• 한국결정성장학회지
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• 제19권4호
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• pp.190-195
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• 2009

스컬용융법에 의해 Na사규소운모를 합성하였다. $Mg_3(OH)_2Si_4O_{10}:Na_2SiF_6:SiO_2=8.3:24.8:66.9$ mol% 비율로 혼합한 출발원료를 ${\phi}13{\times}H14cm$의 냉각도가니에 채우고 2.84MHz 출력주파수의 고주파발진기를 이용하여 가열하였다. 원료는 융액상태에서 1시간 유지하였으며 도가니 내에서 냉각시켰다. 운모의 비저항은 추정하였으며, 원주모양과 판상으로 합성할 수 있었다.

• 한국표면공학회지
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• 제53권2호
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• pp.59-66
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• 2020

Effects of Na₂SiO₃ concentration added into 0.1 M NaOH + 0.05 M NaF solution on the formation behavior and properties of PEO films on AZ91 Mg alloy were investigated under 1200 Hz of alternating current (AC) by voltage-time curves, in-situ observation of arc generation behavior and measurements of film thickness, surface roughness and micro vickers hardness. In the absence of Na₂SiO₃ in the 0.1 M NaOH + 0.05 M NaF solution, about 4 ㎛ thick PEO film was formed within 1 min and then PEO film did not grow but white spots were formed by local burning. Addition of Na₂SiO₃ up to 0.2 M caused more increased formation voltage and growth of PEO film with uniform generation of arcs. Addition of Na₂SiO₃ from 0.2 M to 0.4 M showed nearly the same voltage-time behavior and uniform arc generation. Addition of Na₂SiO₃ more than 0.5 M resulted in a decrease of formation voltage and non-uniform arc generation due to local burning. PEO film growth rate increased with increasing added Na₂SiO₃ concentration but maximum PEO film thickness was limited by local burning if added Na₂SiO₃ concentration is higher than 0.5 M. Surface roughness of PEO film increased with increasing added Na₂SiO₃ concentration and appeared to be proportional to the PEO film thickness. PEO film hardness increased with increasing added Na₂SiO₃ concentration and reached a steady-state value of about 930 H_V at more than 0.5 M of added Na₂SiO₃ concentration.

• Advances in nano research
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• 제3권4호
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• pp.243-255
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• 2015

In this investigation, ecotoxicity of nano and micro metal oxides, namely silica ($SiO_2$) and alumina ($Al_2O_3$), on the growth of green algae (Porphyridium aerugineum Geitler) is discussed. Effects of nano and micro particles on the growth, chlorophyll content and protein content of algae are analysed using standard protocols. Results indicate that $SiO_2$ nano and micro $SiO_2$ particles are non-toxic to P. aerugineum Geitler up to a concentration of 1000 mg/L. In addition, $Al_2O_3$ microparticles are less toxic to P. aerugineum Geitler, whereas $Al_2O_3$ nanoparticles are found to be highly toxic at 1000 mg/L. Moreover, $Al_2O_3$ nanoparticles decrease the growth, chlorophyll content, and protein content of tested algae. In addition, zeta potential and contact angle are also important in enhancing the toxicity of metal oxide nanoparticles in aquatic environment. This study highlights a new insight into toxicity evaluation of nanoparticles on beneficial aquatic organisms such as algae.

• 한국재료학회지
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• 제24권2호
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• pp.81-86
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• 2014

The nitrogen solubility and nitride capacity of $CaO-SiO_2-Al_2O_3-MgO-CaF_2$ slag systems were measured by using gas-liquid equilibration at 1773K. The nitrogen solubility of this slag system decreased with increasing CO partial pressure, with the linear relationship between nitrogen contents and oxygen partial pressure being -3/4. This system was expected to show two types of nitride solution behavior. First, the nitrogen solubility decreased to a minimum value and then increased with the increase of CaO contents. These mechanisms were explained by considering that nitrogen can dissolve into slags as "free nitride" at high basicities and as "incorporated nitride" within the network at low basicities. Also, the basicity of slag and nitride capacity were explained by using optical basicity. The nitrogen contents exhibited temperature dependence, showing an increase in nitrogen contents with increasing temperature.

• 전자공학회논문지D
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• 제34D권2호
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• pp.27-37
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• 1997

Photoluminescent and cathodoluminescent charcteristics of inorganic luminescent materials were investigated ot develop possible phosphors for thin film electroluminescent (TFEL) device applications. Mg, Zn, and Photoluminescent and cathodoluminescent charcteristics of inorganic luminescent materials were investigated ot develop possible phosphors for thin film electroluminescent (TFEL) device applications. Mg, Zn, and $Si_3N_4$ powders were used to synthesize $(Mg_xZn_{1-x})SiN_2$ host materials. $Tb_4O_7$ and $Eu_2O_3$ powdrs were added as luminescent centers. Very sharp emission spectra of $Tb^{3+}$ ions were observed from $Mg._5Zn._5SiN_2:Tb$ sampels sintered at $1400^{\circ}C$ for an hour and the maximum intensity of emission spectra occured at wavelength of 550nm (green light). Synthetic conditions of $(Mg_xZn_{1-x})SiN_2:Eu$ phosphors were optimized for the hghest luminescence. The Eu concentrations were varied from 0.2% to 1.6%. Before firing, the powders were mixed using ballmills, methanol, acetone, or D.I. water. The Mg/Zn ratio also were varied from x=0.3 to x=0.7. The maximum PL intensity was obtained from a sample with 1.2% Eu concentration and the powder was mixed with methanol and dried before firing. The maximum intensity of the emission spectra occurred t the wavelength of 470nm(blue light). TFEL devices fabricated by using sputter deposition of $(Mg._3Zn._7)SiN_2:Eu$ phosphor layer showed yellowish white emission at the phosphor field of 2MV/cm.

• 한국분말재료학회지
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• 제22권1호
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• pp.15-20
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• 2015

The composite of porous silicon (Si) and amorphous carbon (C) is prepared by pyrolysis of a nano-porous Si + pitch mixture. The nano-porous Si is prepared by mechanical milling of magnesium powder with silicon monoxide (SiO) followed by removal of MgO with hydrochloric acid (etching process). The Brunauer-Emmett-Teller (BET) surface area of porous Si ($64.52m^2g^{-1}$) is much higher than that before etching Si/MgO ($4.28m^2g^{-1}$) which indicates pores are formed in Si after the etching process. Cycling stability is examined for the nano-porous Si + C composite and the result is compared with the composite of nonporous Si + C. The capacity retention of the former composite is 59.6% after 50 charge/discharge cycles while the latter shows only 28.0%. The pores of Si formed after the etching process is believed to accommodate large volumetric change of Si during charging and discharging process.

• 한국지구과학회지
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• 제32권7호
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• pp.707-718
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• 2011

보성-화순지역 하상퇴적물에 대한 지질집단별 자연배경치와 지구화학적 특성에 대해 연구하였다. 이를 위해 1차 수계를 따라 하상퇴적물시료 186개를 채취하였고, 실험실에서 자연건조 시킨 후, XRF, ICP-AES, NAA분석을 실시하였다. 하상퇴적물의 지질집단별 자연배경치와 지구화학적 특성을 알기 위해, 시료를 화강암질편마암(GGn)지역과 반상변정질편마암(PGn)지역으로 분리하였다. 화강암질편마암지역의 주성분원소 함량은 $SiO_2$ 45.5-73.09 wt.%, $Al_2O_3$ 12-20.76 wt.%, $Fe_2O_3$(T) 3.72-8.85 wt.%, $K_2O$ 2.38-4.2 wt.%, MgO 0.75-2.77 wt.%, $Na_2O$ 0.78-1.88 wt.%, CaO 0.27-2.1 wt.%, $TiO_2$ 0.56-1.72 wt.%, $P_2O_5$ 0.06-0.73 wt.% and MnO 0.03-0.95 wt.%이고 반상변정질편마암지역의 주성분원소 함량은 $SiO_2$ 43.74-70.71 wt.%, $Al_2O_3$ 11.54-25.05 wt.%, $Fe_2O_3$(T) 3.44-13.46 wt.%, $K_2O$ 2.08-3.86 wt.%, MgO 0.65-2.99 wt.%, $Na_2O$ 0.63-1.7 wt.%, CaO 0.35-2.07 wt.%, $TiO_2$ 0.68-4.17wt.%, $P_2O_5$ 0.1-0.31 wt.% and MnO 0.07-0.33 wt.%이다. 화강암질편마암지역 하상퇴적물의 위해원소 함량은 크롬 41.7-242 ppm, 코발트 7.6-25.1 ppm, 니켈 12-61 ppm, 구리 10-47 ppm, 아연 48.5-412 ppm, 납 17-215 ppm이고 반상변정질편마암지역은 크롬 29.6-454 ppm, 코발트 5.9-53.7 ppm, 니켈 8.7-287 ppm, 구리 6.4-134 ppm, 아연 43.6-370 ppm, 납 15-37 ppm이다. 화강암질편마암지역에서 크롬은 MgO와 코발트는 $Al_2O_3$, $Fe_2O_3$(T), MgO와 니켈은 $Fe_2O_3$(T), CaO, MgO와 높은 상관성을 가지나, 구리, 아연, 납은 비교적 낮은 상관성을 보였다. 반상변정질편마암지역에서 일반적으로 크롬, 코발트, 니켈, 구리는 주성분원소와 대부분 높은 상관성을 보였으나, 아연과 납은 낮은 상관성을 보였다.

• 한국세라믹학회지
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• 제20권4호
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• pp.305-314
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• 1983

In order to enhance the rate of th nitridation and to give the high density of reaction-bonded silicon nitride MgO powder as nitriding aid were added to silicon powders and the mixture was pressed isostatically into compacts which were nitrided in the furnace of 1, 35$0^{\circ}C$ where 95% $N_2$-5% $H_2$ gases were flowing. As the other nitriding aid $Mg(NO_3)_2 6H_2O$ was selected, A slip made of magnesium nitrate solution and fine silicon particles was spray-dried and then decomposed at 30$0^{\circ}C$. Magnesium oxide-coated silicon powders were formed into compacts prior to the nitridation on the same condition as the former. Magnesium nitrate (MgO, produced from the decomposition of magnesium nitrate) was more effective for the formation of the $\beta$-phase in the initial stage of the nitridation probably due to the easy formation of $MgO-SiO_2$-metal oxide eutectic melt. It has been confirmed that forsterite was formed as a result of the reaction between MgO and $SiO_2$ film of silicon surface. It was considered that MgO produced from magnesium nitrate may be finer more reactive and more uniformly distributed on the surface of silicon particles than original MgO. The higher the forming pressure was the more the $\beta$-phase was formed.

• Current Research on Agriculture and Life Sciences
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• 제4권
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• pp.1-6
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• 1986

수도(水稻) 생육초기(生育初期)에 규산(珪酸)을 처리(處理)할 때 유묘(幼苗)의 엽선단(葉先端)으로부터 배출(排出)되는 일액량(溢液量)과 일액(溢液)을 통(通)해 어느 정도((程度) 규산(珪酸)이 외부(外部)로 배출(排出)되며, 일액중(溢液中)의 규산(珪酸)과 엽소(葉燒)와의 관계(關係)를 구명(究明)하고저 다수계(多收系) 품종(品種) 삼강벼와 일반계품종(一般系品種) 낙동벼를 공시(供試)하여, 온도범위(溫度範圍)가 $29{\sim}33^{\circ}C$인 실내(室內) 자연광하(自然光下)에서 $50cm{\times}150cm{\times}70cm$인 vinyl 상자(箱子)로 밀폐(密閉)하여, 수경(水耕) 재배(栽培)한 수도(水稻) 유묘(幼苗)에서 채취(採取)한 일액중(溢液中)의 규산(珪酸)을 분절(分折) 조사(調査)하여던 바 결과(結果)를 요약(要約)하면 다음과 같다. 1. 규산(珪酸) 처리(處理) 농도(濃度)가 200ppm까지 증가(增加)할수록 일액량(溢液量)은 증가(增加)하였으며, 규산(珪酸) 처리(處理) 농도(濃度)가 200ppm 일때 일액량(溢液量)은 낙동벼 4.30mg/plant, 삼강벼 4.34mg/plant이었으며, 250ppm이상(以上)에서는 일액량(溢液量)이 감소(減少)하였다. 2. 규산(珪酸) 처리(處理) 농도(濃度)가 높을수록 일액량(溢液量) 함유(含有)되어 있는 규산(珪酸)의 농도(濃度)는 증가(增加)하였으며, 일액중(溢液中) 규산(珪酸)의 농도(濃度) 대(對) 규산(珪酸) 처리(處理) 농도(濃度) 비(比)는 100ppm 이상(以上)에서는 감소(減少)하였다. 3. 처리(處理)된 규산(珪酸)은 단시간(短時間)에 수도근(水稻根)으로 흡수(吸收)되어 일액(溢液)을 통(通)해 배출(排出)되며 처리(處理) 후(後) 12시간(時間)에 배출(排出)된 일액(溢液)에 규산(珪酸)의 함량(含量)이 가장 많았으며, 규산(珪酸) 처리(處理) 300ppm에서의 일액중(溢液中) 규산(珪酸)의 농도(濃度)는 낙동벼 $SiO_2$ 172.6ppm/cc, 삼강벼 $SiO_2$ 199.8ppm/cc이었다. 4. 일액중(溢液中)에 함유(含有)되어 있는 규산(珪酸)의 농도(濃度)와 엽소(葉燒)의 정도(程度)는 정(正)의 상관(相關)(낙동벼 $r=0.97^{**}$, 삼강벼 $r=0.97^{**}$)이 있었다.

• 한국주조공학회지
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• 제29권5호
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• pp.233-237
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• 2009

The effect of electrolyte on mechanical and corrosion properties of AZ91 magnesium alloy by plasma electrolytic oxidation (PEO) method was investigated. The coating layers formed in the silicate and the aluminate electrolytes showed porous structures. The small pores were randomly distributed on the coatings formed in aluminate electrolyte while the coatings formed in silicate electrolyte showed much bigger pores. In the aluminate electrolyte, the coatings were composed of Mg, MgO and $MgAl_2O_4$, whereas Mg, MgO, $MgAl_2O_4$ and $Mg_2SiO_4$ were identified in the coatings formed in silicate electrolyte. The hardness of coatings in the silicate electrolyte was higher than that of coating grown in the aluminate electrolyte. The AZ91 alloy coated in the silicate electrolyte had higher tensile strength and elongation than that coated in the aluminate electrolyte. In addition, the coatings formed in the silicate electrolyte showed much better corrosion resistance compared to the coatings formed in the aluminate electrolyte.