Creosote

Assessing the feasibility of sequential aerobic respiration and heterotrophic denitrification of a high-strength mixture of phenol and its derivatives in the field single-well-drift test

Biological degradation of high strength phenol and its derivatives in groundwater is problematic because these compounds are toxic to human and microbes. To evaluate the feasibility of in situ bioremediation using sequential aerobic respiration and heterotrophic denitrification, a field single-well-drift test (SWDT) was conducted in groundwater contaminated with coal tar distillates. To stimulate indigenous phenol degrading microorganisms, a 1400 L of oxygen-saturated test solution containing bromide (3.96 ± 0.179 mmol-Br/L) and nitrate (5.34 ± 0.187 mmol NO₃^--N/L) was injected into an aquifer. After injection of the test solution, significant consumption of dissolved oxygen (DO) was immediately observed; then, degradation of the methyl derivatives o-cresol and m,p-cresol was observed with average zero-order rate coefficients of 0.047 mmol/L/d and 0.23 mmol/L^/d, respectively. After 73% of the injected DO was consumed, significant NO₃^- consumption was observed along with degradation of phenol and the dimethyl derivatives 2,4-xylenol and 3,5-xylenol, which had average zero-order rate coefficients of 0.17 mmol/L/d, 0.060 mmol/L/d, and 0.018 mmol/L/d, respectively. The production of CO₂, NO₂^-, and N₂O along with significant consumption of DO and NO₃^- suggest that phenolic compounds were biologically degraded by sequential aerobic respiration and heterotrophic denitrification. The results of 16s RNA analysis revealed that, after injection of the test solution, a bacterium that shared a 99% 16s rRNA sequence similarity with an uncultured bacterium revealed to be Pseudomonas stutzeri, a facultative heterotrophic denitrifier, was found in the aquifer. Thus, these results suggest that simultaneous injection of DO and NO₃^- is an appropriate in situ bioremediation strategy for degrading mixtures of high-strength phenolic compounds in an aquifer.

Polycyclic aromatic hydrocarbons disrupt axial development in sea urchin embryos through a beta-catenin dependent pathway

Sea urchin (Lytechinus anemesis) embryos were used as an experimental system to investigate the mechanisms of the developmental toxicity of creosote, one of the most widely used wood preserving chemicals, as well as some of its polycyclic aromatic hydrocarbon (PAH) constituents (phenanthrene, fluoranthene, fluorene, pyrene and quinoline). Data suggest that creosote and PAHs affect axial development and patterning in sea urchin embryos by disrupting the regulation of beta-catenin, a crucial transcriptional co-activator of specific target genes in the Wnt/wg signaling pathway. When ciliated blastula stage embryos were exposed to these compounds, they developed into exogastrulae with completely evaginated archentera, demonstrating that these chemicals disrupt axial development and patterning. This response occurred in a dose-dependent fashion, with the EC(50) of creosote for complete exogastrulation being 1.57 ppm, while the EC(50)s of the PAHs ranged from 0.41 ppm (2.0 microM) to 4.33 ppm (33.5 microM). Morphologically, the exogastrulae that developed from embryos exposed to creosote and PAHs appeared to be identical to those that resulted from exposure to lithium chloride, a classical agent known to induce vegetalization and exogastrulation in sea urchin embryos. Immunological studies using antibodies against beta-catenin, a multi-functional protein known to be involved in cell-cell adhesion and cell fate specification during embryonic development, revealed high levels of nuclear accumulation of beta-catenin by cells of creosote- and PAH-exposed embryos, irrespective of their positions in the developing embryo. Dissociated embryonic cells cultured in the presence of these agents rapidly responded in a similar fashion. Since beta-catenin accumulation occurs in nuclei of several types of cancer cells, it is possible this may be a general mechanism by which PAHs affect a variety of different cell types.

Potentiation of 2,6-dinitrotoluene genotoxicity in Fischer 344 rats by pretreatment with coal tar creosote

Pretreatment of male Fischer 344 rats for 5 wk with coal tar creosote, a coal distillation product that is widely used as a wood preservative, potentiated the excretion of urinary mutagens in 2,6-dinitrotoluene (DNT) treated rats. Creosote increased the bioactivation of DNT to significantly greater levels of urinary genotoxic metabolites and/or formed DNA adducts in the liver. A significant increase in the excretion of mutagenic DNT metabolites was observed after the first week of creosote treatment, peaked at wk 3, and then decreased by 33% after 5 wk of treatment. Nevertheless, there was a significant increase (66%) in the formation of DNT-derived DNA adducts in the livers of rats treated with DNT plus creosote at wk 5. Increased cecal beta-glucuronidase activity and reduced small intestinal nitroreductase activity may play roles in the bioactivation of DNT. The excretion of mutagenic DNT metabolites supplies useful information about the bioactivation of DNT; it does not provide a useful index of DNT-derived hepatic DNA adduct formation. Such interactions could be important to predictive risk assessment because the overall cancer risk of such chemical mixtures may exceed the sum of the component risks.