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<strong>EnviroInfo</strong> 2002 (Wien)<br />

Environmental Communication in the In<strong>for</strong>mation Society - Proceedings <strong>of</strong> the 16th Conference<br />

Copyright © IGU/ISEP, Wien 2002. ISBN: 3-9500036-7-3<br />

<strong>Floating</strong> <strong>Car</strong> <strong>Data</strong> <strong>as</strong> <strong>Data</strong> <strong>Source</strong> <strong>for</strong> <strong>Modelling</strong> <strong>of</strong><br />

<strong>Air</strong> and Noise Pollution in Regions with High Traffic<br />

Density<br />

Bernhard Nowotny 1 , Peter Maurer 2 , Katja Schechtner 1 , Wilfried<br />

Winiwarter 3 , Jürgen Zajicek 1<br />

Abstract<br />

As air and noise pollution models depend on real-time traffic data, the integration <strong>of</strong> traffic<br />

in<strong>for</strong>mation (air and noise emissions) h<strong>as</strong> been recognised <strong>as</strong> an important step in urban<br />

are<strong>as</strong>. As the equipment <strong>of</strong> fixed me<strong>as</strong>urement stations <strong>for</strong> traffic, air pollution and<br />

noise detection is limited by financial constraints in<strong>for</strong>mation from cars equipped with<br />

sensors (<strong>Floating</strong> <strong>Car</strong>s) supplements in<strong>for</strong>mation from these sources. The position and<br />

the speed <strong>of</strong> cars are acquired by satellite navigation in combination with mobile communication,<br />

cellular phone tracking systems and long wave positioning. Further knowledge<br />

<strong>of</strong> the relation among traffic-related parameters is used to estimate traffic flow in<br />

the road network. B<strong>as</strong>ed on the estimations available models <strong>for</strong> traffic-related air and<br />

noise emissions can be applied to calculate emission inventories with an improved spatial<br />

and temporal resolution. So the development <strong>of</strong> methods <strong>for</strong> the detection, storage<br />

and interpretation <strong>of</strong> <strong>Floating</strong> <strong>Car</strong> data h<strong>as</strong> the potential <strong>of</strong> improving the in<strong>for</strong>mation<br />

b<strong>as</strong>is <strong>for</strong> modelling <strong>of</strong> the traffic situation, air and noise pollution in regions with high<br />

traffic density.<br />

1. Objectives<br />

The state <strong>of</strong> the environment is normally <strong>as</strong>sessed by environmental monitoring systems<br />

(e.g. air pollution monitoring, noise monitoring, water pollution monitoring).<br />

Logistic <strong>as</strong> well <strong>as</strong> financial limitations reduce the amount <strong>of</strong> actually available in<strong>for</strong>mation<br />

to a number <strong>of</strong> sites that are then considered representative. Different<br />

modelling approaches have been developed to estimate the spatial distribution within<br />

1 arsenal research, Business Area Transport Technologies, Faradayg<strong>as</strong>se 3, A-1030 Wien,<br />

email: bernhard.nowotny@arsenal.ac.at , http://www.arsenal.ac.at<br />

2 arsenal research, Business Area Transport Routes Engineering, Faradayg<strong>as</strong>se 3, A-1030<br />

Wien, email: peter.maurer@arsenal.ac.at , http://www.arsenal.ac.at<br />

3 ARC Seibersdorf research GmbH, Systems Research Division, A-2444 Seibersdorf, email:<br />

wilfried.winiwarter@arcs.ac.at , http://www.arcs.ac.at


660<br />

the investigated area [e.g. Loibl et al., 1994]. As emissions <strong>of</strong> noise and atmospheric<br />

pollutants from the transport sector may considerably effect the environment, frequently<br />

the emissions from this sector constitute an input to such models. Emissions<br />

from transport <strong>of</strong> p<strong>as</strong>sengers or goods are known to vary according to a number <strong>of</strong><br />

traffic-related parameters such <strong>as</strong> traffic flow, speed, weather situation and specific<br />

vehicle properties (e.g. vehicle type, hub load). Currently many emission models are<br />

b<strong>as</strong>ed on statistical or historical data (e.g. vehicle licences per area and average driving<br />

time, historical time series <strong>of</strong> traffic flow) so that the modelling domain is covered<br />

in part only, which consequently leads to rather high uncertainty.<br />

The in<strong>for</strong>mation derived from <strong>Floating</strong> <strong>Car</strong> <strong>Data</strong> (FCD) h<strong>as</strong> already been recognised<br />

<strong>as</strong> an important source <strong>for</strong> traffic related in<strong>for</strong>mation (mainly speed, calculation<br />

<strong>of</strong> travel time). FCD technology h<strong>as</strong> the potential to deliver near real-time data<br />

which can be applied <strong>for</strong> traffic control me<strong>as</strong>ures <strong>as</strong> e.g. line management on motorways,<br />

line control systems, generation <strong>of</strong> traffic messages <strong>for</strong> drivers and other traffic<br />

participants [RHAPIT, 1995 and EUROSCOPE / FOCUS, 1999].<br />

The aim <strong>of</strong> this paper is to demonstrate how existing FCD can be applied to <strong>as</strong>sess<br />

the parameters required <strong>for</strong> traffic related environmental modelling. While no results<br />

from emission modelling are available at this stage, we can demonstrate which approaches<br />

are ready <strong>for</strong> application. Thus the described method is a further step towards<br />

integration <strong>of</strong> transport and environmental monitoring [see EEA, 2001].<br />

2. Detecting <strong>Floating</strong> <strong>Car</strong> <strong>Data</strong> and Generating Traffic In<strong>for</strong>mation<br />

The idea <strong>of</strong> using <strong>Floating</strong> <strong>Car</strong> <strong>Data</strong> (FCD) to collect traffic data could initiate a decisive<br />

change in traffic monitoring. This method uses sensors integrated in vehicles<br />

to collect data mainly <strong>of</strong> position and speed, but also additional parameters (steering<br />

wheel angle, road slope, etc.). The metered values are sent to a traffic in<strong>for</strong>mation<br />

sub-center with the help <strong>of</strong> the navigation unit via satellite or via GSM- or GPRS<br />

mobile phones.<br />

There are three ways to locate a vehicle:<br />

1) Satellite navigation (GPS/EGNOS/GALILEO) in combination with<br />

GSM/GPRS/UMTS data transfer<br />

Satellite navigation systems have already been implemented <strong>for</strong> commercial systems<br />

<strong>of</strong> haulage companies and other vehicle fleets (e.g. taxicabs). A wider application <strong>for</strong><br />

the generation <strong>of</strong> traffic in<strong>for</strong>mation h<strong>as</strong> been tested in several pilot trials in European<br />

cities [c.f. Offermann, 2001, EUROSCOPE / FOCUS, 1999], but few systems<br />

evolved beyond the test ph<strong>as</strong>e [e.g. RHAPIT, 1995]. The re<strong>as</strong>ons <strong>for</strong> not entering a<br />

commercial ph<strong>as</strong>e were rather organisational than technical obstacles (e.g. missing<br />

business c<strong>as</strong>es or agreements in <strong>for</strong>m <strong>of</strong> public-private partnerships).<br />

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661<br />

The in<strong>for</strong>mation supplied by satellite navigation systems are geographical coordinates<br />

and direction <strong>of</strong> the vehicle. The precision <strong>of</strong> location in<strong>for</strong>mation depends<br />

on the satellite navigation system used (currently only GPS is available, EGNOS and<br />

GALILEO are still in development).<br />

2) Cellular Phone tracking systems <strong>as</strong> systems used to run Location B<strong>as</strong>ed Services<br />

(LBS)<br />

Another method to collect mobility data is “tracking” <strong>of</strong> mobile phones. The mobile<br />

phones are called from an in<strong>for</strong>mation center via a special code, which requests the<br />

SIM-card <strong>of</strong> the mobile phone to send back an SMS with the number <strong>of</strong> the currently<br />

used radio cell. This cell-ID is linked to the co-ordinates <strong>of</strong> the b<strong>as</strong>e station and supplies<br />

relatively precise in<strong>for</strong>mation about the current position <strong>of</strong> the mobile phone<br />

depending on the size <strong>of</strong> the radio cell (several hundred meters in urban regions).<br />

This position data is collected in fixed time steps. In a similar way <strong>as</strong> by GPS, the<br />

travel times in a region can be metered by tracing some mobile phones. Traffic in<strong>for</strong>mation<br />

<strong>of</strong> the current position <strong>of</strong> the tracked mobile phones is generated by comparing<br />

historic travel time data with the current travel times.<br />

3) Long wave positioning using hyperbolic navigation methods<br />

A combination <strong>of</strong> long wave positioning and satellite navigation reduces the shadowing<br />

and reflection effects (urban canyoning) in urban regions (e.g. DATATRAK system).<br />

Additionally a dGPS-signal is modulated onto the long wave to revise a noisy<br />

signal to get a more exact position value.<br />

A realistic image <strong>of</strong> the current traffic situation can only be produced with a<br />

minimum <strong>of</strong> pursuant-equipped vehicles in the investigated road network. The proportion<br />

<strong>of</strong> floating cars in the whole vehicle fleet depends on the purpose and the<br />

security <strong>of</strong> the result. The recognition <strong>of</strong> a traffic jam demands a smaller proportion<br />

than the calculation <strong>of</strong> an exact average velocity. If a generated traffic message h<strong>as</strong><br />

to be confirmed by more than one vehicle on the same road segment the proportion<br />

(and the correlated probability <strong>of</strong> a p<strong>as</strong>sing vehicle) h<strong>as</strong> to be higher. A pilot trial in<br />

the Rhine/Main Region [RHAPIT, 1995] states that 2 to 3 % <strong>of</strong> traffic volume is<br />

necessary <strong>for</strong> f<strong>as</strong>t and reliable detection <strong>of</strong> a traffic disruption. Due to the currently<br />

low level <strong>of</strong> pursuant-equipped vehicles this traffic data metering method will only<br />

be applicable in a few years. The current architecture <strong>of</strong> a Traffic In<strong>for</strong>mation Center<br />

(TIC) should consider the implementation <strong>of</strong> new interfaces and algorithms to be<br />

able to use in<strong>for</strong>mation from FCD technologies.<br />

The individual position values arriving from the <strong>Floating</strong> <strong>Car</strong>s have to be allocated<br />

to a virtual metering station in a digital road map stored in a Geographic In<strong>for</strong>mation<br />

System (GIS) be<strong>for</strong>e the integration <strong>of</strong> FCD into a traffic simulation.<br />

Unlike <strong>for</strong> stationary metering stations, which collect data <strong>for</strong> fixed road sections,<br />

there is the possibility to generate “dummy metering stations” with any desired distance<br />

in between according to the “traffic sensitivity” <strong>of</strong> the road section. This per-<br />

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Copyright © IGU/ISEP, Wien 2002. ISBN: 3-9500036-7-3


662<br />

mits a more differentiated view on the current traffic situation. Furthermore the network<br />

<strong>of</strong> expensive fixed traffic count devices (loop detectors) can be reduced to a<br />

minimum which may be necessary <strong>for</strong> reference purposes.<br />

As the availability <strong>of</strong> FCD depends on the presence <strong>of</strong> specially equipped vehicles<br />

a fe<strong>as</strong>ible vehicle flow will first be reached in urban are<strong>as</strong> where<strong>as</strong> little in<strong>for</strong>mation<br />

will be available in rural are<strong>as</strong>. As most environmental problems related to transport<br />

occur in urban are<strong>as</strong> or along routes with high traffic flow (e.g. congestion, peaks <strong>of</strong><br />

air pollution, high noise emissions) the method delivers data precisely where it is<br />

most urgently needed.<br />

For the calculation <strong>of</strong> emissions from the transport sector an estimation <strong>of</strong> traffic<br />

flow on a specified road segment h<strong>as</strong> to be available. As FCD mainly deliver position<br />

and speed <strong>of</strong> vehicles the parameter traffic flow on a certain road segment h<strong>as</strong> to<br />

be estimated from further in<strong>for</strong>mation on the road segment (e.g. number <strong>of</strong> lanes,<br />

traffic light ph<strong>as</strong>es and development <strong>of</strong> <strong>as</strong>sociated waiting queue, historical and realtime<br />

data from detectors) and speed. As the vehicle fleet equipped <strong>for</strong> transmitting<br />

<strong>Floating</strong> <strong>Car</strong> <strong>Data</strong> is only a representative sample <strong>for</strong> the whole vehicle fleet the exact<br />

traffic flow and vehicle cl<strong>as</strong>sification will still require the use <strong>of</strong> appropriate loop<br />

detectors.<br />

3. Generating In<strong>for</strong>mation from <strong>Floating</strong> <strong>Car</strong> <strong>Data</strong> <strong>for</strong> Status and<br />

Impact <strong>of</strong> Transport Related Activities<br />

3.1 Atmospheric pollutants<br />

Current approaches to estimate emissions from road traffic all combine an emission<br />

factor with available in<strong>for</strong>mation on vehicle mileage [Ntziachristos and Samar<strong>as</strong>,<br />

2000]. This very simple approach is complicated by the necessity to separate different<br />

vehicle types and vehicle concepts (e.g. Diesel vs. g<strong>as</strong>oline driven cars, with or<br />

without catalytic converter). Emission factors are also available <strong>for</strong> different driving<br />

conditions, ranging from stop-and-go traffic to highway speed traffic. Now the vehicle<br />

fleet may be determined from car registration numbers, or from occ<strong>as</strong>ional <strong>as</strong><br />

well <strong>as</strong> from continuous traffic counts (loop detectors). Also, vehicle mileage <strong>as</strong> well<br />

<strong>as</strong> temporal distribution <strong>of</strong> emissions may be estimated from such traffic counts.<br />

However, especially in cities the number <strong>of</strong> traffic count sites is relatively small in<br />

respect to total mileage and requires the use <strong>of</strong> outputs from sophisticated traffic<br />

models, if at all available. Additionally, speed distribution is very difficult to <strong>as</strong>sess.<br />

Vehicle speed is not only required to apply the correct emission factor, but even the<br />

ratio between different pollutants. Emissions <strong>of</strong> Nitrogen oxides (NO x ) tend to be<br />

higher at higher motor temperatures and speeds, compounds emitted due to incomplete<br />

combustion (carbon monoxide (CO) and volatile organic compounds (VOC))<br />

tend to be extremely high during stop-and-go traffic.<br />

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Copyright © IGU/ISEP, Wien 2002. ISBN: 3-9500036-7-3


663<br />

<strong>Floating</strong> car data deliver in<strong>for</strong>mation on speed <strong>of</strong> vehicles and general traffic<br />

situation. With the help <strong>of</strong> traffic modelling s<strong>of</strong>tware, historical data and a small<br />

number <strong>of</strong> real-time data from me<strong>as</strong>urement points can be used to estimate traffic<br />

flow and total mileage throughout such a model area at an adequate temporal resolution.<br />

Emissions even may be <strong>as</strong>sessed real-time, a feature that is uncommon in standard<br />

emission inventories. Furthermore, the emission in<strong>for</strong>mation can be used <strong>as</strong> input<br />

to photochemical models. As the chemical regime within city centres is generally<br />

VOC limited in terms <strong>of</strong> ozone <strong>for</strong>mation (i.e. further VOC emissions will be critical<br />

<strong>for</strong> further photochemical activity – [see Prevot et al., 1997]) additional in<strong>for</strong>mation<br />

on the stop-and-go traffic will help to strongly incre<strong>as</strong>e reliability <strong>of</strong> emission inventories<br />

used <strong>for</strong> atmospheric modelling or even atmospheric air quality <strong>for</strong>ec<strong>as</strong>ts.<br />

3.2 Traffic-related Noise<br />

The main factors <strong>for</strong> the detection <strong>of</strong> noise emissions from transport are traffic load<br />

and composition (fraction <strong>of</strong> heavy duty vehicles), vehicle speed, road surface, road<br />

gradient and equipment <strong>as</strong> e.g. traffic lights. Traffic noise exposure can be calculated<br />

by appropriate models taking into account these parameters. Additional factors on<br />

noise generation are the distance <strong>of</strong> the receptor point from the roadway, height<br />

above road surface and street or ground morphology, obstacles (e.g. houses) and meteorological<br />

impacts.<br />

<strong>Floating</strong> car data deliver in<strong>for</strong>mation on speed <strong>of</strong> vehicles and general traffic<br />

situation. With the help <strong>of</strong> traffic modelling s<strong>of</strong>tware, historical data and a small<br />

number <strong>of</strong> real-time data from me<strong>as</strong>urement points can be used to estimate traffic<br />

load. This <strong>for</strong>ms the b<strong>as</strong>is <strong>for</strong> calculation <strong>of</strong> noise emissions where no exact me<strong>as</strong>urements<br />

are available.<br />

3.3 Integration <strong>of</strong> models into simulation s<strong>of</strong>tware<br />

The <strong>Floating</strong> <strong>Car</strong> <strong>Data</strong> method delivers b<strong>as</strong>ic dynamic in<strong>for</strong>mation <strong>of</strong> the current<br />

traffic situation at different points <strong>of</strong> times. This method presupposes simulation<br />

tools using variable time steps instead <strong>of</strong> constant time steps like the programs <strong>of</strong>fered<br />

today. Only online simulation can evaluate traffic data sent by moving vehicles<br />

at different times and positions.<br />

The air pollution model operating at ARC Seibersdorf calculates emissions with<br />

time steps <strong>of</strong> about one hour. There<strong>for</strong>e the results <strong>of</strong> an online traffic simulation<br />

have to be aggregated to the time steps used in the air pollution model in an interface<br />

s<strong>of</strong>tware. An open architecture <strong>of</strong> this interface between simulation and pollution<br />

models will <strong>as</strong>sure that changing or new parameters <strong>of</strong> the air pollution model (time<br />

steps, ...) can be considered without any technical ef<strong>for</strong>t.<br />

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Copyright © IGU/ISEP, Wien 2002. ISBN: 3-9500036-7-3


664<br />

4. Conclusions<br />

As air and noise pollution models depend on real-time traffic data the integration <strong>of</strong><br />

traffic in<strong>for</strong>mation with in<strong>for</strong>mation on air and noise emissions h<strong>as</strong> been recognised<br />

<strong>as</strong> an important step in urban are<strong>as</strong> [see HEAVEN, 2001]. Similar to air pollution the<br />

implementation <strong>of</strong> the planned Directive on the Assessment and Management <strong>of</strong> Environmental<br />

Noise will require the investigation <strong>of</strong> the noise situation in urban are<strong>as</strong><br />

[see CALM network, 2002]. As the equipment <strong>of</strong> fixed me<strong>as</strong>urement stations <strong>for</strong><br />

traffic, air pollution and noise detection is limited by financial constraints the application<br />

<strong>of</strong> in<strong>for</strong>mation from <strong>Floating</strong> <strong>Car</strong>s supplements the in<strong>for</strong>mation from these<br />

sources. So the development <strong>of</strong> methods <strong>for</strong> the detection, storage and interpretation<br />

<strong>of</strong> <strong>Floating</strong> <strong>Car</strong> data h<strong>as</strong> the potential <strong>of</strong> improving the in<strong>for</strong>mation b<strong>as</strong>is <strong>for</strong> modelling<br />

<strong>of</strong> traffic situation, air and noise pollution in regions with high traffic density.<br />

Bibliography<br />

CALM Community Noise Research Strategy Plan (2002): EU Commission, DG Research,<br />

GROWTH (5th FP), http://www.calm-network.com/index_start.htm<br />

EEA European Environment Agency (2001): Indicators tracking transport and environment<br />

integration in the European Union (TERM), 2001<br />

EUROSCOPE Efficient Urban Transport Operation Services Co-operation <strong>of</strong> Port Cities in<br />

Europe / subproject FOCUS (1999):, EU Directorate General XIII, Telematics Applications<br />

Programme, TAP - TR1023<br />

HEAVEN Healthier Environment through the Abatement <strong>of</strong> Vehicle Emissions and Noise<br />

(2001): EU Commission, IST Programme (5th FP), http://heaven.rec.org<br />

Loibl W., W. Winiwarter, A. Kopcsa, J. Zueger, R. Baumann (1994): Estimating the Spatial<br />

Distribution <strong>of</strong> Ozone Concentrations in Complex Terrain. Atmos Environ 28, 2557-<br />

2566.<br />

Ntziachristos L., Z. Samar<strong>as</strong> (2000): COPERT III. Computer programme to calculate emissions<br />

from road transport. Methodology and emission factors (Version 2.1). Technical<br />

report No 49. European Environment Agency, Copenhagen, DK<br />

Offermann F., Ein Neuro-Fuzzy-Modell zur Reisegeschwindigkeitsabschätzung auf Richtungs-Fahrbahnen<br />

b<strong>as</strong>ierend auf einer Fusion lokaler und fahrzeuggenerierter Verkehrsdaten,<br />

Dissertation an der Fakultät für Bauingenieurwesen der Rheinisch-<br />

Westfälischen Technischen Hochschule Aachen, Nov. 2001<br />

Prevot, A. S. H., J. Staehelin, G. L. Kok, R. D. Schillawski, B. Neininger, T. Staffelbach, A.<br />

Neftel, H. Wernli, and J. Dommen (1997): The Milan photooxidant plume. J. Geophys.<br />

Res., D102, 23375-23388.<br />

RHAPIT Rhein/Main Area Project <strong>for</strong> Integrated Traffic Project Definition (1995): EU Directorate<br />

General XIII, Programme DRIVE II - V2055<br />

29.08.02, 9202 EI P 074 I2 NowotnyB.doc<br />

Copyright © IGU/ISEP, Wien 2002. ISBN: 3-9500036-7-3

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