2 resultados para fish-ponds

em Aquatic Commons


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Fish introductions have been made from small fish ponds to the largest lakes in Africa. The primary intent of these introductions has been to sustain or increase fish production, although some introductions have been made to develop sport fisheries and to control unwanted organisms. Some of these introductions have fulfilled their objective in the short term, but several of these "successful" introductions have created uncertainties about their long term sustainability. Lates niloticus, Oreochromis niloticus, O. leucostictus, Tilapia melanopleura and T. zilli were introduced into lakes Victoria and Kyoga in 1950s and early 1960s. By the 1980s O. niloticus and O. niloticus dominated the fisheries of these lakes, virtually eliminating a number of endemic fish species. The loss of genetic diversity of the fish in the worlds second largest lake has also been accompanied by a loss of trophic diversity. The transformation of the fish community has, in Lake Victoria coincided with a profound eutrophication (algal blooms, fish kills, hypolimnetic anoxia) which might be related to alterations of the lake's food-web structure. In contrast, the introduction of a planktivore, Limnothrissa miodon into Lake Kivu and the Kariba reservoir has established highly successful fisheries with little documented effect on the pre-existing fish community or trophic ecology of the lakes. The highly endemised species-rich African Great lakes may be particularly sensitive to species introductions and require special consideration and caution when introductions are contemplated because species extinctions, introgressive hybridization and ecosystem alterations may occur following fish introductions.

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In order to evaluating Streptoccocus iniae pathogenicity recovered from trout in Fars province a total number of 400 healthy (15-20g) fingerling fish specimens which were kept in 1000 liters ponds and after spending compatibility (adaptation) period in new environment and desired condition as aspect of temperature, pH, food and density relative to accomplish disease experiments in interamusclar injection method with 3 × 10 3 , 3 × 10 4, 3 × 10 5, 3 × 10 6 ,3 × 10 7 bacterium cell dilutions per each fish, interaperitonal method with 2 × 10 3 , 2 × 10 4, 2 × 10 5, 2 × 10 6 ,2 × 10 7 dilutions of bacterium cell and in water bath method with 2 × 10 3 , 2 × 10 4, 2 × 10 5, 2 × 10 6 2 × 107 dilutions in 20 degree centigrade temperature were used. Control groups according to above (mentioned) method with 0.1cc sterile physiological serum per each fish were injected. Clinical and autopsy signs that observed in injected groups were includes: body darkness, swelling of abdomen, exophthalmy sometime with eye ocular haemorrhagy, anal (rectal) prolaps, blood congestion and petechia in muscles and congestion and haemorrhagy in intestines. Infectious results in interamusclar injection shown that, mortality 22 hours after injection begans and in 3 × 107 cells dilution per each fish 30 hours pass the injection was reached above 50 percent, so that the amount of LD50/ 30h in 3 × 10 7 cells per each fish was estimated. In interaperitonal injection method was shown those 20 hours after injection mortality begins and up to maximum 80 hours after continued and 32 hours after injection in 2 × 10 7 cells dilution mortality was reached above 50 percent, so that LD50 /32 hour in 2 × 10 7 cell dilution per each fish estimated. In water bath method even after sparing 15 days mortality had been too low which indicating long process of disease. By microscopic study of tissues, dilatation of bowman capsule, shrinkage of glomerols, increasing of melano macrophage centers, degeneration, necrosis of urine tubules in kidney tissue, dilatation of sinusoids, congestion of hepatic vessels, increasing of melanoma macrophages and hepatocite vacuolization in liver tissue, spleen congestion, heart pericardit, ocular haemorrhagy, congestion, edema and separating of basement membrane from gill secondary lamellae can be referred.