The comparative study of various unicellular algae, characterised by different carbon chain lengths and different numbers of double bonds per fatty acid (FA) chain, exhibited some similarity in the mechanisms of their response to changes in light conditions, in terms of FA metabolism. In all cases, the optimisation of photosynthetic process resulted in some increase in the relative content of the most unsaturated FA, i.e. C16:3Ω3 and C18:3Ω3 acids in Chlorella cells, C16:4Ω3 and C18:3Ω3 in Dunaliella and Chlamydomonas, C20:5Ω3 in Porphyridium, and C18:2Ω6 in Synechocystis sp. As a rule, these FA were esterified to monogalactosyldiacylglycerols (MGDG), the predominant lipids of thylakoid membranes. Such an increase in the relative content of the polyunsaturated FA usually occurred during the period when the photosynthesis, as well as the biosynthesis of FA de novo, were transiently inhibited following shifts in environmental conditions even at their optimisation. The increase in the relative content of the most unsaturated FA could be performed via desaturation of their immediate precursors. In turn, the deterioration of life conditions (decrease in the light intensity, ageing of cells or cultures, and others) resulted in the accumulation of these precursors. As a result, the cell could change its FA composition without alteration of the whole multistage process but only at the rate of this end reaction of polyunsaturated FA biosynthesis. In the majority of algae, these polyunsaturated acids were Ω3‐homologues, regardless of the difference in their structures, but in some cyanobacteria (e.g. Synechocystis) the relative content of Ω6‐FA increased. The acceleration of Ω3‐FA biosynthesis could be observed, regardless of changes in the total index of unsaturation. This FA desaturation was shown to correlate with the activity of photosystem I (PSI). The specificity of this reaction enables us to assume it to be an adaptive response which provides alterations to lipid‐protein interactions in the membrane that may be important for the self‐assembly of active chlorophyll‐protein complexes for photosynthetic akpparatus.
The effects of copper and zinc on Spirulina platensis (Nordst.) Geitl. growth and the capability of this cyanobacterium for accumulation of these heavy metals (HMs) were studied. S. platensis tolerance to HMs was shown to depend on the culture growth phase. When copper was added during the lag phase, its lethal concentration was 5 mg/l, whereas 4 mg/l were lethal during the linear growth phase. Zinc concentration of 8.8 mg/l was lethal during the linear but not lag phase of growth. HM-treated S. platensis cells were capable for accumulation of tenfold more copper and zinc than control cells. Independently of Cu 2+ content in the medium and of the growth phase, cell cultures accumulated the highest amount of this metal as soon as after 1 h, which may be partially determined by its primary sorption by cell-wall polysaccharides. A subsequent substantial decrease in the intracellular copper content occurred due to it secretion, which was evident from the increased metal concentration in the culturing medium. When zinc was added during the linear growth phase, similar pattern of its accumulation was observed: the highest content after 1 h and its subsequent decrease to the initial level. When the initial density of the culture was low and the cells had much time to adapt to HM, zinc accumulated during the entire linear growth phase, and thereafter the metal was secreted to the medium. The mechanisms of S. platensis tolerance to HM related to both their sorption by the cell walls and secretion of metal excess into the culturing medium and its conversion into the form inaccessible for the cells are discussed.
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.