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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 />

than many earlier ones. Nitrous oxide, and ammonia<br />

emission from animal farming of South, Southeast, and<br />

East Asia, in , was estimated at about . Tg<br />

N O_N and . Tg NH _N, respectively, For providing<br />

spatial distributions of these gases, the emissions of<br />

county and district level were allocated into each<br />

.˚grid by means of weighting by high-resolution land<br />

cover data sets.<br />

Fig. 13 Difference in CO monthly mean total column amounts<br />

between Moshiri /Rikubetsu stations (Hokkaido, Japan)<br />

and Zvenigorod station (near Moscow, Russia) (blue) compared<br />

with calculated contributions from forest fire emissions<br />

(red) and incomplete combustion of wood and oil<br />

products (black).<br />

urements at a tropical rural site in Thailand show<br />

strong seasonal cycles with a peak in the late-dry season<br />

(February-March) and a valley in mid-wet season<br />

(June-August). Analysis of air mass trajectories and<br />

ATSR satellite hot spots data verify that the high O <br />

and CO observed in continental SE Asia are caused<br />

mainly by the regional-scale biomass burning. Longrange<br />

transport of regionally polluted continental air<br />

from East Asia also partly contributes to these high O <br />

and CO levels. Meanwhile, the low O and CO in the<br />

wet season are due to the inflow of clean marine air<br />

masses from the Indian Ocean.<br />

Long-term ozonesonde data (-) for tropospheric<br />

ozone from central Europe and East Asia have<br />

been analyzed using the isentropic backward trajectories.<br />

It was shown that photochemically aged boundary layer<br />

ozone reflects the NOx emission trend in each continent.<br />

We collected data of most of the field studies on<br />

methane emission from rice fields available so far in<br />

mainland China. Based on these region-specific emission<br />

factors and statistical data on rice areas of ,<br />

we estimated CH emission from rice fields during the<br />

rice-growing season (from transplanting to harvest) in<br />

Mainland China to be . Tg yr - , with a range of .<br />

to . Tg CH yr - . This estimate is significantly lower<br />

5. Ecosystem Change <strong>Research</strong> Program<br />

One of the most important research subjects of today<br />

is investigating the influence of climate and environmental<br />

changes such as global warming and desertification<br />

on species distribution and diversities. For this<br />

mission, the objective of the Ecosystem Change<br />

<strong>Research</strong> Program (ECRP) is to research on evaluation<br />

of the influences of climate and environmental changes<br />

on ecosystems and modeling their mechanisms.<br />

Conversely, the influence of ecosystem changes on climate<br />

and the environment are evaluated and their<br />

mechanisms are modeled. Our program consists of the<br />

following four groups, studying environmental dynamics<br />

and conducting research on modeling dynamics.<br />

a. Ecosystem-Atmospheric Interaction Model Group<br />

b. Ecosystem Architecture Model Group<br />

c. Ecosystem Geographical Distribution Model Group<br />

d. <strong>Marine</strong> Biological Process Model Group<br />

In FY , we started the detection of ecosystem<br />

change on land and in the ocean by satellite remote<br />

sensing. ECRP also launched research on the integration<br />

of remote sensing with modeling to improve the<br />

model simulation accuracy.<br />

a. Ecosystem-Atmosphere Interaction Model Group<br />

We have been developing a simulation model of carbon<br />

cycle in land ecosystems (Sim-CYCLE). In<br />

FY, we extended to account for the atmospherebiosphere<br />

exchange of stable carbon isotope composition<br />

(δ C). Global simulation showed average fraction-<br />

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