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Toxicity of Nanomaterials: Can “Computational Nanotoxicology” be helpful? Jackson State University  2009 Dr. Bakhtiyor Rasulev Interdisciplinary Center  for Nanotoxicity 238th ACS National Meeting in Washington, DC   , 2009
[object Object],[object Object],[object Object],[object Object],Nanomaterials in Consumer Products
Objectives ,[object Object],[object Object],[object Object],The main compounds that represents nanomaterials are metal oxides, fullerenes and carbon nanotubes
An Example of Toxicity Pathway for Nanoparticles
Properties of nanoparticles The biological activity of nanoparticles, including toxic and other environmental effects are complex phenomena, which involve the physicochemical properties based on molecular structure, atomic composition of a molecule, in addition to unusual size and surface effects.  The following physicochemical properties of nanoparticles are determine the behavior in environment a :  - CHEMICAL COMPOSITION   (atom composition) - SMALL SIZE   (particle size, size distribution) - LARGE SURFACE   (surface reactivity, surface coatings, surface groups) - CRYSTAL STRUCTURE   (crystallinity) - SOLUBILITY   (solubility in the relevant media) - SHAPE - AGGREGATION   (aggregation status in the relevant media) - PURITY   (purity of sample) In addition, the method of synthesis and/or preparation including postsynthetic modifications also plays important role in nanoparticle behavior. a  Warheit D.B.,  Toxicological Sciences , 2008, 101(2), 183-185
Computational approaches ,[object Object],[object Object],[object Object],Physical  Properties Toxicity Environmental  Distribution Biokinetic Parameters Computational methods can be used to predict the physico-chemical properties, effects of chemicals on the environment, human health, as well as their distribution and fate within the environment and biological organisms
QSAR – what is this? Quantitative Structure-Activity Relationship ,[object Object],[object Object],[object Object],The problem of QSAR is to find coefficients C 0 ,C 1 ,...C n   such that: Biological activity   = C 0 +(C 1 *P 1 )+...+(C n *P n ) and the prediction error is minimized for a list of given m compounds.
QSAR/QSPR: General Approach F:  A =F( S ) Δ A Model Predictivity Prediction – – – – ? – – – – ? New – – – – – – – – – – Te s t – – – – – – – – – – – – – – – – – – – – T r a i n i  n g Descriptors Structure A
Classical QSAR Properties that can be predicted by QSAR analysis: Physico-chemical properties: Boiling points, melting points, density, viscosity, surface tension,   solubility in various solvents , lipophilicity, magnetic susceptibility, retention indices, dipole moments, enthalpy of formation, etc. Biological activity (toxicity):   IC 50 , EC 50 , LD 50 , etc
Types of Molecular Descriptors Electrostatic Geometrical 3-D shape and structure Hybrid descriptors Quantum Chemical Constitutional, Topological 2-D structural formula
Current situation in nanoparticles research   ,[object Object],[object Object],[object Object]
Extension of the traditional (Q)SAR paradigm to nanoparticles ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
The ways towards modeling of nanoparticles properties: ,[object Object],[object Object],[object Object],[object Object]
What was performed by our group: ,[object Object],[object Object],[object Object],[object Object]
Solubility of fullerene C 60  in various solvents ,[object Object],[object Object],[object Object],[object Object]
QSPR modeling of fullerene C 60  solubility in organic solvents. SMILES based optimal descriptors.  (extended set, 122 solvents) Optimal descriptors, calculated with simplified molecular input line entry system have been used for modeling solubility of fullerene C 60  in organic solvents. Statistical characteristics of the model are n = 92, R 2  = 0.861, Q 2  = 0.854, s = 0.401, F = 558 (training set) n = 30, R 2  = 0.891, R 2 pred  = 0.875, s = 0.435, F = 228 (test set). The applied approach entirely based on topological data provides a reliable model for solubility of C 60 . Plot of experimental versus calculated solubility of fullerene C 60  in organic solvents for the training and test sets  (S, 10 4  molar fraction, T = 298 K). Andrey Toropov, Bakhtiyor Rasulev, Danuta Leszczynska, Jerzy Leszczynski, Chemical Physics Letters 444 (2007) 209–214 Andrey A. Toropov, Danuta Leszczynska, Jerzy Leszczynski, Chemical Physics Letters 441 (2007) 119–122
Predicting water solubility and octanol water partition coefficient for carbon nanotubes based on the chiral vector Components of the  chiral vector  of carbon nanotubes have been examined in role of structural descriptors.  Two-variable models of water solubility and octanol water partition coefficient calculated with components of the chiral vectors have  quite good statistical characteristics.  Andrey Toropov,  Danuta Leszczynska, Jerzy Leszczynski, Computational Biology and Chemistry 31 (2007) 127–128 Nanotube  2D-projection If Cn is the chiral vector  then it is defined as Cn= n â1+ m â     The obtained statistical results are in case of  the  water solubility :  n =8,  r 2=0.999,  s =0.053,  F =126611 (training set);  n =8,  r 2=0.999,  s =0.093,  F =674556 (test set)  and in case of  octanol water partition coefficient :  n =8,  r 2=0.999,  s =0.366,  F =2927 (training set);  n =8,  r 2=0.999,  s =0.287,  F  = 5928 (test set).
Results Two-variable models of the water solubility and octanol-water partition coefficient have been calculated by the least squares method. These models are the following log  S  = −5 . 1041 − 3 . 5075 n  − 3 . 5941 m  (1) log  P  = −3 . 9193 + 3 . 7703 n  − 3 . 6001 m  (2) The predictions of the water solubility and octanol water partition coefficient based on the components of the chiral vector are quite good. It is indicates that water solubility and octanol water partition coefficient of CNTs are determined by features of the rolling up of graphite layer. Conclusions Components of chiral vectors of nanotubes can be used as structural descriptors in multiple regression analysis to predict numerical values of water solubility and octanol water partition coefficient.
Quantum-chemical and QSPR modeling of fullerene C 60  solubility first way of solubility estimation – solvent’s descriptor calculations and QSPR ,[object Object],Plot of C 60  solubility data versus HOMO-LUMO gap for both sets.  (a)- alkanes, (b)-alcohols, (c)- other compounds (heteroatom-containing). Tetyana Petrova, Bakhiyor Rasulev, Andrey Toropov, Danuta Leszczynska, Jerzy Leszczynski, Modeling the fullerene C60 solubility in organic solvents: The use of quantum-chemical and topological descriptors in QSPR study, Journal of Nanoparticle Research, 2009,  (submitted)
Quantum-chemical and QSPR modeling of fullerene C 60  solubility another way of solubility estimation  – direct quantum-chemical calculation of C 60 -solvent interactions and solubility ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Tetyana Petrova, Bakhiyor Rasulev, Andrey Toropov, Danuta Leszczynska, Jerzy Leszczynski,  Direct  ab initio  calculation of C60-solvent interactions and predicting the solubility in various organic  solvents, 2009,  (to be prepared)
2.  Study of metal oxides properties in nano-sized form ,[object Object],[object Object],[object Object]
A new approach to the characterization of nanomaterials: Predicting Young’s modulus by correlation weighting of nanomaterials codes Twenty-nine nanomaterials (atom composition and conditions of syntheses) have been studied. Their characteristics were applied to predictions of Young’s modulus values (in GPa).  The obtained statistical characteristics of the models are reasonably good, n=21, r 2  =0.976, s=18.3 GPa, F=761 (training set) and n=8, r 2  =0.895, r 2 pred =0.888, s=34.7 GPa, F=51 (test set). The information on nano substances includes the following characteristics:  (a)  atom composition,  (b)  type of substances (bulk or not), and  (c)  temperature of synthesis. Andrey Toropov, Jerzy Leszczynski, Chemical Physics Letters 433 (2006) 125–129
Toxicity modeling
Toropov A.A., Toropova A., Rasulev B., Puzyn T., Hu X., Hwang H-M., Benfenati E., Leszczynska D., Leszczynski J., QSAR model of toxicity towards  E.coli  bacteria for nanosized oxides by SMILES-based optimal descriptors,  Chemical Biology & Drug Design,  2009 (submitted) QSAR model of toxicity towards  E.coli  bacteria for nanosized oxides by SMILES-based optimal descriptors Toxicity of fourteen metal oxides in nano-sized form towards  E.coli  bacteria has been measured.  To find the structure-toxicity relationship between investigated nanoparticles and toxicity of them the QSAR technique has been applied.  Statistical quality of quantitative structure–activity relationship obtained by the optimal descriptors calculated from simplified molecular input line entry system (SMILES) notations for toxicity towards  E.coli bacteria  (-pLD 50 ) of nanosized oxides are the following: n=7, r 2 =0.99, s=0.053, F=539 (training set); and n=7, r 2 =0.82, s=0.241, F=23 (test set).   First run of the Monte Carlo optimization gave the following model: -pLD 50   = 1.323(  0.031) + 0.274(  0.008) * DCW  n=7, r 2 =0.991, s=0.053, F=539 (training set);  n=7, r 2 =0.823, s=0.241, F=23 (test set). Thus, the SMILES-based optimal descriptors can be used as a tool for prediction of the toxicity nanosized oxides.  This is a first try to model the toxicity relationship for the set of metal oxides in nanosized form, applying quantitative structure-activity methods.
Toropov A.A., Toropova A., Rasulev B., Puzyn T., Hu X., Hwang H-M., Benfenati E., Leszczynska D., Leszczynski J., QSAR model of toxicity towards  E.coli  bacteria for nanosized oxides by SMILES-based optimal descriptors,  Chemical Biology & Drug Design,  2009 (submitted) 0.316 2.826 3.142 5.4808394 O=[V-]O[V-]=O  V 2 O 3 0.172 2.027 2.199 2.5672319 O=[Si]=O  SiO 2 0.101 2.717 2.818 5.0827454 O=[Bi]O[Bi]=O  Bi 2 O 3 -0.223 2.718 2.495 5.0875610 O=[Al]O[Al]=O  Al 2 O 3 0.156 2.717 2.873 5.0833134 O=[La]O[La]=O  La 2 O 3 0.367 2.836 3.203 5.5183250 [Cu]=O  CuO -0.021 2.027 2.006 2.5685177 O=[Sn]=O  SnO 2 Test set 0.003 2.639 2.642 4.7980500 O=[Sb]O[Sb]=O  Sb 2 O 3 -0.044 2.851 2.807 5.5731328 O=[In]O[In]=O  In 2 O 3 0.058 2.093 2.151 2.8084706 O=[Zr]=O  ZrO 2 -0.078 2.946 2.868 5.9178614 O=[Y]O[Y]=O  Y 2 O 3 0.002 2.403 2.405 3.9376291 O=[Fe-]O[Fe-]=O  Fe 2 O 3 -0.014 1.756 1.742 1.5785166 O=[Ti]=O  TiO 2 0.071 3.379 3.450 7.4964167 O=[Zn]  ZnO Training set Expr-Calc Calc, LogLD50 Expr, logLD50 DCW SMILES  Nanooxide
QSAR model of toxicity towards  E.coli  bacteria for nanosized oxides - Another approach.  Puzyn  T. , Rasulev  B. , Hu  X. , Michalkova  A. , Toropov  A. , Hwang  H-M. , Leszczynska  D.  and Leszczynski  J., Cytotoxicity of 14 nano-sized metal oxides: Experimental testing with bacteria  E. coli  and quantitative structure-activity relationships (QSAR) modeling, 2009 (in preparation) The following metal oxides in nanosized form which were selected: ZnO, TiO 2 , SnO 2 , La 2 O 3 , Fe 2 O 3 , CuO, Al 2 O 3 , Sb 2 O 3 , V 2 O 3 , Y 2 O 3 , In 2 O 3 , Bi 2 O 3 , SiO 2  and ZrO 2 .  All of these nanosized metal oxides are widely used in many goods and details that present around us. And all of them are quite toxic to some extent, and for many of them the toxicity increasing accordingly to particle size reducing. In this work we applied quantum-chemical calculations to find parameters that could be responsible for the toxicity properties of these metal oxides. Additionally to quantum-chemical parameters another calculated physico-chemical descriptors have been considered for relationships. Three preliminary models obtained: -Log(LD50)  =  - 0.7397* D_Ox  + 0.0039 *  MSA  + 4.5739  (1) -Log(LD50)  =  - 0.9300* D_Ox  + 0.0235* PSA  + 4.8979  (2) -Log(LD50)  =  - 0.6768* D_Ox + 0.01369* Polarizability2  + 4.6230  (3) N=13 (no ZrO 2 ) D_Ox – oxidation degree MSA – molar surface area (3D) PSA – polarized surface area (2D) Polarizability2 - polarizability 5.3809 5.3809 5.3809 Critical SOR F-value (95%) 23.5000 24.0804 24.6487 Significance-of-regression F-value Yes Yes Yes Significant Regression 0.7308 0.7559 0.7039 q 2  -Cross validated R 2 0.7895 0.7937 0.7976 Adjusted R-squared 0.8246 0.8281 0.8314 R-squared Equation 3 Equation 2 Equation 1 Statistics
[object Object],[object Object],[object Object],[object Object],[object Object]
Acknowledgments The authors would like to thank: National Science Foundation for the NSF-CREST grant (2008) to establish Interdisciplinary Center for Nanotoxicity. The Department of Defense through the U. S. Army Engineer Research and Development Center, Vicksburg, MS, Contract #W912HZ-06-C-0061
List of published and submitted papers ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]

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ACS 238th Meeting, 2009, Rasulev

  • 1. Toxicity of Nanomaterials: Can “Computational Nanotoxicology” be helpful? Jackson State University 2009 Dr. Bakhtiyor Rasulev Interdisciplinary Center for Nanotoxicity 238th ACS National Meeting in Washington, DC , 2009
  • 2.
  • 3.
  • 4. An Example of Toxicity Pathway for Nanoparticles
  • 5. Properties of nanoparticles The biological activity of nanoparticles, including toxic and other environmental effects are complex phenomena, which involve the physicochemical properties based on molecular structure, atomic composition of a molecule, in addition to unusual size and surface effects. The following physicochemical properties of nanoparticles are determine the behavior in environment a : - CHEMICAL COMPOSITION (atom composition) - SMALL SIZE (particle size, size distribution) - LARGE SURFACE (surface reactivity, surface coatings, surface groups) - CRYSTAL STRUCTURE (crystallinity) - SOLUBILITY (solubility in the relevant media) - SHAPE - AGGREGATION (aggregation status in the relevant media) - PURITY (purity of sample) In addition, the method of synthesis and/or preparation including postsynthetic modifications also plays important role in nanoparticle behavior. a Warheit D.B., Toxicological Sciences , 2008, 101(2), 183-185
  • 6.
  • 7.
  • 8. QSAR/QSPR: General Approach F: A =F( S ) Δ A Model Predictivity Prediction – – – – ? – – – – ? New – – – – – – – – – – Te s t – – – – – – – – – – – – – – – – – – – – T r a i n i n g Descriptors Structure A
  • 9. Classical QSAR Properties that can be predicted by QSAR analysis: Physico-chemical properties: Boiling points, melting points, density, viscosity, surface tension, solubility in various solvents , lipophilicity, magnetic susceptibility, retention indices, dipole moments, enthalpy of formation, etc. Biological activity (toxicity): IC 50 , EC 50 , LD 50 , etc
  • 10. Types of Molecular Descriptors Electrostatic Geometrical 3-D shape and structure Hybrid descriptors Quantum Chemical Constitutional, Topological 2-D structural formula
  • 11.
  • 12.
  • 13.
  • 14.
  • 15.
  • 16. QSPR modeling of fullerene C 60 solubility in organic solvents. SMILES based optimal descriptors. (extended set, 122 solvents) Optimal descriptors, calculated with simplified molecular input line entry system have been used for modeling solubility of fullerene C 60 in organic solvents. Statistical characteristics of the model are n = 92, R 2 = 0.861, Q 2 = 0.854, s = 0.401, F = 558 (training set) n = 30, R 2 = 0.891, R 2 pred = 0.875, s = 0.435, F = 228 (test set). The applied approach entirely based on topological data provides a reliable model for solubility of C 60 . Plot of experimental versus calculated solubility of fullerene C 60 in organic solvents for the training and test sets (S, 10 4 molar fraction, T = 298 K). Andrey Toropov, Bakhtiyor Rasulev, Danuta Leszczynska, Jerzy Leszczynski, Chemical Physics Letters 444 (2007) 209–214 Andrey A. Toropov, Danuta Leszczynska, Jerzy Leszczynski, Chemical Physics Letters 441 (2007) 119–122
  • 17. Predicting water solubility and octanol water partition coefficient for carbon nanotubes based on the chiral vector Components of the chiral vector of carbon nanotubes have been examined in role of structural descriptors. Two-variable models of water solubility and octanol water partition coefficient calculated with components of the chiral vectors have quite good statistical characteristics. Andrey Toropov, Danuta Leszczynska, Jerzy Leszczynski, Computational Biology and Chemistry 31 (2007) 127–128 Nanotube 2D-projection If Cn is the chiral vector then it is defined as Cn= n â1+ m â   The obtained statistical results are in case of the water solubility : n =8, r 2=0.999, s =0.053, F =126611 (training set); n =8, r 2=0.999, s =0.093, F =674556 (test set) and in case of octanol water partition coefficient : n =8, r 2=0.999, s =0.366, F =2927 (training set); n =8, r 2=0.999, s =0.287, F = 5928 (test set).
  • 18. Results Two-variable models of the water solubility and octanol-water partition coefficient have been calculated by the least squares method. These models are the following log S = −5 . 1041 − 3 . 5075 n − 3 . 5941 m (1) log P = −3 . 9193 + 3 . 7703 n − 3 . 6001 m (2) The predictions of the water solubility and octanol water partition coefficient based on the components of the chiral vector are quite good. It is indicates that water solubility and octanol water partition coefficient of CNTs are determined by features of the rolling up of graphite layer. Conclusions Components of chiral vectors of nanotubes can be used as structural descriptors in multiple regression analysis to predict numerical values of water solubility and octanol water partition coefficient.
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  • 22. A new approach to the characterization of nanomaterials: Predicting Young’s modulus by correlation weighting of nanomaterials codes Twenty-nine nanomaterials (atom composition and conditions of syntheses) have been studied. Their characteristics were applied to predictions of Young’s modulus values (in GPa). The obtained statistical characteristics of the models are reasonably good, n=21, r 2 =0.976, s=18.3 GPa, F=761 (training set) and n=8, r 2 =0.895, r 2 pred =0.888, s=34.7 GPa, F=51 (test set). The information on nano substances includes the following characteristics: (a) atom composition, (b) type of substances (bulk or not), and (c) temperature of synthesis. Andrey Toropov, Jerzy Leszczynski, Chemical Physics Letters 433 (2006) 125–129
  • 24. Toropov A.A., Toropova A., Rasulev B., Puzyn T., Hu X., Hwang H-M., Benfenati E., Leszczynska D., Leszczynski J., QSAR model of toxicity towards E.coli bacteria for nanosized oxides by SMILES-based optimal descriptors, Chemical Biology & Drug Design, 2009 (submitted) QSAR model of toxicity towards E.coli bacteria for nanosized oxides by SMILES-based optimal descriptors Toxicity of fourteen metal oxides in nano-sized form towards E.coli bacteria has been measured. To find the structure-toxicity relationship between investigated nanoparticles and toxicity of them the QSAR technique has been applied. Statistical quality of quantitative structure–activity relationship obtained by the optimal descriptors calculated from simplified molecular input line entry system (SMILES) notations for toxicity towards E.coli bacteria (-pLD 50 ) of nanosized oxides are the following: n=7, r 2 =0.99, s=0.053, F=539 (training set); and n=7, r 2 =0.82, s=0.241, F=23 (test set). First run of the Monte Carlo optimization gave the following model: -pLD 50 = 1.323(  0.031) + 0.274(  0.008) * DCW n=7, r 2 =0.991, s=0.053, F=539 (training set); n=7, r 2 =0.823, s=0.241, F=23 (test set). Thus, the SMILES-based optimal descriptors can be used as a tool for prediction of the toxicity nanosized oxides. This is a first try to model the toxicity relationship for the set of metal oxides in nanosized form, applying quantitative structure-activity methods.
  • 25. Toropov A.A., Toropova A., Rasulev B., Puzyn T., Hu X., Hwang H-M., Benfenati E., Leszczynska D., Leszczynski J., QSAR model of toxicity towards E.coli bacteria for nanosized oxides by SMILES-based optimal descriptors, Chemical Biology & Drug Design, 2009 (submitted) 0.316 2.826 3.142 5.4808394 O=[V-]O[V-]=O V 2 O 3 0.172 2.027 2.199 2.5672319 O=[Si]=O SiO 2 0.101 2.717 2.818 5.0827454 O=[Bi]O[Bi]=O Bi 2 O 3 -0.223 2.718 2.495 5.0875610 O=[Al]O[Al]=O Al 2 O 3 0.156 2.717 2.873 5.0833134 O=[La]O[La]=O La 2 O 3 0.367 2.836 3.203 5.5183250 [Cu]=O CuO -0.021 2.027 2.006 2.5685177 O=[Sn]=O SnO 2 Test set 0.003 2.639 2.642 4.7980500 O=[Sb]O[Sb]=O Sb 2 O 3 -0.044 2.851 2.807 5.5731328 O=[In]O[In]=O In 2 O 3 0.058 2.093 2.151 2.8084706 O=[Zr]=O ZrO 2 -0.078 2.946 2.868 5.9178614 O=[Y]O[Y]=O Y 2 O 3 0.002 2.403 2.405 3.9376291 O=[Fe-]O[Fe-]=O Fe 2 O 3 -0.014 1.756 1.742 1.5785166 O=[Ti]=O TiO 2 0.071 3.379 3.450 7.4964167 O=[Zn] ZnO Training set Expr-Calc Calc, LogLD50 Expr, logLD50 DCW SMILES Nanooxide
  • 26. QSAR model of toxicity towards E.coli bacteria for nanosized oxides - Another approach. Puzyn T. , Rasulev B. , Hu X. , Michalkova A. , Toropov A. , Hwang H-M. , Leszczynska D. and Leszczynski J., Cytotoxicity of 14 nano-sized metal oxides: Experimental testing with bacteria E. coli and quantitative structure-activity relationships (QSAR) modeling, 2009 (in preparation) The following metal oxides in nanosized form which were selected: ZnO, TiO 2 , SnO 2 , La 2 O 3 , Fe 2 O 3 , CuO, Al 2 O 3 , Sb 2 O 3 , V 2 O 3 , Y 2 O 3 , In 2 O 3 , Bi 2 O 3 , SiO 2 and ZrO 2 . All of these nanosized metal oxides are widely used in many goods and details that present around us. And all of them are quite toxic to some extent, and for many of them the toxicity increasing accordingly to particle size reducing. In this work we applied quantum-chemical calculations to find parameters that could be responsible for the toxicity properties of these metal oxides. Additionally to quantum-chemical parameters another calculated physico-chemical descriptors have been considered for relationships. Three preliminary models obtained: -Log(LD50) = - 0.7397* D_Ox + 0.0039 * MSA + 4.5739 (1) -Log(LD50) = - 0.9300* D_Ox + 0.0235* PSA + 4.8979 (2) -Log(LD50) = - 0.6768* D_Ox + 0.01369* Polarizability2 + 4.6230 (3) N=13 (no ZrO 2 ) D_Ox – oxidation degree MSA – molar surface area (3D) PSA – polarized surface area (2D) Polarizability2 - polarizability 5.3809 5.3809 5.3809 Critical SOR F-value (95%) 23.5000 24.0804 24.6487 Significance-of-regression F-value Yes Yes Yes Significant Regression 0.7308 0.7559 0.7039 q 2 -Cross validated R 2 0.7895 0.7937 0.7976 Adjusted R-squared 0.8246 0.8281 0.8314 R-squared Equation 3 Equation 2 Equation 1 Statistics
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  • 28. Acknowledgments The authors would like to thank: National Science Foundation for the NSF-CREST grant (2008) to establish Interdisciplinary Center for Nanotoxicity. The Department of Defense through the U. S. Army Engineer Research and Development Center, Vicksburg, MS, Contract #W912HZ-06-C-0061
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