1158 IEEE TRANSACTIONS ON GEOSCIENCE AND REMOTE SENSING, VOL. 49, NO. 3, MARCH 2011
ICESat GLAS Data for Urban
Environment Monitoring
Peng Gong, Zhan Li, Huabing Huang, Guoqing Sun, Senior Member, IEEE, and Lei Wang
Abstract—Although the Geoscience Laser Altimeter System
(GLAS) onboard the NASA Ice, Cloud and Land Elevation Satel-
lite was not designed for urban applications, its 3-D measurement
capability over the globe makes it a nice feature for consideration
in monitoring urban heights. However, this has not been previously
done. In this paper, we report some preliminary assessment of the
GLAS data for building height and density estimation in a suburb
of Beijing, China. Building heights can be directly calculated from
a GLAS data product (GLA14). Because GLA14 limits height
levels to six in each ground footprint, we developed a new method
to remove this restriction by processing the raw GLAS data. The
maximum heights measured in the field at selected GLAS foot-
prints were used to validate the GLAS measurement results. By
assuming a constant incident energy and surface reflectance within
a GLAS footprint, the building density can be estimated from
GLA14 or from our newly processed GLAS data. The building
density determined from high-resolution images in Google Earth
was used to validate the GLAS estimation results. The results
indicate that the newly developed method can produce more
accurate building height estimation within each GLAS footprint
(R
2
=0.937, rmse =6.4 m, and n = 26) than the GLA14 data
product (R
2
=0.808, rmse = 11.5 m, and n = 26). However,
satisfactory estimation results on building density cannot be ob-
tained from the GLAS data with the methods investigated in this
paper. Forest cover could be a challenge to building height and
density estimation from the GLAS data. It should be addressed in
future research.
Index Terms—Building density, building height, global change,
laser altimetry, urban growth.
I. I NTRODUCTION
I
T HAS been estimated that, by 2050, 69% of the world
population will be urbanized, from 29% in 1950 [1]. Urban
areas, although covering barely 3%–4% of the land surface on
Manuscript received March 2, 2010; revised July 3, 2010; accepted
August 5, 2010. Date of publication October 11, 2010; date of current version
February 25, 2011. This work was supported in part by the National Natural
Science Foundation of China under Grants 30590370 and 40901235 and in part
by the National High Technology Research and Development Program of China
under Grant 2008AA121702.
P. Gong is with the State Key Laboratory of Remote Sensing Science,
Beijing 100101, China, and also with the Center for Environmental Measure-
ment, Monitoring and Modeling, Department of Environmental Science, Policy
and Management, University of California, Berkeley, CA 94720-3114 USA
(e-mail: gong@irsa.ac.cn).
Z. Li is with the State Key Laboratory of Remote Sensing Science, Beijing
100101, China, and also with the College of Resources and Environment,
Graduate University of the Chinese Academy of Sciences, Beijing 100049,
China.
H. Huang and L. Wang are with the State Key Laboratory of Remote Sensing
Science, Beijing 100101, China.
G. Sun is with the Department of Geography, University of Maryland,
College Park, MD 20742 USA.
Color versions of one or more of the figures in this paper are available online
at http://ieeexplore.ieee.org.
Digital Object Identifier 10.1109/TGRS.2010.2070514
Earth, have a significant global impact. The ecological footprint
of city residents with respect to their tremendous demands
on materials and energy goes far beyond the physical space
of urbanized areas to include not only most agricultural and
forested areas but also all areas where mining has occurred.
Although urbanization brings mankind more efficient living
conditions, it also causes a number of well-known negative
effects including traffic congestion, pollution, and faster spread
of disease. Finding out how these negative effects can be
reduced or avoided in the future and ultimately building more
livable cities have been a top problem facing city governors and
planners. In order to solve this problem, a better knowledge
on where developments have happened and are happening,
how cities are shaping up in the future, and how to model
urban growth is badly needed. Remote sensing has been widely
used in urban morphological measurement and urban growth
monitoring and modeling [2]–[13]. Two recent trends in urban
remote sensing are the more accurate mapping of specific
urban surface cover types using digital aerial images and high
spatial resolution satellite data (e.g., [14] and [15]), and the use
of digital photogrammetry, interferometric synthetic aperture
radar (InSAR), and airborne lidar to measure urban structures
in 3-D [16]–[19]. Compared to the traditional 2-D information
extracted from remotely sensed data on the horizontal extent of
the land use types, the 3-D information about urban structures
is complementary, and when combined with urban land use, it
allows a more realistic estimation of the spatial and temporal
distributions of population in urban areas. This is important
to planners and managers who are responsible for land use,
transportation, telecommunications, and health care.
A new need for the 3-D information in urban areas comes
from the global change community where a concern about
global carbon budget requires an accurate estimation of com-
modity carbon consumptions. Urban structures consuming
most of the world production of steel, cement, and wood
materials occupy a big portion in the global carbon accounting.
More importantly, information about where those high carbon
consuming industrial products contained in urban constructions
are distributed may be globally demanding in future carbon
trade negotiations. Knowledge about the 3-D structure of ur-
banized areas in the world in a relatively consistent time frame
will thus be helpful to the estimation of where those high
carbon commodities will finally end up with. Such information
is currently nonexisting.
High-resolution remote sensing, InSAR, and airborne lidar
technologies are natural sources of data for 3-D information
extraction over urban areas. However, they are limited to rel-
atively developed countries, and it is difficult to coordinate data
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