The Indicator
This indicator reports the total number of acres that are classified
as urban and suburban and the amount of the various
undeveloped land cover types within these areas. More
detail is provided below, but urban and suburban is
defined here as land that is substantially covered by one of the
following land cover types: low-intensity residential, high-intensity
residential, commercialindustrialtransportation, or
urban and recreational grass. These categories are based on remote-sensing
classification of land cover and are defined at http://landcover.usgs.gov/classes.asp.
It was our intent that urban and suburban areas should include all major
metropolises and their outlying suburbs as well as smaller settlements
across the country that have a similar character even though they may
not be adjacent to a metropolis. Our goal was to define those areas across
the United States that should be classified as urban and suburban;
The Heinz Center examined several possibilities before choosing the approach
used here.
The use of the Census Bureaus metropolitan statistical areas (MSAs)
was the coarsest approach considered. MSAs include entire counties (or
cities and townships in New England) rather than only the large urban
centers and those outlying areas that are connected to them in some fashion.
In the West especially, vast counties are included in MSAs even though
only a fraction of the county area is actually urban or suburban. MSAs
account for about 20% of the land area of the lower 48 states; The Heinz
Center believes this is a significant overestimate of the area covered
by cities and suburbs.
Urbanized areas (UAs), also defined by the Census Bureau, offer a more
refined but still incomplete solution. Metropolises and their outlying
areas are included in UAs, but smaller settlements, which share many of
their characteristics with suburbs, are not included. A drawback to using
UAs is that they are determined in part by political/jurisdictional boundaries,
in addition to the degree of development. A potentially larger confounding
issue is that the rules for delineating UAs have changed significantly
since their first use in 1950. The Census Bureau is well aware of The
State of the Nations Ecosystems: Technical Notes 264 this shortcoming
and will be releasing newly constructed UA boundaries in early 2002. The
U.S. Department of Agriculture (USDA) Economic Research Service (ERS)
has estimated urban land area since 1950. ERSs estimate has incorporated
the area of UAs as well as the amount of area in Census-defined places
that have a population of at least 2,500 people. We have used ERSs
estimate to gauge the change in urban land area over time in the national
extent indicator; however, due to the limitations of UAs we chose
not to rely on these estimates exclusively to define urban/suburban areas.
A third and still more refined option considered would have relied totally
on Block Groups (BGs), which are small regions based on political boundaries
within which the Census Bureau counts the population. It would be possible
to choose a density threshold1000 people per square mile is generally
accepted as urbanized by the Census Bureauand define
those BGs that meet or exceed this density as urban and suburban. A shortcoming
of this approach is that BGs dominated by warehouses or railroad yards,
for example, which are certainly urban in character, would be excluded
because of their low population densities. As is discussed below, the
approach chosen for this indicator does, indeed, include most BGs with
densities at or above 1000 people per square mile.
A fourth option was to adopt the estimates for developed lands made by
the USDA Natural Resources Conservation Services National Resources
Inventory (NRI). The definitions used by the NRI agree, in principle,
with those for urban/suburban lands. However, NRI reports on any and all
developed areasincluding those down to about one-quarter acre. In
contrast, this project focuses on those areas with sufficient density
and size to qualify as suburban in character, as well as areas
that are undeniably urban. As noted below, this projects
definition requires an area to be at least 270 acres in size before it
is included within the urban/suburban definitions. In addition,
the NRI data are derived from a statistical sampling rather than a cataloging
of all developed lands. Thus, it would not have been possible to delineate
individual urban/suburban areas on a map (as is done along with the national
extent indicator), which would be necessary to implement several of the
other indicators included in this report.
The approach adopted here (see Data Manipulation below) uses
satellite data to classify land cover. The advantage of this method is
that it includes virtually all the BGs with at least 1000 people per square
mile, as well as other developed but lightly populated land, such as warehouse
districts. In addition, by overlaying BGs on the urban/suburban areas,
it was possible to estimate that about 75% of the 1990 population lived
in these areas (note that the data used to generate urban/suburban areas
came from 1992). As described in more detail below, a series of steps
have been used to define the outlines of urban and suburban areas based
on four different satellite land cover classifications.
A potential shortcoming of using a satellite-based approach rather than
a delineation based in Census data is that it will be more challenging
to correlate environmental quality trends like air and water quality with
human demographic and health data. However, a geographic information system
(GIS) can be generated to associate Census BGs, for example, with urban/suburban
areas. This would permit such correlations to be done for studies of demographics
and human health.
It may be useful in future editions of this report to consider presenting
the data on urban/suburban lands based on the number of people associated
with them. This would require shifting priorities for the indicator and
a GIS analysis as described above. Also, as data become available, it
would be good to add the proportion of native and non-native species to
the graph showing the composition of the undeveloped portion of urban
and suburban lands.
The Data
Data Source: Satellite data are derived from the National Land
Cover Dataset (NLCD), a product of the Multi-Resolution Land Characterization
(MRLC) Consortium, which is a partnership between the U.S. Geographical
Survey (USGS), the U.S. Forest Service, the National Oceanographic and
Atmospheric Administration (NOAA), and the Environmental Protection Agency
(EPA) (see http://www.epa.gov/mrlc/
or http://landcover.usgs.gov/nationallandcover.html).
Data Collection Methodology: Please refer to the national
extent indicator technical note for a discussion of the NLCD.
Data Manipulation: The NLCD divides the lower 48 states of the
United States into several billion square pixels that are about 100 feet
on a side. The data presented for this indicator are based on analysis
of larger pixels (1000 ft on a side), each of which contains 100 of the
smaller pixels. The first step was to classify any 1000-ft pixel as urban
and suburban if a majority of the 100-ft pixels within it fell into one
of the four developed land cover types available in the NLCD:
low-intensity residential, high-intensity residential, commercialindustrialtransportation,
or urban and recreational grasses. Very large aggregates of the 1000-ft
pixels, which were found for metropolises such as New York City, were
smoothed to some degree; that is, small clusters of undeveloped
land pixels that were wholly included within a metropolis were subsumed
in the urban and suburban areas. Other clusters of undeveloped-land pixels
within an urban and suburban area, although connected to the perimeter
by one or more pixels on a diagonal, were also included in the urban and
suburban area. For clusters of developed-land pixels to be counted as
urban/suburban in outlying areas, at least 13 of the 1000-ft pixels had
to touch at their sides or corners for a minimum size of 270 acres. The
final step for this indicator was to evaluate the proportion of different
land cover types within the 1000-foot pixels. This process yielded estimates
of the amount of both developed land and undeveloped land (in several
categories) by region.
Data Quality/Caveats: It is important to note that the methods
used to establish the NLCD relied on two different satellite images of
a given area, plus ancillary data. An image taken during the leaf-off
period in the late fall to early spring was often more important
to the classification process than the fully vegetated image. This was
especially true in urban settings with a good deal of tree-lined streets;
the foliage of deciduous trees should not have obscured the constructed
surfaces during the leaf-off period and, therefore, should not have led
to an underestimate of developed lands in these regions.
Given that the method used here to establish urban/suburban areas is
based on square pixels that are roughly 100 feet on a side, some detail
would have been missed in a typical urban setting. Specifically, the trees
on a tree-lined streets would most likely not be distinguished from the
street and sidewalk. However, a large expanse of trees, such as a heavily
wooded median strip or a small park, may well have been classified as
forest.
Data Access: All these analyses were conducted at the Land Cover
Applications Center at USGSs Earth Resources Observations Systems
Data Center. The raw data from which this indicator was developed are
available at no cost from the MRLC Consortium (http://edcwww.cr.usgs.gov/programs/lccp/mrlcreg.html),
but vast computing power was necessary for this analysis. Note: The data
available at the Web site listed here are the raw data from
which estimates of urban/suburban area, and the size of natural areas
within, were prepared. The actual data presented in this report were prepared
specially for The Heinz Center for this report.
|