• 펄프종이기술
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• 제44권6호
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• pp.15-20
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• 2012

The effects of sulfur dioxide on paper were investigated since these sulfur compounds could cause damages on cellulose and organic materials in papers. For the reason, exposure ageing tests were performed on traditional Korean paper (Hanji) and two different types of modern paper (acid-free and acid paper) to determine the damage with regard to the optical as well as physicochemical properties according to the varying $SO_2$ concentration. As a result, optical properties were not changed while physical and chemical peoperties were remarkably changed with the exposure period. In the case of pH, $SO_2$ had little impact on the pH of the Hanji and acid-free paper while the pH of acid paper was remarkably decreased. The decrease of the folding endurance of the Hanji was relatively smaller than those of the acid-free and acid paper. The results prove Hanji was more resistant to $SO_2$ than the modern paper in terms of optical, physical and chemical properties. In addition, it was also suggested that $SO_2$ concentration should be kept below 0.01 ppm for the preservation of paper objects.

• 한국대기환경학회지
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• 제12권4호
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• pp.449-457
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• 1996

The main purpose of this study was to investigate sulfur dioxide removal performance of flue gas desulfurization system utilizing a Spray Absorption/Drying Reactor. In this system, the size of droplets was considered the most significant factor and tested using a PDA system. Lime slurry flow rate, operating temperature, calcium/sulfur (Ca/S) ratio and applied air pressure were selected as major operation variables and tested/analyzed in terms of system performance. The results are as follows. 1. The $SO_2$ removal efficiencies were 49%, 74%, 85% for Ca$(OH)_2$ slurry flow rate of 10, 20, 30 ml/min, which implies that the increase of slurry flow rate improves removal efficiency. The optimum slurry flow rate in this study was, however, considered 20 ml/min because of constraints of system troubles and absorbent utilization. 2. As Ca/S ratio increased, $SO_2$ removal efficiency was observed to increase. 3. As air pressure, at the atomizing nozzole, increased from 3 to 5 $kg/cm^2, SO_2$ removal efficiency increased from 74% to 80%, because of droplet size reduction due to pressure increase during atomizing process and the increase of surface area, helping mass transfer between gas and liquid phase.

• 동의생리병리학회지
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• 제22권4호
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• pp.948-953
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• 2008

The purpose of this study was to analyze harmful heavy metals, sulfur dioxide and residual pesticides in 27 kinds of oriental medical materials. This study was carried out on 27 samples of oriental medical materials. The GC-ECD(Varian, CP-3800) was used to analyze residual pesticides. ICP-OES(Varian, Vista-MPX) was used to analyze lead, arsenic, cadmium. Mercury was analyzed by amalgamation method. A modified Monier-Williams method was used to analyze sulfur dioxide. Arsenic was detected less than 3(mg/kg) in 14 samples and was not detected 13 samples. Lead was detected less than 5(mg/kg) in 15 samples and was not detected 12 samples. Mercury was detected less than 0.2(mg/kg) in 15 samples and was not detected 12 samples. Cadmium was detected more than 0.3(mg/kg) in 3 samples was detected less than 0.3(mg/kg) in 16 samples and was not detected 11 samples. A few residual pesticides was detected, but all residual pesticides was safe. Sulfur dioxide was detected in all samples, but all residual sulfur dioxide was safe.

• 대한한의학방제학회지
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• 제17권2호
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• pp.53-63
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• 2009

Objective : To compare the contents of heavy metals, residual pesticides and sulfur dioxide before/after a decoction. Methods : The heavy metal contents before/after a decoction were measured by Inductively Coupled Plasma Atomic Emission Spectrometer (ICP-AES) and mercury analyzer. In order to analyze pesticides in 4 samples we used simultaneous multi-residue analysis of pesticides by GC/ECD, which was followed by GC/MSD analysis to confirm the identity of the detected pesticide in each sample. In addition, the contents of sulfur dioxide ($SO_2$) were performed by Monier-Williams distillation method. Results: 1. The mean values of heavy metal contents (mg/kg) for the samples were as follows: Jaeumganghwa-tang (before decoction - Pb; 1.190, Cd; 0.184, As; 0.099 and Hg; 0.028, after decoction - Pb; .033, Cd; 0.003, As; 0.005 and Hg; 0.001), Yukmijiwhang-tang (before decoction - Pb; 0.484, Cd; 0.133, As; 0.053 and Hg; 0.009, after decoction - Pb; 0.065, Cd; 0.008, As; 0.007 and Hg; not detected), Bojungikgi-tang (before decoction - Pb; 0.863, Cd; 0.197, As; below 0.016 and Hg; 0.011, after decoction - Pb; 0.071, Cd; 0.009, As; 0.004 and Hg; 0.001) and Ssangwha-tang (before decoction - Pb; 1.511, Cd; 0.212, As; 0.094 and Hg; 0.016, after decoction - Pb; 0.029, Cd; 0.006, As; 0.005 and Hg; 0.0004). 2. Contents (mg/kg) of sulfur dioxide ($SO_2$) before a decoction in Jaeumganghwa-tang, Yukmijiwhang-tang and Ssangwha-tang exhibited 22.7, 107.3 and 5.5, respectively. However, contents of sulfur dioxide after a decoction in all samples were not detected. 3. Contents (mg/kg) of residual pesticides before/after a decoction in all samples were not detected. Conclusion : These results will be used to establish a criterion of heavy metals, residual pesticides and sulfur dioxide.

• 한국식품과학회지
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• 제35권6호
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• pp.1028-1032
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• 2003

절임류에 함유된 이산화황함량의 정확한 분석을 위해 산 증류후 HPLC-UV detector를 이용한 방법과 Monnier-Williams변법으로 실험해보았다. 산증류-HPLC-UV법은 절임류중의 아황산염을 산증류 시킨 후 발생하는 이산화황을 1% triethanolamine용액에 흡수시켜 이를 UV 240nm에서 정량하는 것으로서, 고정상은 음이온 교환컬럼을, 이동상으로는 1.8mM $Na_2Co_3$와 1.7mM $NaHCO_3$용액을 사용하였다. 이 방법으로 단무지에 아황산염을 첨가하여 실험 한 결과 $84.0{\sim}91.7%$의 회수율을 얻었다. 시중에 유통되는 48종의 절임류에 대해 모니어윌리암스변법과 산증류-HPLC-UV법을 이용하여 이산화황 함량을 조사해본 결과, 산증류-HPLC-UV법에 비해 모니어월리암스법에서 휘발성 산으로 인해 높은 농도를 나타내었다. 산증류-HPLC-UV법으로 분석한 절임류의 이산화황 농도는 불검출${\sim}173.05ppm$이었고, 기준인 30ppm을 초과하는 제품은 3건이었다.

• 멤브레인
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• 제17권4호
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• pp.302-310
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• 2007

이산화황 흡수 수용액이 다공성 분리막 접촉기를 연속적으로 순환하는 시스템에서 다양한 운전변수에 따른 이산화황의 분리 효율을 고찰하였다. 공급 기체로는 이산화황/공기 혼합 기체를 사용하였으며 흡수제로는 $Na_2SO_3$ 수용액을 사용하였다. 운전 변수들인 흡수제 농도와 공급 기체 내의 이산화황 농도, 분리막 재질, 흡수제 유속 변화에 따른 분리 효율에 대한 영향을 확인하고자 하였다. 흡수제의 농도 0.05 M에서 0.2 M로 증가할수록 이산화황 제거 효율은 74%에서 100%로 증가하였다. 이산화황 농도가 700 ppm에서 2,500 ppm으로 증가할수록 제거 효율은 100%에서 75%로 감소하였다. 또한 흡수제의 유속이 2.5 mL/min에서 15 mL/min으로 증가할수록 제거 효율은 85%에서 100%로 증가하였고, 분리막은 기공률이 클수록 제거 효율이 증가함을 확인할 수 있었다.

• 한국식품위생안전성학회지
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• 제29권2호
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• pp.152-157
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• 2014

국내에 유통되고 있는 국산과 수입산 한약재 11종 116건을 대상으로 잔류이산화황에 대한 모니터링을 수행한 결과 108건(93.1%)은 불검출이었고 6건(5.2%)는 이산화황 허용기준치 30 mg/kg을 초과하였고 2건은 30 mg/kg 미만으로 검출되었다. 116건의 이산화황 평균함량은 $17.6{\pm}144.2mg/kg$이고 최대 검출량은 구기자(1,546.3 mg/kg)이었고 중국산 현호색(66.6%)의 이산화황 검출 빈도가 가장 높게 나타났다. 국내산 한약재는 71건 중 1건(1.4%), 수입산 한약재는 45건 중 7건(15.6%)에서 이산화황이 검출되었고 국내산 1건(36.7 mg/kg)과 수입산 5건(118.1 mg/kg)이 허용기준치를 초과하여 국내산보다 수입산 한약재에 이산화황 잔류량이 많았다. 본 연구를 통해 이산화황 허용기준을 초과하는 부적합율은 다소 낮아지고 있지만 이산화황 허용기준을 초과하는 한약재들 중 일부 한약재에서는 잔류이산화황 함량이 높게 나타났고, 특히 국내산 약재에 비해 수입산 약재는 부적합율이 높게 나왔다. 한약재는 일반적으로 수세 및 가열과정을 거치므로 실제 섭취하는 형태의 탕액에서는 원재료보다 이산화황의 잔류량이 크게 감소하지만 완전히 제거되지는 않으므로 유통되는 한약재의 안전성 확립이 절실히 요구되어진다. 강화된 기준이 정착하여 안전한 한약재가 유통될 수 있도록 수입통관시 특별관리가 요구되며, 보다 적극적인 검사 요주의 품목에 대한 지속적인 잔류이산화황 모니터링이 필요할 것으로 사료된다.

• 대한본초학회지
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• 제24권1호
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• pp.111-119
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• 2009

Objectives : To compare the contents of hazardous substances before/after a decoction. Methods : The heavy metal contents before/after a decoction were measured by Inductively Coupled Plasma Atomic Emission Spectrometer (ICP-AES) and mercury analyzer. In order to analyze pesticides in 6 samples we used simultaneous multi-residue analysis of pesticides by GC/ECD, which was followed by GC/MSD analysis to confirm the identity of the detected pesticide in each sample. In addition, the contents of sulfur dioxide (SO2) were performed by Monier-Williams distillation method. Results : 1. The mean values of heavy metal contents (mg/kg) for the samples were as follows: Samchulkunbi-tang (before decoction - Pb; 1.592, Cd; 0.155, As; 0.055 and Hg; 0.014, after decoction - Pb; 0.036, Cd; 0.002, As; not detected and Hg; 0.001), Yijin-tang (before decoction - Pb; 0.830, Cd; 0.077, As; 0.045 and Hg; 0.015, after decoction - Pb; 0.193, Cd; 0.010, As; not detected and Hg; 0.002), Banhabaikchulcheunma-tang (before decoction - Pb; 0.976, Cd; 0.164, As; 0.167 and Hg; 0.019, after decoction - Pb; 0.031, Cd; 0.003, As; 0.006 and Hg; 0.005), Pyungwi-san (before decoction - Pb; 2.162, Cd; 0.128, As; 0.061 and Hg; 0.018, after decoction - Pb; 0.080, Cd; 0.006, As; not detected and Hg; 0.005), Leejung-tang (before decoction - Pb; 1.480, Cd; 0.294, As; 0.034 and Hg; 0.012, after decoction - Pb; 0.064, Cd; 0.007, As; 0.007 and Hg; 0.002) and Kwibi-tang (before decoction - Pb; 0.907, Cd; 0.193, As; 0.085 and Hg; 0.020, after decoction - Pb; 0.072, Cd; 0.006, As; 0.004 and Hg; 0.002). 2. Contents (mg/kg) of sulfur dioxide ($SO_2$) before a decoction in Banhabaikchulcheunma-tang, Pyungwi-san, Leejung-tang and Kwibi-tang exhibited 3.5, 3.4, 3.8 and 12.4, respectively. However, contents of sulfur dioxide after a decoction in all samples were not detected. 3. Contents (mg/kg) of residual pesticides before/after a decoction in all samples were not detected. Conclusions : These results will be used to establish a criterion of heavy metals, residual pesticides and sulfur dioxide.

• 한국대기환경학회지
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• 제2권1호
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• pp.103-110
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• 1986

Since sulfur dioxide is released from the oxidation of sulfur in fuel, the level of $SO_2$ in industrial areas can be effectively managed by optimizing the allocation of fuels: the fuel should be allocated to each industries so as to achieve the air quality goal in the area with minimum fuel cost. The solution for this can be by solved using linear programming technique incorporated with the Gaussian dispersion equation. When this method was applied in Ulsan Industrial Complex, 39.3% of fuel expense could be saved compared with the present uniform fuel policy. With this method, bituminous coal generally was allocated to big emission sources such as power plants or to industries sparsely located in remote areas, and LPG or low-sulfur oils to small or medium-size sources in dense indurstrial aras. However, the particulates emission will increase with this policy, because it maximizes the use of coal within the limit to achieve the air quality goal in the area.

• Bulletin of the Korean Chemical Society
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• 제28권9호
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• pp.1609-1612
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• 2007