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Information and Knowledge Management using ArcGIS ModelBuilder

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Teresa Santos, Ségio Freire <strong>and</strong> José António Tenedório<br />

Remote sensing imagery due to its spectral, temporal <strong>and</strong> geographic characteristics, can be used in<br />

monitoring processes, as a source for related information like l<strong>and</strong> use <strong>and</strong> l<strong>and</strong> cover, surface<br />

roughness, terrain relief or soil moisture. Sawaya et al. (2003) explored the potential of VHR IKONOS<br />

<strong>and</strong> QuickBird satellite imagery for mapping <strong>and</strong> analysis of urban impervious surface area <strong>and</strong> water<br />

resources at local scales. Bauer et al. (2004) mapped <strong>and</strong> quantified the degree of impervious surface<br />

area over a large geographic area <strong>and</strong> over time, <strong>using</strong> a multi-temporal L<strong>and</strong>sat imagery data set.<br />

Yuan <strong>and</strong> Bauer (2006) compared the normalized difference vegetation index (NDVI) <strong>and</strong> percent<br />

impervious surface as indicators of surface urban heat isl<strong>and</strong> effects in L<strong>and</strong>sat imagery. Aponte<br />

(2007) used a QuickBird image in order to detect different types of impervious surfaces, <strong>and</strong> studied<br />

the relationship between the rainfall-infiltration-runoff rates, the l<strong>and</strong> cover <strong>and</strong> the geomorphologic<br />

susceptibility. Zhang et al. (2009) extracted vegetation <strong>and</strong> impervious surface as indicators of urban<br />

l<strong>and</strong> surface temperature from IKONOS imagery.<br />

The present work details the development of an updated <strong>and</strong> detailed map of imperviousness for the<br />

city of Lisbon <strong>using</strong> IKONOS-2 satellite imagery. The Vegetation-Impervious-Soil (VIS) model,<br />

developed by Ridd (1995), was used as the basis for extracting l<strong>and</strong> cover information at the cityscale.<br />

It is a conceptual representation that allows simplifying the analysis of urban surfaces by<br />

decomposing it in three basic l<strong>and</strong> cover components: vegetation, impervious surface <strong>and</strong> soil.<br />

After collecting data on l<strong>and</strong> cover from remote sensing data, several indicators can be assessed.<br />

Indicators on l<strong>and</strong> sealing area, quantification of green area, or the vacant l<strong>and</strong> available in the city,<br />

are ecological measures that can be used for monitoring <strong>and</strong> analyzing trends over the territory.<br />

Studies on impacts of urbanization, responses to natural <strong>and</strong> man-made disasters, vulnerability<br />

analysis or ho<strong>using</strong> conditions, all require l<strong>and</strong>-based indicators. The geographical data constitute the<br />

base of the spatial representation of the indicators. Urban indicators are designed to measure the<br />

quality of life <strong>and</strong> the nature of development of an urban area. These indicators can be used to make<br />

policy <strong>and</strong> planning decisions, to identify whether policy goals <strong>and</strong> targets are being met, <strong>and</strong><br />

sometimes to predict change.<br />

2. Data set <strong>and</strong> study area<br />

The dataset explored in this paper includes spectral data, acquired by the IKONOS-2 satellite. The<br />

IKONOS image was acquired in June, 30, 2008, <strong>and</strong> has a spatial resolution of 4 m in the<br />

multispectral mode (visible <strong>and</strong> near-infrared b<strong>and</strong>s) <strong>and</strong> 1 m in the panchromatic mode, <strong>and</strong> a<br />

radiometric resolution of 11 bits.<br />

The study area is the city of Lisbon (Figure 1). The municipality occupies an area of 84 Km 2 , <strong>and</strong> is a<br />

typical European capital city, with a very diverse l<strong>and</strong> use dynamics, varying from historical<br />

neighborhoods where the street-network is dense <strong>and</strong> the most of the area is built-up, to modern<br />

residential ones, with on-going construction of roads <strong>and</strong> multi-family buildings. Between these two<br />

situations, there are more heterogeneous places with l<strong>and</strong> uses such as residential, parks,<br />

agriculture, vacant l<strong>and</strong>, industrial, utilities, <strong>and</strong> schools.<br />

3. Methodology<br />

The cartographic workflow based on remote sensing data, begins with the pre-processing stage<br />

where the images are orthorectified. Afterwards, the digital processing takes place to produce a map<br />

with the location of the l<strong>and</strong> cover features.<br />

The nomenclature is organized in two levels of detail, following the VIS model. The 1 st level includes<br />

the classes “Vegetation”, “Impervious Surfaces”, <strong>and</strong> “Soil”. On the 2 nd level, seven classes were<br />

defined: “Trees”, “Low Vegetation”, “Buildings”, “Roads”, “Other impervious surfaces”, “Soil”, <strong>and</strong><br />

“Shadows <strong>and</strong> Water” (Table 1).<br />

Green areas are an important l<strong>and</strong> use in urban areas which perform relevant environment functions,<br />

such as improving urban climate, reducing atmospheric pollution, providing amenities, aesthetical<br />

benefits <strong>and</strong> a good environment for urban population. Green l<strong>and</strong> cover includes trees, shrubl<strong>and</strong>,<br />

herbaceous <strong>and</strong> agriculture fields.<br />

Impervious surfaces can generally be defined as anthropogenic features, such as roads, buildings,<br />

sidewalks <strong>and</strong> parking lots, through which water cannot infiltrate into the soil. The artificial surface<br />

cover can be used to evaluate the quality of urban streams, <strong>and</strong> to study effects of runoff. Impervious<br />

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