fugitive dust research at dri portable wind tunnel unpaved road dust emission factors traker...
TRANSCRIPT
![Page 1: Fugitive Dust Research at DRI Portable Wind Tunnel Unpaved Road Dust Emission Factors TRAKER measurements at Lake Tahoe Near Field Deposition Research](https://reader033.vdocuments.us/reader033/viewer/2022051401/56649eab5503460f94bb16db/html5/thumbnails/1.jpg)
Fugitive Dust Research at DRIPortable Wind Tunnel
Unpaved Road Dust Emission FactorsTRAKER measurements at Lake Tahoe
Near Field Deposition
Research by:
Hampden KuhnsVicken Etyemezian
Jack GilliesAlan Gertler
Djordje NikolicSean AhonenCliff DenneyJohn Skotnik
Nicholas NussbaumDave Dubois
Jin Xu
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USDA-ARS Wind Erosion Research Unit http://www.weru.ksu.edu/vids
1. Portable Wind Tunnel
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LWT at Ft. Bliss, TX
•J. Gillies and B. Nickling testing emission flux potential
•LWT is closest measurement to a “standard”
•SWT - e.g. D. James (UNLV), D. Gillette (NOAA)
•Concerns with boundary layer development, maximum wind speeds, and accounting for saltation
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PI-SWIRL Schematic
Side View Bottom View
Computer Controller/ Data System PM Monitor
Sample Tube
Open-bottomed Cylindrical Chamber
Variable Speed Motor
Annular Ring
60 cm
40 cm
Side View Bottom View
Computer Controller/ Data System PM Monitor
Sample Tube
Open-bottomed Cylindrical Chamber
Variable Speed Motor
Annular Ring
Side View Bottom View
Computer Controller/ Data System PM Monitor
Sample Tube
Open-bottomed Cylindrical Chamber
Variable Speed Motor
Annular Ring
60 cm
40 cm
Blower for clean air injection
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PI-SWIRL v.2
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The PI-SWIRL-ogramSWIRLER RPM and PM10 Dust Concentration
0
100
200
300
400
500
14:52 15:21 15:50 16:19 16:48
Time of Day
PM
10 C
on
cen
trat
ion
(m
g/m
3)
0
1000
2000
3000
4000
5000
RP
M
PM10
RPM
Test 1: Stable Soil
Test 2: Disturbed Soil
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PI-SWIRL Status
• Version 3 is currently being tested– Lower weight and smaller size– Faster measurement– Low cost custom circuitry
• Patent application filed• PI-SWIRL has been collocated with LWT to draw
empirical relationship– Data still being analyzed
• Contact Vic Etyemezian ([email protected]) for more information
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2. Unpaved Road Dust Emission Factors
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Emission factor
calculated as horizontal flux
of PM10 passing
instrumented towers
-DT-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
76
517266
128
125
1220570
26040
125
1220570
260
-GR
-GR
-GR
-GR
-GR
-GR
-SA
7005,000
10,000
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
-DT-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
76
517266
128
125
1220570
26040
125
1220570
260
-GR
-GR
-GR
-GR
-GR
-GR
-SA
7005,000
10,000
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
-5
0
5
10
15
20
18:02:10 18:02:27 18:02:44 18:03:01 18:03:19 18:03:36 18:03:53 18:04:11
Time
Du
stT
rak
Rea
din
g (
mg
/m3)
DT_1 DT_3DT_2Baseline
Vehicle passes by DT_1
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Unpaved Emissions Measured on Flux Towers in Ft. Bliss TX (April 2002)
Vehicle Weight (kg) # Wheels
Dodge Neon 1,176 4
Ford Taurus 1,516 4
Dodge Caravan 1,759 4
HUMVEE 2,445 4
TRAKER (Chevy Van) 3,100 4
26’ UHAUL Truck 5,227 6
LMTV 8,060 4
Freightliner (Tractor) 8,982 22
HEMMET 17,727 8
5-ton Truck 14,318 6
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EFPM10 = b W S
EFPM10 [g/VKT] = 10.3 (W [Mg]) (S [m/s])
R2 = 0.89
0
500
1000
1500
2000
2500
3000
3500
4000
4500
0 50 100 150 200 250 300 350
Vehicle Mass*Speed (Mg*m/s)
PM
10
Em
issi
on F
acto
r (g
/VK
T)
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Unpaved Road Dust Emission Factor Status
• Emission factors are dependent on vehicle speed and weight
• Emission potentials of unpaved road soils were relatively constant in Ft. Bliss TX based on TRAKER.
• Need to determine how emission potential varies in other regions.
• Time since last rainfall is correlated with unpaved road emission factors
John A. GILLIES, Vicken ETYEMEZIAN, Hampden KUHNS, Djordge NIKOLIC & Dale A. Gillette (2004) Effect of Vehicle Characteristics on Unpaved Road Dust Emissions. Accepted in Atmospheric Environment
Kuhns H., V. Etyemezian, J. Gillies, S. Ahonen, C. Durham, D. Nikolic (2003) Spatial Variability of Unpaved Road Dust Emissions Factors near El Paso, Texas. Accepted in J. Air & Waste Manage. Assoc.
Kuhns H., V. Etyemezian, M. Green, Karin Hendrickson, Michael McGown, Kevin Barton, Marc Pitchford (2004) Vehicle-based road dust emissions mesasurement (II): Effect of precipitation, winter time road sanding, and street sweepers on PM10 fugitive dust emissions from paved and unpaved roads. Atmospheric Environment.
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3. Testing Re-entrained Aerosol Kinetic Emissions
from Roads (TRAKER)
Measurements in Lake Tahoe
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• Particle Sensors– TSI DustTrak 5830– Grimm Particle Size
Analyzer 1.108
• GPS– Ashtech/Magellan
Promark X
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Data Acquisition and Processing
•Lab View program displays and logs data from
•6 DustTraks•3 Grimms•1 GPS
•Uniform time stamp applied to all data for synchronization•Data tables are loaded into MS Access for processing and analysis
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TRAKER Signal vs Vehicle Speed
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
0 5 10 15 20 25 30 35
Speed (m/s)
TR
AK
ER
Sig
na
l (m
g/m
3 )
Treasure Valley Regression
T=0.00017*speed2.96
R2 = 0.972
•T = Ctire – Cbkgrnd
•T = a S3
•On the same paved road the TRAKER signal increases with the speed cubed
•Factoring out speed leaves a signal proportional to the emission potential of the road.
0
0.5
1
1.5
2
2.5
0 5 10 15 20 25 30 35 40
Speed (m/s)
TR
AK
ER
Sig
na
l (m
g/m
3 )
Ft. Bliss Regression
T=0.00012*speed2.75
R2 = 0.923
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Flux Ladder in Lake Tahoe
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Roadside PM Flux Measurements
PM concentration profile drops off with height
Real time instruments help when wind doesn’t cooperate
0
0.25
0.5
0.75
1
1.25
1.5
16:09:07 16:10:34 16:12:00 16:13:26 16:14:53 16:16:19Time on 2003/03/31
PM
10
Flu
x P
erpi
ndic
ular
to R
oad
(mg/
m s
) .
0
90
180
270
360
Win
d D
irect
ion
(deg
rees
)
Flux PM10Wind Direction
0
50
100
150
200
250
300
350
400
450
0 0.001 0.002 0.003 0.004 0.005 0.006 0.007 0.008 0.009
PM10 Conc Profile 1 m Downwind of Paved Road (mg/m3)
Hei
ght A
bove
Gro
und
(cm
)
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TRAKER vs Horizontal PM Flux
Unpaved EF = 8.36 T1/3
0.1
1
10
100
1000
0.1 1 10 100 1000 10000
Traker Signal (mg/m3)
Em
issi
on
Fac
tor
(g/v
kt)
Lake Tahoe Paved
EF = 0.33 T1/3
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Comparison of EF’s with Snow Precip
0
0.5
1
1.5
2
2.5
3
3.53/
1/20
03
3/8/
2003
3/15
/200
3
3/22
/200
3
3/29
/200
3
4/5/
2003
4/12
/200
3
4/19
/200
3
4/26
/200
3
5/3/
2003
5/10
/200
3
5/17
/200
3
5/24
/200
3
5/31
/200
3
6/7/
2003
6/14
/200
3
6/21
/200
3
6/28
/200
3
7/5/
2003
7/12
/200
3
Date
Sn
ow
Pre
cip
itat
ion
(cm
)
0
0.1
0.2
0.3
0.4
0.5
0.6
Em
issi
on
Fac
tor
(g/v
kt)
Heavenly Valley Snotel
Rubicon Snotel
Marlette Lake Snotel
Average EF CA_Loop
Average EF NV Loop
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Spatial/Temporal Variability of Road Dust
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Tahoe TRAKER Status• Road Dust EF’s drop by 70-80% from Spring to
Summer• Previous TRAKER Calibration based on unpaved
roads was way off– Maybe due to whole fleet vs just TRAKER?
• Cities roads are dirtier than high speed rural highways• Something is different b/w CA and NV roads that
create less dust
Draft report completed for CARB in June. Final expected by Sept.
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Transportable Fraction of Dust
• Basic Problem Statement: Inventory of dust sources appears to be too high compared with what we find in the air
• Possible Causes– Our inventory as measured at the source is
inaccurate– We are not accounting for removal of dust
near the source
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Evolution of Plume Downwind
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Approaches
• Modeling– Advantages: Inexpensive, easy to simulate
countless environments– Disadvantages: Who knows if its right!
• Measurement– Disadvantage: Expensive and labor intensive
(e.g. Gillies SERDP), unclear if possible to measure
– Advantage: Results based on a “Real” data
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Measurements of TF:>95% at 100 m at Ft. Bliss (Etyemezian et al., 2004)
<20% at 100 m at Dugway Proving Grounds Mock Urban Environment (Veranth et al., 2004)
USDA Proposal Submitted to measure TF in cornfield over growing season (Gillies et al., 2004)
-DT-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
76
517266
128
125
1220570
26040
125
1220570
260-GR
-GR
-GR
-GR
-GR
-GR
-SA
7005,000
10,000
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
-DT-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
-DT
76
517266
128
125
1220570
26040
125
1220570
260-GR
-GR
-GR
-GR
-GR
-GR
-SA
7005,000
10,000
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT_1DT_2DT_3
Trailer with visibility
equipment
Generator 200 meters
LIDAR 3,000 meters
Top View
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
DT: DustTrak
GR: GRIMM
SA: Sonic Anemometer
: Wind Vane
: Cup Anemometer
: Laptop computer
Legend
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Change in Integrated Horizontal Flux at Ft. Bliss
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Comparison of Model and
Measurements
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Change is Particle Size Distibution Downwind
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Transportable Fraction Research: Status
• Initial attempt completed (WESTAR report)
• Next round of research should target– Additional field studies– Model improvement– Consideration of vegetation, landscape
Etyemezian V., J. Gillies, H. Kuhns, D. Gillette, S. Ahonen, D. Nikolic, and J. Veranth (2004) Deposition and removal of fugitive dust in the arid southwest United States: Measurements and model results. Acceptd in J. Air & Waste Manage. Assoc.