Abstract:Montmorillonite-benzylamine complexes were formed immediately upon addition of 20 pg to 20 μg of amine per ml of suspensions containing the clay. The extent of amine sorbed was a linear function of equilibrium amine concentration in lake water. Increases in the clay concentration decreased the percentage of the organic compound that was mineralized at amine levels of 20 pg to 200 ng, but not at 20 μg/ml. A larger percentage of the chemical was released from the complex during mineralization in the presence of … Show more
“…In aquatic systems, the solubility of chemicals and the presence of sorptive materials, such as clays and colloidal organic matter, affect the biodegradation [22]. Since the protonated species of erythromycin A (pK a ¼ 8:36) can be strongly adsorbed to clay particles [9,11], the soil-sorbed molecules are less likely accessible to microorganisms.…”
Mineralization of erythromycin A was studied using two differently (14)C-labeled erythromycins A, which were added to aquaculture sediment samples obtained from the two salmon hatchery sites in Washington state. The added erythromycin A did not significantly alter the numbers of the total viable colonies and erythromycin-resistant bacteria. Erythromycin-resistant Pseudomonas species contained a constitutive erythromycin esterase activity contributing to the inactivation of biologically active erythromycin A in aquatic and sediment environments. The initial rate of mineralization of erythromycin A appeared to be governed by the rate of release of soil-sorbed erythromycin A. After a prolonged lag time, the S-curves of erythromycin A mineralization were observed probably because of the increase in the population density metabolizing it. This study suggests that erythromycin A is partially or completely mineralized by the sediment microbial populations.
“…In aquatic systems, the solubility of chemicals and the presence of sorptive materials, such as clays and colloidal organic matter, affect the biodegradation [22]. Since the protonated species of erythromycin A (pK a ¼ 8:36) can be strongly adsorbed to clay particles [9,11], the soil-sorbed molecules are less likely accessible to microorganisms.…”
Mineralization of erythromycin A was studied using two differently (14)C-labeled erythromycins A, which were added to aquaculture sediment samples obtained from the two salmon hatchery sites in Washington state. The added erythromycin A did not significantly alter the numbers of the total viable colonies and erythromycin-resistant bacteria. Erythromycin-resistant Pseudomonas species contained a constitutive erythromycin esterase activity contributing to the inactivation of biologically active erythromycin A in aquatic and sediment environments. The initial rate of mineralization of erythromycin A appeared to be governed by the rate of release of soil-sorbed erythromycin A. After a prolonged lag time, the S-curves of erythromycin A mineralization were observed probably because of the increase in the population density metabolizing it. This study suggests that erythromycin A is partially or completely mineralized by the sediment microbial populations.
“…The [5,6,11,[12][13][14] C]chrysene (specific activity ϭ 47.57 mCi/mmol), [4,5,9,[10][11][12][13][14] C]pyrene (specific activity ϭ 32 mCi/ mmol), and [UL- 14 C]salicylic acid (specific activity ϭ 10 mCi/ mmol) were purchased from Sigma Chemical (St. Louis, MO, USA). 1-Hydroxypyrene, 1-hydroxy-2-naphthoic acid, and NaN 3 were also purchased from Sigma Chemical.…”
Section: Chemicalsmentioning
confidence: 99%
“…By observing systems where aerobic biotransformations are inhibited and comparing them to uninhibited systems, both the bioavailability of compounds for degradation and the impact of biotransformations on hydrophobic organic contaminant availability can be assessed. Sorption to and partitioning into soil organic matter (SOM) have been considered to be the primary interactions limiting the bioavailability of hydrophobic organic contaminants [1,6,[10][11][12][13][14][15].…”
Polycyclic aromatic hydrocarbons (PAHs) are major components of wastes from municipal gas plants and many wood preservatives. Soil contaminated with these wastes is a potential threat to human health because of the carcinogenicity of many PAHs. This study follows the fate of two four-ring PAHs, pyrene and chrysene, in three matrices: an adapted soil (obtained from a site contaminated with PAHs for more than 75 years), an uncontaminated soil (with and without an inoculum of adapted soil), and sand mixed with an inoculum of adapted soil. Radiolabeled pyrene, chrysene, and salicylic acid (a metabolite of PAH biodegradation) were used to trace the mineralization, transformation, extractability, and formation of an unextractable residual over time. Linear approximations of the rates of these processes were made. High-performance liquid chromatography (HPLC) analysis of extracts from inoculated soil showed the transient formation of two known metabolites: 1-hydroxypyrene (from pyrene) and 1-hydroxy-2-naphthoic acid (from chrysene). The amount of extractable label diminished steadily over the course of the study in systems that were not inhibited with sodium azide, whereas the amount of extractable label remained relatively constant in inhibited systems. Correspondingly, the amount of nonextractable residual label generally increased during each incubation in uninhibited systems, whereas the amount of this residual label remained relatively constant in inhibited systems. In contrast, the rate and extent of mineralization varied widely across matrix types. This suggests that alterations of the PAH that impact extractability and residual formation are common, in contrast to mineralization, which was apparently limited to adapted communities.
“…Because PAHs are hydrophobic and sorb strongly to the * To whom correspondence may be addressed (tabak.henry@epa.gov). natural organic matter in sediments [6], the bulk of the contaminant mass resides in a phase separate from degrading microbiota. This makes mass transfer an efficiency-controlling process [7], thus emphasizing the need to study the availability of PAHs to the degrading microorganisms.…”
The widespread contamination by polycyclic aromatic hydrocarbons (PAHs) has created a need for cost-effective bioremediation processes. This research studied a chronically PAH-contaminated estuarine sediment from the East River (ER; NY, USA) characterized by high concentrations of PAHs (approximately 4-190 ppm), sulfide, and metals and a marine sediment from New York/ New Jersey Harbor (NY/NJH; USA) with only trace quantities of PAHs (0.1-0.6 ppm). The focus was to examine the relationship between bioavailability of PAHs and their biological removal in a slurry system. Freshwater and marine sediment toxicity tests were conducted to measure baseline toxicity of both sediments to amphipods, aquatic worms, fathead and sheepshead minnow larvae, and a vascular plant; to determine the cause of toxicity; and to evaluate the effectiveness of the biotreatment strategies in reducing toxicity. Results showed the ER sediment was acutely toxic to all freshwater and marine organisms tested and that the toxicity was mainly caused by sulfide, PAHs, and metals present in the sediment. In spite of the high toxicity, most of the PAH compounds showed significant degradation in the aerobic sediment/water slurry system if the initial high oxygen demand due to the high sulfide content of the sediment was overcome. The removal of PAHs by biodegradation was closely related to their desorbed amount in 90% isopropanol solution during 24 h of contact, while the desorption of model PAH compounds from freshly spiked NY/NJH sediment did not describe the bioavailability of PAHs in the East River sediment well. The research improves our understanding of bioavailability as a controlling factor in bioremediation of PAHs and the potential of aerobic biodegradation for PAH removal and ecotoxicity reduction.
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