浙江农业学报 ›› 2021, Vol. 33 ›› Issue (1): 131-141.DOI: 10.3969/j.issn.1004-1524.2021.01.16
许双燕1(), 张涛1, 张成1,2, 林辉3, 水贤磊1, 郑华宝1,2,*(
)
收稿日期:
2020-07-03
出版日期:
2021-01-25
发布日期:
2021-01-25
通讯作者:
郑华宝
作者简介:
*郑华宝,E-mail:zhenghuabao@zafu.edu.cn基金资助:
XU Shuangyan1(), ZHANG Tao1, ZHANG Cheng1,2, LIN Hui3, SHUI Xianlei1, ZHENG Huabao1,2,*(
)
Received:
2020-07-03
Online:
2021-01-25
Published:
2021-01-25
Contact:
ZHENG Huabao
摘要:
优良的菌种资源是污染环境微生物修复技术的核心。为获取红霉素高效降解菌,采用梯度驯化法,以长期堆放鸡粪的有机肥生产车间土壤为对象,开展降解菌筛选鉴定,并研究不同红霉素质量浓度、培养温度、转速、初始pH值,以及外加碳氮源、金属离子对菌株降解红霉素的影响。结果表明,筛选获得一株红霉素高效降解菌株Ery-6。通过菌落形态和16S rDNA序列分析方法,将该菌株鉴定为甲基菌属(Methylobacillus sp.)。Ery-6菌株可以在以红霉素为唯一碳源的无机盐培养基中快速生长,60 h后进入生长稳定期。接种Ery-6菌株可提高红霉素在培养基中的降解速率常数,使其半衰期从88.4 h降低至30.7 h。该菌株在含有100 mg·L-1红霉素的无机盐培养基中,在温度35 ℃、转速120 r·min-1、初始pH值7.0、外加50 mg·L-1蔗糖的条件下,对红霉素的降解效果最佳,48 h降解率达88.68%。菌株可耐受1 000 mg·L-1高质量浓度的红霉素,在温度35 ℃、转速120 r·min-1、初始pH值7.0的条件下48 h降解率达31.95%。该菌株对多种金属离子具有良好的耐受性;但Cu2+既会抑制Ery-6菌株的生长,也会对其降解红霉素产生一定的影响。本研究首次发现甲基菌属菌株具有降解红霉素的能力,且降解效果较好,为生物降解养殖废弃物与环境中的抗生素污染提供了一种新的微生物资源。
中图分类号:
许双燕, 张涛, 张成, 林辉, 水贤磊, 郑华宝. 一株红霉素降解菌的筛选、鉴定与降解特性[J]. 浙江农业学报, 2021, 33(1): 131-141.
XU Shuangyan, ZHANG Tao, ZHANG Cheng, LIN Hui, SHUI Xianlei, ZHENG Huabao. Isolation and identification of an erythromycin degradation bacterium strain and its biodegradation characteristics[J]. Acta Agriculturae Zhejiangensis, 2021, 33(1): 131-141.
t/min | 流动相比例Mobile phase ratio/% | |
---|---|---|
A | B | |
0 | 90.0 | 10.0 |
1.0 | 90.0 | 10.0 |
2.0 | 80.0 | 20.0 |
3.5 | 77.0 | 23.0 |
5.0 | 76.0 | 24.0 |
8.0 | 76.5 | 23.5 |
9.0 | 70.0 | 30.0 |
16 | 70.0 | 30.0 |
20 | 50.0 | 50.0 |
24 | 90.0 | 10.0 |
25 | 90.0 | 10.0 |
表1 液相色谱测定红霉素时的梯度洗脱程序
Table 1 Gradient elution procedure for erythromycin determination
t/min | 流动相比例Mobile phase ratio/% | |
---|---|---|
A | B | |
0 | 90.0 | 10.0 |
1.0 | 90.0 | 10.0 |
2.0 | 80.0 | 20.0 |
3.5 | 77.0 | 23.0 |
5.0 | 76.0 | 24.0 |
8.0 | 76.5 | 23.5 |
9.0 | 70.0 | 30.0 |
16 | 70.0 | 30.0 |
20 | 50.0 | 50.0 |
24 | 90.0 | 10.0 |
25 | 90.0 | 10.0 |
图2 Ery-6菌株的生长曲线(A)和对红霉素的生物降解动力学曲线(B) Ct/C0为t时体系中红霉素质量浓度与初始红霉素质量浓度之比。CK为不加菌的对照。
Fig.2 Growth curve (A) and biodegradation kinetic curve (B) of Ery-6 strain Ct/C0 was the ratio of erythromycin concentration at t time to the initial concentrution.CK, Control withow Ery-6 strain inoculation.
处理Treatment | 一级反应方程First order reaction equation | k/h-1 | t1/2/h | R2 |
---|---|---|---|---|
不接菌Not inoculated | Ct=92.14e-0.00049t | 0.000 49 | 88.42 | 0.928 4 |
接菌Inoculated | Ct=57.69e-0.00753t | 0.007 53 | 30.65 | 0.925 9 |
表2 红霉素降解的动力学方程与动力参数
Table 2 Biodegradation kinetic equation and kinetic parameter of erythromycin
处理Treatment | 一级反应方程First order reaction equation | k/h-1 | t1/2/h | R2 |
---|---|---|---|---|
不接菌Not inoculated | Ct=92.14e-0.00049t | 0.000 49 | 88.42 | 0.928 4 |
接菌Inoculated | Ct=57.69e-0.00753t | 0.007 53 | 30.65 | 0.925 9 |
图7 外源添加碳氮源对Ery-6菌株降解红霉素的影响 柱上无相同字母的表示处理间差异显著(P<0.05)。下同。对照中不外源添加碳氮源。
Fig.7 Effect of exogenous carbon or nitrogen source on erythromycin degradation by Ery-6 strain Bars marked without the same letters indicated significant difference at P<0.05. The same as below. No exogenous carbon or nitrogen source was added in the control.
图8 外加金属离子对Ery-6菌株降解红霉素的影响 对照中不外源添加金属离子。
Fig.8 Effect of exogenous metal ions on erythromycin degradation by Ery-6 strain No exogenous metal ion was added in the control.
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