• 한국환경보건학회지
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• 제12권1호
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• pp.69-78
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• 1986

In order to determine the content levels of trace metals in cow's milk, 79 market milk samples were collected from markets in major cities of Korea from July to August, 1985 and analyzed for content levels of Cu, Fe, Zn, Mn, Pb, Cd. The Results were as follows Cu, average 43.5 $\mu$g/l range 14 ~ 172.7 $\mu$g/l Fe, average 398.4 $\mu$g/l range 35 ~ 1,873 $\mu$g/l Zn, average 2.917 mg/l range 1.233 ~ 7.46 mg/l Mn, average 26.74 $\mu$g/l range 7.6 ~ 102 $\mu$g/l Pb, average 33.9 $\mu$g/l range N.D. ~ 105 $\mu$g/l Cd, average 1.73 $\mu$g/l range N.D. ~ 5.4 $\mu$g/l

• 디지털콘텐츠
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• 3호통권46호
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• pp.72-73
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• 1997

대한민국 현행법령 타이틀은 서기에 비치되어 있는 두꺼운 법전을 일일이 살펴보지 않고, 컴퓨터를 통한 간단한 검색으로 원하는 법을 살펴볼 수 있도록 국내 현행법을 일목요연하게 제공하는 전자 법령집이다.

• 환경생물
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• 제18권2호
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• pp.269-277
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• 2000

고마리와 소리쟁이에 Cd$^{2+}$와 Pb$^{2+}$를 각각 5 및 10mM로 5일간 처리한 결과, 고마리에서는 중금속 5mM처리구의 경우 Pb$^{2+}$가 Cd$^{2+}$보다 약 3.5배, 10mM의 경우 약 2.9배로 Pb$^{2+}$의 농축량이 높게 검출된 반면, 소리쟁이는 Cd$^{2+}$ 5mM에서 약 1.49$\mu\textrm{g}$/g, 10mM에서 약 2.90$\mu\textrm{g}$/g그리고 Pb$^{2+}$ 5mM에서 약 1.83$\mu\textrm{g}$/g, 10mM에서 약 2.73$\mu\textrm{g}$/g로 검출되어 처리농도별 Cd$^{2+}$와 Pb$^{2+}$의 농축량은 비슷하였다. 고마리와 소리쟁의 배양액(pH 6.5)에 Cd$^{2+}$와 Pb$^{2+}$를 5및 10mM로 혼합하여 처리한 후 각 실험구 토양의 중금속 잔류율과 pH는 대조구에 비해 고마리를 배양하며 Cd$^{2+}$5mM을 처리한 경우 약 77.1%와 pH 6.39, 10mM을 처리한 경우 약 90.2%와 PH 5.97 그리고 Pb$^{2+}$ 5mM을 처리한 경우 약 81.1%와 pH 6.00, 10mM을 처리한 경우 약 85.7%와 pH 5.80, 소리쟁이를 배양하며 Cd$^{2+}$ 5mM을 처리한 경우 약 83.9%와 pH 6.32, 10mM을 처리한 경우 약 93.7%와 pH 6.02 그리고 Pb$^{2+}$ 5mM을 처리한 경우 약 88.6%와 pH 6.27, 10mM을 처리한 경우 약 90.0%와 pH 6.02정도였다. Phytochelatin은 고마리와 소리쟁이에서 모두 Cd$^{2+}$와 Pb$^{2+}$ 무처리구에 비해 5와 10mM처리구에서 유도되었음을 확인하였다. 또한, 각 식물재료 내에서 중금속에 의해 유도된 Phytochelatin의 분자량은 고마리의 경우 Cd$^{2+}$에 의해서는 약 4,300-8,600 da, Pb$^{2+}$에 의해서는 약 3,200-9,700 da, 소리쟁이 의 경우 Cd$^{2+}$에서는 약 4,300 da, Pb$^{2+}$에 의해서는 약 3,200-7,500 da 정도였다.

• Bulletin of the Korean Chemical Society
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• 제23권8호
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• pp.1121-1126
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• 2002

Two anhydrous crystal structures of fully dehydrated Cd2+ - and Cs+ -exchanged zeolite X, Cd32Cs28Si100Al92O384 (Cd32Cs28-X: a = 24.828(11) $\AA)$ and fully dehydrated Cd,sup>2+ - and Rb+ -exchanged zeolite X, Cd28Rb36Si100Al92O384 (Cd28Rb36-X: a = 24.794(2) $\AA$), have been determined by single-crystal X-ray diffraction techniques in the cubic space group Fd3 at $21(1)^{\circ}C.$ The structures were refined to the final error indices, R1 = 0.058 and R2 = 0.065 with 637 reflections for Cd32Cs28-X and R1 = 0.086 and R2 = 0.113 with 521 reflections for Cd28Rb36-X for which I > $3\sigma(I)$. In the structure of Cd,sub>32Cs28-X, 16 Cd2+ ions fill the octahedral sites I at the centers of the double six rings (Cd-O = $2.358(8)\AA$ and O-Cd-O = $90.8(3)^{\circ}$ ). The remaining 16 Cd2+ ions occupy site II (Cd-O = $2.194(8)\AA$ and O-Cd-O = $119.7(4)^{\circ})$ and six Cs+ ions occupy site II opposite to the single six-rings in the supercage; each is $2.322\AA$ from the plane of three oxygens (Cs-O = 3.193(13) and O-Cs-O = $73.0(2)^{\circ}).$ Aboutten Cs+ ions are found at site II', $1.974\AA$ into the sodalite cavity from their three oxygen plane (Cs-O = $2.947(8)\AA$ and O-Cs-O = $80.2(3)^{\circ}).$ The remaining 12 Cs+ ions are distributed over site III' (Cs-O = 3.143(9) and O-Cs-O= $59.1(2)^{\circ})$. In the structure of Cd28Rb36-X, 16 Cd2+ ions fill the octahedral sites I at the center of the double-sixrings (Cd-O = 2.349(15) and O-Cd-O = $91.3(5)^{\circ}$ ). Another 12 Cd2+ ions occupy two different II sites (Cd-O = $2.171(18)/2.269(17)\AA$ and O-Cd-O = $119.7(7)/113.2(7)^{\circ}).$ Fifteen Rb+ ions occupy site II (Rb-O = $2.707(17)\AA$ and O-Rb-O = $87.8(5)^{\circ}).$ The remaining 21 Rb+ ions are distributed over site III' (Rb-O = $3.001(16)\AA$ and O-Rb-O = $60.7(4)^{\circ})$. It appears that the smaller and more highly charged Cd2+ ions prefer sites I and Ⅱ in that order, and the larger Rb+ and Cs+ ions, which are less able to balance the anionic charge of the zeolite framework, occupy sites II and II' with the remainder going to the least suitable site in the structure, site III'.The maximum Cs+ and Rb+ ion exchanges were 30% and 39%, respectively. Because these cations are too largeto enter the small cavities and their charge distributions may be unfavorable, cation-sieve effects might appear.

• 대한환경공학회지
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• 제36권12호
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• pp.851-857
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• 2014

본 연구에서는 해양오염퇴적물의 유기 오염물질을 제거하기 위한 세척기반처리 공정 중 중금속 특히 생물이용이 가능한 중금속 부분(Bioavailable Heavy Metal)의 동시 처리 가능성에 대해 평가하였다. 해양오염퇴적물 정화사업 대상인 N해역에서 퇴적물을 채취하여 본 연구의 시료로 사용하였다. 세척기반처리 공정에서 첨가제로는 산화제인 과산화수소($H_2O_2$)와 비이온 계면활성제(Tween-80)를 사용하였다. 퇴적물과 해수의 고액비는 1 : 3이며 과산화수소의 농도 1 M, 3 M, 4 M, 5 M과 0.05% Tween-80을 첨가하여 각 반응 시간(10, 20, 30, 40, 50, 60, 70, 80분, 24시간) 조건에서 시험하였다. 그 결과 총유기탄소(Total Organic Carbon, TOC) 제거 효율은 5 M + 0.05% Tween-80 24시간에서 최대 55.2%로 나타났다. 중금속 총 함량(Total Heavy Metals)은 구리(Cu), 아연(Zn), 카드뮴(Cd) 각각 29.5, 42.3, 73.0%의 제거 효율로 5 M + 0.05% Tween-80 10분에서 가장 좋은 제거효율을 보였다. 생물이용이 가능한 중금속 부분의 경우도 Cu, Zn, Cd에서 각각 60.0, 77.7, 90.2%로 5 M + 0.05% Tween-80 10분에서 가장 좋은 효율을 나타내어 유기물 처리 공정에서의 Cu, Zn, Cd 등 일부 중금속의 동시 제거 가능성을 확인하였다. 총유기탄소 함량과 생물이용이 가능한 중금속 부분의 상관분석 결과 제거 된 Cu, Zn, Cd은 $r^2$값이 0.94, 0.85, 0.69로 좋은 상관관계를 보여주었다.

• 분석과학
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• 제21권6호
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• pp.480-486
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• 2008

본 연구에서는 시중에 유통중인 광물성 생약에서의 중금속(Pb, Cd, As, Hg)에 대해 모니터링 하였다. Pb, Cd, As의 경우 시료 전처리는 습식분해법으로 하였으며, ICP-MS를 이용하여 검출하였고 Hg의 경우 AMA를 이용하여 모니터링 하였다. 모니터링의 결과 전체 시료(92)의 25.81%(24)가 Pb를 함유하고 있었으며 능자광(85.5 mg/kg), 부석(41.2 mg/kg), 진사(20.4 mg/kg)에서 기준치(0.5 mg/kg) 이상으로 검출되었다. Cd의 경우 전체 시료(92)의 9.68%(17)가 함유되어있었으며, 능자광(345 mg/kg), 부석(0.44 mg/kg), 진사(2.78 mg/kg)에서 기준치(0.3 mg/kg) 이상으로 검출되었고, 전체 시료(92)의 24.73%(23)가 As를 함유하고 있었으며, 능자광(5.72 mg/kg), 조산화납(22.2 mg/kg), 황화제이수은(10.0 mg/kg), 진사(12.5 mg/kg), 흑운모(14.6 mg/kg)에서 기준치(3 mg/kg)이상으로 검출되었다. Hg의 경우는 전체 시료(92)의 76.34%(78)가 함유되어 있었으며, 전체 13 종 광물 중 10종에서 기준치(0.2 mg/kg) 이상으로 검출되었다. 따라서, 국내에 유통되고 있는 광물성 생약재의 품질 평가와 안전관리를 보완하여 광물성 생약에 대한 신뢰성과 안전성을 확보할 필요성이 있는 것으로 판단된다.

• Asian Pacific Journal of Cancer Prevention
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• 제16권8호
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• pp.3147-3152
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• 2015

Background: Phylloides tumors are rare breast neoplasms with a variable clinical course depending on the tumor category. Along with histologic features, the role of immunohistochemical staining has been studied in predicting their behavior. Objectives: Our aim was to evaluate the role of CD 10 immunohistochemical staining in predicting survival, recurrence and metastasis in phylloides tumor. We also evaluated correlations of other clinicopathological features with overall and disease-free survival. Materials and Methods: CD10 expression was studied in 82 phylloides tumors divided into recurrent/metastatic and non-recurrent/non-metastatic cohorts. The Chi-square test was applied to determine the significance of differences in CD10 expression between outcome cohorts. Uni and multivariate survival analyses were also performed using log-rank test and Cox regression hazard models. Results: All 3 metastatic cases, 5 out of 6 (83.3%) recurrent cases and 37out of 73 (50.7%) non-recurrent and non-metastatic cases expressed significant (2+ or 3+) staining for CD10. This expression significantly varied between outcome cohorts (p<0.03). Tumor category and histological features including mitotic count and necrosis correlated significantly with recurrence and metastasis. A significant decrease in overall and disease free survival was seen with CD10 positivity, malignant category, increased mitoses and necrosis. Neither CD10 expression nor any other clinicopathologic feature proved to be an independent prognostic indicator in multivariate analysis. Conclusions: CD10 immunohistochemical staining can be used as a predictive tool for phylloides tumor but this expression should be interpreted in conjunction with tumor category.

• 환경생물
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• 제20권4호
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• pp.303-308
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• 2002

3-weeks old Commelina was transferred to and grown in Hoagland solution ($\pm$ 100 $\mu{M}$ $Cd^{2+}$, 100 $\mu{M}$ $Cd^{2+}$ ＋ 100$\mu{M}$ $Ca^{2+}$, 100 $\mu{M}$ $Cd^{2+}$ ＋ 200 $\mu{M}$ EGTA) for two weeks and then a number of physiological activities was investigated. $Cd^{2+}$ reduced total chlorophyll content up to 29% at a week and 75% at two weeks. In the treatment of $Cd^{2+}$ ＋ $Ca^{2+}$, the total chlorophyll content was reduced to 29% at a week and 80% at two weeks. $Cd^{2+}$ reduced 24% of Fv/Fm after two weeks. In case of $Cd^{2+}$ ＋ $Ca^{2+}$, Fv/Fm was reduced 55% at a week, but after two weeks, the plants were almost dead and Fv/Fm could not be measured. When EGTA was treated with $Cd^{2+}$, the value of Fv/Fm was not affected. There were no differences of water potential between the control and the treatment of $Cd^{2+}$+EGTA toy a week, but in other treatments. water potential was reduced. $Cd^{2+}$ reduced about 21% of water potential and $Cd^{2+}$ ＋ $Ca^{2+}$ reduced 43% of water potential after two weeks. $Cd^{2+}$ inhibited 21% of photosynthetic activity at a week and 32% at two weeks. In case of photosynthetic activity, $Cd^{2+}$ ＋ $Ca^{2+}$ inhibited 58% at a week and 73% at two weeks. $Cd^{2+}$+EGTA inhibited 15% of photosynthetic activity at a week and 21% at two weeks. Similar results were found in stomatal conductance. From the above results, it was observed that the treatment of $Ca^{2+}$ with $Cd^{2+}$ induced more reduction of a series of physiological responses than those of the treatment of $Cd^{2+}$ alone. Therefore, it could be concluded that $Ca^{2+}$ did not reduce the toxicity of $Cd^{2+}$, but enhanced $Cd^{2+}$ -induced physiological toxicities, but EGTA induced an decrease of $Cd^{2+}$ -induced physiological toxicities.

• 환경생물
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• 제22권3호
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• pp.438-445
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• 2004

캘리포오니아 홍합(Mytilus californianus)의 용존 Cd, Se, Zn의 흡수율에 대한 개체 크기와 수온의 영향을 평가하기 위하여 방사성 동위원소를 이용한 실험을 수행하였다. 세 개의 크기 구배(0.07, 0.24 and 0.73g; 육질부 건중량)를 갖는 홍합의 용존 금속 흡수율과 여수율은 동시에 4개의 온도 구배(3, 8, 13 and $21^\circ{C})$에서 측정되었다. 세 원소의 흡수율은 개체 크기가 증가함에 따라 유의하게 감소한 반면, 수온이 증가함에 따라 유의한 증가를 보였다. 홍합의 여수율은 전반적으로 용존 금속의 흡수율과 뚜렷한 상관관계를 보였는데, 이는 여과식자인 홍합이 용존 금속을 흡수하는 과정에 있어서 해수 여과 능력의 기능적인 중요성을 보여주는 결과이다.

• The Korean Journal of Ecology
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• 제20권1호
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• pp.35-41
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• 1997

Effects of cadmium on growth and nitrogen fixation activity of Melilotus suaveolens, a biennial legume plant dominating in the area of poor soil were quantitatively analyzed during the growing period. Cadmium treatments of 10, 30 and 100 ppm resulted in 12, 22 and 35% inhibition of plant height and 14, 25 nd 26% reduction of chlorophyll contents of leaves, respectively. The plant biomass reduced 51, 70 and 89% for leaves, 33, 50 and 59% for stems, and 42, 52 and 70% for roots, respectively by 10, 30 and 100 ppm Cd treatments. Cadmium contents of roots treated with 10, 30 and 100 ppm Cd were 62, 112 and 183 folds higher than that of the control, respectively. Cadmium contents of stems were about 1/2.2 of those of roots, but leaves contained only 1/27.8 of those of roots. Cadmium treatments resulted in increase of T/R ratios and decrease of F/C ratios significantly in the later growth period. Nodule formation was reduced to 8% in 42 days by the treatment of 100 ppm Cd. Specific nitrogen fixation activity of nodules attained 61.0, 24.0, 1.6 and 0.7 mol $C_2H_4{\cdot}g$ fr wt $nodule^{-1}{\cdot}h^{-1}$ on 42nd day, respectively for 0, 10. 30 and 100 ppm of Cd treatments. Total amount of nitrogen fixation per plant reduced by 73, 98 and 99% with the treatments of 10, 30 and 100 ppm Cd.