Decolourization of Selected Procion Dye Using Fungi, Acremonium Chrysogenum a Comparison with Physical Adsorbents.

Azo dyes, based on aromatic amines, may contain these amines as impurities introduced during the manufacturing process. Aromatic amines may also be present as a result of thermal or photochemical degradation of azo dyes. The more stable derivatives contain two aryl groups. As a consequence of п-delocalization, aryl azo compounds have vivid colors, especially reds, oranges, and yellows. Therefore, they are used as dyes, and are commonly known as azo dyes, an example of which is Disperse Orange. Some azo compounds, eg. methyl orange, are used as acid-base indicators due to the different colors of their acid and salt forms. The development of azo dyes was an important step in the development of the chemi azo colorants range in shade from greenish yellow to orange, red, violet and brown. The colours depend largely on the chemical constitution, whereas different shades rather depend on the physical properties. However, the important disadvantage limiting their commercial application is that most of them are red and none are green. The inoculum was prepared by adding 10ml of saline to the culture tube, which contain the Acremoniumchrysogenum. The present study designed to study the degradation of common laboratory dyes using fungi, acremonium chrysogenum. The dye selected was procion red. The selected dye procion red can be toxic in its secondary reactive form so there is a great need of them to be removed from the environment.

Behavioural and histopathological effects of azodye on kidney and gills of Labeo rohita fingerlings.

The present paper emphasizes on the histopathological effects of an azo dye, Direct Green 6 on the kidney and gills of Labeo rohita by light microscopy. Fingerlings were exposed to sublethal concentrations (2.5, 5.0 and 10.0 ppm) of dye for 5, 10 and 15 days to study histopathological changes. No histopathological changes were seen in the kidney and gills of control fingerlings. Unlike control fingerlings, both the target organs showed some histopathological changes. Fingerlings exposed to 2.5 ppm concentration of the dye showed shrinkage of glomerulus, increased peritubular space, decreased lumen while 5.0 ppm produced haemorrhage in the interstitial tissue and mild degeneration in the kidney. Necrosis in the tubular epithelium, distruction of cell membrane and loss of cellular cytoplasm were observed in kidney of fingerlings exposed to 10 ppm dye concentration. Gills of fingerlings exposed to 2.5 ppm of dye showed aneurism and mild degenerated central axis. 5 ppm of dye concentration produced remarkable changes like epithelial lifting, hyperplasia, enlarged and vacuolated cartilage cells. Haemorrhagic tip, fusion and curling of secondary gill lamellae and at some places complete removal of them were also observed in gills of fingerlings exposed to 10 ppm.

Effect of antioxidant vitamins A, C, E and their analogues on azo-dye binding protein in liver of rats treated with p-dimethylaminoazobenzene.

p-Dimethylaminoazobenzene (DAB) is an azo-dye and known to cause liver tumour in rats. Azo-dye binding protein is a specific cytosolic protein involved in the translocation of azo-dye carcinogen metabolites from liver cytoplasm into the nucleus. Administration of vitamin A (40,000 and 50,000 IU), L-ascorbic acid (500 and 1,000 mg) and vitamin E succinate (200–500 mg) reduced the amount of azo-dye binding protein in liver of rats treated with DAB. Supplementation of high doses of vitamin A acetate, vitamin A palmitate, sodium ascorbate, ascorbyl palmitate and vitamin E acetate had no effect on the quantity of azo-dye binding protein in liver. When the vitamin mixture was given, the level of azo-dye binding protein decreased in the liver at all the studied doses, which may be due to their synergistic effect.