Comité du transport en commun
and Council / et au Conseil
19 August 2009 / le 19 août 2009
Submitted
by/Soumis par: Nancy Schepers, Deputy City Manager
Directrice municipale adjointe,
Infrastructure Services and Community
Sustainability
Services d’infrastructure et
Viabilité des collectivités
Contact
Person/Personne ressource: Alain Mercier, General Manager/Directeur général,
Transit
Services/Services du transport en commun
(613) 842-3636 x 2271, Alain.Mercier@ottawa.ca
SUBJECT:
|
|
|
|
OBJET :
|
STRATÉGIE DE RÉDUCTION DES ÉMISSIONS DES VÉHICULES DU TRANSPORT EN COMMUN |
That
Transit Committee recommend that Council:
1.
Receive the Transit Vehicle Emissions Reduction
Strategy as updated from the 2004 Fleet Emissions Reduction Strategy; and
2.
Approve the updated strategy as outlined in the
report.
Que le Comité du transport en commun recommande
au Conseil :
1.
de recevoir la Stratégie de
réduction des émissions des véhicules du transport en commun à titre de mise à
jour de la Stratégie de réduction des émissions du parc automobile de 2004 et
2.
d’approuver la stratégie mise à jour
telle que décrite dans le rapport.
City Council
approved the Fleet Emissions Reduction Strategy (FERS) March 27, 2002 as the
means to determine the best value options for achieving reduced exhaust
emissions from the City of Ottawa fleet of vehicles. The strategy was structured such that implementation could be
carried out in timed objectives, over a number of years, with progressive
achievements in reducing exhaust emissions.
Council directed that the strategy be reviewed regularly and updated,
based on new research and technological advancements. As well, availability of government funding sources needed to be
reviewed and considered. There was a
further requirement to report back to Council at a minimum of once per term.
This Transit
Vehicle Emission Reduction Strategy (TVERS) is the second update of the 2002
Fleet Emissions Reduction Strategy (FERS).
The FERS reports in 2002 and 2004 applied to both the municipal and
transit fleets.
The strategic
objectives approved in 2004 were the following:
Long-Term (11-20
years)
i. Convert the urban transit bus fleet to
near-zero emission fuel-cell technology.
Mid-Term (4-10
years)
i. Introduce hybrid diesel-electric urban
transit buses in transit service, and
ii. Conduct preparatory work to implement the
long-term strategy.
Short-Term (1-3
years)
i. Monitor the cost of bio-diesel fuel for
possible implementation, if economically feasible,
ii. Participate
in government-led retrofit programs that target emission reduction from older
transit buses, and
iii. Execute the multi-phased implementation plan
for hybrid diesel-electric technology.
In June 2008,
the accountability of transit fleet was aligned with the Transit Services
department. This permits Transit
Services to continue down the course of action as defined by the FERS while
giving latitude to municipal fleet to explore other emission reduction
opportunties.
This update
recommends a practical approach for achieving sustainable emission reductions
specifically for the City’s transit fleet.
The City of
Ottawa is committed to a growth management strategy that is part of the City’s
comprehensive Air Quality and Climate Change Management (AQCCM) Plan. In Ottawa, transportation accounts for 40
per cent of the community's greenhouse gases (GHGs), over 85 per ent of
total nitric oxide (NOx) emissions, 90 per cent of carbon monoxide (CO), 60 per
cent of sulphur dioxide (SO2) and smaller amounts of various carcinogenic
substances.
Air pollution is
closely linked with the burning of fossil fuels. Transit vehicles annually consume over 40 million litres of
transportation fuel and are a significant source of community emissions.
The TVERS is an
important component of the City's overall AQCCM plan. However, to be successful in the short term and sustainable in
the long term, it is equally important that budgetary provisions are
considered.
The TVERS must be planned and implemented to meet the challenges of
cost-effective fleet management and operation.
The overall
objective of the TVERS is to rationalize and recommend a practical affordable
approach for achieving sustainable emission reductions from the transit fleet
and equipment, while meeting the requirements of the City’s AQCMM plan.
The TVERS
includes diesel buses, trains, and non-revenue fleet (both diesel and gasoline
vehicles, and equipment). Over 72 per
cent of emissions from the City’s fleet are generated by diesel bus engines.As
a result, reduction within the transit bus fleet offers the greatest potential
for meeting overall reduction goals for the City.
In 1990, the
size of the bus fleet was 787 vehicles. It has grown by 30 per cent. During
that period, the emission requirements for hydrocarbons and nitric oxides have
decreased by 67 per cent and particulate matter by 98 per cent. Transit
Services has procured 404 new buses since 2004 that reflect these reduced
emission figures and has retired 331 buses with an average age greater than 18
years.
Since 2004, the City has initiated a number of projects and strategies to reduce the emissions of the fleet vehicles.
Transit Services
capitalized on a federal program to retrofit 56 buses (1989 and 1993 vintage)
with diesel oxidation catalyst (DOC) mufflers. The mufflers were supplied by
Environment Canada and the program managed by the Canadian Urban Transit
Association (CUTA) and Transit Services supplied the installation labour.
City Council
approved the procurement of diesel-electric hybrid transit buses after
reviewing a compressed natural gas consortium proposal and the Hybrid
Technology and Feasibility Study conducted by National Research Council of
Canada conducted in 2004-05. Two lead buses were procured in 2007 and delivered
the following year to enter service in November 2008. These buses are being
monitored and evaluated during a one year period by comparing their performance
with two Invero diesel buses on similar route profiles. Subsequent orders for
95 and 80 hybrid-electric transit buses have been placed for 2009 and 2010
deliveries.
In addition,
Fleet Services conducted a number of trials in 2007-08 to reduce fuel
consumption. The trials achieved the
following results:
·
A 5 per cent soy-based bio-diesel (B5)
trial test indicated that on a fleet-wide basis the life cycle greenhouse gases
(GHG) could be reduced by 1,130 kg per year. A conversion to bio‑diesel
is not financially supported by the operating budget at this time.
·
A trial test for number two-grade
ultra low sulphur diesel revealed fuel savings from 0.3 per cent to 4.2
per cent depending on the engine model and driving cycle. The potential saving
is being weighed against measured increases with some critical air
contaminants.
·
A tire pressure monitoring study with
25 buses indicated a 1.21 per cent improvement in fuel economy. Other tire
mangement system technologies are being examined to justify a business case.
City Council
approved the acquisition of three double-decker buses for trial service that
were delivered in November 2008. These buses are being monitored for one year
and their performance will be compared and evaluated to the articulated buses.
The double-decker trial will also provide an opportunity to access other
“green” features such as timed automatic engine shutdown on idle and on-board
tire air pressure monitoring.
A number of
transit authorities have demonstrator fuel-cell buses operating in regular
service and indications are that this technology is becoming as reliable as the
diesel technology. The challenges with these bus models remain their initial
capital cost, reliability of fuel-cell membranes and the supply and
distribution of hydrogen. Continued research and development is continuing to
make this technology commercially viable.
The initiatives
undertaken, along with all of the information gathered, has provided a strong
foundation for establishing emission reduction priorities. This review has established the following
strategic objectives for the 2009 TVERS:
Short-Term (1-4
years)
i. Monitor the cost of bio-diesel fuel for
possible implementation (if economically feasible).
ii. Report annually GHG emission of the transit
bus fleet, including rail.
iii. Complete the multi-phased implementation
plan for hybrid diesel-electric technology.
iv. Plan conversion from No.1 to No.2 diesel
fuel.
v. Prepare garages to dispense urea for buses
with EPA 2010 certified engines.
vi. Complete the tire pressure monitoring and
tracking study.
vii. Complete
the double-decker bus evaluation.
viii. Ensure the
non-revenue fleet is right-sized.
Mid-Term (5-10
years)
i. Monitor fuel-cell technology to formulate
a roadmap.
ii. Monitor options for alternate vehicle power
sources.
iii. Proceed
with expansion of the Rapid Transit Network through a near-zero emission rail
system.
Long-Term (11-20
years)
i. Convert the urban transit bus fleet to
near-zero emission.
Due to the nature of this report consultation is not required.
There are no legal/risk management impediments to the implementation of this report's recommendations.
There are no financial implications for this report. Initiatives that require additional funding will be brought forward to Council under a separate report or included in the annual budget submission to Council.
Document 1 Consultant's
Report - Transit Vehicles Emissions Reduction Strategy
Transit Services will implement the short-term objectives of the strategy. Transit Services will conduct a review and update of the strategy for the next term of Council.
Consultant's Report – Transit
Vehicles Emissions Reduction
Strategy DOCUMENT
1
Prepared By: Richard Gunn PEng
Transit Engineer,
Reviewed By: Jean-Yves Carrier
Program
Manager, Transit Vehicle Projects
Transit
Services Branch
Approved By: Alain
Mercier
General
Manager Transit Services
Group: City
of Ottawa
Date: May 2009
Table of Contents
Content Page
EXECUTIVE
SUMMARY |
iii |
INTRODUCTION |
1 |
BACKGROUND |
1 |
FERS
2009 UPDATE -- 1. Objective |
2 |
-- 2.
Emissions Reduction -- National Commitment and Regulation |
2 |
--
3. Traditional Methods for Emissions
Control and Reduction |
3 |
--
4. Current Status and Recent Developments |
5 |
--
5. 2009
Strategic Objectives |
13 |
|
|
Executive Summary
This Transit Vehicle Emission Reduction Strategy (TVERS) is the second update of the 2002 Fleet Emissions Reduction Strategy (FERS). The FERS reports in 2002 and 2004 applied to both the municipal and transit fleets. On June 9, 2008 the municipal and transit fleets were reassigned in two different departments. This update recommends a practical approach for achieving sustainable emission reductions for the City’s transit fleet.
In 1990 the size of the bus fleet was 787 vehicles. It has grown by 30 percent. Over that time period, the emission requirements for hydrocarbons and nitric oxides have decreased by 67 percent and particulate matter by 98 percent. Transit Services has procured 404 new buses since 2004 that reflect these reduced emission figures and has retired 331 buses with an average age greater than 18 years.
Transit Services capitalized on a federal program to retrofit 56 buses (1989 and 1993 vintage) with diesel oxidation catalyst (DOC) mufflers. The mufflers were supplied by Environment Canada and the program managed by CUTA. OC Transpo supplied the installation labour.
City Council approved the procurement of diesel-electric hybrid transit buses after reviewing a compressed natural gas consortium proposal and the Hybrid Technology and Feasibility Study conducted by National Research Council of Canada conducted in 2004-05. Two pilot buses were procured in 2007 and delivered the next year to enter service in November 2008. These buses will be monitored for one year by comparing their performance with two Invero diesel buses on similar route profiles. Subsequent orders for 95 and 80 hybrid-electric transit buses have been placed for 2009 and 2010 deliveries.
Fleet Services conducted a number of trials in 2007-08 to reduce fuel consumption. The trials achieved the following results:
· A five percent soy-based bio-diesel (B5) trial test indicated that on a fleet wide basis the life cycle greenhouse gases (GHG) could be reduced by 1,130 kg per year with B5 bio-diesel fuel. A conversion to bio-diesel is not financially supported by the operating budget at this time.
· A trial test for number 2-grade ultra low sulphur diesel revealed fuel savings from 0.3 percent to 4.2 percent depending on the engine model and driving cycle. The potential saving is being weighed against measured increases with some critical air contaminants.
· A tire pressure monitoring study with 25 buses indicated a 1.21 percent improvement in fuel economy. Other tire monitoring system technologies are being not examined to justify a business case.
City Council approved the acquisition of three double-decker buses for trial service that were delivered in November 2008. These buses will be monitored for one year and their performance will be compared to the articulated buses. The double-decker trial will also provide an opportunity to access other “green” features such as timed automatic engine shutdown on idle and on-board tire air pressure monitoring.
A number of transit authorities have demonstrator fuel-cell buses operating in regular service and indications are that this technology is becoming as reliable as the diesel technology. The challenges with these bus types remain their initial capital cost, reliability of fuel-cell membranes and the supply and distribution of hydrogen. Continued research and development is continuing to make this technology commercially viable.
a. Short-Term
(1-4 years) –
i. Monitor the
cost of bio-diesel fuel for possible implementation, if economically feasible,
ii. Report
annually GHG emission of the transit bus fleet, including rail,
iii. Complete the multi-phased implementation
plan for hybrid diesel-electric technology,
iv. Plan conversion from No.1 to No.2 diesel
fuel,
v. Prepare garages to dispense urea for buses
with EPA 2010 certified engines,
vi. Complete the tire pressure monitoring and
tracking study,
vii. Complete the double-decker bus evaluation,
and
viii. Ensure
the non-revenue fleet is right-sized.
b. Mid-Term
(5-10 years) –
i.
Monitor fuel-cell technology to assist in
formulating a roadmap,
ii.
Monitor options for alternate vehicle power
sources, and
iii. Proceed with
expansion of the Rapid Transit Network through a near-zero emission LRT system.
c. Long-Term
(11-20 years) –
i. Convert the
urban transit bus fleet to near-zero emission.
INTRODUCTION
The City of Ottawa is
committed to a growth management strategy that is part of the City’s
comprehensive Air Quality and Climate Change Management (AQCCM) Plan[1]. In
Ottawa, transportation accounts for 40 per cent of the community's greenhouse
gases (GHGs), over 85 per cent of total nitric oxide (NOx) emissions, 90 per cent of carbon monoxide
(CO), 60 per cent of sulphur dioxide (SO2) and smaller amounts of
various carcinogenic substances.
Air pollution is closely linked with
the burning of fossil fuels. Transit vehicles, which consume over 40 million
litres of transportation fuel annually, are a significant source of community
emissions. Consequently, the Fleet Emissions Reduction
Strategy (FERS) is an important component of the City overall AQCCM plan. However, with increasingly stringent
budgetary requirements, it is equally important that, in order to be both
successful in the short term and sustainable in the long term, the FERS must be
planned and implemented to meet the challenges of cost-effective fleet
management and operation.
BACKGROUND
In 2002, the City of Ottawa adopted
the original Fleet Emissions Reduction Strategy (FERS) as the means to determine the
best value options for achieving reduced exhaust emissions from the City fleet
of vehicles. This strategy was structured such
that implementation could be carried out in timed-objectives, over a number of
years, with progressive achievements in reducing exhaust emissions. City Council also included
a requirement that the strategy be reviewed regularly to update it based on new
research and technological advancements, and on the availability of government
funding sources. There was a further requirement to report back to City Council
at a minimum of once every term.
The re-organization of Transit
Services in June 2008 redeployed transit fleet accountability from Fleet
Services to Transit. This division is
allowing the municipal fleet to explore other emission reduction opportunities
while Transit may pursue its course as defined by the FERS. The new
strategy developed herein for transit vehicles will be referred as the Transit Vehicle Emission Reduction Strategy
(TVERS).
The current review and update of the TVERS represents the second major
revision to the FERS, the first being in 2004 (Fleet Emissions Reduction Strategy - 2004 Update[2]). City Council directed in late 2008 that
Transit Services conduct an internal staff review for this rendition of the
strategy[3]. The strategic objectives approved in 2004
were the following:
a. Long-Term
(11-20 years) –
i. Convert the
urban transit bus fleet to near-zero emission fuel-cell technology.
b. Mid-Term
(4-10 years) –
i. Introduce hybrid
diesel-electric urban transit buses in transit service, and
ii. Conduct
preparatory work to implement the long-term strategy.
c. Short-Term
(1-3 years) –
i. Monitor the cost
of bio-diesel fuel for possible implementation, if economically feasible,
ii. Participate in
government-led retrofit programs that target emission reduction from older
transit buses, and
iii. Execute the
multi-phased implementation plan for hybrid diesel-electric technology.
TRANSIT VEHICLE EMISSION REDUCTION STRATEGY - 2009 UPDATE
1. Objective
The overall objective of the Transit Vehicle Emission Reduction Strategy
(TVERS) is to rationalize and recommend a practicable approach for achieving
sustainable emissions reduction from the Transit fleet of vehicles and
equipment thereby meeting the requirements of the City’s Air Quality and
Climate Change Management (AQCMM) Plan.
The TVERS encompasses the transit fleet diesel
buses, the trains, and the non-revenue fleet (both diesel and gasoline vehicles
and equipment). Over 72 percent of emissions from the City fleet are generated
by City bus diesel engines. Consequently, reduction within the transit bus
fleet offers the greatest potential for meeting overall reduction goals for the
City.
2. Emissions
Reduction -- National Commitment and Regulation
2.1 Regulated Vehicle Exhaust Emissions
The expected next
phase of the US Environmental Protection Act (EPA) standards, (post-2010) is
targeting major gains in fuel economy, as well as a reduction of the
in-cylinder production of both regulated and unregulated pollutants. While a significant reduction in exhaust
emissions has been achieved to date, it has often been at the expense of fuel
economy.
Current diesel engine development is directed towards marked improvements in combustion efficiency by going well beyond existing combustion technology by initiating combustion simultaneously at multiple sites throughout the cylinder volume, by reducing flame propagation and by making shorter the duration of combustion. As a result, the development of the homogeneous charge compression ignition engine, which combines the advantages of the traditional spark ignition gasoline engine with those of compression ignition diesel engine, has the potential to significantly reduce or eliminate incomplete combustion, while improving the combustion process. The developments in this area could impact the mid-term direction of the TVERS, in its next update.
2.2 Kyoto Protocol
In 1997, at the United Nations
Framework Convention on Climate Change in Kyoto Japan, 160 countries from
around the world, including Canada, committed to reducing greenhouse gas
emissions. This agreement became known as the Kyoto Protocol[4].
It was ratified by Canada in December 2002 and the federal government’s role is
defined by Environment Canada[5]. Ratification commits Canada to reducing its
greenhouse emissions to six (6) percent below 1990 levels by the period 2008 to
2012.
While Canadian EPA regulations
have significantly reduced carcinogenic and some greenhouse gas emissions,
carbon dioxide remains unregulated. To reduce the greenhouse gas,
engine-related CO₂
emissions, improvement needs to be made through fuel economy. Some short-term
methods to accomplish this objective are described in following sections.
2.3 Targeted Exhaust Emissions
The National Highway Traffic Safety
Administration (NHTSA) intends to introduce Corporate Average Fuel Economy
legislation for both passenger cars and light trucks. The vehicle
manufacturers’ combined fleet of all passenger cars and light trucks in 2020
must achieve a minimum 35 miles per gallon. Emphasis is now being placed on
improving the vehicles’ fuel economy. At present NHTSA has not announced
similar fuel economy improvements for heavy-duty engine vehicles.
With the phased in of EPA 2010 emissions for
heavy-duty engines, the US Act is legislating onboard diagnostic (OBD) systems
to monitor and control regulated engine emissions.
The OBD systems will
monitor the pollutants; CO, HC, NOx and PM. Once set threshold values have been
reached, the OBD system will activate warning devices. The system will have the
capability of de-rating the engine performance if the emission issue is not
addressed and steadily gets worse. This
type of technology currently exists on engine with PM trap system such as the
double-decker buses and the last group of 60-ft articulated buses delivered to
Ottawa. The OBD system is to be phased in from 2010 to 2013. The effect of this
legislation is to remove poorly maintained heavy-duty engines off the road and
to control the amount of pollutants being emitted by a heavy-duty engine.
3. Traditional Methods for Emissions
Control and Reduction
3.1
Diesel Engines
3.1.1 2010 EPA Diesel Engine and Infrastructure Requirements
Transit
Services is scheduled to receive EPA 2010 certified engines in 2011 as part its
next bus procurement for high-capacity vehicles, either articulated or
double-decker. These buses will have a diesel engine that uses selective
catalytic reduction technology and urea [(NH2)2CO] to
comply with these regulations. The selective catalytic reduction system is
required to follow the EPA guidelines contained in Docket:
EPA–HQ–OAR–2006–0886. The urea is
sprayed into the engine exhaust gases in the front of a new catalytic chamber.
The urea has to comply with ISO standards that define quality, test method,
handling and refilling interface.
As a new
short-term, these documents will be reviewed to determine the necessary
infrastructure, processing and maintenance change requirements to ensure
operation readiness to receive the new technology.
Other
engine manufacturers have for example chosen to use a combination of advanced
technologies of exhaust gas re-circulation, fuel injection and air intake and
accumulated credits to meet the 2010 EPA emissions requirements. The credits
allow them to be compliant for two years.
Within these two years they expect their technologies to mature
sufficiently to be compliant without the credits.
The
development in selective catalytic reduction and advanced exhaust
re-circulation technologies will be closely monitored in the short-term to
determine which is more suitable for OC Transpo’s operating conditions.
3.2
Vehicle Growth, Retirement and
Replacement of the Transit Bus Fleet
Since 2004, 331 heavy-duty transit
buses have been retired. The average age of the buses was well above eighteen
plus years. At the same time 404 new buses were delivered to OC Transpo and the
fleet grew by 73 buses. Each growth bus eliminates between 40 and 90
single-occupant vehicles from City roadways and correspondently reduces
emissions. By the end of 2009, 70 more buses will have been retired and 95 new
hybrid buses will have arrived at OC Transpo, of which 17 will be growth. Table
A depicts the fleet change since 2004. The average age of the bus fleet is now
7.1 years old.
TABLE A
Year |
Quantity of Buses Retired |
Retired Buses Average Age |
Quantity of new buses |
2004 |
141 |
24 years |
98 |
2005 |
36 |
23.5 years |
36 |
2006 |
69 |
24.5 years |
130 |
2007 |
39 |
20 years |
87 |
2008 |
46 |
18 years |
53 |
2009 |
70 |
18.5 years |
95 |
Table
B indicates the change in EPA emission standards emission reduction on a
grams/brake horsepower (g/bhp-hr) basis between 1990 and 2007.
TABLE B
Year |
HC |
CO |
NOx |
HC+NOx |
PM |
|
g/bhp-hr |
g/bhp-hr |
g/bhp-hr |
g/bhp-hr |
g/bhp-hr |
1990 |
1.3 |
15.5 |
6.0 |
(7.3) |
.60 |
2007 |
* |
15.5 |
* |
2.4 |
.01 |
Net difference |
|
0 |
|
4.9 |
.59 |
% of change |
|
0 |
|
67 |
98 |
* In 2004 combined HC+NOx must not exceed 2.4
g/bhp-hr combined or 2.5 with a limit of .5 for NMHC.
In
1990 OC Transpo’s active diesel bus fleet totaled 787. Total number of active
diesel buses in 2009 is 1020. The fleet has grown by 233 buses, or 30 percent.
This excludes the para-transit buses from 2008. The average age of the bus
fleet in 2009 is 7.2 years. By the end of 2009 OC Transpo will have phased out
401 buses whose emissions met 1990 or earlier EPA emission regulations. In
itself, this represents a substantial reduction of fleet emissions for HC, NOx
and PM. With the procurement of buses compliant to the 2010 EPA standards the
HC and NOx pollutants will be reduced to 0.14 g/bhp-hr and 0.2 g/bhp-hr
respectively. This amounts to an 89 per cent and 97 per cent reduction
respectively from the 1990 levels.
4. Current
Status and Recent Developments
This section begins each sub-section with the status of the approved
2004 FERS objectives, as stated below. Consideration of new
initiatives and other developments – since the 2004 FERS – that are germane to
sustainable emissions reduction from the transit vehicles are then discussed in
light of this update.
a. Short-Term (1-3 years)
–
i. Monitor the cost of bio-diesel fuel for
possible implementation, if economically feasible,
ii. Participate in government-led retrofit
programs that target emission reduction from older transit buses, and
iii. Execute the multi-phased implementation plan
for hybrid diesel-electric technology.
b. Mid-Term (4-10 years) –
i. Introduce hybrid diesel-electric urban
transit buses in transit service, and
ii. Conduct preparatory work to implement the
long-term strategy.
c. Long-Term (11-20 years)
–
i. Convert the urban transit bus fleet to
near-zero emission fuel-cell technology.
4.1 Short-term
Objectives
4.1.1 Bio-diesel Fuel
The objective has been achieved as a feasibility study and will
continue.
Diesel fuel standards for sulfur content changed in 2006 from low (<300
ppm) to ultra-low (<15 ppm) under the US and Canadian EPA. The change was initiated at OC Transpo as
early as September 2004 to support the use of particulate traps on some buses.
The use of ultra-low sulfur diesel decreases smog formation.
In 2007, a successful renewable fuel demonstration was carried out using a 5 per cent soy-based bio-diesel blend (B5), during which time over 2.9 million litres of B5 fuel was consumed by transit buses at two garages. The trial started in the spring and ran to the end of the year, with a corresponding reduction in life cycle GHG emissions of over 300 tonnes. If the entire transit fleet was to operate on a 5 per cent bio-diesel mix, then projections indicated that a reduction in lifecycle GHGs of over 4,900 tonnes per year could be expected, in addition to a reduction in criteria air contaminants of 1,130 kg per year. The type of emissions tests performed has an effect on the amount of NOx produced. Vehicle emission tests conducted with Environment Canada as part of the trial on a standard Ottawa duty cycle indicate a slight reduction in NOx over. The trial was discontinued because of budgetary constraints.
The ultimate goal of the bio-diesel program is to use a cost-effective seasonal blend of B5 (to accommodate the winter months) and B15, resulting in an overall average blend ratio of about 11 per cent, using biomass produced in Canada and derived from waste products (e.g., agricultural / forestry), or from crops produced on land not suitable for food production. This policy is also consistent with the federal government’s outlook and its intent, under the Canadian Environmental Protection Act, to require for on-road diesel, a renewal fuel portion approximately equivalent to 5 per cent by 2012[6].
This program will be reinstated when the one or more of following conditions are met:
· The cost of biomass, or B100, is consistently competitive with the price of diesel fuel;
· The supply of biomass can be produced in sustainable quantity and quality solely from waste products (not from the food chain); or
· Legislation (Environment Canada) imposes use of biomass with diesel fuel.
4.1.2
Government-led
Retrofit Programs
The objective has been completed.
Fifty-six (56) model years 1989 and 1993 transit buses participated in a muffler retrofit initiative launched by Environment Canada[7] in 2004-2006 with the collaboration of CUTA (Canadian Urban Transit Association). This retrofit aimed at reducing emissions from older transit buses by replacing conventional mufflers on Detroit 6V92 series engines with diesel oxidation catalyst (DOC) mufflers. The City had at the time over 150 candidate buses with varying expected life. Buses with the longer life expectancy were selected for the retrofit. This program required the City to absorb the cost of the installations, while CUTA provided the DOC mufflers, funded by Environment Canada. The program was not renewed after 2006 and the City obtained 17 percent of the national allotment.
All 56 buses remain in service in 2009, and the DOC reduced exhaust emissions of particulate matter (PM) by 20%, carbon monoxide (CO) by 40% and hydrocarbons (HC) by 50%. Since most buses with 6V92 engines are retiring within the next two years, and replace by diesel-electric hybrid buses, investment to continue or expand this program without government funding is not recommended.
4.1.3
Diesel-electric
Hybrid Technology Implementation Plan
The (mid-term) objective is in progress and will be continued as a short-term objective.
A phased approach, called the Hybrid Bus Implementation Plan[8], was approved by City Council in September 2003.
The primary objective of Phase 1 - the Hybrid Technology and Feasibility Study, conducted by the National Research Council of Canada in 2004-05, was to assess the feasibility of the program and to select the appropriate hybrid diesel-electric technology that will best meet the requirements for transit service. A consortium representing compressed natural gas (CNG) companies challenged the resulting report[9] to Council in 2005, which staff examined and refuted[10]. After re-examination of the CNG Consortium proposal by an independent 3rd party[11], it was determined that the Consortium business case had errors and omissions and that, through a reconstruction process, it failed to generate the proposed savings. Approval to proceed with diesel-electric technology was provided in June 2007, allowing phase 2 to proceed.
Phase 2 – Hybrid Bus Acquisition, proceeded as per the City purchasing by-law through a competitive best-value bid in 2007-08. Daimler Bus North America was awarded the contract with its Orion VII NG (Next Generation) hybrid bus. Transit Services procured two pilot hybrid buses that were delivered in October 2008 and entered service on November 17, 2008. These 40-foot low floor buses incorporate a diesel-electric series hybrid propulsion system and lithium-ion energy storage technology for the traction drive. The use of these pilot buses will provided better understanding of the technology and will be used to complete phases 3 and 4 of the Hybrid Technology Implementation Plan.
The subsequent orders for 95 and 80 Orion VII-NG hybrid buses, for delivery in 2009 and 2010 respectively, are expected to service the routes where the duty cycle optimizes this technology and therefore maximize fuel efficiency and emission reductions, which are low-speed and frequent stop operations, as reported in the feasibility study[12].
Phase 3 – Infrastructure Preparations and Phase 4 – Performance Analysis, will be conducted simultaneously in 2009 and will culminate with a report to Council. Phase 3 will plan and implement the necessary infrastructure changes that will support the hybrid technology while the objective of Phase 4 is to validate the performance characteristics of the selected hybrid bus design against the requirements specification.
The Phase 4 Performance Analysis has begun with the start of service of the two pilot buses. The fuel efficiency is being monitored and compared with the D40i Invero diesel buses. Vehicle fuel consumption varies from season to season so to determine a yearly fuel usage the data will be gathered over the first year of operation. The maintenance and in service efficiency of the hybrid-electric buses will also be compared. An interim report with three months of data will be released in Q3 2009. The final report will be released in 2010.
Hybrid-electric technology is still
maturing. In 2010, BAE Systems will be mounting both the generator and traction
motor on the back of the diesel engine. Their next major scheduled design
change will have the bus auxiliaries driven electrically. This will allow the
bus operator to turn off the engine and still have all the bus systems
operable. ISE Corporation already has this feature available. ISE also has
produced propulsion systems using a combination of diesel electric-hybrid and
ultra-capacitors. The ultra-capacitors allow for a greater use of brake
regeneration energy. The system can be programmed to be more efficient than
diesel electric-hybrid with batteries. The developments in hybrid-electric
technology will continue to be monitored for application in other Ottawa duty
cycles.
4.1.4 Quantitative Analysis of Vehicle
Emissions - GHGenius
This is a new initiative as a short-term objective.
GHGenius[13] was developed by Natural Resources Canada and
made publicly available in Excel spreadsheet format. The GHGenius model focuses on lifecycle assessment up to
the year 2050, for existing and future fuels including renewable
fuels, and for transportation applications including from light-duty vehicles
to heavy-duty buses and Class 8 trucks. The
propulsion systems include conventional internal combustion engines, battery
and fuel-cell powered motors, as well as hybrid systems such as
diesel/gasoline-electric hybrid. GHGenius focuses on estimating life cycle effects on three impact categories --
greenhouse gases emissions, regulated emissions (criteria air contaminants) and
energy usage.
The use of
GHGenius for assessing both tailpipe and life cycle emissions from the current
Transit Services fleets is under consideration. Since GHGenius is not tailored to OC Transpo’s operational
environment, it will be used as a benchmark to indicate engine emission
reductions.
4.1.5 Diesel Fuel Options for
the Transit Fleet
This
is a new initiative as a short-term objective.
Bus
refueling is completed at night when temperatures are cooler. When combined with a positive lock
fuel-dispensing device, the risk of atmospheric release of hydrocarbon vapour
from is substantially reduced.
Two
fuel-savings related studies have been conducted in response to Transportation
Committee motion 39/17[14]
to deal with the 2008 increase in fuel cost.
The two studies examined fuel type and tire pressure monitoring.
4.1.5.1 Seasonal
Number 2 Grade Ultra Low Sulpur Diesel Fuel (#2 Diesel)
The Ottawa transit fleet has historically used #1 grade diesel fuel. Number #1 diesel is used essentially because it is not susceptible to waxing under cold temperature conditions and it is regarded as a cleaner fuel for intercity use: it produces less particulate matter. Conversely, #2 is a denser fuel, adjusted seasonally by blending in #1 diesel fuel with the #2. Consequently, in Ottawa, the winter #2 grade typically contains the equivalent of approximately 80% of #1 diesel.
Transit
organizations across Canada and Northeast USA use either #1 or #2 diesel. A switch to #2 diesel fuel for the transit
fleet has been considered in order to:
·
reduce purchase cost; i.e., historically
#2 is up to 2 cents per litre cheaper, which is significant for an annual
consumption of about 40 million litres; and
·
reduce fuel consumption due to the
higher energy content of #2 diesel, resulting in both reduced consumption and
less tailpipe emissions.
Modern buses with electronic injection control and exhaust after treatment systems do not require the use of #1 diesel to meet current emissions standards. Given that the average bus age of the transit fleet is 7 years, the use of #2 diesel fuel is an attractive option. However, to ensure that switching to #2 grade fuel is operationally and environmentally acceptable, Fleet Services contracted the National Research Council (NRC) in 2008 to oversee a study of the impact of such a change. The study included the following comparative testing components:
·
Dynamometer and exhaust opacity
testing at a transit facility to evaluate any differences in torque, power,
fuel consumption and visible smoke (particulate matter) emissions.
·
Cold chamber testing to assess
cloud point (waxing), starting and engine run performance, and generally any
other fuel temperature dependencies.
·
Tailpipe testing at Environment Canada
facilities to precisely determine fuel consumption and tailpipe pollutants
(criteria air contaminants)
The tests revealed fuel savings from 0.3 percent to 4.2 percent depending on the bus and drive cycle. Based on an annual usage of 40.8 million litres of #1 diesel fuel per year the City would save between 347,000 litres and 856,000 litres. At $0.825 per litre the dollar savings would be from $286,275 to $706,200 per year.
The trade-off between reduced fuel consumption and cost
saving against increased emissions of certain critical air contaminants are
being carefully weighed by staff before implementation. The dominance of electronically controlled
engines in the bus fleet is favouring the conversion of at least two existing
garages and the new garage.
4.1.5.2 Tire Tracking Study
Tire air pressure and temperature are important parameters that are known
to have significant effect on tire wear and fuel economy. For example, operation
for prolonged periods with under inflated tires can result in heat build up
that degrade tires and significantly reduced fuel economy with a corresponding
increase in GHG emissions, and in extreme cases can lead to catastrophic tire failure.
To better assess these effects on transit buses,
a tire tracking study was initiated by Fleet Services in 2008 using 25 buses
equipped with wireless technology for monitoring and transmitting tire
pressures and temperatures. The objective of the study was to validate the
technology and to define potential cost or emissions savings, as well as assess
how this wireless technology can be adapted into a fleet operation. A consultant was retained for the data
reduction phase of the study and to help formulate conclusions and
recommendations.
The test period was from July 14, 2008 to October 14, 2008. During this
time period these buses showed a 1.21% improvement in fuel economy. Full system
implementation into the OC Transpo SmartBus infrastructure is expected to cost
approximately $2,626,000. The total recurring costs on the current transit
fleet is approximately $162,108 annually. Total annual savings identified was
approximately $1,067,500.
The trial report is being re-examined.
Data collection of this system is quite onerous. Similar systems provide the same information
to the vehicle operator and can achieve comparable results without the data
collection, transfer and management infrastructure. System reliability and accuracy needs to be further demonstrated.
4.1.6 Evaluation of Double-Decker Transit Buses
This is a new initiative as a short-term objective.
A demonstration of various high-capacity buses was demonstrated to
Transit Committee in 2006 when three bus models were displayed including the
New Flyer D60LF (CDN), the Van Hool AG300 (B) and the Alexander-Dennis
Enviro-500 (UK). A survey was conducted at the same time to identify areas of
concerns by attending Councilors and staff on bus design issues. The interest for a double-decker bus was
very high.
Two in-service trials were organized following the demonstration. A
two-week summer operational evaluation was held in July 2006 followed by a
winter performance test and operational winter trial in early 2007. The winter performance test included
standard vehicle dynamic testing on a snow and ice covered track owned by
Transport Canada and cold chamber testing.
In
mid-2007, City Council approved the purchase of three Alexander-Dennis
Enviro-500 double-decker buses for a one-year evaluation in Ottawa (Transit
Fleet Acquisition Strategy[15]).
The main advantages of a double-decker bus, as a high-capacity vehicle,
compared to an articulated bus, are the smaller roadway footprint, the greater
seating capacity, and the potential to serve long-distance commuters. The Enviro-500 carries 52% more seated
passengers, relative to Ottawa’s D60LF articulated buses, which translates into
significantly more passenger cars removed from Ottawa roads – on a per bus
basis – hence more efficient cost and emissions reduction.
A
test evaluation program has been developed to compare the in service and
maintenance performance of the Enviro-500 with 60-foot articulated buses
operating on similar routes. The
double-decker evaluation will also provide an opportunity to assess other “green”
features such as timed automatic engine shutdown on idle and on-board tire air
pressure monitoring. A report to
Council is expected in Q3 2010 for consideration of future expansion of
double-decker bus fleet and operation.
4.1.7
Fleet Right Sizing and Green Vehicle Procurement
This
is a new initiative as a short-term objective.
Transit
Services has been operating a shuttle-like bus service on route 123 for many
years. The reliability of that service
was becoming poor in 2002-03 because of its two aging mini-buses. Under the 2004 Universal Program Review, a
single unit replaced the two buses, which has impacted the reliability of that
service.
In
order to provide reliable service of this type, more that one unit is
required. Transit Services has
undertook analyzing busloads and route profiles to determine if more than route
123 could benefit from right sizing to a smaller bus, in the 30-foot model.
In
2007, a project was launched with the issuance of a request for information to
examine products that could possibly meet Ottawa’s demands. Respondents were invited in April 2008 to
conduct demonstrations in Ottawa, which could include a one-week in-service
trial on route 123, where client and operator comments were gathered. The
EZ-Rider II from Eldorado National and the Easy-On from Glaval/Overland Custom
Coach were tried in June and July 2008 while the Van Hool’s A300K model was
displayed in September 2008 for operator evaluation only, as it was being
delivered to AC Transit in California.
The
non-revenue vehicle replacement program provides a valuable means for greening
the fleet through energy efficient right-sizing initiatives for light-duty
vehicles, as well as the replacement of older heavy-duty vehicles with those
meeting modern standards, including more stringent emission requirements. Significant reductions in all of the
criteria air contaminants, such as particulate matter (PM) and NOx emissions
that contribute extensively to smog formation, can be realized by modernizing
the fleet.
The
development in the various fuel engine technologies will be closely monitored
to assess the best choices for Transit Services.
4.2 Mid-Term Objectives
4.2.1 Preparatory Work for Fuel Cell
Technology
This
objective is in progress and will continue.
There have been federal government fuel cell development demonstration
programs at such transit authorities as:
· Connecticut Transit,
· Alameda-Contra Costa (AC) Transit
· Santa Clara Valley Transportation Authority
· University of Delaware
· University of Texas.
BC Transit is procuring 20 New Flyer/Ballard fuel cell
buses for the 2010 Winter Olympics. On going discussions have been held with
Connecticut Transit, AC Transit and BC Transit concerning their operational
experiences with fuel cells. The discussions revealed that fuel cells have
developed to the same level of dependability as diesel buses. Depending on the
bus’ duty cycle, the fuel cells can be twice as efficient as diesel engines.
However, the drawback at this point in time is the capital and maintenance
costs. The cell membrane material and assembly costs are expensive. Substantial
amount of funds are being directed to developing alternative membrane materials
and assembly methods. Once a break through has been achieved in this area fuel
cells will be more common in all forms of vehicles.
The commercial availability, the distribution and storage
of pure hydrogen (99.9%) required to operate fuel cell remains the greatest
challenge. For example, the 2010
Olympic operation of fuel cell buses will be dependent on a supply chain that
will stretch across the nation from Bécancour, QC to Whislter, BC where refueling will be
made by truck. US transit agencies who use local natural gas reformers as a
source of hydrogen reported at the 2008 APTA annual conference experiencing
contamination of the fuel thereby affecting fuel cell performance, high
maintenance cost of their reforming station and long fueling times. It is
noteworthy to state that operating pressure of natural gas is 3,600 psi while
hydrogen fuel cell is 5,000 psi.
The development of trial programs on fuel cell buses has
been enhanced by the aggressive emissions standards established by the
California Air Resources Board. The carbon footprint of the fuelling system and
necessary safety procedures requires research.
Until such time as the technology demonstrates proven results and
reliable source of hydrogen are found, Transit Services will continue to
monitor results of trial programs and learn more from them which should provide
guidance on the development of a roadmap for zero-emission buses in Ottawa.
Transit staff has been involved in 2008 with BC Transit and
TransLink (Vancouver) agencies with two projects. The first was the development
of a specification for a small transit bus multi-purpose and of green
propulsion technologies including hybrid and fuel cell. The second has been an option for two fuel
cell New Flyer buses has been presented to Transit Services by Ballard Systems,
a Canadian fuel cell manufacturer. The
procurement would piggyback onto the BC Transit order for 2010 delivery. The
proposal is under review and will be subject to the annual Transit Fleet report
in Q3 2009. It offers:
·
Fuelling and storage of the buses
at National Energy Canada’s facilities in Ottawa.
·
Bus maintenance be completed at
OC Transpo’s facility with the hydrogen fuelling system turned off and the bus
operating on the battery power
·
Maintenance on the fuel system be completed at
another facility by Ballard
·
Funding from federal departments is expected to
reduce the capital cost of the buses to be approximately equal to that of a
diesel hybrid-electric bus
4.2.2 Ottawa
Rapid Transit Network
This is a new initiative as a mid-term objective.
In May 2008, City
Council approved a Recommended
Rapid Transit Network[16]
for the City of Ottawa that emphasizes electric Light Rail Transit (LRT)
running through a downtown tunnel and along some of the existing Bus Rapid Transitway, as well as along an
upgraded and extended O-Train rail bed.
Additionally, Council further directed that the transit network be
expanded to include LRT service in other regions of the City, once specific
criteria have been achieved. Bus Rapid
Transit will continue to play an important role in the overall rapid transit
network, as will bus service for rural areas and for main line and local feeder
routes. Although growth and replacement
buses will continue to be required on a yearly basis, subject to the normal
budget approval process, the emphasis on LRT for the mid- and long-term is
considered in the strategic planning for transit vehicle emissions reduction.
The power management
of the LRT project from a green renewable source is key to its successes. Acquiring the right technology that will
deliver minimum, or nil, emissions, when compared to diesel buses, will be
favoured. Introduction of a very-low emission LRT will further advance Ottawa’s
objective toward zero emission technology for transit.
4.2.3 Other
Alternative Power Sources and fuels
This is a new initiative as a mid-term objective.
Batteries store electrical energy via chemical means and their
performance is temperature dependent. The existing battery technology does not
perform as well in a northern climate such as Ottawa as compared to New York
City, Washington D.C. or other cities that infrequently have temperatures below
–10 degrees Celcius. Under colder climate conditions, batteries cannot accept
the same amount of brake regeneration energy used in hybrid technologies. An
option is ultra-capacitors, which store energy electro-statically and do not
operate with the same restrictions as batteries.
Long Beach Transit procured in 2005 a quantity of 47 gasoline
electric-hybrid 40-foot transit buses. In lieu of batteries, the buses were
equipped with ultra-capacitors and braking resistors. The buses were used on
routes with eight stops per mile and average route speeds of 13.8 miles
per hours. Ultra-capacitors worked well with frequent stops per mile and low
average speeds with their high charge and discharge rates provided quick bursts
of energy for departures and acceleration. Ultra-capacitors can withstand
hundreds of thousands of charge/discharge cycles without degrading. They have
an expected life cycle of twelve years; whereas, batteries have an expected
life cycle of three to six years.
The next generation of buses may well not be fuel cell powered due to
their continuing challenges. Buses may be powered by a combination of batteries
and ultra-capacitors.
Hydrogen
internal combustion engines have been used in demonstration fleets in North
America. The state of California and the province of British Columbia are
aggressively promoting hydrogen fueling.
These
technologies are among those that could challenge the City’s long-term goal of
using hydrogen fuel cell. With this in mind inquires will be made into the cost
and availability of non-revenue fleet vehicles and in the short term having
them fuelled and stored at National Energy Canada facilities.
4.3 Long-Term Direction
4.3.1 Conversion to Near-Zero Emission
Technology
This
objective is in progress and will continue.
The long-term component of the 2004 FERS is conversion of the City fleets to near-zero emission propulsion, possibly by using fuel cell technology or any equivalent technology. Until such time as fuel-cell, or other technologies and their fuel source, have attained an acceptable level of commercialization and have proven their reliability in transit service, Transit Services will continue to monitor their developments. Customer service through bus availability and reliability will not be traded-off for unproven and unsustainable technology.
Ford and GM have fleets of
light-duty fuel cell test vehicles in service. The test units are performing
better than expected. Once fuel cell technology becomes commercially viable for
mass production Ford and GM along with other vehicle manufactures will be
offering it in their vehicles. The Green Fleet Policy will drive the use of
these vehicle types for Transit Services.
5. 2009
Strategic Objectives
a. Short-Term
(1-4 years) –
i.
Monitor the cost of bio-diesel fuel for possible
implementation, if economically feasible,
ii.
Report annually GHG emission of the transit bus
fleet, including rail,
iii.
Complete the multi-phased implementation plan
for hybrid diesel-electric technology,
iv.
Plan conversion from No.1 to No.2 diesel fuel,
v.
Prepare garages to dispense urea for buses with
EPA 2010 certified engines,
vi.
Complete the tire pressure monitoring and
tracking study,
vii.
Complete the double-decker bus evaluation, and
viii.
Ensure the non-revenue fleet is right-sized.
b. Mid-Term
(5-10 years) –
i.
Monitor fuel-cell technology to assist in
formulating a roadmap,
ii. Monitor
options for alternate vehicle power sources, and
iii.
Proceed with expansion of the Rapid Transit
Network through a near-zero emission LRT system.
c. Long-Term
(11-20 years) –
i. Convert the
urban transit bus fleet to near-zero emission.
THIS PAGE
LEFT INTENTIONALLY
BLANK
[1] http://ottawa.ca/city_services/planningzoning/2020/air/index_en.shtml
[2] http://ottawa.ca/calendar/ottawa/citycouncil/occ/2004/06-23/trc/ACS2004-TUP-FLT-0001.htm
[3] http://www.ottawa.ca/calendar/ottawa/citycouncil/trc/2008/09-03/07%20-%20ACS2008-CCS-TRC-0017.htm
[4] http://unfccc.int/kyoto_protocol/items/2830.php
[5] http://www.ec.gc.ca/cc/default.asp?lang=En&n=46A22765-1
[6] http://www.ec.gc.ca/CEPARegistry/notices/NoticeText.cfm?intNotice=386&intDocument=2608
[7] http://www.ec.gc.ca/cleanair-airpur/Urban_bus_Retrofit-WS2C562D80-1_En.htm
[8] http://ottawa.ca/calendar/ottawa/citycouncil/occ/2003/09-24/csedc/ACS2003-CRS-FLT-0004.htm
[9] http://ottawa.ca/calendar/ottawa/citycouncil/trc/2005/11-16/ACS2005-PWS-FLT-0001eng.htm
[10] http://ottawa.ca/calendar/ottawa/citycouncil/trc/2005/11-16/ACS2005-PWS-FLT-0004eng.htm
[11] http://ottawa.ca/calendar/ottawa/citycouncil/occ/2007/06-27/tc/ACS2007-PWS-FLT-0006.htm
[12] http://ottawa.ca/calendar/ottawa/citycouncil/trc/2005/11-16/ACS2005-PWS-FLT-0001eng.htm
[13] http://www.ghgenius.ca/
[14] http://ottawa.ca/calendar/ottawa/citycouncil/trc/2008/10-15/ACS2008-PTE-DCM-0006.htm
[15] http://ottawa.ca/calendar/ottawa/citycouncil/occ/2007/06-27/tc/ACS2007-PTE-TRA-0009.htm
[16] http://www.ottawa.ca/residents/public_consult/beyond_2020/tmp/transit_options/index_en.html