• 대한화장품학회지
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• 제20권1호
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• pp.37-51
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• 1994

Glutaraldehyde를 사용하여 화학적인 가교반응에 의해 empty cross-linked chitosan microcapsule을 제조하였다. 또한 chitosan bead는 sodium hydroxide 용액을 이용한 coaervation에 의해 제조하였다. 이들의 제조를 위해 수상/유화제/유기상으로 이루어진 w/o emulsion을 형성시킨 후 에멀젼의 안정성에 영향을 미치는 요소들에 대해 조사하였다. 보조계면활선제로 n-hexanol을 첨가한 결과 유화안정성이 상승적으로 증가하는 경향을 보였다. Chitosan microcapsule은 광택이 나는 형태로 내부가 투명한 반면 chitosan bead는 백탁으로 내부가 불투명하며 매우 porous한 구조를 하고 있었다. Chitosan bead의 유리 아미노기의 분석은 picric acid titration으로 수행하였으며, 아미노산 반응의 종결여부는 ninhydrin color test에 의해 판정하였다. 또한 fluoroscamine에 의한 형광분석으로 chitosan bead의 표면에 많은 반응성 아미노기가 존재하고 있음을 정성적으로 확인할 수 있었으며, 이를 생리활성 펩티드의 커플링 반응에 이용할 수 있었다. 모델 펩티드로서 콜라겐의 receptor 부분에 해당하는 생체내 growth factor로 알려진 Gly-His-Lys를 각 아미노산 유도체를 차례로 커플링하여 chitosan bead 위에서 합성할 수 있으며, 세포 성장인자와 같은 여러 가지 생리 활성 펩티드의 운반체로서 chitosan bead가 쉽게 이용될 수 있는 가능성을 보여 주었다.

• 환경위생공학
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• 제11권3호
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• pp.21-27
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• 1996

Chitosan is a natural polyelectrolytic compound. Researches of adsorption capacity using chitosan have been doing actively. We prepared bead type gel, simple modifier of chitosan, And then experimented adsorption test of heavy metals (Cd etc) using it. According to the result adsorption capacity of chitosan bead was five times higher than chitosan powder. Removal rate of cadmium resulted 90% over in the test that initial concentration of Cd was 100mg/L and bead dosage was 6g/100mL. Adsorption type of heavy metals was similar to general adsorption curve. And optical pH range was 4 - 10 in the adsorption test. In the experiments of other heavy metals (Pb, Zn, Cu, Mn) adsorption types had two stages, highly removal rate-stage at the short time (20minutes) and then slow rate-stage at the after. And removal efficiency at the variable pH ranges revealed relatively good.

• 공업화학
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• 제4권2호
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• pp.324-334
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• 1993

천연고분자인 chitin은 인체에 무해무독하며 생분해성이 있는 것으로 알려져 있다. 이 chitin을 탈아세틸화시켜 얻은 chitosan에 propionyl group을 도입하여 porous bead의 형태로 제조하고 이들의 흡수성수지로서의 가능성을 검토하였다. 실험에 사용된 propionyl chitosan porous bead의 합성은 chitosan을 acetic acid 수용액에 녹인 후 emulsion을 이용한 방법으로 아실화 반응을 일으켜 제조하였으며, crosslinked propionyl chitosan porous bead는 ethyleneglycol diglycidyl ether로 부분가교시킨 chitosan을 사용하여 상기와 같은 방법으로 제조하였다. 이때 propionic anhydride의 몰수와 반응시간 그리고 반응온도를 변화시킨 결과, propionyl chitosan의 합성조건은 propionic anhydride 5 moles, 반응시간 10시간 그리고 반응온도가 $22^{\circ}C$일 때 흡수능이 가장 좋은 것을 알 수 있었다. 제조된 porous bead에 대하여 증류수 및 생리식염수, 각종 염용액, 인공뇨 및 인공혈액에 대한 흡수도를 검토하였고, 흡수속도 및 보수력에 대한 교환 사항을 검토하였으며, 나아가 가교에 따른 기계적 강도의 변화를 고찰하였다.

• KSBB Journal
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• 제15권4호
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• pp.352-358
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• 2000

키토산의 가수분해 산물인 키토산 올리고당의 효율적이고 단순화된 분리를 위하여 기질인 키토산을 담체화 하여 효소를 이용한 올리고당의 생산에 있어서 product의 새로운 분리법에 대한 가능성을 연구하였다. 기질로 사용한 chitosan bead 를 W/O emulsion 상분리법을 이용한 유기상의 방법과 키토산 용액을 알칼리 용액에 적하하는 수상의 방법으로 제조하였는데 bead가 효소와 접촉하는 표면적을 최대로 하기 위하여 구형으로 제조하였다. 이때 유기상 bead의 지름은 $200{\mu}m$였고, 수상 bead의 경우 $4000{\mu}m$, $100{\mu}m$, $30{\mu}m$였다. pH 와 온도, 효소의 양을 변화시켜 가면서 반응 시스템에서 최 적의 유기상 bead의 가수분해 조건을 조사한 결과 pH 6.0, 온도는 $50^{\circ}C$, 그리고 효소의 양은 40U이 최적임을 알 수 있 었다. 유기상 bead의 최적 가수분해 조건을 수상 bead에 적 용시켜 반응성을 살펴보았는데 반응에 사용된 수상 bead의 표면적이 유기상 bead에 비하여 낮음에도 불구하고 거의 동 일한 분해도를 나타내었다. 수상 bead의 경우 크기가 작을수록 높은 분해도를 나타냈으며, 각 bead를 사용하였을 때 생산된 최종 산물의 올리고당의 조성을 HPLC와 GPC로 분석하였는데, 유기상 bead로부터 생산된 올리고당의 조성은 주 로 2-4당이었으며, 수상 bead로부터 생산된 올리고당의 조성은 2-5당이었고, 평균 분자량은 M.W. 540과 M.W. 380이었다.

• Journal of Pharmaceutical Investigation
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• 제25권1호
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• pp.37-46
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• 1995

The experiment was designed to investigate the sustained release dosage form of silymarin (SL) from chitosan (CS) carrier. Solid dispersed system was prepared by mixing the drug with chitosan. This solid dispersed system was cross-linked by glutaraldehyde, formaldehyde, acetaldehyde and butylaldehyde, respectively. The dissolution rates of these preparations were compared with each other in vitro. The silymarin was mired with anionic alginate gel and bead was prepared by dropping this mixture to cationic chitosan solution including calcium chloride. Chitosan encapsulated alginate bead after drying in the oven was investigated for the dissolution rate. The dissolution rate of SL-CS mixture was delayed with increase in the amounts of CS and the concentration of aldehyde. The effect on the delay of dissolution rate was in the increasing order of formaldehyde, glutaraldehyde, acetaldehyde, butylaldehyde. The dissolution rate of chitosan encapsulated alginate bead was parallel with the concentration of chitosan in diluted hydrochloric acid solution and delayed with increase in the concentration of chitosan in phosphate buffer solution.

• 환경위생공학
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• 제10권2호
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• pp.1-12
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• 1995

Under accelerated industrial developments environment pollution comes out to be very stirious. Especially the ions of heavy metal from wastewater, even if they are minimal, accumulated in ecology circle and do finally injury to human health. The general process for removal of heavy metals include coagulation and following sedimentation, ion -exchange and active carbon adsorption and sedimentation that applicate in popular, needs the expense of coagulant the additional treatment of sludge on the general process of coagulation and sedimentation. It is also a serious problem that the second pollution caused by coagulant. However chelating adsorption that uses natural chelating high- molecular compound has not pollution problem Among chelating high- molecules, the diminishing chitin that contained in crustaceans as crawfish and crab in our country with affluent water resources are easy to get. So it is advantageous to use this ubiquitous material for removing heavy metals because we could reuse natural resource. In this research, the author tested the effectiveness of the adsorption and removal of heavy metal ions by chitin and its derivatives. Chitin and cellulose became beads and used as flocculant, in this test. The results are as follows . First, bead showed higher removal ratio than powder in the comparative test on adsorbents such as chitin, chitosan and cellulose. Secondly, in the variety test by the kinds of adsorbent and time. chitosan bead and cellulose bead that showed the highest removal ratio. One hour need to remove the ions of heavy metal. Thirdly, the results of the adsorption degree test by pH revealed high removal ratio adsorption of chitin, cellulose and chitosan bead in alkalin condition but chitosan bead in acidic condition.

• 상하수도학회지
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• 제35권4호
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• pp.301-309
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• 2021

Chitosan, natural organic polymer, has been applied in water treatment as adsorbent due to non-toxic for human being. The amino group as functional group, can interacts with cation and anion at the same time. The prepared chitosan bead (HCB) was crosslinked to increase chemical stability (HCB-G) and both HCB and HCB-G were prepared to increase physical strength by drying referred to DCB and DCB-G, respectively. The adsorption effect for crosslinking and drying for four types of chitosan bead was tested using pseudo fist order (PFO), pseudo second order (PSO), and intraparticle diffusion model (ID). Regardless of PFO and PSO, the order of K, rate constant, is as followed: HCB > HCB-G > DCB > DCB-G for Cu(II) and phosphate. Drying leading to contraction of bead significantly reduced adsorption rate due to reduce the porosity of chitosan. In addition, crosslingking also negatively effect on adsorption rate. When compared with Cu(II) using hydrogel bead, phosphate showed higher value than Cu(II) for PFO and PSO. The application of ID showed that both hydrogel beads (HCB and HCB-G) obtained a very low R² ranging to 0.37 to 0.81, while R² can be obtained to over 0.9 for DCB and DCB-G, indicting ID is appropriate for low adsorption rate.

• Journal of Applied Biological Chemistry
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• 제59권1호
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• pp.75-81
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• 2016

Glutaraldehyde was used as a cross-linking agent for immobilization of purified ${\alpha}$-amylase from Exiguobacterium sp. DAU5. Befitting concentration of glutaradehyde and cross-linking time is the key to preparation of cross-linking chitosan beads. Based on optimized immobilization condition for ${\alpha}$-amylase, an overall yield of 56% with specific activity of 2,240 U/g on chitosan beads and 58% with specific activity of 2,320 U/g on chitosan-carbon beads was obtained. The optimal temperature and pH of each immobilized enzyme activity were $50^{\circ}C$ and 50 mM glycine-NaOH buffer pH 8.5, respectively. Those retained more than 75 and 90% of its maximal enzyme activity at pH 7.0-9.5 and after incubation at $50^{\circ}C$ for 1 h, respectively. In addition, the immobilization product showed higher organic-solvent tolerance than free enzymes. The mode of hydrolyzing soluble starch revealed that the ${\alpha}$-amylase possessed high hydrolyzing activity. These results indicate that chitosan is good support and has broad application prospects of enzyme immobilization.

• 상하수도학회지
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• 제32권3호
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• pp.253-259
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• 2018

Cu(II) can cause health problem for human being and phosphate is a key pollutant induces eutrophication in rivers and ponds. To remove of Cu(II) and phosphate from solution, chitosan as adsorbent was chosen and used as a form of hydrogel bead. Due to the chemical instability of hydrogel chitosan bead (HCB), the crosslinked HCB by glutaraldehyde (GA) was prepared (HCB-G). HCB-G maintained the spherical bead type at 1% HCl without a loss of chitosan. A variety of batch experiment tests were carried out to determine the removal efficiency (%), maximum uptake (Q, mg/g), and reaction rate. In the single presence of Cu(II) or phosphate, the removal efficiency was obtained to 17 and 16%, respectively. However, the removal efficiency of Cu(II) and phosphate was increased to 50~55% at a mixed solution. The maximum uptake (Q) for Cu(II) and phosphate was enhanced from 11.3 to74.4 mg/g and from 3.34 to 36.6 mg/g, respectively. While the reaction rate of Cu(II) and phosphate was almost finished within 24 and 6 h at single solution, it was not changed for Cu(II) but was retarded for phosphate at mixed solution.

• 공업화학
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• 제10권1호
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• pp.166-172
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• 1999

폐수중 중금속 이온을 제거하기 위한 방법으로 키토산 비드에 의한 금속 이온의 고정층 흡착 특성을 조사하였다. 게껍질로부터 키틴을 추출하고 이를 탈아세틸화 반응시켜 키토산을 제조하였다. 키토산은 비드로 만들어 중금속 흡착제로 사용하였다. 키토산 비드에 대한 $Cu^{2+}$, $Co^{2+}$, $Ni^{2+}$ 이온의 단성분 평형 흡착 실험 결과로부터 Freundlich와 Langmuir 흡착등온식을 결정하였다. 흡착등온식에 의하면 키토산 비드에 대한 중금속 이온의 흡착 세기는 $Cu^{2+}$>$Co^{2+}$>$Ni^{2+}$의 순서로 나타났다. 키토산 비드에 대한 중금속 이온의 단성분 또는 다성분계 고정층 흡착 실험으로부터 흡착 파과곡선을 구하였다. 단성분 흡착등온식으로 다성분 흡착 평형을 예측할 수 있는 IAS (ideal adsorbed solution) 이론을 적용하여 LDFA (linear driving force approximation)에 의한 고정층 흡착 모델식을 수치해 기법으로 모사하여 실험결과와 비교하였다. LDFA에 의한 모델식을 적용한 결과 키토산 비드에 대한 중금속 이온의 단성분 및 다성분계 고정층 흡착거동을 잘 모사할 수 있었다.