Meteorological and air quality impacts of heat island mitigation measures in three U.S. cities

Author(s): Taha, Haider | Abstract: This report investigates the air pollution reduction benefits associated with mitigating urban heat islands in three U.S. cities. The effects of these measures in Salt Lake City, Baton Rouge, and Sacramento were evaluated through mesoscale meteorological and air quality modeling. The simulations indicate that for these three U.S. cities, adopting heat island reduction measures can result in various meteorological and air quality changes. The meteorological simulations suggest that each of the three pilot cities benefits from reduced ambient air temperatures. Decreases typically range from 1 to 2K (1.8 - 3.6?F) over modified areas. In Salt Lake City, reductions in ambient air temperatures reach up to 2K (3.6?F) at 1600 LST. The city achieves reductions in ozone concentrations of up to 3 or 4 ppb, the equivalent of about 3.5% if it were compared to an urban peak of 95 ppb. In Baton Rouge, reductions in ambient air temperatures of 0.75K (1.4?F) are possible and ozone ! reductions reach up to 4 or 5 ppb, the equivalent of about 4% if compared to an urban peak of 113 ppb. Finally, Sacramento enjoys reductions of 1.2K (2.2?F) as a result of heat island mitigation measures. Although these temperature reductions are not as large as those experienced in Salt Lake City, for example, their impacts on ozone are relatively larger, with reductions of up to 10 ppb from peak ozone concentrations (about 7% of the peak of 139 ppb). Sacramento enjoys larger reductions in ozone as a result of its larger geographical area. The modeling work shows that each of the three regions discussed in this report can benefit from implementing heat island mitigation measures. Clearly, the extent to which urban areas can effectively improve local air quality through heat island mitigation depends on numerous factors. These include meteorology and climate, geography, scale, topography, basin morphology, proximity to water bodies, land-use patterns, precursor emission rates and mix, baseline albedo and vegetative fraction distributions, and potential for modification (increase in albedo and vegetative fraction). Based on our modeling efforts, we found that the larger the modified area, the larger the impacts on meteorology and air quality.

[1]  H. Akbari,et al.  High-albedo materials for reducing building cooling energy use , 1992 .

[2]  T. Vihma,et al.  On the effective roughness length for heterogeneous terrain , 1991 .

[3]  R. Pielke Mesoscale Meteorological Modeling , 1984 .

[4]  F. C. Winkelmann,et al.  Overview of the DOE-2 Building Energy Analysis Program , 1985 .

[5]  Haider Taha,et al.  Modeling the impacts of large-scale albedo changes on ozone air quality in the South Coast Air Basin , 1997 .

[6]  Carlos A. Cardelino,et al.  Natural hydrocarbons, urbanization, and urban ozone , 1990 .

[7]  R. Monson,et al.  Isoprene and monoterpene emission rate variability: Model evaluations and sensitivity analyses , 1993 .

[8]  Hashem Akbari,et al.  Peak power and cooling energy savings of high-albedo roofs , 1997 .

[9]  E. Mcpherson,et al.  The effects of roof albedo modification on cooling loads of scale model residences in Tucson, Arizona , 1997 .

[10]  Timothy R. Oke,et al.  An objective urban heat storage model and its comparison with other schemes , 1991 .

[11]  Gary Whitten,et al.  Development and testing of the CBM-IV (Carbon-Bond Mechanism) for urban and regional modeling. Final report, July 1985-June 1987 , 1988 .

[12]  Sarah Bretz,et al.  Preliminary survey of the solar reflectance of cool roofing materials , 1997 .

[13]  Timothy R. Oke,et al.  Heat Storage in Urban Areas: Local-Scale Observations and Evaluation of a Simple Model , 1999 .

[14]  Haider Taha,et al.  Characterizing the Fabric of the Urban Environment: A Case Study of Sacramento, California , 1999 .

[15]  Hashem Akbari,et al.  Peak power and cooling energy savings of shade trees , 1997 .

[16]  H. Taha Modeling impacts of increased urban vegetation on ozone air quality in the South Coast Air Basin , 1996 .

[17]  D. Sailor Role of Surface Characteristics in Urban Meteorology and Air Quality , 1993 .

[18]  Danny S. Parker,et al.  Roof solar reflectance and cooling energy use: field research results from Florida , 1997 .

[19]  S. Konopacki,et al.  Impacts of Large-Scale Surface Modifications on Meteorological Conditions and Energy Use: A 10-Region Modeling Study , 1998 .

[20]  Haider Taha,et al.  Modifying a Mesoscale Meteorological Model to Better Incorporate Urban Heat Storage: A bulk-parameterization approach , 1999 .