air quality impacts of recreational beach fires: preliminary assessment
TRANSCRIPT
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7/30/2019 Air Quality Impacts of Recreational Beach Fires: Preliminary Assessment
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Posted at www.aqmd.gov
May 15, 2013
Outline Health Effects of Wood Smoke
Preliminary Monitoring Data
Gradient Surveys
Fixed-site Monitoring
Other Results
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Wood Smoke Source of fine particulate (PM2.5)
Source of carcinogenic toxic pollutants
Benzene, Formaldehyde, Polycyclic Aromatic Hydrocarbons(PAH)
Contains respiratory irritants
Acrolein, NOx
Wood burning can affect indoor and outdoor air quality
Multiple studies showing health effects:
In communities with high levels of wood combustion
During large wildfire events
Studies in Communities with
Significant Biomass Burning
Daily particulate matter levels associated with:
Respiratory symptoms in children with asthma
Visits to emergency rooms for asthma episodesHospital admissions related to respiratory symptoms
Naeher, L. et al. Woodsmoke Health Effects: A Review. Inhalation Toxicology, 19(1): 67 106, 2007
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Studies During Southern
California Wildfires - 2003 Increased symptoms in children exposed to smoke
Eye, nose and throat irritation
Cough, wheezing, asthma attacks
Medication use and physician visits
Increased respiratory-related hospital admissions
Strongest associations noted among those over 65 and
those 1-4 years of age
Kunzli, N. et al. Health Effects of the 2003 Southern California Wildfires on Children.
Am J Respir Crit Care Med Vol 174: 12211228, 2006;
Delfino, R. et al. The relationship of respiratory and cardiovascular hospital admissions to
the southern California wildfires of 2003. Occup. Environ. Med. 66:189-197, 2009
Agency Position on Wood Smoke
California Air Resources Board
Wood smoke a serious threat to public health
Aggravates lung and heart disease
Can cause 10% increase in children's hospital admissionsfor respiratory symptoms
U.S. Environmental Protection Agency
Wood smoke can affect everyone
Children, persons with existing health conditions most vulnerable
Health risks can be reduced by switching to gaseousfuels
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PM Health Guidance
National Ambient Air Quality Standards for PM2.5: Annual Average: 12 mg/m3
24 Hour Average: 35 mg/m3
Guidance for Public Health Officials for Wildfire Smoke
Recommended protective measures based upon shorter termPM exposure
Includes Time frames as short as 1 to 3 hours
for both PM2.5 and PM10: 89 - 138 mg/m3 - Unhealthy for Sensitive Groups (USG)
139 - 351 mg/m3
- Unhealthyconsider canceling public events,based on public health and travel considerations
352 - 526 mg/m3 - Very UnhealthyLipsett, Michael and Barbara Materna, Wildfire Smoke A Guide for Public Health Officials , 2008.
Revising the Air Quality Index and Setting a Significant Harm Level for PM2.5 , OAQPS Issue Paperfor Discussion at National Air Quality Conference, U.S. Environmental Protection Agency,OAQPS, 2007.
Beach Fire Pit Emissions
Assessed the emissions of a single fire ring forone evening
One fire event assumed to burn 2 bundles ofwood (approx. 32 lbs total)
Assumed CARB fireplace emission factor
Compared emissions to that of an average on-road 2013 Heavy Duty Diesel Vehicle (HDDV)
One fire pit in one evening estimated toemit as much PM2.5 as one Heavy-DutyDiesel Truck driving 564 miles
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SCAQMD Monitoring Studies
Purpose
Assess potential for human exposure to wood smokefrom beach fires
Approach
Deploy a combination of monitoring technologies andsampling strategies
Other Considerations
Shifting meteorology, variable activity levels, technologylimitations
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Gradient SurveysObjective:
Assess the PM impacts of the Beach Fires at multiple
locations downwind over the course of an evening
Methods:
TSI Inc. DustTrak DRX Measures PM1, PM2.5, PM10
on a second-by-second basis
Advantages: small, portable, high time
resolution, good survey tool for relative
measurements
Limitations: not certified to federal reference
method criteria. A drying inlet implemented to
remove humidity effects
Preliminary Results: Corona Del Mar 3/19/13
10 Minute Average PM2.5 Relative to Background Levels
Fire pits
WindDirection
1.2
1.0
1.0
1.0
1.0
1.21.7
1.61.5
2.4 2.3 1.8
1.9
1.5
1.3
1.7
2.1 2.0
1.0
1.1
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Preliminary Results: Corona Del Mar 3/30/13
10 Minute Average PM2.5 Relative to Background Levels
Fire pits
StationaryMonitor
1.2
1.4
1.4
1.5
3.2
1.2
1.2
1.4 2.7
1.5
1.6
2.8
1.0
1.6
1.8
1.2 1.2
2.8
Preliminary Results: Corona Del Mar 3/30/13
10 Minute Average PM10 Relative to Background Levels
Ratios to Lowest Observe Measurement
Fire pits
StationaryMonitor
1.41.4
1.2
1.1
2.5
2.72.2
2.7
1.5
1.1
1.7
1.1
1.0
1.7
1.2
2.0 2.5
4.9
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4.9
3.7
15 Fire pits
16 Fire pits
1
2.3
Night
Wind
1.1
1.5 1.3
1.3
1.4
1.4
Mobile Measurements: 10minute averages
Measurements:7pm to 10pm average
Preliminary Results: Balboa Beach 3/23/13
10 Minute Average PM2.5 Relative to Background
Preliminary Results: Balboa Beach 3/23/13
10 Minute Average PM10 Relative to Background
12.8
8.2
Measurements:7pm to 10pm average
Night
Wind
2.2
1.0
1.8
1.3
1.4
1.5
1.52.1
Lowest
Mobile Measurements:Relative Ratio to lowestobserved measurement
15 Fire pits
16 Fire pits
1.2
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Preliminary Results: Dockweiler State Beach 4/20/13
10 Minute Average PM2.5 Relative to Background
Fire pits
1.5
2.0
1.0
1.5
3.5
5.0
1.0
2.01.5
1.0 1.01.0
1.0
3.5 1.5
16
Huntington Beach Preliminary Data: 4/06/13
10 Min Average PM2.5 Ratio to Background
1.3
2.2 1.0
1.5
3.110.5
6.7
2.32.0
1.9 0.9
1.0 Background
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Preliminary Results: Huntington Beach 4/13/13
10 Min Average PM2.5 Relative to Background
5.68.0
1.4
3.610.8
0.6
2.4
2.4
1.6
1.8
1.8
1.8 1.8 1.2 1.6
1.2
1.0Background
9.8
2.0
3.2
3.01.8
2.8 1.4
4.8
4.6
1.3
1.4
Preliminary Results: Huntington Beach 4/27/13
Gradient 1
Gradient 2
Gradient 3
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Preliminary Results:
Huntington Beach 4/27/13
0
2
4
6
8
10
12
0 50 100 150 200 250 300 350 400 450
EstimatedPM2.5
RelativetoBackgroundLevel
Distance from Beach (m)
Gradient 1 Gradient 2 Gradient 3
Preliminary Results: Huntington Beach 5/4/13
10 Min Average PM2.5 Relative to Background
5.1
1.3
1.3
0.9
3.2
1.1
2
3.6
0.9
1.2
3.1
3.3
2.4
3.2
1.3
1.4
1.5
4.5
1.11.1
1.2
1.2
1.5
1.2
1.3
1.0
0.9
1.0
1.3
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Fixed-Site MonitoringObjective:
Assess the PM impacts of the Beach Fires at a fixed
locations, continuously over time
Methods:
E-BAM Measures PM2.5 on an hourly basis
Advantages: portable, low power, same
measurement principle as a Federal Equivalent
Method
Limitations: less accurate at low levels
Aethalometer
Measures Black Carbon, anindicator of combustion, on a continuous basis
Condensation Particle Counter (CPC) - Measures
Ultrafine particles, indicative of nearby sources of
combustion
Fixed Site Monitoring: Corona Del Mar
EBAM
Aethalometer
CPC
PM2.5 FilterSampling
Fire pits
StationarySite
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Fixed Site Monitoring: Balboa Beach
EBAM
StationarySite
Fire pits
Fire pits
0
50
100
150
200
250
300
3/29/13
12:00
3/30/13
12:00
3/31/13
12:00
4/1/13
12:00
4/2/13
12:00
4/3/13
12:00
4/4/13
12:00
4/5/13
12:00
4/6/13
12:00
4/7/13
12:00
4/8/13
12:00
4/9/13
12:00
4/10/13
12:00
4/11/13
12:00
4/12/13
12:00
4/13/1312:00
4/14/13
12:00
4/15/13
12:00
4/16/13
12:00
4/17/13
12:00
4/18/13
12:00
4/19/13
12:00
4/20/13
12:00
4/21/13
12:00
4/22/13
12:00
4/23/13
12:00
4/24/13
12:00
4/25/13
12:00
4/26/13
12:00
4/27/13
12:00
4/28/13
12:00
4/29/13
12:00
4/30/13
12:00
5/1/13
12:00
5/2/13
12:00
5/3/13
12:00
5/4/13
12:00
5/5/13
12:00
5/6/13
12:00
5/7/13
12:00
PM2.5Estim
atedConcentrationug/m3)
Date and TimeCorona Del Mar PM2.5 (ug/m3) Balboa Beach PM2.5 (ug/m3)Corona Del Mar PM2.5 B (ug/m3) USG 1 to 3 hour (ug/m3)Unhealthy 1 to 3 hour (ug/m3)
Preliminary Results: Corona Del Mar and Balboa Beach
PM2.5 Time Series
USG = Unhealthy for Sensitive GroupsUnhealthyconsider canceling public events, based on public health and travel considerations
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Fixed Site Monitoring: Huntington Beach
EBAM
Aethalometer
CPC
PM2.5 FilterSampling Stationary
Site
Huntington Beach Preliminary Data: 4/13 to 5/1
PM2.5 Hourly Average Time Series
0
2040
60
80
100
120
140
160
180
200
4/12/13
0:00
4/12/13
12:00
4/13/13
0:00
4/13/13
12:00
4/14/13
0:00
4/14/13
12:00
4/15/13
0:00
4/15/13
12:00
4/16/13
0:00
4/16/13
12:00
4/17/13
0:00
4/17/13
12:00
4/18/13
0:00
4/18/13
12:00
4/19/13
0:00
4/19/13
12:00
4/20/13
0:00
4/20/13
12:00
4/21/13
0:00
4/21/13
12:00
4/22/13
0:00
4/22/13
12:00
4/23/13
0:00
4/23/13
12:00
4/24/13
0:00
4/24/13
12:00
4/25/13
0:00
4/25/13
12:00
4/26/13
0:00
4/26/13
12:00
4/27/13
0:00
4/27/13
12:00
4/28/13
0:00
4/28/13
12:00
4/29/13
0:00
4/29/13
12:00
4/30/13
0:00
4/30/13
12:00
5/1/130:00
5/1/131
2:00
5/2/130:00
HourlyAveragePM2.5
ug/m3
Date/Time
EBAM 1 E-BAM 5 USG 1 to 3 hour (ug/m3) Unhealthy 1 to 3 hour (ug/m3)
USG = Unhealthy for Sensitive GroupsUnhealthyconsider canceling public events, based on public health and travel considerations
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Preliminary Data: Huntington Beach 4/27 to 5/1
PM2.5 Hourly Average Time Series
0
10
20
30
40
50
60
70
80
90
100
4/27/201
3
0:00
4/27/201
3
3:00
4/27/201
3
6:00
4/27/201
3
9:00
4/27/2013
12:00
4/27/2013
15:00
4/27/2013
18:00
4/27/2013
21:00
4/28/201
3
0:00
4/28/201
3
3:00
4/28/201
3
6:00
4/28/201
3
9:00
4/28/2013
12:00
4/28/2013
15:00
4/28/2013
18:00
4/28/2013
21:00
4/29/201
3
0:00
4/29/201
3
3:00
4/29/201
3
6:00
4/29/201
3
9:00
4/29/2013
12:00
4/29/2013
15:00
4/29/2013
18:00
4/29/2013
21:00
4/30/201
3
0:00
4/30/201
3
3:00
4/30/201
3
6:00
4/30/201
3
9:00
4/30/2013
12:00
4/30/2013
15:00
4/30/2013
18:00
4/30/2013
21:00
5/1/201
3
0:00
HourlyAveragePM2.5
ug/m3
Date/Time
EBAM 1 E-BAM 5 USG 1 to 3 hour (ug/m3)EveningHours
Sat Sun Mon Tues
USG = Unhealthy for Sensitive Groups
Preliminary Results: Maximum Hourly PM2.5
Concentration Comparison
0
100
200
300
400
500
600
700
800
Station Fire(2009)
July 4th, 2012 South CoastBasin (2012)
HuntingtonBeach
Corona delMar
BalboaBeach
Maximum
Hou
rlyPM2.5Concentration
(ug/m3)
USG = Unhealthy for Sensitive GroupsUnhealthyconsider canceling public events, based on public health and travel considerations
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Preliminary Results: Corona Del Mar 3/30/13
Black Carbon and Ultrafine Particle ( 1 minute average)
0
5
10
15
20
25
0
50,000
100,000
150,000
200,000
250,000
13:00
13:17
13:34
13:51
14:08
14:25
14:42
14:59
15:16
15:33
15:50
16:07
16:24
16:41
16:58
17:15
17:32
17:49
18:06
18:23
18:40
18:57
19:14
19:31
19:48
20:05
20:22
20:39
20:56
21:13
21:30
BC(ug/m3)
CPCCount
Count MATES IV Count Max BC MATES IV BC Max
Filter analysis
Corona del Mar (3/30 to 4/19), Huntington Beach (4/24 to
current)- PM2.5 Mass (24 hour average) Daily Samples
All below 12.5 ug/m3, under the 24 hour NAAQS level (35 ug/m3)
One day nearly 40 ug/m3, day had very high gusty winds
- PM10 mass (4 hour sample, 4/6) - One Sample Only
Sample collected from 5 to 9pm with burning activity shown to
have PM10 mass concentration of 95 ug/m3.
30% higher concentration than sample collected from 1 to 5pm
Elevated levels of Potassium, an indicator for wood smoke
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Other analysisSix Ash samples:
- Polycyclic Aromatic Hydrocarbons (PAHs): Very low levels
- Elemental Analysis: Compared to wood ash, samples had high
presence of silicon and aluminum, indicative of sand content; most
other elements consistent with wood ash concentrations.
- One sample had an elevated level of total Chromium compared to
wood ash.
Five Sand samples:- PAH: Below analytical detection
Preliminary Conclusions
Beach fire activity is impacting PM2.5 levels at the
beach and extending into neighboring communities
Concentrations can be up to 10 times background levels
for short periods of time in beach parking areas, up to 3
times background at residential locations
1-hour average PM concentrations can exceed public
health guidance levels
Some measurements are higher than observed across
the Basin over a whole year
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Next steps Continue field sampling
Consider deployment of federal equivalent
methods
Continue to report findings to public as they
become available
Continue to work with potentially impacted citiesand state parks
Evaluate propane and natural gas options