Dibenzofuran: Bakterielle Mineralisierung

The degradation of uniformly¹⁴C-labelled dibenzofuran (DBF) by the strainPseudomonas sp HH 69 and a consortium consisting of the DBF-degrading Pseudomonas strain NRM and an accompanying Nocardia-like strain NRH, was monitored in liquid-batch cultures and in different soil samples. Experiments involving the strain and a consortium in aereated liquid cultures (batch process) showed that DBF was utilized as a source of energy and carbon. Thereby, more than 65% of DBF is rapidly converted to CO₂, about 20% to biomass and only about 10% to slow-degrading intermediate metabolites, respectively. The same microorganisms also exhibited comparable degrees of degradation efficiency in various types of soils contaminated with DBF. For instance, DBF, uniformly distributed in sterile soil samples, in concentrations between 0.2 to 200 ppm, was converted to CO₂, within 10 days, to the extent of about 75% by the strainPseudomonas sp. HH 69.     

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Bakterielle Mineralisierung von Dibenzofuran,Dibenzo-p-dioxin und 1,2,4,5-Tetrachlorbenzol in Böden

Quantitative degradation of dibenzofuran (DBF), dibenzo-p-dioxin (DBD), and 1,2,4,5-tetrachlorbenzene (TeCB) by the bacterial strains sphingomonas sp. HH 69, sphingomonas sp. RW1 and pseudomonas sp. PS 14 was investigated by radio-tracer techniques in liquid cultures and especially in samples of different soils. Pure strains converted DBF, DBD and TeCB up to 80% to CO₂ within few days. This degradation occurred not only in aerated liquid cultures but also in heterogeneous soils, with low levels of other pollutatns at favourable pH-values. Rate and degree of the mineralization of DBF, DBD and TeCB were independent of the DBF-, DBD-, or TeCB-concentration in the soils within a broad range. There was obviously a close correlation between the starting concentration of active cells (starting bacterial count) and the rate of degradation of the test substances in soil; by raising the starting bacterial count in the soil samples, mineralization of DBF, DBD, and TeCB, respectively, was clearly accelerated. However, under nearly the same coniditions in more acid soils (pH-values < 4) no significant degradation of DBF, DBD, and TeCB to CO₂ took place. As expected, this difficulty can be overcome by mixing CaCO₂ into the acid soils (liming). Easily utilizable substances like peptone, triolein, and glucose added as special carbon and energy sources to low contaminated soils, had only a small—if any—effect on the mineralization of DBF, DBD, and TeCB. In soils contaminated by a mixture of pollutants, the bacterial strains could develop their degradation capacity only to a limited extent and showed different degradation effects depending on the basic type of contamination. The efficiency of the degradation specialists was thus dependent on the “Chemical Environment” (type and concentration of contaminants present).     

Comparison of four measuring techniques to assess growth inhibition in standardized tests with seven freshwater algae and cyanobacteria

As representatives of primary producers, algae and cyanobacteria play an important role in assessing the risk of chemicals. However, the list of standard algal species commonly used for toxicity testing comprises very few species so that there is an urgent demand to identify further non-standard species which can be used for higher-tier risk assessment in general and the analysis of species sensitivity distributions in particular. In this study, four measuring techniques to assess growth inhibition were compared using five non-standard and two standard algal species and 3,5-dichlorophenol as reference substance. Regarding sensitivity and suitability, the measuring techniques were ranked in the following descending order: delayed fluorescence, prompt fluorescence, photometric absorbance, and microscopic cell count. All five non-standard species fulfilled the validity criteria if tested with delayed fluorescence.     

Spatial and temporal variations in NO2 distributions over Beijing,China measured by imaging differential optical absorption spectroscopy

During the CAREBEIJING campaign in 2006, imaging differential optical absorption spectroscopy (I-DOAS) measurements were made from 08:00 to 16:00 on September 9 and 10 over Beijing, China. Detailed images of the near-surface NO₂ differential slant column density (DSCD) distribution over Beijing were obtained. Images with less than a 30-min temporal resolution showed both horizontal and vertical variations in NO₂ distributions. For DSCD to mixing ratio conversion, path length along the lines of I-DOAS lines of sight was estimated using the light-extinction coefficient and Ångstrom exponent data obtained by a transmissometer and a sunphotometer, respectively. Mixing ratios measured by an in-situ NO₂ analyzer were compared with those estimated by the I-DOAS instrument. The obtained temporal and spatial variations in NO₂ distributions measured by I-DOAS for the two days are interpreted with consideration of the locations of the major NO_x sources and local wind conditions. I-DOAS measurements have been applied in this study for estimating NO₂ distribution over an urban area with multiple and distributed emission sources. Results are obtained for estimated temporal and spatial NO₂ distributions over the urban atmosphere; demonstrating the capability of the I-DOAS technique. We discuss in this paper the use of I-DOAS measurements to estimate the NO₂ distribution over an urban area with multiple distributed emission sources.