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By Walter Z. Tang

This ebook examines the treatability of dangerous wastes by way of assorted physicochemical therapy approaches in line with the Quantitative constitution and job dating (QSAR) among kinetic price constants and molecular descriptors. the writer explores tips to use those types to choose remedy procedures in line with the molecular constitution of natural pollution. He covers the best way to use them to foretell treatability of natural toxins having related molecular buildings through every one therapy technique in either homogeneous and heterogeneous media. The publication is a consultant for assessing the treatability of pollution sooner than designing a remedy procedure and a reference on complex oxidation tactics

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Dimethyl phthalate Polynuclear aromatic hydrocarbons 72. Benzo[a]anthracene 73. Benzo[a]pyrene 74. Chrysene 77. Acenaphthylene 78. Anthracene 79. Benzo[g,h,i]perylene 80. Fluorene 81. Phenanthrene 82. Dibenzo[a,h]anthracene 83. Indeno[1,2,3-c,d]pyrene 84. Pyrene 85. Tetrachloroethylene 86. Toluene 87. Trichloroethylene 88. Vinyl chloride Pesticides and metabolites 89. Aldrin 90. Dieldrin 91. Chlordane 92. 4,4¢-DDT Physicochemical Treatment of Hazardous Wastes 1. Acenaphthlene Dichloropropane and dichloropropylene 2.

Chlorobenzene 37. 1,2-Diphenylhydrazine 8. 1,2,4-Trichlorobenzene 38. Ethylbenzene 9. Hexachlorobenzene 39. Fluoranthene Chlorinated ethanes Haloethers (others than those listed elsewhere) 10. 1,2-Dichloroethane 40. 4-Chlorophenyl phenyl ether 11. 1,1,1-Trichloroethane 41. 4-Bromophenyl phenyl ether 12. Hexachloroethane 42. bis(2-Chloroisopropyl) ether 13. 1,1-Dichloroethane 43. bis(2-Chloroethoxy) methane Halomethanes (others than those listed elsewhere) 14. 1,1,2-Trichloroethane 15. 1,1,2,2-Tetrachloroethane 44.

2 lists the hydrophobic and electronic properties of substituents. The most common substituents include a wide variety of electron-withdrawing substituents, such as –F, –Cl, –Br, –I, –NO2, –SO3H, –CN, and –COOH, and electron-donating substituents, such as –CH3, –C2H5, –NH2, –OH, and –OCH3. These substituents may form thousands of halogenated/nonhalogenated VOCs and SVOCs or non-VOCs. 58 billion pounds of releases occurred in 1997, with two industries reporting more than half of that total. 7 million pounds.

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