The phrase "ecology of
the city" was introduced in 1997 as a simple rhetorical device to
highlight the novelty of the approach to urban ecology adopted in the initial
proposal for the Baltimore Ecosystem Study LTER (Pickett
et al. 1997). We and our
colleagues in the other urban LTER, located in Phoenix AZ, were anxious to
differentiate the proposed work from the usual approach to urban ecology that
had been used in the United States, and indeed most studies elsewhere, up to
that time (Grimm et al. 2000).
I have been surprised that the label and its
contrast with the ecology in the city
has become an organizational and framing tool in many of the contemporary
textbooks of urban ecology (Adler and Tanner 2013, Douglas
and James 2014). However, over
the intervening 20 years, the label has become more than a superficial framing
strategy. It has become invested with
explicit theoretical and empirical content, moving well beyond metaphor (Zhou
et al. 2017). However, it may not
be clear to most people that the label in fact now connotes a field of study and
a mode of application. The evolution of
how the idea is used also serves as an indicator of how the field of urban
ecology itself has developed over that 20 year span.
The predominant approach to urban ecological research in 1997
was called ecology in the city. It is defined as a research approach focusing
on biological organisms and ecological processes that are located in distinct
natural, seminatural, or biologically-dominated patches within the fabric of
cities, towns, suburbs, and exurbs.
These habitats can be considered to be analogs of those outside of
cities, whether those outside locations are rural or wild. Ecology of
the city is defined, in contrast to ecology in
the city, as a research approach that integrates biological, social, and
technological aspects (Grimm et al. 2016) of
urban structures and functions, and focuses on the feedbacks among the
components of urban ecosystems that represent these three aspects. The two approaches share a foundational
concern with the spatial structure, heterogeneity, and functioning of urban
systems ranging from single neighborhoods to urban megaregions (Figure 1).
Figure 1. Urban megaregions in Asia. The ecology of the city approach applies to all urban scales. |
The two approaches can also be differentiated by the way
they conceive of spatial heterogeneity, the models they use to represent
spatial fluxes, and their implications for management and sustainability. Such differences have been described in more
detail in an earlier post (http://besdirector.blogspot.com/2017/09/ecology-for-city-also-means-with.html). The contrast can also be exemplified by
describing how the nine components of theory (Pickett
et al. 2007) differentiate the two approaches (Table 1).
Here, I present a new diagram that may help clarify the
relationship of ecology of and ecology in cities (Figure 2). Ecology in,
as a focus on the biological structure and function of "green" patches
in cities, is a core and ongoing interest of urban ecology. This is because such patches are widely
recognized as important sources of ecosystem services in the urban landscape (Haase
et al. 2014). They can also be
the locus of evolutionary novelty associated with urban environments (Johnson
and Munshi-South 2017). Understanding
how these biologically-dominated patches are put together, what biological
resources they contain, what ecological and evolutionary functions they
support, what benefits and burdens to humans exist within them, or what
services emanate from them, are important outcomes of research focusing on
ecology in the city.
The contrasting approach of ecology of the city continues to work with biologically-dominated patches,
but extends its interest to all habitat types in the urban mosaic (Table 1). Thus, it asks "what ecological and
evolutionary structures and functions, environmental benefits and burdens,
exist in and move among all patches in an urban area?" This inclusive focus means that
ecological research under the umbrella of ecology of the city investigates patch types that may not contain obvious
biological components. Ecology of the city must therefore be
social-ecological research, rather than only biological research.
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Table 1. The components of theory (see Pickett et al. 2007) and an instance of each in
the contrasting approaches of ecology in
the city and ecology of the city. The examples of each component are not
complete or comprehensive. Several of
the examples focus on a "filter" of concern with spatial structure as
a driver of urban function. Note that
"urban" or "city" here refer to the entirety of urban
systems, whether investigated as a whole or not.
Component
|
In
|
Of
|
1.Domain
|
Biotically-dominated urban patches
|
Hybrid social-ecological-technological patches
|
2. Assumptions
|
Drawn from biology and bio-ecology
|
Additions from social-ecological science
|
3. Facts
|
Biodiversity, traits, genetics, population dynamics
|
Additions from social-demographic diversity, land cover and
institutional attributes, information, organizational dynamics
|
4. Generalizations
|
Succession; disturbance; stress; natural selection; stream continuum
|
Resilience cycle; socio-economic disturbance; cultural selection; engineered
stream continuum
|
5. Laws
|
Law of succession
|
Law of adaptive cycle
|
6. Models
|
Patch-corridor-matrix; Island biogeography
|
Landscape mosaic/hybrid patch dynamics; metacity model
|
7. Translation modes
|
Science-driven
|
Engagement-driven
|
8. Hypotheses
|
Patterns and mechanisms of biotic impairment
|
Adaptive capacities and limits
|
9. Framework
|
Nested hierarchy of key components to explain biological features and
processes in "green" patches in cities
|
Nested hierarchy of key components to explain hybrid features and
processes in all patches in urban mosaics
|
Application
|
Biological conservation
|
Sustainability planning and assessment
|
The third approach, ecology for the city, is defined as the co-production of urban research
questions, and the pursuit of social ecological research intended to inform
sustainable transformations in cities.
This approach is discussed more fully elsewhere (Childers
et al. 2015). But for this essay,
the important idea is that the three approaches to ecological research about
cities are not distinct from each other, but in fact interact. They can be depicted as concentric circles,
with ecology in being the core,
ecology of being inclusive of in, and the ecology for embracing the knowledge and approaches of the first two. Ecology in the city supports the social-ecological research exploring the
ecology of the city. Similarly, work pursuant to these two
approaches supports the more transdisiplinary, co-produced research of ecology for the city. Looking in the "opposite direction,"
each larger circle can be considered to require the input and knowledge
provided by the more focused and included domain (Figure 3).
Figure 3. The conception of ecology in, of, and for as an inclusive theoretical framework, showing their relationship to the disciplinary approach each takes. |
The three approaches
seen this way become nodes of interest and action in the larger field of urban
ecological science. None is
"the" urban ecology. Rather
they are complementary and individual researchers may shift their focus and
program among these approaches as time and circumstances permit or require.
The twenty years of research, education, and community
engagement motivated by the first expansion of our attention in Baltimore from
ecology in to ecology of the city, has continued to invite
conceptual clarification. It also
suggests that the empirical content of research of the entire field continues
to require understanding the biology within green patches, but also requires understanding
how biologically-driven processes contribute to the functioning of patches in
which biology may at first seem absent.
The ecology of the city points
to the relevance of ecological research and knowledge throughout the
city-suburban-exurban mosaic, and demands an interdisciplinary social-ecological
stance toward research. Finally, the
necessity and ethical requirement for effective engagement in urban ecological
systems has been codified by the ecology for
the city approach.
All Three
approaches as defined here make up urban ecology, and together are relevant to
the integration of ecological knowledge in urban decision making, ranging from
the scale of households to that of entire metropolitan authorities.
Steward Pickett
Literature Cited
Adler, F. R., and C. J. Tanner.
2013. Urban Ecosystems: Ecological Principles for the Built Environment.
Cambridge University Press.
Childers, D. L., M. L. Cadenasso,
J. M. Grove, V. Marshall, B. McGrath, and S. T. A. Pickett. 2015. An Ecology
for Cities: A Transformational Nexus of Design and Ecology to Advance Climate
Change Resilience and Urban Sustainability. Sustainability 7:3774–3791.
Douglas, I., and P. James. 2014.
Urban Ecology. Routledge, New York.
Grimm, N. B., E. M. Cook, R. L.
Hale, and D. M. Iwaniec. 2016. A broader framing of ecosystem services in
cities: Benefits and challenges of built, natural, or hybrid system function.
Pages 203–212 in K. C. Seto, W. D. Solecki, and C. A. Griffith, editors.
The Routledge Handbook of Urbanization and Global Environmental Change.
Routledge, New York.
Grimm, N., J. M. Grove, S. T. A.
Pickett, and C. Redman. 2000. Integrated Approaches to Long-Term Studies of
Urban Ecological Systems. BioScience 50:571–584.
Haase, D., N. Frantzeskaki, and
T. Elmqvist. 2014. Ecosystem Services in Urban Landscapes: Practical
Applications and Governance Implications. Ambio 43:407–412.
Johnson, M. T. J., and J.
Munshi-South. 2017. Evolution of life in urban environments. Science
358:eaam8327.
Pickett, S. T. A., W. R. B. Jr,
S. E. Dalton, and T. W. Foresman. 1997. Integrated urban ecosystem research.
Urban Ecosystems 1:183–184.
Pickett, S. T. A., J. Kolasa, and
C. G. Jones. 2007. Ecological Understanding. Academic Press, San Diego.
Zhou, W., S. T. A. Pickett, and
M. L. Cadenasso. 2017. Shifting concepts of urban spatial heterogeneity and
their implications for sustainability. Landscape Ecology 32:15–30.
2 comments:
An important implication of this concentric figure is that, if 1) the ecology in cities is concerned with biophysical processes and 2) the ecology in cities is necessary for understanding the ecology of cities, then biophysical processes are present and of concern throughout the social-ecological mosaic associated with the ecology of cities. Further, this suggests that a land ethic concerned with biophysical processes of conservation and restoration are important throughout the social-ecological mosaic.
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