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枯草芽孢杆菌对土臭素和2-甲基异冰片的降解动力学特性
摘要点击 2371  全文点击 1064  投稿时间:2014-09-05  修订日期:2014-11-19
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中文关键词  枯草芽孢杆菌  土臭素  2-甲基异冰片  土腥异味化合物  降解  动力学
英文关键词  Bacillus subtilis  geosmin(GSM)  2-methylisoborneol(2-MIB)  off-flavor compounds  degradation  kinetics
作者单位E-mail
马念念 上海海洋大学水产与生命学院, 上海 201306 mnn2011@126.com 
罗国芝 上海海洋大学水产与生命学院, 上海 201306
上海水产养殖工程技术研究中心, 上海 201306
上海海洋大学水产动物育种中心上海高校知识服务平台, 上海 201306 
gzhluo@shou.edu.cn 
谭洪新 上海海洋大学水产与生命学院, 上海 201306
上海水产养殖工程技术研究中心, 上海 201306
上海海洋大学水产动物育种中心上海高校知识服务平台, 上海 201306 
 
姚妙兰 上海海洋大学水产与生命学院, 上海 201306  
王晓用 上海海洋大学水产与生命学院, 上海 201306  
中文摘要
      土臭素(geosmin, GSM)和2-甲基异冰片(2-methylisoborneol, 2-MIB)是2种普遍存在于养殖水体中的土腥异味化合物,微生物降解是去除这两种物质的有效途径. 本文研究了枯草芽孢杆菌(Bacillus subtilis)降解GSM和2-MIB的动力学特性. 结果表明,枯草芽孢杆菌对GSM(1000~2000 ng ·L-1)和2-MIB(1000~2000 ng ·L-1)具有较好的降解性能,降解率均达90%以上; 枯草芽孢杆菌对这些异味化合物的降解符合伪一级反应动力学,其生物降解速率常数(K)范围为0.14~0.41,降解速率不随GSM和MIB初始浓度的变化而变化; 枯草芽孢杆菌对GSM降解的最大比生长速率umax为0.311,Monod常数KS为1.73,而在降解MIB过程中枯草芽孢杆菌的生长不符合Monod方程(R2=0.781).
英文摘要
      The earthy and musty odor problem in aquaculture systems has been a worldwide problem, especially in freshwater aquaculture systems. Geosmin (GSM) and 2-methylisoborneol (2-MIB), the most common causative agents of the off-flavor in fish, are lipophilic secondary metabolites of cyanobacteria, actinomycetes, and other microorganisms. The odor threshold concentrations for 2-MIB and GSM are approximately 9-42 ng ·L-1 and 4-10 ng ·L-1, and 600 ng ·kg-1 and 900 ng ·kg-1 in the aquaculture water and fish, respectively. With such a low odor threshold concentration, the off-flavor compounds greatly reduce the quality and economic value of aquatic products. This renders the fish, especially some valuable fish produced in recirculating aquaculture systems (RAS), unmarketable.The study reported the kinetic characteristics of degradation of GSM and 2-MIB by Bacillus subtilis and discussed the impacts of the initial concentration of GSM and 2-MIB (T1,T2) and inoculation amount (T1,T3) on the biodegradation rate. The result demonstrated that these two compounds could be degraded by B. subtilis effectively and the biodegradation rate reached more than 90% in T1,T2 and T3 treatments. The biodegradation of these two compounds behaved as a pseudo-first-order kinetics with rate constants (K) in the range of 0.14-0.41. K values indicated that the degradation rate was dependent on the inoculation amount but the start concentration of GSM and MIB. The degradation kinetics showed the maximum specific rate value (umax) and the Monod constant (KS) were 0.311 and 1.73, however, 2-MIB degradation process did not meet the Monod microbial growth equation (R2=0.781).

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