• 한국초전도ㆍ저온공학회논문지
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• 제20권2호
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• pp.24-28
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• 2018

To understand the effects of Cd substitution for Cu, $(Pb_{0.5}Cu_{0.5-x}Cd_x)Sr_2(Ca_{0.7}Y_{0.3})Cu_2O_z$ (x = 0 ~ 0.5) compounds were synthesized and the structural and superconducting properties of the compounds were characterized. Resistivity data revealed that superconducting transition temperature rises initially up to x = 0.25 and then decreases as the Cd doping content increases. Room-temperature thermoelectric power decreases at first up to x = 0.25 and then increases with higher Cd doping content, indicating that the change in $T_c$ is mainly caused by the change in the hole concentration on the superconducting planes by the Cd doping. The non-monotonic dependence of the lattice parameters and the transition temperature with Cd doping content is discussed in connection with the possible formation of $Pb^{+2}$ ions and the removal of excess oxygen caused by Cd substitution in the charge reservoir layer. A correlation between transition temperature and c/a lattice parameter ratio was observed for the $(Pb_{0.5}Cu_{0.5-x}Cd_x)Sr_2(Ca_{0.7}Y_{0.3})Cu_2O_z$ system.

• 한국환경보건학회지
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• 제18권2호
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• pp.135-145
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• 1992

This study was carried out to find out some characteristic responses of biological samples under the exposure of trace metals with the considering of Sex, age, residence period and smoking. Blood, Urine and Hair were collected from 116 dwellers in the vicinity of a smelting factory. Cd, Cu, Pb and Zn concentrations were determined by flame atomic absorption spectrophotometry and the following results were found important. 1) The concentrations of trace metals in the blood were 0.010+ 0.003 $\mu$g/ml in Cd, 0.82+ 0.11 $\mu$g/ml in Cu, 0.23_+ 0.13 $\mu$g/ml in Pb and 5.78_+ 1.43 $\mu$g/ml in Zn, those in the urine were 1.7_+ 1.7 $\mu$g/l in Cd, 16.5_+ 16.0 $\mu$g/l in Cu, 24.6_+ 23.0 $\mu$g/l in Pb and 367.7_+ 283.4 $\mu$g/l in Zn, and those in the hair were 0.52_+ 0.56 $\mu$g/g in Cd, 11.00_+4.01 $\mu$g/g in Cu, 8.53_+ 7.05 $\mu$g/g in Pb and 383.23_+ 110.56 $\mu$g/g in Zn. 2) In sex, the concentrations of Zn in the blood and urine of male were higher than those of female, however, the concentrations of Cd and Zn in the hair of female were higher than those of male. 3) The concentrations of Cd, Pb and Zn in the urine showed an increasing trend by age. 4) While the concentration of Cd in the urine increased, the concentration of Pb in the hair decreased by residential period in all the samples. 5) The concentrations of Cd and Zn in the blood and that of Zn in the urine of smoking group were higher than those of non-smoking group. The concentration of Pb in the blood of smoking group and those of Cd, Pb and Zn in the urine of non-smoking group showed increasing the trend by age. The concentrations of Cd and Zn in the urine of non-smoking group, the concentration of Zn in the hair of smoking group showed increasing trend by residential period, however, the concentrations of Pb in the blood and hair and that of Zn in the hair showed decreasing trend by residential period. 6) When the correlations of the concentrations between Zn (main smelting metal) and other metals were analyzed, Zn in the blood was significantly correlated with Cu, Pb and Zn in the urine (positively) and Zn in the urine was significantly correlated with Zn in the blood, Cd, Cu and Pb in the urine, and Pb in the hair (positively). Zn in the hair was significantly correlated with Cd in the urine and Cu in the hair (positively). 7) Consequently, it was useful to note that samples of urine showed higher sensitivity under the metal exposure than those of blood and hair in individual sampling. In addition, as trace metals showed higher accumulation in the hair of the groups, sampling of hair was more highly recommended than those of urine and blood in group sampling.

• 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.

• 한국환경과학회지
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• 제7권6호
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• pp.803-809
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• 1998

Heavy metal ions in water were removed using algal biomass as adsorbents. Absorbents were dried for 3 days, ground them by 40~60 mesh and then were swelled in a buffer solution for 1hr. After being packed in the column, commercially available standard solution of Cd(II) and Pb(II) ions were diluted to get the suitable concentration and then it was eluted with the rate of 1mι/min. Heavy metals on the adsorbents were recovered with nitric acid. More amounts of Cd(II) or Pb(II) ions in green algae, Ulva pertusa, than in brown algae, Sargassum horneri, were adsorbed. Pb(II) ion was adsorbed more than Cd(II) ion in both algae. The pH effect of adsorbed amounts of Cd(II), Pb(II) ions on the biomass was shown the following order ; pH 10.5 ＞ 8.5 ＞ 7.0 ＞ 5.5 ＞ 3.5. Recovery ratio of metal ions front algae is shown higher in acidic or neutral conditions than it in alkalic ones. Pb(II) ion is recovered relatively more than Cd(II) ion in our system.

• 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.

• 한국초전도ㆍ저온공학회논문지
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• 제17권3호
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• pp.5-8
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• 2015

The effects of Pr substitution on the structural and the superconducting properties for Pb-based 1201 cuprates with compositions of $(Pb_{0.5-x}Pr_xCd_{0.5})SrLaCuO_z(0{\leq}x{\leq}0.25)$ and $(Pb_{0.45}Pr_{0.05}Cd_{0.5})(Sr_{1-y}La_{1+y})CuO_z(0{\leq}y{\leq}0.1)$ were investigated. It is found that $T_c$ decreases as the Pr-doping content x increases in the $(Pb_{0.5-x}Pr_xCd_{0.5})SrLaCuO_z$ samples, whereas $T_c$ of $(Pb_{0.45}Pr_{0.05}Cd_{0.5})(Sr_{1-y}La_{1+y})CuO_z$ samples increases as the La-doping content y increases. The experimental results were discussed in connection with the change in hole concentration of the samples.

• 자원환경지질
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• 제38권3호
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• pp.221-236
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• 2005

도시화$\cdot$산업화의 인위적 오염원에 의한 중금속 원소들의 분산양상과 오염특성을 파악하기 위하여 서울지역내의 은행나무 잎과 가로수 토양 시료를 채취하여 토양 pH와 Fe, Mn, Pb, Zn, Cu, Cd, Ni, Cr, Co등의 중금속 함량을 측정하였다. 서울지역의 대부분의 토양 pH는 6-9의 범위로 약산성 및 약알칼리성을 보였다. 토양에서 Cd-Co, Cr-Ni, Cu-Zn, Pb-Zn는 높은 상관성을 보이고 있어 Cd은 Co와 배출원이 유사하고, Cr은 Ni과 Zn는 Cu, Pb의 배출원이 유사함을 예측할 수 있었다. 가로수 토양과 은행나무 잎 시료에 대한 원소들의 분포특성은 세척하지 않은 은행나무 잎의 Cd과 Pb, Cu와 Zn의 오염양상이 유사하다. 세척하지 않은 은행나무 잎에서 Cr과 Ni이 유사한 분포패턴을 보였다. 토양에 대해 오염지수에 의하면 공단지역과 교통량 밀집지역에서의 오염도가 높고, 특히 Cd, Cu, Zn에 의한 오염이 심하다. 토양시료에 대한 판별분석결과, 주거지역과 전원지역에서보다 공단지역과 교통량 밀집지역에 부화되는 원소는 Ni> Cr>Pb 순이다. 공단지역과 교통량 밀집지역을 구분하는데 가장 큰 설명력을 가지는 원소는 Cd이며, 교통량 밀집지역에서는 다른 원소에 비해 Co, Pb, Zn가 부화되어 있다.

• 한국환경농학회지
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• 제15권3호
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• pp.275-281
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• 1996

중금속으로 오염된 토양에 콩을 재배하였을 때 토양 중 중금속함량이 콩의 생육 및 중금속흡수에 미치는 영향을 요약하면 다음과 같다. 1. 중금속 오염지역의 콩 생육은 현저히 불량하였고, 토양 중 중금속함량도 월등히 많았다. 2. 중금속 오염지역내에 재배되고 있는 작물별 잎중의 Zn, Cu, Pb, Cd, As 등 중금속함량은 콩에서 가장 많았고 다음은 옥수수, 벼 순이었다. 3. 콩의 부위별 중금속함량은 Pb외에 줄기보다 잎에서 많았으며, 원소별로는 Zn > As > Cd > Cu > Pb순이었다. 4. 콩 생육과 토양 중 Zn, Cu, Pb, Cd, As함량과는 유의한 부의 상관이 인정되었다. 5. 토양 중 Zn, Cu, Pb, Cd, As함량과 콩잎의 Zn, Cd, As함량과 콩줄기의 Pb, Cd, As함량과는 고도의 유의성이 있는것으로 보아 중금속 오염지에서는 식물체에 흡수 축적되는 것으로 생각되었다.

• 한국해양환경ㆍ에너지학회지
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• 제10권1호
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• pp.21-28
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• 2007

진주담치와 넙치를 치사농도 이하의 납과 카드뮴을 첨가한 배양수조에 2주간 노출시킨 후 해당 중금속의 생물농축을 조사하였다. 노출 후 생물체내 중금속 농도는 배양액의 중금속 농도에 비례하여 증가하였으며, 진주담치에서 그 경향이 뚜렷하였다. 체내에 농축되어진 중금속 농도는 모두 고농도의 배양액에 노출시킨 시료에서 최대치를 기록하였으며, 납 5.0 mg/L 배양액에서 넙치 및 담치의 납 최대농도는 각각 $170({\pm}10)\;{\mu}g/g$, $5,260({\pm}70)\;{\mu}g/g$, 카드뮴 1.0 mg/L 배양액에서 넙치 및 담치의 카드뮴 최대농도는 각각 $72({\pm}4)\;{\mu}g/g$, $1,040({\pm}40)\;{\mu}g/g$으로 두 금속의 생물축적이 배양액 농도와 직접 관련이 있음을 나타냈다. 납과 카드뮴의 생물농축비(배양액 노출농도에 대한 분석시료의 농도비)는 두 중금속 모두 배양액의 농도에 반비례하여 낮은 노출농도에서 최대치를 보였고, 특히 진주담치에서 납의 생물농축비는 배양액 농도 0.01 mg/L에서 무려 12,100(${\pm}1,400$)을 보여주었다. 이러한 사실은 두 실험생물이 중금속 농도가 낮은 용액에 노출되었을 때 더 빨리 중금속을 섭취한다는 사실을 뒷받침한다. 한편, 진주담치의 중금속 축적을 기관별로 비교, 분석한 결과 납은 내장낭보다 아가미에서 다소 높은 반면 카드뮴은 내장낭에서 더 높은 농축특성을 보였다.

• 한국해양환경ㆍ에너지학회지
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• 제15권4호
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• pp.302-313
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• 2012

마산만과 진해만 해저에서 각각 31개와 65개 표층퇴적물을 채취하여 중금속(Al, Fe, Mn, Cr, Cu, Ni, Zn, Pb, As, Cd)을 분석하였다. 중금속 함량은 우리나라 주변의 만 및 하구 퇴적물에 비해 마산만에서 Fe, Cr, Cu, Zn, Pb, Cd, As 등이 높았고 진해만에서 Mn이 높았다. Cu, Zn, Pb, Cd, As는 항구 및 산업시설이 위치한 마산만 해안에서 매우 뚜렷한 증가를 보였으며 공간분포를 통한 오염물질의 근원지 추정이 가능하였다. 오염에 의한 중금속 농축은 지각의 함량을 배경농도로 한 농축비에 근거할 때 진해만은 국지적으로, 반면에 마산만은 넓은 지역에 걸쳐 활발히 진행된 것으로 확인되었으며 특히 Cu, Zn, Pb 및 Cd의 농축비가 대비되었다. As, Cd, Cr, Cu, Pb, Ni, Zn 함량을 중금속 환경기준에 적용한 결과 진해만 시료의 일부와 마산만 시료의 거의 대부분이 주의기준(NOAA ERL, EC TEL, ANZECC ISQG-low, Hong Kong ISQV-low)을 초과하였으며, Cu 및 Zn 함량은 일부 마산만 시료에서 관리기준(NOAA ERM, EC PEL, ANZECC ISQG-high, Hong Kong ISQV-high)을 초과하였다. $I_{geo}$ 값에 근거한 마산만의 중금속 오염은 Fe, Mn, Cr, Ni는 우려할 만한 수준이 아닌 반면 Cu, Zn, Pb는 강한 오염단계에 직면해 있거나 진입해 있으며, Cd는 시료의 87.1%가 강한 오염단계 이상의 심화된 오염상태로 파악되었다.