European Forum for Geography and Statistics Vienna Conference Vienna, November 2015 Name (s) of author(s) IT Geostat Population Grid 2011

Similar documents
Swedish examples on , and

Copernicus Land HRL Imperviousness: 2012 dataset, indicator Title

Farm Management System. Map Import Standard (Paddocks)

Compact guides GISCO. Geographic information system of the Commission

Validation and verification of land cover data Selected challenges from European and national environmental land monitoring

Globally Estimating the Population Characteristics of Small Geographic Areas. Tom Fitzwater

APPLYING THE END FOR LOMBARDY S AIRPORTS

A n t h r o p o g e n i c P r e s s u r e o n C o a s t a l z o n e s

Display data in a map-like format so that geographic patterns and interrelationships are visible

Utilization of Global Map for Societal Benefit Areas

Welcome to NR502 GIS Applications in Natural Resources. You can take this course for 1 or 2 credits. There is also an option for 3 credits.

Measuring and Monitoring SDGs in Portugal: Ratio of land consumption rate to population growth rate Mountain Green Cover Index

NR402 GIS Applications in Natural Resources

Common geographies for dissemination of SDG Indicators

Summary Description Municipality of Anchorage. Anchorage Coastal Resource Atlas Project

The Combination of Geospatial Data with Statistical Data for SDG Indicators

NEW AIRPORT NOISE MANAGEMENT TECHNIQUES

2.1.2 Land cover data

Location Suitability Analysis

Investigation of the Effect of Transportation Network on Urban Growth by Using Satellite Images and Geographic Information Systems

Summer Heat Risk Index: how to integrate recent climatic changes and soil consumption component

Version 1.1 GIS Syllabus

GIS CONCEPTS ARCGIS METHODS AND. 3 rd Edition, July David M. Theobald, Ph.D. Warner College of Natural Resources Colorado State University

Spanish national plan for land observation: new collaborative production system in Europe

EO Information Services. Assessing Vulnerability in the metropolitan area of Rio de Janeiro (Floods & Landslides) Project

GED 554 IT & GIS. Lecture 6 Exercise 5. May 10, 2013

Land Cover and Land Use Diversity Indicators in LUCAS 2009 data

SWAMP GIS: A spatial decision support system for predicting and treating stormwater runoff. Michael G. Wing 1 * and Derek Godwin

The Milan agglomeration Strategic Noise Map

Improving rural statistics. Defining rural territories and key indicators of rural development

Landuse and Landcover change analysis in Selaiyur village, Tambaram taluk, Chennai

2015 Nigerian National Settlement Dataset (including Population Estimates)

Abstract: Contents. Literature review. 2 Methodology.. 2 Applications, results and discussion.. 2 Conclusions 12. Introduction

Estimation of the area of sealed soil using GIS technology and remote sensing

Comparing CORINE Land Cover with a more detailed database in Arezzo (Italy).

SITMUN: Cooperating to Build Local SDIs in the Barcelona Region

Application of high-resolution (10 m) DEM on Flood Disaster in 3D-GIS

CENSUS MAPPING WITH GIS IN NAMIBIA. BY Mrs. Ottilie Mwazi Central Bureau of Statistics Tel: October 2007

Geo Referencing & Map projections CGI-GIRS 0910

THE OVERALL EAGLE CONCEPT

GIS ADMINISTRATOR / WEB DEVELOPER EVANSVILLE-VANDERBURGH COUNTY AREA PLAN COMMISSION

Geography 281 Map Making with GIS Project Eight: Comparing Map Projections

Introduction. Project Summary In 2014 multiple local Otsego county agencies, Otsego County Soil and Water

How the science of cities can help European policy makers: new analysis and perspectives

- World-wide cities are growing at a rate of 2% annually (UN 1999). - (60,3%) will reside in urban areas in 2030.

Geo Referencing & Map projections CGI-GIRS 0910

Application of Topology to Complex Object Identification. Eliseo CLEMENTINI University of L Aquila

Using Geographic Information Systems and Remote Sensing Technology to Analyze Land Use Change in Harbin, China from 2005 to 2015

7.1 INTRODUCTION 7.2 OBJECTIVE

ENV208/ENV508 Applied GIS. Week 1: What is GIS?

New Land Cover & Land Use Data for the Chesapeake Bay Watershed

Adding value to Copernicus services with member states reference data

ABSTRACT The first chapter Chapter two Chapter three Chapter four

Quality and Coverage of Data Sources

FLOOD HAZARD AND RISK ASSESSMENT IN MID- EASTERN PART OF DHAKA, BANGLADESH

VENETO REGION PILOT AREA

Coastal regions: People living along the coastline and integration of NUTS 2010 and latest population grid

Esri s Living Atlas of the World Community Maps

Hydrology and Floodplain Analysis, Chapter 10

GIS for the Non-Expert

Web Portal to European Soil Database

Research on Topographic Map Updating

Country Report of Spain *

Calculating Land Values by Using Advanced Statistical Approaches in Pendik

Merging statistics and geospatial information

ArcGIS Pro: Essential Workflows STUDENT EDITION

Harrison 1. Identifying Wetlands by GIS Software Submitted July 30, ,470 words By Catherine Harrison University of Virginia

Introduction-Overview. Why use a GIS? What can a GIS do? Spatial (coordinate) data model Relational (tabular) data model

International Journal of Intellectual Advancements and Research in Engineering Computations

Spatial Concepts: Data Models 2

Application of GIS in Public Transportation Case-study: Almada, Portugal

Introduction to GIS I

USE OF SATELLITE IMAGES FOR AGRICULTURAL STATISTICS

Land Cover Classification Mapping & its uses for Planning

Urban settlements delimitation using a gridded spatial support

UK Contribution to the European CORINE Land Cover

GIS = Geographic Information Systems;

Abstract. TECHNOFAME- A Journal of Multidisciplinary Advance Research. Vol.2 No. 2, (2013) Received: Feb.2013; Accepted Oct.

INVESTIGATION LAND USE CHANGES IN MEGACITY ISTANBUL BETWEEN THE YEARS BY USING DIFFERENT TYPES OF SPATIAL DATA

Contents. Introduction Study area Data and Methodology Results Conclusions

Modeling the Rural Urban Interface in the South Carolina Piedmont: T. Stephen Eddins Lawrence Gering Jeff Hazelton Molly Espey

DEVELOPMENT OF DIGITAL CARTOGRAPHIC DATABASE FOR MANAGING THE ENVIRONMENT AND NATURAL RESOURCES IN THE REPUBLIC OF SERBIA

Chapter 6. Fundamentals of GIS-Based Data Analysis for Decision Support. Table 6.1. Spatial Data Transformations by Geospatial Data Types

DATA APPLIANCE FOR ARCGIS

Lessons Learned from the production of Gridded Population of the World Version 4 (GPW4) Columbia University, CIESIN, USA EFGS October 2014

Data Visualization and Evaluation

Acknowledgments xiii Preface xv. GIS Tutorial 1 Introducing GIS and health applications 1. What is GIS? 2

EnvSci 360 Computer and Analytical Cartography

Environmental Impact Assessment Land Use and Land Cover CISMHE 7.1 INTRODUCTION

Systems (GIS) - with a focus on.

GIS and Remote Sensing

GIS CONCEPTS ARCGIS METHODS AND. 2 nd Edition, July David M. Theobald, Ph.D. Natural Resource Ecology Laboratory Colorado State University

Problems and Challenges

HIRES 2017 Syllabus. Instructors:

The Road to Data in Baltimore

ANALYSIS OF URBAN PLANNING IN ISA TOWN USING GEOGRAPHIC INFORMATION SYSTEMS TECHNIQUES

Copernicus for Statistics

Copernicus Overview. Major Emergency Management Conference Athlone 2017

Earth Observation for Sustainable Development to Support Land Use Planning in Urban Areas

Delineation of high landslide risk areas as a result of land cover, slope, and geology in San Mateo County, California

Transcription:

European Forum for Geography and Statistics Vienna Conference Vienna, 10 12 November 2015 Name (s) of author(s) (1) Raffaella Chiocchini (1) Stefano Mugnoli (2) Luca Congedo (2) Michele Munafò Organization (1) ISTAT (Italian National Institute of Statistics) (2) ISPRA (Italian National Institute for Environmental Protection and Research) IT Geostat Population Grid 2011 (1) R. Chiocchini, (1) S. Mugnoli, (2) L. Congedo, (2) M. Munafò (1) National Institute of Statistics (ISTAT), Rome, Italy (2) Italian National Institute for Environmental Protection and Research (ISPRA), Rome, Italy {rachiocc, mugnoli} @istat.it ing.congedo.luca@gmail.com michele.munafo@isprambiente.it Abstract ISTAT presentation has the aim to describe the activities that have brought at the new Italian 1K Population Grid. The final result represents just the last step of a very worthwhile collaboration between ISTAT (Italian National Institute of Statistics) and ISPRA (Italian National Institute for Environmental Protection and Research). The template used was the Italian portion of new GEOSTAT Grid 2011. Many different geographic layers were used. The most important were: - ISTAT 2011 Census cartography and data; - Copernicus Degree of Imperviousness HR Layer at 20m of resolution; - ISTAT Statistics Synthetic Map, and Regional Land/Cover Map to mask the uninhabited areas on the Imperviousness HR Layer; In brief: the Copernicus Degree of Imperviousness is a raster layer that represents the percentage of soil sealing per pixel (i.e. cell), which was assumed to be related to population distribution; but the Degree of Imperviousness layer does not distinguish between residential and non-residential areas, therefore a detailed masking work has been first implemented in order to exclude non-residential pixels using ancillary data. Population data collected for each enumeration area during Census 2011 survey, has been proportionally distributed basing on the sum of Degree of Imperviousness, obtaining the number of resident population per pixel.

Then, the resident population for each GEOSTAT cell has been calculated as the sum of the single pixel values of the raster layer that are included in that cell. Many GIS software tools were used but the main algorithm, used to calculate the population for each 1Kmq cell was Zonal statistics as table of the ARCGIS 10.1 ESRI software. This algorithm calculates the entire pool of spatial statistics of a reference layer on the base of a value raster layer. The output is a table in which there is a single statistic value for each input polygon. Used SW: ARCGIS 10.1 ESRI for desktop (ArcInfo license), ERDAS IMAGINE 2013 INTERGRAPH. Keywords: ISTAT, ISPRA, Enumeration areas, Census project, ARCGIS 10.1, ERDAS IMAGINE, Imperviousness HR Layer, Copernicus, Population grid Introduction This paper has the purpose to describe briefly the principal activities carried out by ISTAT and ISPRA with the aim to realize the 1 km 2 population grid for the entire Italian territory. The final product represents very worthwhile collaboration between two Italian National Research Institutes that permitted a successful synthesis among many geographic datasets, in particular two of them: - Copernicus Degree of Imperviousness HR Layer at 20m of resolution; - ISTAT 2011 Census cartography and data; This new grid can be surely considered a big improvement compared to the one that can be produced by a simple disaggregation techniques. In fact starting from the bond between ISTAT geographic datasets and ISPRA Imperviousness Layer, we could estimate with a really good approximation which are the residential zones. Moreover, the resolution of the Copernicus satellite data ensures very precise estimations. Brief description of the main layers used The European Environmental Agency (EEA), in the frame of Copernicus initiative, has developed several High Resolution Layers (HRLs), referred to the year 2012. These HRLs have the main purpose of monitoring land cover of European countries with a high level of detail (20m resolution); in particular, the following environmental issues are represented in a land cover map: Degree of Imperviousness, Forest, Grassland, Wetland, and Water Bodies. In this work, the HRL Degree of Imperviousness was used as main layer for the definition of built-up areas. In fact, the Degree of Imperviousness describes the percentage of soil sealing inside the pixel area (i.e. 400m 2 ), which is related to the irreversible process of the degradation and removal of the soil surface (Munafò & Tombolini, 2014). The HRL Degree of Imperviousness is the result of a classification methodology, developed by EEA, based on the multispectral classification and object-oriented classification of remote sensing images and the calculation of vegetation indices (e.g. NDVI) and biophysical parameters for improving the

identification of vegetated and non-vegetated areas; also, ancillary data (i.e. land use/cover maps) were used if available, and interactive editing was performed on classification results if needed (EEA, 2012). It is worth mentioning that the HRL Degree of Imperviousness is a land cover raster of the built-up area (without distinction of the land use as shown in Fig.1) that includes the following elements as described by EEA (2012): Housing areas Traffic areas (airports, harbours, railway yards, parking lots) Industrial, commercial areas, factories Amusement parks (excluding the pure green areas associated with them) Construction sites with discernible evolving built-up structures Single (farm) houses (where possible to identify) Other sealed surfaces that are part of fuzzy categories, such as e.g. allotment gardens, cemeteries, sport areas (visible infrastructure), camp sites (roads and infrastructure, possibly influenced by caravans), excluding green areas associated with them. Roads and railways associated to other impervious surfaces Water edges with paved borders Fig. 1: Example of impervious surfaces (in red) from the Degree of Imperviousness 2012 ISTAT Census Enumeration Areas vector layer represents the base to analyze the Italian territory as regards statistical data. In fact, all the data collected during Census surveys are linked to each of the over

400.000 enumeration areas drawn upon Italy. This dense plot helps us to describe Italian Territory in a very detailed way overall in urban areas. It is also important to remember that Italy is planning continuous population Census, that should start in about two years; these activities will be absolutely fundamental to have a very detailed reference cartography and statistical data. So, the Census geographical datasets are essentially used for classifying and characterizing Italian Territory in relation to resident population, buildings, services and industry, and this fact can be considered precisely the starting point to realize a reliable population distribution grid. Furthermore it is very important to remember that several attributes are linked to each enumeration areas; this data were very useful overall during masking activities. In fig.2 an example of ISTAT enumeration areas (in red); in yellow the administrative boundaries. Fig.2 Example of ISTAT enumeration areas layer

Methodology in brief European grid layer re-projection ISTAT enumeration areas layer and ISPRA imperviousness layer are absolutely congruent regarding their geographic reference system. In fact these were both realized in WGS84 / UTM zone 32N (EPSG Projection 32632). So, even if European reference population grid is in ETRS89/ETRS LAEA (Lambert Azimuth Equal Area - EPSG Projection 3035), the re-projection of this has become very simple given that both of them are based on GRS80 Datum. So we decided to re-project European Grid in WGS84/UTM Zone 32N using conventional ARCGIS 10.1 algorithm. This because a projected coordinate system such UTM and LAEA requires a definition for the projection transform. This transform is used to translate between linear positions (e.g. meter) and angular longitude/latitude positions. In the sidebar all the transformation parameters are shown. At the end of the re-projection process, ISPRA layer results completely covered by 310.981 European grid cells. This number is entirely in keeping with the Italian territory extent that can be estimated in 302.070,8 Km 2. Zonal statistics calculation Box 2 Example inputs and output from zonal statistics Project PROJCS['WGS_1984_UTM_Zone_32N', GEOGCS['GCS_WGS_1984', DATUM['D_WGS_1984', SPHEROID['WGS_1984',6378137.0,298.257223563]], PRIMEM['Greenwich',0.0], UNIT['Degree',0.0174532925199433]], PROJECTION['Transverse_Mercator'], PARAMETER['False_Easting',500000.0], PARAMETER['False_Northing',0.0], PARAMETER['Central_Meridian',9.0], PARAMETER['Scale_Factor',0.9996], PARAMETER['Latitude_Of_Origin',0.0], UNIT['Meter',1.0]] ETRS_1989_To_WGS_1984 PROJCS['ETRS_1989_LAEA', GEOGCS['GCS_ETRS_1989', DATUM['D_ETRS_1989', SPHEROID['GRS_1980',6378137.0,298.257222101]], PRIMEM['Greenwich',0.0], UNIT['Degree',0.0174532925199433]], PROJECTION['Lambert_Azimuthal_Equal_Area'], PARAMETER['False_Easting',4321000.0], PARAMETER['False_Northing',3210000.0], PARAMETER['Central_Meridian',10.0], PARAMETER['Latitude_Of_Origin',52.0], UNIT['Meter',1.0]] After the acquisition of European grid projection, the next step involved the calculation of zonal statistics. So using Zonal statistics ARCGIS 10.1 tool, we were able to have the sum of the resident population for each European grid cell. In fact, with the Zonal Statistics tool, statistics are calculated for each zone defined by a zone dataset, based on values from another dataset (a value raster). A single output value

is computed for every zone in the input zone dataset. The Zonal Statistics as Table tool calculates all, a subset or a single statistic that is valid for the specific input but returns the result as a table instead of an output raster. A zone is all the cells in a raster that have the same value, whether or not these are contiguous. The input zone layer defines the shape, values, and locations of the zones. An integer field in the zone input is specified to define the zones. A string field can also be used. Both raster and feature datasets can be used as the zone dataset. The input value raster contains the input values used in calculating the output statistic for each zone. In the following illustration (Box 2), the zone layer is described as an input raster that defines the zones. The Value layer contains the input for which a statistic is to be calculated per zone. In this example, the maximum of the value input is to be identified for each zone. Before calculating resident population for the european grid, a zonal statistics as a table algorhytm has been used to evaluate ISPRA data at municipality scale. So using ISPRA layer as value layer, we calculated resident population for each Italian municipality. The result are shown in the excel file attached where the meaning of the fild are: - COD_REG: Code of the Region in which the Municipality is located; - COD_PRO: Code of the Province in which the Municipality is located; - PRO_COM: ISTAT code of the Municipality; - DEN: Municipality denomination; - PIXEL_COUNT: N. of the DEM pixels (20*20 m) that are included inside the perimeter of the Municipality; - ISPRA_AREA: Area of the Municipality calculated starting from ISPRA data (PIXEL_COUNT*400). Area is expressed in m 2 ; - ISTAT_AREA: Area of the Municipality extract from official ISTAT municipality shapefile. Area is expressed in m 2 ; - POP_ISPRA: Resident population of the Municipality calculated by ISPRA; - POP_ISTAT_2011: Resident population of the Municipality calculated by ISTAT during Census 2011 survey; - DIFF_AREA: Difference between ISTAT_AREA and ISPRA_AREA (ISTAT_AREA- ISPRA_AREA); - DIFF_POP: Difference between POP_ISTAT_2011 and POP_ISPRA (POP_ISTAT_2011- POP_ISPRA); - DIFF_AREA/ISTAT_AREA (%): Percentage value calculated as (DIFF_AREA/ISTAT_AREA)*100; - DIFF_POP/POP_ISTAT_2011 (%): Percentage value calculated as (DIFF_POP/POP_ISTAT_2011)*100; The Masking work As already mentioned in the abstract, the Degree of Imperviousness layer is very suitable to evaluate the percentage of soil sealing per pixel, however it does not discriminate the residential part of sealed soil.

Therefore, it was necessary to plan a strategy to isolate as many uninhabited areas as possible, in order to distribute population data just to imperviousness layer pixels that represents residential zones. Thematic digital cartographies (i.e. Land cover and use Maps, Road Networks, etc.) were used as a mask filtering definitely uninhabited zones: it means that all the imperviousness layer pixels that are included inside the polygons, even if they are sealed, were labeled as not-residential. Examples of these sealed but uninhabited areas are: Streets and Roads, Airport, Railway stations and network, etc. (see fig.3); in yellow the administrative boundaries. Fig.3 Airport enumeration areas before and after masking work. A summary of the process is reported in box 3 describing how the value of each pixel of the imperviusness layer is proportionally calculated depending on resident population of each enumeration area (in red in Box 3a). Then, in Box 3b, for each grid 1km 2 is calculated the sum of the resident population by zonal statistics algorithm and masking work. In the end, in Box 3c, the final result where the square grid is classified depending on the sum of their resident population (in light grey the most populated).

Box 3a) Merge between enumeration areas and Imperviousness HR Layer Box 3b) Merge Imperviousness HR Layer and the grid Box 3c) The final result. In light grey the most populated grid cells.

Use, Future developments and Conclusion This work can be consider the first step to produce important statistical information about population. For example, starting from a grid with a pixel wide 400 m 2, as the Imperviousness HR Layer really is, it is possible to estimate resident population not only inside conventional boundaries (i.e. administrative ones), but inside areas that cannot be obtained grouping enumeration areas too. About this, ISTAT and ISPRA, using Imperviousness HR Layer data, held an experimentation to calculate resident population inside nature conservation areas. Another very important consideration: starting from ISTAT and ISPRA datasets it is possible to draw population nets with small mesh sizes, best suited for urban areas. It is also very easy the grid upgrade, if new data will be available in the future; in fact, the process to distribute resident population inside Geostat grid is computerized into a Python language algorithm that is very easy to change. Moreover, data collected at this resolution can also be used to upgrade DEGURBA (Urbanization degree) algorithm. In order to improve the final product, it could be taken into account the third dimension. In particular: if it is known the exact height and volume of the building, resident population could be distributed in proportion not only on the base of the HRL Imperviousness classification, but also in relation to buildings characteristics. This objective can be achieved, for example, processing both census buildings data and radar images. This is a difficult process if we consider that Italian building census data are georeferenced just for major cities and not for the entire Italian territory. Furthermore nowadays census buildings data have only a geocoding address. Nevertheless, starting from the principal cities data it is possible to draw geo-statistical procedures that automatically associate the building height and then calculate volume for all residential pixels. Another important perspective is the estimation of other relevant environmental statistic data such as those related to biomass in forest or agriculture. These quantitative data are very different from population ones because they come from sample surveys. Some interesting results on these topics could be reached only by integrating a lot of different sources but it is not so easy with current available data. It is worth mentioning that the Copernicus HRL Degree of Imperviousness is planned to be updated every three years, with the next production referred to the year 2015. This frequent production process will be very useful for keeping the Degree of Imperviousness aligned with census data and therefore update the estimation of population distribution. Finally, on the next page IT Geostat Population Grid is shown (fig.4).

Fig.4 IT Geostat Population Grid

REFERENCES - ISTAT Geographic datasets downloaded from: http://www.istat.it/it/archivio/104317#accordions; - Ines Marinosci I servizi Copernicus/GMES per la valutazione del consumo del suolo Convention: Il Consumo di Suolo: lo stato, le cause e gli impatti Rome, feb 5 th 2013 http://www.isprambiente.gov.it/files/eventi/2013/convegno-consumo-del-suolo-2013/marinosci.pdf; - S. Mugnoli, R. Chiocchini, R. Molinaro IT Geostat Population Grid 2011: Passato, Presente, Futuro FORUM PA 2015 Rome, May 28 th 2015; http://www.forumpa.it/forum-pa-2015/geolocalizzazione; - EEA, 2012. Guidelines For Verification Of High-Resolution Layers Produced Under Gmes/Copernicus Initial Operations (Gio) Land Monitoring 2011 2013 version 4. - Freire S., Halkia M. GHSL application in Europe: Towards new population grids EFGS Krakow Convention Krakow, Poland Oct 22-24 th 2014; http://www.efgs.info/workshops/efgs-2014-krakow-poland/efgs-2014-conference-1/ghsl-application-ineurope-towards-new-population-grids; - Goerlich F., Canatrino I. Comparing bottom-up and top-down population density grids: The Spanish Census 2011 - EFGS Krakow Convention Krakow, Poland Oct 22-24 th 2014; http://www.efgs.info/workshops/efgs-2014-krakow-poland/8_efgs-2014_abstract-goerlich - Munafò, M. & Tombolini, I., 2014. Il consumo di suolo in Italia, ISPRA rapporti 195/2014.