[Cyanobacterial toxins in bank filtrate. Under which conditions is their elimination reliable?].

Cyanobacterial toxins are substances produced by cyanobacteria or blue-green algae. They can occur in surface waters worldwide and have to be reliably removed when using affected surface waters as a drinking water source. Bank filtration has been used for 150 years for drinking water (pre-)treatment. It utilizes natural elimination processes like sorption and degradation in the sub-surface. Retention of cells on the sediment surface is the most prominent process for eliminating these primarily cell-bound toxins. Middle to coarse grained sands eliminated more than 99.9 % of intracellular toxins within the first 10 cm of flow path. Elimination of extracellular microcystin during underground passage is mainly due to biodegradation. Reversible adsorption processes do not reduce the total load but lead to longer contact times for extended biodegradation. Laboratory experiments showed that the sediment structure, i.e. high clay/silt and organic content, is crucial for maximum adsorption. However, redox conditions play an important role for degradation rates: under aerobic conditions half-lives of less than one day occurred frequently, whereas anoxic conditions resulted in lag phases of one day and more, as well as in half lives of more than 25 days. Field experiments showed that temperature is crucial for degradation velocity under natural conditions. Under optimal conditions 10 d residence time are sufficient to reduce microcystin concentrations to values below the WHO guidelines value for drinking water (1 microg/L). Under sub-optimal conditions a residence time of up to 90 days may be necessary.