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Acta Alimentaria
Authors:
Zs. Kiss
,
Sz. Kertész
,
C. Hodúr
,
G. Keszthelyi-Szabó
, and
Zs. László

. 2012 389 188 196 Cao , X.H., Ma , J., Shi , X.H. & Ren , Z.J. (2006): Effect of TiO 2 nanoparticle size

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nodes, using a micro-syringe. After the experiment, the resulting particle is removed from the apparatus for further investigation (final moisture content, strength, etc.) The product system under investigation is a titanium dioxide (TiO 2 ) suspension

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AVARRO , S. , 2014 . Minimization of metabenztiazuron residues in leaching water using amended soils and photocatalytic treatment with TiO 2 and ZnO . Journal of Environmental Sciences . 26 . 757 – 764

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. A DAMS , L. K. , L YON , D. Y. & A LVAREZ P. J. J. , 2006 . Comparative eco-toxicity of nanoscale TiO 2 , SiO 2 , and ZnO water suspensions . Water Research . 40 . 3527 – 3532

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partially treated solutions of pesticides using Fe 3+ and TiO 2 solar photo-assisted processes. Ecotoxicology and Environmental Safety 69 , 546–555. Pulgarin C. Evaluating

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Cooper, L. F., Zhou, Y., Takebe, J., Guo, J., Abron, A., Holmen, A., Ellingsen, J. E. (2006) Fluoride modification effects on osteoblast behavior and bone formation at TiO2 grit-blasted c.p. titanium endosseous implants. Biomaterials 27 , 926

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. ( 2009 ). Potent antibacterial activities of Ag/TiO 2 nanocomposite powders synthesized by a one-pot sol–gel method . Environmental Science Technology , 43 : 2905 – 2910 . Zhang , L. , Jiang , Y. , Ding , Y. , Povey , M. , and York , D

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. Z HU , R.R. , W ANG , W.R. , S UN , X.Y , L IU , H. & W ANG , S.L. ( 2010 ): Enzyme activity inhibition and secondary structure disruption of nano-TiO2 on pepsin . Toxicol. in Vitro. , 24 , 1639 – 1647 .

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chitosan/TiO 2 nanocomposites using liquid phase deposition technique . International Journal of NanoScience and Nanotechnology , 4 ( 1 ): 105 – 111 . Bhanarkar , A.D. , Gupta , R.K. , Biniwale , R.B. , and Tamhane , S.M. ( 2014 ). Nitric oxide

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study. Wang et al. (2019) observed the use of Polyaniline/TiO 2 (PANI/TiO 2 ) as an adsorbent to remove methylene blue (MB). The result shows that the maximum adsorption capacity was 458.10 mg g −1 with pH application

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