水生生物学报
水生生物學報
수생생물학보
ACTA HYDROBIOLOGICA SINICA
2010年
2期
250-255
,共6页
邹琴%陈培基%李刘冬%林伟强%陈挺%杨金兰%赵东豪%黎智广
鄒琴%陳培基%李劉鼕%林偉彊%陳挺%楊金蘭%趙東豪%黎智廣
추금%진배기%리류동%림위강%진정%양금란%조동호%려지엄
甲基睾丸酮%消解%罗非鱼苗%养殖模式
甲基睪汍酮%消解%囉非魚苗%養殖模式
갑기고환동%소해%라비어묘%양식모식
17α-methyltestosterone (MT)%Dissipation%Tilapia fry%Aquaculture model
研究了养殖场在大规模养殖下,甲基睾丸酮用于尼罗罗非鱼苗雄性化后在苗种体内的消解规律.采用含200 mg/kg甲基睾丸酮的饲料持续喂养尼罗罗非鱼苗30d来进行雄性化,随后鱼苗放入池塘来进行甲基睾丸酮的消解实验,应用高效液相色谱法检测不同时间鱼苗体内甲基睾丸酮的残留量,并用SPSS Statistics17.0统计软件结合EXCEL 2003进行数据处理和分析,来研究甲基睾丸酮的消解规律.结果表明,两次投喂间甲基睾丸酮在罗非鱼体内是缓慢减少的,但是在罗非鱼雄性化期间甲基睾丸酮在罗非鱼体内具有一致性.此外,停药后甲基睾丸酮消解比较缓慢,在停药约115d,鱼苗体重为(14.12±2.12)g时甲基睾丸酮才基本无检出,拟合回归得到指数方程y=1779.6e~(-0.0369x),R~2=0.9332.这说明甲基睾丸酮的消解符合指数递减,后期消解缓慢,建议在养殖过程中不宜使用甲基睾丸酮.
研究瞭養殖場在大規模養殖下,甲基睪汍酮用于尼囉囉非魚苗雄性化後在苗種體內的消解規律.採用含200 mg/kg甲基睪汍酮的飼料持續餵養尼囉囉非魚苗30d來進行雄性化,隨後魚苗放入池塘來進行甲基睪汍酮的消解實驗,應用高效液相色譜法檢測不同時間魚苗體內甲基睪汍酮的殘留量,併用SPSS Statistics17.0統計軟件結閤EXCEL 2003進行數據處理和分析,來研究甲基睪汍酮的消解規律.結果錶明,兩次投餵間甲基睪汍酮在囉非魚體內是緩慢減少的,但是在囉非魚雄性化期間甲基睪汍酮在囉非魚體內具有一緻性.此外,停藥後甲基睪汍酮消解比較緩慢,在停藥約115d,魚苗體重為(14.12±2.12)g時甲基睪汍酮纔基本無檢齣,擬閤迴歸得到指數方程y=1779.6e~(-0.0369x),R~2=0.9332.這說明甲基睪汍酮的消解符閤指數遞減,後期消解緩慢,建議在養殖過程中不宜使用甲基睪汍酮.
연구료양식장재대규모양식하,갑기고환동용우니라라비어묘웅성화후재묘충체내적소해규률.채용함200 mg/kg갑기고환동적사료지속위양니라라비어묘30d래진행웅성화,수후어묘방입지당래진행갑기고환동적소해실험,응용고효액상색보법검측불동시간어묘체내갑기고환동적잔류량,병용SPSS Statistics17.0통계연건결합EXCEL 2003진행수거처리화분석,래연구갑기고환동적소해규률.결과표명,량차투위간갑기고환동재라비어체내시완만감소적,단시재라비어웅성화기간갑기고환동재라비어체내구유일치성.차외,정약후갑기고환동소해비교완만,재정약약115d,어묘체중위(14.12±2.12)g시갑기고환동재기본무검출,의합회귀득도지수방정y=1779.6e~(-0.0369x),R~2=0.9332.저설명갑기고환동적소해부합지수체감,후기소해완만,건의재양식과정중불의사용갑기고환동.
17α-methyltestosterone (MT), a synthetic androgen drugs, has served as a specific medicine on fry culture and gender control in aquaculture. It found that there were MT residues in tilapia at the market, which would harm the human body as this androgen has great potential hazard on human health. Studies were conducted on the dissipation of MT in Nile tilapia Oreochromis niloticus (L.) fry that received dietary of MT to induce sex reversal under aquaculture model in last winter. Sexually undifferentiated Nile tilapia fry (8-10 mm, 9-13 rag) were fed on a diet containing unlabeled MT (200 mg/kg) for 30d to effect maseulinization in the concrete tank, daily feeding was regular, water was changed once a week, shed was used natural to control the temperature at (28±2)℃. After 30d, the fry were transferred to a pond with normal feed, MT in fry were dissipation in the natural environment. The fry were sampled in different time and frequency in the latter days, then MT residues in fry were measured by high performance liquid chromatography (HPLC), the retention time of MT was approximately 7.6min, the recoveries obtained from fry samples were above 83.2%, with the relative standard deviation were below 3.62%, the detection limits of MT was 20μg/kg. SPSS Statistics 17.0 combines EXCEL 2003 statistical software were applied to the data processing and analysis in order to get the dissipation rule of MT after tilapia sex reversal. The results showed that MT residues in tilapia fry almost maintained consistently during the sex reversal period, MT residues in tilapia fry body at roughly about (1937.17±77.76) μg/kg, although overall trend of the dissipation was still downward while multi-peak phenomenon occurred in the dissipation of MT between two feedings. Besides, following the withdrawal, in the first 45d, MT had rapid reduction, in the subsequent 46-115d, the dissipation of MT was relatively slow, and ended approximately in 115d withdrawal, MT residues was not detected in tilapia fry from that day on, while the main weight of fry was (14.12±2.12) g. In general, the dissipation of MT was following the withdrawal slowly. By regression analysis of the MT dissipation curve, the exponential models were y = 1779.6e~(-0.0369x), R~2=0.9332, where, Y=whole body concentration of MT in μg/kg fry body, and X =time in d after withdrawal of MT-treated feed (R~2=0.9332). It suggested that the dissipation of MT fitted with exponential decline, and the dissipation was slowly in the latter. Though MT residues from tilapia sex reversal were not detected before marketing, but it could not be guaranteed as excessive use of MT and MT, after all, it was a synthetic hormone, its various impacts on organs of the fish itself would probably have indirect impact on human health. For safety's sake, the use of MT in the aquaculture should be forbidden.