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重金属对一种鉴定出的细菌菌株的生长、生理、细胞活力和生物膜形成的诱导调节作用。

Heavy Metals Induced Modulations in Growth, Physiology, Cellular Viability, and Biofilm Formation of an Identified Bacterial Isolate.

作者信息

Syed Asad, Zeyad Mohammad Tarique, Shahid Mohammad, Elgorban Abdallah M, Alkhulaifi Manal M, Ansari Irfan Aamer

机构信息

Department of Botany and Microbiology, College of Science, King Saud University, P.O. Box 2455, Riyadh 11451, Saudi Arabia.

Department of Agricultural Microbiology, Faculty of Agricultural Sciences, Aligarh Muslim University, Aligarh 202002, Uttar Pradesh, India.

出版信息

ACS Omega. 2021 Sep 16;6(38):25076-25088. doi: 10.1021/acsomega.1c04396. eCollection 2021 Sep 28.

Abstract

The release of untreated tannery effluents comprising biotoxic heavy metal (HM) compounds into the ecosystem is one of our society's most serious environmental and health issues. After discharge, HM-containing industrial effluents reach agricultural soils and thus negatively affect the soil microbial diversity. Considering these, we assessed the effect of HMs on identified soil beneficial bacteria. Here, the effects of four heavy metals (HMs), viz., chromium (Cr), cadmium (Cd), nickel (Ni), and lead (Pb), on cellular growth, physiology, cell permeability, and biofilm formation of MC9 (accession no.: MT672587) were evaluated. HMs in a concentration range of 25-200 μg mL were used throughout the study. Among HMs, Cd in general had the maximum detrimental effect on bacterial physiology. With increasing concentrations of HMs, bacterial activities consistently decreased. For instance, 200 μgCr mL concentration greatly and significantly ( ≤ 0.05) reduced the synthesis of indole-3-acetic acid (IAA) by 70% over control. Furthermore, 200 μg mL Cd maximally and significantly ( ≤ 0.05) reduced the synthesis of 2,3-dihydroxybenzoic acid (2,3-DHBA), salicylic acid (SA), 1-aminocyclopropane 1-carboxylate (ACC) deaminase, and extra polymeric substances (EPSs) of MC9 by 80, 81, 77, and 59%, respectively, over control. While assessing the toxic effect of HMs on the P-solubilizing activity of , the toxicity pattern followed the order Cr (mean value = 94.6 μg mL) > Cd (mean value = 127.2 μg mL) > Pb (mean value = 132.4 μg mL) > Ni (mean value = 140.4 μg mL). Furthermore, the colony-forming unit (CFU) count (Log) of strain MC9 was completely inhibited at 150, 175, and 200 μg mL concentrations of Cr and Cd. The confocal laser scanning microscopic (CLSM) analysis of HM-treated bacterial cells showed an increased number of red-colored dead cells as the concentration of HMs increased from 25 to 200 μg mL. Likewise, the biofilm formation ability of strain MC9 was maximally ( ≤ 0.05) inhibited at higher concentrations of Cd. In summary, the present investigation undoubtedly suggests that strain MC9 recovered from the HM-contaminated rhizosphere endowed with multiple activities could play an important role in agricultural practices to augment crop productivity in soils contaminated with HMs. Also, there is an urgent need to control the direct discharge of industrial waste into running water to minimize heavy metal pollution. Furthermore, before the application of HMs in agricultural fields, their appropriate field dosages must be carefully monitored.

摘要

未处理的制革废水含有生物毒性重金属(HM)化合物,排放到生态系统中是当今社会最严重的环境与健康问题之一。排放后,含重金属的工业废水进入农业土壤,进而对土壤微生物多样性产生负面影响。考虑到这些,我们评估了重金属对已鉴定的土壤有益细菌的影响。在此,评估了四种重金属,即铬(Cr)、镉(Cd)、镍(Ni)和铅(Pb)对MC9(登录号:MT672587)细胞生长、生理、细胞通透性和生物膜形成的影响。在整个研究中使用了浓度范围为25 - 200μg/mL的重金属。在这些重金属中,Cd总体上对细菌生理的有害影响最大。随着重金属浓度的增加,细菌活性持续下降。例如,200μg Cr/mL的浓度比对照显著(≤0.05)大幅降低了吲哚 - 3 - 乙酸(IAA)的合成达70%。此外,200μg/mL的Cd比对照最大且显著(≤0.05)地分别降低了MC9的2,3 - 二羟基苯甲酸(2,3 - DHBA)、水杨酸(SA)、1 - 氨基环丙烷 - 1 - 羧酸(ACC)脱氨酶和胞外聚合物(EPSs)的合成,降幅分别为80%、81%、77%和59%。在评估重金属对MC9解磷活性的毒性作用时,毒性模式为Cr(平均值 = 94.6μg/mL)> Cd(平均值 = 127.2μg/mL)> Pb(平均值 = 132.4μg/mL)> Ni(平均值 = 140.4μg/mL)。此外,在Cr和Cd浓度为150、175和200μg/mL时,菌株MC9的菌落形成单位(CFU)计数(Log)被完全抑制。对经重金属处理的细菌细胞进行共聚焦激光扫描显微镜(CLSM)分析表明,随着重金属浓度从25μg/mL增加到200μg/mL,红色死细胞数量增加。同样,在较高浓度的Cd下,菌株MC9的生物膜形成能力最大程度(≤0.05)受到抑制。总之,本研究无疑表明,从受重金属污染的根际环境中分离出的具有多种活性的菌株MC9,在提高受重金属污染土壤中作物生产力的农业实践中可发挥重要作用。此外,迫切需要控制工业废物直接排放到流水之中,以尽量减少重金属污染。此外,在将重金属应用于农业领域之前,必须仔细监测其合适的田间用量。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/085e/8482775/de3559c06409/ao1c04396_0002.jpg

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