Linking satellite images and hand-held infrared thermography to observed neighborhood climate conditions
Introduction
Research on urban heat islands (e.g., Bonan, 2000, Oke, 1973, Svensson, 2004) suggests even settlements with a small population can have a substantial heat island impact. The metropolitan area of Phoenix, Arizona, USA with a population of over 3 million, has a well studied urban heat island (UHI), characterized by higher urban vs. rural temperatures, and a historical trend of significantly increasing temperatures in the city over the past 50 years (e.g.: Baker et al., 2002, Brazel et al., 2000). Urbanization is rapidly expanding into the open desert and the resultant suburban residential land may be contributing a positive feedback to the spread of the urban heat island. The heterogeneity found within the urban fabric in metropolitan Phoenix creates a complexity of microclimates with significant local variability within the metropolitan area, which is difficult to assess adequately.
Remote sensing is a key to mesoscale modeling through specification of land cover distributions and creating spatial products of moisture, reflectance, and surface temperatures (Zehnder, 2002). Understanding the relationship between the “coarse” scale satellite remotely-sensed data, to “fine” scale hand-held thermography, and then to the observed ambient temperatures at the neighborhood microclimate scale, could allow further extrapolation to estimate the impact of urbanization across the metropolitan area for input into mesoscale models, and enhance prediction of UHI expansion through assessing the microclimate impact of growth and neighborhood design.
While there have been many studies that have highlighted temperature variation in urban areas through the use of high resolution remote sensing imagery (e.g., Eliasson, 1992, Quattrochi and Ridd, 1998), our study also adds the technique of ground thermography surveys and in situ surface climate observations to describe the residential environments. This method quantifies the thermal variation based on urban land use type, using the techniques of thermography, processing of remote sensing data, and utilization of Geographic Information Systems (GIS). These techniques can be easily applied to other arid cities and utilized by non-modeling researchers to describe the thermal environment of residential neighborhoods on the periphery of the city, and generate results that can be provided to urban planners and policy makers.
Connections between urbanization and climate in the region have been studied previously (e.g. Lougeay et al., 1994), but it is not known to what extent new residential developments beyond the urban fringe have an impact on local climatic conditions. Previous mobile transect sampling through urban, residential, and rural areas has shown on clear, calm days, the existence of very large thermal gradients across the urban fringe zone into rural areas, but the details of rural thermal patterns, associated with new developments, has not been fully investigated (Brazel et al., 1999, Hawkins et al., 2004, Hedquist, 2002, Stabler et al., 2005). In order to generate accurate models of Phoenix's mesoclimate, the impacts of large acreage tract residential developments on the urban fringe should be understood.
Section snippets
Regional
Greater Phoenix (Fig. 1: 33° 26′N /112°W, elevation ca. 350 m) encompasses approximately 38,000 sq. km in a two county region of Maricopa and Pinal counties in central Arizona, USA. It is an arid, subtropical region that has experienced explosive growth during the past half century. Regional population increased from 1,600,000 in 1980 to 2,238,000 in 1990; reached 3,379,000 as of July 2001, gaining 101,400 people annually since 1990 (HUD, 2002) — the highest percentage change of urbanized
Research methodology
A combination of methods was utilized: ASTER images, walking transects, and a fixed station observational sampling network with hand-held thermographic images for ground measurements. Ground measurements/thermography were part of a larger microclimate study (Hartz, 2004). Thermography was taken on June 10, 2004 with the nearest available times of day and night ASTER image data being June 7th for 10:40 pm LST, nighttime — and June 17, 2004 at 11:20 am LST, for daytime. Since the ideal
Surface and air temperature comparisons
Table 3 summarizes near-ground level (ca. 1.5 m) ambient air temperatures and remotely-sensed ASTER surface temperatures, albedo and SAVI for both the transects (a portion of the study areas) and for each neighborhood's full study area. Also included are the extrapolated mean surface temperature for each neighborhood derived from the thermographically-sensed measurements of built and natural features. At each of the air–dew point sensor placements, sky horizon angles were measured to determine
Conclusions
This study shows that ASTER images could be successfully used to estimate relative neighborhood temperatures at an urban microscale level especially for the evening hours — the prime hours of largest air temperature UHI formation. The overall rankings (hottest to coolest) by remotely-sensed surface temperatures were very similar to those measured by both the hand-held thermography and the neighborhood microclimate study. The nighttime images also accurately reflected the heterogeneity of the
Acknowledgements
Our thanks to the members of the transdisciplinary UHI research program of the Global Institute of Sustainability at Arizona State University, which focuses on urban topics in the context of Sustainability: Buildings, surface materials and pavements, urban forestry, and climate and modeling at the micro and mesoscales (http://www.urbanheat.org and http://www.ASUsmart.org). We are particularly grateful for the assistance of Kamil Kaloush, Assistant Professor in the Civil and Environmental
References (36)
The microclimates of a suburban Colorado (USA) landscape and implications for planning and design
Landscape and Urban Planning
(2000)A soil-adjusted vegetation index (SAVI)
Remote Sensing of Environment
(1988)- et al.
Plant gas exchange and water status in urban desert landscapes
Journal of Arid Environments
(2002) City size and the urban heat island
Atmospheric Environment
(1973)- et al.
Analysis of vegetation within a semi-arid urban environment using high spatial resolution airborne thermal infrared remote sensing data
Atmospheric Environment
(1998) - et al.
Microclimates in a desert city were related to land use and vegetation index
Urban Forestry & Urban Greening
(2005) - et al.
Monitoring urban land cover change: An expert system approach to land cover classification of semiarid to arid urban centers
Remote Sensing of Environment
(2001) - et al.
Thermal remote sensing of urban climates
Remote Sensing of Environment
(2003) - AZMET: Arizona Meterological Network (2005). Available at:...
- et al.
Urbanization and warming of Phoenix (Arizona, USA): Impacts, feedbacks, and mitigation
Urban Ecosystems
(2002)
High-resolution nighttime temperature patterns in Phoenix
Journal of the Arizona–Nevada Academy of Science
Canyon geometry, street temperatures and urban heat island in Malmo, Sweden
Journal of Climatology
Mean diurnal circulation and thermodynamic evolution of urban boundary layers
Microclimate and housing waves along the urban fringe
The tale of two climates — Baltimore and Phoenix urban LTER sites
Climate Research
Heat transfer. A practical approach
The climate of London
Infrared thermography and urban temperature patterns
International Journal of Remote Sensing
Cited by (81)
Infrared thermography in the built environment: A multi-scale review
2022, Renewable and Sustainable Energy ReviewsSurface urban heat island intensity in five major cities of Bangladesh: Patterns, drivers and trends
2021, Sustainable Cities and SocietyAssessment of constructing canopy urban heat island temperatures from thermal images: An integrated multi-scale approach
2020, Scientific AfricanCitation Excerpt :It also operates in a reasonable imaging cycle of daily (AVHRR and MODIS) and 16-days (Landsat and ASTER) revisit. Some studies have been conducted to compare canopy and surface UHIs and evaluate the applications of TIRRS data in urban climatology [4,5,16,21,23,37], estimating air temperature [15,29,34,42,52,55], or even, unlike common, predicting LST from NSAT when direct observations from satellites are unavailable [20] and when soil temperature monitoring in weather stations is inadequate [54]. Wemegah et al. [47] compared the weather station-based temperature trends versus the surface UHI intensities that are derived from Landsat imageries in Greater Accra.