GUIDANCE DOCUMENT ON
AIR ZONE MANAGEMENT
PN 1593
ISBN 978-1-77202-050-2 PDF
© Canadian Council of Ministers of the Environment, 2019
TABLE OF CONTENTS
GLOSSARY ................................................................................................................ i
ACRONYMS .............................................................................................................. ii
1.0 INTRODUCTION ................................................................................................... 1
2.0 AIR QUALITY MANAGEMENT SYSTEM ............................................................ 1
2.1 Continuous Improvement and Keeping Clean Areas Clean .................................... 2
3.0 CANADIAN AMBIENT AIR QUALITY STANDARDS ......................................... 2
3.1 Implementation of the CAAQS ............................................................................. 4
4.0 AIR ZONE MANAGEMENT FRAMEWORK ......................................................... 4
5.0 ASSIGNING THE MANAGEMENT LEVEL TO AIR ZONES ............................... 6
5.1 For Pollutants with a Single CAAQS .................................................................... 6
5.2 For Pollutants with Multiple CAAQS .................................................................... 7
6.0 GUIDANCE ON ACTIONS WITH EACH MANAGEMENT LEVEL ..................... 8
6.1 The Role of Governments ..................................................................................... 9
7.0 EFFECTIVE MANAGEMENT LEVEL ................................................................. 13
7.1 Addressing Management Perspective .................................................................. 13
7.2 Communicating Change in Management Levels .................................................. 13
8.0 COMMUNICATION AND REPORTING .............................................................. 14
REFERENCES .............................................................................................................. 15
APPENDIX 1 THE CANADIAN AMBIENT AIR QUALITY STANDARDS ........ 16
APPENDIX 2 THE MANAGEMENT LEVELS ..................................................... 17
TABLES
Table 5-1: Assigning the management level for pollutants with a single CAAQS ............ 6
Table 5-2: Example for assigning the ozone management level to air zones ..................... 7
Table 5-3: A NO
2
example for assigning the management level for pollutants with multiple
CAAQS ........................................................................................................................... 8
Table 6-1: Suggested actions under the air zone management framework ...................... 10
FIGURES
Figure 4-1: The Air Zone Management Framework .......................................................... 5
TEXT BOXES
Text Box 1: Example for the calculation of the SO
2
1-hour CAAQS metric value ........... 3
i
GLOSSARY
Air Quality
Management System
(AQMS)
A comprehensive approach for protecting and improving air
quality in Canada.
AQMS is built on a foundation of
intergovernmental collaboration and the engagement of
stakeholders and interested parties
with an emphasis on
transparency and accountability to the public.
Air zone
A finite geographic area used to manage local air quality by
the province or territory in which it is located.
Airshed
A broad geographic area that encompasses a number of air
zones and may cross provincial, territorial, and international
boundaries.
Air zone management
framework (AZMF)
A framework to manage air quality in air zones. It includes
four colour-
coded management levels which are associated
with a suite of monitoring, reporting and management
actions that become progressively more
rigorous as air
pollutant concentrations approach or exceed the CAAQS.
Canadian Ambient Air
Quality Standards
(CAAQS)
Health and environmental-based air quality objectives to
further protect human health and the environment and to
provide the drivers for
air quality improvement across the
country.
CAAQS metric value
The measured concentrations of an air pollutant calculated in
the statistical form of the CAAQS.
CAAQS reporting
station
An air quality monitoring station designated to report on the
achi
evement status of the CAAQS by the province or
territory in which it is located. All CAAQS reporting stations
must meet or exceed the quality assurance and quality control
procedures of the National Air Pollution Surveillance
(NAPS) program.
Continuous
improvement (CI)
Remedial and preventative actions to reduce emissions from
anthropogenic sources toward the long-
term goal of reducing
overall ambient concentrations of pollutants.
Keeping clean areas
clean (KCAC)
Preventative measures intended to avoid or minimize
increases in overall ambient concentrations of pollutants in
air zones in the green management level.
ii
ACRONYMS
AQMS
Air Quality Management System
AZMF
air zone management framework
BLIERs
base-level industrial emissions requirements
CAAQS
Canadian Ambient Air Quality Standards
CCME
Canadian Council of Ministers of the Environment
CEPA 1999
Canadian Environmental Protection Act, 1999
CI/KCAC
Continuous improvement/keeping clean areas clean
EE
exceptional events
GDAD
guidance documents on achievement determination (for each CAAQS)
GDTFEE
Guidance Document on Transboundary Flows and Exceptional Events for
Air Zone Management, 2019
NAPS
National Air Pollution Surveillance
PM
2.5
airborne particulate matter less than or equal to 2.5 micrometers in
aerodynamic diameter, also called fine particulate matter
ppb
parts per billion (by volume)
QA/QC
quality assurance/quality control
TF
transboundary flows
µg/m³
micrograms per cubic metre
1
1.0 INTRODUCTION
Air quality impacts all Canadians and affects many aspects of our lives and our society,
including human health, the natural environment, buildings and infrastructure, crop
production, and the economy. Federal, provincial and territorial governments share
responsibility for air quality management. Under the Canadian Council of Ministers of the
Environment (CCME), federal, provincial, and territorial governments work collaboratively
to improve air quality by implementing the Air Quality Management System (AQMS)
1
.
This document supersedes the 2012 Guidance Document on Air Zone Management.
Under AQMS, each province and territory is responsible for delineating its territory into one
or more air zones. Air zones provide a defined area for stakeholders, other interested parties
and governments to work together to improve local air quality and maintain air pollutant
concentrations below the Canadian Ambient Air Quality Standards (CAAQS).
This guidance document outlines a structured approach for federal, provincial and territorial
governments in managing air quality in air zones under AQMS. The objectives of this
document are to:
provide an understanding of the air zone management framework (AZMF)
clarify the roles of government regarding air zone management
provide guidance for assigning management levels to air zones and the related
monitoring, reporting and management actions
formalize the principle that CAAQS are not “pollute-up-to levels” and encourage
governments to take action to improve air quality, considering that some pollutants can
affect human health even at concentrations below the standards
encourage actions that prevent deterioration in air quality, promote continuous
improvement (CI), and encourage keeping clean areas clean (KCAC) in air zones with
pollutant levels well below the CAAQS.
More information on AQMS and guidance on its implementation is available on ccme.ca.
2.0 AIR QUALITY MANAGEMENT SYSTEM
AQMS provides a comprehensive approach for collaborative actions to improve air quality
across Canada to further protect the health of Canadians and the environment. Key elements
of AQMS include the following:
1. Air zones geographical areas that are used to manage local air quality within the
provinces and territories in which they are located.
1
Although Québec supports the general objectives of AQMS, it will not implement the System since it includes federal
industrial emission requirements that duplicate Québec's Regulation. However, Québec is collaborating with jurisdictions on
developing other elements of the system, notably air zones and airsheds.
2
2. Airsheds broad geographic areas that encompass a number of air zones and may cross
provincial, territorial, and international boundaries. They provide a framework for
interjurisdictional collaboration to address transboundary air quality issues.
3. CAAQS health and environmental-based air quality objectives to further protect
human health and the environment and to provide the drivers for air quality
improvement across the country.
4. AZMF a framework to manage air quality in air zones.
5. Base-level industrial emissions requirements (BLIERs) emission requirements that
are intended to apply to major industrial sectors or equipment types to ensure that
significant industrial sources achieve a good base-level of performance.
6. Mobile sources work that builds on the existing range of federal, provincial and
territorial initiatives aimed at reducing emissions from mobile sources.
2.1 Continuous Improvement and Keeping Clean Areas Clean
Several principles underpin AQMS including CI and KCAC.
CI refers to remedial and preventative actions to reduce emissions from anthropogenic
sources, toward the long-term goal of reducing overall ambient concentrations of pollutants.
KCAC refers to preventative measures that are intended to avoid or minimize increases in
overall ambient concentrations of pollutants in air zones that are assigned a green management
level.
The guiding principles of CI/KCAC are intended to ensure that air quality does not deteriorate
but is maintained or improved to the extent practicable. Maintaining or improving air quality
minimizes risk to human health and the environment for the benefit of future generations. The
CI/KCAC principles are inherently incorporated in the AZMF.
3.0 CANADIAN AMBIENT AIR QUALITY STANDARDS
All CAAQS consist of three inter-related elements:
1. an averaging time
2. a concentration “standard” (or “numerical value”) associated with the averaging time
3. the statistical form for the standard.
The CAAQS as of the date of publication of this document are listed in Appendix 1.
The averaging time refers to the averaging period over which the corresponding standard
applies. The statistical form describes the calculation method for the specific concentration
which must be used for comparison to the standard to determine if the concentrations
measured at a monitoring station exceeded the standard. For example, the 1-hour SO
2
standard
of 70 ppb (for 2020) means that the standard applies to 1-hour average SO
2
concentrations
and the statistical form of the standard means that the concentration to use to determine if 70
3
ppb was exceeded at a monitoring station is the 3-year average of the annual 99
th
percentile
of the daily-maximum 1-hour average concentrations measured at the station.
To simplify terminology, the concentrations measured at a monitoring station calculated in
the statistical form of a standard are referred to as “CAAQS metric values” or simply “metric
values.” A CAAQS is achieved at a monitoring station if the corresponding metric value is
less than or equal to the standard, otherwise it is exceeded. To ensure that consistent
procedures are used to calculate metric values, CCME publishes GDADs for each of the
pollutants that have CAAQS. These documents will be available on the CCME web site as
they are developed. Metric values are also used to determine the management level for air
zones; this is discussed in sections 4 and 5 of this document.
Text Box 1 provides an example for the calculation of metric values for the 1-hour SO
2
CAAQS. The 3-year period for this example is 2018-20 and this implies that it is the 2020
standard of 70 ppb which applies. The 99
th
percentile of the measured daily-maximum 1-hour
average SO
2
concentrations were first calculated for each station and for each year in the 3-
year period 2018-20 based on the procedures specified in the GDAD for SO
2
. The 3-year
average of the annual 99
th
percentiles were then calculated and rounded as specified in the
GDAD, and these rounded averages are the 1-hour CAAQS metric values which are used for
comparison to the standard of 70 ppb. For the 3-year period 2018-20, the SO
2
1-hour CAAQS
for 2020 was achieved at Station A (since the metric value of 44 ppb is less than the standard
of 70 ppb) and exceeded at Station B.
Text Box 1: Example for the calculation of the SO
2
1-hour CAAQS metric value
For most pollutants CAAQS were established for more than one averaging time, as shown in
Appendix 1, because the effects of some pollutants on health and environment can occur over
various exposure times and at various concentrations. For example, SO
2
has both a 1-hour
CAAQS and an annual CAAQS.
Federal, provincial and territorial governments work together to develop CAAQS through a
consensus-based process with industry stakeholders, non-governmental health and
environmental organizations, and Indigenous organizations. CAAQS are designed to become
Annual 99
th
percentile of the SO
2
Dmax 1-hour
2018 2019 2020
Station A 39.4 ppb 55.6 ppb 38.0 ppb
Station B 92.7 ppb 85.6 ppb 70.5 ppb
3-year average of the annual 99
th
percentile
1-hour SO
2
CAAQS metric
value for 2018-2020
Station A (39.4+55.6+38.0)÷3 =133÷3 = 44.333 ppb 44 ppb
Station B (92.7+85.6+70.5)÷3 =248.8÷3=82.933 ppb 83 ppb
4
increasingly more stringent over time and periodically reviewed to ensure continuous
improvement to further protect the health of Canadians and the environment. Once endorsed
by CCME, the federal government establishes the CAAQS as environmental quality objectives
under sections 54 and 55 of the Canadian Environmental Protection Act, 1999.
3.1 Implementation of the CAAQS
AQMS recognizes jurisdictional flexibility as a key principle that enables jurisdictions to
implement the CAAQS in a manner that is consistent with their specific management practices
and circumstances. Jurisdictions may consider a number of principles and guidelines as they
implement the CAAQS such as
2
:
CAAQS are intended to drive continuous improvement in air quality and should not
function as “pollute-up-to” limits.
While CAAQS are established to further protect health and the environment, measures
mandated to achieve the CAAQS and associated management levels should take into
account technical achievability, practicality, and implementation costs.
CAAQS are intended to be used in air zones as standards for ambient air quality
management, consistent with the information presented in this guidance document as
well as other CCME guidance, including the AQMS Roles and Responsibilities
document, GDADs for each CAAQS and the GDTFEE.
CAAQS were not developed as facility level regulatory standards. Rather, they are used
by provinces and territories to guide air zone management actions intended to reduce
ambient concentrations below the CAAQS and prevent CAAQS exceedances.
Management actions should consider all important sources of air pollution emissions
in an air zone. In the context of management actions, provinces and territories have
primary regulatory authority governing local aspects of environmental management,
including policy frameworks for land-use and resource management, as well as
establishing environmental regulations and standards, and issuing permits and
authorizations.
Provinces and territories may consult with different stakeholders or interested parties to guide
the prioritization and implementation of air zone management actions that are informed by
the AZMF discussed in section 4.
4.0 AIR ZONE MANAGEMENT FRAMEWORK
Under AQMS, each province and territory is responsible for delineating air zones in its
jurisdiction. Air zones are geographic areas that may be delineated by considering
meteorology, wind patterns, topography, level of industrial activity, population density, and
other factors that may contribute to similar air quality characteristics and trends in the area.
2
Although Québec supports the general objectives of AQMS, it did not implement the System since it includes federal
industrial emission requirements that duplicate Québec's Regulation. However, Québec is collaborating with jurisdictions on
developing other elements of the system, notably air zones and airsheds.
5
AQMS includes the AZMF which provides guidance to jurisdictions on the level of
monitoring, reporting and management actions to implement in air zones depending on the
level of prevailing concentrations of air pollutants. The AZMF includes four air quality
management categories, or levels, denoted by the colours green, yellow, orange and red. Each
of these management levels is associated with a corresponding range of concentrations of air
pollutants which were established during the CAAQS development process. The management
levels that have been developed as of the date of publication of this guidance are presented in
Appendix 2. Prevailing air quality in the red management level corresponds to exceedances
of standards, while prevailing air quality in the green management level corresponds to clean
air quality.
The structure of the AZMF is outlined in Figure 4-1. Key objectives of the AZMF are KCAC,
support CI and prevent the CAAQS from being exceeded. By its very nature, the AZMF
stipulates that the CAAQS are not pollute-up-to levels and that proactive actions be taken to
prevent CAAQS exceedances. Accordingly, under the AZMF actions become progressively
more rigorous as air quality deteriorates from the green to the red management level. The
AZMF applies to all air pollutants for which CAAQS have been established. Detailed
information on the guidance for the suite of monitoring, reporting and management actions
under each management level is provided in section 6.
Figure 4-1: The Air Zone Management Framework
Green Management Level
The lowest level of air quality management
Objective: To maintain good air quality through
Proactive Air Management Measures to Keep Clean
Areas Clean
Orange Management Level
The second highest level of air quality management
Objective: To improve air quality through Active Air
Management and Prevent exceedance of the CAAQS
Red Management Level
The highest level of air quality management
Objective: To reduce pollutant levels below the
CAAQS through Advanced Air Management Actions
Yellow Management Level
The second lowest level of air quality management
Objective: To improve air quality using Early and
Ongoing Actions for Continuous Improvement
Actions
become
progressively
more
rigorous as
air quality
deteriorates
from Green
to Red
6
5.0 ASSIGNING THE MANAGEMENT LEVEL TO AIR ZONES
As mentioned in section 4, under AZMF provinces and territories assign management levels
to their air zones for each of the pollutants with CAAQS. In the simplest case, assigning the
management level to an air zone essentially involves determining which management level
the highest CAAQS metric values fall into, and then assigning to the air zone that management
level. The next two sections provide detailed procedures for assigning management levels. In
assigning management levels, jurisdictions have the options of considering the influence of
transboundary flows (TF) and exceptional events (EE). Information on the consideration for
TF-EE influences can be found in the GDTFEE.
5.1 For Pollutants with a Single CAAQS
Pollutants with a single CAAQS are pollutants for which CAAQS have been established for a
single averaging time. For example, ozone CAAQS have been established only for an 8-hour
averaging time (as of the date of publication of this guidance). The main steps for assigning
managements level to air zones for CAAQS with a single averaging time are provided in Table
5-1. Specifically note that management levels are to be assigned based on the highest metric
value in the air zone.
Table 5-1: Assigning the management level for pollutants with a single CAAQS
Action
Step 1
Calculate the actual CAAQS metric value
3
for each reporting station in the air
zone.
Step 2
Optional consider influences of TF-EE and calculate the (TF-EE) adjusted metric
values
4
as applicable.
Step 3
Select the highest metric value in the air zone including both the actual metric
values for stations not influenced by TF-EE, and the adjusted metric values for
stations influenced by TF-EE.
Step 4
Determine in which management level the highest metric value falls by comparing
the highest metric value to the management levels provided in Appendix 2.
Step 5 Assign to the air zone the colour-coded management level determined in Step 4
Table 5-2 provides an ozone example for assigning management levels to air zones using the
steps in Table 5-1. The ozone management levels are presented in Table A2-1 in Appendix 2.
The 3-year period for this example is 2019-21, meaning that it is the 2020 ozone management
levels that apply.
3
Actual CAAQS metric values are those calculated based on all measured concentrations.
4
Adjusted CAAQS metric values are those calculated after the removal of concentrations found to be influenced by TF-EE.
7
Table 5-2: Example for assigning the ozone management level to air zones
Air Zone
CAAQS
reporting
station
Actual
metric
value
(ppb)
Adjusted metric
value after
consideration of
TF-EE
(ppb)
Highest
metric value
in air zone
(ppb)
Air zone
management
level
A 1 61 Not applicable 61 Orange
B
1 75
63
63 Red 2 58 51
3 54 Not applicable
In this example, Air Zone A has only one CAAQS reporting station and the actual metric
value (before consideration of TF-EE) is 61 ppb. Analyses indicated that this station was not
influenced by TF-EE, and this implies that the actual metric value is used to determine the
ozone management level. The metric value of 61 ppb falls in the orange level (Table A2-1)
and therefore Air Zone A is assigned the orange management level.
Air zone B has three reporting stations. The actual metric values are 75, 58 and 54 ppb
respectively. Analyses indicated that the first and second stations were influenced by EE while
Station 3 was not influenced by TF-EE. Consideration of EE leads to adjusted metric values
of 63 ppb for Station 1 and 51 ppb for Station 2. With these adjusted metric values, and the
actual metric value for station 3, the highest metric value is now 63 ppb and this value falls
in the red level. Air Zone B is therefore assigned the red management level for ozone.
5.2 For Pollutants with Multiple CAAQS
Pollutants with multiple CAAQS are pollutants for which CAAQS have been established for
more than one averaging time. For example, nitrogen dioxide (NO
2
) CAAQS have been
established for a 1-hour and annual averaging times. For these pollutants, only a single
management level will be assigned to the air zone, corresponding to the highest of the
management level associated with each averaging time.
The steps for assigning the management level to air zones for pollutants with multiple
averaging times essentially involves first determining a management level associated with
each averaging time based on steps 1-4 in Table 5-1, and then assigning to the air zone the
highest of these management levels.
Table 5-3 provides a NO
2
example for assigning the management level for pollutants with
multiple CAAQS. For this example, a management level associated with each averaging time
8
was first determined by applying steps 1-4 in Table 5-1. The air zone was next assigned the
higher of the 1-hour and annual management levels.
Table 5-3: A NO
2
example for assigning the management level for pollutants with
multiple CAAQS
Air Zone
1-hour CAAQS
management
level
Annual CAAQS
management
level
NO
2
management level assigned
to air zone
A Green Yellow Yellow
B
Red
5
Orange Red
C Orange Green Orange
6.0 GUIDANCE ON ACTIONS WITH EACH MANAGEMENT LEVEL
Table 6-1 at the end of this section provides guidance for the suite of monitoring, reporting
and management actions that are associated with each management level. Jurisdictions can
help improve air quality by developing and implementing an air quality management plan for
a given pollutant based on the assigned management level. These plans:
should consider the potential for co-benefits of multiple pollutant reduction programs
should consider interactions between air pollutants to determine where a decrease in
one air pollutant may result in increased concentrations of another air pollutant
may engage a broad range of participants, communities, health and environmental
organizations and Indigenous organizations to ensure that all participants are
represented and have the opportunity to contribute to improving air quality.
Jurisdictions should also consider implementing actions for continuous improvement of air
quality regardless of the management level, because some air pollutants (e.g. PM
2.5
, ozone,
NO
2
) can have negative impact on human health even at concentrations below their standards.
The suggested actions in Table 6-1 relate to medium or long-term measures to improve air
quality. During poor air quality episodes where meteorological conditions contribute to
producing elevated concentrations of air pollutants
6
, jurisdictions may choose to issue air
quality advisories and could request immediate actions by local community members to
5
It should be noted that the highest management level that can be assigned is red. This means that for a given pollutant
with CAAQS for multiple averaging times, once it is assessed that a metric value is in the red level for a given averaging
time, the air zone will necessarily be assigned the red management level for that pollutant.
6
Real-time and forecasted health risk associated with air pollution is available for many communities across Canada through
the web-based Air Quality Health Index (AQHI) at:
https://www.canada.ca/en/environment-climate-change/services/air-quality-health-index.html.
9
reduce the contribution of air pollutants. Some jurisdictions have the authority to issue
mandatory emission curtailment orders during air pollution episodes
7
.
6.1 The Role of Governments
Air quality management is a responsibility shared by federal, provincial and territorial
governments
8
. These governments have agreed to work collaboratively to implement AQMS,
recognizing that
9
:
good air quality is important for Canadians to protect health and the environment
air quality is affected by many factors such as meteorological conditions,
anthropogenic sources (e.g., industrial activities, mobile sources and residential wood
burning), natural sources (e.g., wind-blown dust), TF, and EE (e.g., forest fires)
Canadians and all orders of government have a responsibility to prevent the air quality
from deteriorating.
Provinces and territories are responsible for managing air quality in their air zones with early
efforts focussed on areas where the standards are exceeded or where a significant population
is at risk of pollutant exposure. For emission sources and lands that fall under federal authority
(such as transportation sources, federal lands and national parks) the federal government will
collaborate with provinces and territories on air quality management.
Regarding the influence of transboundary flows from one Canadian jurisdiction to another,
the affected downwind jurisdiction should engage in discussions with the upwind source
jurisdiction. The federal government collaborates with provinces and territories to better
understand the flow of air pollution among airsheds. For transboundary flows from the United
States, the federal government uses provisions set out under the Canada-United States Air
Quality Agreement and lead the discussions in collaboration with the affected provinces or
territories.
An outline of the federal, provincial and territorial roles and responsibilities to improve air
quality under AQMS can be found on the CCME website.
7
For example, the Ontario Ministry of the Environment, Conservation and Parks can issue orders for the curtailment of the
operation of sources of air pollution during air pollution episodes under Ontario Regulation 419/05.
8
In some areas of Canada air quality management is a responsibility also shared with municipal (e.g. Montréal, Metro
Vancouver) governments.
9
Although Québec supports the general objectives of AQMS, it did not implement the System since it includes federal
industrial emission requirements that duplicate Québec's Regulation. However, Québec is collaborating with jurisdictions on
developing other elements of the system, notably air zones and airsheds.
10
Table 6-1: Suggested actions under the air zone management framework
Action Green Yellow Orange Red
Responsible
jurisdiction
Characterizing air
pollutant
concentrations in
air zones
Basic monitoring to
establish baseline
concentrations and
trends, potentially via
passive sampling,
remote sensing or
modeling. Refer to the
NAPS monitoring
protocol.
Ensure air pollutant monitoring is adequate to capture spatial and
temporal variability in concentrations. Refer to the NAPS QA/QC
guidelines. Air quality modelling may be a useful tool for jurisdictions when
choosing monitoring locations.
Provinces and
territories with
assistance from
federal government as
required and as
possible.
Compilation of
emission
inventories in air
zones
Not applicable (NA)
Compile, as required, emissions inventory for air zones to evaluate main
sources of air pollutants. Use of national, provincial, and territorial
emissions inventories, supplemented with local emissions may assist this
activity.
Airshed
coordination
NA Initiate airshed coordination if there are transboundary issues.
The federal
government will
collaborate with
provinces and
territories to better
understand the flow of
air pollution among
airsheds.
The federal
government leads
international air
pollution discussions.
Stakeholder
engagement
NA
Engage local
stakeholders as
appropriate.
Engage local stakeholders with roles and
deliverables identified.
Provinces and
territories.
11
Action Green Yellow Orange Red
Responsible
jurisdiction
Development of
an air zone
management plan
NA
Develop an air
zone management
plan if required to
prevent air quality
deterioration.
Consider all
important sources
of air pollutants,
and provincial and
territorial policies.
The plan should
consider CI/KCAC
and may consider
current and future
projections of air
quality, defined air
zone goals, the role
of stakeholders,
priority emission
sources,
mechanisms to
achieve air quality
improvements, and
any additional
monitoring and
inventory required.
Develop a
comprehensive air
zone management plan
to improve air quality.
Consider all important
sources of air
pollutants, provincial
and territorial policies,
including short,
medium and long-term
milestones and targets.
The plan should
consider CI/KCAC and
may identify key
emissions sources,
consider current and
projected air quality
based on ambient air
pollutant trends, and
set out actions to be
undertaken by
governments and
stakeholders to reduce
emissions.
Develop a comprehensive
air zone management
plan to reduce
concentrations below the
CAAQS. Consider all
important sources of air
pollutants, provincial and
territorial policies,
including short, medium
and long-term milestones
and targets.
The plan should consider
CI/KCAC and current and
future directions in air
quality based on trends or
projections, and include:
actions to be undertaken
by governments and
stakeholders to reduce
emissions with short,
medium and long-term
milestones and targets;
and detailed modeling to
show how planned
actions will improve air
quality.
Provinces and
territories to lead the
development of air
zone management
plans.
All orders of
government have a
responsibility to ensure
that pollutant levels do
not increase and that
CAAQS are not
exceeded.
Implement air
zone
management plan
NA
Implement the air zone management plan that outlines the roles and
responsibilities of all participants, estimated timelines, and the process for
review.
Provinces and
territories to lead. All
orders of government
have a responsibility to
ensure CAAQS are not
exceeded.
12
Action Green Yellow Orange Red
Responsible
jurisdiction
Publish air zone
management plan
NA
Provinces and territories review and publish the air zone management
plan, ensuring it is achievable and consistent with provincial/territorial
policies.
Provinces and
territories.
Assess progress NA
Assess progress in implementing the air zone management plan, track the
implementation of the management plan, and demonstrate how the
management actions contribute to improved air quality. The air zone
management plan to be revised as needed to achieve continuous
improvement in air quality.
Provinces and
territories.
Air zone reports
Prepare and publish annual reports summarizing current ambient air quality levels, ambient and
emissions trends, air zone management levels, and management actions to reduce air pollutant
levels.
Provinces and
territories.
Public outreach
Educate the public on local air quality. Publish best practices guides on how the public may contribute
to improving air quality. Include information on websites about actions individuals can undertake to
improve air quality.
Provinces and
territories.
13
7.0 EFFECTIVE MANAGEMENT LEVEL
Annual variations in emissions of air pollutants and meteorological conditions can cause
variations in CAAQS metric values and this in turn can cause variations in the management
level assigned to an air zone between years. For example, an air zone could be in the red
management level for sulphur dioxide in one year and in the yellow the next. This raises
possible issues from management and communication perspectives.
7.1 Addressing Management Perspective
When an air zone is in the red management level (for example) in a reporting-year, the
jurisdiction should initiate the development and implementation of actions to try to improve
air quality below the CAAQS and try to prevent future exceedances.
Developing and implementing an action plan to improve air quality is a process that can
span many years. As such, if an air zone drops from a higher management level in one year
to a lower level the next, the jurisdiction must choose what course to follow for the
management plan. Depending on the air zone situation, the jurisdiction may:
amend the development and implementation of the plan to manage instead at the
lower level, which could include scaling back actions proposed in the original
implementation plan
continue developing and implementing the plan at the higher level.
Unless improvements in air quality have occurred to make a return to a higher management
level unlikely, jurisdictions are encouraged to maintain actions at a consistent management
level, even if the management level in subsequent years drops to a lower level. This
approach is recommended to protect air quality and reduce the risk of deterioration. This
would also be consistent with the principle of continuous improvement.
7.2 Communicating Change in Management Levels
Jurisdictions can communicate in their air zone reports variations in management levels
between years. Some options for this communication include:
1. report only the “reporting-year” management level, which is the management level
obtained for the reporting period under consideration (e.g. 2016 to 2018)
2. report the management level which is actually (or effectively) being implemented
based on a higher level from a previous year
3. report both the reporting-year management level and the management level actually
being implemented.
For cases where the actions being developed and implemented are those from a higher
management level from a previous year, the jurisdiction should consider communicating
this in its air zone reports. For option 3, the reports could say that while the reporting-year
14
management level for an air zone is yellow, for example, the air zone is actually assigned
a higher level because in a previous year the management level assigned to the air zone
was higher and the zone is still being managed to the higher level.
8.0 COMMUNICATION AND REPORTING
Communicating with the Canadian public is an important component of AQMS. Each
jurisdiction will regularly publish reports on air quality for each of their air zones and these
reports will include the actual metric values and achievement status of the CAAQS for each
CAAQS-reporting station and air zone. Other common elements which could be part of
these reports include:
1. adjusted metric values (as applicable) after the consideration of TF-EE influences
2. achievement status of the CAAQS for each CAAQS-reporting station and air zone
based on adjusted metric values
3. weight of evidence analyses to support the occurrence of influences from TF-EE
4. reporting-year management level (after consideration of TF-EE as applicable) for
the air zone and the effective management level (as applicable)
5. management actions taken to reduce emissions or preventing emissions from
increasing
6. information on any management plan being developed or implemented (as
applicable).
Air zone reports are typically available on the web site of each jurisdiction. In addition,
CCME also provides an interactive web-based State of the Air report titled Canada’s Air.
Canada’s Air provides an overview of the status of air quality across Canada, including:
information on ambient concentrations of air pollutants and emission sources
the impact of air pollutants on human health and the environment
actions Canadians can undertake to improve air quality.
Canada’s Air is updated regularly to complement annual air zone reports compiled by
jurisdictions.
15
REFERENCES
CCME (Canadian Council of Ministers of the Environment). Canada’s Air. Available online:
www.ccme.ca
.
CCME 2012. The Air Quality Management System Federal, Provincial and Territorial Roles and
Responsibilities. CCME, Winnipeg. Available online: www.ccme.ca
.
CCME 2019. Guidance Document on Transboundary Flows and Exceptional Events
for Air Zone
Management. CCME, Winnipeg. Available online: www.ccme.ca
.
Environment and Climate Change Canada. Guidelines and Objectives. Available online:
http://www.ec.gc.ca/lcpe-cepa/default.asp?lang=En&n=E9DBBC31-1
(viewed 2018-02-26).
Environment and Climate Change Canada. NAPS Data Products. Available online:
http://maps-
cartes.ec.gc.ca/rnspa-naps/data.aspx (viewed 2018-02-26).
Environment and Climate Change Canada and Health Canada. Air Quality Health Index. Available online:
https://www.canada.ca/en/environment-climate-change/services/air-quality-health-index.html
(viewed 2018-02-26).
Environment Canada. 2004. National Air Pollution Surveillance Network Quality Assurance and Quality
Control Guidelines. EC, Ottawa. Available online:
https://docs.neb-one.gc.ca/ll-
eng/llisapi.dll/fetch/2000/90464/90552/548311/956726/2392873/2449925/2451574/2797907/C234-
12-3_-_attachment_1_-_Evidence_IR_Response_-_A4R3F2.pdf?nodeid=2796900&vernum=-2
(viewed 2018-02-26).
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APPENDIX 1 THE CANADIAN AMBIENT AIR QUALITY STANDARDS
10
10
Consult the CCME web site for the most up to date list of CAAQS.
11
The metric values for comparison to the standard must be rounded to the same number of digits as the standard.
12
2015 and 2020 CAAQS established as ambient air quality objectives by the federal government on May 25, 2013; 2025
CAAQS on June 29, 2019 (Canada Gazette Part 1).
13
Established as ambient air quality objectives by the federal government on May 25, 2013 (Canada Gazette Part 1).
14
Established as ambient air quality objectives by the federal government on October 28, 2017 (Canada Gazette Part 1).
15
Established as ambient air quality objectives by the federal government on December 9, 2017 (Canada Gazette Part 1).
Pollutant
Averaging
time
Standard
11
(numerical value)
Statistical form of the standard
2015
2020 2025
Ozone
12
8-hour 63 ppb 62 ppb 60 ppb
The 3-year average of the annual
4
th
highest of the daily- maximum
8-hour average concentrations.
Fine
particulate
matter
(PM
2.5
)
13
24-hour
28 µg/m
3
27 µg/m
3
The 3-year average of the annual
98
th
percentile of the daily 24-hour
average concentrations.
1-year
(annual)
10.0 µg/m
3
8.8 µg/m
3
The 3-year average of the annual
average of the daily 24-hour
average concentrations.
Sulphur
Dioxide
(SO
2
)
14
1-hour 70 ppb 65 ppb
The 3-year average of the annual
99
th
percentile of the daily-
maximum 1-hour average
concentrations.
1-year
(annual)
5.0 ppb 4.0 ppb
The arithmetic average over a
single calendar year of all 1-hour
average concentrations.
Nitrogen
Dioxide
(NO
2
)
15
1-hour 60 ppb 42 ppb
The 3-year average of the annual
98
th
percentile of the daily-
maximum 1-hour average
concentrations.
1-year
(annual)
17.0 ppb 12.0 ppb
The arithmetic average over a
single calendar year of all 1-hour
average concentrations.
17
APPENDIX 2 THE MANAGEMENT LEVELS
16
Table A2-1: Management levels for ozone
Management level 2015 2020 2025
Red > 63* ppb > 62 ppb > 60 ppb
Orange 57 to 63 ppb 57 to 62 ppb 57 to 60 ppb
Yellow 51 to 56 ppb
Green < 50 ppb
*The concentrations have the same statistical form as the corresponding CAAQS and the metric values for comparison
to the concentrations must be rounded to the same number of digits as the shown concentrations.
Table A2-2: Management levels for PM
2.5
Management
level
PM
2.5
24-hour PM
2.5
annual
2015 2020 2015* 2020
Red
> 28* µg/m
3
> 27 µg/m
3
> 10.0 µg/m
3
> 8.8 µg/m
3
Orange
20 to 28 µg/m
3
20 to 27 µg/m
3
6.5 to 10.0 µg/m
3
6.5 to 8.8 µg/m
3
Yellow
11 to 19 µg/m
3
4.1 to 6.4 µg/m
3
Green
< 10 µg/m
3
< 4.0 µg/m
3
*The concentrations have the same statistical form as the corresponding CAAQS and the metric values for comparison
to the concentrations must be rounded to the same number of digits as the shown concentrations.
16
Consult the CCME web site for the most up to date list of management levels.
18
Table A2-3: Management levels for sulphur dioxide
Management
level
SO
2
1-hour SO
2
annual
2020 2025 2020* 2025
Red > 70* ppb > 65 ppb > 5.0 (CAAQS) > 4.0 ppb
Orange 51 to 70 ppb 51 to 65 ppb 3.1 to 5.0 ppb 3.1 to 4.0 ppb
Yellow 31 to 50 ppb 2.1 to 3.0 ppb
Green 30 ppb 2.0
*The concentrations have the same statistical form as the corresponding CAAQS and the metric values for comparison
to the concentrations must be rounded to the same number of digits as the shown concentrations.
Table A2-4: Management levels for nitrogen dioxide
Management
level
NO
2
1-hour NO
2
annual
2020 2025 2020* 2025
Red > 60 ppb > 42 ppb > 17.0 ppb > 12.0 ppb
Orange 32 to 60 ppb 32 to 42 ppb 7.1 to 17.0 ppb 7.1 to 12.0 ppb
Yellow 21 to 31 ppb 2.1 to 7.0 ppb
Green 20 ppb 2.0 ppb
*The concentrations have the same statistical form as the corresponding CAAQS and the metric values for comparison
to the concentrations must be rounded to the same number of digits as the shown concentrations.