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Urban Remote Sensing


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infrastructure (i.e. highway overpasses, bridges, levees, etc.) for built‐up volume calculation over extensive urban areas, and (ii) temporal resolution, or data collection frequency, enables change detection analyses through multi‐temporal comparisons (e.g. annual data across a decadal record). Correspondingly, Figure 2.1 shows previous, current, and future remotely sensed 3D data sources organized by spatial and temporal resolutions, and sized by swath (i.e. width of data collection pass by satellite or airborne platform).

Schematic illustration of current, former, and future 3D data sources for Earth observation.

      Airborne discrete‐return lidar data provide high spatial resolution data (see Figure 2.1) but is collected on a nonregular basis over small areas due to high cost. Lidar data acquisition is expensive and, regarding multi‐temporal data capture of particular locations for change analyses, is often not repeated for several years unless a specific funding source or project is in place. Multi‐temporal lidar analyses, therefore, commonly need to integrate lidar data from a variety of sources with varying point densities (Gamba et al. 2005). In the United States, government agency‐collected lidar data are often publicly available and free to download, but this is not always the case with other data collectors and holders. Some of these lidar data sources include the following:

       Federal governmentUnited States Geological Survey (USGS) through the 3D Elevation Program (3DEP) for topographic mapping National Oceanic and Atmospheric Administration (NOAA) for coastal mappingFederal Emergency Management Agency (FEMA) for flood risk mapping

       State governmentMichigan Statewide Authoritative Imagery & LiDAR (MiSAIL) programOregon Department of Geology and Mineral Industries Lidar Program

       Regional and local governmentCapital Area Council of Governments (CAPCOG), a 10 county collaboration in central TexasCity of New York (topographic and bathymetric lidar collections in 2017)

      Unfortunately, lidar data are not collected regularly in many countries worldwide or not accessible due to potential classified military operations; hence, the desire for spaceborne lidar and/or other data collection avenues for 3D data such as radar platforms. Spaceborne lidar platforms such as ICESat‐2 and GEDI offer open, free lidar data with increased repeatability though not to the level of spatial detail of the airborne options previously discussed and with extended repeat acquisition time (see Figure 2.1).

      Remote sensing analyses increasingly require higher/finer spatial and temporal resolutions along with large swaths that realistically can only all be provided by spaceborne radar platforms, which attests to the significance of integration of radar data including Synthetic Aperture Radar (SAR) into analyses. To date and for the foreseeable future, radar platforms/sensors provide ample spatial and temporal resolution data for urban built‐up analysis compared to lidar alternatives (e.g. airborne lidar, GEDI, ICESat‐2). QuikSCAT SeaWinds scatterometer data have proven effective at estimating 3D build‐up within urban environments though at relatively coarse spatial and temporal resolutions (Nghiem et al. 2017; Mathews et al. 2019). Unfortunately, QuikSCAT is no longer operating while fully calibrated backscatter data at Level‐1B have not yet become completely and freely available from international satellite scatterometers (e.g. Oceansat‐2 in 2009–2014, HY‐2A in 2011–present, and SCATSAT‐1 in 2016–present). Subsequently, SAR platforms, of which several are now operating (or have operated over the past several decades) and with many future missions are planned such as NISAR and LOTUSat 1 and 2, provide the most promising 3D data option for future urban remote sensing analyses. SAR data options (e.g. COSMO‐SkyMed [CSK], TanDEM‐X [TDX], Sentinel‐1) too, as shown in Figure 2.1, provide both high spatial and temporal resolution data for highly detailed multi‐temporal assessments.

      2.3.1 BACKGROUND

      Airborne discrete‐return lidar is the de facto data standard for urban built‐up height estimation and volume calculation in research and in practice because it rapidly captures highly detailed 3D data for relatively large areas with minimal vertical error (Dong and Chen 2018). In fact, lidar data commonly are more accurate in the vertical dimension than the horizontal (Cheuk and Yuan 2009). Significantly, discrete‐return lidar data collection records multiple returns for each laser pulse sent toward the Earth's surface and laser pulses can penetrate vegetative canopy gaps (unlike passive, optical data). Lidar, therefore, captures terrain data beneath canopy as well as structural information about the canopy itself (Shan and Toth 2018). However, for urban applications emphasizing built‐up infrastructure, this is not as important as acquiring rooftop heights and structures – although in residential areas tree canopies often overhang rooftops of homes where multiple returns are important for vertically separating the two.

      Specific to this chapter on built‐up volume, research focusing on buildings is of special interest. For example, Dong et al. (2010) and Zhao et al. (2017) use lidar data to calculate building volume for portions of several Texas cities (Dong et al.: Denton; Zhao et al.: Austin, Dallas, Houston, and San Antonio) to estimate population with the assumption that higher building volumes signify increased population. Both studies extracted buildings from lidarderived raster data to explore how built‐up volume relates to several US Census population datasets. Results of regression analyses indicate that built‐up volume can serve as a proxy for population with moderate to high success. Although from remotely sensed data alone, complexities of land use are difficult to resolve – i.e. large industrial buildings might indicate many people work at these locations but does not mean they reside there (Zhao et al. 2017). Other urban remote sensing studies implement rasterized lidar data to demarcate building footprints by way of height thresholding and masking (Rottensteiner and Briese 2002) or through image classification techniques (Priestnall et al. 2000). Evaluation of built‐up change requires differencing of multi‐temporal 3D datasets along with additional efforts to extract and characterize types of change (Vu et al. 2004; Stal et al. 2013; Teo and Shih 2013; Dong et al. 2018).

      2.3.2 DATA PROCESSING AND ANALYSIS

      Raw lidar data are stored as point clouds, simple vector points with XYZ locations (with intensity, return number, etc. attributes), typically in LAS format (ASPRS 2013; LAZ files are compressed versions of LAS files) although other formats exist (e.g. XYZ, PLY, OBJ, PCD). Though a relatively simple file type, lidar point clouds are large datasets