본 연구에서는 막 결합형 축전식 탈염공정에 적용하기 위하여 고분자 지지체 polyvinylidene fluoride (PVDF)에 상용화된 양이온 및 음이온교환수지를 배합하여 불균질 이온교환막을 제조하였다. PVDF와 이온교환수지의 배합비율을 1 : 1, 1.4 : 1, 2 : 1, 3 : 1로 달리하였으며 SEM, 함수율, 이온교환용량, 메탄올 투과도, 이온전도도를 측정하여 물리화학적 특성을 평가하였다. 특성평가 결과 모든 특성을 고려하였을 때 2 : 1의 배합비율이 가장 우수한 값을 나타내었다. 2 : 1의 배합비율로 제조한 불균질 양이온교환막의 함수율은 34%, 이온교환용량은 1.54 meq/g, 이온전도도는 0.019 S/cm, 메탄올 투과도는 2.28 × 10-7~8.86 × 10-7 cm2/s의 값을 나타내었으며 불균질 음이온교환막에서는 각 각 37%, 2.18 meq/g, 0.034 S/cm, 1.46 × 10-7~8.66 × 10-7 cm2/s의 값을 나타내었다.

전기탈이온(EDI) 공정은 전기투석법과 이온교환수지법을 혼합한 공정이다. 그리고 공정에 이용되는 모듈은 전기투석을 위한 양･음이온교환막이 있으며 두 막 사이에 이온교환수지로 채워지는 형태이다. 그리고 모듈의 성능을 결정하는 인자로는 이온교환수지의 균질한 크기 분포도가 있다. 이러한 점들을 바탕으로 현재 이온교환수지를 글라인딩하여 bipolar형태의 막으로 만든 electroadsorption- deionization(EAD) 공정 모듈이 생산되고 있다. 본 연구는 현재 생산 되고 있는 모듈보다 높은 이온교환능력을 가지며 바인더 역할을 할 수 있는 고 무상의 고분자를 합성하고 이온교환수지대신 이온교환능을 가진 nano particle을 이용하여 복합막을 제조하였다.

상용화되고 있는 이온교환막의 경우 제조공정은 PVC를 분말을 paste로하여 PVC천에 함침시켜 제조하고 있다. 이러한 제조공정은 공정상의 어려움 및 제조 원가의 상승의 요인으로 지적되어 왔고, 이에 최근 PVC 비다공성 필름 지지체 가 특정 모노머에 팽윤하는 성질을 이용하여 함침 시키는 기술이 소개되고 있다. 그러나 이 또한 이온교환기를 도입하기 위해서는 슬폰화반응 및 4급 아민화 반응이 수반되어져야만 한다. 본 연구에서는 이런 이온교환기의 도입공정을 보다 단순화시키기 위한 방안의 제안 및 기초실험과정을 보고하고자 한다.

현재 사용되는 전기탈이온(EDI)공정은 전기투석법과 이온교환수지법을 혼합한 공정이다. 이 공정은 전기투석을 위한 양/음이온교환막이 사용되고 두 막 사이 에 이온교환수지로 채워서 모듈을 제작한다. 전기탈이온공정은 농축수가 강한 산성과 염기성이기 때문에 전극의 손상과 같은 문제점을 초래한다. 이러한 문제 점을 해결하기 위해서 전기흡착탈이온(EAD)공정을 사용한다. 전기흡착탈이온공 정은 반대 전하 이온을 흡착시켜 제거하고 역전을 통해서 탈착시켜 이온교환기 를 재생시키는데, 이 때 재생시간이 필요하다. 따라서, 이온교환막을 Bipolar막으 로 제조하여 해결할 수 있고, 전기탈이온공정과 공통적으로 모듈을 작게 만들기 위해서 나노사이즈의 이온교환입자를 제조하여 별도의 처리과정 없이 성능을 구현하고자하였다. 본 연구는 현재 생산되고 있는 모듈보다 높은 이온교환능력 을 가지며 바인더 역할을 할 수 있는 고무상의 고분자를 합성하고 이온교환수 지대신 이온교환능을 가진 nano particle을 이용하여 복합막을 제조하였다.

전기탈이온(EDI) 공정은 전기투석법과 이온교환수지법을 혼합한 공정이다. 모듈을 제조 하는데 있어 전기투석을 위한 양이온교환막과 음이온교환막이 있으며 그사이에 이온교환수지로 채워지는 형태이다. 이온교환수지의 균질한 크기 분포도 및 당량비 또한 장치의 성능을 결정하는 매우 중요한 인자이다. 이러한 점들을 바탕으로 현재 이온교환수지를 글라인딩하여 bipolar형태의 막으로 만든 electroadsorption-deionization(EAD) 공정 모듈이 생산되고 있다. 지금 생산되고 있는 모듈보다 성능을 더 높이기 위하여 이온교환능력을 가지며 바인더 역할을 할 수 있는 고무상의 고분자를 제조 하였다.

이온교환막이 결합된 축전식 탈염공정(Membrane capacitive deionization, MCDI)을 진행하기 위하여 양이온고분자로는 Sulfonated PPO(Poly(2,6-dimethyl-1.4-phenyl oxide)를 사용하였으며 음이온고분자로써 Aminated Polysulfone을 제조하여 전극 표면에 직접 코팅하여 사용하였다. 코팅여부는 SEM 사진을 통하여 확인하였으며, 성능을 알아보기 위하여 흡/탈착실험을 진행하였다. 유속(15, 25, 30 ml./min), 흡착시간(2, 3, 5, 7 min), 유입수의 농도(100, 200, 300, 500ppm)를 변화시켰는데 그 결과 유속은 느릴수록, 흡착시간은 길어질수록, 유입수의 농도가 낮을수록 염 제거 효율이 높게 나타났다.

기존의 전기탈이온(EDI) 공정은 전기투석법과 이온교환수지법을 혼합한 공정이다. 모듈을 제조 하는데 있어 전기투석을 위한 양이온교환막과 음이온교환막이 있으며 그사이에 이온교환수지로 채워지는 형태이다. 이온교환수지의 균질한 크기 분포도 및 당량비 또한 장치의 성능을 결정하는 매우 중요한 인자이다. 이러한 점들을 바탕으로 현재 이온교환수지를 글라인딩하여 bipolar형태의 막으로 만든 electroadsorption-deionization(EAD) 공정 모듈이 생산되고 있다. 지금 생산되고 있는 모듈보다 성능을 더 높이기 위하여 이온교환능력을 가지며 바인더 역할을 할 수 있는 고무상의 고분자를 제조하였다.

In this study, cation and anion exchange process for performance evaluation was conducted. A pilot plant for the ultrpure water production was installed with the capacity of 25 m3/d. The various production rate and regeneration of ion exchange rate were tested to investigate the design parameters. The test resulst was applied to calculate the operating costs. Changing the flow rate of the ion exchange capacity of the reproduction reviewed the cation exchange process as opposed to the design value is 120 to 164% efficiency , whereas both anion exchange process is 82 to 124% efficiency, respectively. This results can be applied for more large scale plant if the scale up parameters are consdiered. The ion exchange capacity of the application in accordance with the design value characteristic upon application equipment is expected to be needed. In this study, the performance of cation and anion exchange resin process was evaluated with pilot plant(25m3/d). The ion exchange capacity along with space velocity and regeneration volume was evaluated. In results, the operation results was compared with design parameters.

다공성 전극표면에 이온교환고분자를 직접 casting하여 만들어진 복합탄소전극의 성능을 알아보기 위해서 NaCl 수용액을 이용하여 흡착시간, 공급액 농도, 유속, 탈착전압에 따라 흡/탈착실험을 진행하였다. 유입수가 100 mg/L일 때 동일 조건에서 흡착시간이 3분에서 5분으로 증가하면서 제거율이 3% 증가하였는데 이는 유입수의 셀 내부 잔류시간의 증가로 인 한 것으로 사료되며 또한 유속이 15 mL/min에서 23 mL/min 증가하면서 효율이 12% 정도 낮음을 보인 것은 유속이 상승하 면서 유입수의 셀 내부 잔류시간이 짧아지면서 나타나는 영향으로 사료된다. 유입수의 농도를 200 mg/L로 증가하였을 때 효 율은 100 mg/L보다 10~15% 정도 낮은 값을 보였는데, 이는 탈착구간에서 완전탈착이 되지 않아 나타나는 것으로 판단된다.

The reduction of setup time is very important in a lot production system. A punch press is a typical system of lot production. This paper describes a case study to reduce setup time of a punch press manufacturing system. Especially, this case study reduce

In this study, an enthalpy exchanger was coated by silver nano particles via spark discharge method and its antimicrobial and heat exchange efficiencies were evaluated. A method utilizing thermophoretic force was used to improve coating efficiency. Four spark discharge systems were parallel connected and generated silver nano aerosol particles (number concentration of 1.65×10⁸ particles/cc, mode diameter of 31 nm). The coating efficiency was evaluated according to various face velocities (V=0.25~1 m/s) and temperature gradients ((T_hot-T_cold)/T_hot=0~0.09). The maximum coating efficiency was 90.8 % when the face velocity was 0.25 m/s and the temperature gradient was 0.09 (Thot=30℃, Tcold=2℃). Silver nano particles were coated onto the enthalpy exchange element and two different coating amounts of silver nano particles (0.11 ㎍/cm³ , 0.22 ㎍/cm³ ) were tested. For evaluation of antimicrobial efficiency, the suspension test method with E. coli was used. After the suspension test method, CFU(colony forming unit)s of each test sample were counted and colony ratio was calculated. The colony ratio was decreased more quickly when the amount of coated silver particles was increased. When the contact time between each sample and suspension was over 3 hours, antimicrobial efficiencies of coated samples were more over 99.9 % for both amount of silver nano particle(0.11 ㎍/cm³ , 0.22 ㎍/cm³ ). The coating of silver nano particles did not affect the heat exchange efficiency.

HF purification performance of an ion exchange membrane(IEM) was evaluated with 0.5% HF spiked with 10ppb of Fe, Ni and Cu nitrates. The result show that after less than five turnovers through an IEM, the metallic impurity concentration drops below 1ppb. The decrease rate can be fitted to a model assuming the experimental tanks to be continuously stirred tank reaction and that the metallic impurity concentration after the IEM is a function of the single-pass purification efficiency of the membrane, the concentration before purification and the metals desorbed form the IEM. The Concentration after purification was investigated up to a cumulative Fe loading of 300ppb in the 23 liter recirculated loop. It increases linearly vs. cumulative loading and can be explained by the Langmuir theory resulting in a purification efficiency at the equilibrium of close to 99.5% in this loading regime.

Functionalized organic polymers have been used as supports for heterogenized homogeneous catalytic process[1]. Sprcific advantages of using these resins as support reagents have been reviewed[2-4]. These include: -ease of by-product separation from the main reaction product usuallyby simple filtration. -prevention of intermolecular reaction of reactive species or functional groups by simulating high dilution conditions[5]. -utility of the "fish-hook" principle in which a minor component in fished out of a large excess substrate by the insoluble polymer[6]. -the possibility of reusing recovered reagents as well as eliminating the use of volatile or noxious substances[7]. Catalysis by ion-exchange membranes is perhaps one of the latest examples of the use of a polymer-supported species. Conceptually, catalysts on membrane supports offer several possible advantages over traditional powder type systems. They are: (1) Membranes immobilize the catalyst, preventing agglomeration. (2) Filtration is unnecessary for the catalyst separation and so complete catalyst recovery is facilitated. (3) Catalytyic and separation processes can be combined, allowing membrane supported catalysts for the continous flow reactors. reactors.

This study proposes a method to define Information Delivery Manual (IDM) for effective assembly process of modular steel bridge. Assembly process is identified according to assembly step then process algorithm for defining Exchange Requirement (ER) is proposed.

Nitrate-selective ion exchange resin which have bulky tertiary amine as functional group have been synthesized by the reaction of chloromethylated polystyrene-divinylbenzene copolymer and the corresponding tertiary amine [NR3=NEt3 1, N(C2H4OH)3 2] in ethanol, while commercial resin has NMe3 as functional group. The fundamental properties such as bulk density, water content, appearance index, exchange capacity, effective size, uniformity coefficient of synthesized anion exchange resin (1) have been measured. The ion exchange resin (1) and (2) exhibited the better selectivity for nitrate than sulfate in both batch and continuous column experiments.

A kinetic study for nitrate removal by anion exchange resin was performed using continuous column reactors. Kinetic approach from the packed bed showed the reaction rate constant k1 was 0.07∼0.17 ℓ/㎎·hr and maximum exchange quantity q0 was 27.75∼31.81 ㎎/g. The results from the continuous column well agreed with that from the batch reactor. An economic analysis of the water treatment plant by anion exchange resin with a regenerating system was performed to design plant and process. Based on the treatment of 20 ㎎/ℓ nitrate-contained wastewater of 10,000 gallons per day to 2 ㎎/ℓ , total capital cost and total annual cost are estimated to be 836 million wons and 211 million wons, respectively.

A kinetic study for anion exchange was performed for commercially available Cl- type anion exchange resin in use to remove nitrate in water. The obtained results from the batch reactor were applied to the Langmuir and Freundlich models. The constants for Langmuir model were qmax=29.82 and b=0.202, and for Freundlich model were K=5.509 and n=1.772. Langmuir model showed better fit than Frendlich model for the experimental results. Ion exchange reaction rate was also calculated and the approximate first-order reaction, rate constant k1 was 0.16 L/㎎·hr. Effective diffusion coefficient was obtained in the range from 9.67×10 exp (-8) to 1.67×10 exp (-6) ㎠/sec for initial concentration change, and from 6.09×10 exp (-7) to 3.98×10 exp (-6) ㎠/sec for reaction temperature change. Activation energy during the diffusion was calculated as 36 ㎉/㏖.

Ion exchange performance to remove nitrate in water was studied using commercially available strong base anion exchange resin of Cl^- type in the batch and continuous column reactors. The performance was tested using the effluent concentration histories for continuous column or equilibrium concentrations for batch reactor as a function of time until resins were exhausted or reached ionic equilibrium between resin and solution. Anion exchange resin used in this study was more effective than activated carbon or zeolite for nitrate removal. With large resin amount or low initial concentration, nitrate removal characteristics for a typical gel-type resin was increased. On considering the relation between the breakthrough capacity and nitrate concentration of the influent, the use of anion exchange resin were suitable for the higher order water treatment. The nitrate removal of above 90% could be possible until the effluent of above 650 BV was passed to the column. Thus, the commercially available strong base anion exchange resin of Cl^- type used in this study could be effectively used as economic material for treatment of the groundwater. The breakthrough curves showed the sequence of resin selectivity as SO_4^2- > NO_3, > NO^2- > HCO_3^-. The results of this study could be scaled up and used as a design tool for the water purification system of the real groundwater and surface water treatment processes.