• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

有机肥料可提高黄秋葵(Abelmoschus esculentus(L.)Moench)耐盐诱导的渗透和氧化胁迫能力。

Organic amendments improve salinity-induced osmotic and oxidative stress tolerance in Okra (Abelmoschus esculentus (L.)Moench).

机构信息

Department of Botany, Lahore College for Women University, Lahore, Pakistan.

Institute of Botany, University of the Punjab, Lahore, Pakistan.

出版信息

BMC Plant Biol. 2023 Oct 27;23(1):522. doi: 10.1186/s12870-023-04527-x.

DOI:10.1186/s12870-023-04527-x
PMID:37891469
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC10605961/
Abstract

AIMS

Salinity adversely affects okra [Abelmoschus esculentus (L.) Moench] plants by inducing osmotic and oxidative stresses. This study was designed to enhance salinity-induced osmotic and oxidative stress tolerance in okra plants by applying organic amendments.

METHODS

The effects of different organic amendments (municipal solid waste compost, farmyard manure (FYM) and press mud) on osmotic potential, water use efficiency, activities of antioxidant enzymes, total soluble sugar, total soluble proline, total soluble protein and malondialdehyde (MDA) contents of okra plants grown under saline conditions (50 mM sodium chloride) were evaluated in a pot experiment. The organic amendments were applied each at the rate of 5% and 10% per pot or in various combinations (compost + FYM, FYM + press mud and compost + press mud each at the rate of 2.5% and 5% per pot).

RESULTS

As compared to control, high total soluble sugar (60.41), total soluble proline (33.88%) and MDA (51%) contents and increased activities of antioxidant enzymes [superoxide dismutase (83.54%), catalase (78.61%), peroxidase (53.57%] in salinity-stressed okra plants, were indicative of oxidative stress. Salinity significantly reduced the osmotic potential (41.78%) and water use efficiency (4.75%) of okra plants compared to control. Under saline conditions, 5% (farmyard manure + press mud) was the most effective treatment, which significantly improved osmotic potential (27.05%), total soluble sugar (4.20%), total soluble protein (73.62%) and total soluble proline (23.20%) contents and superoxide dismutase activity (32.41%), compared to saline soil. Application of 2.5% (FYM + press mud), 5% press mud, and 10% compost significantly reduced MDA content (27%) and improved activities of catalase (38.64%) and peroxidase (48.29%), respectively, compared to saline soil, thus facilitated to alleviate oxidative stress in okra plants.

CONCLUSIONS

Using organic amendments (municipal solid waste compost, farmyard manure and press mud) was a cost-effective approach to improve salinity-induced osmotic and oxidative stress tolerance in okra plants.

摘要

目的

盐分通过诱导渗透胁迫和氧化胁迫对黄秋葵(Abelmoschus esculentus(L.)Moench)植物造成不利影响。本研究旨在通过施用有机改良剂来提高黄秋葵植物对盐胁迫诱导的渗透胁迫和氧化胁迫的耐受性。

方法

采用盆栽试验,评估了不同有机改良剂(城市固体废物堆肥、农家肥(FYM)和压榨泥)对盐胁迫(50 mM 氯化钠)下黄秋葵植物的渗透势、水分利用效率、抗氧化酶活性、总可溶性糖、总可溶性脯氨酸、总可溶性蛋白和丙二醛(MDA)含量的影响。有机改良剂的施用量为每盆 5%和 10%,或按不同组合(堆肥+FYM、FYM+压榨泥和堆肥+压榨泥,各为每盆 2.5%和 5%)施用。

结果

与对照相比,盐胁迫下黄秋葵植物的总可溶性糖(60.41%)、总可溶性脯氨酸(33.88%)和 MDA(51%)含量升高,抗氧化酶活性[超氧化物歧化酶(83.54%)、过氧化氢酶(78.61%)、过氧化物酶(53.57%)]增强,表明存在氧化胁迫。与对照相比,盐胁迫显著降低了黄秋葵植物的渗透势(41.78%)和水分利用效率(4.75%)。在盐胁迫条件下,5%(农家肥+压榨泥)是最有效的处理方法,与盐土相比,它显著提高了渗透势(27.05%)、总可溶性糖(4.20%)、总可溶性蛋白(73.62%)和总可溶性脯氨酸(23.20%)含量以及超氧化物歧化酶活性(32.41%)。施用 2.5%(FYM+压榨泥)、5%压榨泥和 10%堆肥分别显著降低了 MDA 含量(27%),并提高了过氧化氢酶(38.64%)和过氧化物酶(48.29%)的活性,从而缓解了黄秋葵植物的氧化胁迫。

结论

使用有机改良剂(城市固体废物堆肥、农家肥和压榨泥)是一种经济有效的方法,可以提高黄秋葵植物对盐胁迫诱导的渗透胁迫和氧化胁迫的耐受性。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/978b2cb0c06c/12870_2023_4527_Fig12_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/5a89d058ee1b/12870_2023_4527_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/86de23c42b25/12870_2023_4527_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/f366a69e829e/12870_2023_4527_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/6a05a1254977/12870_2023_4527_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/f54f312720e7/12870_2023_4527_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/f0bd94d22af6/12870_2023_4527_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/687d473f294f/12870_2023_4527_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/a948cc18c96a/12870_2023_4527_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/4a1e8662d15e/12870_2023_4527_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/62ee57ec5298/12870_2023_4527_Fig10_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/49db6b92c5fb/12870_2023_4527_Fig11_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/978b2cb0c06c/12870_2023_4527_Fig12_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/5a89d058ee1b/12870_2023_4527_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/86de23c42b25/12870_2023_4527_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/f366a69e829e/12870_2023_4527_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/6a05a1254977/12870_2023_4527_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/f54f312720e7/12870_2023_4527_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/f0bd94d22af6/12870_2023_4527_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/687d473f294f/12870_2023_4527_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/a948cc18c96a/12870_2023_4527_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/4a1e8662d15e/12870_2023_4527_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/62ee57ec5298/12870_2023_4527_Fig10_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/49db6b92c5fb/12870_2023_4527_Fig11_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f578/10605961/978b2cb0c06c/12870_2023_4527_Fig12_HTML.jpg

相似文献

1
Organic amendments improve salinity-induced osmotic and oxidative stress tolerance in Okra (Abelmoschus esculentus (L.)Moench).有机肥料可提高黄秋葵(Abelmoschus esculentus(L.)Moench)耐盐诱导的渗透和氧化胁迫能力。
BMC Plant Biol. 2023 Oct 27;23(1):522. doi: 10.1186/s12870-023-04527-x.
2
Effects of malic acid and EDTA on oxidative stress and antioxidant enzymes of okra (Abelmoschus esculentus L.) exposed to cadmium stress.亚硫酸氢钠和 EDTA 对镉胁迫下蕹菜(Abelmoschus esculentus L.)氧化应激和抗氧化酶的影响。
Ecotoxicol Environ Saf. 2022 Dec 15;248:114320. doi: 10.1016/j.ecoenv.2022.114320. Epub 2022 Nov 21.
3
Manure-biochar compost mitigates the soil salinity stress in tomato plants by modulating the osmoregulatory mechanism, photosynthetic pigments, and ionic homeostasis.粪肥-生物炭堆肥通过调节渗透调节机制、光合色素和离子平衡来缓解番茄植株的土壤盐胁迫。
Sci Rep. 2024 Sep 20;14(1):21929. doi: 10.1038/s41598-024-73093-5.
4
Foliar Spray of Alpha-Tocopherol Modulates Antioxidant Potential of Okra Fruit under Salt Stress.α-生育酚叶面喷施对盐胁迫下秋葵果实抗氧化能力的影响
Plants (Basel). 2021 Jul 6;10(7):1382. doi: 10.3390/plants10071382.
5
Spatial variations in the biochemical potential of okra [Abelmoschus esculentus L. (Moench)] leaf and fruit under field conditions.田间条件下黄秋葵[Abelmoschus esculentus L. (Moench)]叶片和果实生化势的空间变化。
PLoS One. 2022 Feb 3;17(2):e0259520. doi: 10.1371/journal.pone.0259520. eCollection 2022.
6
Unlocking the potential of co-application of steel slag and biochar in mitigation of arsenic-induced oxidative stress by modulating antioxidant and glyoxalase system in Abelmoschus esculentus L.通过调节黄秋葵中的抗氧化剂和乙二醛酶系统,释放钢渣和生物炭联合应用在减轻砷诱导的氧化应激方面的潜力
Chemosphere. 2024 Mar;351:141232. doi: 10.1016/j.chemosphere.2024.141232. Epub 2024 Jan 17.
7
Exogenous proline effects on photosynthetic performance and antioxidant defense system of young olive tree.外源脯氨酸对幼龄橄榄树光合作用及抗氧化防御系统的影响。
J Agric Food Chem. 2010 Apr 14;58(7):4216-22. doi: 10.1021/jf9041479.
8
[Effect of NaCl stress on physiological characteristics of Physalis alkekengi var. franchetii test-tube plantlet].[NaCl胁迫对酸浆试管苗生理特性的影响]
Zhong Yao Cai. 2014 Oct;37(10):1725-9.
9
Citrus Epicarp-Derived Biochar Reduced Cd Uptake and Ameliorates Oxidative Stress in Young Abelmoschus esculentus (L.) Moench (okra) Under Low Cd Stress.柑橘外果皮衍生生物炭降低了低镉胁迫下嫩黄秋葵对镉的吸收并减轻了氧化应激
Bull Environ Contam Toxicol. 2018 Jun;100(6):827-833. doi: 10.1007/s00128-018-2339-z. Epub 2018 Apr 17.
10
Antioxidant enzyme and osmotic adjustment changes in bean seedlings as affected by biochar under salt stress.盐胁迫下生物炭对菜豆幼苗抗氧化酶及渗透调节的影响
Ecotoxicol Environ Saf. 2017 Mar;137:64-70. doi: 10.1016/j.ecoenv.2016.11.029. Epub 2016 Dec 19.

引用本文的文献

1
Salt gradient-driven adaptation in okra: uncovering mechanisms of tolerance and growth regulation.秋葵中盐梯度驱动的适应性:揭示耐受性和生长调节机制。
Front Plant Sci. 2025 Jul 23;16:1648092. doi: 10.3389/fpls.2025.1648092. eCollection 2025.

本文引用的文献

1
Physically separated soil organic matter pools as indicators of carbon and nitrogen change under long-term fertilization in a Chinese Mollisol.长期施肥下中国潮土中物理分离的土壤有机物质库作为碳氮变化的指标。
Environ Res. 2023 Jan 1;216(Pt 2):114626. doi: 10.1016/j.envres.2022.114626. Epub 2022 Oct 26.
2
Mitigation of Salinity Stress in Maize Seedlings by the Application of Vermicompost and Sorghum Water Extracts.通过施用蚯蚓堆肥和高粱水提取物缓解玉米幼苗的盐分胁迫
Plants (Basel). 2022 Sep 28;11(19):2548. doi: 10.3390/plants11192548.
3
The Effects of Hydro-Priming and Colonization with and on Physio-Biochemical Traits, Flavonolignans and Fatty Acids Composition of Milk Thistle () under Saline Conditions.
盐胁迫条件下,水引发处理以及接种和 对水飞蓟生理生化特性、黄酮木脂素和脂肪酸组成的影响。 (注:原文中“and ”部分内容缺失,这可能影响对完整意思的准确理解)
Plants (Basel). 2022 May 10;11(10):1281. doi: 10.3390/plants11101281.
4
Melatonin Induced Cold Tolerance in Plants: Physiological and Molecular Responses.褪黑素诱导植物的耐寒性:生理和分子反应
Front Plant Sci. 2022 Mar 14;13:843071. doi: 10.3389/fpls.2022.843071. eCollection 2022.
5
Crucial Cell Signaling Compounds Crosstalk and Integrative Multi-Omics Techniques for Salinity Stress Tolerance in Plants.植物耐盐胁迫的关键细胞信号传导化合物的相互作用及整合多组学技术
Front Plant Sci. 2021 Aug 13;12:670369. doi: 10.3389/fpls.2021.670369. eCollection 2021.
6
Morpho-Physio-Biochemical and Molecular Responses of Maize Hybrids to Salinity and Waterlogging during Stress and Recovery Phase.玉米杂交种在胁迫和恢复阶段对盐渍化和涝渍的形态生理生化及分子响应
Plants (Basel). 2021 Jul 1;10(7):1345. doi: 10.3390/plants10071345.
7
Metagenomic insights into nitrogen and phosphorus cycling at the soil aggregate scale driven by organic material amendments.土壤团聚体尺度上有机物料添加驱动的氮磷循环的宏基因组学研究
Sci Total Environ. 2021 Sep 1;785:147329. doi: 10.1016/j.scitotenv.2021.147329. Epub 2021 Apr 24.
8
The potential mitigation effect of ZnO nanoparticles on [ L. Moench] metabolism under salt stress conditions.氧化锌纳米颗粒在盐胁迫条件下对[L. Moench]代谢的潜在缓解作用。
Saudi J Biol Sci. 2020 Nov;27(11):3132-3137. doi: 10.1016/j.sjbs.2020.08.005. Epub 2020 Aug 6.
9
ACC deaminase in plant growth-promoting bacteria (PGPB): An efficient mechanism to counter salt stress in crops.植物促生细菌(PGPB)中的 ACC 脱氨酶:一种应对作物盐胁迫的有效机制。
Microbiol Res. 2020 May;235:126439. doi: 10.1016/j.micres.2020.126439. Epub 2020 Feb 15.
10
An Overview of Hazardous Impacts of Soil Salinity in Crops, Tolerance Mechanisms, and Amelioration through Selenium Supplementation.土壤盐分对作物危害的概述、耐盐机制及硒的缓解作用。
Int J Mol Sci. 2019 Dec 24;21(1):148. doi: 10.3390/ijms21010148.