.ufug.2019.126448
Benson, A., Koeser, A., & Morgenroth, J. (2019b). A test of tree protection zones: Responses of Quercus
virginiana Mill trees to root severance treatments. Urban Forestry & Urban Greening, 38, 54-63.
https://doi.org/10.1016/j.ufug.2018.10.015
Day, R. (1991). Damage of Structures due to Tree Roots. Journal of Performance of Constructed
Facilities, 5(3).
https://doi.org/10.1061/(ASCE)0887-3828(1991)5:3(200)
Despot, D., Gerhold, H. (2003). Preserving trees in construction projects: Identifying incentives and
barriers.Journal of Arboriculture, 29(5), 267-275.
https://auf.isa-arbor.com/content/29/5/267
Fini, A., Frangi, P ., Mori, J., Sani, L., Vigevani, I., & Ferrini, F. (2020). Evaluating the effects of trenching on
growth, physiology and uprooting resistance of two urban tree species over 51-months. Urban Forestry &
Urban Greening, 53, 126734.
https://doi.org/10.1016/j.ufug.2020.126734
Grahn, P ., Stigsdotter, U. (2003). Landscape Planning and Stress. Urban Forestry and Urban Greening,2,
1-18.
https://doi.org/10.1078/1618-8667-00019
Hauer, R. J., Koeser, A. K., Parbs, S., Kringer, J., Krouse, R., Ottman, K., …Werner, L. P . (2020). Long-term
effects and development of a tree preservation program on tree condition, survival, and growth.
Further Reading
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Landscape and Urban Planning, 193, 103670.
https://doi.org/10.1016/j.landurbplan.2019.103670
Hilbert, D. R., Roman, L. A., Koeser, A. K., Vogt, J. and van Doorn, N. A. (2019). Urban Tree Mortality: A
Literature Review. Arboriculture & Urban Forestry, 45 (5) 167-200.
https://doi.org/10.48044/jauf.2019.015
Hotte, N., Barron, S., Cheng, Z., Nesbitt, L., & Cowan, J. (2015). The Social and Economic Values of
Canada's Urban Forests: A National Synthesis.
https://doi.org/10.1016/j.ufug.2017.05.005
Matheny, N. & Clark, J. (1998). Trees and Development: A Technical Guide to Preservation of Trees during
Land Development. International Society of Arboriculture.
https://wwv.isa-arbor.com/store/product/108/
Navarro, V., Candel, M., Yustres, Á., Alonso, J., & García, B. (2009). Trees, lateral shrinkage and building
damage. Engineering Geology, 108(3), 189-198.
https://doi.org/10.1016/j.enggeo.2009.07.006
Overbeke, C. (2008). Do trees really cause so much damage to property? Journal of Building Appraisal,
3(4), 247-258.
https://doi.org/10.1057/jba.2008.6
Sorvig, K. & Thompson, J. W. (2018). Sustainable Landscape Construction: A Guide to Green Building
Outdoors (3 ed.). Washington, DC: Island Press.
https://link.springer.com/book/10.5822/978-1-61091-811-4
Vorwerk, S., Cameron, D., & Keppel, G. (2015). Chapter 22 - Clay Soil in Suburban Environments:
Movement and Stabilization through Vegetation. In B. Indraratna, J. Chu, & C. Rujikiatkamjorn (Eds.),
Ground Improvement Case Histories (pp. 655-682): Butterworth-Heinemann.
https://doi.org/10.1016/B978-0-08-100191-2.00022-8
Watson, G., Hewitt, A., Custic, M., & Lo, M. (2014). The management of tree root systems in urban and
suburban settings: A review of soil in�uence on root growth. Arboriculture & Urban Forestry, 40(4).
https://doi.org/10.48044/jauf.2014.021
Watson, G., Neely, D. (1995). Trees and Building Sites: Proceedings of an International Conference Held in
the Interest of Developing a Scienti�c Basis for Managing Trees in Proximity to Buildings. International
Society of Arboriculture, Champaign, IL.
Yung, Y. K. (2018). State of Urban Forest Policy and Bylaws across Ontario Municipalities (thesis).
https://tspace.library.utoronto.ca/handle/1807/81308
rd
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Abiotic Stresses
Urban trees face numerous abiotic stresses that signi�cantly affect their health,
growth, and longevity. These stresses include limited soil volume, soil compaction,
air pollution, road salts, heavy metals, drought, mechanical damage, light pollution,
and the urban heat island effect, to name a few. The local conditions of urban
environments intensify the magnitude of these stressors and their impact on trees.
Understanding and managing these cumulative impacts is crucial for the
sustainability of urban forests (Collins, 2007).
Soil compaction and inadequate soil volume are persistent challenges for trees in
built-up areas. Unfavourable soil conditions and limited rooting space negatively
impact sustained tree growth and physiological functions due to reduced oxygen,
restrained water and nutrient availability. For example, soil compaction increases
bulk density and reduces soil pore space, restricting the growth of �ne feeder roots
essential for absorbing water and nutrients. In turn, this makes trees more vulnerable
to drought and other stressors, which can lead to the premature decline of urban
trees over time and threaten the overall health and resilience of the urban forest
(Cushing, 2009; Jim, 2023).
Highlights
Key abiotic stresses
Soil compaction, air pollution, de-icing salts, heavy metals, droughts, mechanical
damage.
Mitigation strategies
Green infrastructure solutions, selection of resilient tree species, and regular tree
maintenance.
Cumulative impacts
Multiple abiotic stresses.
Management
Integrated management, landscape planning, tree planting standards.
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Air pollution, including particulate matter, ozone, sulphur dioxide, and nitrogen oxides,
impacts urban trees by reducing their photosynthetic e�ciency and growth. It has
been shown that trees exposed to high levels of air pollution may exhibit symptoms
like chlorosis, reduced leaf size, and premature leaf drop, which weaken trees,
making them more susceptible to other stresses (Grote, 2016; Moore, 2023).
The use of de-icing salts is another stressor that poses a signi�cant threat to urban
trees in Canada. Road salts, primarily sodium chloride, accumulate in the soil, leading
to osmotic stress and toxicity. Symptoms of excessive road salt on trees include leaf
scorch, reduced growth, and even death, particularly in poorly drained areas (Equiza
et al., 2017; Government of Canada, 2015). With regards to road salts, reducing salt
application, using alternative de-icing materials such as sand, choosing salt-tolerant
species, and designing landscapes to minimize salt runoff are effective strategies
that help sustain urban forests (Government of Canada, 2015; Transportation
Association of Canada (TAC, 2024).
Urban trees, particularly those near tra�c and industrial sites, often accumulate
heavy metals in their tissues, causing toxicity and leading to impaired tree growth.
These contaminants can reduce growth rates, cause leaf discoloration, stress trees
and increase their vulnerability to pests and diseases. Studies have shown that heavy
metals like copper, mercury, manganese, nickel, lead, and zinc are found in higher
concentrations in the bark of trees growing closer to streets, contributing to long-
term physiological stress and reduced growth (Nechita et al., 2021; Yousaf et al.,
2020; Kargar, 2013). It is essential to monitor and manage soil quality regularly,
remediate contaminated sites when necessary, and select tree species tolerant of
pollutants (Nechita et al., 2021)
Drought is a common stress in urban areas, especially during summer when water
availability is limited. Urban trees, already stressed by poor soil conditions and
impermeable surfaces, are more vulnerable to drought, leading to reduced growth,
dieback, and mortality. The urban heat island effect exacerbates these conditions by
increasing temperatures within urban areas and accelerating water loss through
evapotranspiration (Dale & Frank, 2022). This phenomenon is particularly concerning
in the context of climate change, which intensi�es heat waves and further stresses
urban trees, weakening them and increasing their susceptibility to diseases and
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pests (Duinker et al., 2015; Ziter et al., 2019). Selecting drought-tolerant species,
implementing e�cient irrigation, and using mulching improve the water-holding
capacity of urban soils and reduce the impact of drought (Saddle Hills County, n.d.).
Mechanical damage from construction, vehicular impacts, and improper pruning are
also common in urban areas. Such injuries become entry points for pathogens,
resulting in decay and structural weakness, which can signi�cantly reduce a tree's
lifespan (Krige, 2024). For example, mechanical damage has been identi�ed as a
signi�cant threat to the urban forest in Toronto, requiring careful management and
mitigation strategies like using physical barriers or fences around trees, pruning trees
of concern, and post-construction soil/wound treatment (City of Toronto, 2017; Krige,
2024; Shinwary, 2021; Fraedrich, n.d.). When it comes to reducing mechanical
damage, it is essential to implement protective measures, such as tree guards, and to
educate the public and professionals about proper tree care practices. Regular
inspections and maintenance can also help identify and address mechanical injuries
before they lead to more severe issues (City of Toronto, 2017; Krige, 2024; Shinwary,
2021)
Some other overlooked stressors include arti�cial light and dog urine. Arti�cial light
can disrupt the natural growth cycles of urban trees, interfering with photosynthesis
and respiration. It has been shown that excessive light exposure can delay leaf drop,
disrupt �owering, and reduce overall vigour, weakening trees and increasing their
susceptibility to other stresses (Meng et al., 2022). Using shielded lighting, adjusting
light timing, and selecting species less sensitive to light �uctuations can mitigate the
effects of light pollution (Meng et al., 2022). Dog urine is an abiotic stressor linked to
increasing urban population density and, thus, dog ownership. Studies have shown
that though dog urine deposition and "fertilization" are localized due to their high
nitrate, ammonium, and phosphorus concentrations, they have a negative impact on
soils and trees. Soils impacted by dog urine also have signi�cantly higher salt
concentrations (lower osmotic potential), making it harder for trees, especially
younger trees, to take up water (De Frenne, 2022).
Strategies like increasing tree canopy cover, using re�ective materials in urban
design, and creating green infrastructure that cools the urban environment can be
used to mitigate the impact of heat on trees. Green infrastructure solutions, such as
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rain gardens and permeable pavements, also help reduce heat stress (Dale & Frank,
2022; Ziter et al., 2019). These strategies bene�t trees and improve overall urban
livability by reducing heat and improving air quality (Dale & Frank, 2022).
In addition, resilient species that can withstand a range of environmental conditions
should be prioritized. Selecting tree species that tolerate urban conditions is crucial.
For example, it has been observed that species like Ginkgo (Ginkgo biloba),
Honeylocust (Gleditsia triacanthos), Oak (Quercus spp., and Elm (Ulmus spp.), as well
as Kentucky Coffee-tree (Gymnocladus dioicus) and Northern Red Oak (Quercus
rubra) might show higher resilience against urban stressors like drought, soil
compaction, and pollution (Carol-Aristizabal, 2024; Credit Valley Conservation, 2022).
Considering the complex interactions between abiotic stresses and the health of
urban trees, integrated management and planning approaches are necessary to
maintain resilient urban forests. Regular monitoring and adaptive management
ensure the long-term sustainability of urban forests. In addition, landscape designs
combined with strategic species selection and tree planting standards can help to
minimize salt leakage and soil contamination.
Abiotic stressors on trees and tree management within such conditions are
considered in urban forest management plans and actions in many Canadian cities
[see chapter: Urban Forest Management Planning]. Well-planned management that
includes regular maintenance activities, such as pruning, watering during dry periods,
and monitoring tree health, is essential for managing the cumulative impacts of
abiotic stresses. By implementing best management practices in urban forestry,
Canadian cities can ensure that their urban forests continue to provide ecological,
social, and economic bene�ts for a longtime.
Resources
Government of Canada. (2013). Understanding and dealing with interactions between trees, sensitive clay
soils and foundations: NH18-24/31-2005E-PDF - Government of Canada Publications - Canada.ca.
https://publications.gc.ca/site/eng/405406/publication.html
Canadian National
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Government of Canada. (2015). Road salt injury.
https://tidcf.nrcan.gc.ca/en/diseases/factsheet/49
Transportation Association of Canada (TAC). (2024). Syntheses of Best Practices – Road Salt
Management: 1.0 Salt Management Plans (2013) | Transportation Association of Canada (TAC).
Transportation Association of Canada (TAC) |.
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Saddle Hills County. (n.d.). Drought & Trees - Impact, care, and maintenance.
https://www.saddlehills.ab.ca/news/posts/drought-trees-impact-care-and-maintenance/
Bellis, E. (2023). Recommendations to improve the health of Vancouver's street trees surrounded by
hardscape. University of British Columbia.
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Government of Manitoba. (2016). Manitoba Drought Management Strategy.
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City of Toronto (2017). Mechanical injuries & other threats. City of Toronto.
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injuries-and-other-threats/
Credit Valley Conservation. (2022). Urban Tolerant Trees - Credit Valley Conservation.
https://cvc.ca/the-garden-post/urban-tolerant-trees/
Government of Ontario. (n.d.). Weather risks: strategies to mitigate the risk of insu�cient moisture.
ontario.ca.
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Bassuk, N., Curtis, D. F., Marranca, B. Z., and Neal, B. (2009). Recommended Urban Trees: Site Assessment
Canadian Provincial
Alberta
British Colombia
Manitoba
Ontario
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and Tree Selection for Stress Tolerance. Cornell University Department of Horticulture, Ithaca.
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Davey Tree Expert Company. (2022). Symptoms Of Tree Stress (Plus Treatment). Davey.
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Duiker, S. W. (2005). Effects of soil compaction.
https://extension.psu.edu/effects-of-soil-compaction
Feeley, T. (n.d.). Stress is a Tree Killer.
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Fite, K. (n.d.). Simple steps to aid stressed trees. Bartlett Tree Experts.
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Minnesota Pollution Control Agency. (2022). Environmental impacts of road salt and other deicing
chemicals - Minnesota Stormwater Manual.
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icing_chemicals
Moore, G. (2023,). Polluted trees: Pollutants and Street Tree Health. Treenet.
https://treenet.org/resource/pollutants-and-street-tree-health/
Percivel, G.C. (2017). Abiotic Stress. Routledge Handbook of Urban Forestry, 1, 237-250. ISBN
9781315627106
University of Massachusetts Amherst. (2011). Helping trees to manage stress. Center for Agriculture,
Food, and the Environment.
https://ag.umass.edu/fact-sheets/helping-trees-to-manage-stress
University of Minnesota. (2018). Soil compaction. UMN Extension.
https://extension.umn.edu/soil-management-and-health/soil-compaction
Vogt, S. (2021). Tree stress - Dyck Arboretum. Dyck Arboretum.
https://dyckarboretum.org/tree-stress/
Aristizabal, C., & Isabel, M. (2021). Identi�cation of the most damaging environmental pressures for the
urban trees of the northeast of North America: a Delphi approach - Dépôt institutionnel de l'UQO. Université
du Québec À Montréal.
https://di.uqo.ca/id/eprint/1330/
Carol-Aristizabal, M., Dupras, J., Messier, C., & Sousa-Silva, R. (2023). Which tree species best withstand
urban stressors? Ask the experts. Arboriculture & Urban Forestry, 50(1), 57-75.
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Collins, D. J. (2007). Biotic and abiotic stressors of the urban forest. The Journal of Horticultural Science
and Biotechnology, 82(6), 1.
Further Reading
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https://doi.org/10.1080/14620316.2007.11512312
Cushing, S. P . (2009). Urban tree selection based on environmental stresses and plant responses:
development of a selection guide.
https://atrium.lib.uoguelph.ca/items/660d70c5-29f0-4a91-ba6f-a8764a00659b
Dale, A. G., & Frank, S. D. (2022). Water availability determines tree growth and physiological response to
biotic and abiotic stress in a temperate North American urban forest. Forests, 13(7), 1012.
https://doi.org/10.3390/f13071012
De Frenne, P ., Cougnon, M., Janssens, G. P . J., & Vangansbeke, P . (2022). Nutrient fertilization by dogs in
peri-urban ecosystems. Ecological Solutions and Evidence, 3(1).
https://doi.org/10.1002/2688-8319.12128
Duinker, P . N., Ordóñez, C., Steenberg, J. W. N., Miller, K. H., Toni, S. A., & Nitoslawski, S. A. (2015). Trees
in Canadian cities: indispensable life form for urban sustainability. Sustainability, 7(6), 7379–7396.
https://doi.org/10.3390/su7067379
Egerer, M., Schmack, J.M., Vega, K., Ordóñez-Barona, C., and Raum, S. (2024). The challenges of urban
street trees and how to overcome them. Frontiers in Sustainable Cities, 6.
https://www-frontiersin-org.myaccess.library.utoronto.ca/journals/sustainable-cities/articles/10.3389/
frsc.2024.1394056/full
Equiza, M., Calvo-Polanco, M. M., Cirelli, D., Señorans, J., Wartenbe, M., Saunders, C., & Zwiazek, J.
(2017). Long-term impact of road salt (NaCl) on soil and urban trees in Edmonton, Canada. Urban
Forestry & Urban Greening, 21, 16–28.
https://doi.org/10.1016/j.ufug.2016.11.003
Fraedrich, B. R. (n.d.). Preventing Construction Damage to Trees – Research Laboratory Technical Report.
Bartlett Tree Experts.
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Grote, R., Samson, R., Alonso, R., Amorim, J. H., Carinanos, P ., Churkina, G., Fares, S., Thiec, D. L.,
Niinemets, U., Mikkelsen, T. N., Paoletti, E., Tiwary, A., & Calfapietra, C. (2016). Functional traits of urban
trees: air pollution mitigation potential. Frontiers in Ecology and the Environment, 14(10), 543–550.
https://doi.org/10.1002/fee.1426
Hauer, R. J., Wei, H., Koeser, A. K., & Dawson, J. O. (2021). Gas Exchange, Water Use E�ciency, and
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Ordóñez, C., Jr., Sabetski, V., Millward, A. A., Steenberg, J. W. N., Grant, A., & Urban, J. (2018). The
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Insects and Diseases
Trees in urban environments face signi�cant abiotic and climate change-related
stresses, which make them particularly vulnerable to insects and diseases (Climate
Atlas of Canada, n.d.). As climate change leads to warmer temperatures and drier
conditions, the susceptibility of urban forests to these threats is expected to increase
[see chapter: Air Quality and Climate Change]. While many native insect species
contribute positively to urban biodiversity and ecosystems, some native and non-
native insects can cause severe damage to urban forests. They can defoliate trees,
suck sap, bore into bark, carry diseases, weaken trees, and lead to tree death and
costly management consequences.
Forest insects and diseases in Canada can be classi�ed into three broad categories:
native, alien, and invasive species (NRCan, 2023). Invasive species, whether native or
alien, are species that spread beyond their known usual range and that are capable of
causing environmental and/or economic damage. The mountain pine beetle, which
has extended its range from British Columbia to Alberta, exempli�es a native insect
behaving invasively (NRCan, 2024a). Native species outbreaks occur periodically and
can be severe (e.g., spruce budworm (Choristoneura fumiferana), mountain pine
beetle (Dendroctonus ponderosae)). Alien insects have been introduced into Canada
and often become pests, invading new hosts and ecosystems. Notable examples are
the emerald ash borer (Agrilus planipennis), which has signi�cantly impacted
Highlights
Key definitions
Native, alien, and invasive species.
Impacts
Negative effects of invasive insect pests and diseases.
Management and mitigation
Monitoring, cultural practices, biological and chemical controls, public education,
and biodiversity conservation.
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populations of Ash trees (Fraxinus spp). Beetle species primarily spread Dutch Elm
Disease (DED). DED, which includes fungal pathogens (Ophiostoma novo-ulmi, a more
aggressive strain, and Ophiostoma ulmi), has already devastated elm trees (Ulmus
spp) in Eastern North America and poses a threat to elms across Canada
(Government of Saskatchewan, n.d.).
Pests and diseases cause economic and ecological damage and affect the social
fabric of communities by altering landscapes and reducing the aesthetic value of
urban areas. Effective management and mitigation strategies, including monitoring,
cultural practices, biological and chemical controls, public education, and promoting
diversity, are essential to protect these valuable urban forests and ensure their
continued contribution to the health and well-being of Canadian cities.
Insects
Historically, Canadian cities have faced signi�cant challenges from various insects
and diseases that have had profound economic and environmental impacts. The
Emerald Ash Borer (EAB), �rst detected in Canada in 2002, is one of the most
destructive pests in North America. It has killed millions of ash trees across Ontario,
Quebec, and other regions, causing substantial economic losses (NRCan, 2024b)
[see chapter: Economic Value and Appraisal of Trees]. For example, Windsor, Ontario
had to remove over 10,000 ash trees, drastically altering the urban landscape and
increasing municipal management costs (Arnberger et al., 2017). The City of
Montreal has also faced severe impacts, with large-scale tree removals disrupting
recreational areas and incurring high costs for tree treatment, replacement, and
removal, highlighting broader social and economic impacts of pest infestations (Ville
de Montreal, 2023). The economic impact of the EAB alone is expected to cost
Canadian municipalities $2 billion in treatment, tree replacement, and removal over
the coming decades (NRCan, 2018; Vogt, Hauer & Fischer, 2015).
The Asian Longhorned Beetle (ALB) (Anoplophora glabripennis), detected in Toronto
in 2003, poses a signi�cant threat to hardwood trees in urban areas (Haak et al.,
2009). It kills trees by boring into their trunks and branches, leading to structural
failure. Efforts to eradicate the beetle in Toronto have involved the removal of over
25,000 trees, affecting local biodiversity and the aesthetic value of green spaces
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(Wilson and Smith, 2017). These ALB populations have been successfully eradicated
(NRCan, 2024a).
The Spongy Moth (Lymantria dispar) is another pest that defoliates various tree
species, weakening them and making them susceptible to other stresses. In 2020,
southern Ontario experienced one of the largest spongy moth outbreaks, leading to
signi�cant defoliation and stress on Oak (Quercus spp), Maple (Acer spp), and other
tree species (Invasive Species Centre, 2024b). The Woolly Adelgid (Adelges tsugae),
an invasive insect, threatens forests in eastern Canada and remnants of native
forests in urban areas. It feeds on hemlock trees (Tsuga canadeanis ), causing them
to decline and eventually die, which could have cascading effects on forest
ecosystems (Dreistadt, Dahlsten & Frankie, 1990).
Diseases
The Dutch Elm Disease (DED), introduced to Canada in the mid-20th century,
devastated elm populations across the east and continues to spread across the
country (Government of Saskatchewan, n.d.). Winnipeg, known as the "City of Elms,"
has lost thousands of elms to this fungal disease. The loss of these trees has not
only reduced urban canopy cover but has also affected the aesthetic and cultural
value of the city (Hildahl, 1977). Chestnut Blight, caused by Cryphonectria parasitica, a
fungus introduced from Asia, has eradicated native chestnut trees (genus Castanea)
throughout the Carolinian zone. This has reduced biodiversity, changed forest
communities, and impacted wildlife that once relied on chestnuts as a food source.
Tree diseases also impact the Canadian economy, particularly in regions where these
species are abundant (Invasive Species Centre, 2024a).
Although not yet widespread in Canada, Sudden Oak Death (SOD), caused by the
invasive pathogen water mold (Phytophthora ramorum), poses a signi�cant threat to
Canadian urban forests. The potential introduction of SOD could lead to widespread
oak tree mortality, signi�cantly altering the landscape and biodiversity of urban
forests in Canadian cities (Braddy, 2023). Another emerging threat recently detected
in Ontario, Oak Wilt, is a fungal disease caused by Ceratocystic fagacearum that
blocks the water-conducting vessels of oak trees, causing them to wilt and die.
These diseases have the potential to cause widespread oak tree mortality,
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highlighting the need for thorough monitoring and rapid response strategies (Forest
Pathology, 2024).
Management and Mitigation Strategies
The decline of native tree species across Canada due to pests and diseases has had
many negative impacts and signi�cant impacts on forests, biodiversity, ecological
functions, and the Canadian economy. The decline of species populations like the
American chestnut, black ash (Fraxainus nigra), and hemlock contributes to the loss
of genetic diversity of urban forests, making them more vulnerable to future threats.
Managing the impact of invasive species is costly ecologically and economically.
Ecological cost is the loss of species, biodiversity, habitat, and ecological and cultural
functions, while the economic cost of dealing with the impact, managing the impacts,
and loss of ecological services is also signi�cant (Crystal-Ornelas et al., 2021). For
example, municipalities and conservation groups in Ontario spend approximately
$50.8 million annually on managing invasive species (Invasive Species Centre, 2023).
The cost of dealing with EAB's impact and management in urban streets could reach
around $1.38 billion by 2035 (Hope et al., 2020).
The management and mitigation of insect and disease infestations in Canadian
urban forests require a comprehensive approach that includes monitoring, cultural
practices, biological and chemical controls, public education, and promoting diversity
(Hotte et al., 2015). Monitoring and Early Detection is one method that employs
regular inspections and the use of traps, which are crucial for the early detection of
pests and rapid intervention. This approach has been effective in managing pests like
the ALB and EAB in Toronto and Montreal (NRCan, 2018; Ville to Montreal, 2023), as
early detection and eradication stopped the spread of the invasive insect. The use of
natural predators (biological control) and the judicious application of insecticides
(chemical control) can also help manage pest populations. For example, Montreal's
response to the EAB has included a combination of tree removal, biological controls,
and public education to limit the spread (Les Amis de la Montagne, 2022).
Urban forest management plans for Canadian cities have recognized invasive
species issues, preventing and managing their impact. For example, the City of
Calgary’s strategic management plan incorporates several invasive species
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strategies: early detection and response, research and development of new
eradication strategies, inventorying, prevention, community outreach, and integrated
weed management that uses biological, chemical and cultural control methods to
eliminate or prevent priority invasive species (City of Calgary, 2020). Additionally, the
plan recognizes that maintaining tree health through proper watering, mulching,
pruning, and other cultural practices increases tree resilience against pests and
diseases [see chapter: Tree Maintenance].
Removing and properly disposing of infected or infested trees and plant materials are
vital to preventing the spread of pests and diseases. Federal quarantines and local
initiatives, such as the "ash-free" zone in southwestern Ontario, have been slowing
the spread of pests like the EAB (NRCan, 2018; MacFarlane and Meyer, 2005).
Raising awareness about urban forest health and involving the community in
monitoring efforts are also essential for effective pest and disease management.
Public education campaigns in cities like Montreal and Toronto have been critical in
controlling the spread of pests like the EAB and ALB (Les Amis de la Montagne,
2018). The Ontario Ministry of Agriculture, Food and Rural Affairs also emphasizes
integrated pest management practices that focus on prevention and cultural
methods (OMAFRA, 2012). Finally, promoting species and genetic diversity in urban
forests reduces the risk of widespread damage from any single pest or disease. This
strategy is important for mitigating the effects of invasive species like the spongy
moth and sudden oak death, but also for other tree species and urban forest
management in general (Braddy, 2023).
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Sharpe, S., Stephens, E., Hervet, V., Aboukhaddour, R., & Vankosky, M. (2021). We stand on guard for thee:
A brief history of pest surveillance on the Canadian Prairies. Crop Protection, 149, 105748.
https://doi.org/10.1016/j.cropro.2021.105748
Ontario Ministry of Agriculture, Food and Rural Affairs. (2022). Integrated pest management and
protecting natural enemies and pollinators.
https://www.ontario.ca/�les/2022-10/omafra-agronomy-guide-for-�eld-crops-chapter-14-
en-2022-10-13.pdf
Paap, T., Burgess, T. I., & Wing�eld, M. J. (2017). Urban trees: bridge-heads for forest pest invasions and
sentinels for early detection. Biological Invasions, 19(12), 3515–3526.
https://doi.org/10.1007/s10530-017-1595-x
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to North America’s ash resource. Journal of Forestry, 104(3), 118–124.
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Invasive Plant Species
Invasive plant species pose a signi�cant threat to urban forests across Canada,
impacting biodiversity, ecosystem health, ecological functions and services of green
spaces and natural urban areas while also causing signi�cant economic impact.
According to the 2021 national survey led by the Invasive Species Council, Canadian
municipalities estimated annual expenditures on invasive plant species ranged from
$95.8 million to $400 million (Vyn & Invasive Species Centre, 2022). Effective and
integrated prevention and management of invasive plant species is crucial to
maintaining the integrity and resilience of urban forests to ensure biodiversity
conservation and a steady �ow of economic and ecological bene�ts provided by
urban forests.
Due to the history of land use change (e.g., previously agricultural land or disturbed
land converted to urban), the introduction of, and preferences for introduced plant
species, urban areas tend to have numerous non-native plants, some of which are
invasive. The introduced invasive species are either planted or spontaneously
established across various land uses, threatening the biodiversity of natural areas.
For example, some invasive plants such as Japanese knotweed (Reynoutria japonica),
Garlic mustard (Alliaria petiolata), Dog-strangling vine (Vincetoxicum rossicum),
European buckthorn (Rhamnus cathartica), Himalayan blackberry (Rubus armeniacus),
and Tree of heaven (Ailanthus altissima) proliferate through urban areas,
monopolizing natural areas while outcompeting native �ora and disrupting local
Highlights
Impacts
Negative impacts of invasive plants and examples from urban forests in Canada.
Management
Chemical, physical, and biological control methods.
Monitoring
Detecting, slowing, and stopping invasive spread.
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ecosystems and ecological functions (City of Toronto, 2013; Ministry of Forests,
2024; Ontario's Invading Species Awareness Program, n.d.; Stanley Park Ecology
Society, 2013; Saskatchewan Invasive Species Council, n.d.).
Invasive plant species often alter soil biological properties (e.g., mycorrhizal
properties), chemistry, and nutrient availability, which hinders the establishment of
native species, promoting further expansion and establishment of invasive plants
(Ehrenfeld, 2003; Kourtev et al., 2002). Invasive plants modify vegetation
composition, growing conditions, and light conditions, and decrease water availability
for native plants, making environments less hospitable for native species (Lamarque
et al., 2011). Another risk from invasive plants involves the possibility of them
hybridizing with native plants and eventually eliminating native genetic potential
(Mooney & Cleland, 2001). These cumulative impacts ultimately change the
composition and structure of natural vegetation in urban areas (Delavaux et al.,
2023). It has been shown that non-native, invasive trees reduce the diversity of native
insects and could facilitate the spread of non-native pests (Branco et al., 2019).
Moreover, invasive plant species can signi�cantly change ecosystem functions and
negatively impact human health (Vila et al., 2011).
Some of the planted or self-established trees in Canadian cities are also listed as
invasives and include: Black Locust (Robinia pseudoacacia), European black alder
(Alnus incana), White mulberry (Morus alba), Scots pine (Pinus sylvestris), Norway
maple (Acer platanoides), Manitoba maple (Acer negundo), Tree of heaven (Ailanthus
altissima), Autumn olive (Elaeagnus umbellata), Japanese barberry (Berberis
thunbergii), and European buckthorn (Rhamnus cathartica). However, many other
invasive trees, shrubs, and grasses occur in Canadian urban areas and pose a threat
to natural ecosystems.
Managing Invasive Plant Species in Urban Forests
Invasive species management is multifaceted and includes various tools and
methods ranging from policy, control, and eradication measures to public education
and prevention actions. In Canada, different levels of government have introduced
weed and/or invasive species control legislation prohibiting plant introduction and
distribution. At the national level, provincial control measures with federal regulations
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can be adopted to control the spread of invasive species in Canada (Government of
Canada & Environment and Climate Change Canada (ECCC), 2024; Sherman &
Ontario Invasive Plant Council, 2015). For example, the government of Ontario
prohibits and restricts the import, possession, transport, or release of 42 invasive
species under the Invasive Species Act (Government of Ontario, 2023). Not all
invasive species have the same impact; a few species cause most of the damage. In
British Columbia, six invasive species alone caused an estimated $65 million in
damage in 2008 (Invasive Species Council of British Columbia, 2024b).
Invasive Plants Control
The control and eradication of invasive plant species range from mechanical and
chemical techniques to burning, �ooding, biological control, and other control
methods. Mechanical removal methods such as hand-pulling, mowing, and cutting
can effectively manage small infestations. More recently, controlled goat grazing has
been used to manage invasive species in natural areas (Rathfon, 2021; City of
Mississauga, 2021).
Herbicides and other chemical controls may also be used selectively to control
invasive species, mainly when mechanical methods are impractical. However, the
application of these chemicals must comply with local regulations and be conducted
by certi�ed professionals (Invasive Species Centre, 2021; Wisconsin Department of
Natural Resources, n.d.). Also, the use of certain chemicals to control weeds and
invasive plants has been forbidden by many municipalities across Canada (The
Ontario Pesticides Act, 2024; City of Vancouver, n.d.; Health Canada, 2024).
Biological control methods are also used to introduce natural predators or pathogens
speci�c to the invasive species to manage its populations. This approach requires
research and careful ecological risk assessment to avoid unintended ecological
impacts (Invasive Species Centre, 2021). For example, after conducting over a
decade of testing, the Canadian Food Inspection Agency, as part of a larger
integrated management strategy for invasive Phragmites (Phragmites australis),
approved the release of two stem-boring moths (Archanara neurica and Lenisa
geminipuncta) to control the spread of this species. Phragmites is one of Canada's
most disruptive invasive species (Ducks Unlimited Canada, 2024) that has been
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threatening wetlands' biodiversity, but has also been rapidly spreading along roads,
including urban areas. However, biocontrol measures alone are not enough to
eradicate invasive phragmites. They are expected to gradually reduce species
dominance and habitat disturbances, allowing native plants and animals to recover
(Ducks Unlimited Canada, 2024).
Early Detection and Rapid Response
Early identi�cation and control of invasive species is another essential tool that is
based on regular monitoring and community reporting of invasive plant observations.
One such approach is early detection and rapid response (EDRR) of invasive species.
In British Columbia, for instance, EDRR activities are conducted in partnership with
the Canadian Food Inspection Agency and involve key land managers and
stakeholders across B.C. and neighbouring regions (British Columbia Inter-Ministry
Invasive Species Working Group (IMISWG), 2014). Moreover, invasive species
monitoring and management through remote sensing, drone-based imaging, and
data processing and analysis have emerged as practical solutions to map and detect
large plant invasions in urban forests (Singh et al., 2024).
Education
Educating the community about the impacts of invasive species and encouraging the
use of native plants in landscaping can signi�cantly aid in prevention and control
efforts. Across Canada, different levels of government, non-pro�t organizations,
regional groups, and conservation authorities have been educating the public and
eradicating or preventing invasive plants from spreading in urban areas (Government
of Alberta, 2014; Invasive Species Council of British Columbia, 2024). These groups
often initiate and engage in developing invasive species strategic management plans
and best management practices (BMPs), as part of urban forest management
(Ontario Invasive Plant Council, 2024). Community members and the public are also
actively involved in controlling invasive species and removing them from natural
areas. Examples of community efforts in coordination with municipalities, NGOs, or
on their own exist from the east to the west coast (Invasive Species Centre, 2024).
Collaborative efforts between municipalities and academia and the continuous
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adaptation of best management practices based on current research and local
conditions also enhance invasive species control effectiveness and contribute to
urban forest sustainability (Sherman & Ontario Invasive Plant Council, 2015).
Municipalities have integrated invasive plant management strategies into their urban
forest management plans to preserve the ecological health and resilience of urban
green spaces and natural areas (City of Toronto, 2024a; Government of Alberta, 2024;
Patterson, 2015). Many municipalities started prioritizing planting native and non-
invasive and introduced tree species to lead by example and stop the spread of
invasive species (Patterson, 2015). However, some invasive species, such as Norway
maple (Acer platanoides), are still planted and produced by tree nurseries.
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Danyluk, A., Clement, E., & Houghton, K. (2016). Delta’s Invasive Species Strategy: A framework.
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https://pub-trca.escribemeetings.com/�lestream.ashx?DocumentId=6533
Government of Prince Edward Island. (2023). Weed Control Act, W-2.1.
https://www.princeedwardisland.ca/en/legislation/weed-control-act
Government of Prince Edward Island. (2023). Invasive Plant and Animal Species.
https://www.princeedwardisland.ca/en/information/environment-energy-and-climate-action/invasive-
plant-and-animal-species
Prince Edward Island Invasive Species Council. (2021). PEI Invasive Species Council – Home.
https://peiinvasives.com
Conseil régional de l'environnement de Laval. (n.d.). Invasive exotic species.
https://www.credelaval.qc.ca/en/alien-invasive-species
Fédération interdisciplinaire de l’horticulture ornementale du Québec (FIHOQ). (n.d.). Faites la lutte aux
plantes envahissantes. Plantes Envahissantes.
https://plantesenvahissantes.org/
Ville de Baie-D'Urfé. (n.d.). Invasive species.
https://www.baie-durfe.qc.ca/en/our-departments/page/invasive-species
Ville de Sherbrooke. (n.d.). Invasive and undesirable species.
https://www.sherbrooke.ca/en/population-services/environment/natural-areas-and-biodiversity/
invasive-and-undesirable-species
Battle River Watershed Alliance (BRWA). (2017). Non-native and Invasive Species Management in the
Battle River and Sounding Creek Watersheds. BRWA Planning Document, 66 pages.
https://www.battleriverwatershed.ca/wp-content/uploads/2018/08/BRWA-Non-native-and-Invasive-
Species-Report-2017.pdf
Government of Saskatchewan. (2020). Weed Control Act, W-11.1.
https://publications.saskatchewan.ca/#/products/31364
Saskatchewan Invasive Species Council. (n.d.). Facilitating action against invasive species in
Saskatchewan. SISC.
https://www.saskinvasives.ca/
Prince Edward Island
Quebec
Saskatchewan
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Yukon Invasive Species Council, Yukon Environmental and Socio-economic Assessment Board. (n.d.).
YESAB Assessments: Toolkit for identifying and mitigating risks related to terrestrial invasive species.
https://www.yukoninvasives.com/~documents/resources/reports/yesab-invasive-species-toolkit/?
layout=default
Yukon Invasive Species Council. (2024). Invasive Plants - Yukon Invasive Species Council.
https://www.yukoninvasives.com/invasive-species/plants/
Yukon Invasive Species Council. (2023). Invasive Species Best Practices Brochures.
https://www.yukoninvasives.com/best-practices/
EDD Maps, University of Georgia. (n.d.). Species Listing – Federal Noxious Weeds.
https://www.eddmaps.org/lists/list.cfm?id=16
New York Invasive Species (IS) Information. (n.d.). Best Management Practices – New York Invasive
Species Information.
https://nyis.info/best-management-practices/
Patterson, M. (2015). Gwinnett County Parks and Recreation Invasive Plant Species Management Plan.
Oregon State University College of Forestry.
https://studylib.net/doc/11184508/invasive-plant-species-management-plan
The Nature Conservancy's Adirondack Park Invasive Plant Program. (2020). Invasive Species Best
Management Practices.
https://www.adkinvasives.com/data/�les/Documents/APIPP-BMPs-Feb-2019.pdf
U.S. Department of Agriculture (USDA). (2012). Non-native Invasive Species Best Management Practices
Guidance for the U.S. Forest Service Eastern Region.
https://www.fs.usda.gov/Internet/FSE_DOCUMENTS/stelprdb5412628.pdf
Wisconsin Council on Forestry. (n.d.). Invasive Species Best Management Practices: Urban Forestry.
Wisconsin Department of Natural Resources (DNR).
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Wisconsin Council on Forestry. (2009). Best management practices for preventing the introduction and
spread of invasive species.
https://councilonforestry.wi.gov/Documents/InvasiveSpecies/UF-BMP-
ConsolidatedManual_090811.pdf
Aoshana, A. (2021). Invasive Plant Management for Stewardship of Naturalized Urban Forests. (Master
Yukon
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in Forest Conservation (MFC) Student Research Project), University of Toronto, TSpace Repository.
http://hdl.handle.net/1807/104164
Delavaux, C. S., Crowther, T. W., Zohner, C. M., Robmann, N. M., Lauber, T., van den Hoogen, J., Maynard,
D. S. (2023). Native diversity buffers against severity of non-native tree invasions. Nature, 621(7980),
773-781.
https://doi.org/10.1038/s41586-023-06440-7
Derickx, L., & Antunes, P . (2013). A Guide to the Identi�cation and Control of Exotic Invasive Species in
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Id%20&%20Control%20of%20Exotic%20Invasive%20species%20in%20Ont.%20SRI-2013.pdf
DiTommaso, A., Lawlor, F. M., & Darbyshire, S. J. (2005). The Biology of Invasive Alien Plants in Canada.
2. Cynanchum rossicum (Kleopow) Borhidi [= Vincetoxicum rossicum (Kleopow) Barbar.] and
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Lapointe, M., & Brisson, J. (2012). A Comparison of Invasive Acer platanoides and Native A. saccharum
First-Year Seedlings: Growth, Biomass Distribution and the In�uence of Ecological Factors in a Forest
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e13361.
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Fire and the Urban-Rural Interface
Forest �res in the boreal forests of Canada are a natural disturbance that drives
vegetation dynamics by increasing the diversity of trees and vegetation. However,
over the last few decades, the frequency, intensity, and severity of wildland �res have
been increasing due to a con�uence of factors. Common forestry practices of �re
suppression have led to a sizable accumulation of dead wood and debris, as there
are no natural �re regimes to reduce debris buildup (Stocks & Martell, 2016). The
increased fuel load allows �res to reach higher into the canopy and burn much hotter.
These conditions are compounded by anthropogenic climate change, which has led
to drier and longer summers that create an ideal environment for intense and
sustained �res. Some Canadian urban and Indigenous communities have traditionally
been embedded within forested landscapes, while some new urban areas have also
expanded into these areas. These urban-rural interfaces are at risk of experiencing
forest �res as �re intensity and frequency increase in Canada.
While wild�res occur year-round, the �re season in Canada is generally concentrated
from May to September. For Canada, 2023 was the most destructive wild�re year on
record. In June 2023, more land was burned in Quebec than in the last 20 years
combined (Natural Resources Canada, 2024). The impacts of severe wild�res extend
beyond the loss of forests. They destroy communities, displace people, tear down
buildings, and displace large groups of people from their homes. Additionally, wild�re
Highlights
Urban-rural interface
Impacts of wild�res on communities within the interface.
Fire management
How Canadian municipalities are working to prevent and mitigate wild�re impacts
at small and large scales.
Indigenous communities and fire
Traditional/cultural burning practices.
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weather and smoke can extend well beyond the wild�re area and have long-lasting
human health impacts (UNDRR, 2024).
Fires can also severely impact urban forests by destroying large numbers of trees
and green spaces, reducing overall tree canopy and forest diversity. Such impacts
leave communities within this interface with little to no tree canopy cover. The severe
reduction in canopy cover can intensify summer heat and exacerbate heat-related
issues associated with urban heat islands. Tree loss in urban areas also impacts
wildlife and plant species that rely on them for food and shelter, while simultaneously
decreasing the aesthetic appeal and recreational value of these communities.
Additionally, the sudden and large-scale tree canopy losses have long-term
implications for community resilience and environmental health. The recovery
process requires subsequent tree replanting and forest restoration efforts in urban
areas, which can be a costly and time-consuming process.
Fire Management
Fire management involves appropriate forest management techniques, public
education, and updating landscape management plans and methods at the individual
and community level. Individuals in high-risk areas can reduce �re risk to dwellings
by clearing �ammable materials around the home, creating �re breaks at the building
scale, and incorporating �re-resistant material into building construction. Studies
have shown that many buildings catch �re through embers landing on or near the
property and spreading out to another adjacent dwelling (BC Wild�re Service, n.d.),
and it is common for wind to carry embers hundreds of meters away (Partners in
Protection, 2003). As such, maintaining a clean gutter, removing wood piles from the
property, and creating a �re break between wooden structures and the house can
reduce the chances of ignition. For instance, decks attached to houses and wood
furniture can be sources of ignition. Choosing �re-resistant plant species, clearing
low branches of adjacent trees to prevent crown �res, and clearing plant debris help
to reduce the chance of �re spreading (Beverly et al., 2020). These preventative
measures can reduce the risk of dwellings catching on �re and reduce �re spread
through communities.
On a community or regional level, larger-scale initiatives such as conducting a
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wild�re assessment, identifying factors that increase the risk of wild�re in the urban
area, and carrying out plans to reduce this risk can better prepare communities for
the annual �re season. A review of studies in the Paci�c Northwest has shown that a
combination of forest thinning and burning is the most effective at decreasing �re
severity (Copes-Gerbitz et al., 2022). Thinning lower branches helps to deter the
upward spread of �res into the canopy and the spread of �re through the canopy.
However, thinning alone has been documented to increase the severity of �res as the
overall fuel load at ground level has increased; therefore, a combination of thinning
and surface treatments makes the most signi�cant difference, whether prescribed
burning or pile burning, in decreasing the intensity of future �res (Davis et al., 2024).
Post-treatment wildland �res are less intense and show higher tree survival rates
(Davis et al., 2024). These managed landscapes are also easier for �re control
personnel to traverse, leading to more effective control of wildland �res (Davis et al.,
2024). Over time, treatment effectiveness declines, making long-term forest �re
management crucial.
Fire and Indigenous Communities
Over the past decades, wild�res with the most extreme intensity and spread have
often happened in remote areas of Canada. As a result, smaller towns and
Indigenous communities have been disproportionately impacted by wild�res. Smaller
towns and Indigenous communities have fewer resources and are less likely to have
a developed community wild�re plan (Copes-Gerbitz et al., 2022). Even though
Indigenous communities are actively concerned about wild�re risks to wildlife, water
quality, and biodiversity, unequal access to �re prevention resources is a systemic
barrier that must be overcome to reduce the impact of wild�re (Copes-Gerbitz et al.,
2022). Compared to larger municipal and regional districts, Indigenous groups also
have a more limited social capacity and have been historically excluded from the
planning process; therefore, they often cannot take advantage of government-
sponsored programs. Outreach and community-centered approaches should be
considered in implementing wild�re prevention plans, and traditional knowledge from
Indigenous communities should be included in the discussions (Government of
British Columbia, 2022).
Prescribed Burns
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Indigenous people have historically used �re to manage the land and sustain their
culture, values, and practices, but modern �re suppression forest management
techniques have often prevented these cultural prescribed burns in many areas of
Canada (Lambert, 2021; FireSmart Canada, 2022; FireSmart Canada, 2024). This
absence of �re on the landscape results in a loss of biodiversity – remnants of native
prairie-savannah ecosystems found in Canadian cities (City of Toronto, 2002; District
of Saanich, 2023) are testimony to this. Prairie-savannah ecosystems are one of
Canada's most threatened vegetation and habitat types due to land conversion and
the absence of �re. Prescribed burns help to manage these ecosystems in cities and
maintain their biodiversity. Controlled �res help remove dead vegetation, control
invasive species, and recycle nutrients back into the soil to prompt the growth of
native grasses and wild�owers. For example, with a better understanding of �re
ecology, the City of Toronto introduced annual prescribed burns to maintain the
native black oak savannah in one of the most iconic city parks: High Park. The
practice started in 2000 and has continued every year since. The annual prescribed
burn resulted in many positive ecological and social bene�ts, which include public
education and the incorporation of traditional knowledge and practice into managing
vegetation in urban areas (Martin, 2024; Prescribed Fire, n.d.).
Resources
Canadian Climate Institute. (2024). Fact Sheet: Climate change and wild�res.
https://climateinstitute.ca/wp-content/uploads/2024/07/Fact-sheet_-Wild�res-�nal.pdf
Climate Action Against Disinformation (CAAD). (2024). Flame Wards: Misinformation and Wild�re in
Canada’s Climate Conversation.
https://caad.info/wp-content/uploads/2024/06/2024-Final-REPORT%E2%80%93Wild�re-
Misinformation-01d-2.pdf
Climate Atlas of Canada. (n.d.) Forest Fires and Climate Change. Prairie Climate Centre.
https://climateatlas.ca/forest-�res-and-climate-change
FireSmart Canada. (2022). FireSmart Guide to Landscaping – Second edition (24p).
https://�resmartcanada.ca/wp-content/uploads/2022/01/328254-PIP-Landscape-low-res.pdf
FireSmart Canada. (2024). Blazing the Trail: Celebrating Indigenous Fire Stewardship (47p).
https://�resmartcanada.ca/wp-content/uploads/2024/06/Booklet_Blazing-the-Trail_Web-version.pdf
FireSmoke Canada. (2021). Smoke Forecasts.
Canadian National
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https://�resmoke.ca/
Government of Canada. (2024). Prepare for wild�res.
https://www.getprepared.gc.ca/cnt/hzd/wldfrs-en.aspx
Internal Displacement Monitoring Centre (IDMC). (2024). Canada - Record wild�res spread to urban areas.
https://www.internal-displacement.org/spotlights/canada-record-wild�res-spread-to-urban-areas/
Natural Resources Canada. (2025). Canadian Wildland Fire Information System.
https://cw�s.cfs.nrcan.gc.ca/home
Natural Resources Canada. (2024). Canada’s record-breaking wild�res in 2023: A �ery wake-up call.
Government of Canada.
https://natural-resources.canada.ca/simply-science/canadas-record-breaking-wild�res-2023-�ery-
wake-call/25303
Partners in Protection. (2003). (rep.). FireSmart: Protecting Your Community from Wild�re.
https://www.�resmartcanada.ca/wp-content/uploads/2018/10/FireSmart-Protecting-Your-
Community.pdf.
Prescribed Fire. (n.d.). Cultural Burning and Prescribed Fire.
https://prescribed�re.ca/cultural-burning/
Province of Alberta. (2024). 2024 Alberta Wildland Urban Interface Guidelines. Ministry of Forestry and
Parks.
https://open.alberta.ca/dataset/238797a1-ef97-40aa-a0b0-ac9ca76aaa53/resource/6aef5441-
d183-45e8-8a6b-4fc8d1a66cb6/download/pses-alberta-wildland-urban-interface-guidelines-2024.pdf
FireSmart Canada. (n.d.). Alberta FireSmart – Resources.
https://�resmartalberta.ca/resources/
BC Wild�re Service. (n.d.). (rep.). Firesmart Begins at Home Manual: Reduce the Potential Impacts of
Wild�re on Your Home.
https://www2.gov.bc.ca/assets/gov/public-safety-and-emergency-services/wild�re-status/prevention/
prevention-home-community/bcws_homeowner_�resmart_manual.pdf
District of Saanich. (2023). (rep.). State of Biodiversity Report.
https://www.saanich.ca/assets/Parks~Recreation~and~Community~Services/Documents/
State%20of%20Biodiversity%20Report%20-%20FINAL.pdf
Government of British Columbia. (2022). How cultural burning enhances landscapes and lives.
Canadian Provincial
Alberta
British Colombia
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https://blog.gov.bc.ca/bcwild�re/how-cultural-burning-enhances-landscapes-and-lives/
City of Toronto. (2002). (rep.). High Park Woodland & Savannah Management Plan.
https://highparknature.org/wp-content/uploads/2018/12/HighParkMgmtPlan.pdf
High Park Nature. (2024). Prescribed Burns in High Park.
https://highparknature.org/article/prescribed-burns-in-high-park/
Martin, S. (2024). Indigenous wisdom guides High Park’s traditional and prescribed burn. Excalibur.
https://www.excal.on.ca/news/2024/05/02/indigenous-wisdom-guides-high-parks-traditional-and-
prescribed-burn/
United Nations O�ce for Disaster Risk Reduction (UNDRR). (2024). Canada wild�res, 2023 - Forensic
analysis.
https://www.undrr.org/resource/canada-wild�res-2023-forensic-analysis
Susskind, J. (2023). Playbook for the Pyrocene: Design Strategies for Fire-Prone Communities.
https://swacdn.s3.amazonaws.com/wp-content/uploads/2023/09/13195714/Playbook-for-the-
Pyrocene-Design-Strategies-for-Fire-Prone-Communities.pdf
The Climate & Wild�re Institute. (n.d.). Intentional �re.
https://intentional�re.org/
Abo-El-Ezz, A., AlShaikh, F., Farzam, A., Côté, M. O., & Nollet, M. J. (2023). Post-�re Damage Assessment
of Buildings at the Wildland Urban Interface. Paper presented at the Lecture Notes in Civil Engineering.
doi.org/10.1007/978-3-031-34593-7_55
Bénichou, N., Adelzadeh, M., Singh, J., Gomaa, I., Elsagan, N., Kinateder, M., . . . Sultan, M. (2021).
National guide for wildland-urban-interface �res: guidance on hazard and exposure assessment, property
protection, community resilience and emergency planning to minimize the impact of wildland-urban
interface �res (196p). National Research Council of Canada.
https://doi.org/10.4224/40002647
Beverly, J. L., Leverkus, S. E. R., Cameron, H., & Schroeder, D. (2020). Stand-level fuel reduction
treatments and �re behaviour in Canadian boreal conifer forests. Fire, 3(3), 1-23.
doi:10.3390/�re3030035
Calkin, D. E., Cohen, J. D., Finney, M. A., & Thompson, M. P . (2014). How risk management can prevent
future wild�re disasters in the wildland-urban interface. Proceedings of the National Academy of Sciences
Ontario
Non-Canadian
Further Reading
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of the United States of America, 111(2), 746-751.
doi:10.1073/pnas.1315088111
Copes-Gerbitz, K., Dickson-Hoyle, S., Ravensbergen, S. L., Hagerman, S. M., Daniels, L. D., & Coutu, J.
(2022). Community Engagement with Proactive Wild�re Management in British Columbia, Canada:
Perceptions, Preferences, and Barriers to Action. Frontiers in Forests and Global Change, 5.
doi:10.3389/ffgc.2022.829125
Davis, K. T., Peeler, J., Fargione, J., Haugo, R. D., Metlen, K. L., Robles, M. D., & Woolley, T. (2024). Tamm
review: A meta-analysis of thinning, prescribed �re, and wild�re effects on subsequent wild�re severity in
conifer dominated forests of the Western US. Forest Ecology and Management, 561.
https://doi.org/10.1016/j.foreco.2024.121885
Erni, S. Johnston, L. Boulanger, Y., Manka, F., Bernier, P ., Eddy, B. ... Gauthier, S. (2021). Exposure of the
Canadian wildland–human interface and population to wildland �re, under current and future climate
conditions. Canadian Journal of Fire Research, 51(9), 1357-1367.
https://doi.org/10.1139/cjfr-2020-0422
Gaur, A., Bénichou, N., Armstrong, M., and Hill, F. (2021). Potential future changes in wild�re weather and
behavior around 11 Canadian cities. Urban Climate, 35, 100735.
https://doi.org/10.1016/j.uclim.2020.100735
Lambert, E. (2021). Shackan Indian Band and Xwisten First Nation: Reinstating cultural burning practices.
The Institute for Catastrophic Loss Reduction.
https://www.iclr.org/wp-content/uploads/2021/04/11_cities_adapt_wild�re_SIB_and_XFN.pdf
Moritz, M. A., Batllori, E., Bradstock, R. A., Gill, A. M., Handmer, J., Hessburg, P . F., . . . Syphard, A. D.
(2014). Learning to coexist with wild�re. Nature, 515(7525), 58-66.
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Public Health Agency of Canada. (2023). Public health risk pro�le: Wild�res in Canada, 2023. Government
of Canada.
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response/rapid-risk-assessments-public-health-professionals/risk-pro�le-wild�res-2023/wild�re-risk-
pro�le.pdf
Safford, H. D., Schmidt, D. A., & Carlson, C. H. (2009). Effects of fuel treatments on �re severity in an area
of wildland-urban interface, Angora Fire, Lake Tahoe Basin, California. Forest Ecology and Management,
258(5), 773-787.
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Stocks, B. J., & Martell, D. L. (2016). Forest �re management expenditures in Canada: 1970-2013.
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Your Forest Podcast. (n.d.). Good Fire Podcast – List.
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Equity Considerations in Urban Forestry
Importance of Equity in Urban Forestry
Urban forest equity is crucial to addressing the systemic and historical disparities of
greening while supporting future environmental resilience. From a social perspective,
urban forest equity is crucial to ensuring that marginalized and underserved
communities receive fair investments in green spaces, that all communities have
access to the health bene�ts of trees and greening, and experience equal opportunity
to foster strong social connections, recreate, and thrive within urban green spaces.
From an ecological perspective, urban forest equity is important for supporting
biodiversity and overall ecosystem functioning, which improves climate resilience,
provides wildlife habitat, and mitigates pollution.
Trends
The importance of tree equity issues in Canada is gaining attention locally and
nationally (Watkins & Gerrish, 2018). Urban forestry conferences, action plans,
Highlights
Equity perspectives
Equitable urban forestry from social and ecological perspectives.
Environmental justice
Inclusive decision-making, equitable funding, community engagement, and
education.
Multicultural considerations
People of different cultures and urban forestry.
Labour equity
Gender inequality in the �elds of urban forestry, forestry, and arboriculture.
Where to start
Solutions and strategies for funding, planning, and engagement.
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management strategies, and research are more intentionally integrating equity into
their work across sectors in all regions. Some key research hubs contributing to
knowledge advancements are: The University of British Columbia, The University of
Toronto, Carleton University, Concordia University, UQAM, and Université Laval – to
name a few. Researchers at these universities focus on social, environmental, or
technological (such as AI) equity considerations.
Key knowledge includes:
• Access to tree canopy: There has been a signi�cant shift in Canada, with more
attention being paid to planting projects in underserved areas through the 2 Billion
Trees program.
• Integrating a lens of environmental justice, for example, considering how
temperature regulation can mitigate health risks due to extreme heat, particularly in
low-canopy, health-vulnerable communities.
• Inclusive decision-making involving residents and ensuring their voices shape
design, priorities, and practices.
• Equitable funding for tree planting and long-term maintenance to ensure
disadvantaged areas are not overburdened with tree care post-planting.
• Community engagement to provide education, jobs, and training opportunities to
foster long-term stewardship: A critical part of this is recognizing the role of
Indigenous knowledge and Indigenous-led greening in community engagement to
achieve equitable green spaces in planning and operations; in addition, increasing
diverse group representation in urban forestry career pathways to support
recognitional justice – they need to see themselves in the pro�ling of the �eld to
feel welcome (Vabi & Konijnendijk, 2021)
• Lastly, there is emerging interest in credentials for urban forest professionals to
support the "legitimization" of their role and skillsets (O'Herrin et al., 2023).
Defining Equity in Urban Forestry
The common de�nitions of urban forest equity in Canada center on the fair
distribution of tree-related bene�ts, particularly in marginalized or underserved areas.
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Urban forest equity strives to ensure that all residents, regardless of income, race, or
location, have equal access to the environmental, social, and economic bene�ts that
urban trees provide.
Emerging research has shown that equity in urban forests goes beyond access to
green space and should be broader to address three areas: distributional,
recognitional, and procedural equity and/or justice (Nesbitt et al., 2019). These are
not mutually exclusive. Distributional equity refers to the fair spread of urban forest
resources and bene�ts across communities. Recognitional equity acknowledges and
respects diverse identities, histories, and perspectives within communities. It is
about understanding who lives in a community: where they come from, their unique
needs, and the barriers they face in accessing green spaces. Lastly, procedural equity
focuses on the fairness of decision-making processes, ensuring that all community
members have a voice in urban forestry projects and that their voices in�uence
outcomes.
Urban Tree Canopy Distribution and Access to Green
Space
Urban forests are the �rst and only experience of nature for many, and these forests
shape the experiences of nature for millions of Canadian residents, making access to
urban green spaces a crucial topic in urban forest strategies; a national poll indicates
that 95% of Canadians agree that access to green spaces is important to their quality
of life (Environics Research, 2017). However, not all urban residents bene�t equitably
from the ecological services that urban forests and green spaces provide.
To date, urban forests have been distributed inequitably in Canadian cities. On
average, lower-income neighbourhoods (below 50% of median household incomes)
and marginalized neighbourhoods (disempowered or lacking the capacity to
participate and gain full respect in society) have less green space and canopy cover
than wealthier, predominantly white neighbourhoods (GoC 2022; Public Health
Ontario, 2021; Cusick, 2021). In many Canadian cities, neighbourhoods with lower-
income households and larger Black, Indigenous, and people of colour (BIPOC)
populations were found to have up to 20-30% less canopy cover (Wittingham et al.
2022). When considering the physical and environmental health bene�ts that urban
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forests provide, the disparities in tree canopy distribution and inequitable access to
these bene�ts raise a question of social equity (Schell et al., 2020). Moreover, in
areas suffering from poverty and racialization, women have been found to use green
spaces less frequently if they perceive them to be 'unsafe' due to poor lighting,
maintenance, or cleanliness (Braçe, Garrido-Cumbrera & Correa-Fernández, 2021).
These �ndings show that low-income neighbourhoods, marginalized communities,
racialized groups, and women do not equitably enjoy the bene�ts provided by quality
green spaces. Addressing these issues and the equitable distribution of tree canopy
and environmental bene�ts is essential for building just and sustainable treed urban
communities and a healthy society. Community well-being, social inclusion, gender
equity, environmental health, and climate resilience in racialized and low-income
neighbourhoods will all bene�t from equitable and strategic urban forest planning
(Bikomeye et al., 2021).
Canada is not immune to the issues of urban forest equity in its cities and towns. For
example, in major cities such as Toronto, Ottawa, Montreal, Vancouver, Calgary,
Surrey, and Quebec City, the lower tree canopy cover has a signi�cant negative
correlation with poverty and racialization (Wittingham et al. 2022). In an effort to
address the problem, municipalities like the cities of Ottawa and Toronto have made
equitable access to urban forests a guiding principle in their urban forest plans and
strategies (Engage Ottawa, 2024). However, despite the efforts, urban forest planning
(meaning their development and planning) and tree canopy equality implementation
in Canadian cities are still lacking, and equity strategies or engagement plans to
assist speci�c to marginalized communities still have a minor impact (Mullenix,
2022).
Immigration and Multicultural Considerations
How Canadian citizens feel about their urban forest matters in terms of what they
receive and bene�t from, and whether and how they are willing to engage in urban
forest conservation and management. Researchers often measure residents'
attitudes toward green spaces through public surveys, and the information obtained
can help municipalities better manage their urban forests (Jennings et al., 2016).
However, people living in different regions may have different attitudes and
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preferences related to urban forests or may face unique barriers to their ability to
participate in public referendums, surveys, and engagement opportunities (Avolio et
al., 2015). Language barriers to new immigrants and people of various cultures can
go unconsidered when municipalities conduct public surveys or hold open public
participatory meetings (Ornelas Van Horne et al., 2023).
Additionally, low-income communities may lack time, funds, and access to the
technology required to participate in events- time off work, childcare, internet, and
computers/smartphones are more accessible in higher-income communities, but to
many low-income Canadians, these things are luxuries that prevent participation
(Chianelli, 2019). Meaningful public discourse cannot be achieved without
considering barriers to engagement when discussing urban planning and
environmental issues, especially in marginalized communities where sustainable and
equitable planning is that much more signi�cant.
Moreover, participation and inclusion of new Canadians, BIPOC, and multicultural
individuals are also vital to building equitable urban forestry. Due to its far-reaching
bene�ts, urban forestry involves multidisciplinary teams with diverse skills and
knowledge. Foresters, urban planners, landscape architects, arborists, scientists, and
community leaders help create healthy and sustainable urban forests, and this
multidisciplinary �eld can greatly bene�t from the inclusion of people from diverse
backgrounds and experiences.
Labour and Gender Equity
Labour and gender equity are also crucial issues in the �elds of urban forestry and
arboriculture in Canada, where both sectors have traditionally been male-dominated.
Labour equity focuses on ensuring fair representation, remuneration, and career
advancement opportunities for individuals from all backgrounds. This issue is
particularly important as the urban forestry profession seeks to diversify its
workforce and attract more varied talent. Gender equity, on the other hand,
speci�cally addresses the persistent underrepresentation of women in urban forestry
and arboriculture, where women often occupy lower-level roles and encounter
obstacles to career advancement due to systemic biases and discrimination
(Bardekjian et al., 2019; Kuhns et al., 2004).
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Recent efforts, such as mentorship/training programs and workshops aimed at
reducing barriers to entry, are working to create more inclusive environments for
women and other underrepresented groups in the �eld of urban forestry (City of
Toronto, 2023; FSC, 2022). The biennial Canadian Urban Forest Conference,
coordinated by Tree Canada in partnership with a host city, along with initiatives like
Free to Grow, Women in Forestry, and Women in Wood networks, are helping to bring
professionals together and advocate for a more equitable, diverse, and inclusive
workforce (Free to Grow in Forestry, 2021; Women in Forestry, n.d.; Women in Wood,
2017). These initiatives are critical as urban forests play an increasingly vital role in
the climate resilience and social well-being of Canadian cities, necessitating a
broader range of voices and perspectives for their sustainable management.
As the �eld of urban forestry continues to evolve, addressing labour and gender
equity within the profession will be essential for ensuring that all professionals,
regardless of gender or background, can contribute meaningfully to the design,
planning, and management of urban forests (Bardekjian, 2016; Bardekjian et al.,
2019).
Solutions and Strategies
An equity-based approach to urban greening should be adopted to ensure that
Canadian cities can work towards canopy cover goals without propagating further
social and economic disparity (Angelo, MacFarlane, Sirigotis & Millard-Ball, 2022;
Bassett, 2024; Puric-Mladenovic, 2024). Increasing canopy cover/tree planting goals
are part of many Canadian cities' urban forest management plans, and urban
greening in low-income/racialized areas presents an opportunity to address two
issues at once. However, increasing canopy cover in underserved areas faces some
challenges, such as a lack of funding, the absence of a planning process that values
trees and long-term tree survival, and weak public engagement with communities
that need trees the most (Mullinex 2022). Additionally, a lack of physical space to
plant trees and sometimes environmental contaminants can lower chances of tree
survival (Danford et al., 2014; Wattenhofer and Johnson, 2021).
Where to Start
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There are several tools and methods that already exist for addressing inequality in
urban forestry. For example, Statistics Canada created a tool to address the need to
understand gentri�cation in a Canadian context. The tool is called GENUINE, which
stands for Gentri�cation, Urban Interventions, and Equity (see Team INTERACT,
2016), and it automatically populates maps for several Canadian cities across four
separate measures (Firth et al., 2021). In addition to assessing what is already there
through available tools, there are recognition and certi�cation programs such as the
Arbor Day Foundation's Tree Cities of the World (TCOW) program and the Sustainable
Forestry Initiative's (SFI) Urban and Community Forestry standards that offer
structured guidelines and criteria for successful management. The �rst step is
identifying a community’s equity-related goals; once goals are established, these
kinds of tools can be helpful, staged approaches for planning and review.
Funding
To address the lack of funding for urban forestry activities, some municipalities,
including Toronto and Winnipeg, support urban forestry grants and incentive
programs (City of Toronto, 2021). Integrating urban forestry funding into yearly
municipal budget planning is another way to ensure funding allocation to urban
forest management. Alternatively, federal funding programs such as the 2 Billion
Trees Program (GoC, 2023) and the Forest Innovation Program (NRCan, 2023) should
work to enhance equitable access to urban forests and sustainable management of
urban green spaces, while the Natural Infrastructure Fund (GoC, 2024) should
improve natural infrastructure in underserved communities, which can reduce heat
stress, limit extreme weather damage, and support stormwater management
(Wittingham et al., 2021). Additionally, the federal government should increase
funding availability for municipalities to protect and maintain existing trees and
expand urban tree canopy equitably and fairly. One success story is the Growing
Canada's Community Canopies (GCCC) program delivered in partnership between
Tree Canada and the Federation of Canadian Municipalities (FCM), where there are
two broad streams of funding: the �rst is for increasing canopy and getting trees
planted, the second is for capacity building in all other areas that are required for
urban forest sustainability.
Planning
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Planning processes need to prioritize equity by using evidence-based decision-
making informed by tools such as current tree inventories and the Tree Equity Index,
income data, and immigration and BIPOC data (Ordonez et al., 2024). Additionally,
municipalities must assess current canopy cover data compared to canopy goals
while supplementing urban greening decisions by identifying areas with lower canopy
cover, which have low Tree Equity Index values (Fleming and Steenberg, 2023).
Integrated and intersectional planning processes for urban trees should be created,
with adequate municipal and provincial funding allocation towards increasing urban
tree cover equity across municipalities in racialized and marginalized communities
(Jennings et al., 2019). Furthermore, these planned urban forests/green spaces must
be accessible (within 300m of residences) and be of good enough quality to
su�ciently supply bene�ts to underserved communities (Wittingham et al. 2022).
Engagement
Finally, fostering public engagement by building stakeholder relationships between
governments, academia, industry, community organizations, practitioners, and
citizens is vital to sustainable and equitable urban forest management (Campbell,
Svendsen, Johnson & Plitt, 2022). Community members should be engaged from the
beginning stages of planning processes and consulted throughout the planning and
execution process. Nurturing ongoing relationships with existing neighbourhood
associations and stewardship programs (or creating them where they do not exist) is
an important step in starting discourse with residents. Consulting community leaders
on equitable and accessible suggestions for building community interest and
participation should be part of the beginning stages of public engagement strategies.
Outreach efforts should be the predominant recipients of allotted urban greening
budgets for target neighbourhoods in the beginning stages to ensure consideration
of diverse perspectives, proper community consultation, and meaningful community
engagement. Relationship-building with the people impacted by urban forest inequity
can help make sure community needs are considered and responded to while
building programs that are sustainable, successful, and robust (Wittingham, 2022).
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Lambert, M. R. (2020). The ecological and evolutionary consequences of systemic racism in urban
environments. Science,369(6510), eaay4497.
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Vabi, V. & Konijnendijk, C. (2021). The Urgency and Opportunity to Increase the Access of All Canadians to
Urban Forests: An interview with Dr. Cecil Konijnendijk on the 3-30-300 rule for creating greener and
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Awareness and Community Stewardship
What sets urban forestry apart from other branches of forestry is its direct
connection and relevance to people, and its role in providing social and ecological
bene�ts that extend to all urban residents, not just individuals or speci�c groups.
People around the world are becoming increasingly involved in their communities,
and recent decades have seen a remarkable rise in community engagement with
urban forestry. Today, urban residents are more concerned than ever about the
greenery in their neighborhoods and the health of their trees. They are eager to
contribute to the protection and care of these natural resources. This growing
awareness about the importance of urban forests and their management has led to
an increase in public and community participation in urban forest stewardship across
Canada.
Awareness and stewardship in urban forestry are driven by people caring about their
communities and wanting to be involved in tree care and management (Su et al.,
2022). There is a diversity of perceptions about urban forests and green spaces, and
many reasons why people and communities get engaged. Whether for aesthetics,
recreation, or a general appreciation for the environment, people feel connected to
the trees in their cities. A recent survey found that around 90% of urban residents felt
some sort of connection to urban trees, and nearly half responded that they had a
‘favourite tree’ (University of Derby, 2023). A large percentage of urban dwellers (over
85%) acknowledged that trees contribute to cleaner air and water, wildlife habitat,
Highlights
Awareness and stewardship
Public awareness and involvement in urban forest management.
Stewardship and NGOs
NGO involvement in stewardship and support of community urban forestry.
Community stewardship
Public and citizen engagement in urban forest management and conservation.
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and better mental health. This shows that urban residents are aware of the value and
bene�ts they receive from urban trees and want to contribute to their continued
stewardship (Conway & Scott, 2020; Damian, 2020).
In many ways, the success of urban forestry depends on involvement from multiple
stakeholders and partners, including organizations, various levels of government, and
citizens. There are also many non-government organizations, organized and
uno�cial, that contribute to raising awareness and supporting stewardship of urban
forestry.
Community Stewardship in Canadian Municipalities
Many municipalities in Canada have urban forestry strategies, many of which have
explicit objectives concerning community awareness, stewardship, and involvement
in urban forest management. Stewardship and community engagement are major
components of urban forest management, where communities and individuals help
municipalities. Community stewardship is a cornerstone of effective urban forest
management, whether through tree planting events, monitoring and inventory efforts,
or just caring for public and private trees in a city neighbourhood.
Additionally, many municipalities across Canada also provide support and funding
for community members interested in contributing to urban forestry. For example,
municipalities such as Ottawa, Kitchener, and Halifax directly acknowledge in their
urban forest master plans that community involvement and stewardship are
essential for long-lasting, proactive management. The city of London, Ontario created
a program called Neighbourhood ReLeaf to encourage community members to get
involved in planting and caring for urban trees by providing funding for trees and
planting events, guidance for caring for and maintaining urban trees, and education
about the human bene�ts and ecological value provided by urban trees (ReForest
London, n.d).
The city of Vancouver also recently put out a call for local support in maintaining
urban trees during drought seasons. The city published a how-to guide to inform
residents on the importance of urban trees, what their needs are, and how to keep
them healthy and watered during the summer months (City of Vancouver, 2023).
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Various other Canadian municipalities across the country have embarked on similar
endeavours, including the City of Oakville (2024), the City of Wolfville (2024), the City
of Saddle Hills (Bozic, 2024), and the City of Saskatoon (2024).
Toronto leads Canadian municipalities in the robustness of its urban forest
management program, being one of Canada’s largest leaders in terms of investing in
urban forest stewardship (City of Toronto, 2024). In six years, the city’s Urban
Forestry Grants and Incentives Program invested over $20.5 million in urban forestry,
funding over 200 independent projects across the city and planting upwards of
100,000 trees (City of Toronto, 2024). The program supports partnerships and
collaborations with citizens, landowners, and non-pro�t organizations to bolster the
city’s priorities outlined in its strategic forest management plan (City of Toronto,
2013).
The city of Edmonton also supports a well-established urban forest stewardship
program called the Grow Together program, which allows the city to expand urban
forests by partnering with community groups and neighbourhood associations
interested in learning more about urban forest stewardship and planting more trees
within their neighbourhood (City of Edmonton, n.d.). The program provides
educational events, tree planting efforts, and support for citizens looking to engage
in proper urban forest management.
But stewardship doesn’t just mean helping hands and planting trees; it includes
engaging citizens in envisioning the future of their urban forest by engaging them in
urban forest management planning. Engaging community members across Canada
to develop guiding principles, intended outcomes, responsibility expectations, and
speci�c strategies and actions for management plans can support the most effective
urban forest management. For example, Edmonton, like several other municipalities
across Canada, has an urban forest management plan that is advised by community
members and scienti�c experts.
Residential support for urban forestry policy, including policies speci�cally targeting
residential areas, is an understudied component of successful urban forest
management. This ties into the awareness aspect of community engagement, and
cities are beginning to incorporate open meetings, information sessions, and
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avenues for public input regarding forestry goals, desired outcomes, and policy
application (Conway and Wang, 2014).
NGO Groups
Non-government organizations are an important part of urban forest stewardship
efforts in Canada. They promote education and information about urban forest
stewardship, sustainable development, and community engagement in municipal
forestry management. These organizations hold workshops, public speaking events,
and educational meetings so citizens can understand how to get involved in urban
forestry. Such efforts involving local communities in urban forestry initiatives result
in engaged residents who are more likely to support and care for urban trees. This, in
turn, can supplement municipal tree care efforts and ensure urban forestry's long-
term success and sustainability (Bourque et al., 2021).
NGOs' contributions are critical to stewardship initiatives outside of the city-owned
land, but some NGOs also often support municipal initiatives. There are many
creative urban forest partnerships and initiatives where NGOs partner with cities,
governments, and foundations to deliver urban forest stewardship and education,
and raise awareness. Non-pro�t organizations such as the Green Municipal Fund,
Network of Nature, and Tree Canada provide tree-planting and urban forestry grants
or lists of grants for municipalities and other organizations in Canada, helping to
create connections and partnerships between communities and environmental
organizations (Green Municipal Fund, n.d.; Network of Nature, 2024; Tree Canada,
n.d.).
NGOs also contribute funds and labour to urban forestry initiatives. They mobilize
donations from industry and corporate groups and often broker public-private
partnerships. For example, the McMaster Marauders (Rukavina, 2024) and sports
events like the Allstate Soccer Show in Calgary (PlanIT Geo, n.d.) come together to
raise money for tree planting efforts in their communities.
Large-scale citizen-led groups are also important in starting and maintaining
stewardship initiatives. In Ontario, citizens in the township of Centre Wellington
assembled an organization called Tree Trust, which is dedicated to raising
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awareness about old and irreplaceable urban trees in hopes of preserving them (Tree
Trust Centre Wellington, n.d.). By educating residents about the value of large old
trees, not just for aesthetic purposes but also for their carbon sequestration/storage
capacity, Tree Trust has been able to o�cially protect over 80 large, mature trees in
multiple chapters across southern Ontario, and is working to expand its efforts. In
Manitoba, residents have coalesced to form an organization called Trees Winnipeg
with the goal of protecting urban trees, speci�cally with a coalition to save elm trees,
which are suffering from a fatal fungal infection known as Dutch Elm Disease (DED).
By building awareness and educating Winnipeg residents about how to recognize
signs and symptoms of DED, the organization is able to increase its monitoring
bandwidth and increase the probability of catching incidences of DED before they
progress too far or spread (Trees Winnipeg, n.d.).
The public and residents can take part in certain tree maintenance tasks, such as
caring for young trees. Several programs and non-governmental organizations
(NGOs) provide education and assistance to community groups and residents for
maintaining urban trees. One example is the Citizen Pruners program, launched by
Tree Trust, which teaches volunteers how to properly prune trees and also keeps
community members engaged in urban forestry beyond the initial planting phase.
This training is conducted under the supervision of professional arborists, and the
program effectively enlists volunteers to help maintain young trees following planting
efforts, ensuring proper growth and survivorship. The program has been piloted in
Elora, Thunder Bay, and the Long Branch neighborhood of Toronto (EEC, n.d.).
Similarly, in Vancouver, BC, the TreeKeepers' Citizen Forester Program, led by certi�ed
arborists, educates Citizen Foresters on selecting, planting, and caring for urban
trees, equipping them with knowledge they can share with their community (Tree
Keepers, n.d.). Tree Canada, through its Community Tree Grants, supports
community-led tree planting and tree care initiatives across the country by providing
funding and resources to municipalities, Indigenous communities, and non-pro�t
organizations for tree planting and stewardship projects (Tree Canada, n.d.).
There are efforts to raise awareness and appreciation for large trees across Canada.
On North Pender Island in British Columbia, the Raincoast Conservation Fund has
organized an effort to register big trees in an effort to increase opportunities for
community engagement in conservation. Using tools like iNaturalist, residents are
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encouraged to submit large trees to the registry in efforts to protect them from
logging and development (Willis, 2023). Ontario also has several initiatives to raise
awareness and appreciation for large trees, such as the Tree Trust program, which
focuses on preserving mature trees, recognizing their substantial environmental and
social values, and funding their professional care.
Community Groups
Community involvement is one of the pillars of urban forestry in Canada. At the local
scale, neighbourhood organizations and community groups are responsible for many
of the most successful grassroots movements in Canadian urban forestry. Usually
born out of concern for speci�c geographic areas, these local volunteering
organizations mobilize around certain topics, like saving a park from development,
restoring a degraded site, protecting certain trees and tree species in urban areas,
conducting tree inventories, and monitoring their urban forest.
For example, Vancouver employs an urban forestry strategy that provides tools for
maintaining healthy, resilient urban green spaces by increasing community
involvement in forest stewardship, providing education and information to urban
residents about the bene�ts and importance of urban forests, and creating programs
to improve access to urban green spaces (City of Vancouver, n.d.). In 2015, the city of
Vancouver developed a strategic urban forestry plan to be implemented over �ve
years, using community involvement and stewardship to achieve concrete objectives
and goals guided by science, with the end goal of protecting and improving urban
forests and biodiversity (City of Vancouver, 2015).
Neighbourwoods© is Canada’s �rst urban forest citizen science program, founded by
Dr. Kenney and Dr. Puric-Mladenovic to connect academic research with community
involvement. They pioneered community engagement and citizen science initiatives
for forest conservation that train citizens to inventory and monitor urban trees,
assess their health, and identify potential areas for planting. The program has been
instrumental in urban forest stewardship on private lands, training hundreds of
volunteers and numerous communities across Ontario. It has also engaged many
students from the Master of Forest Conservation (MFC) program to assist
communities with inventory, education, and the creation of relevant reports and
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plans. The standard and spatial data collected have enabled data-driven
management and stewardship decisions, leading to the development of community
stewardship plans. Data from this program continues to be utilized in applied
research related to carbon sequestration, invasive species management, tree growth,
risk assessment, and more. Other community efforts, such as a Bioblitz, an event
where citizens help identify, inventory, and catalogue different species of plants,
insects, and birds, are also a way to increase community involvement in urban
biodiversity and stewardship (iNaturalist, 2024). Local efforts to save parks from
development, such as the Save City Hall Park effort in Vancouver, are an example of
residents coming together to stand up for urban green spaces and become involved
in their protection and stewardship (City Hall Watch, 2024).
Overall, awareness and stewardship are some of the most powerful and unique
aspects of urban forestry in Canada. Municipalities, NGOs, neighbourhoods, and
individuals are all vital in the effort to manage urban forests in Canadian cities
effectively and sustainably.
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Landry, F. (2022). Greening Toronto to Increase Resilience and Equity: Study on Citizens’ Preferences
Regarding the Urban Forest. David Suzuki Foundation. P31.
Livingstone, S.W., Cadotte, M.W., & Isaac, M.E. (2018). Ecological engagement determines ecosystem
service valuation: A case study from Rouge National Urban Park in Toronto, Canada. Ecosystem
Services,30A, 86-97.
https://doi.org/10.1016/j.ecoser.2018.02.006
Nadeau, S., Beckley, T. M., Huddart Kennedy, E., McFarlane, B. L., and Wyatt, S. (2007). Public views on
forest management in New Brunswick: report from a provincial survey. Natural Resources Canada:
Fredericton, NB.
https://www2.gnb.ca/content/dam/gnb/Departments/nr-rn/pdf/en/ForestsCrownLands/
ForestSurvey.pdf
Rukavina, P . (2024). 99 trees for 99 years: McMaster soccer teams participate in celebration for
philanthropist Stephen Jarislowsky with tree planting.
https://marauders.ca/news/2024/9/10/mens-soccer-99-trees-for-99-years-mcmaster-soccer-teams-
participate-in-celebration-for-philanthropist-stephen-jarislowsky-with-tree-planting.aspx
Su et al. (2022). Values and beliefs about urban forests from diverse urban contexts and populations in
the Greater Toronto area. Urban Forestry & Urban Greening, 72, 127589.
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https://doi.org/10.1016/j.ufug.2022.127589
UBC Forestry. (2023). The rise of urban forestry.
https://forestry.ubc.ca/branchlines-articles/the-rise-of-urban-forestry/
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Indigenous Collaboration and Integration of
ITK
The Indigenous Peoples of Canada have lived in harmony with nature and sustainably
stewarded lands and forests for many generations. They hold intimate knowledge of
the intricacies of the ecosystems and biodiversity of Canada's forests and lands.
Their knowledge has been built over numerous generations through direct interaction
with the environment and respect for the land. First Nations, Inuit, and Métis peoples
have always been in�uential forces on the structure of forests in Canada, but
historically, they have rarely been championed as land stewards and knowledge
holders. Indigenous people are to this day �ghting to protect their right to cultural
practices and values, as well as their inherent and inalienable right to steward
Canadian land (Native Land, 2024).
Recently, the value of Indigenous Traditional Knowledge (ITK) for conservation and
management purposes has been recognized and has come to the forefront of
discourse among scientists and practitioners (Sinthumule, 2023; Alexander et al.,
Highlights
Historical land stewardship
Indigenous Peoples of Canada, using intimate knowledge of ecosystems, have
sustainably managed forests and lands for generations.
Traditional Ecological Knowledge (TEK)
Indigenous knowledge is increasingly recognized as valuable for conservation and
land management.
Rights and cultural practices
Indigenous communities continue to �ght for their cultural practices and the right
to steward the land.
TEK and Indigenous stewardship in urban areas
Potential of weaving TEK with Western scienti�c methods.
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2019). Increasingly, Traditional Ecological Knowledge (TEK) is being viewed as a
form of conservation capable of improving traditional Canadian forest management
practices. Weaving TEK with Western science knowledge has also been seen as one
way to address the historical injustice and exclusion of Indigenous Peoples from
management decisions on their land (CCFM, 2024; McGreggor, 2002).
Since the �rst settlers set foot on Canadian grounds, land development, land use
changes, and urbanization have happened quickly. Permanent settlements, cities,
towns, and villages, all products of Western civilization, sprang up across Canada
within a few decades of land clearing. As of the early 1900s, and particularly after the
Second World War, the existing settlements, cities, towns, and villages grew
exponentially and intensi�ed, while many new urban areas were established. This
extensive urbanization has driven the growth of the gray infrastructure network
(roads, electricity, power lines, etc.) needed to support urban centres and their
surrounding areas. As a result of all these changes and economic opportunities in
urban areas, Canada's population has become predominantly urban, and this includes
Indigenous people. Today, over 800,000 Indigenous people are living in cities in
Canada (Trovato & Price, 2024). According to the 2016 Census, about 45% of
registered Indigenous, 76% of Non-Status Indigenous, 50% of Inuit, and 70% of Métis
live in urban areas (Indigenous Services Canada, 2020).
Traditional Ecological Knowledge (TEK)
Indigenous Traditional Ecological Knowledge (TEK) has a signi�cant cultural and
traditional value for Indigenous communities and Canadian settlers. TEK has grown
and evolved over thousands of years of lived experiences and shaped Canada’s
culture and economy. Indigenous peoples held essential knowledge of practices
related to navigating the natural environment. They mastered how to navigate
waterways and use lakes, rivers, and streams as travel routes. For travelling by water,
Indigenous people crafted canoes using birch bark (Marsh & Parrott, 2021) and
designed snowshoes for travelling and hunting across the land in snowy months
(Atleo & Boron, 2022).
Indigenous People, masters in trapping and hunting techniques, taught settlers how
animals migrate, how to follow their tracks, and how to trap and skin them. Tapping
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maple trees to produce maple syrup, a knowledge and skill originally held by
Indigenous Peoples in Canada, has become a staple of Canadian culture. While many
parks and groups within and around urban areas host maple syrup festivals,
demonstrating how the settlers tapped maple trees, they do not necessarily
acknowledge and demonstrate Indigenous contribution (Pine, 2016; Moody, 2015;
Huron, 2014).
Indigenous agricultural practices used by Haudenosaunee included methods such as
the "Three Sisters" (corn, beans, and squash), which helped maximize crop yields and
retain soil fertility (Decaire, 2012). In the early days of settlement, nature was the �rst
medicine, and Indigenous Peoples hold profound knowledge of local plants with
healing and medicinal properties. For example, Willow bark (similar to aspirin) was
used to relieve pain, and Eastern white cedar was brewed into tea, which was used by
settlers to prevent scurvy (Turner, 2019; Durzan, 2009). Indigenous Peoples also have
a depth of knowledge in land management practices such as controlled burns to
maintain vegetation communities and the associated wildlife on the landscape they
rely on. In several cities, controlled �re has been used as a management practice in
urban parks, and selective tree felling has also been acknowledged as bene�cial
(Moola et al., 2024).
While these Indigenous practices and TEK have been used for survival and economic
gain by settlers, shaping the Canadian culture as we know it today, TEK has
historically not been acknowledged or honoured (Parks Canada, n.d.). TEK was taken,
and proper credit and respect were not given to the Indigenous people who taught
and shared their skills and knowledge, and land. What the settlers did not learn or
take from Indigenous people was how not to overcut, overhunt, over�sh, how to
respect the land, and how to think for future generations (Dick et al., 2022).
Perceptions about the land and values between Indigenous people and the European
settlers were also two worlds apart. TEK, along with the abounded resources and
land taken from Indigenous people, enabled colonizers to bene�t economically to the
point that the economic gains drove deforestation, erosion, pollution, loss of species,
the collapse of �sheries, and many other problems caused by looking at the land as a
commodity. This quickly led to the eventual control, marginalization, and exclusion of
Indigenous Peoples and culture in Canada, causing devastating outcomes that still
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reverberate today.
Indigenous Stewardship in Urban Canada
Since the establishment of permanent settlements and urban areas by colonial
settlers, urban trees and gardens and their management in cities and towns have
been dominated by Western values, design, and science to the exclusion of
Indigenous Peoples and their knowledge and collaboration (Mullenbach et al., 2003).
However, Canadian society, including different levels of government and NGOs, is
starting to engage Indigenous groups and perspectives in information sessions and
at decision-making tables from conservation to land development actions. TEK is
increasingly being viewed as a conservation method with the potential to improve
traditional Canadian forest management practices while also addressing the
historical exclusion of Indigenous peoples from management decisions on their land
(CCFM, 2024). In some forest management cases, traditional and cultural activities
are integrated in forest management plans where design and mapping of land
protection zones are based on TEK (Cheveau et al. 2008). Indigenous Peoples are
connected to and dependent on functioning, healthy forest ecosystems and their
non-timber forest products, which brings a holistic perspective on how forests should
be viewed and managed (Cheveau, Imbeau, Drapeau, & Bélanger, 2008). While
Indigenous collaboration at the policy level of forestry requires more attention, there
are many pockets of Indigenous stewardship across forested landscapes. For
example, designations of "community forests" with management based on local
values, beliefs, and decision-making are emerging across Canada in British Columbia,
Ontario, and Quebec (NRCan, 2024). These community forests represent both
industry-joint and Indigenous-led initiatives, which allow for self-determined co-
management. With the support of industry and government, Indigenous communities
can implement traditional stewardship practices and de�ne their own desired
outcomes for urban forest management while working towards forestry goals that
are agreed upon by both forestry associations and residents.
Effective cooperation and co-management between industry, government, and
Indigenous peoples in urban planning can also produce impactful land use and
management practices. Recently, several First Nations in Manitoba showcased a
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landmark display of Indigenous-led urban development by securing the largest urban
Indigenous reserve in Canada on the former site of the Winnipeg Kapyong Barracks.
With largely Indigenous-led decision-making and strategic planning, green
infrastructure (urban forests, water bodies, vegetation) was acknowledged as "vital"
to sustainable community building in the Naawi-Oodena Master Plan. The First
Nation will use native species for urban vegetation as a means of knowledge-sharing
and appreciation of the cultural value of local plants while also creating essential
habitat for native species of fauna and pollinators (Canada Lands Company, 2021).
Urban forests are a new phenomenon that emerged with the growth of urban centers.
They are the result of complex changes and interactions between people and land,
and their desire to make cities livable. Though urban forests are a complex mix of
native and non-native trees and plants, they often receive a positive response from
Indigenous people. Indigenous people, as small groups or individuals, bring their
voices to urban areas and are often the �rst ones to stand for nature. They stand for
trees, wildlife, and even Eastern white cedar fences in the face of development
(Therrien, 2022). They observe the creatures that urban forests host and see what
trees offer beyond dollar values.
History, experience, and research have shown that TEK and traditional forestry
practices contribute to higher levels of biodiversity and healthier ecosystems (Nitah,
2021). Indigenous people use and manage the land sustainably and respectfully
(Fisher et al., 2019). Their historical practices, such as cultural burning and selective
tree felling, have now been incorporated into select contemporary forest
management plans, with prescribed burns and selective forestry taking place in
almost all provinces and territories in Canada. Additionally, when locals are
empowered to steward and manage urban forests, these forests tend to be more
resilient, biodiverse, and socio-economically bene�cial (NRCan, 2023). The
incorporation of traditional practices such as prescribed burns, tree felling, pollinator
gardens, and native plant protection into contemporary urban forestry is vital to not
only fostering sustainable urban forest management practices but also a
fundamental step towards reconciliation (see Tree Canada, n.d.). Pathways forward
will require more knowledge, input, collaboration, and Indigenous led management in
urban forestry.
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The weaving of TEK into urban forest management, as well as fostering discourse,
collaboration, and self-determination of Indigenous peoples, is essential to
sustainable urban forest management (Reconciling Ways of Knowing, n.d.).
Historically and today, urban forest management often excludes traditional
Indigenous knowledge and management practices, but the pathway forward shows
the importance, value, and need for TEK in urban forest management for the future.
Resources
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Natural Resources Canada. (2024). Community forests manage for multiple values at multiple scales in
increasingly uncertain landscapes.
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Natural Resources Canada. (2023). Biodiversity, conservation, and Indigenous Peoples' well-being.
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being/24801
Parks Canada. (n.d.). Prescribed �re.
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Reconciling Ways of Knowing. (n.d.). Online Dialogue Series.
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greening initiatives [infographic].
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Trovato, F. and Price, J. A. (2024). Article – Urban Migration of Indigenous Peoples in Canada. The
Canadian Encyclopedia.
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Truth and Reconciliation Commission of Canada. (2015). Truth and Reconciliation Commission of
Canada: Calls to Action. Government of British Columbia.
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aboriginal-peoples-documents/calls_to_action_english2.pdf
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Agencies on Indigenous Knowledge. Council on Environmental Policy.
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United Nations. (2018). United Nations Declaration on the Rights of Indigenous Peoples.
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UNDRIP_E_web.pdf
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United States Department of Agriculture. (2024). Indigenous Voices and Stewardship in Urban Landscapes
[webinar].
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urban-landscapes
Alexander, S.M., Provencher, J.F., Henri, D.A. et al. Bridging Indigenous and science-based knowledge in
coastal and marine research, monitoring, and management in Canada. Environ Evid 8, 36 (2019). https://
doi.org/10.1186/s13750-019-0181-3 Canada Lands Company. (2021). Former Kapyong Barracks Master
Plan.
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Atleo, C., & Boron, J. (2022). Land Is Life: Indigenous Relationships to Territory and Navigating Settler
Colonial Property Regimes in Canada. Land, 11(5), 609.
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Canadian Parks and Wilderness Society (CPAWS). (n.d.). Winnipeg's First National Urban Park?
Assiniboine Forest.
https://cpawsmb.org/campaigns/assiniboine-forest/
Cheveau, M., Imbeau, L., Drapeau, P ., & Bélanger, L. (2008). Current status and future directions of
traditional ecological knowledge in forest management: a review. The Forestry Chronicle, 84(2), 231-243.
https://doi.org/10.5558/tfc84231-2
City of Hamilton. (2019). City of Hamilton Urban Indigenous Strategy [report].
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Decaire, R. (2012). Understanding indigenous agricultural systems. Heritage Matters.
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Dick, Chief A., Sewid-Smith, D., Recalma-Clutesi, K., Deur, D., and Turner, N.J. (2022). “From the beginning
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Fisher, J., Shackelford, N., Hocking, M., Trant, A., and Starzomski, B. (2019). Indigenous peoples'
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Further Reading
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Goan, H., Martin, A., Valiquette, J. & Klein, R. (2025). Indigenous Engagement in Urban Forestry. In: City
Trees – Urban and Community Forestry Society magazine, Jan/Feb 2025. 14-18.
https://read.dmtmag.com/i/1530859-january-febuary-2025/13
Huron, R. (2014). Historical Roots of Canadian Aboriginal and Non-Aboriginal Maple Practices. Thesis
submitted to Faculty of Geography, Wilfrid Laurier University.
https://scholars.wlu.ca/ges_mrp/3/
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Landry, F. (2022). Greening Toronto to Increase Resilience and Equity: Study on Citizens' Preferences
Regarding the Urban Forest. (31 pp). David Suzuki Foundation.
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Equity-Study-on-Citizens-Preferences-Regarding-the-Urban-Forest-Report-082022.pdf
MacLean's. (2023). How Indigenous participation in forest management is changing resource development
in Canada.
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Marsh, J. & Parrott, Z. (2021). Birchbark Canoe. The Canadian Encyclopedia.
https://www.thecanadianencyclopedia.ca/en/article/birchbark-canoe
McGrath, D., Plummer, R., & Bowen, A. (2021). Cultivating our urban forest future: a value-chain
perspective. FACETS, 6, 2084-2109.
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McGregor, D. (2002). Indigenous knowledge in sustainable forest management: Community-based
approaches achieve greater success. The Forestry Chronicle, 78(6), 833-836.
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Moody, H. (2015). Indigenous Knowledge and Maple Syrup: A Case Study of the Effects of Colonization in
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Moola, F., Jolly, H., Borah, J. and Roth, R. (2024). The potential for Indigenous-led conservation in
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agenda for urban greening and conservation. Conservation Letters, 15, e12889.
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Nitah, S. (2021). Indigenous peoples proven to sustain biodiversity and address climate change: Now it's
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Pine, D. (2016). “Ziisabaakodakaan: The Place Where Sugar is Made”. Thesis submitted to Faculty of
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Geography and Planning, University of Toronto.
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content
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forest/
Sinthumule, N. I. (2023), Traditional ecological knowledge and its role in biodiversity conservation: a
systematic review. Frontiers in Environmental Science, 11, 1164900.
https://doi.org/10.3389/fenvs.2023.1164900
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Therrien, L. (2022). HELP - Long Branch Red Squirrel Habitat.Change.org.
https://www.change.org/p/help-long-branch-trees-at-risk
Turner, N. (2019). Indigenous Peoples' Medicine in Canada. The Canadian Encyclopedia.
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Vallis, C. (2023). Waterloo's urban forest receives national healing forest designation. University of
Waterloo – Waterloo News.
https://uwaterloo.ca/news/environment/waterloos-urban-forest-receives-national-healing-forest
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Education and Professional Development
To build more sustainable urban communities, there is a growing need to integrate
urban ecology into our cities across Canada by incorporating living ecosystems into
urban planning and development projects. This goes beyond protecting parks and
planting trees; it means reconnecting people with nature, developing a relationship
between city residents and the natural features of their cities, and understanding the
importance of urban forests for sustainability in cities. Building this connection
involves more than just exposure to green spaces and requires a deeper
understanding of the role of urban forestry in Canadian cities, and fostering
knowledge that will help to best implement it. Consequently, educational and
environmental programs are adapting to these demands, fostering a population and
workforce that is ecologically educated and informed.
Highlights
Urban ecology is essential
Sustainable cities require integrating nature and fostering public connection with
urban forests.
Education is evolving
Programs across Canada are training ecologically informed citizens and
professionals.
Higher education leads
Universities now offer specialized degrees and training in urban forestry.
Professional development matters
A wide range of certi�cations, workshops, and partnerships support urban forestry
careers.
Broad outreach is growing
Many organizations deliver environmental education nationwide, linking urban
populations with nature.
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Urban forestry practices and priorities are ever-changing, as there is a growing need
to utilize urban ecological education in building more sustainable and treed urban
communities, as well as raising an urban population that is ecologically educated
and informed. Thus, fostering adaptive and diverse educational programs is integral
to keeping young Canadians, working practitioners, and the public educated and
properly informed. Also, disseminating knowledge and information on new and
developing urban forestry practices and priorities is a vital part of keeping Canadian
citizens and professionals educated and ready for professional development in the
�eld of urban forestry.
Higher Education
Urban forestry in Canada emerged from scholars and graduates from the Faculty of
Forestry, University of Toronto (UofT), now part of the John H. Daniels Faculty of
Architecture, Landscape and Design [see chapter: History of Urban Forests in
Canada]. In addition, since 1997, many urban forestry professionals have graduated
from the UofT's Master of Forest Conservation (MFC) program, the �rst graduate-
level program to have urban forestry courses, internships, and capstone papers in
urban forestry. MFC graduates specializing in urban forestry have been urban
forestry leaders in Canada’s municipalities, NGOs, federal and provincial
governments, consulting groups, and abroad. In the past ten years, more educational
opportunities across Canada have been created within existing or new academic
programs, offering urban forestry programs, courses, topics, and Canada’s �rst
Bachelor of Urban Forestry program (2015) and the more recent Master of Urban
Forest Leadership at the University of British Columbia. The Urban Forestry Training
Program (Ufor) is designed to train new urban forest managers. The Ufor network
consists of members from universities across Canada, as well as collaborators from
around the globe. It includes graduate students (both MSc and PhD), postdoctoral
researchers from various parts of Canada, and many partner organizations.
Today, there are eight faculties with accredited forestry-speci�c programs in Canada,
although some other departments and schools, such as Environmental Studies/
Sciences, Geography, and Landscape Architecture, also provide courses related to
urban forestry. All of these post-secondary institutions across Canada are also
advancing the pace of public education about urban forestry through e-lectures,
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seminars, conferences, and in-person workshops.
Professional Development
In practice, urban forestry involves the collaboration of diverse and cross-sector
professionals, including foresters, arborists, landscape architects, biologists,
ecologists, utilities workers, urban planners, engineers, politicians, economists, policy
analysts, geographers, information analysts, project managers, and others. Some
aspects of urban forestry may require working with licensed practitioners who must
meet certain requirements set by professional regulatory bodies; as a result, the
educational backgrounds of urban forestry professionals can vary widely across
different sectors.
International programs such as the International Society of Arboriculture (ISA) offer
multiple levels of arboriculture certi�cations, which are valid internationally. In
Canada, a provincial certi�cation as a Registered Forest Professional (RFP) is
required for arboriculture work in most provinces. Urban foresters are often
registered as RFPs and can be employed by municipalities, regionally, and by the
province. While accredited programs offer professional urban forestry education,
countless organizations and community movements also offer educational
opportunities for both the public and practicing professionals. These organizations
range from community-led events and workshops to talks and meetings that are
occasionally run by municipalities or independent organizations. Educational and
professional development opportunities, such as Project Learning Tree and the
Canadian Institute of Forestry Job Board, also exist through online platforms to serve
and mobilize Canadian Urban Forest Network engagement goals such as connecting
Canadians with forestry jobs, promoting regular dialogue, and providing entry points
for Canadians hoping to enter or progress in the forestry sector (Tree Canada, 2024;
SFI, 2024; CIF, 2024)
Many regions across Canada have in-person meetings to provide interdisciplinary
experiences. Hands-on workshops and educational events are common ways to
foster professional development and community education. Additionally, urban
forestry education is kept relevant and adaptive through the publication of timely
urban forestry topics and special series on prevalent and signi�cant topics in urban
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forestry, such as the engagement of Indigenous peoples in urban forestry, or
deconstructing myths and preconceptions about trees.
Additionally, programs such as the Canadian Urban Forest Network and Conference
at Tree Canada offer resources and national networking, learning, and professional
development opportunities for all Canadians (Tree Canada, 2024). Federally funded
and non-government organizations collaborate through projects such as the
Government of Canada’s collaboration with the Federation of Canadian
Municipalities’ Green Municipal Fund to plant two billion trees across Canada by
2031 (FCM, 2024). This program provides educational opportunities, �nancial
support, and technical resources to Canadians and organizations wishing to engage
in urban greening and tree planting efforts, giving Canadians the information and
support they need to properly grow, manage, and protect their tree canopies.
Urban Forestry-Related Public Education
As the urban population grows and more land is urbanized in Canada, urban forests
and related environmental education are critical in fostering connections among
individuals, cities, and the environment. In support of this, many educational and
environmental programs, particularly those concerning individuals in urban settings
and their relationship with the natural environment, have been established in Canada.
Thus, besides professional schools and bodies, diverse organizations are engaged in
urban forestry and relevant environmental education programs. They range from
government entities to non-pro�t organizations and NGOs.
A recent study conducted to understand a broad spectrum of urban forestry and
urban ecology-related educational programs in Canada revealed some interesting
results (Puric-Mladenovic & Bardekjian, 2024). This study focused primarily on
organizations with national, provincial, and regional scopes and included a few local
programs for larger urban centers. For Vancouver, Calgary, and Montreal, data mining
involved examining local and municipal educational programs related to urban
forestry. The study surveyed 188 organizations across Canada, which collectively
offered 482 diverse environmental education programs that are either directly or
indirectly related to urban forestry or urban ecology. These organizations come from
various backgrounds, with primary activities ranging from biodiversity and
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conservation, climate change, and ecotourism to education, forestry, landscape/
horticulture, public outreach, and urban forestry. As expected, the results of the study
reveal that organizations primarily focused on education (47%) tend to deliver the
majority of educational programs. However, organizations with a primary focus on
biodiversity and conservation take second place, providing 29% of educational
programs, highlighting the growing importance of education related to urban
environments and ecology.
Resources
University of Alberta: Faculty of Agricultural, Life & Environmental Sciences
Program: Bachelor of Science in Forestry
University of British Columbia: Faculty of Forestry
Programs: Bachelor of Urban Forestry; Master of Urban Forestry Leadership
University of Northern British Columbia: Forest Ecology and Management
Program: Bachelor of Science in Forest Ecology and Management
University of New Brunswick: Faculty of Forestry & Environmental Management
Bachelor of Science in Forestry; Bachelor of Science in Environmental Management
Université de Moncton à Edmundston: École de foresterie
Programs: Bachelor of Forest Management; Master of Science in Forestry
Lakehead University: Faculty of Natural Resources Management
Program: Honours Bachelor of Science in Forestry
University of Toronto: Graduate School of Forestry, Institute of Forestry and Conservation
Program: Master of Forest Conservation
Université Laval: Faculté de foresterie, de géographie et de géomatique
Program: Bachelor of Forest Management and Environmental Studies
The Urban Forestry Training Program (Ufor). The network of seven Canadian universities.
Fleming College, Ontario: School of Environmental & Natural Resource Science
Program: Arboriculture (Co-op)
Post-secondary Forestry and Natural Resources Education
Canada
Arboriculture Degrees and Certificates
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Humber College, Ontario: School of Applied Technology
Program: Urban Arboriculture - Tree Care
Olds College of Agriculture & Technology, Alberta
Program: Arboriculture Technician Certi�cate
Alberta Learning Information Service. (n.d.). Forester: Certi�cations in Alberta.
https://alis.alberta.ca/occinfo/certi�cations-in-alberta/forester/
Forest Professionals British Columbia. (n.d.). Become a forest professional – Registered Professional
Foresters.
https://www.fpbc.ca/become-a-forest-professional/registered-professional-foresters/
Forestry is not a regulated profession in this province
Association of Registered Professional Foresters of New Brunswick. (2020). ARPFNB
Admission Process. https://www.arpfnb.ca/admission-process.php
Registered Professional Foresters Association of Nova Scotia. (2017). About Us – RPFANS.
https://rpfans.ca/aboutus.php
Ontario Professional Foresters Association. (n.d.). Practising Forestry – How to become a professional
forester.
https://opfa.ca/practising-forestry/becoming-a-professional-forester/
Professional Forester Designations by Province
Alberta
British Columbia
Manitoba
New Brunswick
Nova Scotia
Ontario
Prince Edward Island
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Forestry is not a regulated profession in this province
Government of Quebec. (2025). Forestry Professionals – Training and Requirements.
https://www.quebec.ca/en/employment/learn-trade-occupation/exploring-trades-occupations/21111-
forestry-professionals
Association of Saskatchewan Forestry Professionals. (2024). ASFP – Becoming a member.
https://www.asfp.ca/registration/becoming-a-member
International Society of Arboriculture (ISA). (n.d.). ISA – Welcome.
https://www.isa-arbor.com/
ISA Ontario. (2024). Welcome to the Ontario Chapter of the International Society of Arboriculture.
https://www.isaontario.com/
ISA Prairie. (2025). Welcome to the Prairie Chapter of the International Society of Arboriculture.
https://isaprairie.com/
SIAQ. (n.d.). SIAQ – Société Internationale d’Arboriculture - Québec.
https://siaq.org/fr/
Canadian Institute of Forestry (CIF). (2024). CIF Job Board.
https://www.cif-ifc.org/job-board/
Federation of Canadian Municipalities (FCM). (2024). Government of Canada and FCM’s Green Municipal
Fund Collaborate on 2 Billion Trees Program. Retrieved from FCM News
https://fcm.ca/en/news-media/news-release/gmf/government-canada-and-fcms-green-municipal-
fund-collaborate-2-billion-trees-program
Forest Professional Regulators of Canada. (2025). Programs and Services.
https://www.fprc-orpfc.ca/programs
International Society of Arboriculture (ISA). (2018). ISA Certi�cation and Credentials.
https://wwv.isa-arbor.com/certi�cation/index
Sustainable Forestry Initiative (SFI). (2024). Project Learning Tree (PL T) Canada.
https://forests.org/plt-canada/
Quebec
Saskatchewan
International Association of Arboriculture
Canadian
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Sustainable Forestry Initiative (SFI). (n.d.). SFI Urban and Community Forest Sustainability Standard – How
to certify.
https://forests.org/how-to-certify/
Tree Canada. (2024). Canadian Urban Forest Conference 2024.
https://treecanada.ca/research-engagement/canadian-urban-forest-conference/about-the-conference/
Canadian Forests. (n.d.). Canadian Universities and Colleges offering forestry and forest management
programs.
https://www.canadian-forests.com/universities-colleges.html
Canadian Institute of Forestry. (2022). Forest Education.
https://www.cif-ifc.org/get-engaged/forest-education/
Conway, T.M., Ordóñez, C., Roman, L. A. et al. (2021). Resident Knowledge of and Engagement with
Green Infrastructure in Toronto and Philadelphia. Environmental Management 68, 566–579.
https://doi.org/10.1007/s00267-021-01515-5
Puric-Mladenovic, D. and Bardekjian, A. (2024). National Urban Environmental Education Scan (NUEES) (in
preparation for publishing).
Further Reading
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Additional Resources
Expand your knowledge with the curated resources and further reading below.
Resources
Cardou, F., Aubin, I., Bergeron, A., & Shipley, B. (2020). Functional markers to predict forest ecosystem
properties along a rural-to-urban gradient. Journal of Vegetation Science, 31(3), 416-428.
https://doi.org/10.1111/jvs.12855
Cities4Forests. (2020). Urban Forests for Healthier Cities: Policy, Planning, Regulations, And Institutional
Arrangements – Learning Guide.
https://cities4forests.com/wp-content/uploads/2020/06/C4F-Urban-Forests-for-Healthier-Cities.pdf
EcoHealth Ontario. (2025). Policy Toolkit for Developing and Implementing Ecohealth Policies and
Practices.
http://ecohealth-ontario.ca/policy-toolkit/
Engel-Yan, J. B., Kennedy, C. A., & Pressnail, K. D. (2005). Natural infrastructure and neighbourhood
sustainability. Paper presented at the Proceedings, Annual Conference - Canadian Society for Civil
Engineering.
https://www.scopus.com/inward/record.uri?eid=2-
s2.0-33748971338&partnerID=40&md5=34c8a66d2028283f3733d716ee074db5
Forest Gene Conservation Association. (n.d.). Homepage – FCGA.
https://fgca.net/
Green Infrastructure Ontario Coalition (GIOC). (2016). Toolkit Part I: Communicating the Bene�ts of the
Urban Forest in a Municipal Context.
https://greeninfrastructureontario.org/app/uploads/2016/06/UF-Toolkit-Part-I-Communicating-
Bene�ts-Bulletin-Final.pdf
Hotte, N., Nesbitt, L., Barron, S., Cowan, J., Cheng, Z. and Sheppard, S. (2016). The social and economic
values of Canada's urban forests: A national synthesis. Canadian Forest Service.
http://dx.doi.org/10.13140/RG.2.2.13909.12001
Housing, Infrastructure and Communities Canada. (2022). Canada and Prince Edward Island invest in new
water infrastructure for Charlottetown. Government of Canada.
https://www.canada.ca/en/housing-infrastructure-communities/news/2022/03/canada-and-prince-
edward-island-invest-in-new-water-infrastructure-for-charlottetown.html
Larouche, J., Rioux, D., Bardekjian, A. C., & Gélinas, N. (2021). Urban forestry research needs identi�ed by
Canadian
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Canadian municipalities. Forestry Chronicle, 97(2), 158-167. doi:10.5558/tfc2021-017
Mendes, P ., Bourgeois, B., Pellerin, S. et al. (2024). Linkages between plant functional diversity and soil-
based ecosystem services in urban and peri-urban vacant lots. Urban Ecosystems, 27, 1011–1026.
https://doi.org/10.1007/s11252-023-01470-5
Ontario Network on Ecosystem Services. Access Information – Guidance.
https://onecosystemservices.ca/information/guidance/
Owen, D., Fitch, A., Fletcher, D., Knopp, J., Levin, G., Farley, K., . . . Jones, L. (2024). Opportunities and
constraints of implementing the 3–30–300 rule for urban greening. Urban Forestry & Urban Greening, 98,
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Toronto Public Health. (2015). Green City: Why nature matters to health – An Evidence Review. Toronto,
Ontario.
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Quinton, J. M. and Duinker, P . N. (2019). Beyond burial: researching and managing cemeteries as urban
green spaces, with examples from Canada. Environmental Reviews, 27(2), 252-262.
https://doi.org/10.1139/er-2018-0060
Alivio, M. B., Šraj, M. and Bezak, N. (2023). Investigating the reduction of rainfall intensity beneath an
urban deciduous tree canopy. Agricultural and Forest Meteorology, 342, 109727.
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Borelli, S., Conigliaro, M., Di Cagno, F. (2023). Urban forests: a global perspective. Rome, FAO.
https://doi.org/10.4060/cc8216en
Kane, R. (2004). The Green Fuse: Using plants to provide ecosystem services – a literature review. SPROUT
Sustainable Plant Research and Outreach.
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Washington.
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The Nature Conservancy. (2022). The Biodiversity Action Guide.
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Sustainable Forestry Initiative. (2024). SFI Urban and Community Forest Sustainability Standard.
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University of Washington. (2018). Green Cities: Good Health – More Resources.
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Wentworth, J. (2017). Urban Green Infrastructure and Ecosystem Services – Research Brie�ng.
Non-Canadian
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Parliamentary O�ce of Science and Technology, UK.
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