Estimation of carbon dioxide emissions per urban center link unit using data collected by the Advanced Traffic Information System in Daejeon, Korea
Introduction
The continuous increase in greenhouse gases has brought about global warming (IPCC, 2007). In particular, carbon dioxide (CO2) is a major cause of global warming (IPCC, 2007). In various urban activities, CO2 is emitted as a by-product, and the transportation sector is one of the major sources of CO2 emission (Zegras, 2007, Christen et al., 2011, Vicente et al., 2013). In 2008, road emissions accounted for 80% of the total emission in the transportation sector, which has since then increased continuously (Li et al., 2013).
To resolve this problem, Intelligent Transportation Systems (ITS) were introduced for reducing CO2 emissions by improving road efficiency and mitigating traffic congestion (Lu et al., 2007). For the US, the United States Department of Transportation (USDOT) undertook Connected Vehicle Research, which focuses on “improving systematic productivity and individual mobility and reducing the negative environmental impacts of the surface transportation system (Glassco et al., 2011).” Applications for the Environment: Real-time Information Synthesis (AERIS), a sub-project of the Connected Vehicle Research, uses vehicle-to-vehicle (V2V) and vehicle-to-infrastructure (V2I) technologies to collect real-time traffic data and to support ITS services that can reduce CO2 emissions by using the collected data (Miller et al., 2011).
Glassco et al. (2011) claimed that an exact estimation of CO2 road emissions is required before executing ITS services for having certain desired environmental effects and presented modeling measurement, which is the most widely used technology for measuring the CO2 emission. Modeling measurement calculates emission by vehicle movement and is then divisible into microscale and mesoscale models. The microscale model (e.g. PHEM, CMEM) uses the driving cycles of vehicles, vehicle data, road gradient, etc., for calculating the amount of instantaneous emission (Smit et al., 2010, Franco et al., 2013). The advantage of this model is the use of detailed input data for the estimation of the exact amount of instantaneous emission. However, its major drawback is the impossibility of collecting the driving cycle data of all of vehicles on the road for calculating the amount of CO2 emission. The mesoscale model (e.g. COPERT, MOBILE, EMFAC) uses emission factors (EFs) and vehicle kilometers traveled (VKT) per average speed of different vehicle types for calculating the amount of emission per link unit (Smit et al., 2010). The advantage of this model is its capability of calculating the amount of emission per average speed of the total traffic volume within the given link, but the use of the average speed as the calculation basis has a drawback in that it cannot reflect driver behaviors and road characteristics.
Traffic emission estimation as calculated by modeling measurement can be used for supporting decision making (e.g. reducing personal mobility, restructuring urban areas and switching to low carbon vehicle) for greenhouse gas reduction (Carmichael et al., 2008, Escobedo et al., 2008, Mensink and Cosemans, 2008, Nejadkoorki et al., 2008). Greenhouse gas emissions on a regional scale refer to the total emission from traffic, and mesoscale modeling is the most appropriate emission estimation technique for these. The existing studies used simulations (e.g. SATURN, EMME/2, TransCAD, TRAEMS) for calculating emissions via average speed and VKT (Nejadkoorki et al., 2008, Affum et al., 2003). Emissions on the roads are estimated by predicting the traffic flow and the average speed per link unit as the output data on the basis of the input data regarding a trip (or journey) matrix and road traffic networks, etc., and the output data are used for calculating the emission volumes. However, such simulations can reflect subjective viewpoints of planners. As emissions are calculated on the basis of the input data, it is impossible for ever-changing real-time traffic situations to be reflected in the calculation. Accordingly, this study uses real-time traffic data collected from Advanced Traffic Information System (ATIS) to estimate CO2 emissions per link unit in central urban areas. ATIS, which has recently been introduced to provide drivers with real-time traffic information, uses a V2I wireless technology (Kianfar and Edara, 2013). It directly collects data from PVs that pass urban links to estimate a space-mean speed (Li et al., 2011, Miwa et al., 2012). For Daejeon metropolitan city, where this study is based, the IDs and travel-time information of PVs, which are equipped with an on-board unit (OBU) and pass within the communication range of roadside equipment (RSE), are collected via dedicated short-range communication (DSRC) and transmitted to the center. The traffic center calculates the differences between RSEs, whereupon the link travel time of each PV is calculated. When the mesoscale model is applied to the calculation of CO2 emissions in central urban links, VKT information is required, which in turn requires the collection of passing traffic volume per link unit. However, it is impossible to install fixed detectors (loop, video, radar and infrared etc.) at every link to collect the traffic volume, considering the implementation and operational costs that doing so would involve (Zhang et al., 2007, Zhou et al., 2011). In this study, therefore, traffic volume is estimated on the basis of the data collected from PVs. As PVs, Daejeon uses OBU, which enables the use of the electronic toll collection system (ETCS) attached to a vehicle. The distribution rate of OBU in Daejeon is currently 10.6%. Therefore, the number of OBUs collected per unit time data can be determined as a sample extracted from a specific ratio of the entire traffic population that passes the links. Of the PV data collected to estimate traffic speeds at links, the number of PVs per unit time is additionally collected. Accordingly, in this study, we first use the number of PVs and the data collected from ATIS and estimate the total population that passes the links. The objective of this study is to estimate CO2 emissions from the road networks by utilizing VKT calculated from the traffic data collected from link units, and the average speed.
This rest of this paper is organized as follows: In Section 2, the analysis of the structure of road networks of Daejeon, the current status of ATIS, and the characteristics of the collected data are described. In Section 3, the application of a multiple linear regression model and an artificial neural network model (ANN) to suggest ways to estimate the traffic volume is discussed. In Section 4, the use of the estimated traffic volume for the calculation of the CO2 emission in urban road networks is described, and in the Section 5, conclusions and future study directions are discussed.
Section snippets
Study area
In 2013, the area of Daejeon is 539.84 km2, and the population is 1,527,857 (Statistics Korea, 2013). The total length of the road networks is 1030 km, which consists of 2411 links and 820 nodes. Major arterial roads are 240 km long with 586 links and 285 nodes.
Daejeon installed 376 units of RSE at major intersections to collect ATIS traffic data. Further, major spots are installed with 60 visual detectors in order to measure the traffic volume. The current status of the road networks, RSE, and
Overview
This study uses the mesoscale modeling technique in order to estimate CO2 emissions on the roads, which requires speed and traffic volume per link unit. Currently, speeds are collected from 1572 links where RSEs are installed, but it is impossible to install a fixed detector at each necessary link to collect the traffic volume. Therefore, in this study, we use the PV data collected every 15 min to estimate the traffic volume. The PV data are the number of PVs equipped with OBU that pass the
Method for estimating CO2 emissions
In this study, mesoscale modeling is applied to estimate CO2 emissions. In order to estimate CO2 emissions per link unit in the urban center, the traffic speed, VKT, and emission factor by vehicle type are required. VKT can be calculated using the traffic volume (veh/15 min) and link length (km). Accordingly, the calculation for emissions per link unit is shown below in Eqs. (6), (7).where Emissioni is an estimation of CO2 emissions (g/15 min)
Discussion and conclusion
In this study, we attempted to calculate CO2 emissions per link unit using real-time data. Currently, Daejeon's ATMS provides traffic speeds by using PV data that contain a daily average of 1 million PVs. Besides speeds, the numbers of PVs is collected but not currently used. In this study, we estimated traffic volume per link unit by utilizing the number of PVs per 15-min unit. The estimated traffic volume in turn is used for calculating VKT and then the emissions per link unit. Multiple
Acknowledgment
This work was researched by the supporting project to educate GIS experts
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