• 제목/요약/키워드: iron removal

검색결과 445건 처리시간 0.024초

자력에 의한 산성 광산 배수의 처리 - 철(Fe) 성분의 제거- (The Treatment of Acid Mine Drainage - The removal of Iron(Fe) component-)

  • 송근호;이광래
    • 산업기술연구
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    • 제32권A호
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    • pp.21-27
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    • 2012
  • The characteristics of floc formation of the iron(Fe) ions contained in the acid mine drainage was studied for developing the process treating the acid mine drainage. The iron(Fe) ions were formed into flocs by the acid-base reaction with the added $Ca(OH)_2$. The molal ratio of iron(Fe) vs $Ca(OH)_2$ was one of major control variables in treatment; pH change, iron(Fe) ions concentration in treated drainage, DO (dissolved oxygen content). In addition, the air gave much effect on the color of the $iron(Fe)-Ca(OH)_2$ flocs and the attachment to magnet. The attaching to the magnet of the flocs formed in the air was much less than the case without air.

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수중의 철 제거 시 생기는 산화철의 결정구조에 관한 연구 (On the Crystalline Structures of Iron Oxides formed During Removal Process of Iron in Water)

  • 조봉연
    • 대한토목학회논문집
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    • 제26권1B호
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    • pp.107-111
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    • 2006
  • 2종류의 제철 반응조에 있어서, 각종의 반응조건 하에 생성한 산화철을 x-ray회절과 M$\ddot{o}$ssbauer spectroscopy실험으로 철산화 물질을 동정한 결과, 여재 표면에 부착한 철 산화물의 결정은 pH 조건에 관계없이 Ferrihydrite($Fe_5HO_8{\cdot}4H_2O$)이었으며, Batch(회분) 실험에서 생긴 철 산화 물질은 가수분해에 의해 생긴 것으로, Microcrystalline Goethite 이었다.

철, 구리, 은 첨착활성탄을 이용한 브롬산염의 제거 (Removal of Bromate by Iron, Copper and Silver Impregnated Activated Carbon)

  • 최성우;박승조
    • 대한환경공학회지
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    • 제28권2호
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    • pp.178-182
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    • 2006
  • 오존으로 상수처리시 생성되는 소독부산물로써 독성이 강한 브롬산염을 철, 구리, 은 첨착활성탄을 이용하여 제거할 목적으로 회분식과 연속식으로 실험하였다. 활성탄 주입량별 브롬산염 제거 실험에서 각각의 활성탄을 0.1, 0.3, 0.5, 1.0 g씩 주입하여 240분 반응시킨 결과 브롬산염의 제거량은 주입량에 비례하였다. 그리고 산 처리한 활성탄을 사용할 때에는 브롬산염 제거 효율이 약 20%정도 증대되었다. 철, 구리, 은 첨착활성탄은 일반 활성탄보다 약 $30{\sim}50%$ 정도 제거 효율이 좋았으며 특히 철 첨착활성탄은 브롬산염을 약 92%제거하였다. 일반 활성탄을 이용하여 브롬산염을 제거하였을 경우 약 $0.02{\sim}0.45mg\;{BrO_3}^-/g$ AC이였지만 철, 구리, 은 첨착활성탄은 약 $0.9{\sim}1.5mg\;{BrO_3}^-/g$이었다. 연속식 칼럼 반응에서 브롬산염 유입량을 $15.6{\sim}46.8mL/min$으로 변화시켜 EBCT를 1, 2, 3 분으로 실험한 결과 96, 180, 252 시간에서 파과 현상을 보였다.

Preparation of chitosan, sunflower and nano-iron based core shell and its use in dye removal

  • Turgut, Esra;Alayli, Azize;Nadaroglu, Hayrunnisa
    • Advances in environmental research
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    • 제9권2호
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    • pp.135-150
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    • 2020
  • Many industries, such as textiles, chemical refineries, leather, plastics and paper, use different dyes in various process steps. At the same time, these industrial sectors are responsible for discharging contaminants that are harmful and toxic to humans and microorganisms by introducing synthetic dyes into wastewater. Of these dyes, methylene blue dye, which is classified as basic dyes, is accepted as a model dye. For this reason, methylene blue dye was selected in the study and its removal from the water was studied. In this study, two efficient biosorbents were developed from chitosan and sunflower waste, an agro-industrial waste and modified using iron nanoparticles. The biosorption efficiency was evaluated for methylene blue (MB) dye removal from aqueous solution under various parameters such as treating agent, solution pH, biosorbent dosage, contact time, initial dye concentration and temperature. We investigated the kinetic properties of dye removal from water for Chitosan-Sunflower (CS), Chitosan-Sunflower-Nanoiron (CSN). When the wavelength of MB dye was spectrophotometrically scanned, the maximum absorbance was determined as 660 nm. For the core shell biosorbents we obtained, we found that the optimum time for removal of MB from wastewater was 60 min. The pH of the best pH was determined as 5 in the studied pH. The most suitable temperature for the experiment was determined as 30℃. SEM-EDAX, TEM, XRD, and FTIR techniques were used to characterize biosorbents produced and modified in the experimental stage and to monitor the change of biosorbent after dye removal. The interactions of the paint with the surface used for removal were explained by these techniques. It was calculated that 80% of CS and 88% of CSN removed MB in optimum conditions. Also, the absorption of MB dye onto the surface was investigated by Langmiur and Frendlinch isotherms and it was determined from the results that the removal was more compatible with Langmiur isotherm.

철침착 입상활성탄(Fe-GAC)을 이용한 지하수 내 비소 제거기술 (Arsenic Removal Using Iron-impregnated Ganular Activated Carbon (Fe-GAC) of Groundwater)

  • 윤지영;고경석;유용재;전철민;김규범
    • 자원환경지질
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    • 제43권6호
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    • pp.589-601
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    • 2010
  • 최근 들어 지질기원에 의해 발생되는 지하수내 비소오염이 많이 보고되고 있다. 본 연구에서는 지하수내 비소를 효과적으로 제거하거 위하여 철침착 입상활성탄(Fe-GAC)을 제조하고 이에 대한 흡착능을 평가하였다. Fe-GAC는 질산 염철 용액으로 입상활성탄에 철화합물을 침착시켜 제조하였으며, 이를 이용하여 침착반응시간에 따른 등온흡착, pH에 따른 비소 동력학 흡착반응 및 수처리시스템 예비평가를 위한 칼럼 실험을 수행하였다. 연구결과 침착반응 시간이 최소 12시간 이상에서 비소 제거에 필요한 철의 함량을 가진 Fe-GAC가 제조되었으며, 이들의 흡착능은 등온흡착실험에서도 확인되었다. 입상활성탄에 침착된 철화합물은 XRD 분석결과 대부분 질산염수산화철($Fe_4(OH)_{11}NO_3{\cdot}2H_20$)이었으나 일부 소량의 적철석($Fe_2O_3$)도 관찰되었다. 등온흡착실험은 Langmuir가 Freundlich 모델보다 더 적합하였으며, 모델링 결과 얻어진 Freundlich 분배계수($K_F$) 및 Langmuir 최대 흡착량($Q_m$)은 입상활성탄에 침착된 철 함량과 로그-로그 양의 상관관계를 보여주었다. 동력학 흡착실험 결과 pH 11을 제외한 모든 조건 (pH 4-9)에서 Fe-GAC는 비소에 대해 뛰어난 흡착능을 나타내었으며, 따라서 일반적인 지하수의 pH가 6-8 사이임을 고려하면 Fe-GAC는 비소를 흡착에 매우 효과적인 흡착제로 이용될 것이다. 동력학 모델링 결과 Fe-GAC와 비소의 흡착은 화학적 흡착(chemisorption) 과정을 나타내는 pseudo-second order 모델이 가장 적합하였다. 비소 수처리시스템에 대한 예비 평가를 위하여 칼럼실험을 수행한 결과, 지연계수 482.4이고 분배계수 581.1 L/mg으로 이는 12-24시간 침착반응에서 제조된 Fe-GAC의 Freundlich 등온흡착 모델의 분배계수(511.5-592.5 L/mg)와 유사한 값을 나타내었다. 이러한 연구결과는 향후 지하수를 활용하는 마을상수도 수처리시스템에서 Fe-GAC가 지하수의 비소를 제거하는 뛰어난 흡여재로 사용될 수 있음을 나타내는 것이다.

Arsenic Removal from Water Using Various Adsorbents: Magnetic Ion Exchange Resins, Hydrous Ion Oxide Particles, Granular Ferric Hydroxide, Activated Alumina, Sulfur Modified Iron, and Iron Oxide-Coated Microsand

  • Sinha, Shahnawaz;Amy, Gary;Yoon, Yeo-Min;Her, Nam-Guk
    • Environmental Engineering Research
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    • 제16권3호
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    • pp.165-173
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    • 2011
  • The equilibrium and kinetic adsorption of arsenic on six different adsorbents were investigated with one synthetic and four natural types (two surface and two ground) of water. The adsorbents tested included magnetic ion exchange resins (MIEX), hydrous ion oxide particles (HIOPs), granular ferric hydroxide (GFH), activated alumina (AA), sulfur modified iron (SMI), and iron oxide-coated microsand (IOC-M), which have different physicochemical properties (shape, charge, surface area, size, and metal content). The results showed that adsorption equilibriums were achieved within a contact period of 20 min. The optimal doses of adsorbents determined for a given equilibrium concentration of $C_{eq}=10\;{\mu}g/L$ were 500 mg/L for AA and GFH, 520-1,300 mg/L for MIEX, 1,200 mg/L for HIOPs, 2,500 mg/L for SMI, and 7,500 mg/L for IOC-M at a contact time of 60 min. At these optimal doses, the rate constants of the adsorbents were 3.9, 2.6, 2.5, 1.9, 1.8, and 1.6 1/hr for HIOPs, AA, GFH, MIEX, SMI, and IOC-M, respectively. The presence of silicate significantly reduced the arsenic removal efficiency of HIOPs, AA, and GFH, presumably due to the decrease in chemical binding affinity of arsenic in the presence of silicate. Additional experiments with natural types of water showed that, with the exception of IOC-M, the adsorbents had lower adsorption capacities in ground water than with surface and deionized water, in which the adsorption capacities decreased by approximately 60-95%.

Humic Acid Removal from Water by Iron-coated Sand: A Column Experiment

  • Kim, Hyon-Chong;Park, Seong-Jik;Lee, Chang-Gu;Han, Yong-Un;Park, Jeong-Ann;Kim, Song-Bae
    • Environmental Engineering Research
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    • 제14권1호
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    • pp.41-47
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    • 2009
  • Column experiments were performed in this study to investigate humic acid adhesion to iron oxide-coated sand (ICS) under different experimental conditions including influent humic acid concentration, flow rate, solution pH, and ionic strength/composition. Breakthrough curves of humic acid were obtained by monitoring effluents, and then column capacity for humic acid adsorption ($C_cap$), total adsorption percent (R), and mass of humic acid adsorbed per unit mass of filter media ($q_a$) were quantified from these curves. Results showed that humic acid adhesion was about seven times higher in ICS than in quartz sand at given experimental conditions. This indicates that humic acid removal can be enhanced through the surface charge modification of quartz sand with iron oxide coating. The adhesion of humic acid in ICS was influenced by influent humic acid concentration. $C_cap$ and $q_a$ increased while R decreased with increasing influent humic acid concentration in ICS column. However, the influence of flow rate was not eminent in our experimental conditions. The humic acid adhesion was enhanced with increasing salt concentration of solution. $C_cap$, $q_a$ and R increased in ICS column with increasing salt concentration. On the adhesion of humic acid, the impact of CaCl2 was greater than that of NaCl. Also, the humic acid adhesion to ICS decreased with increasing solution pH. $C_cap$, $q_a$ and R decreased with increasing solution pH. This study demonstrates that humic acid concentration, salt concentration/composition, and solution pH should be controlled carefully in order to improve the ICS column performance for humic acid removal from water.

PVC에 의한 일메나이트 광석 중 선택염화에 의한 Fe의 제거 (Removal of Iron from Ilmenite through Selective Chlorination Using PVC)

  • 손용익;링리에;손호상
    • 자원리싸이클링
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    • 제25권3호
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    • pp.74-81
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    • 2016
  • 고정층 반응기에서 PVC를 염화제로 사용하여 일메나이트 광석 중 철을 선택적으로 제거하기 위한 염화반응에 대하여 조사하였다. 철의 제거율에 미치는 PVC첨가량과 반응온도의 영향에 대하여 조사하였다. 철의 제거율은 PVC 첨가량과 온도가 증가할수록 상승하였다. PVC에서 생성된 HCl가스와 반응한 후의 시편 표면에는 많은 기공이 관찰되었다. 이러한 기공에 의해서 일메나이트 입자의 중앙부분에 있는 철과 반응할 수 있었던 것으로 생각된다. 선택적 염화반응을 속도론적 모델에 의해 조사한 결과 입자 계면에서의 화학반응에 의해서 율속되는 것으로 생각된다. PVC를 사용한 일메나이트의 선택적 염화반응에서 활성화 에너지는 20.47 kJ/mol로 계산되었다.

Removal Efficiency of Arsenic by Adsorbents having Different Type of Metal Oxides

  • Min, Sang-Yoon;Kim, Byeong-Kwon;Park, Sun-Ju;Chang, Yoon-Young;Yang, Jae-Kyu
    • Environmental Engineering Research
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    • 제14권2호
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    • pp.134-139
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    • 2009
  • In this study, oxidation of As (III) as well as removal of total arsenic by adsorbents coated with single oxides or multi-oxides (Fe (III), Mn (IV), Al (III)) was investigated. In addition, multi-functional properties of adsorbents coated with multi-oxides were evaluated. Finally, application of activated carbon impregnated with Fe or Mn-oxides on the treatment of As (III) or As (V) was studied. As (V) adsorption results with adsorbents containing Fe and Al shows that adsorbents containing Fe show a greater removal of As (V) at pH 4 than at pH 7. In contrast adsorbents containing Al shows a favorable removal of As (V) at pH 7 than at pH 4. In case of iron sand, it has a negligible adsorption capacity for As (V) although it contains 217.9 g-Fe/kg-adsorbent, Oxidation result shows that manganese coated sand (MCS) has the greatest As (III) oxidation capacity among all metal oxides at pH 4. Oxidation efficiency of As (III) by IMCS (iron and manganese coated sand) was less than that by MCS. However the total removed amount of arsenic by IMCS was greater than that by MCS.

Evaluation of dynamic behavior of coagulation-flocculation using hydrous ferric oxide for removal of radioactive nuclides in wastewater

  • Kim, Kwang-Wook;Shon, Woo-Jung;Oh, Maeng-Kyo;Yang, Dasom;Foster, Richard I.;Lee, Keun-Young
    • Nuclear Engineering and Technology
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    • 제51권3호
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    • pp.738-745
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    • 2019
  • Coprecipitation using hydrous ferric oxide (HFO) has been effectively used for the removal of radionuclides from radioactive wastewater. This work studied the dynamic behavior of HFO floc formation during the neutralization of acidic ferric iron in the presence of several radionuclides by using a photometric dispersion analyzer (PDA). Then the coagulation-flocculation system using HFO-anionic poly acrylamide (PAM) composite floc system was evaluated and compared in seawater and distilled water to find the effective condition to remove the target nuclides (Co-60, Mn-54, Sb-125, and Ru-106) present in wastewater generated in the severe accident of nuclear power plant like Fukushima Daiichi case. A ferric iron dosage of 10 ppm for the formation of HFO was suitable in terms of fast formation of HFO flocs without induction time, and maximum total removal yield of radioactivity from the wastewater. The settling time of HFO flocs was reduced by changing them to HFO-PAM composite floc. The optimal dosage of anionic PAM for HFO-anionic PAM floc system was approximately 1-10 ppm. The total removal yield of Mn-54, Co-60, Sb-125, Ru-106 radionuclides by the HFO-anionic PAM coagulation-flocculation system was higher in distilled water than in seawater and was more than 99%.