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1
Seasonal Modeling: Comparison of Phases 1 and 2
Emission inputs to CMAQ
Shaheen R. Tonse
Lawrence Berkeley National Laboratory
CCOS Technical Committee MeetingSacramento, 29th November, 2006
2
Gridded Emission Comparisons
• Compare the sums and temporal profiles of Area, Biogenic, Motor Vehicle and Point sources
• Former emissions: Obtained Fall 2004 for Phase 1. For reference purposes: CCAQS4k_Ep000729_AR_rf934_V042104_R0003_SAPRCV5_CAMX
• New emissions: Obtained Summer 2006 for Phase 2. For reference purposes: cc.A20000729_00.RF964.arb.20060629.CAMX.SAPRC_V1
(Claire Agnoux, visiting student from France, in summer 2006)
3
Gridded Emission Comparisons
• Emissions summed by hour over:• SARMAP domain (96 ×117 grid) for area, biogenic and motor
vehicle
• CCOS domain (190 × 190 grid) for point sources emissions.
• Sat July 29th to Wed August 2nd 2000 (Days 211 to 215)
• Times on plots are in PDT
• Units are either moles/hour or moles/s
4
SARMAP domain within CCOS domain
CCOS4km res.190 x 190
SARMAP4km res.96 x 117
Vertical resolution: 27 layers. Lowest layers: 20m thickUppermost layer at P=100 mbar, (16km) is 2km thick
5
NOx emissions by category(next 3 figures from Phase 1 report)
6
VOC emissions by category
7
CO emissions by category
8
Area Emissions
Area emissions: NOx
0.0E+00
4.0E+05
8.0E+05
1.2E+06
1.6E+06
2.0E+06
0 12 0 12 0 12 0 12 0 12 0 12
hour/day
sum
ove
r th
e S
AR
MA
P d
om
ain
(m
ole
s/h
ou
r)
former emissions new emissions
211 212 213 214 215 216
9
Area Emissions
Area emissions: VOC
0.0E+00
2.0E+05
4.0E+05
6.0E+05
8.0E+05
1.0E+06
1.2E+06
0 12 0 12 0 12 0 12 0 12 0 12
hour/day
sum
ove
r th
e S
AR
MA
P d
om
ain
(m
ole
s/h
ou
r)
former emissions new emissions
211 212 213 214 215 216
10
Area Emissions
Double counting of fires intwo counties.
11
Motor Vehicle Emissions
MV emissions: NOx
0.0E+00
4.0E+05
8.0E+05
1.2E+06
1.6E+06
2.0E+06
0 12 0 12 0 12 0 12 0 12
hours/day
sum
ove
r S
AR
MA
P d
om
ain
(m
ole
s/h
ou
r)
former emissions new emissions new-light duty new-heavy duty
211
12
Biogenic Emissions
Biogenic emissions: VOC
0.0E+00
1.0E+06
2.0E+06
3.0E+06
4.0E+06
0 12 0 12 0 12 0 12 0 12 0 12
hour/day
sum
ove
r S
AR
MA
P d
om
ain
(m
ol/
ho
ur)
former emissions new emissions
13
Point Emissions
Point sources: VOC
0.00E+00
5.00E+04
1.00E+05
1.50E+05
2.00E+05
2.50E+05
0 12 0 12 0 12 0 12 0 12 0 12
day/hour
sum
ove
r C
CO
S d
om
ain
(m
ole
s/h
r)
former emissions new emissions
213 214 215212211 216
14
Fire Emissions
Xiao Ling Mao (visiting researcher at) and Ling Jin (UCB) compiled fires during episode, by location, duration, acreage.
Summary of sensitivity study to fire emissions:•Very high local influence on ozone and its precursor concentrations.
•At upper layers large percentage change in O3 and very concentrated effects•More scattered longer-lasting effects at surface layer
16
Summary of comparisons
Area: Wildfires need to be removed from Tuolumne and Northern Fresno counties
Biogenic: VOC emissions have more than doubled in the new emissions. NOx emissions are zero
Motor Vehicle: Good improvement in weekend NOx time profile. We do not see any obvious problems.
Point: VOCs are down by half in the new inventory
Fire: LBNL can provide useful input to improve the fire inventory
17
A Timing and Scalability Analysis of the Parallel
Performance of CMAQ v4.5 on a Beowulf Linux Cluster
Shaheen Tonse Lawrence Berkeley National Laboratory
Berkeley, CA, USA.
18
Parallel Performance
In general, for parallel codes, improvement in performance scales worse than linearly with number of PEs.
1. Parts of the code simply not parallelizable. Execute redundantly on all the PEs
2. Load imbalance between PEs: those with lighter loads wait for others until they have finished
3. Increased inter-PE communication costs relative to actual computation
4. Latency: Operations whose cost is dominated by startup costs eg. disk file accesses
19
Method
• Inserted timing calls into CMAQ to measure time spent in various portions of code.
• Most timing calls placed in the scientific processes subroutine (SCIPROC) or its daughter subroutines, which calculate the chemistry, horizontal/vertical diffusion, and horizontal/vertical advection.
• Measurement of times spent for pure calculation, inter-PE communication, and disk access.
Single PE Benchmark Times
Module Name
SMVGear time in
seconds(%)
EBI time in
seconds(%)
CHEM 238K (94%) 7K (32%)
HADV 7K (2.7%) 7K (33%)
HDIFF 634 (-) 633 (2.7%)
VDIF 7K (2.7%) 7K (29%)
ZADV 733 (-) 733 (3%)
(Modules) 253K 23K
SMVGear: dominated by CHEM only
EBI: HADV, CHEM and VDIF all contribute
EBI Parallel Performance
HADV: scales poorly and expensive
CHEM: scales ~100% cost mid-level
VDIF: scale and cost both mid-level
HDIF: scales poorly but cheap
ZADV: scales ~100% and cheap
SMVGear Parallel Performance
# PE Time (s)Scalability
(%) Imbalance CHEM (%)
1 255K 100 ---
4 70K 91 11
9 33K 86 16
18 18K 78 20
25 14K 73 20
• Imbalance even for 25PEs is ~20%. Scalability of the overall code good even for 25 PEs.•Chemistry imbalance accounts for much of the scalability loss (since chemistry dominates). (Also note: 100-Scalability Imbalance)