Comprehensive model evaluation of PM2.5 species over Japan:

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Comprehensive model evaluation of PM2.5 species over Japan: -Comparison among AERO5, AERO6, and AERO6-VBS models Yu Morino, Tatsuya Nagashima, Seiji Sugata, Kei Sato, Kiyoshi Tanabe, Akinori Takami, Hiroshi Tanimoto, and Toshimasa Ohara National Institute for Environmental Studies, Japan ーContentsー  1.Introduction - PM2.5 in Japan / PM2.5 modelling  2.Methodology - Chemical transport models / Observations  3.Results - Model evaluations  4.Summary ーAcknowledgementー Funds: Environment Research and Technology Development Fund (5-1408, S12-1, 5B-1101) Technical support: K. Suto and T. Noguchi (NIES) The 13th Annual CMAS Conference, October 28, 2014

PM2.5 in Japan PM2.5 environmental standard in Japan (Sept. 2009 ‒) 1. Introduction PM2.5 in Japan Ministry of Environment (2013) PM2.5 standard was not attained in western Japan and Tokyo Metropolitan Area. PM2.5 env. standard ○:Attained ■▲:Not-attained Spatial variations in 2012 Temporal variations during 2001-2010 Attained Urban (N=12) Rural (N=5) Roadside (N=16) PM2.5 concentrations PM2.5 environmental standard in Japan (Sept. 2009 ‒) Annual mean: 15 μg m-3 Daily mean: 35 μg m-3 Unattained 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 Ministry of Environment (2012)

PM2.5 modelling in Tokyo Metropolitan Area (in summer 2007) 1. Introduction PM2.5 modelling in Tokyo Metropolitan Area (in summer 2007) Fossil-SOA: Underestimation by a factor of 6-8 Model evaluation of fossil- and biogenic SOA (Morino et al., ES&T, 2010) (CMAQ–MADRID was used.) Biogenic-SOA: Underestimation by a factor of 1.5 - 2 Model intercomparison of PM2.5 species (Morino et al., JSAE, 2010) (CMAQ v4.7.1 and CMAQ 4.6 were used.) Organic aerosol S1: Komae, S2: Kisai, S3: Maebashi, S4: Tsukuba All models significantly underestimated OA.

Intercomparison of SOA models in TMA (in summer 2004) 1. Introduction Intercomparison of SOA models in TMA (in summer 2004) MCM, CACM-MADRID: Explicitly simulate multi-generation oxidation AERO4, AERO5: Yield models Volatility Basis Set (VBS): Grouping of SVOC and IVOC based on volatility Obs S=0.193 mgm-3/ppbv VBS S=0.130 CACM S=0.016 Others S=0.003-0.011   #Gas # Reaction Aerosol models MCM v3.2 5731 16933 Pankow CACM -MADRID2 366 MADRID2 SAPRC99 -AERO4 79 214 AERO4 -AERO5 88 224 AERO5 -VBS 92 214#1 VBS #1: exclude aging reactions    from CMAQ-MADRID CMAQ v4.6 CMAQ v4.7.1 (Morino et al., JGR, in revisions)

Background of PM2.5 modelling in Japan 1. Introduction Background of PM2.5 modelling in Japan SOA models: OA concentrations were largely underestimated by yield and mechanical models in TMA, Japan. VBS model better reproduced SOA in TMA. Limitation of observational data: Simultaneous measurement of PM2.5 chemical composition were limited in Japan. → Model evaluation of PM2.5 species were spatially and temporally limited. Simultaneous measurements of PM2.5 species over Japan were conducted in 2012. Objectives of this study Model performance of PM2.5 chemical composition were evaluated using the observational data over Japan in 2012. Results of three simulation models, including the VBS model, were compared.

Chemical transport models 2. Methodology Chemical transport models Three versions of CMAQ Models Chemical Modules Aerosol modules ① CMAQ v4.7.1 SAPRC99 AERO5 ② CMAQ v5.0.2 CB05 AERO6 ③ AERO6VBS Global-scale CTM MIROC-ESM-CHEM Δx = 300 km Regional-scale CTM WRF/CMAQ Δx = 60km Δx = 15km Setups of emission data Target Emission data Spatial resol. Anthropogenic (Japan) JATOP ~1km (vehicles) ~10km (others) (Easi Asia) REAS v2.1 0.25° Biomass burning GFED v3.1 0.5° Volcano AEROCOM/JMA Points Biogenic VOC MEGAN v2.10 ~0.04°

SOA models ー yield models 2. Methodology SOA models ー yield models AERO5 PNCOM POC aging AERO6 Carlton_10EST_CMAQ.pdf AERO6 Carlton et al., 2010

SOA models ー Volatility basis-set (VBS) model 2. Methodology SOA models ー Volatility basis-set (VBS) model VBS model SOA (I/S) aging SVOC1 SVOC2 SVOC3 cond./ evapo. emis. Yield model POA Merit 1 emis. Emission sources SVOC3 aging SVOC2 cond./ evapo. emis. oxidation Merit 2 SVOC1 VOC cond./ evapo. SOA (V) Merit 1: Merit 2: Simulate primary emissions and oxidation (aging) of SVOC/IVOC (semi-/intermediate- VOC) Simulate aging processes of oxidation products from VOCs

Observations of PM2.5 species in 2012 2. Methodology Observations of PM2.5 species in 2012 ■Periods:  -Winter: Jan 9 – 20  -Spring: May 6 – 12  -Summer: Jul 24 – Aug 1 ■Points ■Sampling duration: 6 h or 12 h ■Target species  -Ion (SO42–, NO3–, NH4+): IC  -Carbon (EC and OC) : TOT (IMPROVE protocol) Remote Urban/rural Kyusyu #1:Tsushima #2:Dazaifu Chugoku #3:Oki #4:Matsue Kinki #5:Kyotango #6: Osaka #7:Otsu Chubu #8:Tateyama #11:Sadoseki #9:Toyama #10:Niigata Hokkaido #13:Rishiri #12:Sapporo

Temporal variations of PM2.5 species (winter) 3. Results Temporal variations of PM2.5 species (winter) #6 Urban ( Osaka) #7 Urban (Shiga) #5 Rural (Kyotango) SO42– NO3– NH4+ EC OA #6: Osaka #7: Shiga #5: Kyotango

Temporal variations of PM2.5 species (winter) 3. Results Temporal variations of PM2.5 species (winter) #6 Urban ( Osaka) #7 Urban (Shiga) #5 Rural (Kyotango) SO42– ・Largely underestimated both in urban and remote areas. NO3– ・Overestimated at all sites. ・Better reproduced when Vd of HNO3&NH3 were enhanced (×5). (Neuman et al., 2004; Shimadera et al., 2014) NH4+ ・Combined trends of SO42– and NO3–. EC ・Well reproduced at the urban site and underestimated at the rural site. OA ・Large underestimation ・Similar results by the all three models.

Temporal variations of PM2.5 species (summer) 3. Results Temporal variations of PM2.5 species (summer) #6 Urban ( Osaka) #7 Urban (Shiga) #5 Rural (Kyotango) SO42– ・Generally reproduced, though some peaks were underestimated. NO3– ・Low NO3– was reproduced. NH4+ ・Combined trends of SO42– and NO3–. EC ・Reproduced at the urban site and underestimated at the rural site. OA ・Underestimated by the yield models. ・VBS better reproduced the observation. VBS Obs AERO5 AERO6

Comparison of observed and simulated PM2.5 species 3. Results Winter Spring Summer SO42– NO3– NH4+ EC OA Urban/rural Remote Vd×5 Model VBS AERO5 AERO6 Observed

Comparison of observed and simulated PM2.5 species 3. Results Winter Spring Summer SO42– ・Underestimated in winter and spring. ・Well reproduced in summer. NO3– ・Overestimated in winter and spring. ・Better reproduced when we enhance Vd (×5) of HNO3&NH3. NH4+ ・Combined characteristics of SO42– and NO3–. EC ・Well reproduced (with some variability). OA ・Underestimated over the three seasons ・Better reproduced by the VBS. Model VBS AERO5 AERO6 Observed

Simulated spatial distributions of organic aerosol 3. Results Winter (Jan.) Spring (May) Summer (Jul.) CMAQ v4.7.1 SAPRC99-AERO5 OA (μg m-3) CMAQ v5.0.2 CB05-AERO6 OA (μg m-3) CMAQ v5.0.2 CB05-AERO6VBS OA (μg m-3) In spring and summer, AERO6VBS simulated the highest OA over Japan.

Simulated spatial distributions of organic aerosol 3. Results Winter (Jan.) Spring (May) Summer (Jul.) AERO6VBS–AERO5 AERO6VBS AERO6VBS–AERO6 AERO6VBS Ratio CMAQ v5.0.2 CB05-AERO6VBS OA (μg m-3) In spring and summer, AERO6VBS simulated the highest OA over Japan.

Simulated average OA over Japan 3. Results OA concentrations (μg m–3) Winter (Jan.) Spring (May) Summer (Jul.) High OA concentrations by the AERO6VBS model are due to high ASOA concentrations.

Summary Performance of three simulation models on PM2.5 species were evaluated over Japan in 2012. Concentrations of SO42– , NO3–, and NH4+ were well reproduced by the all models in summer, while SO42– was underestimated NO3– was overestimated in winter and spring. OA concentrations were underestimated by all the models in winter and spring. OA concentrations were largely underestimated by AERO5 and AERO6 summer, and better reproduced by AERO6-VBS because higher ASOA was simulated by AERO6-VBS.

Uncertainty analysis of VBS SOA yields SVOC emission profiles AERO6VBS Tsimpidi Anthro. BB Nonvolatile 0.4 0.27 C*=10^(-2) 0.03 C*=10^(-1) 0.06 C*=10^(0) 0.26 0.09 C*=10^(1) 0.40 0.42 0.14 C*=10^(2) 0.51 0.54 0.18 C*=10^(3) 1.43 1.50 0.30 C*=10^(4) C*=10^(5) 0.50 C*=10^(6) 0.80 SVOC aging reaction rates (cm3/molec/sec) AERO6VBS Tsimpidi k(AVOC +OH) 2×10^(-11) 1×10^(-11) k(BVOC +OH) k(S/IVOC +OH) 4×10^(-11)

Uncertainty analysis of VBS Simulation [SOA]/[Ox] [V-SOA]/[Ox] [SI-SOA]/ [Ox] POA   (μg m-3/ppmv) (μg m-3) Standard 151.3 93.7 57.6 0.27 No aging 1.3 – 0.19 Aging of BVOC 152.6 95.0 Aging rate × 10 503.4 343.9 159.5 0.29 Aging rate ÷ 10 6.4 4.3 2.1 0.20 SVOC of Shrivastava et al. [2011] 290.4 117.7 172.8 1.45 SVOC of Tsimpidi et al. [2010] (low volatility case) 115.8 86.0 29.7 0.60 (high volatility case) 188.3 101.0 87.3 0.28 Nonvolatile POA 89.1 2.36 Nonvolatile POA/no aging 15.5 AERO6VBS 178.0 94.6 83.4 Obs 192.6