wrap rmc windblown dust emission inventory project summary
DESCRIPTION
WRAP RMC Windblown Dust Emission Inventory Project Summary. Dust Emission Joint Forum 6 June 2006. PM dust emissions from wind erosion Relies on land use and soil characteristics in order to estimate threshold surface friction velocities and emission rates - PowerPoint PPT PresentationTRANSCRIPT
WRAP Regional Modeling Center
WRAP RMC Windblown Dust Emission Inventory
Project Summary
Dust Emission Joint Forum
6 June 2006
WRAP Regional Modeling Center
WRAP Fugitive Windblown Dust (WBD) Emissions Model
• PM dust emissions from wind erosion
• Relies on land use and soil characteristics in order to estimate threshold surface friction velocities and emission rates
• Special treatment for agricultural lands
• Current version of model uses updated landuse/landcover (2000 NLAC)
• Revised PM10/PM2.5 ratios
• Updated Transport Fractions (TFs)
• Project Final Report available from
www.pah.cert.ucr.edu/aqm/308/emissions.shtml or www.wrapair.org/
WRAP Regional Modeling Center
Data Sources
• Landuse/Landcover– 2000 North American Land Cover Database (2000 NALC)
• Soil Texture– STATSGO soils database (from Penn State)
• Meteorology– Penn State/NCAR MM5 model simulations– Annual 2002 36-km WRAP modeling domain
• Fugitive dust transport fractions from EPA (Pace, 2005)– Developed at grid-cell level based on 2000 NALC
WRAP Regional Modeling Center
• Landuse/Landcover (LULC)
WRAP Regional Modeling Center
Soil Texture Transport Fractions
WRAP Regional Modeling Center
LULC Summary
State Other Agricultural Grasslands Shrublands Barren Grand TotalArizona 18,758,664 219,547 3,134,865 44,041,477 4,292,737 70,447,290California 70,657,941 4,393,081 6,784,617 35,016,552 2,651,292 119,503,483Colorado 28,378,893 2,926,349 11,615,014 20,022,217 121,338 63,063,810Idaho 23,874,792 2,131,780 4,609,782 20,838,492 391,058 51,845,903Montana 23,090,186 5,453,456 25,847,871 35,794,753 170,443 90,356,709Nevada 8,413,608 209,584 2,246,357 56,934,277 1,209,823 69,013,649New Mexico 19,532,239 365,082 7,721,162 43,892,028 3,002,496 74,513,007North Dakota 2,231,768 27,031,363 11,413,970 3,733,372 170,799 44,581,271Oregon 29,960,558 1,273,161 2,618,555 26,092,683 427,352 60,372,310South Dakota 3,947,226 15,203,919 17,713,946 10,901,218 316,333 48,082,642Utah 4,633,623 536,236 9,246,251 34,461,812 3,668,967 52,546,889Washington 27,627,735 1,789,827 3,336,621 9,164,410 786,385 42,704,978Wyoming 6,127,043 650,102 41,469,891 11,428,559 550,825 60,226,419Total 267,234,276 62,183,486 147,758,903 352,321,849 17,759,848 847,258,361
Acreage by Landuse Category
WRAP Regional Modeling Center
Transport Fractions (Tom Pace, EPA, 6/2005)
• Effects of near-source dust removal & deposition
• Varies by LULC; Applied at grid-cell level (12-km)
LULC Category Pre02d Base02b
Urban 0.30 0.00
Agricultural 0.85 0.75
Grasslands 0.70 0.75
Shrublands 0.60 0.75
Forest 0.30 0.00
Barren/Water 0.97 1.00
WRAP Regional Modeling Center
PM10 WB Dust Emission Summary (tpy)2002 Annual 12-km Modeling Results
State Agricultural Grasslands Shrublands Barren TotalAZ 353 1,727 107,849 7,524 117,452CA 18,203 8,173 147,970 15,751 190,096CO 7,647 17,570 154,609 351 180,178ID 7,924 5,657 70,686 866 85,132MT 23,214 80,254 362,561 663 466,693NV 365 2,148 176,439 6,069 185,020NM 4,111 12,950 228,901 12,328 258,290ND 115,017 21,218 61,558 592 198,384OR 12,377 10,709 158,633 3,859 185,579SD 191,557 77,251 248,843 4,073 521,724UT 601 5,880 121,885 21,419 149,786WA 10,903 6,604 78,938 4,520 100,966WY 1,036 57,958 31,989 1,418 92,402WRAP Total 393,306 308,099 1,950,862 79,435 2,731,702
WRAP Regional Modeling Center
2002 Annual WB Dust PM10 Emissions
0
100,000
200,000
300,000
400,000
500,000
600,000
AZ CA CO ID MT NV NM ND OR SD UT WA WY
State
PM
10
(tp
y)
Barren
Shrublands
Grasslands
Agricultural
2002 Annual 12-km Modeling Results
WRAP Regional Modeling Center
2002 Annual WRAP 36-km WB Dust2000 LULC (TFs Applied)
0
100,000
200,000
300,000
400,000
500,000
600,000
700,000 A
L A
R A
Z C
A C
O C
T D
C D
E F
L G
A IA ID IL IN KS
KY
LA
MA
MD
ME
MI
MN
MO
MS
MT
NC
ND
NE
NH
NJ
NM
NV
NY
OH
OK
OR
PA
RI
SC
SD
TN
TX
UT
VA
VT
W WI
W W
Y
States
PM
10
(to
ns
/ye
ar)
Agricultural Grasslands
Shrublands Barren
WRAP Regional Modeling Center
2002 Annual PM10 WB Dust Emissions
WRAP Regional Modeling Center
WRAP Regional Modeling Center
2002 Monthly WB PM10 Dust EmissionsWRAP States
Monthly WB Dust PM10 Emission by Dust Category WRAP States
0
100,000
200,000
300,000
400,000
500,000
600,000
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Month
PM
10
(to
ns
)
Agricultural Grasslands
Shrublands Barren
WRAP Regional Modeling Center
Model Performance Evaluation
• Evaluate reasonableness of WBD Model results– Compare predicted PM dust emissions near IMPROVE monitors with
Observed fine soil and coarse mass
• Evaluate CMAQ model sensitivity to WB PM Dust emissions– Modified CMAQ simulations to track WB Dust emissions separately
– Review modeling results for fine soil and coarse mass
• Evaluate CMAQ model performance with and without WB Dust emissions– Investigate model performance at IMPROE monitors w/ and w/o WB
Dust emissions (time series and scatter plots)
WRAP Regional Modeling Center
Saguaro West, AZ, Coarse MassSAWE(CM vs pm10(-1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(-
1,1)
Em
issi
on
SAWE(CM vs pm10(0,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(0
,1)
Em
issi
on
SAWE(CM vs pm10(1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(1
,1)
Em
issi
on
SAWE(CM vs pm10(-1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(-
1,0)
Em
issi
on
SAWE(CM vs pm10(0,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(0
,0)
Em
issi
on
SAWE(CM vs pm10(1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(1
,0)
Em
issi
on
SAWE(CM vs pm10(-1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(-
1,-1
) E
mis
sion
SAWE(CM vs pm10(0,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(0
,-1)
Em
issi
on
SAWE(CM vs pm10(1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(1
,-1)
Em
issi
on
WRAP Regional Modeling Center
Saguaro West, AZ, SoilSAWE(SOIL vs pm10(-1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(-
1,1)
Em
issi
on
SAWE(SOIL vs pm10(0,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(0
,1)
Em
issi
on
SAWE(SOIL vs pm10(1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(1
,1)
Em
issi
on
SAWE(SOIL vs pm10(-1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(-
1,0)
Em
issi
on
SAWE(SOIL vs pm10(0,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(0
,0)
Em
issi
on
SAWE(SOIL vs pm10(1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(1
,0)
Em
issi
on
SAWE(SOIL vs pm10(-1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(-
1,-1
) E
mis
sion
SAWE(SOIL vs pm10(0,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(0
,-1)
Em
issi
on
SAWE(SOIL vs pm10(1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(1
,-1)
Em
issi
on
WRAP Regional Modeling Center
Salt Creek, NM, Coarse MassSACR(CM vs pm10(-1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(-
1,1)
Em
issi
onSACR(CM vs pm10(0,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(0
,1)
Em
issi
on
SACR(CM vs pm10(1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(1
,1)
Em
issi
on
SACR(CM vs pm10(-1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(-
1,0)
Em
issi
on
SACR(CM vs pm10(0,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(0
,0)
Em
issi
on
SACR(CM vs pm10(1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(1
,0)
Em
issi
on
SACR(CM vs pm10(-1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(-
1,-1
) E
mis
sion
SACR(CM vs pm10(0,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(0
,-1)
Em
issi
on
SACR(CM vs pm10(1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized CM Concentration
Nor
mal
ized
pm
10(1
,-1)
Em
issi
on
WRAP Regional Modeling Center
Salt Creek, NM, SoilSACR(SOIL vs pm10(-1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(-
1,1)
Em
issi
on
SACR(SOIL vs pm10(0,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(0
,1)
Em
issi
on
SACR(SOIL vs pm10(1,1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(1
,1)
Em
issi
on
SACR(SOIL vs pm10(-1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(-
1,0)
Em
issi
on
SACR(SOIL vs pm10(0,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(0
,0)
Em
issi
on
SACR(SOIL vs pm10(1,0))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(1
,0)
Em
issi
on
SACR(SOIL vs pm10(-1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(-
1,-1
) E
mis
sion
SACR(SOIL vs pm10(0,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(0
,-1)
Em
issi
on
SACR(SOIL vs pm10(1,-1))
0%
10%
20%
30%
40%
50%
60%
70%
80%
0% 10% 20% 30% 40% 50% 60% 70% 80%
Normalized SOIL Concentration
Nor
mal
ized
pm
10(1
,-1)
Em
issi
on
WRAP Regional Modeling Center
CMAQ Sensitivity Simulations
WRAP Regional Modeling Center
Model Performance Evaluation
Coarse MassFine Soil
WRAP Regional Modeling Center
Saguaro West, AZ
Fine Soil
Coarse Mass
WRAP Regional Modeling Center
Salt Creek, NMFine Soil
Coarse Mass
WRAP Regional Modeling Center
Badlands, NP
Glacier, NP
WRAP Regional Modeling Center
Grand Canyon, NP
San Gabriel