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

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(1 000~2 000 ng·L-1)和2-MIB(1 000~2 000 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).

Kinetic Characteristics of Degradation of Geosmin and 2-Methylisoborneol by Bacillus subtilis

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 (u_max) and the Monod constant (K_S) were 0.311 and 1.73, however, 2-MIB degradation process did not meet the Monod microbial growth equation (R²=0.781).