Allelopathic effects of anthurium on cyanobacterium microcystis aeruginosa

被引:0
作者
Zhu, Jiacheng [1 ]
Zhou, Li [1 ]
Zhu, Jia [2 ]
Gao, Jingsi [3 ]
机构
[1] College of Environmental and Municipal Engineering, Qingdao Technological University, Qingdao
[2] Department of Building and Environmental Engineering, Shenzhen Polytechnic, Shenzhen
[3] Harbin Institute of Technology Shenzhen Graduate School, Shenzhen
关键词
Allelopathic effect; Anthurium; Microcystis aeruginosa; Photosynthetic activity;
D O I
10.13198/j.issn.1001-6929.2015.10.20
中图分类号
学科分类号
摘要
Allelopathic inhibitory effects of different amounts of root and planting water of Anthurium on Microcystis aeruginosa were comparatively studied. The results showed that large amounts (3.0 and 4.0 g/L) of Anthurium root could effectively inhibit the growth of M. aeruginosa, with inhibition rates over than 90%. The photosynthetic activity of M. aeruginosa was greatly affected. The Φmax, Φ and ETR were reduced compared to the control group. The enzyme system of M. aeruginosa cells was also inhibited after the treatments. The cell membranes and organelles membranes were attacked by free radicals seriously. MDA accumulated rapidly and POD was reduced drastically. The inhibition rates increased along with the increase of root amounts. Compared with the control group, the light quantum yield of the experimental groups with high amounts of Anthurium root was reduced by 0.3, yet c(MDA) increased over 10 nmol/mL and activities of POD decreased nearly 3 U/mg. At the end of the 18thday of the experiment, the ρ(Chla) of the control group and the 0.5, 1.0, 2.0, 3.0, 4.0 g/L root treated groups were 515.80, 396.35, 246.44, 160.50, 3.67 and 4.13 μg/L respectively. The planting water of Anthurium could inhibit the growth of M. aeruginosa, but the inhibitory effect was worse than that of root with high amounts. ©, 2015, Editorial Department of Molecular Catalysis. All right reserved.
引用
收藏
页码:1638 / 1644
页数:6
相关论文
共 29 条
[1]  
Codd G.A., Bell S.G., Kaya K., Et al., Cyanobacterial toxins, exposure routes and human health, European Journal of Phycology, 34, 4, pp. 405-415, (1999)
[2]  
Rao P.V.L., Bhattacharya R., The cyanobacterial toxin microcystin-LR induced DNA damage in mouse liver in vivo, Toxicology, 114, 1, pp. 29-36, (1996)
[3]  
Smith D.W., Biological control of excessive phytoplankton growth and the enhancement of aquacultural production, Canadian Journal of Fisheries and Aquatic Sciences, 42, 12, pp. 1940-1945, (1985)
[4]  
Li W., Li X., Cao D., Et al., Effect of combined ecological floating bed technology on improvement of eutrophic source water quality, China Water & Wastewater, 24, 3, pp. 34-38, (2008)
[5]  
Li M., Wu Y., Yu Z., Et al., Nitrogen removal from eutrophic water by floating-bed-grown water spinach (Ipomoea aquatica Forsk.) with ion implantation, Water Research, 41, 14, pp. 3152-3158, (2007)
[6]  
Fan P., Yang W., Li H., Et al., Removal of Microcystis aeruginosa by modified clay with quaternary ammonium surfactant, Environmental Science & Technology (China), 34, 11, pp. 91-94, (2011)
[7]  
Pan G., Zou H., Chen H., Et al., Removal of harmful cyanobacterial blooms in Taihu Lake using local soils. III: factors affecting the removal efficiency and an in situ field experiment using chitosan-modified local soils, Environmental Pollution, 141, 2, pp. 206-212, (2006)
[8]  
Pang C., Fan X., Zhou J., Et al., Optimal dosing time of acid algaecide for restraining algal growth, Water Science and Engineering, 4, pp. 402-408, (2013)
[9]  
Garcia-Villada L., Rico M., Altamirano M.A., Et al., Occurrence of copper resistant mutants in the toxic cyanobacteria Microcystis aeruginosa: characterisation and future implications in the use of copper sulphate as algaecide, Water Research, 38, 8, pp. 2207-2213, (2004)
[10]  
Zhao L., Li X., Liang S., Et al., Effect on Microcystis aeruginosa inactivation by manganese copper composited algaecide, The 3rd International Conference on Bioinformatics and Biomedical Engineering, (2009)