• Proceedings of the Materials Research Society of Korea Conference
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• 2004.05a
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• pp.84-84
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• 2004

• Tuberculosis and Respiratory Diseases
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• v.50 no.5
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• pp.579-590
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• 2001

Background : The aging process may be induced, at least in part, by reactive oxygen species(ROS). It has been thought that the lung could be a good source of ROS because it has a high oxygen tension. In the present study, we invetigated the inducibility of the first and last lines against oxidative stress, superoxide dismutases(CujZn-SOD and Mn-SOD) as a scavenger of ${O_2}^-\;{\cdot}$ and metallothionein(MT) as a scavenger of $OH{\cdot}$, respectively, in mouse lungs with age. Methods : Oxidative stress was induced by paraquat, an intracellular superoxide generator, at 1, 4, 8, and 12 months of age and then SODs and MT mRNAs were determined by RT-PCR method. Results : The steady-state level of Mn-SOD mRNA increased from 1 to 8 months but decreased thereafter. However, Mn-SOD mRNA was not induced by paraquat after 1 month. On the other hand, there was no change in the steady-state level of Cu/Zn-SOD mRNA, which decreased abruptly at 12 months of age. Additionally, Cu/Zn-SOD mRNA was not induced by paraquat at any age. There was no change in the steady-state level of MT mRNA with age whereas its inducibility by paraquat was intact at all ages. Conclusion : These results indicate that lack of induction of SODs with age may be one of the causative factors in the aging process while induction of MT may play an important role in the defense against oxidative stress. It is therefore implicated that the tissue antioxidant/prooxidant balance could be one of determinants of mean life span.

• Current Photovoltaic Research
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• v.3 no.2
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• pp.54-60
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• 2015

ZnSnO thin films were deposited by atomic layer deposition (ALD) process using diethyl zinc ($Zn(C_2H_5)_2$) and tetrakis (dimethylamino) tin ($Sn(C_2H_6N)_4$) as metal precursors and water vapor as a reactant. ALD process has several advantages over other deposition methods such as precise thickness control, good conformality, and good uniformity for large area. The composition of ZnSnO thin films was controlled by varying the ratio of ZnO and $SnO_2$ ALD cycles. The ALD ZnSnO film was an amorphous state. The band gap of ZnSnO thin films increased as the Sn content increased. The CIGS solar cell using ZnSnO buffer layer showed about 18% energy conversion efficiency. With such a high efficiency with the ALD ZnSnO buffer and no light soaking effect, AlD ZnSnO buffer mighty be a good candidate to replace Zn(S,O) buffer in CIGSsolar cells.

• Proceedings of the Korean Vacuum Society Conference
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• 2015.08a
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• pp.257.1-257.1
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• 2015

Cu(In,Ga)Se2 (CIGS) 박막 태양 전지에서 buffer layer는 CIGS 흡수층과 TCO 사이의 밴드갭 차이에 대한 문제점과 lattice mismatch를 해결하기 위해 필수적이다. 흔히 buffer layer 물질로는 CdS가 가장 많이 사용되고 있으나 Cd의 독성에 관한 문제가 야기되고 있다. 따라서 ZnS(O, OH) buffer layer가 친환경 물질로 기존의 CdS 버퍼 층의 대체 물질로 각광 받고 있으며, 단파장 범위에서 높은 투과율로 인해 wide band gap의 Chalcopyrite 태양 전지에 응용되는 buffer layer로 많은 연구가 이루어지고 있다. 또한 buffer layer를 최적화 하여 carrier lifetime과 양자 효율이 증가시킬 수 있는 특성을 가지고 있다. 이 연구에서는 Cu(In,Ga)Se2 (CIGS) 박막에 화학습식공정 (CBD) 방법을 이용하여 최적화된 ZnS(O, OH)의 증착 조건을 찾고, 고품질의 buffer layer를 제조하기 위한 실험에 초점을 맞췄다. 또한, buffer layer의 막질을 개선하고 균일한 막을 제조하기 위해 processing parameters인 시약의 농도, 제조 시간 및 온도 등의 다양한 변화를 통해 실험을 진행하였다. 그 후 최적화된 ZnS(O, OH) buffer layer의 특성 분석을 위해 X-ray diffraction(XRD), photoluminescence (PL), scanning electron microscope (SEM) and GD-OES을 이용하였고, 이를 통해 제조된 CIGS 박막 태양전지는 light induced current-voltage (LIV) and external quantum efficiency (EQE)를 통해 특성 분석을 실시 하였다. 결과적으로, 제조된 ZnS(O, OH) buffer layer의 $ZnSO4{\cdot}7H2O$의 농도는 0.16 M, Thiourea는 0.5 M, NH4OH는 7.5 M, 그리고 반응 온도는 77.5 oC의 조건 하에 CIGS 기판 위에 균일하고 균열이 없는 ZnS(O, OH) 박막을 제조하였으며 이때 제조된 태양전지의 소자 특성은 Voc = 0.478 V, Jsc = 35.79 mA/cm2, FF = 47.77%, ${\eta}=8,18 %$이다.

• 한국신재생에너지학회:학술대회논문집
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• 2009.06a
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• pp.138-138
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• 2009

Recently, thin-film solar cells of Cu(In,Ga)$Se_2$(CIGS) have reached a high level of performance, which has resulted in a 19.9%-efficient device. These conventional devices were typically fabricated using chemical bath deposited CdS buffer layer between the CIGS absorber layer and ZnO window layer. However, the short wavelength response of CIGS solar cell is limited by narrow CdS band gap of about 2.42 eV. Taking into consideration the environmental aspect, the toxic Cd element should be replaced by a different material. It is why during last decades many efforts have been provided to achieve high efficiency Cd-free CIGS solar cells. In order to alternate CdS buffer layer, ZnS buffer layer is grown by using chemical bath deposition(CBD) technique. The thickness and chemical composition of ZnS buffer layer can be conveniently by varying the CBD processing parameters. The processing parameters were optimized to match band gap of ZnS films to the solar spectrum and exclude the creation of morphology defects. Optimized ZnS buffer layer showed higher optical transmittance than conventional thick-CdS buffer layer at the short wavelength below ~520 nm. Then, chemically deposited ZnS buffer layer was applied to CIGS solar cell as a alternative for the standard CdS/CIGS device configuration. This CIGS solar cells were characterized by current-voltage and quantum efficiency measurement.

• Korean Journal of Materials Research
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• v.8 no.1
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• pp.33-37
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• 1998

Sn-Zn계 solder에서 Zn함량의 변화에 따른 납땜성을 납땜분위기 및 용제를 달리하여 연구하였다. 계면에서의 미세조직 관찰은 열처리온도를 8$0^{\circ}C$와 10$0^{\circ}C$로 달리하여 100일간 열처리한 후 관찰하였다. 젖음성 측정 결과, Zn함량이 증가함에 따라 젖음성은 감소하였고 RMA-용제를 사용한 경우가 R-용제를 사용한 경우에 비해 젖음성이 향상되었다. Sn-9Zn의 접촉각은 약 45도이고, 공기중에서 보다 질소 분위기에서 납땜한 경우가 젖음성 개선을 나타냈다. Sn-9Zn땝납과 Cu기판에서의 계면반응을 XRD, EDS로 분석한 결과 계면화합물은 r상(Cu$_{5}$Zn$_{3}$)으로 구성되어 있음을 알 수 있으며, 시효처리에 따라 접합부의 solder쪽에는 Zn상의 고갈이 나타남을 확인할 수 있었다.

• Korean Journal of Food Science and Technology
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• v.18 no.6
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• pp.458-467
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• 1986

This study was conducted to investigate the contamination level of some heavy metals for common restaurant meals in Seoul area and further to estimate the total dietary intake of heavy metals from the meals. The samples included seolong-tang (beef and rice soup) or galbi-tang (beef-rib soup), yeukkye-jang (spicy beef soup), doenjang-chigye-bab (boiled rice with soy paste stew), bibim-bab (boiled rice with assorted mixtures), and bibim-naengmyon (buckwheat vermicelli with assorted mixtures), which were separated into drained residues and fluids and determined for their heavy metal contents by atomic absorption spectrophotometry. The average concentrations of heavy metals in drained residues and fluids of 105 meal samples were 0.034 ppm, 0.017 ppm in Cd, 0.179 ppm, 0.073 ppm in Pb, 0.491 ppm, 0.308 ppm in Cu and 4.624 ppm, 1.403 ppm in Zn, respectively. The total amount of heavy metals per meal was $28\;{\mu}g\;Cd$, $145\;{\mu}g\;Pb$, $416\;{\mu}g\;Cu$ and $3654\;{\mu}g\;Zn$. The total dietary intake per day was estimated to give $84\;{\mu}g\;Cd$, $434\;{\mu}g\;Pb$, $1247\;{\mu}g\;Cu$ and $10960\;{\mu}g\;Zn$. Intake levels of Cd and Pb were higher than the daily intake limit established by FAO/WHO.

• Progress in Superconductivity
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• v.11 no.1
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• pp.47-51
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• 2009

For many large-scale applications of high-temperature superconducting materials, large critical current density ($J_c$) in high applied magnetic fields are required. A number of methods have been reported to introduce artificial pinning centers in $YBa_2Cu_3O_{7-{\delta}}$ films for enhancement of their $J_c$. We studied the microstructures and characteristic of $YBa_2Cu_3O_{7-{\delta}}$ films fabricated on $SrTiO_3$ (100) substrates with ZnO nanorods as pinning centers. Au catalyst nanoparticles were synthesized on STO substrates with self assembled monolayer to control the number of ZnO nanorods. The density of Au nanoparticles is approximately $240{\sim}260{\mu}m^{-2}$ with diameters of $41{\sim}49nm$. ZnO nanorods were grown on STO by hot-walled PLD with Au nanoparticles. Typical size of ZnO nanorod was around 179 nm in diameter and $2{\sim}6{\mu}m$ in length respectively. YBCO films deposited directly on STO substrates show the c-axis orientation, while YBCO films with ZnO nanorods exhibit any mixed phases without any typical crystal orientation.

• Journal of Korean Society of Forest Science
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• v.4 no.1
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• pp.14-16
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• 1965

(1) The sterilizing effects of NaF, $CuSO_4$, $CuCO_3$, $HgCl_2$, $ZnSO_4$, and coaltar creosote on the mycelial growth of Irpex consors Berk. Polystictus versicolor L. Fr, Polystictus versicalor L. var. nigricans, and Schizophyllum commune Fr. Were studied. (2) The range of minimum density of the fungicides to check the growth of four fungi mentioned above was as follows; NaF 0.15~0.25(%) $CuSO_4$ 0.20~0.35(%) $CuCO_3$ 0.40~0.50(%) $HgCl_2$ 0.05(%) $ZnSO_4$ 0.40~0.45(%) Creosote 0.10~0.15(%) Of the fungicides tested, $HgCl_2$ was most effective in fungicidal effects, and Creosote, NaF, $CuSO_4$, $ZnSO_4$, $CuCO_3$, followed. The order of resistance of the fungi to the fungicides was as follows: S. Commune Fr. P. Versicalor L. var.nigricans I. Consors Berk P. Versicalor L. Fr. (3) The fungicides were added to the pepton-agor culture medium at the concentration between 0.01 and 0.5%, and the medium was filled into 9cm petridshes. Two square millimeter agar blocks prepared separately from the fungi Contained agar were placed in the middle of the Petri-dishes, in cubated six days at $26^{\circ}C$. Diameter of biggest Colonies were measured.

• Economic and Environmental Geology
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• v.40 no.1 s.182
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• pp.15-28
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• 2007

The study is for contaminations of major, rare earth and trace elements of the farmland soils from the Boeunjeil mine area. The results are compared with the soils of Chungjoo, Deokpyeong, Boeun and Chubu areas. Fe and S contents of the contaminated area are high relative to those from the uncontaminated areas, Chungjoo and Boeun areas. Trace elements of the contaminated area are high relative to those from uncontaminated area, Chunajoo, Deokpyeong, Boeun and Chubu areas. The trace elements ares divided into Cd, Ni, Sr, U, V, Zn and As, Co, Cu, Mo, Pb, Sb, based on these dispersion and correlation. Two groups show the positive correlation. Enrichment factor of potentially toxic elements from contaminated area is >5 value, but <4 value in the uncontaminated area. In the geoaccumulation index of the minor elements, the contaminated area has >1 value and the uncontaminated area has <1 value except Mn. Enrichment index of potentially toxic elements(As, Cd, Co, Cu, Ni, U, Zn) ranges from 0.3 to 87.0 in the contaminated area and from 0.4 to 3.9 in the uncontaminated area. Overall results show that the high contents of farmland soils for the elements(Fe, S, As, Cd, Co, Cu, Ni, U, Zn) indicate the contamination by coal-related activities.