Linear free energy relationships on rate constants for the gas-phase reactions of hydroxyl radicals with PAHs and PCDD/Fs.

Polyparameter linear free energy relationships (LFERs) on rate constants (kOH) for gas-phase reactions of hydroxyl radicals with polycyclic aromatic hydrocarbons (PAHs) and polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) were developed. Quantum chemical descriptors and partial least squares (PLS) regression were used for model development. Acenaphthylene was found to be an outlier and was excluded in the final model development. The cumulative variance of the dependent variable explained by the PLS components and determined by cross-validation (Q2(cum)), for the optimal model, is 0.97, indicating good robustness and predictive power of the model. The main molecular structural factor governing kOH values of PAHs and PCDD/Fs is molecular ability to donate electrons, as described by the energy of the highest occupied molecular orbital (E(HOMO)), the average of net atomic charges on hydrogen atoms (qH(+)), and the average of net atomic charges on carbon atoms (qC). PAH and PCDD/F molecules with high E(HOMO) and low qH(+) and qC values tend to have high log kOH values. The LFER model indicates the temperature dependence of log kOH is weak.

[1]  R. Schwarzenbach,et al.  Linear free energy relationships used to evaluate equilibrium partitioning of organic compounds. , 2001, Environmental science & technology.

[2]  Aleksandar Sabljic,et al.  Predicting the night-time NO3 radical reactivity in the troposphere , 1990 .

[3]  A Sabljić,et al.  Predicting tropospheric degradation of chemicals: from estimation to computation. , 1995, SAR and QSAR in environmental research.

[4]  M Younes,et al.  Specific issues in health risk assessment of endocrine disrupting chemicals and international activities. , 1999, Chemosphere.

[5]  Andreas Klamt,et al.  Estimation of gas-phase hydroxyl radical rate constants of oxygenated compounds based on molecular orbital calculations , 1996 .

[6]  M. Castegnaro,et al.  Effects of ozonation on mutagenic activity of polycyclic aromatic hydrocarbons , 1991, Bulletin of environmental contamination and toxicology.

[7]  K. Schramm,et al.  Data evaluations and quantitative predictive models for vapor pressures of polycyclic aromatic hydrocarbons at different temperatures , 2004, SAR and QSAR in environmental research.

[8]  Jean-Pierre Gauchi,et al.  Comparison of selection methods of explanatory variables in PLS regression with application to manufacturing process data , 2001 .

[9]  W. Klöpffer,et al.  Environmental hazard assessment of chemicals and products. Part VI. Abiotic degradation in the troposphere. , 1996, Chemosphere.

[10]  K. Jones,et al.  PAHs associated with the leaves of three deciduous tree species. I--Concentrations and profiles. , 2000, Environmental pollution.

[11]  S. Wold,et al.  PLS-regression: a basic tool of chemometrics , 2001 .

[12]  R. Hites,et al.  Polychlorinated Dibenzo-p-dioxins and Dibenzofurans: Gas-Phase Hydroxyl Radical Reactions and Related Atmospheric Removal , 1997 .

[13]  J. Arey,et al.  Reactions of hydroxyl radicals and ozone with acenaphthene and acenaphthylene. , 2002, Environmental science & technology.

[14]  J. Arey,et al.  Gas-phase atmospheric chemistry of dibenzo-p-dioxin and dibenzofuran. , 1994, Environmental science & technology.

[15]  S. M. Aschmann,et al.  Kinetics of the reactions of acenaphthene and acenaphthylene and structurally‐related aromatic compounds with OH and NO3 radicals, N2O5 and O3 at 296 ± 2 K , 1988 .

[16]  J. Arey,et al.  Rate constants for the gas-phase reactions of a series of alkylnaphthalenes with the nitrate radical. , 2002, Environmental science & technology.

[17]  R. Atkinson A structure-activity relationship for the estimation of rate constants for the gas-phase reactions of OH radicals with organic compounds , 1987 .

[18]  N. Bunce,et al.  Reaction of naphthalene and its derivatives with hydroxyl radicals in the gas phase , 1997 .

[19]  H. Güsten,et al.  Predicting the abiotic degradability of organic pollutants in the troposphere , 1999 .

[20]  A. Grochowalski PCDDs and PCDFs concentration in combustion gases and bottom ash from incineration of hospital wastes in Poland. , 1998, Chemosphere.

[21]  J. Arey,et al.  Reactions of Gas-Phase Phenanthrene under Simulated Atmospheric Conditions. , 1994, Environmental science & technology.

[22]  Sanja Sekušak,et al.  An ab Initio Study on Reactivity of Fluoroethane with Hydroxyl Radical: Application of G2 Theory† , 1996 .

[23]  H. Güsten,et al.  Prediction of hydroxyl radical reaction rates with organic compounds in the gas phase , 1981 .

[24]  Wen-Jhy Lee,et al.  PAH emission from the incineration of waste oily sludge and PE plastic mixtures , 1995 .

[25]  D. Grosjean,et al.  Environmental persistence of organic compounds estimated from structure-reactivity and linear free-energy relationships. Unsaturated aliphatics , 1992 .

[26]  Y. Kurokawa,et al.  Distribution of polychlorinated dibenzo-p-dioxins and dibenzofurans in various sizes of airborne particles. , 1998, Chemosphere.

[27]  A. Winer,et al.  Kinetics of the gas-phase reactions of the hydroxyl radical with naphthalene, phenanthrene, and anthracene. , 1985, Environmental science & technology.

[28]  Willie J.G.M. Peijnenburg,et al.  Modeling lifetime and degradability of organic compounds in air, soil, and water systems (IUPAC Technical Report) , 2001 .

[29]  L. Klasinc,et al.  Prediction of the abiotic degradability of organic compounds in the troposphere , 1984 .

[30]  J. Arey,et al.  Rate Constants for the Gas-Phase Reactions of the OH Radical with Dichlorobiphenyls, 1-Chlorodibenzo-p-dioxin, 1,2-Dimethoxybenzene, and Diphenyl Ether: Estimation of OH Radical Reaction Rate Constants for PCBs, PCDDs, and PCDFs. , 1995, Environmental science & technology.

[31]  Andreas Klamt,et al.  Estimation of gas-phase hydroxyl radical rate constants of organic compounds from molecular orbital calculations , 1993 .

[32]  M. M. Ramirez-Corredores,et al.  A new concept for the application of linear free energy relationships in catalysis , 2000 .

[33]  S. M. Aschmann,et al.  Kinetics of the reactions of naphthalene and biphenyl with hydroxyl radicals and with ozone at 294 .+-. 1 K. , 1984, Environmental science & technology.

[34]  K. Arcaro,et al.  Antiestrogenicity of environmental polycyclic aromatic hydrocarbons in human breast cancer cells. , 1999, Toxicology.

[35]  R. Grabic,et al.  The effect of oils on PAH, PCDD, PCDF, and PCB emissions from a spark engine fueled with leaded gasoline. , 2000, Chemosphere.

[36]  R. Hites,et al.  OH Reaction Kinetics of Polycyclic Aromatic Hydrocarbons and Polychlorinated Dibenzo-p-dioxins and Dibenzofurans , 1998 .

[37]  D. Truhlar,et al.  Interpolated variational transition-state theory and semiclassical tunneling calculations of the rate constant of the reaction hydroxyl + ethane at 200-3000 K , 1994 .

[38]  R. Atkinson,et al.  Estimation of hydroxyl radical reaction rate constants for gas-phase organic compounds using a structure-reactivity relationship : an update , 1995 .

[39]  S. Casini,et al.  Nondestructive biomarkers of exposure to endocrine disrupting chemicals in endangered species of wildlife. , 1999, Chemosphere.

[40]  S. M. Aschmann,et al.  Kinetics of the reactions of naphthalene, 2‐methylnaphthalene, and 2,3‐dimethylnaphthalene with OH radicals and with O3 at 295 ± 1 K , 1986 .

[41]  Aleksandar Sabljic,et al.  Comparative QSAR study on hydroxyl radical reactivity with unsaturated hydrocarbons: PLS versus MLR , 1996 .

[42]  M. Karelson,et al.  Quantum-Chemical Descriptors in QSAR/QSPR Studies. , 1996, Chemical reviews.

[43]  Klaus R. Liedl,et al.  Reactivity and Regioselectivity of Hydroxyl Radical Addition to Halogenated Ethenes , 1998 .