Mibolerone (MI), a synthetic steroid, was used to sex‐reverse undifferentiated Oreochromis aureus fry. Fry were exposed to 0.0, 0.3, 0.6, or 1.0 ppm MI in static‐water solutions for five weeks (immersion treatments) or were fed a diet containing 1.0 ppm MI for four weeks in a flow‐through system. Following hormone treatment, the fish were grown to over 60 mm total length prior to sex determination using gonadal squash examination.
Fish immersed in 1.0, 0.6, or 0.3 ppm MI had average tissue MI concentrations of 14.4, 5.6, and 3.3 ppm, respectively. Immersion in either 1.0 or 0.6 ppm MI for five weeks resulted in an average of 82% males and 18% ovo‐testicular fish (inter‐sex fish) with no gonadal females being produced. Exposure to 0.3 ppm MI resulted in 78.7% males, 20.7% ovo‐testicular fish, and 0.7% gonadal females. Feeding a diet containing 1.0 ppm MI resulted in 85% males, 11% ovo‐testicular fish, and 4% gonadal females. Fry growth and survival were negatively correlated with the MI concentration of the immersion treatments.
Exposing tilapia fry to static‐water solutions of 0.6 ppm MI for five weeks appears to be a feasible method of eliminating the production of functional females. Immersion solutions should be changed at least weekly to maintain an effective hormone concentration.
Mibolerone (MI), a synthetic steroid, was used to sex‐reverse undifferentiated Oreochromis aureus fry. Fry were exposed to 0.0, 0.3, 0.6, or 1.0 ppm MI in static‐water solutions for five weeks (immersion treatments) or were fed a diet containing 1.0 ppm MI for four weeks in a flow‐through system. Following hormone treatment, the fish were grown to over 60 mm total length prior to sex determination using gonadal squash examination.
Fish immersed in 1.0, 0.6, or 0.3 ppm MI had average tissue MI concentrations of 14.4, 5.6, and 3.3 ppm, respectively. Immersion in either 1.0 or 0.6 ppm MI for five weeks resulted in an average of 82% males and 18% ovo‐testicular fish (inter‐sex fish) with no gonadal females being produced. Exposure to 0.3 ppm MI resulted in 78.7% males, 20.7% ovo‐testicular fish, and 0.7% gonadal females. Feeding a diet containing 1.0 ppm MI resulted in 85% males, 11% ovo‐testicular fish, and 4% gonadal females. Fry growth and survival were negatively correlated with the MI concentration of the immersion treatments.
Exposing tilapia fry to static‐water solutions of 0.6 ppm MI for five weeks appears to be a feasible method of eliminating the production of functional females. Immersion solutions should be changed at least weekly to maintain an effective hormone concentration.
Feeding trials were conducted in prawn ponds (freshwater) and shrimp ponds (brackishwater) with red tilapia stocked in floating 0.8‐m3 cages. Pond sizes ranged from 0.23 to 0.45 ha. Seven ponds were stocked at a density of 26 cages/ha. One hundred 9‐9 tilapia fingerlings were stocked into each cage. Fish survival after 8 weeks averaged 98.5% excluding a set of six cages from one pond which was preempted from the study due to high mortality, possibly caused by algal toxins. The growth of caged tilapia fed supplemental diets was significantly (α = .05) higher in brackishwater than in freshwater ponds. Tilapia raised in freshwater cages without supplemental feeding grew at a significantly lower rate than caged fish in any other treatment analyzed. Feed conversion rates were calculated for caged fish grown in fresh water and brackish water. The costs and revenues derived from this polyculture strategy were analyzed. Gross profitha of brackishwater red tilapia cage culture is estimated to be more than double the gross profit obtained in freshwater ponds.
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