Polycyclic aromatic hydrocarbons PAHs degradation

Geiselbrecht AD, BP Hedland, MA Tichi, IT Staley (1998) Isolation of marine polycyclic aromatic hydrocarbon (PAH)-degrading Cycloclasticus strains from the Gulf of Mexico and comparison of their PAH degradation ability with that of Puget Sound Cycloclasticus strains. Appl Environ Microbiol 64 4703-4710. 

Bastiaens L, D Springael, P Wattiau, H Harms, R deWachter, H Verachtert, L Diels (2000) Isolation of adherent polycyclic aromatic hydrocarbons (PAH)-degrading bacteria using PAH-sorbing carriers. Appl Environ Microbiol 66 1834-1843. 

In contrast to the results of Bossmann et al., Lindsey and Tarr [31,32] observed equivalent rate constants for polycyclic aromatic hydrocarbon (PAH) degradation with Fenton systems as had been previously observed for PAH reaction with hydroxyl radicals as generated by pulse radiolysis techniques [33], Such kinetic agreement suggests, but does not confirm, equivalent mechanisms. PAHs, unlike 2,4-dimethylaniline, are not expected to directly coordinate iron in aqueous solutions. 

Kastner M, M Breuer-Jammali, B Mahro (1998) Impact of inocnlnm protocols, salinity, and pH on the degradation of polycyclic aromatic hydrocarbons (PAHs) and survival of PAH-degrading bacteria introduced into soil. Appl Environ Microbiol 64 359-362. 

Chemicals degraded by WRF include pesticides such as organochlorines DDT and its very toxic metabolite DDE [8, 9] and organophosphate pesticides such as chlorpyrifos, fonofos and terbufos [10] polychlorinated biphenyls (PCBs) of different degrees of chlorine substitution [11-13], some even to mineralization [14, 15] diverse polycyclic aromatic hydrocarbons (PAHs) in liquid media and from contaminated soils or in complex mixtures such as creosote [16-18] components of munition wastes including TNT and its metabolites DNT [19-23], nitroglycerin [24] and RDX [25]. 

An important extension of this carboxylation strategy has recently been suggested by Zhang and Young (1997) who studied the degradation of two polycyclic aromatic hydrocarbons (PAHs), naphthalene and phenanthrene, in a sulfate-reducing sediment. The naphthalene was found to be converted to 2-naphthoic acid and the phenanthrene to phenanthrene carboxylic acid (see below). Further degradation to C02 was rapid after the presumptive initial carboxylation. Possibly carbon dioxide derivatives can be made so electrophilic by enzymatic interactions (shown... 

Antizar-Ladislao, B., Lopez-Real, J., and Beck, A.J. 2006. Degradation of polycyclic aromatic hydrocarbons (PAHs) in an aged coal tar contaminated soil under in-vessel composting conditions. Environment Pollution, 141 459-68. 

Readman J. W., Mantoura R. F. C., Rhead M. M., and Brown L. (1982) Aquatic distribution and heterotrophic degradation of polycyclic aromatic hydrocarbons (PAHs) in the tamer estuary. Estuar. Coast. Shelf Sci. 14, 369-389. 

A series of related experiments investigated nonionic surfactant sorption onto soil, mechanisms of nonionic surfactant solubilization of polycyclic aromatic hydrocarbon (PAH) compounds from soil, and microbial mineralization of phenanthrene in soil-aqueous systems with nonionic surfactants. Surfactant solubilization of PAH from soil at equilibrium can be characterized with a physicochemical model by using parameters obtained from independent tests in aqueous and soil-aqueous systems. The microbial degradation of phenanthrene in soil-aqueous systems is inhibited by addition of alkyl ethoxylate, alkylphenyl ethoxylate, or sorbitan- (Tween-) type nonionic surfactants at doses that result in micellar solubilization of phenanthrene from soil. Available data suggest that the inhibitory effect on phenanthrene biodegradation is reversible and not a specific, toxic effect. 

Bioremediation has been successfully demonstrated for a variety of contaminant classifications. The majority of the studies have focused on petroleum compounds (BTEX, gasoline, diesel, jet fuel, etc.) because of their widespread occurrence as a contaminant. The other major waste classifications where bioremediation has been successful are solvents (toluene, trichloroethylene, etc.), creosote, pulp and paper, pesticides, textiles, polycyclic aromatic hydrocarbons (PAHs), and polychlorinated biphenyls (PCBs). Table 1 contains a partial list of the microbial genus successfully implemented for these contaminants. For aqueous petroleum contaminants, bacteria and yeasts are the most prevalent degraders. In contaminated soil systems, bacteria and fungi are the microorganisms responsible for degradation. ... 

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