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在镉胁迫下增强花椰菜生长:耐镉菌株与茉莉酸叶面喷施的协同效应

Enhancing cauliflower growth under cadmium stress: synergistic effects of Cd-tolerant strains and jasmonic acid foliar application.

作者信息

Shahid Shumila, Dar Abubakar, Hussain Azhar, Khalid Imran, Latif Muhammad, Ahmad Hafiz Tanvir, Mehmood Tariq, Aloud Saud S

机构信息

Department of Soil Science, The Islamia University of Bahawalpur, Bahawalpur, Pakistan.

Department of Extension Education, The Islamia University of Bahawalpur, Bahawalpur, Pakistan.

出版信息

Front Microbiol. 2024 Aug 7;15:1444374. doi: 10.3389/fmicb.2024.1444374. eCollection 2024.

DOI:10.3389/fmicb.2024.1444374
PMID:39220045
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11363903/
Abstract

The pollution of heavy metals (HMs) is a major environmental concern for agricultural farming communities due to water scarcity, which forces farmers to use wastewater for irrigation purposes in Pakistan. Vegetables grown around the cities are irrigated with domestic and industrial wastewater from areas near mining, paint, and ceramic industries that pollute edible parts of crops with various HMs. Cadmium (Cd) is an extremely toxic metal in arable soil that enters the food chain and damages the native biota, ultimately causing a reduction in plant growth and development. However, the use of microbes and growth regulators enhances plant growth and development as well as HM immobilization into the cell wall and hinders their entry into the food chain. Thus, the integrated use of bacterial consortium along with exogenously applied jasmonic acid (JA) mitigates the adverse effect of metal stress, ultimately reducing the metal mobility into roots by soil. Therefore, the current study was conducted to check the impact of Cd-tolerant bacteria and JA on the growth, nutrient status, and uptake of Cd in the cauliflower (). Our results demonstrated that increasing concentrations of Cd negatively affect growth, physiological, and biochemical attributes, while the use of a bacterial consortium (SS7 + SS8) with JA (40 μmol L) significantly improved chlorophyll contents, stem fresh and dry biomass (19.7, 12.7, and 17.3%), root length and root fresh and dry weights (28.8, 15.2, and 23.0%), and curd fresh and dry weights and curd diameter (18.7, 12.6, and 15.1%). However, the maximum reduction in soil Cd, roots, and curd uptake was observed by 8, 11, and 9.3%, respectively, under integrated treatment as compared to the control. Moreover, integrating bacterial consortium and JA improves superoxide dismutase (SOD) (16.79%), peroxidase dismutase (POD) (26.96%), peroxidase (POX) (26.13%), and catalase (CAT) (26.86%). The plant nitrogen, phosphorus, and potassium contents were significantly increased in soil, roots, and curd up to 8, 11, and 9.3%, respectively. Hence, a consortium of strains in combination with JA is a potential phytostabilizer and it reduces the uptake of Cd from soil to roots to alleviate the adverse impact on cauliflower's growth and productivity.

摘要

由于水资源短缺,重金属污染成为农业种植社区主要的环境问题,这迫使巴基斯坦的农民使用废水进行灌溉。城市周边种植的蔬菜使用来自采矿、油漆和陶瓷工业附近地区的生活和工业废水灌溉,这些废水用各种重金属污染了农作物的可食用部分。镉(Cd)是耕地土壤中一种剧毒金属,它进入食物链并损害本地生物群,最终导致植物生长发育受阻。然而,微生物和生长调节剂的使用可以促进植物生长发育,并将重金属固定在细胞壁中,从而阻止它们进入食物链。因此,联合使用细菌联合体和外源施用茉莉酸(JA)可减轻金属胁迫的不利影响,最终减少土壤中金属向根部的迁移。因此,开展本研究以检测耐镉细菌和JA对花椰菜生长、养分状况及镉吸收的影响。我们的结果表明,镉浓度增加对生长、生理和生化特性产生负面影响;而使用细菌联合体(SS7 + SS8)与JA(40 μmol·L)显著提高了叶绿素含量、茎的鲜重和干重(分别提高了19.7%、12.7%和17.3%)、根长以及根的鲜重和干重(分别提高了28.8%、15.2%和23.0%),还有花球的鲜重、干重和花球直径(分别提高了18.7%、12.6%和15.1%)。然而,与对照相比,综合处理下土壤镉、根部和花球吸收量的最大降幅分别为8%、11%和9.3%。此外,联合使用细菌联合体和JA可提高超氧化物歧化酶(SOD)(提高16.79%)、过氧化物歧化酶(POD)(提高26.96%)、过氧化物酶(POX)(提高26.13%)和过氧化氢酶(CAT)(提高26.86%)的活性。土壤、根部和花球中的植物氮、磷和钾含量分别显著提高了8%、11%和9.3%。因此,菌株联合体与JA相结合是一种潜在的植物稳定剂,它减少了镉从土壤到根部的吸收,以减轻对花椰菜生长和生产力的不利影响。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/349a91067f0c/fmicb-15-1444374-g008.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/47cf7ad578a1/fmicb-15-1444374-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/6155748cda3c/fmicb-15-1444374-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/349a91067f0c/fmicb-15-1444374-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/489161983a0d/fmicb-15-1444374-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/c4ade27b2ff3/fmicb-15-1444374-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/9e05433ab0c2/fmicb-15-1444374-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/fe3bdd407412/fmicb-15-1444374-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/388c8dc7af58/fmicb-15-1444374-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/47cf7ad578a1/fmicb-15-1444374-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/6155748cda3c/fmicb-15-1444374-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b53e/11363903/349a91067f0c/fmicb-15-1444374-g008.jpg

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