Improving Transportation Inventories Summary of February 14th Webinar

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Presentation transcript:

Improving Transportation Inventories Summary of February 14th Webinar

Developing a Multi-Year Urban GHG Emission Inventory by Harnessing the Breadth and Depth of an Urban Traffic Count Program Marianne Hatzopoulou (University of Toronto)

Motivation: Why are we doing this: On-road transportation constitutes a significant portion of GHG emissions in urban areas. Exposure to traffic-related air pollution has been associated with a wide range of health effects: chronic illnesses, respiratory, cardiovascular diseases. Why are we doing this: To understand GHG emissions and traffic related air pollution

How we can really use count data from traffic counts to generate volumes on the road and use those to further generate an emission inventory? We are generating an emission inventory for transportation There are two ways – from travel demand model (assigning cars) – problem: they are not accounting for all cars Challenge: Traffic counts are not conducted on every single road in an urban area To move from these isolated points where traffic counts are conducted into generating a map that featured annual average daily traffic or other measure throughout the entire network.

Opportunity The city of Toronto manages an extensive traffic count which allows to harness the depth and breadth of the program to estimate traffic volumes across the entire road network The data is collected by: - permanent stations - located on highways and major roads and they are capturing data from 1990 till now. - short-period traffic count – these are done by automated recorders. They cover a large part of the city but the challenge is that they capture certain period of time (day of data, week of data and etc.) - turning movement count – which are conducted manually – short period, usually for a specific project

Research Question: How do we use the information from all types of stations in order to create volumes across the entire network? We develop an algorithm: • Traffic component: - PECOUNT -1 – that looks at the long-term traffic database; - PEACONT -2 which looks at the medium range traffic database. We have an aggregation algorithm - PRTCS – the short –traffic database where we have an algorithm for pattern recognition. - KCOUNTS - is predicting volumes where we don’t have a station at all - AADT database – Annual Average Daily Traffic for every road for every year. • Emission Component Using the volume (AADT) we can estimate emissions

Traffic Emissions Prediction (TEPs) scheme is also a software application that generate all the information in an automotive way. Using Traffic Prediction Emissions we can generate: - AADT and vehicle kilometers travelled on all roads (2006 -2016) - Emissions of GHG, NOx, PM2.5 on all roads (2006-2016) - Total kilometers travelled and emissions per year for the City of Toronto (2006-2016) This allows city to calculate multi-year GHG emissions inventory

What else can you do with this tool? Having spatially refined traffic and emissions information open doors for the development of exposure surfaces for traffic-related air pollution – for example distribution of ultra-fine particles, black carbon and etc. We can identify better population exposure (using Transportation Tomorrow Survey (TTS) to track people how they move in the city in order to accumulate the 24h exposure) We can highlight these exposures from a health perspective We can identify factors that influence daily exposure while being outside (depending on neighborhood, activities, and trips taken)

Conclusion: We developed a tool that makes use of the extensive traffic data collection program in Toronto to generate emissions estimates at the level of individual roads and for multiple years. This tool enables agencies to maintain an up to date emissions Travel demand models are better suited for scenario and policy analysis

Discussion/Questions: 1. How transferable is this tool among different jurisdictions? - It is transferable if you have the data for that particular municipality traffic volume. 2. Different municipalities use different data: example vehicle owner information and estimation of how much travel per year, or taking national average amounts. Have you compared those types of inventories with the work that you have done? - Yes. The motivation was to come up with robust emission inventory. 3. How different are the GHG emissions between the two models? - Travel demand model cannot capture everything that goes on the road compared to model transportation.

Discussion/Questions: 4. What are the implementation to inform the policy (provincial, municipal) in terms of translation between policy and inventories? - We really try to find the gap between these messages – inform policy starts with having very good idea of what and how are the GHG emissions generated. We have to do policy analysis. But this model does not do policy analysis. This model shows problematic areas. The strength is to show where is the problem, the spatial distribution. And over time you will be able to see patterns and learn from that.

Discussion/Questions: 5. How do you move from home exposure to daily exposure? - We took everyone that is on the TTS data (which is a survey of travel patterns – people report on all the trips; activities they are taking in a day; it is conducted every 5 years; it covers GTHA area). We linked all these activities and intercepted that with the air pollution data. That is how we aggregate for the 24h exposure. 6. Moving from inventory stage to scenarios. How do we see the two playing together? - It is a key question. The inventory can highlight a problem, which is the first part in creating a policy. You need to know the problem (what and where it is) and then to develop policy. 7. Can you take your findings and assess future exposure based on climatic changes and new developments – such as the switched from fossil fuel to EVs? Is that moving into the scenario planning? - Yes, it is. And we are doing that. Looking at exposures and public health as of result of this exposure.