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干旱和镉胁迫下深色有隔内生真菌的生物学特性及其对调节……抗逆性的影响研究

Study on the Biological Characteristics of Dark Septate Endophytes under Drought and Cadmium Stress and Their Effects on Regulating the Stress Resistance of .

作者信息

Wang Duo, Xie Yali, Zhang Wanyi, Yao Li, He Chao, He Xueli

机构信息

School of Life Sciences, Hebei University, Baoding 071002, China.

Institute of Medicinal Plant Development, Chinese Academy of Medical Sciences & Peking Union Medical College, Beijing 100193, China.

出版信息

J Fungi (Basel). 2024 Jul 16;10(7):491. doi: 10.3390/jof10070491.

DOI:10.3390/jof10070491
PMID:39057377
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11277632/
Abstract

is a famous traditional medicinal plant. However, drought and cadmium (Cd) pollution are the main abiotic stress factors that affect plant growth and yield and the ability to improve the host's stress resistance through the use of beneficial endophytic fungi. To evaluate the tolerance of dark septate endophytes (DSE) to various abiotic stresses, 10 DSE strains [ (), (), (), (), (), (), (), (), (), and ()] were investigated under different drought and Cd stressors in vitro by using solid-plate cultures and liquid-shaker cultures in the current study. The experiments involved using varying concentrations of PEG (0, 9, 18, and 27%) and Cd (0, 25, 50, and 100 mg/L) to simulate different stress conditions on DSE. Additionally, the effect of DSE ( and ) on the growth of at different field water capacities (70% and 40%) and at different CdCl concentrations (0, 5, 10, and 15 mg Cd/kg) in soil was studied. The results demonstrated that the colony growth rates of , , , , and were the first to reach the maximum diameter at a PEG concentration of 18%. , , and remained growth-active at 100 mg Cd/L. In addition, , , and were selected for drought and Cd stress tests. The results of the drought-combined-with-Cd-stress solid culture indicated that the growth rate of was significantly superior to that of the other strains. In the liquid culture condition, the biomasses of and were the highest, with biomasses of 1.39 g and 1.23 g under the concentration of 18% + 25 mg Cd/L, and had the highest biomass of 1.71 g at 18% + 50 mg Cd/L concentration, respectively. The CAT and POD activities of reached their peak levels at concentrations of 27% + 50 mg Cd/L and 27% + 25 mg Cd/L, respectively. Compared to the control, these levels indicated increases of 416.97% and 573.12%, respectively. , , and positively influenced SOD activity. The glutathione (GSH) contents of , , and were increased under different combined stressors of drought and Cd. The structural-equation-modeling (SEM) analysis revealed that positively influenced biomass and negatively affected Cd content, while and positively influenced Cd content. Under the stress of 40% field-water capacity and the synergistic stress of 40% field-water capacity and 5 mg Cd/kg soil, and significantly increased root weight of . This study provides guidance for the establishment of agricultural planting systems and has good development and utilization value.

摘要

是一种著名的传统药用植物。然而,干旱和镉(Cd)污染是影响植物生长和产量的主要非生物胁迫因素,而利用有益内生真菌可提高宿主的抗逆能力。为了评估深色有隔内生菌(DSE)对各种非生物胁迫的耐受性,在本研究中,通过固体平板培养和液体摇床培养,在体外不同干旱和镉胁迫条件下对10株DSE菌株[()、()、()、()、()、()、()、()、()和()]进行了研究。实验使用不同浓度的聚乙二醇(PEG,0、9、18和27%)和镉(0、25、50和100 mg/L)来模拟对DSE的不同胁迫条件。此外,还研究了DSE(和)在土壤中不同田间持水量(70%和40%)以及不同CdCl浓度(0、5、10和15 mg Cd/kg)下对的生长影响。结果表明,、、、、的菌落生长速率在PEG浓度为18%时最先达到最大直径。、和在100 mg Cd/L时仍保持生长活性。此外,选择、和进行干旱和镉胁迫试验。干旱与镉胁迫固体培养结果表明,的生长速率显著优于其他菌株。在液体培养条件下,和的生物量最高,在18% + 25 mg Cd/L浓度下生物量分别为1.39 g和1.23 g,在18% + 50 mg Cd/L浓度下的生物量最高,为1.71 g。的CAT和POD活性分别在27% + 50 mg Cd/L和27% + 25 mg Cd/L浓度时达到峰值水平。与对照相比,这些水平分别提高了416.97%和573.12%。、和对SOD活性有正向影响。在干旱和镉的不同复合胁迫下,、和的谷胱甘肽(GSH)含量增加。结构方程模型(SEM)分析表明,对生物量有正向影响,对镉含量有负向影响,而和对镉含量有正向影响。在田间持水量为40%的胁迫以及田间持水量为40%和土壤中5 mg Cd/kg的协同胁迫下,和显著增加了的根重。本研究为农业种植系统的建立提供了指导,具有良好的开发利用价值。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/915f/11277632/f81ea228292a/jof-10-00491-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/915f/11277632/d2206877f78a/jof-10-00491-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/915f/11277632/0056b4bb8f83/jof-10-00491-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/915f/11277632/f81ea228292a/jof-10-00491-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/915f/11277632/d2206877f78a/jof-10-00491-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/915f/11277632/0056b4bb8f83/jof-10-00491-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/915f/11277632/f81ea228292a/jof-10-00491-g007.jpg

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