Einsatz des Biolumineszenz-Hemmtests zur Untersuchung kontaminierter Böden

The luminescence inhibition test was applied to contaminated soils. Two different methods were used: The standard sediment elutriate test and the so-called “solid-phase test”. Cadmium sulfate, p-cresol and o-nitroanisole were used as model substances for the contamination of two different soils that show significant differences in grain size. While five of six elutriates acted toxically in the standard elutriate test, the solid-phase test detected only the heavy metal clearly. The interpretation of the solid-phase test results, unlike those of the standard sediment test, is problematic because of the high and varied ground inhibitions of the uncontaminated soils. This suggests that the rate of adsorption of the bacteria depends on the type of soil. An interpretation without an uncontaminated reference seems impossible. A good correlation between the portion of elutriated contaminants and the values of inhibition was only obtained by using the standard elutriate test.     

Transformations of <Emphasis Type="Italic">n</Emphasis>-alkanes from petroleum pollutants in alluvial groundwaters

Investigations presented in this paper were aimed at defining the alterations of n-alkane composition in cases of oil-polluted alluvial sediments. Therefore, oil-polluted groundwater samples, taken in five different time intervals during a period of 28 months, were investigated. Samples of alluvial sediments were taken from two boreholes within an oil refinery at Pancevo, Yugoslavia. In both boreholes significant alterations with characteristic degradation of "oil" n-alkanes with no odd- or even-member predominance were observed, as well as subsequent synthesis of new ones with pronounced even-member predominance, and with maxima at C₁₆ and C₁₈. Since no additional contamination of boreholes was observed by analyses of steranes and triterpanes, the observed changes can only be attributed to microbial activity. It is assumed that for the degradation of oil n-alkanes, as well as for the synthesis of "new" n-alkanes, algae such as dinoflagellates are responsible. This assumption was confirmed by identification of n-alcohols with even-member predominance (C₁₄–C₂₀), by identification of cholesterol, as well as of n-fatty acids with even-member predominance (C₁₄–C₁₈) in the extract with n-alkane even-member predominance. Electronic Publication     

Development and validation of a method for determination of trace levels of alkylphenols and bisphenol A in atmospheric samples

A method has been developed and validated in order to assess the occurrence of the alkylphenols tert-octylphenol and the isomers of technical nonylphenol as well as bisphenol A in gasphase and aerosol samples of a remote area. Gasphase samples were adsorbed to XAD2 resin, aerosol samples were taken on glass fiber filters. After ultrasonic extraction, clean-up by column chromatography and silylation of the analytes, ten nonylphenol peaks were quantified separately using a GC-MSD-SIM method. The absolute limits of detection and determination are in the range of a few pg per compound, which is a prerequisite for the quantification of the analytes in relatively unpolluted air. The precision of the whole analytical method is in the range of 1-17% and the recoveries range from 57% to 80%. Problems were encountered during method development due to the tendency of the analytes to sorb to glass surfaces. Silanisation of glassware was crucial to achieve acceptable recoveries. The widespread use of the analytes in plastic resins resulted in sample contamination. For this reason a careful choice of sampling material was necessary. Measured concentrations in gasphase samples (lower nanogram per m3 range) and aerosol samples (upper picogram per m3 range) are one to three orders of magnitude below already published concentrations.     

Das Problem der Krebsverbreitung und Krebsbekämpfung

The Science of Nature -