Ein einfaches Modell zur Simulation der Schwermetallmigration im Boden

The heavy-metal ions are bonded in the soil in different ways. With increasing concentration in the soil the soluble share of heavy-metal ions which is transported by the percolation water into lower soil layers and finally into the ground-water grows. The decrease of the distribution quotients and sorption capacities in the lead > cadmium series can be explained by the form of bonding at the soils which is specific to heavy metals. The elements are fixed as monohydroxo complexes. The heavy-metal retention capacity decreases with increasing time of introduction. For the estimation of the migration of heavy metals in agriculturally used soils it is recommended to combine accumulation models with migration models.     

Trends und Verteilungsmuster in der Schadstoffbelastung von Sedimenten aus östlichen Bundeswasserstraßen

Trends and Patterns in the Contamination of Sediments from Federal Waterways in Eastern Germany The following study presents a concept for a sediment pollution cadastre and the results of systematic investigations of sediment contamination for eight toxic heavy metals and arsenic, as well as for eight classes of organic priority pollutants in all together 21 reaches in the Elbe and Oder waterway systems. Based on data from the years 1991 to 1995; multivariate statistical evaluations were carried out to identify local and temporal trends in the overall contamination. It was possible to differentiate between more non-point and point sources of sediment contamination. Because of the closure of substantial parts of the industry in Eastern Germany and by common sanitation efforts of both the German and the Czech sides since 1990, the situation in the Elbe river system with respect to the heavy metals has improved markedly. For the Oder river system, a comparable trend does not exist yet, and the sediment contamination by heavy metals is stagnant there. As a consequence, the pollution situation in both German parts of the rivers has become similar except for mercury and arsenic. Regarding organic pollutants, the picture is quite different. With the exception of PAHs, Oder sediments are contaminated by organics only to a lower extent and compare better with the ones from unpolluted waters found in parts of Brandenburg and Mecklenburg-Western Pomerania than with those of rivers Elbe, Mulde, and Saale with its tributaries. On the one hand, organic pollution generally also decreased since 1991 in these rivers. On the other hand, due to continuing inputs from plants in the Czech Republic and from old contaminated sites, both in Czechia and Germany, a decreasing trend is not significant or cannot be found at all for such pollutants as HCB, PCBs, or PAHs. The general trends are discussed in detail, e.g., by comparison with quality targets for sediments and suspended matter, and illustrated at the example of individual contaminants being typical for the overall situation.