In 1997, the U.S. Environmental Protection Agency (EPA) established the ''Heat Island Reduction Initiative'' to quantify the potential benefits of Heat-Island Reduction (HIR) strategies (i.e., shade trees, reflective roofs, reflective pavements and urban vegetation) to reduce cooling-energy use in buildings, lower the ambient air temperature and improve urban air quality in cities, and reduce CO2 emissions from power plants. Under this initiative, the Urban Heat Island Pilot Project (UHIPP) was created with the objective of investigating the potential of HIR strategies in residential and commercial buildings in three initial UHIPP cities: Baton Rouge, LA; Sacramento, CA; and Salt Lake City, UT. Later two other cities, Chicago, IL and Houston, TX were added to the UHIPP. In an earlier report we summarized our efforts to calculate the annual energy savings, peak power avoidance, and annual CO2 reduction obtainable from the introduction of HIR strategies in the initial three cities. This report summarizes the results of our study for Chicago and Houston. In this analysis, we focused on three building types that offer the highest potential savings: single-family residence, office and retail store. Each building type was characterized in detail by vintage and system type (i.e., old and new building constructions, and gas and electric heat). We used the prototypical building characteristics developed earlier for each building type and simulated the impact of HIR strategies on building cooling- and heating-energy use and peak power demand using the DOE-2.1E model. Our simulations included the impact of (1) strategically-placed shade trees near buildings [direct effect], (2) use of high-albedo roofing material on the building [direct effect], (3) urban reforestation with high-albedo pavements and building surfaces [indirect effect] and (4) combined strategies 1, 2, and 3 [direct and indirect effects]. We then estimated the total roof area of air-conditioned buildings in each city using readily obtainable data to calculate the metropolitan-wide impact of HIR strategies. The results show that in Chicago, potential annual energy savings of $30M could be realized by ratepayers from the combined direct and indirect effects of HIR strategies. Additionally, peak power avoidance is estimated at 400 MW and the reduction in annual carbon emissions at 58 ktC. In Houston, the potential annual energy savings are estimated at $82M, with an avoidance of 730 MW in peak power and a reduction in annual carbon emissions of 170 ktC.
[1]
H. Akbari,et al.
Long-term performance of high-albedo roof coatings
,
1997
.
[2]
Max H. Sherman,et al.
Variability in Residential Air Leakage
,
1986
.
[3]
S. Konopacki,et al.
Cooling energy savings potential of light-colored roofs for residential and commercial buildings in 11 US metropolitan areas
,
1997
.
[4]
L. Gu,et al.
Measured and simulated performance of reflective roofing systems in residential buildings
,
1998
.
[5]
F. C. Winkelmann,et al.
Overview of the DOE-2 Building Energy Analysis Program
,
1985
.
[6]
R. Moore,et al.
Assessing the impacts of white roofs on building energy loads
,
1998
.
[7]
Hugh Henderson,et al.
Residential equipment part load curves for use in DOE-2
,
1999
.
[8]
H. Akbari,et al.
Energy Savings Calculations for Heat Island Reduction Strategies in Baton Rouge, Sacramento and Salt Lake City
,
2000
.
[9]
H. Akbari,et al.
Integrated estimation of commercial sector end-use load shapes and energy use intensities in the PG&E service area
,
1993
.