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- Bleaching Herbicides (1)
- Carotenoids (1)
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Among chlorosis-inducing herbicides that interfere with carotenoid synthesis two groups of different potency can be discriminated (group 1: aminotriazole amd haloxidine; group 2 with more extensive photodestructions: pyridazinone herbicides and difunon). After application of herbicides of group 2 colored carotenoids were completely absent and preexisting chlorophyll was degraded by photochemical reactions requiring high light intensity and O2, that occurred also at 0°C. In treatments with group 1 herbicides direct photodegradation of chlorophyll was not sufficient to generate the chlorosis. Light-induced interference with constituents of the chloroplast protein synthesis apparatus being more sensitive to photooxidative damage than chlorophyll, appeared to indirectly mediate the chlorosis. In the absence of chloroplast protein synthesis further chlorophyll accumulation is prevented. Photodegradation of chlorophyll in the presence of group 2 herbicides involved the participation of O2- radicals and was accompanied by lipid peroxidation. In all herbicide treatments the catalase activity of the leaves was very low. Only in the presence of group 2 herbicides chloroplast enzymes of cytoplasmic origin (e.g. NADP-glyceraldehyde-3-phosphate dehydrogenase) were also inactivated. Rapid inactivation of catalase as well as of NADP-glyceraldehyde-3-phosphate dehydrogenase was induced by exposure of dim-light-grown herbicide-treated leaves to bright light, also at 0°C. In treatments with herbicides of group 2 also other peroxisomal enzymes (e.g. glycolate oxidate, hydroxy-pyruvate reductase) were affected. The elimination of these peroxisomal enzymes also appeared to depend on photooxidative processes of the chloroplast.
Effect of UV-B radiation on biomass production, pigmentation and protein content of marine diatoms
(1984)
Several species of marine diatoms were grown at + 18 °C and + 22 °C under normal air conditions (0.035 vol.% C02) at a light/dark alteration of 14: 8̄ h. Intensity of white light was 1 mW (~ 5000 lux). An artifical nutrient solution of 35%o salinity was used. Algae - harvested during exponential growth - were exposed to different intensities of UV-B radiation (439, 717 and 1230 J · m-2 · m-1) for 2 days. UV-B radiation depressed the growth of all tested marine diatoms. Low levels of UV-B resulted in a slight increase of the biomass production (dry weight) compared to not UV-B treated cells. Enhanced UV-B doses caused a diminution of the primary productivity in all species. Algae exposed to UV-B stress showed a marked decrease in the protein and pigment content (chlorophyll a, chlorophyll c1 + c2 and carotenoids). In + 22°C grown cells of Lauderia annulata and Thalassiosira rotula were more sensitive to UV-B radiation than those cultures grown at + 18 °C. Bellerochea yucatanensis cells grown at +22 °C were less affected after UV-B exposure than at +18°C grown algae. The UV-B sensibility and growth of the individual species varied in a mixture of several marine diatoms. Results were discussed with reference to the UV-B effect on metabolic processes.