interactive online micro-spatial population analysis based...

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1 Interactive Online Micro-spatial Population Analysis Based on GIS Estimated Building Population Ko Ko Lwin and Yuji Murayama Author Contact Information Division of Spatial Information Science Graduate School of Life and Environmental Sciences University of Tsukuba Tennodai 1-1-1, Ibaraki Ken Japan 308-0821 ABSTRACT Population data used in GIS analyses are generally assumed to be homogeneous and planar (i.e., census tracts, townships, or prefectures) due to the public unavailability of building population data. Moreover, within the GIS domain, spatial analysis functions performed within the census tract do not acquire any significant changes in population. However, information on building population is required for micro-spatial analysis for improved disaster management and emergency preparedness, public facility management for urban planning, consumer and retail market analysis, environment and public health programs, and other demographic studies. In this paper, we discuss the building population estimation method and potential applications by utilizing modern remote sensing data acquisition systems such as LIDAR (Light Detection and Ranging) and building footprints to improve the accuracy in a micro-spatial analysis case study of Tsukuba City. In this study, we used a LIDAR derived Digital Volume Model (DVM) to estimate the population at building level and introduced the online interactive micro-spatial population analysis based on estimated building population. Keywords: Online active micro-spatial analysis, LIDAR, Digital Volume Model INTRODUCTION Little attention has been focused on population data analysis at micro-scale level due to the lack of available population data at the smallest geographical unit. Moreover, current population data used in GIS are represented as a point, polygon, or grid with aggregated values. Population data are always considered as a homogeneous plane. Openshaw (1992) identified the following sources of error in GIS: errors in the positioning of objects; errors in the attributes associated with objects; and errors in modeling spatial variation (e.g., by assuming spatial homogeneity between objects). Population data exhibit spatial variation, especially in areas with a mix of high- and low-rise buildings such as urban areas, residential areas patched with unpopulated spaces (paddy fields, parks, playgrounds, or government institutions) as in rural areas. Moreover, most census boundaries do not coincide with the boundaries of geographic features such as land use/land cover, soil type, geological units, and floodplain and watershed boundaries; this is known as “spatial incongruity”. On the other hand, spatial analysis functions performed within the census tract do not acquire any significant changes in population. This creates errors when trying to establish accurate rates for GIS analyses pertaining to health studies, crime patterns, hazard/risk assessment, land-use planning, or environmental impacts, among others, which rely on a smaller unit of analysis than the original zones. Examples of this are impact buffers that intersect the census enumeration unit, or a different set of zones altogether that do not coincide with the original set (e.g., overlaying data from units with non- coincident boundaries and/or overlapping spatial units such as census tracts and police precincts or health districts) (Maantay et al. 2007).

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Interactive Online Micro-spatial Population Analysis Based on GIS Estimated Building Population

Ko Ko Lwin and Yuji Murayama Author Contact Information Division of Spatial Information Science Graduate School of Life and Environmental Sciences University of Tsukuba Tennodai 1-1-1, Ibaraki Ken Japan 308-0821

ABSTRACT Population data used in GIS analyses are generally assumed to be homogeneous and planar (i.e., census tracts, townships, or prefectures) due to the public unavailability of building population data. Moreover, within the GIS domain, spatial analysis functions performed within the census tract do not acquire any significant changes in population. However, information on building population is required for micro-spatial analysis for improved disaster management and emergency preparedness, public facility management for urban planning, consumer and retail market analysis, environment and public health programs, and other demographic studies. In this paper, we discuss the building population estimation method and potential applications by utilizing modern remote sensing data acquisition systems such as LIDAR (Light Detection and Ranging) and building footprints to improve the accuracy in a micro-spatial analysis case study of Tsukuba City. In this study, we used a LIDAR derived Digital Volume Model (DVM) to estimate the population at building level and introduced the online interactive micro-spatial population analysis based on estimated building population. Keywords: Online active micro-spatial analysis, LIDAR, Digital Volume Model

INTRODUCTION Little attention has been focused on population data analysis at micro-scale level due to the lack of available population data at the smallest geographical unit. Moreover, current population data used in GIS are represented as a point, polygon, or grid with aggregated values. Population data are always considered as a homogeneous plane. Openshaw (1992) identified the following sources of error in GIS: errors in the positioning of objects; errors in the attributes associated with objects; and errors in modeling spatial variation (e.g., by assuming spatial homogeneity between objects). Population data exhibit spatial variation, especially in areas with a mix of high- and low-rise buildings such as urban areas, residential areas patched with unpopulated spaces (paddy fields, parks, playgrounds, or government institutions) as in rural areas. Moreover, most census boundaries do not coincide with the boundaries of geographic features such as land use/land cover, soil type, geological units, and floodplain and watershed boundaries; this is known as “spatial incongruity”. On the other hand, spatial analysis functions performed within the census tract do not acquire any significant changes in population. This creates errors when trying to establish accurate rates for GIS analyses pertaining to health studies, crime patterns, hazard/risk assessment, land-use planning, or environmental impacts, among others, which rely on a smaller unit of analysis than the original zones. Examples of this are impact buffers that intersect the census enumeration unit, or a different set of zones altogether that do not coincide with the original set (e.g., overlaying data from units with non-coincident boundaries and/or overlapping spatial units such as census tracts and police precincts or health districts) (Maantay et al. 2007).

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In order to improve the accuracy in population data analysis at micro-scale level, we need a quantitative estimate of building population and exact locations of their distributions. However, building population information is not available for use in the public domain due to privacy concerns. Nowadays, it is possible to generate population data at the building level due to the emergence of commercial remote sensing data available at finer spatial resolution with more diverse geo-information sources (IKONOS, QuickBird, LIDAR, etc.) and GIS data available at smaller map scales with better attribute information (building footprint data with number of floors, building name, block number, etc.).

On the other hand, the emergence of user friendly web GIS technologies such as Google

Map/Earth and Microsoft Virtual Earth empower the internet users to make interactive spatial decisions in a timely manner. Nowadays, web GIS is part of our daily lives. For example, finding a restaurant, browsing our neighborhoods, or choosing a place to live are important considerations for potential home buyers and can be achieved through the internet. Retail shop owners are ever seeking populated areas inside the city. Urban planners are always watching for population growth and their spatial distribution patterns in order to maintain and improve the urban system.

BACKGROUND STUDIES Several methods have been developed to generate smaller geographical units of population distribution based on aggregated values with ancillary datasets, commonly known as “Dasymetric Mapping”. From a cartographic point of view, common cartographic forms of population mapping are the choropleth map and the dasymetric map. Choropleth maps provide an easy way to visualize how a measurement varies across a geographic area. However, these maps have limited utility for detailed spatial analysis of population data, especially where the population is concentrated in a relatively small number of villages, towns, and cities. Moreover, choropleth maps cannot express statistical variation, such as changing population density, within the administrative areal units. One way to avoid this limitation is by transforming the administrative units into smaller and more relevant map units through a process known as dasymetric mapping (Bielecka 2005). Dasymetric maps use ancillary information to help delineate new zones that better reflect the changing patterns over space. Recent research suggests that dasymetric mapping can provide small-area population estimates that are more accurate than many areal interpolation techniques that do not use ancillary data (Mrozinski and Cromley 1999, Gregory 2002). Although dasymetric mapping has been in use since at least the early 1800s, it has never achieved the ubiquity of other types of thematic mapping, and thus the means of producing dasymetric maps have never been standardized and codified in the way other types of thematic mapping techniques have been (Eicher and Brewer 2001, Slocum 1999). Therefore, dasymetric methods remain highly subjective, with inconsistent criteria. The reason for this relative lack of popularity and the paucity of standard methodology surely lies at least partially in the difficulty inherent in constructing dasymetric maps, and until recently, the difficulties in obtaining the necessary data, as well as access to the computer power required to generate them (Maantay et al. 2007). The following are some developed methods and approaches in dasymetric mapping: areal interpolation (Langford et al. 1991, p. 56), filtered areal weighting (binary method) (Eicher and Brewer 2001), filtering with land use/land cover data (Sleeter 2004), and cadastral-based expert dasymetric system (CEDS) (Maantay et al. 2007).

The use of Light Detection and Ranging (LIDAR) data in urban applications is increasing

by means of realistic visualization of various landscapes for telecommunication and mobile network planning and identification of the relationship between urban morphology and surface temperature (Nichol 1996). Hug (1997) stated that laser scanners are the best choice for

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obtaining digital surface models, especially for dense urban areas. Haala and Brenner (1997) reported on similar work using airborne LIDAR data for the generation of 3D city models. Kim et al. (2000) provided a concise examination of the use of photogrammetric imagery and LIDAR data for obtaining a DTM in urban areas. However, incorporating LIDAR data with demographic data is very rare in GIS applications.

A GIS APPROACH TO ESTIMATION OF BUILDING POPULATION

Methodology We have introduced two estimation methods: (1) Areametric (which does not require information on the number of building floors); and (2) Volumetric (which does require information on the number of floors) (Lwin and Murayama 2009). For improved accuracy, we also allow filtering by other categories into the computation, such as filtering by minimum footprint area and building use types, e.g., commercial, industrial, educational, and other building use types that are not occupied by residents. The calculation is demonstrated by the following mathematical expressions: Areametric Method

𝐵𝑃𝑖 = 𝐶𝑃

𝐵𝐴𝑘nk=1

𝐵𝐴𝑖 Using building footprint surface area (1)

Volumetric Method

𝐵𝑃𝑖 = 𝐶𝑃

𝐵𝐴𝑘nk=1 .𝐵𝐹𝑘

𝐵𝐴𝑖 .𝐵𝐹𝑖 Using number of floors information (2)

Moreover, advances in remote sensing data acquisition technologies such as LIDAR can be used for extraction of building footprints, building height (Digital Height Model (DHM)) and building volume (Digital Volume Model (DVM)). Equations (3) and (4) shown below can be used for LIDAR data.

𝐵𝑃𝑖 = 𝐶𝑃

𝐵𝐴𝑘nk=1 .𝐵𝐻𝑘

𝐵𝐴𝑖 .𝐵𝐻𝑖 Using average building height (3)

𝐵𝑃𝑖 = 𝐶𝑃

𝐵𝑉𝑘nk=1

𝐵𝑉𝑖 Using total building volume (4)

where BPi Population of building i CP Census tract population BAi Footprint area of building i BFi Number of floors of building i BHi Average height of building i (from LIDAR data) BVi Total volume of building i (from LIDAR data) i, k Summation indices n Number of buildings that meet user-defined criteria and fall inside the CP polygon

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The Areametric method is suitable for low-rise buildings, especially in rural areas, and the Volumetric method is suitable for high-rise buildings, especially in downtown areas. Study Area The study area is Tsukuba City central area also known as Tsukuba Science City which is a planned city for research and scientific purposes. Tsukuba is sometimes considered as a part of the Greater Tokyo Area and about 50Km North-East of Tokyo. Tsukuba Science City represents one of the world's largest coordinated attempts to accelerate the rate of and improve the quality of scientific discovery. The city was closely modeled on other planned cities and science developments, including Brasilia, Novosibirsk's Akademgorodok, Bethesda, and Palo Alto. The city was founded by the merger of Ōho, Sakura, Toyosato, and Yatabe.

According to emergence of research and development facilities in Tsukuba City, the

population are ever increasing and the government requires to establish public facilities such as bus stations, hospitals, glossary stores, schools, shopping centers, etc. Another aspect of selecting Tsukuba City for case study is population integrity. Most of the people are living and working inside the Tsukuba City and home of the University of Tsukuba. Rich of spatial data availability of Tsukuba City (such as high resolution aerial imagery, LIDAR altitude data and other fine scale GIS data) is another favor of study area selection. Although, national census investigation (door-to-door) takes place five year intervals in Japan, most up-to-date resident registration information by wards can be get from city or local government office by monthly intervals in Tsukuba City. The study area is part of the Tsukuba City. In this study, total 94 census tracts and population 84955 were used. Total study area is 5959.13 Hectares (14725.34 Acres).

Figure 1. Study area and transportation network.

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Estimation of Building Population from LIDAR Derived DVM In this study, we used LIDAR data provided by the PASCO Corporation in ESRI point format for both a Digital Surface Model (DSM) and a Digital Terrain Model (DTM). Each DSM and DTM scene is 800 m wide and 600 m long. There were 164 DSM and 164 DTM scenes used for the whole study area. DSM points are on average 0.9 m apart and DTM points are at a regular 5 m spacing. PASCO also provided 18 cm ortho images, which were acquired along with the LIDAR surveying. Choosing the appropriate method for generating the DSM and DTM is important in LIDAR data processing since surface height information is collected as points. In this process, both DSM and DTM point features were converted into a triangulated irregular network (TIN) model (i.e., TIN-DSM and TIN-DTM). Under the ArcGIS program, the TIN process allows users to convert multiple scenes at one time. This reduces the time for mosaicking. Moreover, the TIN process is faster than other interpolation processes such as IDW, SPLINE, and Kirging. Each TIN-DSM and TIN-DTM was then converted into a raster format, setting the spatial resolution to 0.5 m. We subtracted the DTM from the DSM raster layers to achieve the Digital Height Model (DHM). This DHM raster layer was multiplied by the cell surface area (i.e., 0.25 m2) to convert to a digital volume model (DVM).

Figure 2. Process flow of DHM and DVM generation from LiDAR point data. Since we do not generate building footprints from LIDAR derived DHM, we need to perform spatial adjustment for some building footprints. The generation of building footprints from LIDAR data is presently under development and the results cannot be used in this study. To improve the visualization and to remove the noise from DHM data, we applied a 5×5 low-pass filtering process. We also filtered out pixels with heights less than 2 m and performed hill shading. This removed the cars, small bushes and other objects with heights less than 2 m. To perform spatial adjustment, we overlaid building footprints on the shaded DHM and adjusted

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the building footprint based on the shaded DHM. After spatial adjustment was performed, the building height and volume were extracted from the DHM and DVM, respectively, by applying Zonal Statistics as a Table in ArcGIS (ToolBox ► Spatial Analysis Tools ► Zonal ► Zonal Statistics as Table). This function allows users to summarize the values of a raster (i.e., DHM and DVM raster) within the zones of another dataset (i.e., building footprint polygons) and reports the results to a table. Later this table was joined with building footprint polygons based on the same polygon ID. We extracted average and standard deviation values from the DHM and total value from the DVM raster dataset. Finally we obtained the building footprint polygons with average building height, standard deviation of building height, and total building volume attribute fields.

Figure 3. Example of TIN-DSM, TIN-DTM and extraction of building average height and total volume for each building footprint. In order to separate residential and non-residential buildings, we downloaded iTownpage data from the NTT website, which includes business name, type, category, content, address, and other information in comma separated value (CSV) format. This CSV data were converted to ESRI point features using commercial geo-coding software with building level accuracy. We also computed the number of shops per point by applying the Dissolved Method in ArcGIS based on X, Y coordinate fields. Some points may include multiple shops such as shopping centers or malls, which share the same address. This is important for the identification of mixed building use type (i.e., a home-based business from shopping-center based business), where the number of shops per point is less than in a shopping mall. The separation of residential and non-residential building lies at the heart of the estimation process because the accuracy of the building population result is fully dependent on the building use types, such as residential, non-residential, and mixed. There are four steps to separate residential from non-residential buildings.

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Step 1: Filter by zero census tracts building Remove all building footprints that fall inside the zero census tracts, such as the university and research centre campus. Step 2: Filter by Building Area and Height Remove all building footprints with areas of less than 20 m2 and with a height of less than 2 m, thus removing bicycle stand roofs, garbage boxes, porticos, and other footprints not occupied by people. Step 3: Filter by Public Facilities In this step, we used the facility Point Layer, which was generated from NTT iTownpage, to identify the large scale public facilities such as financial institutions, governmental organizations, educational organizations, etc. This can be accomplished by intersecting the NTT Facility Point Data with the building footprints polygons. Although the geo-coding accuracy of NTT data conversion is building level, we applied a 3 m tolerance buffered to each facility point during the intersecting process. Step 4: Manual Filtering This step involved the removal of other unpopulated building footprints, which cannot be detected automatically, such as large building footprints for multi-storey car parking lots. Adjustment factor and mixed building use type. In order to improve the accuracy of the estimation process, we needed to consider mixed building use type (e.g., buildings using their first floor/ground floor for business activities such as a coffee shop, barber shop, restaurant, real estate agency, etc.). These can be detected from the number of shops per point, sub-business category, and business content attribute information from iTownpage data. Calculation of adjusted floor and volume is as follows. Adjusted Floor = Total number of floors – Number of business used floors Adjusted Volume = Total building volume * (Adjusted floors / Total number of floors) For example, the adjustment factor for a four-floor building with one commercial use floor is 0.75 (3/4) and zero for an empty building (abandoned house). Now we are ready to compute building population since we have census tracts with population and building footprints with building use types (residential, non-residential, and mixed), adjusted floor, and adjusted volume attribute information (Table 1). Table 1. Example of building footprint polygons with average height, height standard deviation, total volume, adjusted floors, and adjusted volume attribute fields.

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We implemented a standalone GIS tool (named PopShapeGIS) to calculate building population based on user defined criteria. More details about this tool and program can be downloaded from the following URL. http://giswin.geo.tsukuba.ac.jp/sis/en/software.html

Figure 4. Dasymetric Mapping based on GIS estimated building population (Left) and 3D visualization of building population data (Right)

IMPLEMENTATION OF ONLINE INTERACTIVE MICRO-SPATIAL POPULATION ANALYSIS (µSPA) Spatial analysis based on building population data is a key benefit for disaster management teams in order to prepare humanitarian assistance when disaster occurs. They need specific quantitative data on population with certain geographical units such as 500 m away from along the coast lines in the case of a tsunami strike, or 5 km distant from an earthquake’s epicenter. We have developed a web-based interactive micro-spatial population analysis function based on building population with other ancillary datasets such as public facility locations and the transportation network. This web site can be reached at the following URL: http://land.geo.tsukuba.ac.jp/microspa/welcome.aspx

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Figure 5. Graphical user interface of online interactive micro-spatial population analysis. Map Layers and Data Sources The list of map layers to be used in micro-spatial population analysis is shown in Table 1. Road centerline data were acquired from the Geographical Survey Institute (GSI) as line features and then real nodes and dangling nodes were extracted. Table 2. List of map layers and data sources.

Layer Order

Layer Name Description Feature

Visibility

Source

1 BUILDING Building footprints with estimated population

Polygon Visible Zmap-TOWNII

2 FACILITY Facility locations Point Visible NTT Townpage 3 ROAD Road outlines Line Visible Zmap-TOWNII 4 ROAD_NODE Road nodes Point Hidden GSI 5 ADMIN-BND Administration

boundary Polygon Visible Zmap-TOWNII

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Measurements Under the Online Micro-spatial Analysis system, measurements are based on three spatial elements, namely building population, public facility, and transportation network. These three spatial elements are core components in urban systems and interrelated with each other. For example, people need to find the ways to travel from one place to another inside the city. They may need to find the shortest path to buy food and use other utilities. On the other hand, business owners want to know their potential client volume and how they can reach their services. Urban planners or transportation planners need to know the spatial distribution patterns of population and facilities in order to improve the urban transportation system. Each measurement is based on the mean center of three spatial elements such as building Population Mean Center (PMC), Facility Mean Center (FMC), Connectivity Mean Center (CMC), Population Mean Center Index (PMC-I), Facility Mean Center Index (FMC-I), and Connectivity Mean Center Index (CMC-I).

𝑋𝑤 = 𝑤 𝑖𝑖 .𝑋𝑖

𝑤 𝑖𝑖 ,𝑌𝑤 =

𝑤 𝑖𝑖 .𝑌𝑖

𝑤 𝑖𝑖 (5)

Figure 6. Use of building population or number of shops as weighted factors. The Connectivity Mean Center was calculated based on X and Y coordinates of road nodes (both real and dangling nodes).

X = X ii

n , Y =

Yi

n (6)

In order to evaluate the availability and quality of basic services for spatial decision

makers, we also measured the Facility Mean Index (FMI) and Connectivity Mean Index (CMI). As generally defined, accessibility reflects the ease of reaching needed or desired activities and thus reflects characteristics of both the land-use system (where activities are located) and the transportation system (how the locations of activities are linked) (Handy and Clifton 2001). There are several approaches to measuring accessibility index or degree ranging from simple distance measurement to time and cost integrated measurements. Extensive academic literature on accessibility measures suggests many ways of defining and measuring accessibility, although examples of the actual use of accessibility measures in planning are relatively scarce (Handy and Clifton 2001). To quantify the abstract idea of connectivity, Dill (2003) defines and makes several measurements such as link-node ratio, which is measured by dividing the number of links (segments between nodes) in a study area by the number of nodes (intersections plus cul-de-sac termini); the connected node ratio, which is a ratio of the number of street intersections to intersections plus the number of cul-de-sacs, thus capturing the number of connected nodes relative to the total number of nodes; and intersection density, which is simply the number of street intersections per unit of area. Accessibility is an important concept for urban planners because it reflects the possibilities for activities, such as working or shopping, available to residents of a neighborhood, a city, or a metropolitan area. Nowadays, interactive web based

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accessibility assessment or walkability score calculation are useful for home buyers and business owners.

In order to measure accessibility index or degree, average distance was calculated

between a user’s defined point and facility or road node points. We construct the accessibility index by dividing average distance by circle radius. The circle radius is how far users are willing to travel, or the size of the service area in the case of market analysis. The index value is between 0 and 1. The interpretation of this value depends on the user’s application. For example, the lower Facility Index is favorable for local residents and nearest competitor for business owners. Local residents can define various locations and travel distances to evaluate their potential living place with the Facility Mean Index (FMI) and Connectivity Mean Index (CMI). Business owners can assess their potential business location with Population Mean Center (PMC) and Connectivity Mean Index (CMI). Urban planners can make future actions based on Population Mean Center (PMC) and Facility Mean Index (FMI). Transportation planners can evaluate each bus station or railway station and their served population by specific buffered distances.

Table 3. Summary of available map tools and measurement parameters

Map Tool Measurement Parameters Analysis Mode TBP PMC FMC CMC FMI CMI

Circle Find Domain Line

Polygon Find Location Rectangle

TBP = Total Building Population PMC = Population Mean Center FMC = Facility Mean Center CMC = Connectivity Mean Center FMI = Facility Mean Index CMI = Connectivity Mean Index

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Weighted building population mean center

Weighted facility mean center

Connectivity mean center (road nodes mean center)

User defined point or location (center of the circle) Figure 7. Use of circle tool to evaluate a business site.

With the line tool analysis, a user can define a buffer distance from the line and calculate total building population in the case of traffic noise impact studies or local community bus route planning or disaster management.

Figure 8. Find Domain analysis using Line Tool for local community bus route planning.

Figure 9. Find Location analysis using Polygon Tool for site selection.

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CONCLUSION Current population data represented in GIS are not suitable for use in micro-spatial population analysis. Spatial analysis functions performed inside the census tract do not acquire any significant changes in population. This paper introduced online interactive micro-spatial population analysis based on building population, which was estimated from LIDAR derived DVM and the number of floor information with census tracts for local residents, business owners, and other urban planners. Integrating LIDAR derived DVM with demographic data is a key benefit for urban and city planners, improving their decision making processes in a timely manner.

Acknowledgements We would like to thank PASCO Corporation for providing the LIDAR data and ortho images used in this study.

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