• Restorative Dentistry and Endodontics
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• 제46권1호
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• pp.11.1-11.11
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• 2021

Objectives: The aim of this study was to compare smear layer removal by conventional application (CA), passive ultrasonic irrigation (PUI), EasyClean (EC), and XP-Endo Finisher (XPF), using 17% ethylenediaminetetraacetic acid (EDTA) after chemomechanical preparation, as evaluated with scanning electron microscopy (SEM). Materials and Methods: Forty-five single-rooted human mandibular premolars were selected for this study. After chemomechanical preparation, the teeth were randomly divided into 5 groups according to the protocol for smear layer removal, as follows: G1 (control): CA of distilled water; G2 (CA): CA of 17% EDTA; G3 (PUI): 17% EDTA activated by PUI; G4 (EC): 17% EDTA activated by EC; and G5 (XPF): 17% EDTA activated by XPF. SEM images (×1,000) were obtained from each root third and scored by 3 examiners. Data were evaluated using the Kruskal-Wallis and Dunn tests (p < 0.05). Results: In the apical third, there were no statistically significant differences among the groups (p > 0.05). In the cervical and middle thirds, the experimental groups performed better than the control group (p < 0.05); however, G2 presented better results than G3, G4, and G5 (p < 0.05), which showed no differences among one another (p > 0.05). Conclusions: No irrigation method was able to completely remove the smear layer, especially in the apical third. Using CA for the chelating solution performed better than any form of activation.

• Bulletin of the Korean Chemical Society
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• 제20권12호
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• pp.1409-1412
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• 1999

The spectrophotometric determination method of scandium with eriochrome cyanine R (ECR) and the composition ratio of the complex were investigated in the presence of surfactants. A volume of 5 mL of 1.0×$10^{-3}$ M ECR and 10 mL of 2.0×$10^{-4}$ M CTMAB are necessary for the determination of 1.0×$10 ^{-7}$ ~ 3.0×$10^{-6}$ M Sc(III) at pH 6.5. The apparent molar absorption coefficient of the Sc(III)-ECR-CTMAB, ternary complex at 610 nm is 5.6×$10^5$ $mol^{-1}cm{-1}$L and its detection limit is 1.0×$10^{-7}$ M. Separation studies were conducted by the column method. The effect of pH, elution solution and the influence of rare earth elements as interferents was discussed. Their separation was carried out in 0.1 M HCl-50% methanol solution and 1.0 M HCl media. The method was applied for the determination of Sc(III) in monazite.

• 한국의류산업학회지
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• 제8권4호
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• pp.458-464
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• 2006

The adsorption ability of heavy metal ions from the aqueous solution by chitosan, which it is well known natural biopolymer, has been investigated. The fundamental study in this research is focusing on the physicochemical adsorption utilizing the chitosan as a organic chelating adsorbent, adsorb especially heavy metal ions from the waste liquid solution. The adsorption ability of the chitosan between metal ions, having different characteristics with Mw of 188,600, 297,200, and 504,200 g/mol and degree of deacetylation (DD) of 86.92% and 100% were investigated targeting on the $Ni^{2+}$, $Co^{2+}$, $Zn^{2+}$, and $Pb^{2+}$ ions, respectively. The uptake of heavy metal ions with chitosan was performed by atomic absorption flame emission spectrophotometer (AAS) as conducted residual metal ions. It was found that chitosan has an strong adsorption capacity for some metals under certain conditions. Chitosan, which have 100% degree of deacetylation showed high adsorption recovery ratio and have an affinity for all kinds of heavy metals. In contrast, the molecular weight of chitosan was not completely affected on metal ion adsorption.

• 한국환경과학회지
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• 제13권4호
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• pp.435-440
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• 2004

The thiophene or furan-containing hexadentate ligands 1, 12-bis (2-theophene )-2,5,8,ll-tetraazadodecane(Thiotrien ㆍ 4HCl) and 1,12-bis (2-furan)-2,5,8,11-tetraazadodecane(Furatrienㆍ4HC1) were synthesized as their tetrahydrochloride salt and characterized by EA, IR, NMR, and Mass spectrum. Their protonation constants (logK$_{nH}$) and stability constants (logK$^{M}_{L}$ for Cd$^{2+}$, Pb$^{2+}$, $Zn^{2+}$ and Cu$^{2+}$ ions were determined in aqueous solution by potentiometry and compared with 1, 12-bis(2-pyridyl)-2,5,8, 11-tetra-azadodecane(Pytrien) of pyridyl-containing ligand. The effect stability constants of ligands and metal ion for removal of heavy metals in aqueous solution were described.

• 분석과학
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• 제9권3호
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• pp.279-291
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• 1996

미량 금속이온을 선택적으로 분리, 농축 및 회수하기 위해 물리적 특성이 서로 다른 XAD-2, 4 및 16 다공성 수지에 2-(2-thiazolylazo)-p-cresol(TAC) alc 4-(2-thiazolylazo)orcinol(TAO)을 화학적으로 결합시켜 킬레이트 수지를 합성하고 뱃치법으로 U(VI) 등 10개 금속이온들의 흡착 특성을 조사 비교하였다. 킬레이트 수지의 합성률은 XAD-16-TAC형 수지는 0.60 mmol/g이었고 XAD-16-TAO형은 0.68mmol/g으로서 수지의 표면적이 큰 XAD-16형 수지가 XAD-2, 4형 수지보다 높은 합성률을 나타내었다. XAD-16-TAC와 XAD-16-TAO 킬레이트 수지는 1~5M 의 $HNO_3$, HCl 및 NaOH 등의 산과 염기성 용액에서 비교적 안정하였다. 그리고 U(VI) 이온을 10회 이상 반복적으로 흡착 및 탈착을 시킨 결과 연속적으로 재사용할 수 있는 안정한 내구성을 가지고 있음을 확인하였다. XAD-16-TAC 및 XAD-16-TAO형 수지에 대한 금속 이온의 최척 흡착조건과 흡착 특성을 조사한 결과는 금속이온이 킬레이트 수지에 흡착될 때 평형에 도달하는 시간은 약 1시간 정도였으며, XAD-16형 수지에서 흡착률이 가장 높았다. 그리고 금속이온들의 흡착률에 미치는 pH의 영향을 보면 U(VI)을 비롯한 대부분의 금속이온들은 pH 5~6 범위에서 최대로 흡착됨으로써 최척 pH 를 5로 정하였다. 또한 U(VI) 이온의 흡착에 미치는 공존이온의 영향을 보면 음이온인 $Cl^-$, $NO{_3}^-$, ${SO_4}^{2-}$, $CH_3COO^-$ 이온 및 $Na^+$, $K^+$, $Mg^{2+}$ 및 $Ca^{2+}$과 같은 양이온들은 흡착에 거의 영향을 미치지 않았다. 그러나 $CO{_3}^{2-}$는 $UO{_2}^{2+}$와 $[UO_2(CO_3)_3]^{4-}$의 안정한 착물을 형성하므로 U(VI) 이온의 흡착능을 크게 감소시켰다. 선택적인 특정 금속이온의 분리를 위하여 EDTA, CDTA 및 NTA 등과 같은 가리움제를 첨가하여 그 영향을 조사한 결과 NTA에 의한 가리움 효과가 10가지 혼합 금속이온 중 U(VI) 이온에 대하여 가장 큰 것으로 나타났다.

• 분석과학
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• 제17권3호
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• pp.199-210
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• 2004

Amberite XAD-16 다공성 수지에 4,5-dihydroxynaphthalene-2,7-disulfonic acid (chromotropic acid, CTA)를 화학적으로 결합시켜 XAD-16-CTA형 새로운 킬레이트 수지를 합성하고, 적외선분광법과 원소분석법으로 확인하였다. 이 킬레이트 수지에 대한 금속마감 산업과 관련 있는 9개 금속이온을 포함하는 Cr(III) 및 Cr(VI) 이온들의 흡착 및 탈착 특성을 뱃치법과 용리법으로 조사하였다. XAD-16-CTA 킬레이트수지는 1~5 M의 HCl, $HNO_3$ 및 NaOH 등의 산과 염기 용액에서 매우 안정하였다. pH 2에서 Cr(VI) 이온과 Cr(III) 이온이 공존하는 혼합용액으로부터 Cr(VI) 이온만을 선택적으로 분리할 수 있음을 확인하였으며, Cr(VI)의 최대 흡착용량은 1.2 mmol/g 이었다. 또한 Cr(VI) 이온의 흡착에 미치는 공존 음이온의 영향을 검토한 결과 음이온인 $F^-$, $SO{_4}^{2-}$, $CN^-$, $CH_3COO^-$, $NO{_3}^-$ 이온은 흡착율을 감소시켰으며, $PO{_4}^{3-}$와 $Cl^-$는 흡착에 큰 영향을 미치지 않았다. pH 2에서 킬레이트 수지에 의한 돌파점용량과 총괄용량으로부터 얻은 금속이온의 용리순서는 Cr(VI)>Sn(II)>Fe(III)>Cu(II)>Cd(II)${\simeq}Pb(II){\simeq}Cr(III){\simeq}Mn(II){\simeq}Ni(II){\simeq}Al(III)$이었다. 한편 $HNO_3$, HCl 및 $H_2SO_4$ 등의 탈착제에 의한 Cr(VI) 이온의 탈착특성을 조사한 결과 3 M HCl에서 높은 탈착효율을 나타내었다. 결과적으로, XAD-16-CTA 킬레이트 수지는 여러 가지 금속이온이 혼합된 금속마감산업 인공폐액 중 Cr(VI) 이온의 선택적 분리, 농축 및 회수에 매우 유용함을 알 수 있었다.

• 한국결정성장학회지
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• 제12권5호
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• pp.229-233
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• 2002

유기화학적 방법인 착체중합법을 이용하여 나노사이즈의 ZnO 분말을 저온에서 합성하였다. 고분자 전구체는 Zn nitrate hexahydrate를 사용하였고, chelating agent로서 citric acid를 reaction medium으로서 ethylene glycol을 혼합하여 제조하였다. 고분자 전구체를 300~$700^{\circ}C$의 온도범위에서 3시간 동안 하소하였으며, 열분해와 결정화 과정을 TG-DTA, FI-IR과 XRD 등을 이용하여 분석하였다. 결정화 온도에 따른 입자의 형상이나 크기를 SEM, TEM의 분석 및 Scherrer's equation을 이용한 계산을 통하여 관찰 및 비교를 하였다. ZnO의 결정화는 $300^{\circ}C$부터 시작되었고, $400^{\circ}C$에서 완전히 합성되었음을 알 수 있었다. 400~$700^{\circ}C$에서 하소된 ZnO 입자들은 대부분 둥근 형태로 균일하게 분포되었으며, $400^{\circ}C$에서 하소된 분말의 평균입도는 약 30~40nm를 보였다. 일반적으로 온도의 상승에 따라 입경이 증가되는 일반적인 경향이 관찰되었다.

• 대한화학회지
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• 제53권2호
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• pp.152-158
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• 2009

산성 용액에서 $Ca^{2+},\;Mg^{2+},\;Mn^{2+},\;Fe^{3+},\;Co^{2+},\;Ni^{2+},\;Cu^{2+}$ 및 $Zn^{2+}$와 Cefpodoxime proxetil (CFP)의 상 호작용을 분광학적으로 조사한 결과 1:1 착물이 형성됨을 알 수 있다. 순수한 약품의 흡수스펙트럼은 270과 345 nm에서 두 개의 현저한 봉오리를 보였다. 여러 pH에서 스펙트럼은 두 개의 isosbestic 점(305 과 330 nm)을 나타내었다. 이는 용액상에서 약품의 쯔비터 이온이 존재함을 의미한다. 다른 농도의 금 속이온에서 CFP의 형광방출 스펙트럼은 chelating enhancement fluorescence(CHEF)효과에 의해 형광강 도가 증가함을 알 수 있었다. 착체의 화학량론은 Job’'s 와 Benesi-Hildebrand 방법에 의해 결정되었다. 착 체의 안정도는 다음 순서와 같다. $Ca^{2+}\;<\;Mg^{2+}\;<\;Co^{2+}\;<\;Ni^{2+}\;<\;Zn^{2+}\;<\;Mn^{2+}\;<\;Cu^{2+}\;<\;Fe^{3+}$.

• Journal of Ecology and Environment
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• 제30권3호
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• pp.271-276
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• 2007

A simple and efficient protocol was developed for culturing Cu-tolerant and Cu-accumulating plants via pre-adaptation to Cu during plant tissue culture. We induced multiple shoots from begonia (Begonia evansiana Andr.) leaf explants on MS medium supplemented with naphtaieneacetic acid and benzyladenine. After 3 months, small plantlets were transferred to MS medium supplemented with $100{\mu}M\;CuCl_2$ for pre-adaptation to Cu and cultured for 5 months. Then, these plantlets were individually planted in pots containing artificial soil. An additional 500 mg of Cu dissolved in 1/4 strength MS solution was applied to each pot during irrigation over the course of 2 months. We planted pre-adapted and control begonias in soil from the II-Kwang Mine, an abandoned Cu mine in Pusan, Korea, to examine their ability to tolerate and accumulate Cu for phytore-mediation. Pre-adapted begonias accumulated $1,200{\mu}g$ Cu/g dry root tissue over the course of 45 days. On the other hand, non-Cu-adapted controls accumulated only $85{\mu}g$ Cu/g dry root tissue. To enhance Cu extraction, chelating agents, ethylenediamine tetraacetic acid (EDTA)-dipotassiun and pyridine-2,6-dicarboxylic acid (PDA), were applied. While the chelating agents did not enhance accumulation of Cu in the roots of control begonias, EDTA application increased the level of Cu in the roots of pre-adapted begonias twofold (to $2,500{\mu}g$ Cu/g dry root tissue). Because pre-adapted begonias accumulated a large amount of Cu, mainly in their roots, they could be used for phytostabilization of Cu-contaminated soils. In addition, as a flowering plant, begonias can be used to create aesthetically pleasing remediation sites.

• Restorative Dentistry and Endodontics
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• 제42권2호
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• pp.105-110
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• 2017

Objectives: This study investigated the cleaning ability of ultrasonically activated irrigation (UAI) and a novel activation system with reciprocating motion (EC, EasyClean, Easy Equipamentos $Odontol\acute{o}gicos$) when used with a relatively new chelating agent (QMix, Dentsply). In addition, the effect of QMix solution when used for a shorter (1 minute) and a longer application time (3 minutes) was investigated. Materials and Methods: Fifty permanent human teeth were prepared with K3 rotary system and 6% sodium hypochlorite. Samples were randomly assigned to five groups (n = 10) according to the final irrigation protocol: G1, negative control (distilled water); G2, positive control (QMix 1 minute); G3, QMix 1 minute/UAI; G4, QMix 1 minute/EC; G5, QMix 3 minutes. Subsequently the teeth were prepared and three photomicrographs were obtained in each root third of root walls, by scanning electron microscopy. Two blinded and pre-calibrated examiners evaluated the images using a four-category scoring system. Data were statistically analyzed using Kruskal-Wallis and Dunn tests (p < 0.05). Results: There were differences among groups (p < 0.05). UAI showed better cleaning ability than EC (p < 0.05). There were improvements when QMix was used with auxiliary devices in comparison with conventional irrigation (p < 0.05). Conventional irrigation for 3 minutes presented significantly better results than its use for 1 minute (p < 0.05). Conclusions: QMix should be used for 1 minute when it is used with UAI, since this final irrigation protocol showed the best performance and also allowed clinical optimization of this procedure.