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1 Spatial Modelling of the Terrestrial Environment - Georeferencial

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Index 275<br />

higher, usefulness <strong>of</strong> 189–90, 190<br />

passive microwave systems 43–4<br />

scales <strong>of</strong> variation and size <strong>of</strong> support 266–7<br />

spatial variability, <strong>of</strong> environmental parameters 267<br />

spatially explicit wind erosion and dust flux model<br />

143–6<br />

issues in integration <strong>of</strong> parameters for 144–6, 145<br />

processing stream for 145<br />

predicting wind erosion and dust flux at <strong>the</strong> Jornada<br />

Basin 146–53<br />

data sources and model inputs 145, 146–8, 146,<br />

147, 147, 148<br />

relations between model parameters and<br />

vegetation/soil parameters 144, 144<br />

Special Sensor Microwave Imager (SSM/I) 43, 44,<br />

253<br />

SPOT-HVR XS images 203<br />

SSM/I snow depth estimates, spatial representivity <strong>of</strong>,<br />

an example 47–9<br />

standard deviation (SD), relationship with error 122,<br />

123–4, 124<br />

Stefan’s Law 187<br />

stereo-photogrammetry, limitations over ice sheets 15<br />

Structural Analysis and Mapping System (SAMS)<br />

210, 215<br />

and built-form constellations 209<br />

surface mass balance model 19–2020<br />

surface quality<br />

description 118–19<br />

quantification 116–18<br />

surface temperature remote sensing 253<br />

suspended sediment concentration, used to map flow<br />

patterns 82<br />

sustainable planning policy 229<br />

sustainable urban development 200<br />

SWE see snow water equivalent (SWE)<br />

SWEMO see spatially explicit wind erosion and dust<br />

flux model<br />

Syn<strong>the</strong>tic Aperture Radar (SAR)<br />

airborne 84, 97–8<br />

dynamic flooding processes 83<br />

River Severn floods (1998 and 2000) 84–5<br />

polarimetric or multi-frequency and accurate flood<br />

mapping 84<br />

new sensors for measurement <strong>of</strong> inundation extent<br />

83–4<br />

statistical active contour methods (snakes) 83–4<br />

Tanganyika, Lake 5, 157–8<br />

deficiency in sediment delivery model, Malagarasi<br />

River sediment 167–8<br />

estimation <strong>of</strong> lake sediment concentrations 164–5<br />

use <strong>of</strong> AVHRR and ATSR-2 imagery 164–5<br />

key regions prone to erosion, deforested and<br />

degraded 166, 167<br />

Lake Tanganyika Biodiversity Project (LTBP)<br />

Special Sediment Study 158<br />

mapping <strong>of</strong> sediment plumes 158<br />

remote sensing <strong>of</strong> sediment plumes 164, 168,<br />

169–71<br />

Ruzizi River plumes 168<br />

sediment monitoring system 158<br />

estimation <strong>of</strong> lake sediment concentrations 164–5<br />

sediment transport and routing 163–4, 167–8, 172<br />

soil erosion modelling 159–63<br />

sediment yield estimations 172<br />

sensitive to sedimentation problems 157, 158<br />

severe erosion in <strong>the</strong> nor<strong>the</strong>rn catchment, Rwanda,<br />

Burundi and eastern Zaire 166, 167, 167<br />

soil erosion model <strong>of</strong> <strong>the</strong> catchment 158<br />

terrestrial environment 1<br />

connected to spatial modelling 1–2<br />

topographic data, high resolution 92–4<br />

integration with standard hydraulic models 92<br />

topography<br />

controlling sediment route through a catchment 164<br />

in hydraulic models 86<br />

ice sheet 4, 14–15, 31, 265<br />

from InSAR and SRA 21–3, 24<br />

see also ice sheet topography; surface quality<br />

Total Ozone Mapping Spectrometer (TOMS) 137–8,<br />

139<br />

trace gases and aerosols, emissions from fires 177, 182<br />

tractability, in computer modelling 3<br />

traffic congestion, Cambridgeshire 238<br />

traffic emissions, modelling impact <strong>of</strong> on <strong>the</strong> urban<br />

environment 228–43<br />

integrated land use and transport modelling<br />

framework 231–3<br />

emissions model 233–5<br />

integrating models within <strong>the</strong> framework <strong>of</strong> SHIRE<br />

2000 GIS 229–30, 231<br />

modelling emmissions impact in Cambridgeshire<br />

235–41<br />

emissions impact <strong>of</strong> <strong>the</strong> policy scenarios 239–41<br />

Tropical Rainfall Measuring Mission (TRMM)<br />

Microwave Imager (TMI) 253<br />

UK<br />

local authorities responsible for an ‘Air Quality<br />

Strategy’ 228–9<br />

National Atmospheric Emissions Inventory (NAIE)<br />

229<br />

uncertainty estimation<br />

using spatial data and distributed risk mapping<br />

98–101<br />

probability mapping 100, 101<br />

uniform flow <strong>the</strong>ory 86<br />

universal soil loss equation (USLE) 109<br />

urban growth 200

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