This document discusses air pollution from diesel school buses and its health impacts on children. It notes that while school buses are safe, most emit substantial air pollutants like particulate matter that can negatively impact children's health. The document recommends strategies for school bus operators to reduce emissions and children's exposures, including replacing older buses, retrofitting buses with emission control devices, implementing anti-idling practices, and using cleaner fuels. Adopting these measures can meaningfully improve air quality and children's health.
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WeblineGlobal shares ERP statistics and applications of M-ERP based upon our analysis with startups, small and medium enterprises scared to migrate to ERP due to complexities and investment threat.
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WeblineGlobal shares ERP statistics and applications of M-ERP based upon our analysis with startups, small and medium enterprises scared to migrate to ERP due to complexities and investment threat.
First, someone will give an overview of air quality concerns and current statistics. Next, there will be a presentation of propane buses and how they fit with improving air
quality and cutting costs. Next, administrators will talk about how their districts have incorporated language into their RFP and contracts to encourage more environmentally friendly buses for their students.
Sustainable development is defined as development that satisfies the needs of the present without compromising the ability of future generations to satisfy theirs. Sustainable development insists on the need to protect the diversity of genes, species, and all terrestrial and aquatic ecosystems in nature. This is possible in particular to protect the quality of the environment, and by the restoration, development, and maintenance of habitats that are essential to species.
Can diesel help to meet both air quality and climate goals? What about rebound effect?Even in-use emissions regulation is difficult.
Do we have effective solutions?
A look at how automotive emissions legislation and the drive for energy sustainability are impacting the refining industry.
Both recent - and upcoming - legislation on automobile emissions has become the major change agent within this environmental arena. As with all legislation, regulation around emissions levels the playing field for all stakeholders in the automotive industry, effectively ensuring a competitive business climate. All participants must adjust their operations to comply with the latest regulations, leaving no-one at a competitive disadvantage.
Carbon monoxide Content of Exhaust Emissions from Agricultural Tractor Engine...IJAEMSJORNAL
This study aims at contributing to the information buildup required for advocating the need for urgent reduction of environmental pollution by exhaust emissions from fossil fuel powered Engines in Nigeria. It was, concluded from the results obtained from the study that carbon monoxide content of the exhaust emissions of agricultural tractors are approximately forty nine(49) times higher than the recommended maximum level of 0.5 % vol CO (v/v) by the US Environmental Protection Agency (EPA). FIAT 70-666 contributed the largest content of 2.9 % vol of CO (v/v) while MASSEY FERGUSSON MF 375 contributed the least amount of 1.7 % vol of CO(v/v). Only the engine capacity had significant effect on the carbon monoxide content of the exhaust emissions of the agricultural tractors; the model/make selection did not significantly affect the CO content of their exhaust emissions.
First, someone will give an overview of air quality concerns and current statistics. Next, there will be a presentation of propane buses and how they fit with improving air
quality and cutting costs. Next, administrators will talk about how their districts have incorporated language into their RFP and contracts to encourage more environmentally friendly buses for their students.
Sustainable development is defined as development that satisfies the needs of the present without compromising the ability of future generations to satisfy theirs. Sustainable development insists on the need to protect the diversity of genes, species, and all terrestrial and aquatic ecosystems in nature. This is possible in particular to protect the quality of the environment, and by the restoration, development, and maintenance of habitats that are essential to species.
Can diesel help to meet both air quality and climate goals? What about rebound effect?Even in-use emissions regulation is difficult.
Do we have effective solutions?
A look at how automotive emissions legislation and the drive for energy sustainability are impacting the refining industry.
Both recent - and upcoming - legislation on automobile emissions has become the major change agent within this environmental arena. As with all legislation, regulation around emissions levels the playing field for all stakeholders in the automotive industry, effectively ensuring a competitive business climate. All participants must adjust their operations to comply with the latest regulations, leaving no-one at a competitive disadvantage.
Carbon monoxide Content of Exhaust Emissions from Agricultural Tractor Engine...IJAEMSJORNAL
This study aims at contributing to the information buildup required for advocating the need for urgent reduction of environmental pollution by exhaust emissions from fossil fuel powered Engines in Nigeria. It was, concluded from the results obtained from the study that carbon monoxide content of the exhaust emissions of agricultural tractors are approximately forty nine(49) times higher than the recommended maximum level of 0.5 % vol CO (v/v) by the US Environmental Protection Agency (EPA). FIAT 70-666 contributed the largest content of 2.9 % vol of CO (v/v) while MASSEY FERGUSSON MF 375 contributed the least amount of 1.7 % vol of CO(v/v). Only the engine capacity had significant effect on the carbon monoxide content of the exhaust emissions of the agricultural tractors; the model/make selection did not significantly affect the CO content of their exhaust emissions.
1. 0
200
400
600
800
Figure1: Emissions per Vehicle Kilometre Travelled
PM2.5, Different Vehicle Types,
Ontario,2005 Gasoline- Car
Gasoline- Truck
Diesel -Small Truck
Diesel -LargeTruck
Diesel -TransitBus
Diesel - School Bus
Healthy School
Buses for School Bus
Operators
School Buses & Air Pollution
School Buses are very safe vehicles. However, most are heavy-duty diesel vehicles that can emit
substantial quantities of diesel-related air pollutants such as fine particulate matter (PM2.5), nitrogen
oxides (NOx), and diesel particulate matter (DPM) as they travel to and from our children’s schools.
They can also be self-polluting vehicles that expose
children on-board to elevated levels of PM2.5 and
DPM. Exposure studies have found that emissions
from school bus tailpipes and engine compartments
can contribute substantially to levels of air
pollutants on-board school buses. Levels of air
pollution on-board are also influenced by local air
quality, the density of traffic on the roads travelled,
wind direction, the position of windows (i.e. open
or closed), and idling and queuing patterns.
While children may spend only a few hours per day on school buses, the elevated levels of air pollution
that can be encountered on-board school buses can add considerably to their daily and annual
exposures to PM2.5 and DPM. This is a concern because children in many Ontario communities are
already exposed to levels of air pollution that are harmful to their health. The Ontario Medical
Association estimates that air pollution contributes to approximately 1,829 premature deaths, 16,907
hospital admissions, and 59,696 emergency room visits in Ontario each year.
PM2.5 and DPM have been clearly associated with a broad spectrum of acute and chronic impacts.
They have been found to:
Reduce lung function
Aggravate asthma, leading to more frequent and more severe asthma attacks
Increase the number of respiratory infections and school and work day absences
Aggravate and induce allergies
Increase, emergency room visits, hospital admissions, and premature deaths
Contribute to chronic heart and lung diseases such as lung cancer and asthma
2. Children are Sensitive to Air Pollution
With approximately 800,000 Ontario children being
transported on school buses each year, school bus
exposures represent a substantial public health concern.
The respiratory systems of children are sensitive to air
pollution. Children with pre-existing respiratory conditions
such as asthma are particularly vulnerable. Childhood
exposures also influence health in later life. A small shift in
the average lung function of a group of children today can
translate into a substantial increase in the number of adults
who are vulnerable to chronic respiratory diseases such as
lung cancer later in life.
Reducing Childhood Exposures
Exposures studies have found that exposures on-board
school buses can be significantly reduced, even under idling
conditions, by retrofitting school bus tailpipes with emission
control devices such as Diesel Particulate Filters (DPFs), and school bus engines with Closed Crankcase
Ventilation devices (CCVs). These studies also suggest that on-board exposures can be reduced by
keeping doors and windows closed when buses are idling, avoiding idling when buses are waiting in
front of schools, and avoiding caravanning on roadways.
Diesel-Related Air Pollutants
Diesel exhaust is composed of hundreds of different air pollutants. For the purpose of engine
emission standards, these air pollutants have been broken into four groups:
Carbon Monoxide (CO) is a gas that can be toxic to humans in high concentrations.
Nitrogen Oxides (NOx) is a small group of nitrogen-based air pollutants. Nitrogen dioxide (NO2)
can be harmful to the lungs in a direct way. All of the NOx can react with other compounds in the
air to create ground-level ozone and/or PM2.5. These two air pollutants are harmful to health
and trigger most, if not all, of the smog advisories issued in Ontario.
Particulate Matter (PM) is the term for air pollutants that are present in liquid or solid form. A
significant portion of diesel exhaust is present as particulate matter (PM). Most of these particles
are less than 2.5 microns in size (called PM2.5), while a substantial portion are less than 0.1
microns in size (called ultra-fine particles or UFP). Because of their small size, PM2.5 and UFP can
penetrate deep into the lungs, enter the blood stream, and travel throughout the body.
Hydrocarbons (HC) is the term used for a broad group of chemical compounds that includes a
number of the toxic contaminants, such as benzene, that are found in diesel exhaust. Many of
the hydrocarbons in diesel exhaust adhere to the PM2.5 and/or the UFP and are transported into
the lungs and throughout the body on these particles.
3. Newer Buses are Healthier Buses
As can be seen by Table 1, emissions from school buses have
declined significantly over the last 20 years as new fuel and engine
emission standards have been developed and rolled out by the
Government of Canada. Buses built to:
1994-2003 standards emit 2.5 times less PM than 1993 buses
2004-2006 standards emit 10 times less HC than 2003 buses
2007-2009 standards emit 10 times less PM than 2006 buses
2010 emission standards emit 6 times less NOx than 2009
buses.
With buses built to 2007 emission standards, it is expected that
levels of air pollutants on-board will approach levels in ambient air.
These buses, which will be outfitted with DPFs and CCVs, will not be
self-polluting. This is great news for children’s health and for local
air quality. However, for older school buses, concerns remain for on-board exposures and local air
quality.
Reducing Emissions & Exposures
School bus operators can adopt a number of practices to reduce emissions and exposures associated
with pre-2007 school buses. They can:
1. Replace Older Buses: The Model Contract Template developed by stakeholders in Ontario
recommends a maximum age limit of 12 years and an average fleet age of 7 years for full-size school
buses. Pre-1994 school buses should not be used at all and pre-1998 school buses should be
retired, used for emergency purposes only, or retrofitted with emission control devices.
2. Assign Routes with an Awareness for Emissions: Buses should be assigned to routes with an
awareness for bus emissions. Buses that do multiple routes in heavily populated areas should be
assigned to school buses with post-2006 model year engines wherever possible to reduce air levels
along heavily travelled roads and exposures on-board. Newer buses should also be considered for
longer routes in which children spend longer periods of time on-board.
3. Implement Driver Training: Drivers should be trained using Natural Resources Canada’s
SmartDriver Program available from FleetSmart at www.fleetsmart.gc.ca. It covers information
about: the health impacts associated with diesel exhaust; the impact of unnecessary idling in school
yards and residential neighbourhoods; best operating practices (e.g. to avoid starting the bus until
children are on-board and doors are closed); and driving practices that reduce fuel consumption and
emissions.
4. Retrofit with Auxillary Heaters: In areas where idling is associated with defrosting windows or
heating cabins, operators should consider installing auxillary heaters that heat engines and/or
Table 1: Emission for School
Buses by Model Year in
Canada
Model
Years
Emissions
(g/brake horse
power hour)
PM HC NOx
< 1991 0.60 1.3 6
1991-93 0.25 1.3 5
1994-03 0.10 1.3 4
2004-06 0.10 0.14 2.25
2007-09 0.01 0.14 1.2
2010 0.01 0.14 0.2
4. cabins without idling. These devices, which
cost about $400 to $1,500, can reduce idling
and emissions, while saving fuel and money.
5. Retrofitting with Closed Crankcase
Ventilation Devices (CCVs): Operators
should consider retrofitting all pre-2007
school buses with CCVs. These devices,
which cost about $200 to $1,000, can
substantially reduce air levels of PM2.5 on-
board school buses while also reducing
tailpipe emissions. With proper installation
and a filter change once or twice a year, these devices can substantially reduce childhood exposure
to air pollutants on-board school buses. For optimal operation, installation by the vendor should be
considered.
6. Retrofit with Diesel Oxidation Catalysts (DOCs): Operators should consider retrofitting pre-2005
buses that have > 2 years of remaining service life with DOCs. At a cost of about $1,100 to $1,400
per bus installed, DOCs can reduce emissions of PM and HC by 40% and 75% respectively. DOCs are
easy to install, require no maintenance, do not affect fuel economy, and present no operational
problems. These retrofits are particularly important for children who live in communities that
experience elevated levels of PM2.5.
7. Retrofit with Flow Through Filters (FTFs): Operators should consider retrofitting pre-2005 school
buses that have > 5 years of service life remaining with FTFs. At a cost of $5,700 per bus installed,
FTFs can reduce emissions of PM by more than 50% . These devices are sensitive to the
temperature of the engine so they should only be installed on buses that have been shown, with
data logging, to have the proper duty-cycle. Unlike DPFs, FTFs will not adversely affect the
operation of the bus if the duty-cycle and temperature are not well matched. These devices require
only a few hours for installation. They do not affect fuel economy. They have no filters to change or
clean.
8. Biodiesel: In areas that have easy access to biodiesel, operators should consider fuelling buses with
a 5 to 20% biodiesel blend (B5 to B20). Biodiesel can produce modest reductions in air pollutants
and greenhouse gases. It is a clean fuel that can improve performance on Drive Clean opacity tests.
School bus operators in Ontario have had no operational problems when using biodiesel from April
to November. Unfortunately, fuel costs continue to be volatile; ranging from $0.01 per litre less
than conventional diesel to $0.07 per litre more.
For more information see: http://www.cleanairpartnership.org/schoolbus