“…The intracellular (cytoplasmic) ammonium concentration, which must be exceeded before toxicity is observed, is very high in some organisms (e.g. Siegel & Giumarro, 1966;Siegel et aL, 1967;Siegel, Nathan, & Roberts, 1968;Sayeed & Kenny, 1978;Hoddinott, Reid & Ingledew, 1978;Raven, 1980), A problem in all considerations of toxicity and metabolism of ammonium is that it is not clear whether the active species is NH3 or NH^, Work on other phototrophs which attempts to distinguish between NH3 and NH^*^ as the major species crossing the plasmalemma includes that of Barr, Koh & Ryan (1974) and of Loppert (1979), in addition to the work of Walker et al ( 1979a) and Walker et al (1979b) on Chara corallina which was discussed in the Introduction. Barr et al (1974) showed that the ammonium distribution between the vacuole of Nitella elavata and the bathing medium could be explained in terms of vacuolar and external pH values and passive NH3 transport, with i' NH3 ^^^ ^^^ plasmalemma plus tonoplast of 4,4,10"^ cm s-', With the relatively high (2,5-14 mmol m^^) concentrations of NH3 in the bathing medium in these experiments, it is likely that diffusive NH3 entry could supply both assimilatory and storage demands for ammonia; any NH^ uniporter present in the plasmalemma would presumably be subject to feedback inhibition under these conditions (cf.…”