Urban forestry

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Tree pruning in Durham, North Carolina
James Kinder, an ISA Certified Municipal Arborist examining a Japanese Hemlock at Hoyt Arboretum

Urban forestry is the care and management of single trees and tree populations in urban settings for the purpose of improving the urban environment. Urban forestry advocates the role of trees as a critical part of the urban infrastructure. Urban foresters plant and maintain trees, support appropriate tree and forest preservation, conduct research and promote the many benefits trees provide. Urban forestry is practiced by municipal and commercial arborists, municipal and utility foresters, environmental policymakers, city planners, consultants, educators, researchers and community activists.

Benefits[edit]

Professional Tree Climber (arborist: Zack Weiler) climbing a willow tree in Port Elgin, ON. Canada

Urban forests provide environmental, health, and economic benefits to cities. Urban forests mitigate the effects of urban heat island through evapotranspiration and the shading of streets and buildings. This improves human comfort, reduces the risk of heat stroke and decreases costs to cool buildings.[1] Urban forests improve air quality by absorbing pollutants such as ozone, nitrogen dioxide, ammonia, and particulate matter as well as performing carbon sequestration.[2] Urban forests are important to stormwater management. Trees absorb and store rainwater through the canopy, and slow down and filter runoff with their roots.[3] Urban forests also encourage more active lifestyles by providing space for exercise and are associated with reduced stress and overall emotional well-being. Urban forests may also provide products such as timber or food, and deliver economic benefits such as increased property values and the attraction of tourism, businesses and investment.[4]

The City of Denver Department of Parks and Recreation website[5] hosts interactive online tools that allow residents to view the financial impact to their neighborhoods directly related to healthy tree planting. In the Washington-Virginia Vale neighborhood the city website cites 2,002 individual trees as having been planted and maintained by the City Forester. These trees are believed to bring in an annual ecosystem benefit of $159,521. This is mostly wrapped up in property benefits, which cite a contribution to this total of $143,331. The majorities of these trees are between 0 and 12 feet tall and are a mix of mostly Elm, Maple, Pine, and Locust species.[6]

Mental health impacts[edit]

A 2018 study asked low income residents of Philadelphia "how often they felt nervous, hopeless, restless, depressed and worthless."[7] As an experimental mental health intervention, trash was removed from vacant lots. Some of the vacant lots were "greened", with plantings of trees, grass, and small fences. Residents near the "greened" lots who had incomes below the poverty line reported a decrease in feelings of depression of 68%, while residents with incomes above the poverty line reported a decrease of 41%. Removing trash from vacant lots without installing landscaping did not have an observable mental health impact.[7]

Practice[edit]

Urban forestry is a practical discipline, which includes tree planting, care, and protection, and the overall management of trees as a collective resource. The urban environment can present many arboricultural challenges such as limited root and canopy space, poor soil quality, deficiency or excess of water and light, heat, pollution, mechanical and chemical damage to trees, and mitigation of tree-related hazards. Among those hazards are mostly non-immediate risks like the probability that individual trees will not withstand strong winds (as during a thunderstorm) and damage parking cars or injure passing pedestrians. Although quite striking in an urban environment, large trees in particular present a continuing dilemma for the field of urban forestry due to the stresses that urban trees undergo from automobile exhaust, constraining hardscape and building foundations, and physical damage (Pickett et al. 2008). Urban forestry also challenges the arborists that tend the trees. The lack of space requires greater use of rigging skills and traffic and pedestrian control. The many constraints that the typical urban environment places on trees limits the average lifespan of a city tree to only 32 years – 13 years if planted in a downtown area – which is far short of the 150-year average life span of trees in rural settings (Herwitz 2001).

Management challenges for urban forestry include maintaining a tree and planting site inventory, quantifying and maximizing the benefits of trees, minimizing costs, obtaining and maintaining public support and funding, and establishing laws and policies for trees on public and on private land. Urban forestry presents many social issues that require addressing to allow urban forestry to be seen by the many as an advantage rather than a curse on their environment. Social issues include under funding which leads to inadequate maintenance of urban trees. In the UK the National Urban Forestry Unit produced a series of case studies around best practice in urban forestry which is archived here.

By country[edit]

United States[edit]

History[edit]

Tree warden laws in the New England states are important examples of some of the earliest and most far-sighted state urban forestry and forest conservation legislation. In 1896, the Massachusetts legislature passed the first tree warden law, and the other five New England states soon followed suit: Connecticut, Rhode Island, and New Hampshire in 1901, Vermont in 1904, and Maine in 1919. (Kinney 1972, Favretti 1982, Campanella 2003).

As villages and towns grew in population and wealth, ornamentation of public, or common, spaces with shade trees also increased. However, the ornamentation of public areas did not evolve into a social movement until the late 18th century, when private individuals seriously promoted and sponsored public beautification with shade and ornamental trees (Favretti 1982, Lawrence 1995). Almost a century later, around 1850, institutions and organization were founded to promote ornamentation through private means (Egleston 1878, Favretti 1982). In the 1890s, New England's "Nail" laws enabled towns to take definitive steps to distinguish which shade trees were public. Chapter 196 of the 1890 Massachusetts Acts and Resolves stated that a public shade tree was to be designated by driving a nail or spike, with the letter M plainly impressed on its head, into the relevant trunk. Connecticut passed a similar law in 1893, except its certified nails and spikes bore the letter C. (Northrup 1887).

The rapid urbanization of American cities in the late 19th century was a concern to many as encouraging intellectual separation of humanity and nature (Rees 1997). By the end of the 19th century, social reformers were just beginning to understand the relationship between developing parks in urban areas and "[engendering] a better society" (Young 1995:536). At this time, parks and trees were not necessarily seen as a way to allow urban dwellers to experience nature, but more of a means of providing mechanisms of acculturation and control for newly arrived immigrants and their children (e.g., areas to encourage "structured play" and thus serve as a deterrent for youth crime) (Pincetl and Gearin 2005). Other prominent public intellectuals were interested in exploring the synergy between ecological and social systems, including American landscape architect Fredrick Law Olmsted, designer of 17 major U.S. urban parks and a visionary in seeing the value of including green space and trees as a fundamental part of metropolitan infrastructure (Young 2009). To Olmsted, unity between nature and urban dwellers was not only physical, but also spiritual: "Gradually and silently the charm comes over us; the beauty has entered our souls; we know not exactly when or how, but going away we remember it with a tender, subdued, filial-like joy" (Beveridge and Schuyler 1983 cited in Young 2009:320). The conscious inclusion of trees in urban designs for American cities such as Chicago, San Francisco, and Minneapolis was also inspired by Paris's urban forest and its broad, tree-lined boulevards as well as by the English romantic landscape movement (Zube 1973). The belief in green cover by early park proponents as a promoter of social cohesion has been corroborated by more recent research that links trees to the presence of stronger ties among neighbors, more adult supervision of children in outdoor areas, more use of the neighborhood common areas, and fewer property and violent crime (Kuo et al. 1998, Kuo and Sullivan 2001, Kuo 2003).

Many municipalities throughout the United States employ community-level tree ordinances to empower planning officials to regulate the planting, maintenance, and preservation of trees. The development of tree ordinances emerged largely as a response to the Dutch Elm Disease that plagued cities from the 1930s to 1960s, and grew in response to urban development, loss of urban tree canopy, and rising public concern for the environment (Wolf 2003). The 1980s saw the beginning of the second generation of ordinances with higher standards and specific foci, as communities sought to create more environmentally pleasing harmony between new development and existing infrastructure. These new ordinances, legislated by local governments, may include specific provisions such as the diameter of tree and percentage of trees to be protected during construction activities (Xiao 1995). The implementation of these tree ordinances is greatly aided by a significant effort by community tree advocates to conduct public outreach and education aimed at increasing environmental concern for urban trees, such as through National Arbor Day celebrations and the USDA Urban and Community Forestry Program (Dwyer et al. 2000, Hunter and Rinner 2004, Norton and Hannon 1997, Wall et al. 2006). Much of the work on the ground is performed by non-profits funded by private donations and government grants.

Policy on urban forestry is less contentious and partisan than many other forestry issues, such as resource extraction in national forests. However, the uneven distribution of healthy urban forests across the landscape has become a growing concern in the past 20 years. This is because the urban forest has become an increasingly important component of bioregional ecological health with the expanding ecological footprint of urban areas. Based on American Forests' Urban Ecosystem Analyses conducted over the past six years in ten cities, an estimated 634,407,719 trees have been lost from metropolitan areas across the U.S. as the result of urban and suburban development (American Forests 2011). This is often due to the failure of municipalities to integrate trees and other elements of the green infrastructure into their day-to-day planning and decision-making processes (American Forests 2002). The inconsistent quality of urban forestry programs on the local level ultimately impacts the regional context in which contiguous urban forests reside, and is greatly exacerbated by suburban sprawl as well as other social and ecological effects (Webb et al. 2008). The recognition of this hierarchical linkage among healthy urban forests and the effectiveness of broader ecosystem protection goals (e.g., maintaining biodiversity and wildlife corridors), highlights the need for scientists and policymakers to gain a better understanding of the socio-spatial dynamics that are associated with tree canopy health at different scales (Wu 2008).

United Kingdom[edit]

In the UK urban forestry was pioneered around the turn of the 19th century by the Midland reafforesting association, whose focus was in the Black Country. England's Community Forests.[8] programme was established in 1990 by the then Countryside Commission as a pilot project to demonstrate the potential contribution of environmental improvement to economic and social regeneration. Each Community Forest was established as a partnership between local authorities and local, regional and national partners including the Forestry Commission and Natural England. Collectively, this work has formed the largest environmental regeneration initiative in England. In the mid 1990s the National Urban Forestry Unit (NUFU) grew out of a Black Country Urban Forestry Unit and promoted urban forestry across the UK, notably including the establishment of the Black Country Urban Forest.[9] As urban forestry become more mainstream in the 21st century, NUFU was wound up, and its advocacy role now carried on by organisations such as The Wildlife Trusts and the Woodland Trust.

Constraints[edit]

Resolving limitations will require coordinated efforts among cities, regions, and countries (Meza, 1992; Nilsson, 2000; Valencia, 2000).

  • Loss of green space is continuous as cities expand; available growing space is limited in city centres. This problem is compounded by pressure to convert green space, parks, etc. into building sites (Glickman, 1999).
  • Inadequate space is allowed for the root system.
  • Poor soil is used when planting specimens.
  • Incorrect and neglected staking leads to bark damage.
  • Larger, more mature trees are often used to provide scale and a sense of establishment to a scheme. These trees grow more slowly and do not thrive in alien soils whilst smaller specimens can adapt more readily to existing conditions.
  • Lack of information on the tolerances of urban tree cultivars to environmental constraints.
  • Poor tree selection which leads to problems in the future
  • Poor nursery stock and failure of post-care
  • Limited genetic diversity
  • Too few communities have working tree inventories and very few have urban forest management plans.
  • Lack of public awareness about the benefits of healthy urban forests.
  • Poor tree care practices by citizens and untrained arborists.

Organizations[edit]

See also[edit]

References[edit]

Notes[edit]

  1. ^ Pearlmutter, David (2017-02-27). The Urban Forest: Cultivating Green Infrastructure for People and the Environment. Springer. ISBN 9783319502809. Retrieved 25 April 2018.
  2. ^ Konijnendijk, Cecil C. (2005-05-20). Urban Forests and Trees: A Reference Book. Springer. ISBN 9783540251262. Retrieved 25 April 2018.
  3. ^ "Stormwater to Street Trees" (PDF). United States Environmental Protection Agency. United States Environmental Protection Agency. Archived (PDF) from the original on 2015-05-15. Retrieved September 4, 2015.
  4. ^ Salbitano, Fabio. "Guidelines on urban and peri-urban forestry" (PDF). Food and Agriculture Organization of the United Nations. Archived (PDF) from the original on 2018-01-07. Retrieved 25 April 2018.
  5. ^ "Power BI Report". Retrieved 2018-06-01.
  6. ^ "Forestry (Trees)". City of Denver Parks and Recreation (Forestry). Archived from the original on 2018-04-22. Retrieved May 31, 2018.
  7. ^ a b Hui, Mary (August 17, 2018). "Study: When a city's trashy lots are cleaned up, residents' mental health improves". Washington Post. Archived from the original on 2018-08-17. Retrieved 2018-08-18.
  8. ^ "England's Community Forests". communityforest.org.uk. Archived from the original on 2017-11-11. Retrieved 2017-11-23.
  9. ^ "Archived copy". Archived from the original on 2004-07-25. Retrieved 2004-07-02.CS1 maint: Archived copy as title (link)

Further reading[edit]

  • American Forests. 2002. "Urban Ecosystem Analysis, Knox County, Tennessee." American Forests. Available online as a pdf (archived page).
  • American Forests. 2011. Urban Ecosystem Analysis. Available online (archived page)
  • Anderson, L. M., & Cordell, H. K. 1988. Influence of Trees on Residential Property-Values in Athens, Georgia (USA) - a Survey Based on Actual Sales Prices. Landscape and Urban Planning, 15(1-2), 153-164.
  • Barro, S. C., Gobster, P. H., Schroeder, H. W. & Bartram, S. M. 1997. "What Makes a Big Tree Special? Insights from the Chicagoland Treemendous Trees Program." Journal of Arboriculture, 23(6), 239-49.
  • Campanella, T.J. 2003. Republic of shade: New England and the American elm. Yale University Press, New Haven, CT.
  • Coder, K. 1996. Cultural aspects of trees: traditions and myth. Athens, GA: Cooperative Extension Service, Forest Resources Unit, University of Georgia.
  • Dwyer, J. F., McPherson, E. G., Schroeder, H. W., & Rowntree, R. A. 1992. Assessing the Benefits and Costs of the Urban Forest. Journal of Arboriculture, 18(5), 227-234.
  • Dwyer, J. F., Nowak, D. J., Noble, M. H. & Sisinni, S. M. 2000. "Connecting People with Ecosystems in the 21st Century: an assessment of our nation's urban forests." General technical report PNW ; GTR-490 Portland: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station.
  • Dwyer, J. F., Schroeder, H. W. & Gobster, P. H. 1991. "The Significance of Urban Trees and Forests: Toward a Deeper Understanding of Values." Journal of Arboriculture, 17(10), 276-84.
  • Egleston, N.H. 1878. Villages and village life with hints for their improvement. Harper and A Brothers, Publishers, New York.
  • Favretti, R.J. 1982. The ornamentation of New England towns: 1750–1850. J. Garden Hist. 2(4):325–342
  • Fernow, B.E. 1910. The care of trees in lawn, street and park. Henry Holt and Company, New York.
  • Glickman, D. 1999. "Building Cities of Green". 1999 National Urban Forest of Conference. American Forests, Washington, DC. pp. 4–7.
  • Hansen-Moller, J. & Oustrup, L. 2004. "Emotional, physical/functional and symbolic aspects of an urban forest in Denmark to nearby residents." Scandinavian Journal of Forest Research, 19, 56-64.
  • Hanson, Michael L. (1990). Urban & Community Forestry, a Guide for the Interior Western United States, USDA Forest Service, Intermountain Region, Ogden, Utah.
  • Hastie, C. 2003. The Benefits of Urban Trees. Warwick District Council, UK.
  • Herwitz, E. 2001. Trees at Risk: Reclaiming an Urban Forest. Worchester, MA: Chandler House Press.
  • Hunter, L. M. & Rinner, L. 2004. "The Association Between Environmental Perspective and Knowledge and Concern With Species Diversity." Society and Natural Resources: An International Journal, 17:6, 517 - 32.
  • Jones, O. & Cloke, P. 2002. Tree Cultures: The Place of Trees and Trees in Their Place. Oxford and New York: Berg.
  • Kaplan, R. & Kaplan, S. 1989. The Experience of Nature: A Psychological Perspective. Cambridge: Cambridge University Press.
  • Kaplan, R. 1992. Urban Forestry and the Workplace (No. NC-163). Chicago, IL: USDA Forest Service, North Central Forest Experiment Station.
  • Kellert, S. R. & Wilson, E. O. 1993. The Biophilia Hypothesis. Washington, D.C.: Island Press/ Shearwater Books.
  • Kinney, J. P. 1972. The development of forest law in America including legislation in America prior to March 4, 1789. Arno Press, New York.
  • Konijnendijk, C. C, Nilsson, K, Randrup, T. B, Schipperijn J (Eds.) 2005. Urban Forests and Trees- A Reference Book. ISBN 978-3-540-25126-2 (Print) 978-3-540-27684-5 (Online) Springer
  • Kuo, F. E., & Sullivan, W. C. 2001. "Environment and crime in the inner city: Does vegetation reduce crime?" Environment and Behavior, 33(3), 343-65.
  • Kuo, F. E. 2003. "The Role of Arboriculture in a Healthy Social Ecology." Journal of Arboriculture, 29(3).
  • Kuo, F. E., Bacaicoa, M. & Sullivan, W. C. 1998. "Transforming inner-city landscapes – Trees, sense of safety, and preference." Environment and Behavior, 30(1), 28-59.
  • Lohr, V. I., Caroline H. Pearson-Mims, John Tarnai, and Don A. Dillman. 2004. How Urban Residents Rate and Rank the Benefits and Problems Associated with Trees in Cities. Journal of Arboriculture, 30(1), 28-35.
  • Mansfield, C, Pattanayak, S. K., McDow, W., McDonald, R., & Halpin, P. 2005. Shades of Green: Measuring the value of urban forests in the housing market. Journal of Forest Economics, 11(3), 177-199.
  • McPherson, E. G. & Simpson, J. R. (2000). Reducing Air Pollution Through Urban Forestry. Proceedings of the 48th meeting of California Pest Council (available online, pdf file).
  • McPherson, E. G. 1994. Using Urban Forests for Energy Efficiency and Carbon Storage. Journal of Forestry, 92(10), 36-41.
  • McPherson, E. G., & Rowntree, R. A. 1993. Energy Conservation Potential of Urban Tree Planting. Journal of Arboriculture, 19(6), 321-331.
  • McPherson, E. G., Simpson, J. R. & Scott, K. (2002). Actualizing Microclimate and Air Quality Benefits with Parking Lot Shade Ordinances. Wetter und Leben 4: 98 (available online, pdf file).
  • McPherson, E. G. 1998. Structure and sustainability of Sacramento's urban forest. Journal of Arboriculture 24(4):174–90.
  • Meza, H.M.B. 1992. "Current Situation of the Urban Forest in Mexico City". J. Arbor., 18: 33-36
  • Morales, D. J., Micha, F. R., & Weber, R. L. 1983. Two Methods of Valuating Trees on Residential Sites. Journal of Arboriculture, 9(1), 21-24.
  • Mudrack, L. 1980. "Urban Vegetation: A Reference for New York Communities". New York Department of Environmental Conservation.
  • Nillsson, K., Randrup, T.B., and Wandell, B.I.M. 2000. "Trees in the Environment". Oxford University Press, New York, NY.
  • Northrup, B. G. 1887. Arbor Day: Its history and aims, and how to secure them. Rep. Sec. Connecticut Board of Agric. 13 p.
  • Norton, B. G., & Hannon, B. 1997. "Environmental values: A place-based theory." Environmental Ethics, 19(3), 227-45.
  • Nowak, D., & Wheeler, J. Program Assistant, ICLEI. February 2006.
  • Nowak, D. (1993). Plant Chemical Emissions. Miniature Roseworld 10 (1) (available online, pdf file).
  • Nowak, D. (1995). Trees Pollute? A "Tree Explains It All". Proceedings of the 7th National Urban Forest Conference (available online, pdf file).
  • Nowak, D. (2000). Tree Species Selection, Design, and Management to Improve Air Quality Construction Technology. Annual meeting proceedings of the American Society of Landscape Architects (available online, pdf file).
  • Nowak, D. The Effects of Urban Trees on Air Quality USDA Forest Service (available online, pdf file).
  • Orland, B., Vining, J., & Ebreo, A. 1992. The Effect of Street Trees on Perceived Values of Residential Property. Environment and Behavior, 24(3), 298-325.
  • Pickett, S. T. A., Cadenasso, M. L., Grove, J. M., Nilon, C. H., Pouyat, R. V., Zipperer, W. C. & Costanza, R. 2008. "Urban Ecological Systems: Linking Terrestrial Ecological, Physical, and Socioeconomic Components of Metropolitan Areas." Urban Ecology, 99-122.
  • Pincetl, S. & Gearin, E. 2005. "The reinvention of public green space." Urban Geography, 26(5), 365-84.
  • Rees, W. E. 1997. "Urban ecosystems: the human dimension." Urban Ecosystems, 1:1, 63-75.
  • Simpson, J. R., & McPherson, E. G. 1996. Potential of Tree Shade for Reducing Residential Energy Use in California. Journal of Arboriculture, 22(1), 10-18.
  • Solotaroff, W. 1911. Shade-trees in towns and cities. John Wiley & Sons, New York.
  • USDA Forest Service. 2003. Benefits of Urban Trees: Urban and Community Forestry: Improving Our Quality of Life. In Southern Region (Ed.), Urban Forestry Manual. Athens, GA: USDA Forest Service.
  • USDA Forest Service. 2004. Urban Forestry Manual – Benefits and Costs of the Urban Forest. Athens, GA: USDA Forest Service.
  • Valencia, R.L. 2000. Management of Green Area in Mexico City. Presentation to the 20th Session of the North American Forestry Commission, June 6–10, St. Andrews, Canada.
  • Wall, B. W. T. J. S., and Stephen E. Miller 2006. "An Econometric Study of the Factors Influencing Participation in Urban and Community Forestry Programs in the United States." Arboriculture & Urban Forestry, 32(5), 221-28.
  • Webb, T. J., Bengston, D. N. & Fan, D. P. 2008. "Forest value orientations in Australia: An application of computer content analysis." Environmental Management, 41:1, 52-63.
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  • Wolf, K. L. 2004. Economics and Public Value of Urban Forests. Urban Agriculture Magazine, 13 (Special Issue on Urban and Periurban Forestry), 31-33.
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  • Wu, Jianguo. 2008. "Toward a Landscape Ecology of Cities: Beyond Buildings, Trees, and Urban Forests." in Ecology, Planning, and Management of Urban Forests: International Perspectives, edited by M. M. Carreiro. New York: Springer.
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