Myriophyllum spicatum (Haloragaceae) is a highly competitive freshwater macrophyte that produces and releases algicidal and cyanobactericidal polyphenols. Among them, -1,2,3-tri-O-galloyl-4,6-(S)-hexahydroxydiphenoyl-d-glucose (tellimagrandin II) is the major active substance and is an effective inhibitor of microalgal exoenzymes. However, this mode of action does not fully explain the strong allelopathic activity observed in bioassays. Lipophilic extracts of M. spicatum inhibit photosynthetic oxygen evolution of intact cyanobacteria and other photoautotrophs. Fractionation of the extract provided evidence for tellimagrandin II as the active compound. Separate measurements of photosystem I and II activity with spinach (Spinacia oleracea) thylakoid membranes indicated that the site of inhibition is located at photosystem II (PSII). In thermoluminescence measurements with thylakoid membranes and PSII-enriched membrane fragments M. spicatum extracts shifted the maximum temperature of the B-band (S 2 Q B Ϫ recombination) to higher temperatures. Purified tellimagrandin II in concentrations as low as 3 m caused a comparable shift of the B-band. This demonstrates that the target site of this inhibitor is different from the Q B -binding site, a common target of commercial herbicides like 3-(3,4-dichlorophenyl)-1,1-dimethylurea. Measurements with electron paramagnetic resonance spectroscopy suggest a higher redox midpoint potential for the non-heme iron, located between the primary and the secondary quinone electron acceptors, Q A and Q B . Thus, tellimagrandin II has at least two modes of action, inhibition of exoenzymes and inhibition of PSII. Multiple target sites are a common characteristic of many potent allelochemicals. Allelopathy (sensu;Molisch, 1937) is considered an effective trait of submerged aquatic angiosperms (Wium-Andersen, 1987; Gross, 1999, and refs. therein) to counteract the usually strong competition for light and carbon with other primary producers, especially phytoplankton and epiphytes (SandJensen and Søndergaard, 1981). Allelopathically active compounds known from terrestrial plants generally act as natural herbicides and often have multiple effects on the metabolism of target organisms (Einhellig, 2001). Some have even been explored as natural substitutes for commercial herbicides (Duke et al., 2000). Few studies have, however, targeted the mode of action of allelochemicals from aquatic angiosperms.Several allelochemicals isolated from cyanobacteria or higher plants specifically inhibit photosynthesis of target organisms (Einhellig et al., 1993;Gonzalez et al., 1997;Smith and Doan, 1999). This results in a lower primary production and might consequently cause slower growth of competing photoautotrophs. To prove effects on primary production, the radiocarbon assay (fixation of radioactive labeled 14 C) has been frequently used, e.g. with extracts from Zostera marina (Harrison and Durance, 1985) and Chara globularis (Wium-Andersen et al., 1983). More detailed studies involved separate measureme...