The levels of sulfites in wooden chopsticks were analyzed using two different methods, distillation- alkali titration and ion chromatography. According to the two methods, Sulfur dioxide (SO₂) was validated by 0.6 and 0.2 μg/ml of limit of detection (LOD), 1.8 and 0.5 μg/ml of limit of quantification, (LOQ) and a R² > 0.998 for linearity, respectively. The recoveries of SO₂ from food simulants spiked ar levels of 100 ppm were 70.2-100.2%. 158 samples of wooden chopsticks were monitored the migrated amounts of sulfites. Sulfites were detected in 30 samples in ranged of 0.6 to 15.5 ppm. Maximum migration level, 15.5 ppm of sulfites was considered giving no harmful effect to human since it was reached 5.5% of estimated SML.

The re-emission of mercury (Hg), as a consequence of the formation and dissociation of the unstable complex HgSO3, is a problem encountered in flue gas desulphurization (FGD) treatment in coal-fired power plants. A model following a pseudo-second-order rate law for Hg2+ reduction was derived as a function of [SO32-], [H+] and temperature and fitted with experimentally obtained data to generate kinetic rate values of (0.120 ± 0.04, 0.847 ± 0.07, 1.35 ± 0.4) mM-1 for 40°, 60°, and 75℃, respectively. The reduction of Hg2+ increases with a temperature increase but shows an inverse relationship with proton concentration. Plotting the model-fitted kinetic rate constants yields ΔH = 61.7 ± 1.82 kJ mol-1, which is in good agreement with literature values for the formation of Hg0 by SO32-. The model could be used to better understand the overall Hg2+ re-emission by SO32- happening in aquatic systems such as FGD wastewaters.

2005년 3월부터 10월까지 과채류 152건을 대상으로 아황산염류의 자연함유량과 인위적인 사용실태를 비교하기 위하여 모니어-윌리암스 변법을 사용하여 이산화황의 함유량을 분석하였다. 가공하지 않은 14품목 42건에 대한 이산화황 분석결과 평균검출범위는 이었으며, 각 품목별 평균으로는 무가 8.97 mg/kg으로 가장 높았고 양파가 8.04 mg/kg 순으로 조사되었다. 가공한 23품목 110 건에 대한 이산화황 평균분석결과 검출범위는 이었으며,

To investigate the effects of sulfite on the chloroplast development, etiolated barley seedlings were treated with 100 mM sulfite solution every 3 hour by spraying during 96 hours greening period. The effects were determined by chlorophyll a, b and carotenoids contents, photosynthetic electron transport activity, chlorophyll fluorescence yield and fluorescence quenching parameters. The contents of chlorophyll a and carotenoids were decreased than that of control by treatment of sulfite over 48 hours greening. PS Ⅱ is more sensitive to sulfite than PS I is. And by the addition of DPC to the chloroplasts of the barley seedling treated with sulfite, the photoreduction of DCPIP was not recovered. In greening with sulfite treated barley leaves, Fo, Fv and Fv/Fm ratio were decreased with little difference from that of control. But qP, qNP and qR were lowed in comparison with those of controls whereas qE was slightly higher than that of control. Especially, it is interesting that qR was decreased markedly compared to that of control. The results in the change of PS I activity, Fv/Fm and qP suggest that the site of inhibition by sulfite is carbon dioxide reduction cycle.