controlling particulate nitrate pollution in...

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Controlling particulate nitrate pollution in China Shixian Zhai with Daniel J. Jacob*, Xuan Wang, Viral Shah, Ke Li, Jonathan Moch, Kelvin H. Bates, Shaojie Song, Lu Shen, and Yuzhong Zhang from Harvard University Zirui Liu, Tianxue Wen, and Yele Sun, IAP/CAS; Gan Luo and Fangqun Yu, U. at Albany; Litao Wang and Mengyao Qi, Hebei U. of Engineering; Jun Tao, Jinan U.; Ke Gui, CAMS; Honghui Xu, Zhejiang Institute of Meteorological Sciences; Qiang Zhang, Tsinghua U.; Hyun Chul Lee and Hyoungwoo Choi, Samsung; Tianliang Zhao and Hong Liao, NUIST. AGU FALL MEETING 2020: A172-06 LIVE Q&A: Tuesday, 15 December 2020, 04:00 – 05:00 PST Funding: JLAQC and SAMSUNG

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Page 1: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

Controlling particulate nitrate pollution in China

Shixian Zhai

with Daniel J. Jacob*, Xuan Wang, Viral Shah, Ke Li, Jonathan Moch, Kelvin H. Bates, Shaojie Song, Lu Shen, and Yuzhong Zhang from Harvard University

Zirui Liu, Tianxue Wen, and Yele Sun, IAP/CAS; Gan Luo and Fangqun Yu, U. at Albany; Litao Wang and Mengyao Qi, Hebei U. of Engineering; Jun Tao, Jinan U.; Ke Gui, CAMS; Honghui Xu, Zhejiang Institute of Meteorological Sciences; Qiang Zhang, Tsinghua U.; Hyun Chul Lee and Hyoungwoo Choi, Samsung; Tianliang Zhao and Hong Liao, NUIST.

AGU FALL MEETING 2020: A172-06

LIVE Q&A: Tuesday, 15 December 2020, 04:00 – 05:00 PST

Funding: JLAQC and SAMSUNG

Page 2: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

China’s rigorous Clean Air Action has greatly improved its PM2.5 air quality

Zheng et al., ACP, 2018

MEIC emission inventory

Zhai et al., ACP, 2019

2013 2018

Observed annual mean PM2.5

30~50%108 → 55

67 → 40

47 → 3171 → 40

Air quality standard:35μg m-3(Phase I), 10μg m-3(WHO).

China Clean Air action

↓59%

↓33%↓23%↓21%

BC: ↓28%OC: ↓32%

Page 3: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

NitrateSulfateAmmoniumOABCChlorineOthers

2011

2012

2013

2014

2015

2016

2017

2018

Concentration, µg m-3

Observations in winter & autumn at Beijing

Particulate nitrate didn’t decrease with the decrease of NOx emissions

From National Air Pollution Prevention and Control Center (provided by PKU)

120

80

40

40

40

40

0

Percentage

2011

2012

2013

2014

2015

2016

2017

2018

0%

30%

60%

90%40

40

40

40

Page 4: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

Tota

l PM

2.5

PM1

nitra

te

2014-2015 2016-2017 2017-2018 2018-2019a

b

Mean observed: 90 μg m-3

Model: 71 μg m-310078

4238

5257

Mean observed: 9 μg m-3

Model: 7 μg m-31810

55

109

μg m-3

Mass ratio of

PM1 nitrate / total PM

2.5

Particulate nitrate on winter haze days has increasedBeijing wintertime data: nitrate is now the most important component of PM2.5

Observation data are provided by Yele Sun from IAP/CASZhai et al., submitted

Page 5: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

Standard simulation Fixed meteorology

Nitrate in winter would have increased were it not for favorable meteorologyNitrate under winter haze conditions increased by > 30%

Chemical drivers of particulate nitrate trends:

Model results overNorth China Plain

Zhai et al., submitted

Page 6: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

Faster conversion from NOx to nitrate

NO3T

Nonlinearity:

NOx-limited: NOx ↓à HOx ↓à NOx lifetime ↑(slower NOx to nitrate)

NOx-saturated: NOx ↓à HOx ↑à NOx lifetime ↓(faster NOx to nitrate)

Diagram for nitrate production

Faster NOx to nitrate conversion rate in winter.

(shorter NOx lifetime)

Shah et al., ACP, 2019

NOx trends over China

NO3T = NO3

- + HNO3

Daytime

Nighttime

(from Viral Shah)

Page 7: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

Faster conversion from NOx to nitrate is insufficient to explain the increase of nitrate under winter haze conditions

Winter hazeWinterSummer

NOx lifetime, hours NO3T production, µg m-3 hr-1

Zhai et al., submitted

Page 8: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

Increase in NO3T lifetime against deposition is the dominant factor

explaining the lack response of nitrate to NOx emission controlsThe lifetime of NO3

T is controlled by the small fraction present as HNO3(g).

[NO3-]/[NO3

T] ratio NO3T lifetime, hours

SO2 ↓ NH3 ↑NO3

- HNO3(g)

Surface

x10 ≈Slow Fast

deposition

Vice versa: decreasing NH3 emissions should be able to decrease NO3

T total nitrate lifetime.Zhai et al., submitted

In large excess

Page 9: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

NH3 is the most effective lever for PM2.5 nitrate controlResponse of particulate nitrate

to emission controls

Zhai et al., submitted

Ø Reducing NH3 emissions by any increment is beneficial.

Ø Reducing NOx emissions drives a decrease in NOx lifetime which offsets the decrease in NO3

T

production.

SO2 NOx VOCs NH3NOx + VOCs + NH3

Page 10: Controlling particulate nitrate pollution in Chinaacmg.seas.harvard.edu/presentations/2021/szhaiAGU2020.pdfand has increased during winter haze pollution events in the North China

Conclusions

1. Stringent emission controls have decreased PM2.5 concentrations in China by 30-50% over the 2013-2018 period.

2. Particulate nitrate has not responded effectively to emission controls on NOx, and has increased during winter haze pollution events in the North China Plain.

3. The dominant factor driving the observed nitrate trends is the increase in NO3T

lifetime against deposition as the particulate fraction of NO3T approaches unity.

4. Decreasing wintertime ammonia emissions would be most effective for decreasing particulate nitrate in China.

Welcome to my LIVE Q&A SESSION: A172-06 Tuesday, 15 December 2020, 04:00 – 05:00 PST

Contact: Shixian Zhai ([email protected])