Abstract.With the rapid development of the economy, the sulfur dioxide (SO 2 ) emission from China since 2000 is of increasing concern. In this study, we estimate the annual SO 2 emission in China after 2000 using a technology-based methodology specifically for China. From 2000 to 2006, total SO 2 emission in China increased by 53%, from 21.7 Tg to 33.2 Tg, at an annual growth rate of 7.3%. Emissions from power plants are the main sources of SO 2 in China and they increased from 10.6 Tg to 18.6 Tg in the same period. Geographically, emission from north China increased by 85%, whereas that from the south increased by only 28%. The emission growth rate slowed around 2005, and emissions began to decrease after 2006 mainly due to the wide application of flue-gas desulfurization (FGD) devices in power plants in response to a new policy of China's government. This paper shows that the trend of estimated SO 2 emission in China is consistent with the trends of SO 2 concentration and acid rain pH and frequency in China, as well as with the increasing trends of background SO 2 and sulfate concentration in East Asia. A longitudinal gradient in the percentage change of urban SO 2 concentration in Japan is found during 2000-2007, indicating that the decrease of urban SO 2 is lower in areas close to the Asian continent. This implies that the transport of increasing SO 2 from the Asian continent partially counteracts the local reduction of SO 2 emission downwind. The aerosol optical depth (AOD) products of Moderate ResoluCorrespondence to: Z. Lu (zlu@anl.gov) tion Imaging Spectroradiometer (MODIS) are found to be highly correlated with the surface solar radiation (SSR) measurements in East Asia. Using MODIS AOD data as a surrogate of SSR, we found that China and East Asia excluding Japan underwent a continuous dimming after 2000, which is in line with the dramatic increase in SO 2 emission in East Asia. The trends of AOD from both satellite retrievals and model over East Asia are also consistent with the trend of SO 2 emission in China, especially during the second half of the year, when sulfur contributes the largest fraction of AOD. The arrested growth in SO 2 emissions since 2006 is also reflected in the decreasing trends of SO 2 and SO 2− 4 concentrations, acid rain pH values and frequencies, and AOD over East Asia.