• 대한본초학회지
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• 제24권1호
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• pp.89-98
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• 2009

Objectives : The purpose of this study was to evaluate effects of processed sulfur with red ginseng on streptozotocin(STZ) induced diabetic rats for expansion of processed sulfur internal application. Methods : We prepared red ginseng with non processed sulfur extracts(GS), red ginseng with processed sulfur I extracts(GPS I) and red ginseng with processed sulfur II extracts(GPS II). In the present study, we examined about contents of crdue saponin, antioxidant activity, $\alpha$-glucosidase inhibitory activity, and effects of STZ induced diabetic rats. Results : Contents of crude saponin increased by processed sulfur, and GPS II was shown highest contents in crude saponin and sulfur compared with another groups. Electron donating ability of GPS II was shown highest activity compared with GS and GPS I, SOD-like activity showed same tendency as electron donating ability at 1 $mg/m\ell$ concentration. Inhibitory activity of $\alpha$-glucosidase was approximately same level in acarbose and GPS II. Blood glucose level of GPS II group was decreased 18.34% compared with DC(diabetes control) group and maintained stability range in glucose level. but GS and GPS I showed high level compared to GPS II. Serum triglycerides concentration also showed lowest level in GPS II. The activity of ALT, AST and ALP was shown high level in diabetic induced groups, and lowest level in GPS II. Creatinine was shown non-significantly difference in each groups and GPS II was shown lowest level in BUN. Conclusions : These results suggested that processed sulfur with red ginseng have improvement effects on diabetes and internal application of processed sulfur with red ginseng have no specific toxicity in liver and kidney.

• 한국대기환경학회지
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• 제1권1호
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• pp.25-32
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• 1985

To examine the effects of air pollution on Pinus thunbergii growing around Yocheon Industrial Complex, evaluation of visible injury based on Injury Index and chemical analysis of water-soluble sulfur and fluorine contents in needles were carried out on 30 sampling sites. Histological responses of needles were also investigated on the necrotic needle tissues. Not only Injury Index but water-soluble sulfur and fluorine contents were higher at all sites than those at control site, and showed significant correlationship among them. Especially, they were rather higher in the vicinity of air pollutants sources. Water-soluble sulfur contents were positively correlated with average atomospheric $SO_3$ concentrations. Microscopic examination of necrotic needle tissues showed that mesophyll cells were collapsed with hypertrophy and collapse of transfusion cells.

• 한국식품저장유통학회지
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• 제20권2호
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• pp.278-283
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• 2013

법제화된 유황이 육계사육에 미치는 영향을 알아보고자 유황사료를 급여한 닭의 폐사율, 무게 증가량을 측정 하였으며, 혈액의 항산화 활성과 혈액 내 글루타치온 및 콜레스테롤 함량, 그리고 계육의 단백질, 지방 분석과 닭유래 세포에서의 법제유황의 세포독성을 알아보았다. 먼저 일반사료에 비해 유황사료를 급여한 닭의 경우 폐사율이 감소하며, 닭의 무게가 증가하는 것을 알 수 있었다. 혈액 내 항산화활성을 FRAP 측정법을 이용하여 확인 한 결과 일반사료 급여군에 비해 유황사료 급여군에서 항산화 활성이 증가하였다. 혈액 내 전체 콜레스테롤 함량에는 큰 차이가 나지 않지만, 고밀도 콜레스테롤은 증가하는 반면, 저밀도 콜레스테롤은 감소하는 것을 확인하였다. 또한 계육에서의 총 아미노산과 단백질 함량은 변화가 없지만 지방 함량은 크게 감소시키는 것을 알 수 있었으므로 유황사료가 계육의 품질을 향상시켜 상품성을 높여줄 수 있을 것으로 사료되었다

• 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.

• 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.

• 사상체질의학회지
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• 제22권3호
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• pp.132-140
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• 2010

1. Objective: To compare the contents and transfer rate of hazardous substances in crude, washing solution, crude after washing, decoction and remnant after boiling. 2. Methods: The heavy metal contents of each step were measured by inductively coupled plasma mass spectrometer (ICP-MS) and mercury analyzer (MA-2). In order to analyze pesticides in each sample 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. 3. Results: 1) Contents (mg/kg) of heavy metals in decoction of all herbal medicine prescriptions were not detected. 2) Transfer rates (%) of heavy metals from crude to remnant were As (83.3%), Cd (100.0%), Pb (182.6%) and Hg (100.0%). 3) Contents (mg/kg) of residual pesticides were not detected. 4) Transfer rate (%) of sulfur dioxide (SO2) from crude to remnant was 44.2%. 4. Conclusion: Our results showed that boiled herbal medicine prescriptions which we take is safe from the hazardous substances.

• 한국산림과학회지
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• 제81권2호
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• pp.117-123
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• 1992

본(本) 연구(硏究)는 전주(全州)-군산간(群山間) 국도변(國道邊) 약(約) 40Km에 열식(列植)된 왕벚나무를 대상으로 하여 자동차 배기가스에 의한 공기오염(空氣汚染)이 왕벚나무의 생육(生育)에 미치는 영향(影響)을 규명(糾明)하고자, 선정(選定)된 전주(全州)-군산간(群山間) 국도변양측(國道邊兩側)에 10개의 지점(地點)에서 각(各) 지점(地點) 당 5그루씩 총(總) 100주(株)에 있어서 수관중간부위(樹冠中間部位)에서 성숙엽(成熟葉)을 채취(採取)하여 엽중(葉中) 수용성(水容性) 황(黃), Pb, 그리고 Cd 함유량(含有量)을 조사(調査)하였다. 주요결과는 다음과 같다. (1) 엽중수용성(葉中水溶性) 황(黃) 함유량(含有量)은 0.06-0.07%의 범위를 보였고, 대조구보다 2배(倍)가 더 많았다. 전주(全州)-이리간(裡里間)보다는 이리(裡里)-군산간(群山間)의 시료(試料)가 더 높은 수용성(水容性) 황(黃) 함유량(含有量)을 보였다. 대조시료(對照試料)와 비교할 때 황(黃)의 오염(汚染)이 인정되었다. (2) Pb 함유량(含有量)은 12-35ppm의 범위를 보였고 도로우측시료(道路右側試料)의 함유량(含有量)이 좌측시료(左側試料) 함유량(含有量)보다 높았다. 대조시료(對照試料)와 비교할 때 Pb의 더 많은 흡수량(吸收量)을 인정할 수 있었다. Pb 오염원(汚染源)은 일단 차량의 배기(排氣)가스에서 오는 것으로 추단(推斷)하고 이곳을 스쳐가는 바람의 영향도 생각 될 수 있는 것으로 보았다. (3) Cd 함유량(含有量)은 0.42-0.98ppm의 범위를 보였고 대조시료(對照試料)와 비교할 때 Cd의 오염(汚染)이 인정 될 수 있었다. (4) 벚나무 도로수(道路樹)의 건강도(健康度)는 주로 교통에 의한 오염이외(汚染以外)에도 개체(個體)에 따fms 유전적(遺傳的) 차이(差異), 그리고 국소입지(局所立地)의 차등(差等), 제인자(諸因子)의 혼합작용(混合作用)이 생각될 수 있을 것이다.

• 사상체질의학회지
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• 제22권2호
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• pp.93-100
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• 2010

1. Objectives: To compare the contents of hazardous substances such as crude, washing solution, crude after washing, decoction and remnant. 2. Methods: The heavy metal contents of each step were measured by inductively coupled plasma (ICP) spectrometer and mercury analyzer (MA-2). In order to analyze pesticides in Yanggyeoksanhwa-tang 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. 3. Results: 1) The mean values of heavy metal contents (mg/kg) for each steps in Yanggeoksanhwa-tang were as follows: crude (Pb; 1.87, As; 1.29, Cd; 0.28 and Hg; N.D.), washing solution (Pb; 1.98, As; 1.13, Cd; 0.10 and Hg; N.D.), crude after washing (Pb; 1.90, As; 1.40, Cd; 0.22 and Hg; N.D.), decoction (Pb; 1.90, As; 1.14, Cd; 0.11 and Hg; N.D.) and remnant (Pb; 2.39, As; 1.29, Cd; 0.25 and Hg; 0.01). 2) Contents (mg/kg) of residual pesticides in crude and decoction were not detected. 3) Contents (mg/kg) of sulfur dioxide (SO2) in crude, crude after washing and remnant exhibited 3.00, 2.00 and 2.00 mg/kg, respectively. However, contents of sulfur dioxide in washing solution and decoction were not detected. 4. Conclusions: These Results: will be used to establish a criterion of heavy metals, residual pesticides and sulfur dioxide of each step in Yanggeoksanhwa-tang.

• 동의생리병리학회지
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• 제21권4호
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• pp.1039-1044
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• 2007

We investigated the residual contents of sulfur dioxide ($SO_2$) on the 280 kinds of herbal medicines distributed at 8 cities including in Seoul, Busan, Daegu, Gwangju, Jecheon, Yeongju, Geumsan and Jeonju in Korea. The residual contents of $SO_2$ were determinated by modified Monier-Williams method. The residual contents of $SO_2$ were not detected at 206 products in total 280 products. However, it was detected below 100 ppm in 39 products, between 101 and 1000 ppm in 30 products and exceeded 1000 ppm in 5 products. $SO_2$ contents ranged 11 ${\sim}$ 2339 mg/kg (mean 293 mg/kg) at domestic samples distributed. Regardless of region, $SO_2$ contents were not found at Notopterygii Rhizoma, Ligustici Scinensis Rhizoma et Radix, Bombyx Batryticatus, Coicis Semen, Cnidii Rhizoma, Anemarrhenae Rhizoma, Gardeniae Fructus, Alismatis Rhizoma. But it's found at Batatatis Rhizoma, Paeoniae Radix and Codonopsitis Radix of every region collected the samples. $SO_2$ contents were not detected at 58 products which collected cultural fields of dometic. After treated with water wash and hot water extraction, the reduction rates of sulfur dioxide were appeared with 14.3% ${\sim}$ 40.4% and 55.2% ${\sim}$ 100.0%, respectively. These data will be used to establish a criteron of residual sulfur dioxide in herbal medicines.

• 대한본초학회지
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• 제24권2호
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• pp.13-20
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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 (S02) were performed by Monier-Williams distillation method. Results : 1. The mean values of heavy metal contents (mg/kg) for the samples were as follows: Socheongryong-tang (before decoction - Pb; 1.115, Cd; 0.179, As; 0.069 and Hg; 0.028, after decoction - Pb; 0.110, Cd; 0.011, As; 0.005 and Hg; 0.002), Insampaedok-san (before decoction - Pb; 1.207, Cd; 0.148, As; 0.171 and Hg; 0.026, after decoction - Pb; 0.075, Cd; 0.006, As; not detected and Hg; O.OOD, Oryung-san (before decoction - Pb; 1.955, Cd; 0.430, As; 0.063 and Hg; 0.027, after decoction - Pb; 0.083, Cd; 0.013, As; 0.006 and Hg; 0.002), Hwangryunhaedok-tang (before decoction - Pb; 1.825, Cd; 0.210, As; 0.050 and Hg; 0.009, after decoction - Pb; 0.107, Cd; 0.010, As; 0.005 and Hg; O.OOD, Bangpungtongseong-san (before decoction - Pb; 1.740, Cd; 0.162, As; 0.585 and Hg; 0.018, after decoction - Pb; 0.041, Cd; 0.006, As; 0.022 and Hg; not detected) and Oyaksungi-san (before decoction - Pb; 1.199, Cd; 0.183, As; 0.321 and Hg; 0.031, after decoction - Pb; 0.096, Cd; 0.008, As; 0.021 and Hg; 0.0004). 2. Contents (mg/kg) of sulfur dioxide (S0$_2$) before a decoction in Socheongryong-tang, Insampaedok-san, Oryung-san, Hwangryunhaedok-tang, Bangpungtongseong-san and Oyaksungi-san exhibited 3.2, 5.7, 4.5, 49.8, 7.8 and 22.4, 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.