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The Trees Lining our Streets: Diversity and equity of Canada’s street trees

Video source: School of Cities

Cities across Canada are working to grow their urban forest based on the range of environmental, social, and health benefits provided by trees. These benefits include cooling during hot summer months, reduction in local flooding vulnerability, fostering community cohesion and a sense of place, and contributing to positive mental and physical health outcomes. The number of trees, their size, and species composition influence the type and extent of benefits created. However, most benefits are localized: experienced in the immediate area adjacent to the trees. As a result, an even spatial distribution of trees is important to ensure that all urban residents are receiving those benefits.

Drawing on a recently created repository of municipal street tree inventories across Canada, Alexander Martin (MSc ‘25, Department of Geography & Planning, U of T) and Tenley Conway (Professor, Department of Geography, Geomatics and Environment, UTM) examined the density, size, and species of street tree assemblages in 32 Canadian cities to understand if trees are spatially distributed evenly and if distributions of street trees unfairly burden marginalized populations. They calculated the Gini index, a measure of inequality, to determine if trees are evenly distributed. They then conducted regression analyses using variables from the Canadian Index of Multiple Deprivation to determine if marginalized communities are inequitably associated with fewer, smaller, or less diverse trees in their neighbourhoods.

There are substantial inequalities in street tree distribution in the 32 cities, and also inequities associated with population density and four measures of socio-economic deprivation. However, specific street tree inequities varied between cities, highlighting the importance of understanding local context. Cities should address inequities, ensuring all residents equally benefit from street trees. Steps toward just street tree assemblages include planning for adequate space for large trees to thrive, focusing on diversifying species in neighbourhoods with high populations, supporting street tree planting and stewardship in marginalized communities, and using tools like the Gini index to track progress over time.

Open Urban Forests Project (OUFP) repository

The Canadian Institute of Forestry through their Open Urban Forests Project (OUFP) created a repository of municipalities’ tree inventories in 2024. The repository represents the first effort of its kind in Canada to support learning and informed decision-making about urban trees.

Conway and Martin used the repository data to explore 32 cities’ street tree populations. Street trees are often the most visible trees in urban areas. These trees face challenging growing conditions, like high levels of vehicle pollution and limited growing space, that may restrict their growth and limit the type of species that can survive. In most cases, street trees are the responsibility of municipal governments, meaning management by municipal urban foresters and arborists directly impacts the planting and health of street trees. These trees and their attributes are also most frequently recorded in municipal tree inventories.

Pacific Maritime
Montane Cordillera
Prairie
Mixedwood Plain
Atlantic Maritime
City in this study with street tree data

Comparing Canada’s street trees populations

Street Tree Density

Street Tree Density (trees/km²)

The number of street trees per square kilometre of city land area. Higher density suggests more trees lining streets, which increases the potential for shade, stormwater absorption, and urban cooling.

Sort:
Vancouver
1283.0
Mississauga
1147.0
Toronto
1135.2
Victoria
1024.9
Montreal
951.2
Regina
881.5
Ajax
763.0
Longueuil
740.8
Burlington
739.5
Windsor
699.9
New Westminster
686.8
Winnipeg
682.0
St. Catharines
653.7
Whitby
621.4
Calgary
575.9
Ottawa
575.6
Kitchener
563.0
Edmonton
552.5
Strathcona County
540.2
Waterloo
538.3
Niagara Falls
497.7
Guelph
489.4
Peterborough
478.4
Kingston
466.0
Welland
451.8
Quebec City
410.3
Halifax
377.8
Fredericton
358.0
Lethbridge
273.0
Maple Ridge
246.1
Moncton
230.5
Kelowna
183.3
Atlantic Maritime Prairie Pacific Maritime Montane Cordillera Mixedwood Plain

Canada’s 32 cities contain over 3 million street trees, with the number of trees ranging from 9,787 trees in New Westminster, B.C. (population 78,916 in 2021) to 652,547 trees in Toronto (population 2,731,571 in 2021). All municipalities have more small trees and fewer large trees than recommended size class benchmarks, which may be a result of smaller stature trees being planted or a dominance of young trees that have not yet reached their mature height.[1]

Collectively, there is a diversity of species planted along Canada's city streets, with 726 street tree species across the 32 study cities. Vancouver has the most species (373), while Regina has the fewest (29). In most cities a few species dominate, with just four species representing 34% of the trees in the dataset. This is even more pronounced in the six Prairie cities in the dataset, with green ash and American elm comprising more than half of their street trees.

The percentage of each municipality’s street trees that are native species is highly variable, ranging from just under 5% in Maple Ridge B.C. to 89% in Regina, Sask.. While warmer Canadian municipalities have a larger number of species, they also tend to have a smaller percentage of native street trees. Additionally, there are notable differences between nearby cities. For example, in Ontario, St. Catherines has 28% native street trees and Welland has 48%, but they are only 25 km apart. This suggests that management decisions, in addition to climate and other biophysical factors, are important influences on what species are present in a given city.

Winnipeg, MB · Prairie

Street treedensityMedianDBHBasalareaSpeciesrichness% nativetrees

Montreal, QC · Mixedwood Plain

Street treedensityMedianDBHBasalareaSpeciesrichness% nativetrees

Street tree equality

Street tree equality is reached when there is an even spatial distribution of trees, which can provide similar levels of benefits to all neighbourhoods in a city. Many Canadian municipalities are working to create more equal distributions of urban trees.

Conway and Martin set out to explore if street tree populations are equally distributed across each city. To measure equality, they used the Gini Index. Traditionally, the Gini Index has been used to measure income (in)equality, but in recent years it has been applied to understanding inequalities in urban tree distributions. Index values less than 0.2 are generally considered to represent equal distributions and those over 0.5 indicate significant disparity. However, benchmarks specific to urban forests have not been identified.

The Gini index can also be depicted graphically through Lorenz curves, which show the proportion of trees associated with the cumulative share of people. Perfect equality is represented by the straight y=x. Curves further from the line of equality indicate greater inequality.

0025%25%50%50%75%75%100%100%Line of perfect equalityLorenz curveABCumulative population shareCumulative tree count

Gini = A / (A + B)

The curves show relatively high levels of inequality for neighbourhood tree count (median Gini = 0.401), with Fredericton, N.B. having the most equal distribution (Gini = 0.259) and Maple Ridge, B.C. (Gini = 0.681) having the least. The distribution of neighbourhood basal area, a measure reflecting the cumulative volume of trees associated with the magnitude of benefits produced, showed a median Gini value of 0.469, with highest equality in Windsor, Ont. (Gini = 0.324) and least equality in Lethbridge, Alta. (0.709).

Gini index — Tree Count

The Gini index for neighbourhood tree count measures how evenly street trees are distributed across a city's neighbourhoods. Values closer to 0 indicate more equal distribution; values closer to 1 indicate high inequality.

Sort:
0.10.20.30.40.50.60.70.8
Maple Ridge
0.681
Lethbridge
0.552
Kelowna
0.544
Edmonton
0.536
Quebec City
0.512
Longueuil
0.507
Halifax
0.495
Kingston
0.492
Ottawa
0.489
Calgary
0.488
Moncton
0.476
Ajax
0.455
New Westminster
0.445
Strathcona County
0.421
Kitchener
0.409
Toronto
0.402
Welland
0.400
Niagara Falls
0.396
Waterloo
0.386
Mississauga
0.384
Winnipeg
0.379
Montreal
0.365
Peterborough
0.355
Guelph
0.350
Vancouver
0.348
Windsor
0.345
Whitby
0.339
Victoria
0.338
St. Catharines
0.309
Burlington
0.303
Regina
0.283
Fredericton
0.259
Atlantic Maritime Prairie Pacific Maritime Montane Cordillera Mixedwood Plain

Street tree equality

Are unequal distributions of street trees unfairly burdening marginalized populations? In other words, are the uneven distributions creating inequities between neighbourhoods with different socio-demographics? Such inequities are common in many U.S. cities,[2] with lower income households and racial minorities often living in neighbourhoods with relatively low tree canopy cover.

Conway and Martin explore the possibility of inequities using the Canadian Index of Multiple Deprivation, developed by Statistics Canada.[3] The index includes four measures:

  • Residential instability, which measures fluctuations in neighbourhood residents,
  • Economic dependency, which addresses a population’s reliance on the workforce,
  • Ethno-cultural composition, which measures the immigrant and visible minority populations, and
  • Situational vulnerability, which describes additional demographic characteristics such as education levels and home value.
Positive association Not significant Negative association Each dot = 1 city (n = 23)
Tree Density(trees/km²)Median DBH(cm)Basal Area(m²/km²)Species Diversity(n)Population DensityResidential InstabilityEthno-cultural CompositionEconomic DependencySituational Vulnerability

Insights

Street tree populations reflect a complex landscape of inequities across Canadian cities. There are specific relationships between deprivation index measures and tree density, tree size, and species richness varying between cities. The findings highlight that street tree inequities cannot be generalized across cities, and municipal responses must be tailored to local realities.

Neighbourhoods with higher population density regularly have a higher density of street trees but a lower diversity of species. This may reflect how municipal urban foresters prioritize planting along streets in denser residential neighbourhoods where other green spaces are more limited, but rely on a small number of species that are known to survive in stressful conditions associated with constrained planting sites.

Residential instability is frequently negatively associated with tree density, median DBH, and basal area. This may be because in areas with lower instability – generally longer-term, wealthier residents living in owner-occupied, single-family houses – residents are requesting more street tree plantings and performing more consistent stewardship to helping trees thrive.

Situational vulnerability was often positively or not significantly associated with tree density and our two measures of tree size. This differs from the negative associations often observed for residential instability and ethnocultural composition. This distinction may be due to neighbourhoods with higher situational vulnerability containing older housing and lower levels of recent re-development, which results in larger trees.

Calls to action

Cities need to plant and maintain large trees. Many cities already prioritize protection and planting of shade trees, which can be challenging due to stressful roadside conditions and infrastructure conflicts. However, the overabundance of smaller street trees across the dataset suggests that more work is needed to meet size class benchmarks that are associated with increased and sustained street tree benefits. Re-designing spaces for larger stature trees, including adopting soil volume standards – like the City of Toronto has within the Toronto Green Standard – is needed to ensure adequate space for root growth, supporting larger tree growth.

Cities should plant a diversity of species. Increased species diversity will ensure that a variety of benefits are produced, while also reducing a city’s vulnerability to pests and disease. This is particularly important in prairie cities, which are dominated by green ash and American elm. Both species are vulnerable to pests (emerald ash borer and Dutch elm disease) that have decimated ash and elm populations elsewhere in North America.

Monitor equality of spatial distributions. Adopting metrics like the Gini Index can quantify current unevenness and allow cities to track changes over time. Many Canadian cities have invested in tree planting initiatives, but it remains unclear if new plantings have increased or decreased unequal distributions.

Investigate local drivers of inequity. The analysis found that inequities in street trees are common, but the specific socio-demographic relationship varied between cities. This suggests that local histories and current conditions matter, with efforts to understand city-specific inequities needed to develop strategies to grow more equitable distributions.

Next steps

While identifying uneven distributions and inequities within street trees or across the urban forest is an important first step, simply planting more trees in underserved areas will not necessarily achieve a just outcome. Rather, recognitional justice concerns need to be addressed, which acknowledges that different communities have diverse needs and expectations. With funding from the School of Cities UCG Catalyst Grant, Tenley Conway and PhD student Isaac Mendita are working in partnership with the City of Toronto Urban Forestry division and local tree planting NGOs to engage in community mapping in two marginalized communities identified as having below average tree cover. Through this project we hope to learn where community members do and do not want trees planted, along with desired tree characteristics. Findings will be shared with community leaders and research partners to develop an approach that incorporates communities’ needs and helps guide future tree planting efforts.

Related publications and resources


  • Martin, A.J.F., A. Fleming, & T.M. Conway, "Distributional inequities in tree density, size, and species diversity in 32 Canadian cities," npj Urban Sustainability 5, no. 18 (2025), DOI
  • Martin, A.J.F. & T.M. Conway, "Using the Gini Index to quantify urban green inequality: A systematic review and recommended reporting standards," Landscape and Urban Planning 254, no. 105231 (2025), DOI
  • Martin, A.J.F., L.G. Olson, E.S. Bacon, et al., "A biogeographical analysis of taxonomic diversity and native species dominance in 32 Canadian street tree populations," Urban Ecosystems 28, no. 158 (2025), DOI
  • Martin, A.J.F., L.G. Olson, E.S. Bacon, et al., "The structural diversity of Canada's urban forests: A national summary and an analysis of street tree size across ecozones, city sizes, and within cities," Journal of Forestry 123, 217–240 (2025), DOI
  • Canadian Institute of Forestry/Institut forestier du Canada. "Open Urban Forests." Link

Footnotes

[1]

N.A. Richards, “Diversity and stability in a street tree population,” Urban Ecology 7, no. 2(1983): 159–171, DOI; and Andrew A. Millward and Senna Sabir, “Structure of a forested urban park: Implications for strategic management,” Journal of Environmental Management 91, no. 11 (2010): 2215–2224, DOI.

[2]

Elliott Volin, et al., “Assessing macro-scale patterns in urban tree canopy and inequality,” Urban Forestry and Urban Greening, 55, (2020): 126818, DOI, and Dexter H. Locke, et al., “Residential housing segregation and urban tree canopy in 37 US Cities,” Urban Sustainability 1, n.15 (2021), DOI

[3]

Statistics Canada. (2023). The Canadian Index of Multiple Deprivation, 2021. Statistics Canada Catalogue no. 45‑20-0001.