Ökotoxikologische Untersuchung von Sedimenten und Schwebstoffen

The potential risk of ground-water contamination through the infiltration of contaminants originating from suspended matter and sediments deposited within flood retention areas in the Upper Rhine valley, as well as subsequent problems for drinking water production, were analyzed by means of the bacterial dehydrogenase activity (DHA; sediment contact test) assay with Arthrobacter globiformis and in a prolonged embryo toxicity assay using zebrafish (Danio rerio). Since the direct uptake of contaminants from particle-bound sources has usually been assumed to play only a minor role in bioaccumulation, the availability of organic extracts to biota has generally been regarded as being overestimated. In order to confirm or discard this hypothesis, organic (acetone) extracts of recently suspended, freeze-dried matter, as well as freeze-dried sediments collected from Rhine flood plains (i.e. soil samples) were compared to corresponding native samples in order to screen for the relative availability of particle-bound contaminants. Whereas a significantly higher ecotoxicological burden was observed for some native soil samples, organic extracts of suspended matter proved to be more toxic than corresponding native samples when compared to organic extracts using each test system. With respect to organic extracts, the suspended matter samples were more toxic than soil samples taken from a rarely flooded site. In contrast to the native samples, the rarely flooded soils revealed a higher toxicity than suspended matter. Therefore, organic extracts did not necessarily overestimate the toxicity of soil and suspended matter samples. Moreover, considerable toxicity of particle-bound contaminants to both bacteria and fish embryos, even in native samples, corroborate the hypothesis that particle-bound contaminants may be more readily available than is generally assumed.     

Enzymatische Umsetzung von Arsenkampfstoffen durch das Pilzenzym Mangan-Peroxidase

Degradation of organo-arsenical chemical warfare agents by fungal enzyme manganese peroxidase. The fungal enzyme manganese peroxidase was used to degrade different organo-arsenical chemical warfare agents in cell-free reaction mixtures (in vitro). The decrease in the concentration of arsenical chemical warfare agents was determined by gas chromatography after derivatization with thiols. All organo-arsenical compounds tested were converted by room temperature for more than 90%. Aliphatic arsenical compounds were attacked more rapidly than aromatic derivatives.     

DDT und Metaboliten in Sedimenten Berliner Gewässer

Sediment samples from rivers and lakes of Berlin (Germany) were analysed for their contamination with organic compounds by means of qualitative and quantitative GC/MS analysis. The principal compounds detected were PAH, organotin derivates, several classes of chlorinated, brominated and mixed halogenated compounds and some of their related metabolites. The DDT metabolites DDD, DDE, DDCN, DDMU and DDMS were the most abundant compounds of halogenated pesticides in a wide range of samples. The main metabolite determined was p,p′-DDD, with concentrations up to 1230 μg/kg dw. The parent DDT compound was detected in only a few samples. The acute cytotoxicity of selected DDT-metabolites was determined with the permanent cell line RTG-2 from the gonads of the rainbow trout (Oncorhynchus mykiss). The results indicate a high cytotoxic potential of these metabolites. The oestrogenic potential was determined by the Dot-Blot/RNase-Protection-Assay an the order from o,p′-DDT>p,p′-DDMS>p,p′-DDMU≥p,p′-DDCN. Risk assessments based on chemical analysis of DDT, DDD and DDE alone is not able to estimate the real toxic potential of DDT and its metabolites. The development of a method for bioassay directed assessment seems to be an effective strategy to solve this problem. Especially scarce or not available data of combinatory effects, differences between different trophic levels and their availability to biota and low knowledge about the metabolism in situ as well as the enantioselective characteristics of most chiral DDT metabolites warrant future analyses.     

Biologische Tests von Bodenextrakten zur Erkennung von Bodenkontaminationen Einstiegswerte und Test-Fensterbreite

Initial values and windows of competence together with a biological test system are introduced to identify soil contaminations. Theinitial values are defined as the amount of extract equivalent to a defined amount of soil (gramm soil equivalent) and the same amount of test medium. This is equivalent to a complete replacement of the test medium with the soil being tested. Theeffect limits should be at least the double standard deviation of the blank values. Based on the values found when testing uncontaminated soils, a higher threshold value has to be established for some test systems. Should no relationship be found to a standard test medium (e.g. agar as a matrix in the Ames assay), the so-calledwindow of competence is defined. Within this window no natural response is found when ex amining uncontaminated soil. For mutagenicity tests, the double spontaneous reversion rate (reversion coefficient of 2) as related o the blank sample is evaluated as the effect limit.     

Einfluß von salzgehalt und temperatur auf entwicklung,wachstum, fortpflanzung und energiebilanz von Artemia salina

The influence of salinity and temperature on various life processes of Artemia salina (L.) from the Great Salt Lake, Utah, USA, was investigated. Hatching rate, hatching success, energetics and metabolism of hatching, growth rate, maturation rate and reproductive rate were measured at all combinations of 4 temperature levels (10°, 15°, 20°, 30°C) and 4 salinity levels (5, 15, 32, 70‰S). Optimal temperature-salinity combinations differ for different life cycle stages and parameters. The hatching rate rises with increased temperature and sinks with increased salinity. Hatching success is optimal at 20°C and 32‰S. Larval growth is best at 30°C and 15‰S; however, the maximum growth is attained at 20°C and 32‰S. Maturation rate, onset of reproduction, interval between clutches as well as the total number of offspring are primarily influenced by temperature, whereas the clutch size is a function of salinity. As the temperature is lowered, the capacity to survive low salinities is decreased. At low temperature, reproduction is only possible at high salinity. The energy consumption of the hatching embryo is primarily determined by the salinity level of the medium and is directly proportional to it. Carbohydrate consumption is under all conditions greatest by weight, but measured by its caloric contribution the relative importance decreases with increased energy drain. Additional energy requirements, particularly during the later stages of hatching, are met by raising fat and protein metabolism, fat being the main energy reserve.     

Bioakkumulation und Deposition von Antimon, Blei und polyzyklischen aromatischen Kohlenwasserstoff-Immissionen

The combination of biomonitoring with standardized grass cultures and deposition monitoring of antimony (Sb), lead (Pb) and 12 polycyclic aromatic hydrocarbon compounds (PAH) was carried out in the conurbation of Munich, Germany in 1993 and resumed at the German-Czech border in 1995. Results from different location types in different areas and years seem to be comparable for Sb and PAH, because relevant background data fit in the same range. Biomonitoring reveals a seasonal course of PAH accumulation. Mean PAH contents are found to be significantly higher in grass cultures at locations along heavily traveled roads, compared to sites in living areas or in a rural background. The traffic related PAH bioaccumulation of both regions fits in the same range, although traffic composition is different and traffic density is ten times smaller at the German-Czech border. Correlation of Pb and Sb bioaccumulation in grass vs. deposition suggested abrasions of brake linings and tires to be one possible emission source. This might be the explanation for the mean contents of Pb and Sb in grass cultures at traffic locations in Munich exceeding those in living or rural areas. Deposition (Bergerhoff method) indicates analogous pollution dynamics in association with traffic. Pb bioaccumulation and deposition along the main roads at the German-Czech border show wider ranges compared to Munich. On the whole, Pb and Sb values at border traffic are found to be lower than those in Munich two years previously.     

Bioakkumulation von Metallen und Stickstoff zwischen 1990 und 2005 in Niedersachsen

Background, aim, and scope Since 1990 the UN ECE Heavy Metals in Mosses Surveys provide data inventories of the atmospheric heavy metal bioaccumulation across Europe. In the survey 2005 the nitrogen accumulation was measured for the first time in most of the participating countries. In Germany, the surveys were conducted in close cooperation of the relevant authorities of both the Federal Republic and the sixteen states. Therefore, statistical evaluations of the moss survey data with regard to the whole German territory and single federal states are of interest. This article concentrates on Lower Saxony, dealing with the mapping of the spatiotemporal trends of metal accumulation from 1990 to 2005, the spatial patterns of nitrogen accumulation in 2005, and the spatial variability of bioaccumulation due to characteristics of the sampling sites and their surroundings. Materials and methods The bioaccumulation of up to 40 trace elements and nitrogen in mosses was determined according to a Europe-wide harmonised methodology. The according experimental protocol regulates the selection of sampling sites and moss species, the chemical analysis and quality control and the classification of the measured values for mapping spatial patterns. In Lower Saxony all sampling sites were described with regard to topographical and ecological characteristics and several criteria to be fulfilled according to the guideline. Together with the measurements this metadata was combined with other information regarding land use in the surroundings of the sampling sites in the WebGIS MossMet. The spatial structure of the metal bioaccumulation was analysed and modelled by variogram analyses and then mapped by applying different Kriging techniques. Furthermore, multi metal indices (MMI) were derived for both the sampling sites and raster maps with help of percentile statistics: The MMI_1990–2005 was calculated for As, Cd, Cr, Cu, Fe, Ni, Pb, Ti, V and Zn. The statistical association of the metal and nitrogen bioaccumulation, site specific characteristics as well as information on land use and emissions was analysed by bivariate nonparametric correlation analysis, contingency tables and Classification and Regression Trees (CART). Results The results of the quality controlled chemical analyses shows a significant decrease of the metal bioaccumulation in Germany from 1990 to 2000 for all elements but Zn. From 2000 to 2005 a further significant decrease can be stated for Cd, Hg and Pb, to most parts non significant increases can be observed for Cr, Cu, Fe, Sb and Zn. Cr thereby exhibits the highest accumulation in 2005 when compared to the results of 1990, 1995 and 2000. The MMI illustrates the temporal trend of the metal bioaccumulation as a whole: From 1990 to 2000 a continuous significant decrease can be observed. From 2000 to 2005 the median of the MMI increases, again significantly, from 3.4 to 4. The N concentration in mosses in Lower Saxony reaches from 1.1 to 1.9?% in dry mass. High N concentrations were detected in agriculturally intensively used areas. Highly significant bivariate correlations between the metal bioaccumulation and land use in the surroundings of the sampling sites were found reaching from 0.3 to 0.5. Other location criteria with similar correlation coefficients/Cramér’s V are moss species, altitude, distance to the North and Baltic Sea and the distance of the sampling site to the nearest tree crown. N only shows negative correlations to urban land use and the distance to the nearest tree. Exemplified for Sb multivariate correlations were furthermore detected by CART. It could be shown that the Sb bioaccumulation interacts with the moss species and the ratio of agriculture, forests and urban areas around the sampling site. Discussion The decrease of the continuously decrease of heavy metals reflects the improving air quality in the past 15 years. Compared to other environmental monitoring and modelling programmes the moss surveys registered increasing concentrations of toxic metal elements between 1990 and 2005, e.?g. Cr. High Cr loads in mosses were also registered in other European countries like in Switzerland. Further investigations are therefore necessary to investigate whether this is due to different emission conditions or biogenic effects (e.?g. as a result of increasing nitrogen depositions). Contrary to deposition measurements that exhibit a higher temporal resolution the moss surveys provide measurement data on a wide range of elements. Some of these elements are important with regard to human-toxicological aspects (e.?g. As, Al, Hg, Sb, V). Due to its ecotoxicological relevance nitrogen was monitored in the European moss survey 2005 for the first time. Compared to the metals regionally high emissions of nitrogen compounds into the atmosphere can be detected in Lower Saxony. The standardised biomonitoring of atmospheric pollution with mosses is an important link between the technical acquisition of depositions and the accumulation in biological material. To claim that the element concentrations in mosses should correlate to a high degree with measured or modelled depositions is not appropriate since these approaches are considering different biological or physical receptors. Nevertheless, the accumulation of air pollutants in terricolous mosses reflects the degree of air pollution which is permanently deposited and affects the system of plants and soils. The degree of correlation thereby depends on the boundary conditions of the physical processes, like regional and site-specific meteorological conditions within the accumulation period, the vertical and horizontal vegetation structure or land use conditions. Conclusions The moss surveys contribute to the heavy metal and the multi-component-model of CLRTAP because they prove on different spatial scales how air pollution control influences the accumulation of emitted substances in environmental subjects of protection like vegetation incl. arable crops. If environmental monitoring is seen as a continuous task and the applied methodology works well as an early warning system then environmental policy is enabled to act in preventative sense and to pursue unexpected developments. No other environmental monitoring programme provides such a wide range of ecotoxicologically relevant elements measured as spatially dense as the case for the moss surveys. The spatial distribution of environmental information is an essential criterion for their usability in terms of political measures for the federal states and the federation. Recommendations and perspectives Heavy Metals in Mosses Surveys are a positive example for environmental monitoring activities reaching across three spatial and administrative levels: regional (e.?g. federal state or natural landscape), nation wide (e.?g. Germany) and continental (e.?g. Europe). In Germany the harmonised and quality controlled moss data are made available via a WebGIS portal. Therefore the moss data may easily be accessed for environmental monitoring purposes and the control of environmental political actions. Hence, the continuous task of environmental monitoring can be met and carried on in the future.     

Aufkommen und Verteilung von Feststoffen in Kanalsystemen

Suspendend solids (SS) are important parameters in the assessment of potential effects of emissions out of sewer systems. This is due to the fact that many pollutants are transported with particles in the sewer systems and therefore are emitted into receiving waters. In this paper, significant emissions in commonly applied sewer systems (combined sewer system [CSS], separate sewer system [SSS]) are mentioned, and typical concentration ranges of SS are listed. Furthermore, data from selected pollutants (lead, polycyclic aromatic hydrocarbons [PAH]) are collected and concentration ranges in typical flow types of the sewer systems are calculated. In the second part of the paper results from pollution load simulations are introduced. The calculations are based on assumptions from literature and were conducted in a hypothetical catchment. Main interest was the comparison of emissions out of SSS and CSS, shown for selected parameters SS, lead and PAH. Results of the pollution load simulation show that emissions for surface runoff related compounds like lead are extremely high in the SSS in comparison to the CSS. This is mainly reasoned by the high elimination rate in the waste water treatment plant (WWTP). In summary, a general answer, which sewer system emits higher pollution loads is not possible. It is extremely dependent on the considered substance and its specific properties and resulting behaviour in the sewer systems. For a first estimation, new classes of substances are distinguished considering their origin (surface runoff versus dry weather flow) and their elimination capacity in the WWTP.     

Adsorption von Blei und Cadmium an Tonen

Clay minerals as major components of soils can adsorb heavy metals. The release of toxic heavy metals such as lead and cadmium into soil presents a serious problem. To evaluate the behaviour of these elements in the environment, it is necessary to develop methods which allow precise analysis of heavy metals. This article compares and optimizes AAS methods for lead and cadmium.