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This report examines the health impacts of air pollutants in Hamilton, focusing on sources such as transportation and industry. It identifies and ranks major pollutants, including NOx, SO2, CO, and PM10, utilizing mobile monitoring techniques. The study assesses the effects of vehicle idling, especially around schools, and highlights the issue of road dust. Data from various monitoring locations provide insights into pollution levels and their correlation with community health risks. The findings aim to inform community actions for cleaner air through cooperative risk management strategies.
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Air Pollution in Hamilton – Health Effects and SourcesNovember 22, 2006McMaster Centre for Spatial Analysis
Clean Air Hamilton Strategy Risk Management Approach Applied to Community Wide Actions • Identify Problem • Measure/Evaluate • Prioritize Risks • Inform Community • Cooperative Actions www.cleanair.hamilton.ca
The Problem Health Impacts of Air Pollutants in Hamilton Sahsuvaroglu & Jerrett 2003
Health Impacts in Hamilton – by Air Pollutant Sahsuvaroglu & Jerrett 2003
Study Objectives, Phase 1“Where is it coming from?” • Identify and rank sources, including transportation sources, of NOx, SO2, Airborne Particles and CO, using mobile monitoring techniques (no direct local sources of Ozone). • Investigate the effect of idling vehicles at a designated school during student drop off and pickup times. • Investigate trackout/road dust issues
National Pollutant Release Inventory – Hamilton Point Sources • PM10 56 Sources • CO 14 Sources • NOx 13 Sources • SO2 9 Sources
What We’d Expect to See • Carbon Monoxide – 66% Transportation, 23% Industry • Sulphur Dioxide – 92% Industry, 5% Transportation • Nitrogen Oxides – 57% Transportation, 37% Industry • PM10 – 73% Open Sources/Road Dust, 18% Industry Note: MOE identified trackout/road dust resuspension as a major problem
Emission Sources by Regions in Hamilton Flamborough/Waterdown NE Ind Stny Crk East Mtn
Roof Mounting Sampling Intakes Gaseous/Particulate
City/Traffic Monitoring • City Wide Sampling • Road Dust/Road Impacts • Intersection Impacts • Arterial Road Impact/ Burlington St. • Cycle Routes/ Anti Idling
NO ppb Wind
Burlington St Contribution (Approx. 600 Trucks/Hr)
Trackout/Diesel Trucks • PM2.5, PM1 Components • Photos • Sample Trace • Consolidated PM10 Data • Comparison Previous Data
Road Dust/Trackout 18 Locations Monitored, 14 Sources Identified
PM10 ROAD DUST Ben Garden, Savas Kanaroglou, Pat DeLuca, Spatial analysis Unit, McMaster University
Source Tracking • Photos • SO2 Tracing • Other Contaminants • SO2 Data Consolidation • Source Ranking/NPRI Comparison, SO2, NO, PM10
Source Source Impact Plume Back Tracking
Ambient SO2 vs NPRI SO2 Point Sources: A-Integrated Steel, B-Integrated Steel, AN- Steel Byproducts, C-Carbon Black, G-Steel, B-Integrated Steel, A-Integrated Steel, D-Lime, CP-Rail Yard.
Ambient NO vs NPRI NO Point Sources: B-Integrated Steel, CP-Rail Yard, G-Steel, A-Integrated Steel, AN- Steel Byproducts, D-Lime, C-Carbon Black, AM-Cogeneration, AT-Chemical.
Ambient PM10 vs NPRI PM10 Point Sources: B-Integrated Steel, ABP-Recycling, AY-Agricultural Product Handling, AG-Aggregate or AZ-Steel Handling, AU-Recycling, AT-Chemical, M-Foundry, G-Steel, CP-Rail Yard, A-Integrated Steel, AM-Natural Gas Cogeneration Facility, C-Carbon Black.
Ambient CO vs NPRI CO Point Sources: AM-Cogeneration, AT-Chemical; AN- Steel Byproducts; B-Integrated Steel; A-Integrated Steel; G-Steel; C-Carbon Black; CP-Rail Yard.
Continuous Monitoring Locations Centre Industrial
SO2 NE