Dehalogenation transformation

Hydroxyphthalazin-l(2//)-one is obtained in a smooth reaction between phthalic anhydride and hydrazine hydrate and this is again the starting compound for many 1-substituted and/or 1,4-disubstituted phthalazines. The transformations of 1,4-dichloro-phthalazine, which is prepared in the usual manner, follow a similar pattern as shown for pyridazines in Scheme 110. On the other hand, phthalonitrile is the preferential starting compound for amino- and hydrazino-phthalazines. The most satisfactory synthesis of phthalazine is the reaction between a,a,a, a -tetrachloro-o-xylene and hydrazine sulfate in sulfuric acid (67FRP1438827), alt iough catalytic dehalogenation of 1-chloro- or 1,4-dichloro-phthalazine or oxidation of 1-hydrazinophthalazine also provides the parent compound in moderate yield. 

Degradation of trichloroethylene by anaerobes via reductive dehalogenation can be problematic because a common product is vinyl chloride, a known carcinogen (Ensley 1991). In an anaerobic colunm operated under methanogenic conditions, 100% transformation of injected tetrachloroethylene and trichloroethylene to... 

Reductive dechlorination in combination with the elimination of chloride has been demonstrated in a strain of Clostridium rectum (Ohisa et al. 1982) y-hexachlorocyclohexene formed 1,2,4-trichlorobenzene and y-l,3,4,5,6-pentachlorocyclohexene formed 1,4-dichlorobenzene (Figure 7.69). It was suggested that this reductive dechlorination is coupled to the synthesis of ATP, and this possibility has been clearly demonstrated during the dehalogenation of 3-chlorobenzoate coupled to the oxidation of formate in Desulfomonile tiedjei (Mohn and Tiedje 1991). Combined reduction and elimination has also been demonstrated in methanogenic cultures that transform 1,2-dibromoethane to ethene and 1,2-dibromoethene to ethyne (Belay and Daniels 1987). 

FIGURE 9.29 Transformation of 2-halogenated benzoates to catechol by concomitant decarboxylation and dehalogenation. (From Neilson, A.H. and Allard, A.-S., The Handbook of Environmental Chemistry, Vol. 3R, Springer Verlag, 2002, pp. 1-74. With permission.)... 

One shortcoming in many field studies is a failure to address adequately exposure to toxic transformation products. In efforts to manage time and cost constraints, the concentrations of parent materials and transformation products are often added together to produce a total toxic residue amount. However, it is more appropriate to evaluate individual transformation products as their toxicity may be significantly increased (e.g. active oxons) or decreased (e.g. dehalogenation or dealkylation products) relative to the parent compound. 

Abstract Recent advances in the metal-catalyzed one-electron reduction reactions are described in this chapter. One-electron reduction induced by redox of early transition metals including titanium, vanadium, and lanthanide metals provides a variety of synthetic methods for carbon-carbon bond formation via radical species, as observed in the pinacol coupling, dehalogenation, and related radical-like reactions. The reversible catalytic cycle is achieved by a multi-component catalytic system in combination with a co-reductant and additives, which serve for the recycling, activation, and liberation of the real catalyst and the facilitation of the reaction steps. In the catalytic reductive transformations, the high stereoselectivity is attained by the design of the multi-component catalytic system. This article focuses mostly on the pinacol coupling reaction. 

Scheme 6.176 Nitrocyclohexanol synthesis [332], an a,/ -dibromoester transformation [333], and a dehalogenation reaction [334].

The applications of polyoxometalates in catalytic dehalogenation of halocar-bons have been succinctly reviewed by Hill and coworkers [188]. This reaction involves the photocatalytic transformation of organic halides coupled with the oxidation of sacrificial organic reductants (secondary alcohols or tertiary amides) (Eq. (9)) [189, 190] ... 

Halogenated aliphatics can be partially or completely degraded under anaerobic conditions through a transformation reaction called reductive de-halogenation. Often a co-metabolic degradation step, reductive dehalogenation... 

Transformation of Dicamba under sulfate reducing conditions did occur, but the extent of dehalogenation after O-demethylation remained unclear. 

A project at the University of Arizona (FEDRIP 1996) will study microbial dehalogenation of several compounds, including chloroform. A major part of the study will focus on the facultative anaerobic bacteria Shewanella putrefaciens sp., which is known to catalyze the transformation of carbon tetrachloride to chloroform and other as yet unidentified products. The organic substrates will also contain metals. It is hoped that the end-products from the biochemical treatment can be subjected to a photolytic finishing process that will completely mineralize any remaining halogenated compounds. 

Comparison of this reactivity order with that found in the amination of 2-X-4-phenyl pyrimidines (SCH3 Br = Cl > F > SO2CH3 I > (013)3 > CN see Table 11.5 in Section ll,C,l,d) shows that these reactivity orders differ considerably. The fluoro substituent, especially, which has in the pyrimidine series about the same reactivity order as the chloro or bromo atom, shows in the 1,2,4-triazine series a low ANRORC activity. Comparison of both series of reactivities is, however, a delicate matter, mainly because the yields obtained for the amino compounds in the 1,2,4-triazine series are much lower than those obtained in the pyrimidine series, because of the occurrence of many side reactions, such as ring contraction, dehalogenation, ring transformations, and degenerate ring transformations... 

Transformation and degradation of chlorinated compounds presumably via reductive dehalogenation and subsequent aerobic metaboAsm ... 

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