• Microbiology and Biotechnology Letters
• /
• v.17 no.6
• /
• pp.580-586
• /
• 1989

Penicillium sp. CB-20 was selected for strong polygalacturonase activity among various strains of molds found in soil. The optimum pH for the enzyme activity was 5.0 and optimum temperature was 4$0^{\circ}C$. The enzyme was relatively stable in acidic condition and unstable by heat treatment. The activation energy, Km and V$_{max}$ for the polygalacturonase were 2.499 Kcal/mol, 2.13$\times$10$^{-2}$mol/l, and 104.17 $\mu$mol/min. The activity of polygalacturonase was inhibited by Ag$^{+}$, Cu$^{++}$, Pb$^{++}$, Fe$^{+++}$, $Ca^{++}$, Na$^+$, Mn$^{++}$. The enzyme can be inactivated by the treatment ethylenediamintetra acetic acid, 2,4-dinitrophenol and $H_2O$$_2$. The results indicate the possible involvement of histidine, chelate and terminal amino group as active site. The enzyme was endo-type polygalacturonase.

• Proceedings of the Korean Vacuum Society Conference
• /
• 2014.02a
• /
• pp.323-323
• /
• 2014

기존의 태양전지 기술은 기술 장벽이 매우 낮고 대량 생산을 통한 단가 절감하는 구조를 가지고 있어 대규모 자본을 가진 후발 기업에게 잠식되기 쉽다. 그러나, III-V족 화합물 반도체를 이용한 집광형 고효율 태양전지는 기술 장벽이 매우 높은 기술 집약 산업이므로 독자적인 기술을 확보하게 되면 독점적인 시장을 확보 할 수 있어 미래 고부가 가치 산업으로 적합하다. 특히 III-V족 화합물 반도체 태양전지는 III족 원소(In, Ga, Al)와 V족 원소(As, P)의 조합으로 0.3 eV~2.5 eV까지 밴드갭을 가지는 다양한 박막 제조가 가능하여 다양한 흡수 대역을 가지는 태양전지 제조가 가능하기 때문에 다중 접합 태양전지 제작이 가능하다. 또한 III-V 화합물 반도체는 고온 특성이 우수하여 온도 안정성 및 신뢰성이 우수하고, 또한 집광 시 효율이 상승하는 특성이 있어 고배율 집광형 태양광 발전 시스템에 가장 적합하다. Si 태양전지의 경우 100배 이하의 집광에서 사용하나, III-V 화합물 반도체 태양전지의 경우 500~1000배 정도의 고집광이 가능하다. 이러한 특성으로 III-V 화합물 반도체 태양전지 모듈 가격을 낮출 수 있고, 따라서 Si 태양전지 시스템과 비교하여 발전 단가 면에서 경쟁력을 확보할 수 있다. III-V 화합물 반도체는 다양한 밴드갭 에너지를 가지는 박막 제조가 용이하고, 직접천이(direct bandgap) 구조를 가지고 있어 실리콘에 비해 광 흡수율이 높다. 또한 터널정션(tunnel junction)을 이용하면 광학적 손실과 전기적 소실을 최소화 하면서 다양한 밴드갭을 가지는 태양전지를 직렬 연결이 가능하여 한 번의 박막 증착 공정으로 넓은 흡수대역을 가지며 효율이 높은 다중접합 태양전지 제작이 가능하다. 이에 걸맞게 본연구에서는 화학기상증착장치(MOCVD)를 이용하여 InAsP 나노선을 코어 쉘 구조로 성장하여 태양전지를 제작하였다. P-type Dopant로는 Disilane (Si2H6)을 전구체로 사용하였다. 또한 Benzocyclobutene (BCB) 폴리머를 이용하여 Dielectric을 형성하였고 Sputtering 방법으로 증착한 ZnO을 투명 전극으로 사용하여 나노선 끝부분과 실리콘 기판에 메탈 전극을 형성하였다. 이를 통해 제작한 태양전지는 솔라시뮬레이터로 측정했을때 최고 7%에 달하는 변환효율을 나타내었다.

• Journal of Bio-Environment Control
• /
• v.15 no.1
• /
• pp.35-46
• /
• 2006

Objective of this research was to determine the effect of application rate of a slow release fertilizer (SRF) in three root media, peatmoss+vermiculite (1:1, v/v; PV), peatmoss+composted rice hall (1:1, v/v; PR), and peatmoss+composted pine bark (1:1, v/v; PB), on growth and nutrient contents of potted chrysanthemum 'Lima Honey'. All media contained polyacrylic acid sodium salt at a rate of $4.5g L^{-1}$. The fresh and dry weights at 43 days after transplanting did not show statistical differences among treatments in each root media. Elevated application rate of SRF increased fresh and dry weights at 80 days after transplanting in PV and PB media, but not in PR medium. Elevated application rates of SRF resulted in the increase of tissue phosphorus content and decrease of tissue Ca, Na, and Zn contents at both 43 and 80 days after transplanting. Elevated application rates of SRF resulted in the decrease of pH and increase of EC and concentrations of ${NO_3}^-$ and ${P_2O_5}^{3-}$, K, Ca, and Mg in the soil solution of PV and PR media. The trends of those in PR media were also similar except ${NO_3}^-$. The differences among treatments in EC at 80 days after transplanting were less significant as compared to those at 43 days after transplanting in three media.

• Korean Journal of Materials Research
• /
• v.30 no.10
• /
• pp.558-565
• /
• 2020

AZO thin films are grown on a p-Si(111) substrate by RF magnetron sputtering. The characteristics of various thicknesses and heat treatment conditions are investigated by X-ray diffraction (XRD), X-ray photoelectron spectroscopy (XPS), Hall effect and room-temperature photoluminescence (PL) measurements. The substrate temperature and the RF power during growth are kept constant at 400 ℃ and 200 W, respectively. AZO films are grown with a preferred orientation along the c-axis. As the thickness and the heat treatment temperature increases, the length of the c-axis decreases as Al³⁺ ions of relatively small ion radius are substituted for Zn²⁺ ions. At room temperature, the PL spectrum is separated into an NBE emission peak around 3.2 eV and a violet regions peak around 2.95 eV with increasing thickness, and the PL emission peak of 300 nm is red-shifted with increasing annealing temperature. In the XPS measurement, the peak intensity of Al_2p and O_ll increases with increasing annealing temperature. The AZO thin film of 100 nm thickness shows values of 6.5 × 10¹⁹ cm^-3 of carrier concentration, 8.4 cm^-2/V·s of mobility and 1.2 × 10^-2 Ω·cm electrical resistivity. As the thickness of the thin film increases, the carrier concentration and the mobility increase, resulting in the decrease of resistivity. With the carrier concentration, mobility decreases when the heat treatment temperature increases more than 500 ℃.

• Korean Journal of Fisheries and Aquatic Sciences
• /
• v.32 no.2
• /
• pp.121-126
• /
• 1999

In order to degrade chitin by enzymatic hydrolysis, it is required from screening highly active deacetylase. To this end, we examined three fungal strains and it turned out that Mucor rouxii produced highly active deacetylase, this enzyme exhibited the highest enzymatic activity against colloidal chitin. The conditions for growing Mucor rouxii are as follows; the effective carbon source, nitrogen source, adequate initial pH, temperature and incubation time were $2\%$ glucose, $1.33\%$ yeast extract, $0.66\%$ pepton, 4.5, $25{\pm}2^{\circ}C$ and 48hr, respectively. The optimum pH and temperature for purified enzyme activity were 5.5 and $40^{\circ}C$, respectively. The purified enzyme was stable at pH ranging from 4.5 to 5.5. However, the enzyme activity was decreased to less than $50\%$ at pH blow 45 and above 7.5. At temperatures above $50^{\circ}C$, the enzyme activity was decreased remarkably. The enzyme was inhibited by LiC1, $HgCl_2$, and $BaCl_2$, but stimulated by $CaCl_2$ and $ZnC1_2$, The activity of purified enzyme was increased by L-cysteine and 2-mercaptoethanol, while decreased by O-phenanthroline, p-CMB, EDTA, and iodoacetate. The $K_m$ and the $V_{max}$ value of purified enzyme were $1.2\%$ and 59.5 U/mg, respectively. The deacetylation activity of purified enzyme was not detected at optimal reaction condition when chitin particle suspension was used.

• Proceedings of the Korean Vacuum Society Conference
• /
• 2012.08a
• /
• pp.194-195
• /
• 2012

박막 실리콘 태양전지에 입사한 빛 중 흡수층인 진성 비정질 실리콘층(i-a-Si)에 흡수된 빛은 출력으로 변환되나, 기타의 층에서 흡수된 빛은 손실 성분이 된다. 이 중 흡수 손실이 큰 층은 도핑 층(p-a-SiC 및 n-a-Si)들인데, 이 들의 흡수 손실을 측정된 광학함수를 이용해 계산해 보면 Fig. 1과 같이 나타난다. p-a-SiC은 광 입사부에 위치하여 단파장 영역의 흡수 손실을 일으키고, n-a-Si 은 태양전지의 후면에 위치하여 장파장 영역의 흡수손실을 일으킨다. 이러한 도핑층에서의 흡수 손실을 제거 또는 개선하기 위해 도핑층의 재료를 기존 재료보다 광학적 밴드갭이 큰 재료로 대체하여 개선하는 방안에 대해 논하고자 한다. 금속 산화물의 밴드갭은 실리콘 화합물에 비하여 대체로 큰 값을 가지기 때문에 이를 기존의 실리콘 화합물 대신으로 사용한다면 광학적 흡수 손실을 효과적으로 줄일 수 있다. 단, 이때 태양전지의 광 전압을 결정하는 인자가 p층과 n층 사이의 일함수 차이에 해당하므로, p층의 대체층으로 사용 가능한 금속 산화물은 일함수가 큰(＞5 eV) 재료 중에서 선택하는 것이 적합하며, n층의 대체층으로 사용 가능한 금속 산화물은 일함수가 작은(＜ 4.2 eV) 재료 중에서 선택하는 것이 적합하다. Table 1에서 p층과 n층 대체용 금속산화물의 후보들을 정리하였다. 먼저 도핑층에서의 광 흡수가 광손실이 될 수 밖에 없는 물리적 근거에 대해서 논하고, 그 실험적인 증명을 제시한다. 이러한 개념을 바탕으로 도핑층의 내부 전기장의 방향을 제어하여 전자-정공쌍을 분리 수집하는 방법을 실험적으로 구현하였다. 이어서 금속 산화물을 부분적으로 대체하여 흡수 손실을 개선하는 방안을 제시한다. WOx, NiOx, N doped ZnO 등을 적용하여 그 효과를 비교 검토하였다. 끝으로 금속산화믈 대체 또는 쇼트키 접합을 적용하여 도핑층의 광 흡수를 줄이고 효율을 향상하는 방안을 제시한다. 그 사례로서 WOx, MoOx, LiF/Al의 적용결과를 살펴보고 추가 개선방안에 대해 토의할 것이다. 결론적으로 광학적 밴드갭이 큰 재료를 도핑층 대신 사용하여 흡수 손실을 줄이는 것이 가능하다는 것을 알 수 있고, 이 때 일함수 조건이 만족이 되면 광 전압의 손실도 최소화할 수 있다는 점을 확인할 수 있었다. 현재까지 연구의 한계와 문제점을 정리하고, 추가 연구에 의한 개선 가능성 및 실용화 개발과의 연관관계 등을 제시할 것이다.

• Korean Journal of Environmental Agriculture
• /
• v.17 no.1
• /
• pp.65-69
• /
• 1998

In order to evaluate the utility of bituminous coal fly ash, gypsum, oyster shell as soil amendments, aadic clayloam paddy soils with low calaum content were amended in the upper 15㎝ with amendments, and then Chinese cabbage was cultivated under plastic film house. Amendments treated were, in metric tons per hectare, i) none(Check) ; ii) 80 fly ash(FA) ; iii) 4 shell(SH) ; iv) 56 fly ash+24 gypsum (FG) ; v) 40 fly ash+24 gypsum+0.8 shell(FGS). On the whole, soil chemical properties were improved by amendments treatments. Amongst treatments, FA prominently neutralized soil pH and increased contents of Av. $P_2O_5$, Ex. K, and Av. B in soils. Besides, it showed the highest ratio in bacteria/fungi and (bacteria+actinomycetes)/fungi. FGS also affected the neutralization of soil pH and the increment of Ex. Mg. Amendments plants appeared alkaline damages only at early growing stage, but showed positive responses in fresh weight yields : 23% for FGS : 21% for FG : 19 18% for SH. At harvesting, leaves both of FA and FGS plants had higher values in contents of N, P, K, Ca, Mg, Fe, Mn, Zn, B, reduang-sugar, and vitamin-C than of others. In especial, Check plants appeared the heart rot symptoms owing to calaum defiaency differently from amendments plants. Taken together, FGS was an effective combination enable to maximize the utility of fly ash, gypsum, shell as soil amendments, espeaally in cabbage yield and quality.

• Economic and Environmental Geology
• /
• v.32 no.6
• /
• pp.611-631
• /
• 1999

Enviromental geochemisty and heary metal contamination at the Kongjueil mine creek were underaken on the basis of physicohemical properties and mineralogy for various kinds of water (surface, mine and ground water),soil, precipitate and sediment collected of April and December in 1998. Hydrgeochemical composition of the water samples are characterized by relatively significant enricant of Ca+Na, alkiali ions $NO_3$ and Cl inground and surfore water, wheras the mine waters are relatively eneripheral water of the mining creek have the characteristics of the (Ca+Mg)-$(HCO_3+SO_4)$type. The pH of the mine water is high acidity (3.24)and high EC (613$\mu$S/cm)compared with those of surface and ground water. The range of $\delta$D and $\delta^{18}O$ values (relative to SMOW) in the waters are shpwn in -50.2 to -61.6% and -7.0 to -8.6$\textperthousand$(d value=5.8 to 8.7). Using computer program, saturation index of albite, calcite, dolomite in mine water are nearly saturated. The gibbiste, kaolinite and smectite are superaturated in the surface and ground water, respectively. Calculated water-mineral reaction and stabilities suggest that weathing of silicate minerals may be stable kaolinite owing to the continuous water-rock reaction. Geochemical modeling showed that mostly toxic heavy metals may exist larfely in the from of metal-sulfate $(MSO_4\;^2)$and free metal $(M^{2+})$ in nmine water. These metals in the ground and surface water could be formed of $CO_3$ and OH complex ions. The average enrichment indices of water samples are 2.72 of the groundwater, 2.26 of the surface water and 14.15 of the acid mine water, normalizing by surface water composition at the non-mining creek, repectively. Characteristics of some major, minor and rate earth elements (Al/Na, K/Na, V/Ni, Cr/V, Ni/Co, La/Ce, Th/Yb, $La_N/Yb_N$, Co/Th, La/Sc and Sc/Th) in soil and sediment are revealed a narrow range and homogeneous compositions may be explained by acidic to intermediate igneous rocks. And these suggested that sediment source of host granitic gneiss colud be due to rocks of high grade metamorphism originated by sedimentary rocks. Maximum concentrations of environmentally toxic elements in sediment and soil are Fe=53.80 wt.% As=660, Cd=4, Cr=175, Cu=158, Mn=1010, Pb=2933, Sb=4 and Zn=3740 ppm, and extremely high concentrations are found are found in the subsurface soil near the ore dump and precipitates. Normalizing by composition of host granitic gneiss, the average enerichment indices are 3.72 of the sediments, 3.48 of the soils, 10.40 of the precipitates of acid mine drainage and 6.25 of the soils near the main adit. The level of enerichment was very severe in mining drainage sediments, while it was not so great in the soils. mineral composition of soil and sediment near the mining area were partly variable being composed of quartz, mica, feldspar, chlorite, vermiculite, bethierin and clay minerals. reddish variable being composed of quartz, mica, feldspar, chlorite, vermiculite, bethierin and clay minerals. Reddish brown precipitation mineral in the acid mine drainage identifies by schwertmanite. From the separated mineralgy, soil and sediment are composed of some pyrite, arsenopyite, chalcopyrite, sphalerite, galena, malachite, goethite and various kinds of hydroxied minerals.

• Economic and Environmental Geology
• /
• v.22 no.1
• /
• pp.35-63
• /
• 1989

Geochemical characteristics of the Guryongsan (Ogcheon) uraniferous black slate show that this is an analogue to the conventional Chattanooga and Alum shales in occurrences. Whereas, its highest enrichment ratio in metals including uranium, among others, is explained by the cyclic sedimentation of the black muds and quartz-rich silts, and the uniform depositional condition with some what higher pH condition compared to the conditions of the known occurrences. The cyclic sedimentation, caused by the periodic open and close of the silled basin, has brought about the flush-out) of the uranium depleted water and the recharge with the new metal-rich sea water, which consequently contributed to the high concentration of metals in mud. The metal-rich marine black muds, which mostly occur in the early to middle Palaeozoic times, is attributed by the geologic conditions which related to the atmospheric oxygen contents, and these are scarcely met in the late Precambrian and/or with the onset of Palaeozoic era in the geologic evolution of the earth.