Chlorophenols may be present in soils by land application of biocides or chlorophenol- and chloroguaiacol-containing sludges from pulp bleaching effluent treatment. Polychlorophenols like 2,4,5-trichlorophenol (2,4,5-TCP) are priority pollutants resistant to biodegradation. In this work, the mineralization ( 14 CO 2 evolution) of [U- 14 C-2,4,5]-TCP in soil not previously exposed to chloroorganics was studied. After 60 days of incubation, soil mineralized 15−45% of 2,4,5-TCP when it was exposed to 1, 10, or 100 ppm of this compound. Minimal half-lives for 2,4,5-TCP of 35−170 days were estimated. Less than 2% of mineralization was observed in soil exposed to 500 ppm or in incubations with sterile soil spiked with 10 or 100 ppm of 2,4,5-TCP. Thirty days of preincubation of soil with 10 or 100 ppm of 2,4,5-TCP increased the rate of mineralization of an additional amount of this pollutant. On the other hand, the presence of a mixture of chloroguaiacols decreased the mineralization of trichlorophenol in this soil. No microorganisms were able to grow using 2,4,5-TCP as the sole carbon and energy source. However, the absence of mineralization in sterile soil, the effect of the amount of and the preincubation with 2,4,5-TCP, and the effect of the presence of chloroguaiacols strongly support the involvement of microorganisms in this degradative process.
No takes yet. Share an insight, caveat, or question.
Matus et al. (1996) studied this question.
Synapse has enriched 5 closely related papers on similar clinical questions. Consider them for comparative context: