DOI QR코드

DOI QR Code

Bacteriophage removal in various clay minerals and clay-amended soils

  • Park, Jeong-Ann (Environmental Functional Materials & Biocolloids Laboratory, Seoul National University) ;
  • Kang, Jin-Kyu (Environmental Functional Materials & Biocolloids Laboratory, Seoul National University) ;
  • Kim, Jae-Hyun (Environmental Functional Materials & Biocolloids Laboratory, Seoul National University) ;
  • Kim, Song-Bae (Environmental Functional Materials & Biocolloids Laboratory, Seoul National University) ;
  • Yu, Seungho (Research Division for Industry and Environment, Korea Atomic Energy Research Institute) ;
  • Kim, Tae-Hun (Research Division for Industry and Environment, Korea Atomic Energy Research Institute)
  • 투고 : 2014.12.10
  • 심사 : 2015.02.27
  • 발행 : 2015.06.30

초록

The aim of this study was to investigate the bacteriophage removal in various clay minerals and clay-amended soils. Batch experiments in kaolinite, montmorillonite, and bentonite showed that kaolinite was far more effective at the MS2 removal than montmorillonite and bentonite. In kaolinite, the log removal increased from 0.046 to 2.18, with an increase in the adsorbent dose from 0.3 to $50g\;L^{-1}$, whereas the log removals in montmorillonite and bentonite increased from 0.007 to 0.40 and from 0.012 to 0.59, respectively. The MS2 removal in kaolinite-amended silt loam soils was examined at three different soil-to-solution (STS) ratios. Results indicated that the log removal of MS2 increased with an increase in the kaolinite content and the STS ratio. At the STS ratio of 1:10, the log removal of MS2 increased from 2.33 to 2.80 with an increase in the kaolinite content from 0% to 10% in kaolinite-amended soils. The log removals of MS2 at the STS ratios of 1:2 and 1:1 increased from 2.84 to 3.47 and from 3.46 to 4.76, respectively, with an increase in the kaolinite content from 0% to 10%. Results also indicated that the log removals of PhiX174 and $Q{\beta}$ in kaolinite-amended soils were similar to each other, but they were far lower than those of MS2 at all the kaolinite contents. The log removal of PhiX174 increased from 0.16 to 0.32, whereas the log removal of $Q{\beta}$ changed from 0.17 to 0.22 with an increase in the kaolinite content from 0% to 10%.

키워드

참고문헌

  1. Macler BA, Merkle JC. Current knowledge on groundwater microbial pathogens and their control. Hydrogeol. J. 2000;8:29-40. https://doi.org/10.1007/PL00010972
  2. Sinton LW. Microbial contamination of alluvial gravel aquifers by septic tank effluent. Water Air Soil Poll. 1986;28:407-425.
  3. Abu-Ashour J, Joy DM, Lee H, Whiteley HR, Zelin S. Transport of microorganisms through soil. Water Air Soil Poll. 1994;75: 141-158. https://doi.org/10.1007/BF01100406
  4. Mawdsley JL, Bardgett RD, Merry RJ, Pain BF, Theodorou MK. Pathogens in livestock waste, their potential for movement through soil and environmental pollution. Appl. Soil Ecol. 1995;2:1-15. https://doi.org/10.1016/0929-1393(94)00039-A
  5. Moore RS, Taylor DH, Sturman LS, Reddy MM, Fuhs GW. Poliovirus adsorption by 34 minerals and soils. Appl. Environ. Microbiol. 1981;42:963-975.
  6. Schiffenbauer M, Stotzky G. Adsorption of coliphages T1 and T7 to clay minerals. Appl. Environ. Microbiol. 1982;43:590-596.
  7. Sobsey MD, Dean CH, Knuckles ME, Wagner RA. Interaction and survival of enteric viruses in soil materials. Appl. Environ. Microbiol. 1980;40:92-101.
  8. Chattopadhyay D, Chattopadhyay S, Lyon WG, Wilson JT. Effect of surfactants on the survival and sorption of viruses. Environ. Sci. Technol. 2002;36:4017-4024. https://doi.org/10.1021/es0114097
  9. Walshe GE, Pang L, Flury M, Close ME, Flintoft M. Effects of pH, ionic strength, dissolved organic matter, and flow rate on the co-transport of MS2 bacteriophages with kaolinite in gravel aquifer media. Water Res. 2010;44:1255-1269. https://doi.org/10.1016/j.watres.2009.11.034
  10. Chattopadhyay S, Puls RW. Adsorption of bacteriophages on clay minerals. Environ. Sci. Technol. 1999;33:3609-3614. https://doi.org/10.1021/es9811492
  11. Syngouna VI, Chrysikopoulos CV. Interaction between viruses and clays in static and dynamic batch systems. Environ. Sci. Technol. 2010;44:4539-4544. https://doi.org/10.1021/es100107a
  12. Degryse F, Smolders E, Cremers A. Enhanced sorption and fixation of radiocaesium in soils amended with K-bentonites, submitted to wetting-drying cycles. Eur. J. Soil Sci. 2004;55: 513-522. https://doi.org/10.1111/j.1365-2389.2004.00619.x
  13. Jones DR, Paul L, Mitchell NG. Effects of ameliorative measures on the radiocaesium transfer to upland vegetation in the UK. J. Environ. Radioact. 1999;44:55-69. https://doi.org/10.1016/S0265-931X(98)00065-4
  14. Gracia-sanchez A, Alvarez-ayuso E, Rodiriguez-martin F. Sorption of As(V) by some oxyhydroxides and clay minerals: application to its immobilization in two polluted mining soils. Clay Miner. 2002;37:187-194. https://doi.org/10.1180/0009855023710027
  15. Ling W, Shen Q, Gao Y, Gu X, Yang Z. Use of bentonite to control the release of copper from contaminated soils. Soil Res. 2007;45:618-623. https://doi.org/10.1071/SR07079
  16. Jin Y, Pratt E, Yates MV. Effect of mineral colloids on virus transport through saturated sand columns. J. Environ. Qual. 2000;29:532-539.
  17. Leclerc H, Edberg S, Pierzo V, Delattre JM. Bacteriophages as indicators of enteric viruses and public health risk in groundwaters. J. Appl. Microbiol. 2000;88:5-21.
  18. Adams MH. Bacteriophages. New York: Interscience Publishers; 1959.
  19. Uzum C, Shahwan T, Eroglu AE, Hallam KR, Scott TB, Lieberwirth I. Synthesis and characterization of kaolinitesupported zero-valent iron nanoparticles and their application for the removal of aqueous $Cu^{2+}$ and $Co^{2+}$ ions. Appl. Clay Sci. 2009;43:172-181. https://doi.org/10.1016/j.clay.2008.07.030
  20. del Hoyo C, Rives V, Vicente MA. Electronic spectra of phenyl salycilate/montmorillonite and sepiolite complexes obtained be grinding and melting. Spectrosc. Lett. 1995;28:1225-1234. https://doi.org/10.1080/00387019508009460
  21. Seki Y, Yurdakoc K. Adsorption of promethazine hydrochloride with KSF montmorillonite. Adsorption 2006;12:89-100. https://doi.org/10.1007/s10450-006-0141-4
  22. Assaad E, Azzouz A, Nistor D, et al. Metal removal through synergic coagulation-flocculation using an optimized chitosan -montmorillonite system. Appl. Clay Sci. 2007;37:258-274. https://doi.org/10.1016/j.clay.2007.02.007
  23. Chrysikopoulos CV, Syngouna VI. Attachment of bacteriophages MS2 and ${\Pi}$X174 onto kaolinite and montmorillonite: Extended-DLVO interactions. Colloids Surf. B Biointerfaces 2012;92:74-83. https://doi.org/10.1016/j.colsurfb.2011.11.028
  24. Moore RS, Taylor DH, Sturman LS, Reddy MM, Fuhs GW. Poliovirus adsorption by 34 minerals and soils. Appl. Environ. Microbiol. 1981;42:963-975.
  25. Sobsey MD, Shields PA, Hauchman FH, Hazard RL, Caton LW. Survival and transport of hepatitis A virus in soils, groundwater and wastewater. Water Sci. Technol. 1986;18:97-106.
  26. Bhattacharyya KG, Gupta SS. Adsorption of a few heavy metals on natural and modified kaolinite and montmorillonite: a review. Adv. Colloid Interface Sci. 2008;140:114-131. https://doi.org/10.1016/j.cis.2007.12.008
  27. Lipson SM, Stotzky G. Adsorption of reovirus to clay minerals: effects of cation exchange capacity, cation saturation, and surface area. Appl. Environ. Microbiol. 1983;46:673-682.
  28. Fukushima Y. X-ray diffraction study of aqueous montmorillonite emulsion. Clays Clay Miner. 1984;32:320-326. https://doi.org/10.1346/CCMN.1984.0320410
  29. Wan J, Tokunaga TK. Partitioning of clay colloids at air-water interface. J. Colloid Interface Sci. 2002;247:54-61. https://doi.org/10.1006/jcis.2001.8132
  30. Zerda K. Adsorption of Viruses to Charge-Modified Silica [dissertation]. Houston (TX): University of Baylor; 1982.
  31. van Duin J. The single-stranded RNA bacteriophages. In: R. Calendar eds. The bacteriophages. New York: Plenum Press; 1988.
  32. You Y, Vance GF, Sparks DL, Zhuang J, Jin Y. Sorption of MS2 bacteriophage to layered double hydroxides: Effect of reaction time, pH, and competing anions. J. Environ. Qual. 2003;32:2046-2053. https://doi.org/10.2134/jeq2003.2046
  33. Langlet J, Gaboriaud F, Duval JFL, Gantzer C. Aggregation and surface properties of F-specific RNA phages: Implication for membrane filtration processes. Water Res. 2008;42:2769-2777. https://doi.org/10.1016/j.watres.2008.02.007
  34. Hall CE, Maclean EC, Tessman I. Structure and dimensions of bacteriophage-PhiX174 from electron microscopy. J. Mol. Biol. 1959;1:192-194. https://doi.org/10.1016/S0022-2836(59)80050-4
  35. Daems WT, Eigner J, van der Sluys, Cohen JA. The fine structure of the 114-S and 70-S components of bacteriophage phiX174 as revealed by negative and positive staining methods. Biochim. Biophys. Acta. 1962;55:801-817. https://doi.org/10.1016/0006-3002(62)90893-4
  36. Aach HG. Elektrophoretische untersuchungen an mutanten des phagen PhiX 174. Z. Naturforsch. B J. Chem. Sci. 1963;18:290-293.
  37. Shields PA, Farrah SR. Characterization of virus adsorption by using DEAE-Seoharose and Octyl-Sepharose. Appl. Environ. Microbiol. 2002;68:3965-3968. https://doi.org/10.1128/AEM.68.8.3965-3968.2002
  38. Calendar R. The bacteriophage, Vols. 1 and II. New York: Plenum Press; 1988.
  39. Feng YY, Ong SL, Hu JY, Tan XL, Ng WJ. Effects of pH and temperature on the survival of coliphages MS2 and Q${\beta}$. J. Ind. Microbiol. Biotechnol. 2003;30:549-552. https://doi.org/10.1007/s10295-003-0080-y
  40. Park JA, Kang JK, Kim JH, Kim SB, Yu S, Kim TH. Transport and removal of bacteriophages MS2 and PhiX174 in steel slag-amended soils: column experiments and transport model analyses. Environ. Technol. 2014;35:1199-1207. https://doi.org/10.1080/09593330.2013.865061
  41. Kim JH, Park JA, Kim SB. Mg/Al layered double hydroxide for bacteriophage removal in aqueous solution. Water Sci. Technol. 2012:66;761-767. https://doi.org/10.2166/wst.2012.239
  42. Attinti R, Wei J, Kniel K, Sims JT, Jin Y. Virus' (MS2, ${\pi}$X174, and Aichi) attachment on sand measured by atomic force microscopy and their transport through sand columns. Environ. Sci. Technol. 2010;44:2426-2432. https://doi.org/10.1021/es903221p
  43. Zhuang K, Jin Y. Virus retention and transport through Al-oxide coated sand columns: effects of ionic strength and composition. J. Contam. Hydrol. 2003;60:193-209. https://doi.org/10.1016/S0169-7722(02)00087-6
  44. Dowd SE, Pillai SD, Wang S, Corapcioglu MY. Delineating the specific influence of virus isoelectric point and size on virus adsorption and transport through sandy soils. Appl. Environ. Microbiol. 1998;64:405-410.

피인용 문헌

  1. A new approach for remediation of As-contaminated soil: ball mill-based technique vol.23, pp.4, 2016, https://doi.org/10.1007/s11356-015-5896-2
  2. Comparative Analysis of Bacteriophages and Bacteria Removal in Soils and Pyrophyllite-Amended Soils: Column Experiments vol.228, pp.3, 2017, https://doi.org/10.1007/s11270-017-3288-6
  3. A review of the fate and transport of nitrogen, phosphorus, pathogens, and trace organic chemicals in septic systems vol.47, pp.7, 2017, https://doi.org/10.1080/10643389.2017.1327787
  4. Biopolymeric nano/microspheres for selective and reversible adsorption of coronaviruses vol.76, pp.None, 2015, https://doi.org/10.1016/j.msec.2017.03.047
  5. Synthesis conditions of porous clay heterostructure (PCH) optimized for volatile organic compounds (VOC) adsorption vol.36, pp.11, 2019, https://doi.org/10.1007/s11814-019-0369-9
  6. Microbial Interaction with Clay Minerals and Its Environmental and Biotechnological Implications vol.10, pp.10, 2020, https://doi.org/10.3390/min10100861
  7. Porous Clay Heterostructure with Alginate Encapsulation for Toluene Removal vol.11, pp.2, 2015, https://doi.org/10.3390/nano11020388
  8. Assessment of Clay Mineral Attenuation Capacity for Human Viral Pathogens vol.26, pp.1, 2015, https://doi.org/10.1061/(asce)hz.2153-5515.0000643