280 likes | 706 Views
Smoke Management. Smoke Management is about managing the emissions from fire by:Reducing EmissionsReducing Impacts of the EmissionsSmoke is unlike most other pollutant sources ? a control can not be put on it to scrub the emissions.. Smoke Management. Reduce Smoke EmissionsIncrease combustion ef
E N D
1. Smoke Management Susan O’Neill
NRCS Air Quality and Atmospheric Change Team
09/2006, 03/2007
2. Smoke Management Smoke Management is about managing the emissions from fire by:
Reducing Emissions
Reducing Impacts of the Emissions
Smoke is unlike most other pollutant sources – a control can not be put on it to scrub the emissions.
3. Smoke Management Reduce Smoke Emissions
Increase combustion efficiency
Burn smaller units and/or burn more frequently
Employ alternatives to burning
Reduce Smoke Impacts
Tools to help time burning – Is today a good day to burn?
Where are my sensitive receptors?
Monitor plume during the burn
Post burn considerations – smoldering, mop-up
4. Why do we need tomanage smoke? Health Impacts -> National Ambient Air Quality Standards (NAAQS)
Public Safety and Nuisance
Economic and social issues (vacations, tourism).
Smoke across roads.
Visibility – Regional Haze Rule
Scenic vistas are a resource to preserve.
We are a Conservation Agency – Air Quality is a resource concern
5. Smoke Management Plans Goals
Allow for fire function as a management tool
Protect public health
If a smoke management plan is in place for a region, burners must comply with.
Oregon Smoke Management Plans
Willamette Valley/Western Oregon
Union County
Jefferson County
Umatilla Indian Reservation
6. Emissions from Fire Complete Combustion
Carbon Dioxide (CO2)
Water (H2O)
Incomplete Combustion
Carbon Monoxide (CO)
Particulate Matter (PM)
Hydrocarbons (HC)
Oxides of Nitrogen (NOx)
Sulfur Dioxide (SO2)
Ammonia (NH3)
7. Particulate Matter Health impacts associated with PM2.5 – particles are inhaleable into the lungs. Dangerous to children, elderly, asthmatics.
Define PM2.5 and PM10 and PM coarse.Health impacts associated with PM2.5 – particles are inhaleable into the lungs. Dangerous to children, elderly, asthmatics.
Define PM2.5 and PM10 and PM coarse.
8. PM2.5 NAAQS SIP/TIPs
24-hr average. Prescribed fire concentrations tend to be more acute and get averaged out over the 24-hr period.SIP/TIPs
24-hr average. Prescribed fire concentrations tend to be more acute and get averaged out over the 24-hr period.
9. NRCS Air QualityResource Concerns Particulate Matter
Ozone Precursors
Greenhouse Gases
Ammonia
Odor
10. Smoke Behavior in aStable Atmosphere Smoke Behavior – the following pictures are of smoke from large wildfires, but what I want to show is the interaction of the smoke with the atmosphere.
Capping inversion is trapping smoke.
Some of the plume (on the right) has reduced lifting – not as hot perhaps and atmospheric stability is hindering its lift.
Heat from the convective column is high enough to punch through the inversion.
Fumigation below mixing height.Smoke Behavior – the following pictures are of smoke from large wildfires, but what I want to show is the interaction of the smoke with the atmosphere.
Capping inversion is trapping smoke.
Some of the plume (on the right) has reduced lifting – not as hot perhaps and atmospheric stability is hindering its lift.
Heat from the convective column is high enough to punch through the inversion.
Fumigation below mixing height.
11. Smoke Behavior in anUnstable Atmosphere Smoke Behavior in an unstable atmosphere. No capping inversion.
Looping plume – instability of the atmos.
Smoke is not on the ground near the source.
Transport by upper level winds.Smoke Behavior in an unstable atmosphere. No capping inversion.
Looping plume – instability of the atmos.
Smoke is not on the ground near the source.
Transport by upper level winds.
12. Smoke Behavior in Valleys Smoke caught under a valley inversion that is being transported by down-valley winds in the early morning.Smoke caught under a valley inversion that is being transported by down-valley winds in the early morning.
13. NOAA ARL – Forecast Meteorologyhttp://www.arl.noaa.gov/ready/cmet.html Meteograms
Wind Roses
Soundings
Time Series
14. Ag Burn Outlook Application Guidance for farmers and ranchers about atmospheric dispersion conditions for burning.
Is today a good day to burn?
Simple-to-operate web-based application
Based on Northwest Regional Modeling Consortium MM5 operation at UW
4-km domain
Produces a forecast for today and tomorrow
By zip code
Graphic map with pop-up table of meteorology data
15. Ag Burn OutlookToday and Tomorrow Mixing height = the unstable atmospheric layer that extends from the surface up to the base of an inversion. Within this layer, the air is well stirred.
Ventilation Index = mixing height * 20m/surface wind speed
There needs to be a minimum amount of ventilation for a burn to disperse adequately. If you’re not getting some minimum ventilation, then conditions may not be adequate to burn.
Designed to be conservative.Mixing height = the unstable atmospheric layer that extends from the surface up to the base of an inversion. Within this layer, the air is well stirred.
Ventilation Index = mixing height * 20m/surface wind speed
There needs to be a minimum amount of ventilation for a burn to disperse adequately. If you’re not getting some minimum ventilation, then conditions may not be adequate to burn.
Designed to be conservative.
16. Example of the Web Application
17. What Do the Maps Display? Burn prediction
Average surface wind speed and direction arrows
Zip code areas (outlined in blue)
Location Information: counties, cities, roads, rivers, schools, hospitals, shaded relief
18. Burn Outlook for Prineville Simple easy to use tool available daily on the web (by 6am typically).
Please send me feedback.
While based on meteorological parameters typically used by fire weather forecasters, this merging of them together has not been evaluated so I would appreciate feedback. It can be customized regionally.
Any features/behaviors you like/don’t like? Let me know. I can help modify.
Can take nationally and customize for regions.
Does not need to be zip-code based – other ideas?Simple easy to use tool available daily on the web (by 6am typically).
Please send me feedback.
While based on meteorological parameters typically used by fire weather forecasters, this merging of them together has not been evaluated so I would appreciate feedback. It can be customized regionally.
Any features/behaviors you like/don’t like? Let me know. I can help modify.
Can take nationally and customize for regions.
Does not need to be zip-code based – other ideas?
19. Oregon Department of ForestryFire Weather Information http://egov.oregon.gov/ODF/FIRE/fire.shtml#Smoke_Management Won’t start the forecasts up until end of Sept or early Oct – need precip first before entering the prescribed burning season.Won’t start the forecasts up until end of Sept or early Oct – need precip first before entering the prescribed burning season.
20. Oregon Department of AgricultureFire Weather Information http://www.oregon.gov/ODA/NRD/weather.shtml
21. Identify Smoke Impacted Area Determine Area Affected by Smoke Plume
5 miles for grass
5 miles backing fires in other fuels
10 miles for head fires other fuels or large ( >500 ac) burns
Draw line from each end of the fire at 30 degrees from wind direction and draw arc at five and ten miles (45 degrees with variable winds). This is the probable smoke impact area.
Go down drainage one-half the distance (2.5 and 5 miles). This is night time impact area.
The goal of smoke management is to limit the impacts of smoke on people, haziness of the air and visual impairment of the view shed.
Currently there are two types of smoke screening procedures -
The low tech version
The high tech version
Low Tech version involves a pencil, paper, maps and scale
High Tech version involves computer models
We will deal with the low tech version. This procedure was developed for rural areas and is qualitative and does not give a quantitative answer.
Step 1. - Determine the area affected by the smoke plume.
Plot wind direction and distances of 5 or 10 miles downwind depending on fuel types.
The goal of smoke management is to limit the impacts of smoke on people, haziness of the air and visual impairment of the view shed.
Currently there are two types of smoke screening procedures -
The low tech version
The high tech version
Low Tech version involves a pencil, paper, maps and scale
High Tech version involves computer models
We will deal with the low tech version. This procedure was developed for rural areas and is qualitative and does not give a quantitative answer.
Step 1. - Determine the area affected by the smoke plume.
Plot wind direction and distances of 5 or 10 miles downwind depending on fuel types.
22. Identify Sensitive Receptors in Smoke Impact Area Identify Smoke Sensitive Areas
If none - continue with prescribed burn
If smoke sensitive areas are found continue screening process
Identify CRITICAL Smoke Sensitive Areas
Areas with existing air quality or visibility problems
5 miles - one half mile is critical
10 miles - one mile is critical
If critical area is identified
Prescribe new wind direction
If in “outer half” burn in small units that are completed prior to sundown
Consider alternative to burning
Step two is to identify the smoke sensitive areas within the delineation.
If there are no smoke sensitive areas in the delineation, continue with the planned burn. If smoke sensitive areas do exist, continue with the screening process.
Identify CRITICAL smoke sensitive areas
Areas with existing air quality or visibility problems
If 5 miles is used the first one-half mile is critical
If 10 miles is used the first mile is critical
Step two is to identify the smoke sensitive areas within the delineation.
If there are no smoke sensitive areas in the delineation, continue with the planned burn. If smoke sensitive areas do exist, continue with the screening process.
Identify CRITICAL smoke sensitive areas
Areas with existing air quality or visibility problems
If 5 miles is used the first one-half mile is critical
If 10 miles is used the first mile is critical
23. Monitoring the Smoke Plume Before ignition
Evaluate Meteorology
Evaluate Airshed
Other sources emitting in the airshed?
What are the current air quality conditions?
During Burn
Evaluate meteorological conditions
Evaluate Plume Behavior
Is plume rising and dispersing?
Is plume staying close to the surface?
After Burn is complete
Smoldering
Mop-up
24. Oregon Air Quality Monitoring Data
25. AIRNOW – Air Quality Index http://www.airnow.gov/index.cfm?action=airnow.local
26. BlueSkyRAINSwww.blueskyrains.org View other burning activity
27. Thank You!Questions? susan.oneill@por.usda.gov
503-273-2438
http://www.airquality.nrcs.usda.gov