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Comparison of Air Quality Forecasts over Korea with CMAQ and CAMx during 2014 Changhan Bae Byeong-Uk Kim 1) Hyuncheol Kim 2,3) Soontae Kim* Ajou University, Dept. of Environmental Engineering, Suwon, Korea, 1) Georgia Environmental Protection Division, Atlanta, GA, 2) NOAA/Air Resources Laboratory, College Park, MD, 3) UMD/Cooperative Institute for Climate and Satellites, College Park, MD AJOU UNIVERSITY, AQRL [email protected]; *[email protected] Introduction Methodology Results 1: Model performance evaluation Results 2: Overall comparison Conclusions Results 3 : Case study Acknowledgement Ensemble method combines the results of several simulations to increase prediction accuracy. As a part of an ensemble air quality forecast system, Community Multi-scale Air Quality (CMAQ) model and Comprehensive Air quality Model with eXtensions (CAMx) were implemented to predict PM concentrations over Northeast Asia. In this study, we compare CMAQ and CAMx performances in terms of PM 10 predictability over Seoul Metropolitan Area (SMA) CCTM CMAQ (v4.7.1) CAMx (v6.1) WRF Version 3.5.1 Foreign Emissions INTEX-B 2006 Domestic Emissions CAPSS 2007 Chemical Mechanism SAPRC 99 Aero module AERO5 CF CMAQ-ready emissions are converted to prepare CAMx-ready emissions. Low-level and elevated emissions are separated for CAMx operations. Major differences are listed as follows: Meteorological data processing: MCIP (CMAQ), WRF2CAMx(CAMx) Aerosol module : AERO5(CMAQ), CF(CAMx) Elevated emission placement: Offline (CMAQ), Inline (CAMx) Grid nesting: One way(CMAQ), Two-way(CAMx) Modeling domains Operation of the forecast system In this study, we compare CMAQ and CAMx performances in terms of PM predictability over SMA the simulated PM 10 show similar daily variation compared to the observations. However, both models under-predicted the observed PM 10 by 30~40%(~15 /) for the annual mean. CAMx generally predicts higher daily average PM 10 than CMAQ. The difference ranges from -20 /to 60 /. CAMx may confine PM10 and its precursor emissions near the surface. Vertical diffusivity(Kz) will be further investigated in near future. Conversion rates would be different in two models. CMAQ & CAMx configuration CAMx predicts ~15 /higher PM 10 concentrations than CMAQ when compared for over sub-region A while ~5 /higher over the SMA. The curtain plots show that CAMx may confine PM 10 and its precursor emissions near the surface. Vertical diffusivity(Kz) will be further investigated in near future. CAMx exhibits higher concentrations for primary pollutants and lower concentrations for secondary pollutants over high emission areas in China. Conversion rates would be different in two models under the emission conditions. For the entire year of 2014, simulated daily PM 10 concentrations were evaluated with the measured concentrations available from the AirKorea surface observation network in the Seoul Metropolitan Area (SMA). Overall, the simulated PM 10 shows similar daily variation compared to the observations. However, both models under-predicted the observed PM 10 by 30~40%(~15 /) for the annual mean. Annual average PM 10 spatial plots CMAQ(PM 10 ) CMAQ(PM 2.5 ) Difference of annual average PM10 concentration (CAMx CMAQ) -20 0 20 40 60 Difference in daily average PM 10 predicted by CAMx and CMAQ CAMx-CMAQ(PM 10 ) (㎍/㎥) CAMx generally predicts higher daily average PM 10 than CMAQ. The difference ranges from -20 /to 60 /. Case1. January, 25, 2014 Case2. March, 15, 2015 PM species mapping table PM 2.5 and species concentration on January Vertical distribution(CAMx) CAMx-CMAQ(NOx) CAMx-CMAQ(SO 2 ) CAMx-CMAQ(Nitrate) CAMx-CMAQ(Sulfate) CAMx-CMAQ(PM 2.5 ) CMAQ CAMx PM 10 PM 2.5 Sulfate ASO4J PSO4 ASO4I Nitrate ANO3J PNO3 ANO3I Ammonium ANH4J PNH4 ANH4I EC AECJ PEC AECI OC AALKJ + AXYL1J + AXYL2J + AXYL3J + ATOL1J +ATOL2J + ATOL3J +ABNZ1J + ABNZ2J + ABNZ3J +ATRP1J + ATRP2J + AISO1J +AISO2J + AISO3J + ASQTJ + AORGCJ +AORGPAJ + AORGPAI +AOLGAJ +AOLGBJ SOA1 + SOA2 + SOA3 + SOA4 + SOA5 + SOA6 + SOA7 + SOPA + SOPB + POA PMFINE A25J PMFINE Sea salt ANAJ + ACLJ + ACLI NA + PCL PMC ACORS + ASOIL + ANAK + ACLK + ASO4K+ NH4K + ANO3K CPRM CCRS Results 4 : forecasts skill score In Case1, CAMx predicts higher PM 10 than CMAQ upwind (Northern China) in previous days. A high-low pressure system brings down CAMx pridicted high PM 10 air plume to the SMA though North Korea. In Case2, CMAQ predicts higher PM 10 , especially for nitrate than CAMx around offshore China. While transported, CMAQ-simulated high PM 10 plume is maintained over Yellow Sea and arrives South Korea. This study was supported by Korean Ministry of Environment, National Institute of Environmental Research, and PM 2.5 research center funded by Ministry of Science, ICT, and Future Planning (MSIP) and National Research Foundation (NSF) of Korea (2014M3C8A5030624). This study was supported by the Korean National Institute of Environmental Research (NIER). A B C D A B C D CAMx CMAQ OBS Mean ( / ) 37.1 31.8 49.6 BIAS ( / ) -12.52 -17.87 IOA 0.8199 0.7618 R 2 0.6285 0.6574 Nitrate (CAMx-CMAQ) 2014. 03. 15. 00KST 06KST 12KST 18KST Sub-region A SMA The forecast system has been operating since January 2014 over Northeast Asia (27-km), Korea (9-km) and over the Seoul Metropolitan area (3-km; SMA). 2014. 01. 25. 00KST 06KST 12KST 18KST PM 10 (CAMx) PM 10 (CAMx-CMAQ) The contingency table Observed violation True False Forecasted violation True a b Forecasted true violation (FTV) False c d Forecasted false violation (FFV) Observed true violation (OTV) Observed false violation (OFV) Total a : HITS - the event was forecast and observed b : FALSE ALARMS - the event was forecast but not observed c : MISSES - the event was not forecast but observed d : CORRECT NEGATIVES - the event was neither forecast not observed CAMx OTV OFV No. of Forecast FTV 14 3 17 FFV 23 312 335 No. of Observation 37 315 CMAQ OTV OFV No. of Forecast FTV 13 0 13 FFV 24 315 339 No. of Observation 37 315 Average forecast accuracy (a.k.a. hit rate) of two models defined as “a/(a+c)” is 45% during high daily PM 10 concentration days when observed daily PM 10 concentrations were over 80 /m 3 .

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Page 1: Comparison of Air Quality Forecasts over Korea with CMAQ ... · ACORS + ASOIL + ANAK + ACLK + ASO4K+ NH4K + ANO3K CPRM CCRS Results 4 : forecasts skill score In Case1, CAMx predicts

Comparison of Air Quality Forecasts over Korea with

CMAQ and CAMx during 2014

Changhan Bae • Byeong-Uk Kim1) • Hyuncheol Kim2,3) • Soontae Kim*

Ajou University, Dept. of Environmental Engineering, Suwon, Korea, 1)Georgia Environmental Protection Division, Atlanta, GA,

2) NOAA/Air Resources Laboratory, College Park, MD, 3) UMD/Cooperative Institute for Climate and Satellites, College Park, MD

AJOU UNIVERSITY, AQRL [email protected]; *[email protected]

Introduction

Methodology

Results 1: Model performance evaluation

Results 2: Overall comparison

Conclusions

Results 3 : Case study

Acknowledgement

Ensemble method combines the results of several

simulations to increase prediction accuracy.

As a part of an ensemble air quality forecast system,

Community Multi-scale Air Quality (CMAQ) model and

Comprehensive Air quality Model with eXtensions (CAMx)

were implemented to predict PM concentrations over

Northeast Asia.

In this study, we compare CMAQ and CAMx performances

in terms of PM10 predictability over Seoul Metropolitan

Area (SMA)

CCTM CMAQ (v4.7.1) CAMx (v6.1)

WRF Version 3.5.1

Foreign Emissions INTEX-B 2006

Domestic Emissions CAPSS 2007

Chemical Mechanism SAPRC 99

Aero module AERO5 CF

CMAQ-ready emissions are converted to prepare CAMx-ready

emissions. Low-level and elevated emissions are separated for

CAMx operations.

Major differences are listed as follows:

Meteorological data processing: MCIP (CMAQ), WRF2CAMx(CAMx)

Aerosol module : AERO5(CMAQ), CF(CAMx)

Elevated emission placement: Offline (CMAQ), Inline (CAMx)

Grid nesting: One way(CMAQ), Two-way(CAMx)

• Modeling domains • Operation of

the forecast system

In this study, we compare CMAQ and CAMx performances in terms of

PM predictability over SMA

the simulated PM10 show similar daily variation compared to the

observations. However, both models under-predicted the observed

PM10 by 30~40%(~15 ㎍/㎥) for the annual mean.

CAMx generally predicts higher daily average PM10 than CMAQ. The

difference ranges from -20 ㎍/㎥ to 60 ㎍/㎥.

CAMx may confine PM10 and its precursor emissions near the surface.

Vertical diffusivity(Kz) will be further investigated in near future.

Conversion rates would be different in two models.

• CMAQ & CAMx configuration

CAMx predicts ~15 ㎍/㎥ higher PM10 concentrations than CMAQ when

compared for over sub-region A while ~5 ㎍/㎥ higher over the SMA.

The curtain plots show that CAMx may confine PM10 and its precursor

emissions near the surface. Vertical diffusivity(Kz) will be further

investigated in near future.

CAMx exhibits higher concentrations for primary pollutants and lower

concentrations for secondary pollutants over high emission areas in China.

Conversion rates would be different in two models under the emission

conditions.

For the entire year of 2014, simulated daily PM10 concentrations were

evaluated with the measured concentrations available from the AirKorea

surface observation network in the Seoul Metropolitan Area (SMA).

Overall, the simulated PM10 shows similar daily variation compared to the

observations. However, both models under-predicted the observed PM10 by

30~40%(~15 ㎍/㎥) for the annual mean.

• Annual average PM10 spatial plots

CMAQ(PM10)

CMAQ(PM2.5)

Difference of annual average PM10 concentration (CAMx – CMAQ)

-20

0

20

40

60

• Difference in daily average PM10 predicted by CAMx and CMAQ

CAMx-CMAQ(PM10)

(㎍/㎥

)

CAMx generally predicts higher daily average PM10 than CMAQ. The

difference ranges from -20 ㎍/㎥ to 60 ㎍/㎥.

• Case1. January, 25, 2014

• Case2. March, 15, 2015

• PM species mapping table

• PM2.5 and species concentration on January

• Vertical distribution(CAMx)

CAMx-CMAQ(NOx)

CAMx-CMAQ(SO2)

CAMx-CMAQ(Nitrate)

CAMx-CMAQ(Sulfate)

CAMx-CMAQ(PM2.5)

CMAQ CAMx

PM10

PM2.5

Sulfate ASO4J

PSO4 ASO4I

Nitrate ANO3J

PNO3 ANO3I

Ammonium ANH4J

PNH4 ANH4I

EC AECJ

PEC AECI

OC

AALKJ + AXYL1J + AXYL2J +

AXYL3J + ATOL1J +ATOL2J +

ATOL3J +ABNZ1J + ABNZ2J +

ABNZ3J +ATRP1J + ATRP2J +

AISO1J +AISO2J + AISO3J + ASQTJ

+ AORGCJ +AORGPAJ +

AORGPAI +AOLGAJ +AOLGBJ

SOA1 + SOA2 +

SOA3 + SOA4 +

SOA5 + SOA6 +

SOA7 + SOPA +

SOPB + POA

PMFINE A25J PMFINE

Sea salt ANAJ + ACLJ + ACLI NA + PCL

PMC ACORS + ASOIL + ANAK + ACLK

+ ASO4K+ NH4K + ANO3K

CPRM

CCRS

Results 4 : forecasts skill score

In Case1, CAMx predicts higher PM10 than CMAQ upwind (Northern

China) in previous days. A high-low pressure system brings down CAMx

pridicted high PM10 air plume to the SMA though North Korea.

In Case2, CMAQ predicts higher PM10, especially for nitrate than CAMx

around offshore China. While transported, CMAQ-simulated high PM10

plume is maintained over Yellow Sea and arrives South Korea.

This study was supported by Korean Ministry of Environment, National Institute of

Environmental Research, and PM2.5 research center funded by Ministry of Science, ICT, and

Future Planning (MSIP) and National Research Foundation (NSF) of Korea

(2014M3C8A5030624).

This study was supported by the Korean National Institute of Environmental Research (NIER).

A B

C D

A B C D

CAMx CMAQ OBS

Mean (㎍/㎥) 37.1 31.8 49.6

BIAS (㎍/㎥) -12.52 -17.87

IOA 0.8199 0.7618

R2 0.6285 0.6574

Nitrate (CAMx-CMAQ)

2014. 03. 15.

00KST

06KST 12KST 18KST

Sub-region A

SMA

The forecast system has been operating since January 2014 over

Northeast Asia (27-km), Korea (9-km) and over the Seoul

Metropolitan area (3-km; SMA).

2014. 01. 25.

00KST 06KST 12KST 18KST

PM10 (CAMx)

PM10 (CAMx-CMAQ)

• The contingency table Observed violation

True False

Forecasted

violation

True a b Forecasted

true violation

(FTV)

False c d Forecasted

false violation

(FFV)

Observed true

violation

(OTV)

Observed false

violation

(OFV)

Total

a : HITS - the event was forecast and observed

b : FALSE ALARMS - the event was forecast but not observed

c : MISSES - the event was not forecast but observed

d : CORRECT NEGATIVES - the event was neither forecast

not observed

CAMx OTV OFV No. of

Forecast

FTV 14 3 17

FFV 23 312 335

No. of

Observation 37 315

CMAQ OTV OFV No. of

Forecast

FTV 13 0 13

FFV 24 315 339

No. of

Observation 37 315

Average forecast accuracy (a.k.a. hit rate) of two models defined

as “a/(a+c)” is 45% during high daily PM10 concentration days

when observed daily PM10 concentrations were over 80 ㎍/m3.