Saskatchewans Air Modelling and Odour Guidelines Imran Maqsood, - - PowerPoint PPT Presentation
Saskatchewans Air Modelling and Odour Guidelines Imran Maqsood, - - PowerPoint PPT Presentation
Saskatchewans Air Modelling and Odour Guidelines Imran Maqsood, Ph.D., P.Eng. Ministry of Environment Air Quality in Saskatchewan, Saskatoon January 17, 2014 Outline Part 1: Air Modelling Guideline Part 2: Odour Guideline Part 1
Saskatchewan’s Air Modelling and Odour Guidelines
Imran Maqsood, Ph.D., P.Eng. Ministry of Environment Air Quality in Saskatchewan, Saskatoon January 17, 2014
Outline
- Part 1: Air Modelling Guideline
- Part 2: Odour Guideline
AIR MODELLING: GENERAL INFORMATION
Part 1
Why Do We Need Guideline?
- To ensure consistency in conducting air
modelling in Saskatchewan
- Regulatory approvals are treated equitably
- Promote efficient use of resources
How was Guideline Developed?
- Draft prepared in 2010
- Reviewed internally & externally in 2011
- First official guideline released in 2012
- Review and update guideline periodically
Is Guideline Flexible?
- Ministry supports innovation
- We are open to new or improved methods
- Any deviation should be justified
- Pre-consultation with the ministry is
recommended to discuss variations
Is it Consistent with Other Guidelines?
- Efforts were made to maintain consistency
with modelling approaches in AB and BC
- New West Partnership between SK, AB & BC
What Standards to Use?
- Saskatchewan Air Quality Standards
- National or CCME
- Alberta Environment
- Ontario Ministry of the Environment
- Texas Commission on Environmental Quality
AIR MODELLING: TECHNICAL GUIDANCE
Part 1
What is Air Modelling?
- Mathematical simulation of how air
pollutants disperse in atmosphere
- Meteorology, site configuration, emission
and terrain impact transport of pollutants
Why is Modelling Conducted?
- Approval or permit applications
- Predict pollutant concentration
- Stack design
- Select monitoring sites
- Design plans for air quality management
What is SK’s Modelling Approach?
- Simple facility
- Limited number of sources
Screening
Modelling
- Complicated facility
- Multiple sources & contaminants
Refined
Modelling
- Complex terrain, Land/water interface
- Chemical transformation, traffic
Specialized
Modelling
Screening
Simple facility Limited number of sources
Refined
More complicated facility Multiple emission sources Multiple contaminants
Specialized
Complex terrain Land/water interface Chemical transformation Road or rail traffic
SCREEN3 AERSCREEN
Worst case emissions Limited number of sources
AERMOD
Worst case emissions
CALPUFF CALQ3HCR
Compliant? Compliant? Compliant?
Stop Stop Stop
no no refine refine yes yes yes refine
Air Modelling System
Meteorological Data for SK
www.environment.gov.sk.ca
Free of Cost Download Regional Met Data Files Ministry website Or Use AERMET to generate site specific files
North Central Zone
AERMOD-Ready Regional Meteorological Data Files
Surface Class Fully Processed Data Files Partially Processed AERMET Stage 3 Input File Surface/ Upper Air Station Forest Surface Profile Stage 3 Nipawin The Pas Agricultural Surface Profile Urban Surface Profile
Terrain Data for Saskatchewan
- Free download from GeoBase website
- www.geobase.ca
- Use 1:50,000 terrain data for improved
accuracy
SK’s Background Concentrations
Compare (Model Results + Background) to Standards
90th 572.0 572.0 687.0 Carbon Monoxide 99th 915.0 1030.0 1260.0 (µg/m3) 90th 572.0 458.0 687.0 99th 1030.0 1145.0 1260.0 90th 11.3 32.0 39.5 35.7 41.4 Nitrogen Dioxide 99th 28.2 58.3 69.6 69.6 80.9 (µg/m3) 90th 9.4 28.2 32.0 30.1 37.6 99th 16.9 45.1 48.9 48.9 60.2 Annual 50th 3.8 5.6 15.1 9.4 18.8 90th 0.0 2.6 2.6 2.6 2.6 Sulphur Dioxide 98th 5.2 5.2 5.2 5.2 7.9 (µg/m3) 90th 0.0 2.6 2.6 2.6 2.6 99th 2.6 2.6 5.2 5.2 5.2 Annual 50th 0.0 0.0 0.0 0.0 0.0 Fine Particulate Matter 90th 6.5 6.6 7.5 6.6 8.3 (PM2.5) (µg/m3) 99th 13.9 14.3 13.9 8.4 14.7 Annual 50th 3.1 3.0 3.3 3.3 3.7 Particulate Matter 90th 23.1 36.3 (PM10) (µg/m3) 99th 49.1 63.3 Pollutant Averaging Period Percentile Background Concentrations For Air Dispersion Modelling Northern North Central Central Southwestern Southeastern 24 Hour 24 hours 1 Hour 8 Hour 1 Hour 24 Hour 1 Hour 24 Hour
Modelling Report Check List
IV AMBIENT IMPACT SUPPORTING DOCUMENTATION IV.A Electronic Files
- List and description of electronic files
- Required e-files to be submitted with report
- Input & output files for models
- Input & output files for pre-processors (if applicable)
- Input & output files for post-processors (if applicable)
- Digital terrain files
- Plot files
- Final report
IV.B Report shall include a discussion on deviations from the modelling checklist
ODOUR GUIDELINE
Part 2
Did you know?
The human genome has
- 1 gene for hearing
- 3 genes for seeing
- 12 genes for tasting
- ? genes for smelling?
- 1,000
Why odour is not an ordinary air contaminant?
- Odour is a complex mixture of compounds
- It is the results of a perception
- Perception and tolerance vary from individuals
- Individual compounds cannot represent the
actual impact of a mixture
- Because of synergies, chemical measurements
cannot be used to quantify odour
- Best tool of measuring odour is still the human
nose
How is Odour Measured?
- Odour is measured using air dilution
equipment and an odour panel
- Olfactometer dilutes an odour sample with
- dour-free air to various levels
- Diluted odorous air is presented to panel
- When half of odour panel can detect
- dour, it is called odour detection threshold
- r dilution ratio
Odour concentration can be expressed as:
- D/T - Detection Threshold or Dilution to Threshold
- OU - Odour Unit or Odour Unit per volume (OU/m3)
- For example, 500 OU/m3 means when 1
volume of odour sample is diluted with 500 volumes of fresh air and it can be detected by 50% of a panel.
- All units have same conceptual meaning
- Different methods used to measure odour result
in different units
- Use OU when measured by olfactometers
- Use D/T when measured by scentometers
Scentometer / Nasal Ranger (D/T) Odour measured at receptor location Olfactometry Lab Method (OU) Odour measured at source location
Why is Odour Guideline Needed?
- No odour guideline in place
- Residents are less tolerant to odour and its
impact on property value
- Guideline defines reference criteria to which
- dour impacts can be judged
- Guideline defines the process to
demonstrate compliance with odour criteria
Odour Criteria for Field Investigation
Odour criteria Averaging time Land use 2 D/T 2 tests not less than 15 minutes apart nor more than 60 minutes apart Residential/Urban zone 4 D/T Mixed residential and commercial/Rural zone 7 D/T Industrial/Agricultural zone
Nasal Ranger (D/T) Odour measured at receptor location
Odour Criteria for Modelling
Odour Criteria Averaging Time Annual Frequency Land Use 1 OU/m3 1 hour* 99.5% Urban residential zones 2 OU/m3 Urban commercial zones or mixed residential and commercial zones 4 OU/m3 Industrial or restricted business zones and rural zones with mixed utilisation 6 OU/m3 Industrial or agricultural zones with predominantly agricultural utilisation Olfactometry Lab Method (OU) Odour measured at source location
Odour Assesement Process
Complaint verified? Conduct field odour investigation using Scentometer Stop Quantify source odour emission using olfactometry method
If 3 or more verified complaints exceed odour criteria in 30 days No If measured odour level is 2 levels higher than the criteria
Conduct odour modelling Odour complaint received
Yes Yes
Next Steps
- Validation of odour criteria study is in
progress
- Criteria will be used as a “guideline” - a
tool for odour management in Sask.
- Guideline will be reviewed periodically