The Indicator
Cities have modified climates based on factors such as building density and
type and energy use, as well as local topography and regional weather patterns.
The urban heat island represents the difference between urban and
nearby rural air temperatures and is directly related to urban land cover and
human energy use. For most cities, this difference often is negligible in the
daytime but develops rapidly after sunset. Maximum difference occurs 23
hours after sunset and may be as great as 18°F. In general, as the population
density of a city increases, the difference in minimum temperature between the
urban core and rural site increases nonlinearly. Urban heat island effect for
a city is calculated by comparing the temperature of a monitoring station in
the urban core with a monitoring station from a neighboring rural location.
This difference might be reported as the average monthly difference between
urban and rural sites. Nationally, the indicator might report the number of
cities with various levels of difference between urban and rural sites: 06°F,
6 to less than 13°F, or more than 13°F.
As constructed surfaces replace natural vegetation, an areas ability
to absorb and store heat increases; the natural cooling effect mediated by trees
and other vegetation is reduced (water moves from the soil into a plant via
its roots, exiting ultimately by evaporation through pores in the leaves in
a process called evapotranspiration a cooling process much like when sweat
evaporates from our skin). The urban heat island represents a change in the
diurnal pattern of ambient temperature. Because many biological processes are
temperature dependent, changes in the temperature regime may have profound effects
on species and ecological processes. In fact, many of the proposed effects from
elevated global temperatures occur in urban areas because of the urban heat
island effect.
It is reported by the Centers for Disease Controls National Center for
Environmental Health that extreme heat events, some of which may be directly
attributable to the heat island effect, are responsible for greater loss of
human life in the United States than hurricanes, lightning, tornadoes, floods,
and earthquakes combined (http://www.cdc.gov/nceh/hsb/extremeheat/).
Other effects may include physiological stress in some species, altered species
composition and structure in ecological communities, modified nutrient and carbon
availability, and altered home range of pathogens. For example, physiological
stress results from altered phenology and modified moisture nutrient availability.
The urban heat island also modifies energy use for heating and cooling buildings
and vehicles.
The Data Gap
National Weather Service temperature data are available for a large number
of locations in the United States and could be used to determine urban heat
island effect and how this temperature differential has changed over time. Analyzing
historical data would require a significant amount of time, energy, and funding
to retrieve archival information, to conduct quality assurance and quality control
on data, and to perform the analysis. Data problems include obtaining long-term
data records for both urban and adjacent rural sites and accounting for changes
in monitoring locations or instrumentation and for changes in population densities
and human activities around monitoring sites. Another problem occurs for desert
cities where the maximum temperature difference between urban and rural monitoring
locations may occur during midday rather at sunset. Although a temperature differential
exists 23 hours after sunset, the evaporative cooling from vegetation
within the city may create cooler temperatures during the day than adjacent
desert temperature.
Remote-sensing data have been used to examine temperature differences between
urban and rural sites; however, these measurements record surface temperatures
rather than ambient temperatures.
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