Reduction of Nitrate using Nanoscale Zero-Valent Iron Supported on the Ion-Exchange Resin

이온교환 능력을 가진 지지체에 부착된 나노 영가철을 이용한 질산성 질소의 환원과 부산물 제거

  • 박희수 (한국과학기술연구원 환경기술연구단) ;
  • 박용민 (한국과학기술연구원 환경기술연구단) ;
  • 조윤성 (한국과학기술연구원 환경기술연구단) ;
  • 오수경 (한국과학기술연구원 환경기술연구단) ;
  • 강상윤 (특허청) ;
  • 유경민 (주식회사 지오윅스) ;
  • 이성재 (주식회사 지오윅스) ;
  • 최용수 (한국과학기술연구원 환경기술연구단) ;
  • 이상협 (한국과학기술연구원 환경기술연구단)
  • Received : 2007.08.10
  • Accepted : 2007.10.29
  • Published : 2007.12.15

Abstract

Nanoscale zero valent ion (nZVI) technology is emerging as an innovative method to treat contaminated groundwater. The activity of nZVI is very high due to their high specific surface area, and supporting this material can help to preserve its chemical nature by inhibiting oxidation. In this study, nZVI particles were attached to granular ion-exchange resin through borohydride reduction of ferrous ions, and chemical reduction of nitrate by this material was investigated as a potential technology to remove nitrate from groundwater. The pore structure and physical characteristics were measured and the change by the adsorption of nZVI was discussed. Batch tests were conducted to characterize the activity of the supported nZVI and the results indicated that the degradation of nitrate appeared to be a pseudo first-order reaction with the observed reaction rate constant of $0.425h^{-1}$ without pH control. The reduction process continued but at a much lower rate with a rate constant of $0.044h^{-1}$, which is likely limited by mass transfer. To assess the effects of other ions commonly found in groundwater, the same experiments were conducted in simulated groundwater with the same level of nitrate. In simulated groundwater, the rate constant was $0.078h^{-1}$ and it also reduced to $0.0021h^{-1}$ in later phase. The major limitation in application of ZVI for nitrate reduction is ammonium production. By using a support material with ion exchange capacity, the problem of ammonium release can be solved. The ammonium was not detected in the batch test, even when other competitive ions such as calcium and potassium existed.

Keywords

Acknowledgement

Supported by : 환경부

References

  1. 연경호 등 (2007) 메조기공 실리카에 부착된 영가철을 이용한 질산성 질소의 환원, 상하수도학회지, 21(1), pp. 139-147
  2. 이순진 등 (2006) 대구 지역 지하수 수질측정망의 수질 특성분석(I). 대한상하수도학회. 한국물환경학회 공동춘계학술발표회 논문집. pp. 1143-1152
  3. 이승학 (2005) 무기 오염물에 대해 부착능과 환원능을 동시에 가지는 반응벽체 내 신물지 개발과 그 적용성 평가, 공학박사 학위논문. 서울대학교
  4. 환경부 (2007) 2006년 지하수 수질측정말 운영결과
  5. Alowitz, M. J.., Scherer, M.M. (2002) Kinetics of nitrate, ritrite, and Cr(VI) reduction by iron metal, Environmental Science & Technology, 36(3), pp.299-306 https://doi.org/10.1021/es011000h
  6. Dash, B.P., Chaudhari, S. (2005) Electrochemical denitrification of simulated groundwater, Water Research, 39, Fp. 4065-4072 https://doi.org/10.1016/j.watres.2005.07.032
  7. Groen, j.C, Perez-Ramirez, l (2004) Critical appraisal of mesoporc characterization by adsortion analysis, Applied Catalysis, General, 268, pp. 121-125 https://doi.org/10.1016/j.apcata.2004.03.031
  8. Huang, Y.H., Zhang, T.e. (2002) Kinetics of nitrate reduction by iron at near neutral pH, Journal of Environmental Enginnering-Asce, 128(7), pp. 604-611 https://doi.org/10.1061/(ASCE)0733-9372(2002)128:7(604)
  9. Li, X.Q, Elliott, D.W., Zhang, wx (2006) Zero-valent iron nanoscales for abatement of environmental pollutants: materials and engineering aspects, Critical Reviews in Solid State and Materials Sciences, 31(4), pp. 111-122 https://doi.org/10.1080/10408430601057611
  10. Liou, Y.H., Lo, S.L., Kuan, W.H., Lin, C.J., Weng, S.e. (2006) Effect of precusor concentration on the characteristics of nanoscale zerovalent iron and its reactivity of nitrate, Water Research, 40(13), pp. 2485-2492 https://doi.org/10.1016/j.watres.2006.04.048
  11. Ponder, S.M., Darab, J.G., Mallouk, T.E. (2000) Remediation of Cr(VI) and Pb(II) aqueous solution using supported, nanoscale zero-valent iron, Environmental Science & Technology, 34(12), pp. 2564-2569 https://doi.org/10.1021/es9911420
  12. Siantar, D.P., Schreier, e.G., Chou, e.S., Reinhard, M. (1996) Treatment of 1,2- dibromo-3-chloropropane and nitrate-contaminated water with zero-valent iron or hydrogen/palladium catalysts. Water Research, 30(10), pp. 2315-2322 https://doi.org/10.1016/0043-1354(96)00120-0
  13. Su, CM., Puls, R.W. (2004) Nitrate reduction by zerovalent iron: effect of Fermate, oxalate, citrate, chloride, sulfate, borate, and phosphate, Environmental Science & Technology, 38(9), pp. 2715-2720 https://doi.org/10.1021/es034650p
  14. Wang, C.B, Zhang, W.X. (1997) Synthesizing nanoscale iron particles for rapid and complete dechlorination of TCE and PCBs, Environmental Science & Technology, 31(7), pp. 2154-2156 https://doi.org/10.1021/es970039c
  15. Yang, G.C.C., and Lee, H.-L. (2005) Chemical reduction of nitrate by nanosized iron: kinetics and pathways, Water Research, 39, pp. 884-894 https://doi.org/10.1016/j.watres.2004.11.030
  16. Zhang, W.X. (2003) Nanoscale iron particles for environmental remediation: An overview, Journal of Nanopartide Research, 5(3-4), pp. 323-332 https://doi.org/10.1023/A:1025520116015