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[短期菲胁迫对大豆(Glycine max)幼苗超氧化物歧化酶活性和丙二醛含量的影响]

[Effect of short-term phenanthrene stress on SOD activities and MDA contents in soybean (Glycine max) seedlings].

作者信息

Liu Wan, Li Peijun, Zhou Qixing, Sun Tieheng, Tai Peidong, Xu Huaxia, Zhang Hairong

机构信息

Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China.

出版信息

Ying Yong Sheng Tai Xue Bao. 2003 Apr;14(4):581-4.

Abstract

Growth of soybean (Glycine max) seedlings, changes of superoxide dismutase (SOD) activities, and malonyldialdehyde (MDA) contents were researched during different concentration phenanthrene stress and following recovery from stress. The results showed that seedling growth was interrupted after 5 d in 200 micrograms.g-1 phenanthrene treatment. However, during the period of recovery, growth was restored, although there was a delay in returning to control levels. The dose-related response of SOD activities were observed in manner of linear for 2 d and of parabola for 5 d and 8 d at 50-200 micrograms.g-1 phenanthrene. SOD activities of seedling were significantly induced by 100 and 200 micrograms.g-1 phenanthrene for 2 d (P < 0.05 and P < 0.01), while declined significantly under phenanthrene stress for 8 d, and was 88% of control at 200 micrograms.g-1 phenanthrene (P < 0.05). When releasing soybean seedlings from phenanthrene stress for 5 d to clear tap water for 2 d or 4 d, their SOD activities at 50 and 100 micrograms.g-1 phenanthrene recovered towards control level, while a significant increase in SOD activities was observed at 200 micrograms.g-1 phenanthrene (P < 0.05). The experiments also revealed that a significant increase of MDA contents in seedlings occurred after 5 d and 8 d in 100 and 200 micrograms.g-1 phenanthrene treatment (P < 0.05 and P < 0.01), which suggested that the membrane systems were damaged by phenanthrene stress. All of the above results showed that SOD activities of soybean seedling might be suitable to be the biomarkers of phenanthrene stress.

摘要

研究了不同浓度菲胁迫及胁迫解除后的恢复过程中大豆(Glycine max)幼苗的生长、超氧化物歧化酶(SOD)活性变化和丙二醛(MDA)含量变化。结果表明,在200微克·克⁻¹菲处理5天后,幼苗生长受到抑制。然而,在恢复期间,生长得以恢复,尽管恢复到对照水平有所延迟。在50 - 200微克·克⁻¹菲处理下,SOD活性的剂量反应在2天呈线性,5天和8天呈抛物线状。100和200微克·克⁻¹菲处理2天显著诱导了幼苗的SOD活性(P < 0.05和P < 0.01),而在菲胁迫8天后显著下降,在200微克·克⁻¹菲处理下为对照的88%(P < 0.05)。当大豆幼苗从菲胁迫5天释放到清水2天或4天时,50和100微克·克⁻¹菲处理下其SOD活性恢复到对照水平,而在200微克·克⁻¹菲处理下观察到SOD活性显著增加(P < 0.05)。实验还表明,100和200微克·克⁻¹菲处理5天和8天后,幼苗中MDA含量显著增加(P < 0.05和P < 0.01),这表明膜系统受到菲胁迫的损伤。上述所有结果表明,大豆幼苗的SOD活性可能适合作为菲胁迫的生物标志物。

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