2007 Annual Report - jamstec japan agency for marine-earth ...
2007 Annual Report - jamstec japan agency for marine-earth ...
2007 Annual Report - jamstec japan agency for marine-earth ...
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production in June. Even in July inflow transport contributes<br />
about a half of in situ photochemical production at Mt. Huang.<br />
The ozone pollution in the Central East China has thus been<br />
characterized in this study.<br />
c. Data analysis of intensive field campaign at Mt. Tai in China<br />
As a part of the project " Spatial and temporal variability<br />
and climate impact of ozone and black carbon in Asia" granted<br />
by Global Environmental Research Fund, Ministry of the<br />
Fig. 6 Concentrations of BC and EC measured y several different<br />
types of instruments during the Mt. Tai campaign in June 2006.<br />
Environment, Japan, a month-long intensive field campaign at<br />
Mt. Tai has been conducted in June 2006, and data analysis has<br />
been made in <strong>2007</strong>. In addition to the JAMSTEC scientists,<br />
those in National Institute <strong>for</strong> Environmental Studies, Tokyo<br />
Metropolitan University, Hokkaido University, Institute of<br />
Atmospheric Physics Chinese Academy of Sciences, and<br />
Fudan University have joined this campaign.<br />
Figsures 6 and 7 show the time series of the concentrations<br />
of BC/EC and O 3 /CO/NOx/NOy obtained during the campaign,<br />
respectively. From Fig. 6 average concentration of BC<br />
PM2.5 by MAAP is obtained at 3.7g/m -3 maximum<br />
hourly averaged value is 40.8g/m -3 , and those of O 3 , CO,<br />
Fig. 7 Concentrations of O 3 , CO, and MAAP-BC observed in the Mt.<br />
Tai campaign in June 2006.<br />
and NOx and NOy are obtained at 82, 560, 1.1 and 6.7 ppbv,<br />
respectively, from Figure7. Very high concentrations of BC,<br />
CO and NOx on June 5-7, and 11-13 as seen in Figures 6 and 7<br />
hatched period are due to biomass burning after harvesting<br />
of spring wheat, and it appeared that such agricultural waist<br />
burning has significant impact on ozone and aerosol pollution<br />
in the North China Plain in June. Further, diurnal variation seen<br />
particularly in the later half of June in Figure6, is due to the<br />
diurnal variation of mixing layer height.<br />
From the analysis of the observational data, radiative <strong>for</strong>cing<br />
of O 3 and BC at Mt. Tai in June has been estimated as<br />
shown in Table 2. The radiative <strong>for</strong>cing of O 3 and BC at the<br />
tropopause are 0.64 and 2.75 W/m 2 . It is concluded that they<br />
exert large radiative impact regionally as compared to longlived<br />
greenhouse gases.<br />
Table 2 Radiative <strong>for</strong>cing of O 3 and BC at Mt. Tai in June calculated<br />
from the observational data<br />
d. Intercomparison of inverse calculation of CO 2 flux by<br />
FRCGC-NIES and JMA models<br />
In this program, source-sink flux estimation of CO 2 with<br />
the highest spatial segmentation globally 64 by high resolution<br />
1 1 FRCGC/NIES transport model has been<br />
conducted with the use of Earth Simulator. In this fiscal year, as<br />
a part of Earth Simulator Project, Intercomparison between<br />
JMA and FRCGC/NIES models has been made under the same<br />
conditions collaborating with Japan Meteorological Agency.<br />
Figure 8 compares the 24-regional segregation so far used in the<br />
international intercomparison program TransCom3, and<br />
the 64-segregation used in the present study. Among observational<br />
data at surface by ground-based and shipboard measurements<br />
and in the upper troposphere by aircrafts, only those<br />
whose difference from the <strong>for</strong>ward model simulation is less<br />
than 2 ppmv were used <strong>for</strong> the inverse modeling.