Compendium of Best Management Practices for Canadian Urban Forests


 
  
 
 
Welcome to the first version of the Compendium of Best Management Practices for Canadian Urban Forests. Simply put, urban forests' time has come. As Canada moves into the 21st century, the 80%+ of Canadians who live in urban communities are increasingly concerned about the viability of their forests. And not just for aesthetic reasons, but for the many ecological, architectural, climatic, psychological and monetary reasons as well. These concerns are pushing the Canadian urban forest envelope like never before. Employment in urban forestry is at an all-time high. Urban forests are making their way into municipal and provincial legislation and into national strategic documents. Membership in urban forest organizations is at an all-time high. Municipalities are being increasingly engaged in strategic urban forest planning. Heritage tree protection is becoming widespread. Environmental and forestry conferences are increasingly including Canada's 9th Forest Region (its urban forests) in their discussions and agendas. Think of this document as the prototype to help you the practitioner with the very best in management practices to ensure that these forests flourish making Canada's cities that much more liveable and an even greater envy of the world. Use it well.
 
Michael Rosen, R.P.F.
Vice President, Tree Canada Foundation

January 2006 



Acknowledgements


We would like to thank the Canadian Forest Service, a sector of Natural Resources Canada, for sponsoring this project of the Tree Canada Foundation. We would also like to extend our appreciation to everyone who provided comments: Andy Kenney, David Domke, Tony Fleischmann, Mark Peterson, Stephen Smith, Julian Ambrosii and Bernard Kradjian.

– Adrina Bardekjian Ambrosii, Author 




PURPOSE OF THIS COMPENDIUM
The purpose of the Compendium is to provide a web-based resource which outlines for municipalities, residents and elected officials some of the components and technical standards of a municipally-based urban forest program. Offering websites, links to on-line resources, initiatives and programs, the Compendium is a dynamic document. We welcome your suggestions for any new additions (or deletions) to the site (see the Submissions section).

 
According to the Canadian Urban Forest Strategy, most people envision endless expanses of closed canopies of mature trees when they think of a forest; but what comes to mind when we think of an urban forest? Trees in containers on sidewalks? Forests in ravines? Backyard trees on lot lines? In 1974 Jorgensen [1] defined the term urban forestry in 1974 as "a specialized branch of forestry and 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 [2] society.  These contributions include the over-all ameliorating effect of trees on their environment, as well as their recreational and general amenity value."
Deneke [3] expanded on the term:
"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 benefits for people. The definition 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 on-going tree planting, protection, and care programs." 
 
Over the years, many other definitions have been proposed, however they all recognize that the urban forest does not stop at the city limits.  Urban forestry embraces the management of trees as well as the associated biotic and abiotic components in small communities and the interstitial areas between.  If the traditional view of forestry focuses on the sustained production of forest products and ecological services in a wildland context then urban forestry focuses on the provision of a wide array of economic, environments and social services to urban society.
 
The history of Canada and the history of its forests are very much intertwined: from the use of the forest by First Nations, the colonization by Europeans, the era of logging white pine for the British navy, the expansion of land clearing in the 1800s to the birth of the conservation movement at the turn of the last century. It was during this last era that Canadian urban forests began. The development of the major park systems in Canada often incorporated forest elements: Stanley Park in Vancouver (created in 1888), High Park in Toronto (1873), Parc Mont-Royal in Montreal (1876) and Point Pleasant Park in Halifax (1866) all prominently featured aspects of the Coast, Deciduous, Great Lakes-St. Lawrence and Acadian Forest Regions. However, aside from roadside planting projects and the most rudimentary protection of natural forests within the scenario of a suburbanizing Canada, no major efforts to develop urban forest programs in Canada were developed until the 1960s, when Dutch Elm Disease struck. Here, the effects of invasive pathogens and monoculture plantings came to roost as thousands of kilometres of roadsides were affectively denuded as a result of the effects of the disease. This resulted in a chain of events which quickly developed urban forestry, including:
- The term "urban forests" by Prof. Erik Jorgensen and the creation of and urban forest program at the University of Toronto in the 1970s;
- The support from 1972-1979, by the Canadian Forest Service of the urban forest program "A Forest for Man"; 
- The International Urban Forestry Conference at Laval University in 1979 (Canada's first);
- The rapid expansion in the 1980s of municipal forestry departments throughout Canada;
- The 1st Canadian Urban Forest Conference in Winnipeg in 1993;
- The first definition of urban forests in legislation in Ontario's Professional Foresters Act 2000;
- The formation of the CANUFNET listserve for urban foresters as a result of the 5th Canadian Urban Forest Conference in 2003;
- The integration of urban forests in the National Forest Strategy 2003-2008; and
- The formation of the Canadian Urban Forest Network in 2004.

 

Protecting and conserving urban forests through proper management is vital to sustaining healthy communities. Urban forests provide a multitude of benefits from an ecological, climatic, architectural, psychological and monetary point of view. They provide habitat and food sources for wildlife, cooler watercourses, mitigate noise and dust levels, improve air and water quality, absorb pollutants, sequester carbon and help conserve energy. Understanding the functions, values and services that urban forests provide are integral to their successful management.
 
Websites & Resources
 
Bibliographical Resources
Kuo, F. (2003). The role of arboriculture in a healthy social ecology. Journal of Arboriculture, Vol. 29 (3), pp. 148-155.
McPherson, G. (2000). Urban Forestry Issues in North America and Their Global Linkages. Western Center for Urban Forest Research and Education, Pacific Southwest Research Station: Davis, CA.
Westphal, L. (2003). Urban greening and social benefits: a study of empowerment outcomes. Journal of Arboriculture, Vol. 29 (3), pp. 137-147.
 

Urban Forest Practices

The following components are essential considerations for effectively developing and implementing an urban forest program. Each practice is supplemented with website links, online documents and resources. This resource is dynamic and we welcome any new additions to the site (see Submissions section).
 
Urban Forestry Best Management Practices for Ontario Municipalities, ISA Ontario

Forestry Commission: Handbook 5 (1989). Urban Forestry Practice. HMSO Publications Centre, London, England.
 
Conservation of trees in the urban environment can only be achieved effectively through the development and implementation of a strategic urban forest management plan that standardizes policies and practices surrounding activities related to trees. Many recommendations have been described (Kenney 1996; Nilsson 2000; Konijendijk 1999; Tschantz and Sacamano 1994; Pouyat and Zipperer 1992; Matheny and Clark 1998) and include: increasing the number of healthy trees and sustaining existing canopy cover, building a basic understanding of ecological principles within the human community, establishing region wide policies and standards for best management practices, developing and implementing strategic management plans based on tree inventories and GIS technologies, undertaking more research on the value of the ecological benefits provided by the urban forest, and; implementing functional urban design strategies that consider benefits such as corridors and shade.
A municipality's strategic urban forest plan attempts to bring together a number of diverse elements in one cohesive document. These elements include:

- Planning, maintenance and protection of trees and how these are linked to the municipalities' Official Plan
- Detailing of responsibilities in Parks, Public Works,
- Bylaw Control and Advisory Committees of the municipality
- Details of tree  inventory, standards for planting, and pruning, pest control, protection during construction, and what operations the municipality is responsible for, and
- Private tree issues, education and regulation
- A plan that encompasses a long-term vision with short-term goals is necessary for the conservation and management of urban trees.

 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites and resources
 
Bibliographical Resources
Federation of Ontario Naturalists (2002). A Smart Future for Ontario: How to Protect Nature and Curb Urban Sprawl in Your Community. Toronto, ON. October 2002.
Greenwood, J., Soulos, G., Thomas, N. (2000). Under cover: Guidelines for shade planning and design. NSW Cancer Council and NSW Health Department Sydney, 1998.
Harris, R., Clark, J., Matheny, N. (2004). Arboriculture: Integrated Management of Landscape Trees, Shrubs, and Vines, 4th Edition. International Society of Arboriculture. Champaigne, IL. 578 pp.
Pouyat, R., and Zipperer, W. (1992). The Uses and Management of Urban Woodlands. In: Proceedings of the Fifth National Urban Forest Conference. Rodbell, P. (editor).  American Forestry Association, pp 26-29.
Smith, D., Mutton, M. (1993). Establishing a naturalized area: A step-by-step guide to planning and installing a natural area on the school grounds. Green Teacher, Vol. 34, pp. 33-36.
van Wassenaer, P. and Kenney, A. (2002). Strategic Urban Forest Management Planning. Faculty of Forestry. University of Toronto.
 
In Canada, legislation is enacted and enforced at the federal, provincial and municipal levels. Because the urban forest is largely managed at the municipal level, it is the municipalities who enact and enforce legislation regarding trees on both municipal and private land. Municipalities can pass these laws only under the authority of enabling legislation from the province (municipalities being creations of the provinces). Some common elements of tree cutting bylaws include:

- Regulating tree protection during construction activities, hydro utility practices, and damaging practices by residents (topping etc.)
-
Heritage trees for protection
-
Building envelope placement, tree preservation plans, permits, replacement trees etc.

Legal precedents in Canada regarding trees on private and public property involve the joint ownership between private landowners and municipalities (Dunster and Murray 1995) Tree by-laws clearly state prohibited activities, exemptions, processes and enforcement through fixed fines and penalties.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Dunster, J., Murray, S. (1995). Arboriculture and the Law in Canada. International Society of Arboriculture. Vancouver, BC. 225 pp.

 

Tree Inventory and the Tree Inspection Cycle

The foundation of an effective urban forest management program is a detailed tree inventory. A tree inventory provides information such as tree health, species, size and location; this information is used to generate reports that can help urban foresters in their strategic planning. Inventory data can be used to identify species diversity and distribution, percentage of canopy cover, size/class distribution, etc. Coupled with an inventory, a tree inspection cycle is integral for proper tree maintenance and hazard abatement. Effective tree monitoring enables park managers, urban foresters and planners to evaluate the urban forest resource and develop short and long-term initiatives which can in turn provide substantial cost savings and mitigate safety issues.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Head, C. (2001). Community Tree Program. Athens-Clarke County, Georgia: Unified Government of Athens-Clarke County: Landscape Management Division.
Kenney, A, Puric-Mladenovic, D. (2001). Neighbourwoods© Tree Inventory Manual. Faculty of Forestry, University of Toronto.
Matheny, N., Clark, J. (1994). A Photographic Guide to the Evaluation of Hazard Trees in Urban Areas. International Society of Arboriculture. Champaign, IL. 85 pp.
Phillips, L.  (1979). Implementing A Street Tree Inventory and Planning System. Weeds, Trees and Turf.  pp.18-20, 22-23.
 
In recent years, Geographic Information Systems (GIS) and other technologies have been increasingly used in urban forest management. A GIS is a database where the output generated is a visual representation of the geographic relationships of that information. The potential for mapping trees has many implications for forest management and education; vector and raster techniques can be used in the digital representation of the geographic data to display and analyze various attributes based on specific objectives (e.g. being able to generate a map displaying underground and overhead infrastructure with elevation data for a proposed planting site; or, coupled with tree inventory data, being able to model sun angle diagrams in relation to existing vegetation or buildings to increase shade provision at a given site, etc.). Other technologies include more sophisticated equipment, hardware and software for dendrology, soil and tree core sampling, leaf area and crown density monitoring, geographic positioning systems (GPS), etc. With the age of technology upon us, the benefit to having access to these tools often proves to be more time efficient and effective in management planning.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Chor, P.L. (2002). Concepts and Techniques in Geographic Information Systems. New York: Prentice Hall.
Falconer, A., Foresman, J. (Eds.). (2002). A System for Survival: GIS and Sustainable Development. Redlands, CA: ESRI Press.
Malone, L., Palmer, A., Voigt, C. (2003). Teacher's Guide: Community Geography: GIS in Action.  Redlands, CA: ESRI Press.
Towle, K. (2002). Using GIS to Identify and Evaluate Forest Conservation and Restoration Opportunities in an Urbanizing Landscape. Poster Presentation. 5th Canadian Urban Forest Conference Oct. 7-9, Region of York, Ontario.
 

Species Selection and Planting

Selecting the appropriate tree species and location for planting is imperative to sustaining a healthy urban forest, providing for a cost effective urban forest program and providing acceptable urban forest solutions to neighbourhoods and communities. The right tree in the right place should always be the urban foresters' modus operandi. Tree species should be considered based on aesthetic appeal, hardiness zone, size, form and site conditions of the growing location. To minimize conflicts and reduce maintenance needs, trees should be visualized at full functional size when surveying a potential site for planting. Selecting a tree that is well suited to the soil conditions, light availability, pedestrian traffic, drainage, space and microclimate of the specific site is essential to its long-term survival and public safety.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Farrar, J. (1995). Trees in Canada. Canadian Forest Service.
Gilman, E. (1996). Trees for Urban and Suburban Landscapes. International Society of Arboriculture. Champaign, IL. 662 pp.
Moll, G. and Young, S. (1992). Growing Greener Cities: A Tree Planting Handbook. Global ReLeaf. Living Planet Press and American Forestry Association, Los Angeles, CA, 126 pp.
ORTHO Books (1982). All About Trees. Chevron Chemical Company.
Watson, G., Himelick, E. (1997). Principles and Practice of Planting Trees and Shrubs. International Society of Arboriculture. Champaigne, IL. 200 pp.
 
The greatest stress on newly-planted (and sometimes established) trees is water stress. Watering can be the most important part of tree maintenance. Related to watering, mulching acts to conserve water on site, keep mowing equipment from damaging trees and minimizes compaction: a common problem in urban soils. Fertilizing urban trees is a common practice to ensure that proper nutrients are available to the tree in nutrient-poor city soils. Cabling involves the installation of wires high in the canopy to allow one tree's branches to support another. Bracing is the installation of large bolts to keep trees from splitting open. Recognizing and removing hazard trees is an important part of urban forest management.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Siewert, A., Siewert, A., Rao, B., Marion, D. (eds.) (2003). Tree and Shrub Fertilization: Proceedings from an International Conference on Tree and Shrub Fertilization. International Society of Arboriculture. 164 pp.

The most common tree maintenance practice is pruning, representing 62% of daily activities in the field. There are several reasons to prune urban trees: to prevent branches from falling on objects or people, to allow remaining branches to bear more weight; to improve the health and quality of the tree by removing damaged, dead, diseased or crossed branches; to control the size and shape of the tree; to correct for storm damage; and clearance from hydro and other utilities. The most widely recognized reason for pruning urban trees is for safety. Pruning can reduce tree size and affect the health of a tree as a result of tissue removal. Reduction of leaf, shoot, or root volumes and the carbohydrate and nutrient reserves they contain directly disrupts and limits potential growth. Ultimate effects of pruning on tree growth and size must be considered in relation to tree age, growth and fruiting habits, stage of tissue development, and the environment to which the tree is exposed (Kozlowski 1991).
 
Websites
 
Online documents (.PDF or .DOC)
 
Bibliographical Resources
Brooklyn Botanic Garden Record. Pruning Techniques. Brooklyn Botanic Garden Inc. New York, New York, 1991. 96 p.
Clair-Maczulajtys, D., Le Disquet, I., Bory, G. Pruning Stress: Changes in the tree physiology and their effects on the tree health. Laboratoire de Physiologie de l'Arbre, Université Paris, France. Symposium on urban tree health, Acta Hort 496. ISHS 1999.
Coder, Kim. Pruning effects on tree growth: Growth regulation consequences. University of Georgia. January 1998.
Gilman, Edward. Trees for Urban and Suburban Landscapes: An Illustrated Guide to Pruning. Delmar: Thomson Learning Inc. Scarborough, Ontario, 1997. 178 p.
Kozlowski, Theodore, Kramer, Paul, Pallardy, Stephen. The Physiological Ecology of Woody Plants. Academic Press, San Diego, California. 1991. 657 p.

One of the most persistent challenges in urban forestry is the ongoing battle between tree roots and pavement. Trees planted close to hard surfaces such as pavement, asphalt, concrete, etc. often suffer from soil volume restriction that leads to root damage and girdling as well as pavement lifting, creating safety hazards for pedestrians. Management practices include planting appropriate tree species, installing covers or grates over planting pits that accommodate tree growth; planting ground covers around tree trunks to reduce foot traffic and compaction; using an appropriate soil medium to encourage deep, tree root growth, constructing continuous channels that connect individual planting pits; and planning for and providing adequate irrigation. A variety of methods have been developed and implemented to increase tree survival in hard surfaces by using the best possible planting method for a given site.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources

Urban woodlots and parks provide wildlife habitat, maintain soil and water quality, are aesthetically appealing and provide a huge amount of human recreational opportunities. There are a number of factors which forest managers must be cognizant of in the management of wooded areas in an urban context. They include:
- Forest
soil compaction: using techniques to restrict traffic in urban woodlots to specific roads and trails

- Invasive species: controlling non-native invasive plant species from displacing native vegetation
- Safety: recognizing hazardous trees and removing them to keep wooded areas safe for people as well as employing techniques to ensure that sight lines are maintained within wooded areas to ensure visitors have a safe and happy experience
Management practices include planting buffer strips to mitigate compaction, pruning to clear sight lines and implementing monitoring programs.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Hilts, S. and Mitchell, P. (1999). The Woodlot Management Handbook: Making the Most of Your Wooded Property for Conservation, Income or Both. Firefly Books. 282 pp.
Hilts, S. and Mitchell, P. (1997). Taking Stock: Preparing an Inventory of Your Woodland. Centre for Land and Water Stewardship, University of Guelph. 46 pp.
Southern Ontario Woodlands: The Conservation Challenge. Federation of Ontario Naturalists. 1999. 164 pp.
Twolan-Strutt, L (1995). Wetlands and Woodlots. North American Wetlands Conservation Council (Canada). 24 pp.
 
 

Tree Protection during Construction/Trees and Building Foundations

Experts agree that tree protection during construction is more important (and less expensive) than tree expansion (see Species Selection and Planting section) programs after the fact. Construction activities such as paving, sidewalk installations, excavation, and road widening can severely affect existing trees. Some areas of impact are root cutting, branch abrasions and trunk fractures; these injuries can lead to rot and decay, structural damage, canopy loss or tree death. Properly valuing green space and implementing a strategy to monitor, sample, measure and protect vegetation is critical to urban development preceding the construction stages to effectively preserve the urban forest and maintain its integrity. Similarly, there exists a wealth of information on the complex relationship between trees and building foundations as they relate to soil types, surface drainage practices and the variation between species of trees.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Despot, D., Gerhold, H. (2003). Preserving trees in construction projects: Identifying incentives and barriers. Journal of Arboriculture, Vol. 29 (5). pp. 267-275.
Grahn, P., Stigsdotter, U. (2003). Landscape Planning and Stress. Urban Forestry and Urban Greening, Vol. 2, pp. 1-18.
Matheny, Nelda and Clark, James. Trees and Development: A Technical Guide to Preservation of Trees during Land Development. International Society of Arboriculture, 1998. 162 p.
Watson, G., Neely, D. (1995). Trees and Building Sites: Proceedings of an International Conference Held in the Interest of Developing a Scientific Basis for Managing Trees in Proximity to Buildings. International Society of Arboriculture, Champaign, IL. 191 pp.
 
Trees planted in the urban environment are often unable to reach their full genetic potential due to unfavourable conditions. Common stresses include soil compaction, salt and air pollution, mechanical injuries and drought. Other environmental stresses include shading and competition for water and nutrients, and artificial light sources (street lamps). A consistent issue in most cities is compaction and the lack of soil volume in sidewalk plantings. Soil compaction in high traffic areas impedes on the root system performing its physiological functions of absorbing water and minerals. Although trees adapt to their environment by adjusting their growth patterns, tactics to promote and improve tree health, such as raising the root ball, spreading a layer of mulch and implementing a watering schedule to suit drainage conditions can greatly increase tree survival. There are a number of techniques and products available to city foresters to assist them in planting in these harsh and unnatural locations.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Costello, L., Perry, E., Matheny, N., Henry, M., Geisel, P. (2003). Abiotic Disorders. International Society of Arboriculture. Champaign, IL. 242 pp.
 

Trees in the urban environment suffer from many stresses that make them susceptible to insects and diseases. Even though most insect species are valuable to trees, some insects can injure trees and weaken structure by defoliating crowns, sucking sap and boring into bark. As such, insects can be categorized by their method of feeding: chewing, sucking or boring. Damage characteristics of each group leave clues for an arborist or tree health care professional to decipher the pest group and implement an effective control measure. Susceptible trees can also become infected by one of two types of diseases: those caused by living agents (diseases) and those caused by nonliving agents (disorders). In either situation, an effective integrated pest management program must be implemented.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Johnson, W., Lyon, H. (1991). Insects That Feed on Trees and Shrubs. International Society of Arboriculture. Champaigne, IL. 560 pp.
MacAloney, H. and Ewan H. (1964). Identification of Hardwood Insects by Type of Tree Injury, North Central Region. U.S. Department of Agriculture Forest Service.
Sinclair, W., Lyon, H., Johnson, W. (2005). Diseases of Trees and Shrubs, Second Edition. International Society of Arboriculture. Champaign, IL. 676 pp.

Invasive and alien plant species can displace native vegetation and may have no natural predators in Canada. Without the presence of their natural controls such as insects and diseases, invasive species may grow aggressively and can monopolize large areas by out-competing native trees by producing toxic chemicals and competing for light and nutrients. Another risk involves the possibility of alien species hybridizing with native vegetation and eventually eliminating native genetic strains. Alien and invasive species can significantly change ecosystem functioning if effective management practices are not implemented. Practices include instigating coordinated policy and education initiatives; avoiding the planting of alien species in landscapes and educating residents about the importance of planting native species; as well as implementing effective monitoring campaigns. 
  
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
 
 
Urban forests help reduce the quantity of storm water flows, soil erosion and stream sedimentation and help improve the quality of storm water runoff through absorption (Bernatzky 1983). Trees attenuate storm water in 3 ways: above ground through interception, evaporation and absorption of precipitation; at ground surface through temporary storage; and below ground through infiltration and permeation (Habecker 2004, PowerPoint presentation). Factors that influence the level of interception and evapotranspiration include tree species, stature, size and leaf area density. Increasing canopy cover is a simple way to help control stormwater runoff and reduce overall quantity.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
 
Forest fires are a natural force in the regeneration of forested ecosystems. However, as our communities have grown to encompass components of the natural forest, and as climate change continues to increase the fire hazard, fire management has become an increasing concern.  Fire management involves proper forest management techniques, public education and changing construction and landscape practices.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources

 

Hydro Line Management

Hydro line operations are a major maintenance practice in all municipalities that can have a large affect on its urban forests. Trees conduct electricity and therefore trees planted under or next to power lines must be regularly pruned or removed to ensure public safety and maintain hydro supply. When tree branches grow into or come in contact with hydro wires, they can cause fires, power outages and can become safety hazards. Some jurisdictions have responded by executing long term plans that involve such practices as site-specific plantings i.e. species that will not reach a height that will interfere, pruning or removing trees to maintain clearance and prevent unsafe conditions.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
International Society of Arboriculture. (1994). Trees and Overhead Electric Wires: Proper Pruning and Selection. 10 pp.
International Society of Arboriculture. Utility Pruning: A Video Guide for Pruning near Utility Conductors.

Emergency Preparedness

The eastern Canadian ice storm of 1998, Hurricane Juan and the BC fires of 2003 illustrated the need for municipalities to properly plan for natural emergencies in the maintenance of their trees. Training and educating urban forestry personnel for emergency situations is important because of the high potential for danger in most forestry operations. According to statistics, more people are injured or killed in the arboricultural and forestry operations than in any other profession - therefore, safety must always be a priority. The risks can only be curtailed with an emphasis on training and prevention.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Darr, B. (1999). Tree Hazard Inspections. Second Annual Tree Board Academy, Alabama Urban Forestry Association Annual Convention: Southern Urban Forestry Associates.
 
Urban forests play an integral role in air quality improvement. Trees reduce temperatures and mitigate the heat-island effect through evapotranspiration; they sequester the emission of greenhouse gasses by removing carbon dioxide from the atmosphere; they remove air pollutants by trapping particulate matter in their leaves, needles and bark. Strategies to help improve air quality include: sustaining healthy large-stature trees; planting trees in heavily populated or polluted areas; and considering long-lived and low maintenance trees for plantings. These strategies help to increase pollution removal; reduce long-term pollutant emissions from power plants and maximize the air quality benefits that trees provide.
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
McPherson, E., Simpson, J. (1999). Carbon Dioxide Reductions through Urban Forestry: Guidelines for Professional and Volunteer Tree Planters. USDA Forest Service.
Nowak, D. (2002). The effects of urban trees on air quality. USDA Forest Service, Syracuse, NY.
Rowntree, R., Nowak, D. (1991). Quantifying the role of urban forests in removing atmospheric carbon dioxide. Journal of Arboriculture, Vol. 17 (10), pp. 269-275.
 
Farr (2004) states that, "Evaluated as a simple landscape amenity, the monetary value ofCanada's urban forest is impressive. Vancouver's 114,500 street trees have an assessed value, using standards of the International Society of Arboriculture, of over $500 million. The 103,000 boulevard trees and 142,000 park trees of Edmonton have an estimated replacement value in excess of $800 million. The value of the Toronto urban forest, based on an average value of $700 per tree set by the Council of Tree and Landscape Appraisers in 1992, is over $16 billion." Natural Resources Canada from Evolving Urban Forest Concepts and Policies in Canada

There are many reasons to conduct tree appraisals. Appraisal methods have been developed and implemented proving that trees have substantial monetary value. The appraisal process can take a considerable amount of time on the site to effectively evaluate all measurables. Often, the process involves collecting samples, taking measurements and photographs, interviewing neighbours and evaluating the tree's environment. Determining the value of a tree considers species type, physical condition such as scarring, storm damage, disease or insect damage, etc. and location factors; these criteria can be found in established tree listings. Urban forests also provide economic benefits such as increased property values, positive impact on real estate consumer preference, and reduction in energy costs by shading buildings and pavement and lowering surrounding temperatures.

Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
Council of Tree and Landscape Appraisers. (2000). Guide for Plant Appraisal, Ninth Edition. 143 pp.

 

One of the things that distinguish urban forestry from other branches of forestry is a close relationship with people. Any urban forestry program has to integrate people as part of the program itself. The basic components of this are an education and awareness program, an advisory urban forest committee and communication in times of emergencies (see Emergency Preparedness section). Education and awareness involves the explanation of the operational aspects of an urban forestry program. Currently, this is best handled by developing and maintaining a section on a municipal website. Within that website are bulletins or publications on management practices.
An urban forest advisory committee has several purposes:
- To act as an advisory committee of council and provide feedback to municipal staff;
- To identify gaps in the program;
- To help staff identify ways to fill those gaps;
- To profile urban forestry to the community through the organization of field tours, open houses, etc.; and
- To educate municipal politicians of the value of urban forests to the community and the need to support it.
Typically, a staff member and a municipal councillor sit on the committee; the meetings are held on a regular basis and recommendations are brought to the attention of council. Throughout Canada, there are many resources, programs and organizations dedicated to public education that focus on sustaining nature and green space in urban communities and fostering a culture of stewardship. Education is one of the most important components of urban forest management to sustain best practices for tree care throughout communities. 
 
Websites
 
Online documents (.PDF or .DOC)
 
Non-Canadian sites & resources
 
Bibliographical Resources
International Society of Arboriculture (2001). Arborist's Certification Study Guide.
League, M. (1997). Leadership Grows in the Schoolyard. Science and Children, Vol. 34 (6), pp. 18-21.
Natural Resources Queensland Government. (1999). Forest Management Education Activity Series: Role of Trees in the Environment Level Years 3-5.
Reading, J., Taven, G. (1996). Outdoor Classrooms: The Learning Links. Green Teacher, Vol. 47, pp. 29-31.
 
Sites to other lists of links and web pages
 
Library and database sites
 
Urban Forestry (General)

 

Submissions

We encourage continuous recommendations for improving this site and suggestions for any additions to include in the Compendium. Please submit any new suggestions by contacting us.
 

 

PHOTO Credits

Adrina Bardekjian Ambrosii (1, 2, 4, 5, 6, 8, 9, 12, 16, 17, 19, 23, 25-27, 29, 33, 38-40, 42)
Julian Ambrosii (15, 37, 41)
Justin Morgenroth (18)
Michael Rosen (3, 7, 10, 11, 13, 14, 20-22, 24, 28, 30-32, 34-36)
 


[1] Jorgensen, E. 1974. Towards an urban forestry concept. Proceedings of the 10th Commonwealth 
Forestry Conference.  Ottawa, Canada; Forestry Service.
[2] According to Statistics Canada, an urban area (UA) has a minimum population concentration of 1,000 persons and a population density of at least 400 persons per square kilometre, based on the current census population count. All territory outside urban areas is classified as rural. Taken together, urban and rural areas cover all of Canada.
 
[3] Deneke, F. 1993.  Urban Forestry in North America:  Towards a Global Ecosystem Perspective.  pp 4-8.  IN Blouin, G. and Comeau, R. [eds.] Proceedings of the First Canadian Urban Forests Conference May 30- June 2, 1993.  Winnipeg MB. 151 pp.

 





Toronto, ON

Winnipeg, MB

Montréal, QC

 

 

Ottawa, ON

 

 

Charlottetown, PEI

Ottawa, ON/Gatineau, QC

 

 

 

 

 

Madrid, Spain

 

 

 

 

 

Madrid, Spain

Banff, AB

 

 

 

 

 

Emerald Ash Borer, Windsor, ON

Emerald Ash Borer

English Ivy, Vancouver, BC

 

Kelowna, BC

Kamloops, BC

 

 

 

 

 

 

 

 


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