Abstract:Isopropyl
N
-phenylcarbamate (IPC) at 400 pg and 1 μg/ml was mineralized in samples of sewage, but only the lower concentration was mineralized in lake water samples in a 50-day period. IPC at 1 μg/ml disappeared from lake water, but it was converted to organic products. Mineralization of IPC at 400 pg/ml in lake water was enhanced by additions of inorganic nutrients or a mixture of nonchlorinated water pollutants but not by yeast extract or mixtures containing aromatic compounds or exc… Show more
“…The same investigation showed that the acclimation period preceding PNP mineralization in lake water was markedly decreased when a mixture of several inorganic salts was added. The present study shows that the acclimation period for PNP mineralization was shortened by adding P, N, or S. A stimulation of biodegradation of organic chemicals in lake water by added inorganic nutrients, including P, N, Fe, and Mg, has been reported previously (la, [3][4][5]9). It is noteworthy that'the greatest effects noted in the present study were obtained at P concentrations much higher than those typically found in New York lakes, which usually range from 1 to 70 ,ug of P per liter (1).…”
The addition of phosphate, nitrate, or sulfate (each at 10 mM) decreased the acclimation period for the mineralization of low concentrations of p-nitrophenol (PNP) in lake water. Added phosphate shortened the acclimation period for biodegradation of 2 ng to 2 ,ug of PNP per ml in various lake water samples and of 2,4-dichlorophenoxyacetate at 100 ng/ml. Added P enhanced the rate of growth of PNP-mineralizing microorganisms in waters containing 200 ng or 2 ,ug of PNP per ml. We suggest that the effect of P on the acclimation period results from an increase in the growth rate of the initially small population of microorganisms able to mineralize the synthetic chemicals.
“…The same investigation showed that the acclimation period preceding PNP mineralization in lake water was markedly decreased when a mixture of several inorganic salts was added. The present study shows that the acclimation period for PNP mineralization was shortened by adding P, N, or S. A stimulation of biodegradation of organic chemicals in lake water by added inorganic nutrients, including P, N, Fe, and Mg, has been reported previously (la, [3][4][5]9). It is noteworthy that'the greatest effects noted in the present study were obtained at P concentrations much higher than those typically found in New York lakes, which usually range from 1 to 70 ,ug of P per liter (1).…”
The addition of phosphate, nitrate, or sulfate (each at 10 mM) decreased the acclimation period for the mineralization of low concentrations of p-nitrophenol (PNP) in lake water. Added phosphate shortened the acclimation period for biodegradation of 2 ng to 2 ,ug of PNP per ml in various lake water samples and of 2,4-dichlorophenoxyacetate at 100 ng/ml. Added P enhanced the rate of growth of PNP-mineralizing microorganisms in waters containing 200 ng or 2 ,ug of PNP per ml. We suggest that the effect of P on the acclimation period results from an increase in the growth rate of the initially small population of microorganisms able to mineralize the synthetic chemicals.
“…However, the present study provides data from the use of sediment: water microcosms for a comparative study of the effects of past chemical exposure and adaptation of sediment microbial populations on the mineralization rates of six PAHs in both estuarine and freshwater ecosystems. Since the degradation rate of PAHs may be affected by temperature [17,20] and exposure concentration [17,18], in this study these variables were held constant (22°C and 500 ng/g) to facilitate the comparison of PAH mineralization rates among ecosystems and different PAHs.…”
The microbial mineralization of six polycyclic aromatic hydrocarbons (PAHs), containing two to five fused benzene rings, and hexadecane were investigated in sediment: water microcosms which modeled degradation in two freshwater and one estuarine ecosystem. A ranking of the PAHs by order of mineralization rates along with calculated half‐lives (range in weeks) are as follows: naphthalene (2.4‐4.4) ≥ hexadecane (2.2‐4.2) > phenanthrene (4‐18) > 2‐methylnaphthalene (14‐20) > pyrene (34‐>90) ≥ 3‐methylcholanthrene (87‐>200) ≥ benzo[a]pyrene (200‐>300). PAH residues persisted from two to over four times longer in a pristine ecosystem than in an ecosystem chronically exposed to low levels of petroleum hydrocarbons. The mineralization of higher‐molecular‐weight PAHs (> four rings) totaled 0.2 to 6.5% after 8 wk. Relative differences in PAH mineralization among the ecosystems were related to hexadecane mineralization rates, the occurrence and concentration of aromatic hydrocarbon residues in sediments, and elevated populations of hydrocarbon‐degrading microorganisms. Total heterotrophic microbial populations were not good indicators of PAH mineralization rates. Chemical analyses of residues in the microcosms detected the presence of extractable polar metabolites in water and sediments which accounted for 0.1 to 6% of the original PAHs.
“…In a related study, Rubin et al (14) found the extent of mineralization of phenylacetate and p-nitrophenol to be greater in a eutrophic lake than in a mesotrophic lake. The effects of inorganic nutrients have been examined by workers in several laboratories (3,4,7,19). Dibble and Bartha (3) reported that mineral nutrient ratios of 60:1 (C/N) and 800:1 (C/P) resulted in the greatest amount of degradation of oil sludge on soil.…”
We investigated the effect of preincubation of environmental waters amended with inorganic nutrients (nitrogen, phosphorus, and traces of iron and magnesium) on the kinetics of the microbial transformation of phenol, propanil, propyl ester of (2,4-dichlorophenoxy)acetic acid, methyl parathion, Ronnel, and methoxychlor in pond and river waters. No effect on the second-order rate constants for these compounds was observed, although there was an increase in the bacterial populations and the pseudo-first-order rate constants. The use of nutrient-amended waters could be a useful tool for estimating second-order rate constants for an expanded number of compounds. This technique would provide a larger data base for predicting the behavior of xenobiotic compounds in the environment by using currently available mathematical models.
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.