Arzneimittel in der aquatischen Umwelt

The German Environmental Advisory Council evaluated German water protection policies in its last environmental report (2004) concluded that despite some great successes in this area there is still considerable need for action. Specifically, diffuse nutrient and chemical substances inputs remain an unsolved problem. The contamination of surface and groundwater with pharmaceuticals has been identified as an environmental risk increasing in pertinence. Pharmaceuticals and their metabolites are being detected in the whole aquatic environment, which they enter through sewage, soil contamination by agriculture, and waste storage facilities. Different pharmaceuticals have been tested for acute toxicity on various aquatic organisms, but almost nothing is known about chronic toxicity of these contaminants. This knowledge, however, is essential for estimating the ecotoxicological potential of pharmaceutical residues. In the opinion of the Environmental Council different strategies are necessary, to reduce the contamination of the environment with pharmaceuticals. Farmers should refrain from using pharmaceuticals for prophylactic purposes or from using hormonally or antibiotically active substances in livestock feed additives, so as to reduce inputs of veterinary drugs. As regards human medications, packaging should better correspond to appropriate dosage amounts, and environmentally responsible disposal measures should be followed. Still under discussion are a programme for the risk evaluation of existing pharmaceuticals and a ban on the use of sewage sludge in agriculture. In the future, improvement of sewage treatment facilities, for instances through membrane technologies, will offer further potential to reduce inputs of hazardous substances.     

Perfluorierte Tenside (PFT) in der aquatischen Umwelt und im Trinkwasser

Recent scientific research on perfluorinated surfactants (PS) revealed their ocurrence in German surface and drinking waters (Skutlarek, Exner, Färber 2006). Since several years, PS have been found in the global environment, especially in animal and human tissues. PS possess extreme persistence against microbiological and chemical degradation and are able to bioaccumulate in animals and humans (Houde et al. 2006). PS concentrations (sum of 12 components) in the Rhine river and its main tributaries were determined below 100 ng/L, but the rivers Ruhr (tributary of the Rhine) and Möhne (tributary of the Ruhr) showed remarkable high concentrations (Ruhr: up to 446 ng/L, Möhne: up to 4385 ng/L). The maximum concentration in drinking waters was 598 ng/L with the major component perfluorooctanoic acid (PFOA). The PS concentrations decreased similarly to the PS concentrations of the raw waters along the flow direction of the Ruhr river. Therefore it seems to be necessary to install legal regulations for these compounds.     

Toxaphen in der Umwelt

Toxaphene is a mixture of more than 200 polychlorinated C₁₀-terpenes. Due to its persistence and long-range transport, it is distributed all over the world. Many of the components are very stable under environmental conditions, while others are easily degraded by UV-light or microorganisms. The main conversion pathway is reductive dechlorination and dehydrochlorination; oxidative degradation possibly occurs only after previous dechlorination. Accumulation especially in the aquatic environment has led in many cases to high residue levels in fish, marine mammals, and sea birds of the northern hemispere. Toxaphene is mutagenic in the Ames test and of high toxicity for fish, but few data are available on the toxicity of single components or their mode of action.     

Körperpflegemittel in der aquatischen Umwelt

Personal care products (PCP) are produced and used in enormous amounts world-wide. In the early 1990s, the annual production volume was more than 550.000 metric tonnes for Germany alone, where liquid bath admixtures, soaps, skin care products, shampoos and dental care products represented the main use patterns of PCPs. These preparations and their ingredients are quasi-continuously introduced into the aquatic environment during regular use, preferably via municipal wastewater treatment plants, and may reach concentrations in the ng/l or μg/l range in surface waters. Furthermore, considerable persistence and bioaccumulation potential has been shown for a number of PCPs (e.g. musk fragrances, disinfectants, antiseptics, some repellents, sunscreen agents). Except for the most important detergents and surfactants used in PCPs, the possible consequences of a chronic exposure of aquatic organisms to these compounds have not been investigated systematically to date. The information on the occurrence of PCPs in different environmental compartments is also rather fragmentary. It is the main objective of this article to provide an overview on the available literature concerning the environmental chemistry and ecotoxicology of selected PCP ingredients (e.g. fragrances, preservatives and antioxidants, disinfectants and antiseptics, repellents, sunscreen agents) The set of data on the occurrence and concentrations of PCPs in the environment and the effects in representative aquatic organisms is insufficient for the majority of the groups of substances considered and does not allow an assessment of their environmental risk. The example of musk fragrances, which represent one of the better analysed groups of PCP ingredients, shows that these compounds tend to accumulate in sediments and biota (including human beings) due to their inherent physicochemical properties, and are likely to attain considerable concentration levels. However, the knowledge about effects in aquatic organisms is rather incomplete and partially contradictory. Furthermore, detailed investigations of their potential reproductive, neuro-, immuno-and genotoxicity are lacking not only for musk fragrances, but also for the overwhelming majority of other PCP ingredients.