不同系统对养殖水体和罗非鱼肌肉异味物质含量的影响
[Abstract]:Tilapia culture and production in China are mainly carried out in still water and non-polluted ponds. Fish activities, feeding and excretion are all carried out in the same pond. Most of the foul smells in the water are caused by cyanobacteria, especially in eutrophic ponds. The nutrient concentration in the water increases when the manure and bait of cultured organisms are discharged into the pond, which provides the conditions for the growth of odorous cyanobacteria. Therefore, controlling nutrient supply in the pond is the key. Bottom drainage technology can eliminate the bottom of the pond. Aquatic plants are often used to absorb inorganic nutrients in ponds, thereby limiting the growth of phytoplankton. Therefore, in this paper, the effects of different systems on muscle odor content of tilapia were preliminarily determined by field sampling in Guangdong and Hainan in 2015, and then simulated in 2016. In order to explore the feasibility of different culture systems to reduce the content of odor substances in Tilapia meat and provide scientific basis for optimizing tilapia culture mode, the effects of bottom sewage and fish-vegetable symbiosis on Tilapia aquaculture water quality, yield and the content of odor substances were analyzed. The results are as follows: 1. Microwave distillation-purge-trap-gas chromatography-mass spectrometry was used to analyze the main odor compounds in tilapia meat, including Geosmin (GSM) and dimethylisoborneol (2-MIB). The power of microwave distillation, time of microwave distillation and purge-trap conditions were optimized. The results showed that under the conditions of 560 W microwave power (70% of the rated power of the instrument), 5 min microwave time, 3:1 shunt ratio, 11 min sweeping time, 75 C sweeping temperature and 20% salt content, the detection limits of soil odor and 2-methylisocamptol reached 2.89ng/L and 2.28ng/L respectively, and the correlation coefficients were 0.05-20 ng/L, respectively. 9980 and 0.9985, with recoveries ranging from 81% to 112% and RSD ranging from 1.8% to 12.9%. This method has high accuracy. 2. In order to preliminarily determine the variation of odor content in water and muscle of tilapia under different tilapia culture systems, the bottom discharges were made in May, June and July, 2015 in Maoming, Guangdong Province and Wenchang, Hainan Province. The results showed that different culture systems in Maoming, Guangdong and Wenchang, Hainan, affected the content of odor substances in water and muscle of tilapia, and the content of odor in ponds equipped with bottom sewage system and fish-vegetable symbiosis system was significantly lower than that in control. In order to verify the changes of odor substances in water and muscle of tilapia under different tilapia culture systems, the water quality changes, tilapia production effects, and the contents of odor substances in cultured water and muscle of tilapia were compared between June, July and August, 2016. The yield of tilapia in fish-vegetable symbiosis system, bottom sewage system and bottom sewage-fish-vegetable symbiosis system was the highest, which were 4.31 (+ 0.13kg/m3) and 4.14 (+ 0.09kg/m3) respectively, significantly higher than that in the control group and bottom sewage system (P 0.05). The yield of tilapia in bottom sewage-fish-vegetable symbiosis system and bottom sewage-fish-vegetable symbiosis system was the highest. The ammonia nitrogen and nitrite contents were low (0.64 The content of odor substances in the pond water of the living system was significantly lower than that of the control group (P 0.05). In addition, the different culture systems affected the content of odor substances in the meat of tilapia, and the effect of the bottom sewage-fish-vegetable symbiosis system was more obvious. The highest level of 2-MIB and GSM in the muscle of tilapia in the control group was 0.67+0.022 ug/kg and 0.87+0.018 ug/kg, reaching human level. The highest levels of 2-MIB and GSM in the muscle of two-system tilapia were 0.31 (+ 0.02) and 0.53 (+ 0.042) ug/kg, which were lower than those of the other three groups at all stages.
【学位授予单位】:上海海洋大学
【学位级别】:硕士
【学位授予年份】:2017
【分类号】:S965.125;TS254.1
【参考文献】
相关期刊论文 前10条
1 周维成;王素钦;高翔;郭亮亮;代亮亮;李根保;;温度与光强对柔细束丝藻3种异味物质产量的影响[J];水生态学杂志;2015年04期
2 吴添天;芮明;朱慧娈;李X;储玲;;巢湖蓝藻异味成分分析及影响因素研究[J];环境科学与技术;2015年03期
3 王国超;李来好;郝淑贤;杨贤庆;辛少平;岑剑伟;刁石强;黄卉;魏涯;;罗非鱼肉中土臭素和2-甲基异莰醇的测定[J];食品科学;2011年22期
4 程莹寅;吴山功;郑英珍;王微微;邹红;李文祥;王桂堂;;主养草鱼池塘底泥微生物群落多样性研究[J];淡水渔业;2011年06期
5 李德亮;张婷;;鱼体异味的产生原因与控制方法研究进展[J];现代农业科技;2011年05期
6 刘安军;褚兰玲;郑婕;何立蓉;;鲤鱼土腥味成分的检测与去除[J];现代食品科技;2011年02期
7 徐立蒲;潘勇;曹欢;赵文;熊邦喜;;渔业水体中土腥异味物质的研究进展[J];大连海洋大学学报;2010年06期
8 薛勇;王超;于刚;黄万成;王玉明;李兆杰;徐杰;薛长湖;;鳙鱼肉中土腥味物质的测定方法[J];中国水产科学;2010年05期
9 尹文林;沈锦玉;潘晓艺;姚嘉峗;徐洋;郝贵杰;;复合硝化菌制剂对水质改良的应用效果[J];水产养殖;2010年09期
10 杨玉平;熊光权;程薇;乔宇;廖涛;林若泰;李小定;吴文锦;;水产品异味物质形成机理、检测及去除技术研究进展[J];食品科学;2009年23期
相关博士学位论文 前2条
1 徐立蒲;鱼池中二甲基异莰醇和土臭味素的含量、来源及产生影响因素的研究[D];华中农业大学;2009年
2 李林;淡水水体中藻源异味化合物的分布、动态变化与降解研究[D];中国科学院研究生院(水生生物研究所);2005年
相关硕士学位论文 前1条
1 王赛;水质、藻类变化对罗非鱼异味产生的影响及异味去除初步探讨[D];广东海洋大学;2012年
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