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Marine Ecosystems Research Department - jamstec japan agency ...

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Japan <strong>Marine</strong> Science and Technology Center<br />

Frontier <strong>Research</strong> System for Global Change<br />

lived greenhouse gasses (CO , CH , N O, etc.), shortlived<br />

reactive gaseous species (O , CO, NOx, VOC,<br />

SO , OH, HO , etc.) and aerosols.<br />

As a part of chemical transport model development,<br />

regional-scale model and higher resolution global<br />

model using the TRACE-P aircraft campaign data have<br />

been successfully verified, which opened the way to<br />

further development of process study. Also, a parallel<br />

version of higher resolution atmospheric transport<br />

model for analysis of sources and sinks of greenhouse<br />

gases has been developed, enabling the use of the Earth<br />

Simulator for future studies.<br />

OH and HO radical field in North and Southeast<br />

Asia has been obtained for the first time by using a<br />

regional chemical transport model. Methane emission<br />

from rice fields in mainland China has been estimated<br />

by using the regional specific emission factors based<br />

on thoroughly compiled datasets. The obtained value<br />

. Tg yr - is substantially lower than the previously<br />

reported values. This lower value is recommended to<br />

be used in future studies.<br />

a. Global Chemical Transport Modeling Group<br />

Using the FRSGC/UCI CTM in conjunction with aircraft<br />

observations from the NASA TRACE-P campaign,<br />

it has been demonstrated that current global<br />

chemical transport models run at high resolution can<br />

successfully reproduce the regional distribution of<br />

ozone over the western Pacific in springtime, including<br />

the high variability induced by the passage of frontal<br />

systems, photochemical production, and intrusion of air<br />

from the stratosphere. In addition, it has been shown<br />

that the chemical production of ozone can be simulated<br />

well compared with observations, and hence that this<br />

type of model is capable of addressing the global implications<br />

for air quality and climate of regional emissions<br />

of ozone precursors with high reliability. Fig. compares<br />

the net production rate of ozone along the flight<br />

tracks of the DC- and P-B aircraft over the western<br />

Pacific during the TRACE-P campaign. The model<br />

reproduced the observed zonal mean vertical profile of<br />

net ozone production successfully.<br />

We participated in the NASDA PEACE-A/B with a<br />

global chemical transport model, CHASER, based on<br />

CCSR/NIES AGCM. The chemical weather forecast<br />

by the model well captured the transport of air pollutant<br />

accompanying with a cold front.<br />

The reaction scheme of SEAMAC is updated to<br />

incorporate an explicit description of the degradation<br />

of up to C hydrocarbons including ethene, propene,<br />

and acetylene. Model calculations evaluated the effect<br />

of these compounds on halogen chemistry in the<br />

marine boundary layer.<br />

b. Regional Chemical Transport Modeling Group<br />

The CMAQ/RAMS model was applied to study the<br />

temporal and spatial distributions of OH and HO in<br />

the springtime of in East Asia when the NASA<br />

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Altitude /km<br />

Net Ozone Production (FRSGC CTM)<br />

2<br />

-2<br />

4<br />

2<br />

-8<br />

2<br />

10N 15N 20N 25N 30N 35N 40N 45N<br />

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Altitude /km<br />

Net Ozone Production (Observations)<br />

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4 0 4<br />

-2<br />

2-2<br />

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8 32<br />

10N 15N 20N 25N 30N 35N 40N 45N<br />

-32 -16 -8 -4 -2 0 2 4 8 16 32<br />

1e5 mol / cm 3 / s<br />

Fig.11 Net production rate of ozone along the flight tracks of the DC-8 and P-3B aircraft<br />

over the western Pacific during the TRACE-P campaign, showing boundary layer<br />

production over Northeast Asia, destruction over marine regions, and slow production<br />

in the upper troposphere.<br />

129

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