THE ADVANTAGES OF ROAD-SIDE AIR POLLUTION DATA FOR IDENTIFYING PRIORITY IN TRAFFIC MANAGEMENT AND URBAN HOTSPOT MONITORING Driejana 1 *, Harmein Rahman.

Slides:



Advertisements
Similar presentations
Current Activities on Urban Air Pollution in Cambodia
Advertisements

1 Urban Air Quality Improvement (UAQi) Program Development Lesson Learned from Indonesian Experience Presented at Better Air Quality Conference Yogyakarta,
TCEQ Air Permits Division Justin Cherry, P.E. Ahmed Omar Stephen F. Austin State University February 28, 2013.
Assessing PM 2.5 Background Levels and Local Add-On Prepared by Bryan Lambeth, PE Field Operations Support Division Texas Commission on Environmental Quality.
Preparation of the guidelines for vehicle non-exhaust emission modelling of PM10 and PM2.5 in Latvia Aiga Kāla, Valts Vilnītis SIA Estonian, Latvian &
Busan, South Korea E. C. Yoo Busan Metropolitan Government Institute of Health and Environment.
The experience from Stockholm city road tax Christer Johansson Lars Burman Tage Jonson Bertil Forsberg Umeå university
Fred Weber 2010 ANNUAL POLIS CONFERENCE 25./26. November 2010, Dresden © Department of Environment – City of Hagen Air quality depending traffic management.
Modelling Motor Vehicle Emissions
2  Density Population: 3,634 persons/ km 2 (2010) Inner areas : 11,400 persons/ km 2 (2008) Outer areas : 2,400 persons/ km 2 (2008)  Population Registered:
Update of EEA´s Core Set Indicator th EIONET Workshop on Air Quality Bern, 30 th September 2014 Alberto González Ortiz Project Manager – AQ data.
Controlling Vehicular Air Pollution in Beijing Professor Kebin He Dept. of Environmental Science & Engineering, Tsinghua University Orlando, Florida, USA.
Jenny Stocker, Christina Hood, David Carruthers, Martin Seaton, Kate Johnson, Jimmy Fung The Development and Evaluation of an Automated System for Nesting.
Air Quality Management Initiatives for Kuala Lumpur: A study of stakeholder roles, emission sources, and vulnerable populations Dr. Scott Kennedy Energy.
Measurement of NO 2 Concentration in Ambient Air in Karachi using Diffusion Sampling By Zia-ul-Islam Director, Pak-EPA.
Joint Intersectoral Task Force on Environmental Indicators Geneva 5 – 7 November 2013 Transport and environment: newly proposed indicators Vladislav Bizek.
1 airpointer ® applications and markets. 2 Main advantages of the airpointer: flexibility, ease of installation and transportation turn key system energy.
Air Quality Management in Mumbai V.K.Phatak MMRDA.
Making Way for Public Rapid Transit in South Asia and its Impact on Energy and Environment Bangalore, Dhaka and Colombo Ranjan Kumar Bose & Sharad Gokhale.
Evaluating Robustness of Signal Timings for Conditions of Varying Traffic Flows 2013 Mid-Continent Transportation Research Symposium – August 16, 2013.
Air quality and health impact assessment AQ information at the regional scale, urban background scale and street scale past, present and future air quality.
Earth System Sciences, LLC Suggested Analyses of WRAP Drilling Rig Databases Doug Blewitt, CCM 1.
1 EEA Activities Collect, process and disseminate air emission and air quality data Report on trends in air emissions and in air quality Support the development,
Harikishan Perugu, Ph.D. Heng Wei, Ph.D. PE
Overview What we’ll cover: Key questions Next steps
AIR QUALITY MINISTRY OF SCIENCE AND ENVIRONMENTAL PROTECTION REPUBLIC OF SERBIA Dusanka Stanojevic Directorate for.
25 June 2009, London Impact significance in air quality assessment Application of EPUK criteria to road schemes?
Kitakyushu Initiative for a Clean Environment: Capacity Building for Urban Air Quality Management Mushtaq Ahmed Memon and Hidefumi IMURA 3 rd Thematic.
*Institute for Environmental Studies, Charles University in Prague, Benátská 2, Prague 2, Czech Republic ** Institute of Chemical Process Fundamentals,
Company LOGO Traffic Impact Study Case: Al-Irsal Center Project in Al-Bireh City Under the Supervision of: Pro.Sameer A. Abu-Eisheh Prepared by: Mohammad.
Ramifications of Charlotte Regional Growth and Weekday Activities on Primary and Secondary Emissions Jenny L. Perry and Patrick M. Owens Department of.
Latvian Environmental, Geology and Meteorology agency Future development scenarios for traffic system and air pollution in Riga city Iveta Steinberga La.
Air Quality & Traffic August 25, 2015.
P. Otorepec, M. Gregorič IVZ RS Use of rutinely collected air pollution and health data on local level for simple evaluation of health impact.
| Folie 1 Assessment of Representativeness of Air Quality Monitoring Stations Geneva, Wolfgang Spangl.
Malé Declaration Joint Training on Regional Refresher Course and Soil Acidification Asian Institute of Technology (AIT), Bangkok, Thailand from
Transboundary Air Pollution Plan of Islamic Republic of Iran
TNO Environment, Energy and Process Innovation Menno Keuken Traffic and air quality in Europe Session 1: Mexico Workshop.
Ozone Transport that Impacts on Tribal Land: Case Study Stan Belone Salt River Pima-Maricopa Indian Community.
Ministry of Environment and Spatinal Planning Environmental Protection Agency Air Quality in the Republic of Kosovo Ajet Mahmuti Officer for air quality.
IN THE NAME OF GOD 1. IRAN Report Hamoun Station at East of Iran By: Reza Mirshekar Malé Declaration Joint Training on Regional Refresher Training Workshop.
TNO Environment, Energy and Process Innovation Menno Keuken Impact of speed control on urban air quality (Rotterdam) Session 2: Mexico Workshop.
Exposure Assessment for Health Effect Studies: Insights from Air Pollution Epidemiology Lianne Sheppard University of Washington Special thanks to Sun-Young.
1 Improvement of Public Transport in Surabaya Multidisciplinary MSc Project Faculty Civil Engineering and Geosciences TU Delft.
The Male’ Declaration Proposal for Phase III. Looking back to think ahead Policy Dialogue Background Materials Ministerial agreement Capacity building.
AIR QUALITY IN SLOVENIA Anton Planinšek Environmental Agency of the Republic of Slovenia.
Voivodeship Inspectorate of Environmental Protection in Szczecin ASSESSMENT OF AIR QUALITY IN SZCZECIN AGGLOMERATION.
Arno Graff Susan Klose UBA-II 4.2 – Air Quality Assessment Some Aspects on Air Quality in Germany related to SOER 14th EIONET Meeting, Warsaw,
OSCAR Optimised Expert System for Conducting Environmental Assessment of Urban Road Traffic (OSCAR) ( )
Forecasting Land Use Change at European and at Urban Level: SASI and PROPOLIS EEA Expert Meeting on Land Use Accounting Copenhagen, 16 March 2005 Spiekermann.
Presented by: Rich Baldauf, EPA National Air Monitoring Conference Denver, CO May 15,
State ecological monitoring system of Moscow-City.
Urban Mobility Management and Emissions Measurement System Boile Maria 1,2 Afroditi Anagnostopoulou 1 Evangelia Papargyri 1 1 Centre for Research and Technology.
Linking Air Quality & Climate Change strategies at city level
Bangkok Metropolitan Administration’s activities to control air quality 1.
Exposure to Air Pollution James Tate and Paul Seakins
Multi-objective Analysis For Passengers’ Routing Using Car/Bicycle
Tasnim Rabee’ Nagham Dmaidi
Suggested Analyses of WRAP Drilling Rig Databases
Jenny L. Perry and Patrick M. Owens Department of Chemistry
SCHOOL OF HIGHWAY, CHANG`AN UNIVERSITY, XI`AN, , CHINA
RDE Discussion of Conformity Factors - JRC views on the ACEA propsal - - August 2015 – RDE Data Evaluation group European Commission - Joint Research Centre.
Portuguese National Strategy for Air 2020 (ENAR 2020)
Forest fires and air pollution in Portugal
Improving Transportation Inventories Summary of February 14th Webinar
U.S. Perspective on Particulate Matter and Ozone
IPA support to West Balkan countries –Air Quality
JDS International seminar 2018
WORK OF THE UNITED KINGDOM AIR QUALITY EXPERT GROUP (AQEG)
Air Quality Management in Mumbai
Presentation transcript:

THE ADVANTAGES OF ROAD-SIDE AIR POLLUTION DATA FOR IDENTIFYING PRIORITY IN TRAFFIC MANAGEMENT AND URBAN HOTSPOT MONITORING Driejana 1 *, Harmein Rahman 2, Andria Sukowati 3, Mahawira S.Dillon 1 and Mega Octaviani 1 1 Air and Solid Waste Management Division; 2 Transportation Engineering Division Faculty of Civil and Environmental Engineering, ITB, Bandung, INDONESIA 3 West Java Environmental Protection Agency, Bandung, INDONESIA Institut Teknologi Bandung

Outline Background Background Methodology Methodology Results and Discussion Results and Discussion Conclusion and recommendations Conclusion and recommendations

Background (1) Indonesia has 34 automatic monitoring stations installed in 10 cities  not enough (data on number of big cities) Indonesia has 34 automatic monitoring stations installed in 10 cities  not enough (data on number of big cities) Monitoring can not cover spatial variations, e.g., hotspots in urban area  health risk of short term exposure can not be evaluated Monitoring can not cover spatial variations, e.g., hotspots in urban area  health risk of short term exposure can not be evaluated Vehicle emission is one of the most significant source of pollution that could be controlled with traffic management Vehicle emission is one of the most significant source of pollution that could be controlled with traffic management

Continuous automatic monitoring is ideal but……. - Not enough equipment to cover the spatial variation - problem in operation and maintenance costs 87 sites Background (2) sites

Objectives To identify and examine parameters to be monitored at hotspots such as road-side in order to optimize urban air quality monitoring system To identify and examine parameters to be monitored at hotspots such as road-side in order to optimize urban air quality monitoring system To analyze the characteristic of road-side air quality as major information for service improvement with strategic traffic management To analyze the characteristic of road-side air quality as major information for service improvement with strategic traffic management

Methodology Continuously measure of 30-minute average concentration of CO, PM 10, NO, NO 2, SO 2, and O 3 at 5 road-side locations in Jakarta and 3 sites in Bandung using mobile monitoring for 1 week Continuously measure of 30-minute average concentration of CO, PM 10, NO, NO 2, SO 2, and O 3 at 5 road-side locations in Jakarta and 3 sites in Bandung using mobile monitoring for 1 week Analysing hourly and daily exceedances of pollutants Analysing hourly and daily exceedances of pollutants Examining diurnal pattern of pollutant parameters in conjunction with traffic pattern Examining diurnal pattern of pollutant parameters in conjunction with traffic pattern Evaluating some options of traffic management Evaluating some options of traffic management LOCATIONS OF MONITORING

Results and Discussion: Exceedances Hourly and daily exceedances during one-week monitoring Hourly exceedances: NO 2 at 3 out of 5 location in Jakarta and 1 location in Bandung Daily exceedances: - NO 2 at all location in Jakarta and 1 location in Bandung - PM 10 at 2 locations in Jakarta Number in red showing number of exceedances occured

Results and Discussion: Pollutant Parameters NO 2 is the parameter that shows more exceedances, both hourly and daily NO 2 is the parameter that shows more exceedances, both hourly and daily PM 10 has daily exceedances PM 10 has daily exceedances PM 10 and O 3 are known as the critical parameter found in PSI (MoE, 2006) PM 10 and O 3 are known as the critical parameter found in PSI (MoE, 2006)  PM 10 were found to be high at urban sites, and O 3 at sub-urban sites (Driejana, 2003)  Health impact of NO 2 short-term exposure in urban area has been overlooked

Result and Discussion: Diurnal variation NO x Influence of traffic on NOx variation, but concentration still comply with hourly standard Need ambient monitoring to monitor traffic emission but do not need a real- time or short term exposure one Can be monitored by more economical approach such as passive sampler Hourly exceedances occurred May need short-term exposure monitoring Needs emission control from traffic activity

Results and Discussion: Categorization of compliance Does not exceed standards Does not exceed standards Exceed the hourly AAQ standard only during certain period of time Exceed the hourly AAQ standard only during certain period of time Exceed the hourly AAQ standard ambient for most of the time of the day Exceed the hourly AAQ standard ambient for most of the time of the day Exceed the daily AAQ standard Exceed the daily AAQ standard

Discussion: Traffic Management Options Link Link Reduce/eliminate side friction (p) Reduce/eliminate side friction (p) One/two system (t) One/two system (t) Road widening (p) Road widening (p) Intersection Intersection Signaling (for un-signalized intersection) (p) Signaling (for un-signalized intersection) (p) Re-setting (for signalized intersection) (p) Re-setting (for signalized intersection) (p) Approach geometric improvement (p) Approach geometric improvement (p) Traffic Traffic Sorting (t) Sorting (t) Re-routing (Public Transport) (t) Re-routing (Public Transport) (t) Limiting (t) Limiting (t) Notes:p = permanent scheme ; t = temporary

Discussion: Example of TM scheme Temporary TM Scheme Implementation Period

Conclusion and Recommendations (1) Available mobile monitoring can be utilised for screening the location and parameter to be monitored Available mobile monitoring can be utilised for screening the location and parameter to be monitored Selected monitoring for certain parameter based on priority will reduce the cost, while allowing better spatial coverage Selected monitoring for certain parameter based on priority will reduce the cost, while allowing better spatial coverage Roadside is a hotspot for NOx, the hourly exceedances are overlooked by the current reporting method Roadside is a hotspot for NOx, the hourly exceedances are overlooked by the current reporting method Roadside data can be used to determine and evaluate traffic management scheme applied in the polluted area Roadside data can be used to determine and evaluate traffic management scheme applied in the polluted area

Conclusion and Recommendations (2) Air pollution parameters and its related traffic parameters define traffic management objective (volume and speed) Air pollution parameters and its related traffic parameters define traffic management objective (volume and speed) The objective determine the suited traffic management scheme The objective determine the suited traffic management scheme Temporary scheme solutions (one way system, 3 in 1, traffic signal re-setting, sorting and re-routing of public transport) are suitable for controlling hourly concentration exceedance Temporary scheme solutions (one way system, 3 in 1, traffic signal re-setting, sorting and re-routing of public transport) are suitable for controlling hourly concentration exceedance Permanent scheme solutions (reducing/eliminating side friction, widening, signaling, geometric improvement) should be used for controlling frequent hourly and daily concentration exceedance Permanent scheme solutions (reducing/eliminating side friction, widening, signaling, geometric improvement) should be used for controlling frequent hourly and daily concentration exceedance

Swisscontact and BPLHD DKI for providing the road-side monitoring data in Jakarta Joint Action Research of CIDA-AIT’s South East Asia - Urban Environmental Management Application Project (SEA UEMA) of the Faculty of Civil and Environmental Engineering ITB, Indonesia, West Java Environmental Protection Agency, Indonesia and the Asian Institute of Technology, Thailand Thank you! Acknowledgement