• 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

改性硅藻土用于土壤修复及其对金盏花中重金属吸收的影响。

Modified diatomite for soil remediation and its implications for heavy metal absorption in Calendula officinalis.

机构信息

Soil Science Department, Faculty of Agriculture, University of Zanjan, Zanjan, Iran.

Centre of Research Impact and Outreach, Institute of Engineering and Technology, Chitkara University, Rajpura, Punjab, 140401, India.

出版信息

BMC Plant Biol. 2024 May 3;24(1):357. doi: 10.1186/s12870-024-05068-7.

DOI:10.1186/s12870-024-05068-7
PMID:38698319
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11067082/
Abstract

BACKGROUND

Among different adsorbents, natural and inorganic compounds such as diatomite are important and advantageous in terms of high efficiency and cost-effectiveness, and function in stabilizing heavy metals in the environment. Calendula officinalis, a plant known as a high accumulator of heavy metals, was cultivated in soil treated with varying concentrations of modified diatomite to demonstrate the efficiency of modified diatomite in stabilizating of heavy metals in soils, RESULTS: The modification of diatomite aimed to enhance Calendula officinalis adsorptive properties, particularly towards heavy metals such as lead (Pb), Zinc (Zn), Chromium (Cr), Nickle (Ni), and Copper (Cu), common contaminants in industrial soils. The experimental design included both control and treated soil samples, with assessments at regular intervals. Modified diatomite significantly decreased the bioaccumulation of heavy metals in contaminated soils except Zn, evidenced by decreased DTPA extractable heavy metals in soil and also heavy metal concentrations in plant tissues. Using 10% modified diatomite decreased 91% Pb and Cu, 78% Cr, and 79% Ni concentration of plants compared to the control treatment. The highest concentration of Zn in plant tissue was observed in 2.5% modified diatomite treatment. Remarkably, the application of modified diatomite also appeared to improve the nutrient profile of the soil, leading to enhanced uptake of key nutrients like phosphorus (P) 1.18%, and potassium (K) 79.6% in shoots and 82.3% in roots in Calendula officinalis. Consequently, treated plants exhibited improved growth characteristics, including shoots and roots height of 16.98% and 12.8% respectively, and shoots fresh and dry weight of 48.5% and 50.2% respectively., compared to those in untreated, contaminated soil.

CONCLUSION

The findings suggest promising implications for using such amendments in ecological restoration and sustainable agriculture, particularly in areas impacted by industrial pollution.

摘要

背景

在不同的吸附剂中,天然和无机化合物,如硅藻土,在高效和经济实惠方面具有重要优势,并且可以稳定环境中的重金属。金盏花是一种重金属高积累植物,在不同浓度改性硅藻土处理的土壤中进行种植,以证明改性硅藻土在稳定土壤重金属方面的效率。

结果

硅藻土的改性旨在增强金盏花的吸附特性,特别是对铅(Pb)、锌(Zn)、铬(Cr)、镍(Ni)和铜(Cu)等重金属的吸附,这些重金属是工业土壤中的常见污染物。实验设计包括对照和处理土壤样本,并定期进行评估。改性硅藻土显著降低了受污染土壤中重金属的生物积累,除 Zn 外,这一点可以从土壤中 DTPA 可提取重金属的减少以及植物组织中重金属浓度的降低得到证明。与对照处理相比,使用 10%的改性硅藻土可使植物中 91%的 Pb 和 Cu、78%的 Cr 和 79%的 Ni 浓度降低。在植物组织中观察到的最高 Zn 浓度出现在 2.5%的改性硅藻土处理中。值得注意的是,改性硅藻土的应用似乎也改善了土壤的营养状况,导致金盏花中关键养分如磷(P)的吸收增加 1.18%,钾(K)的吸收增加 79.6%在地上部分和 82.3%在根部。因此,与未经处理的、受污染的土壤相比,处理过的植物表现出更好的生长特性,包括地上部分和根部的高度分别增加了 16.98%和 12.8%,地上部分和根部的鲜重和干重分别增加了 48.5%和 50.2%。

结论

研究结果表明,在生态恢复和可持续农业中使用这种改良剂具有广阔的前景,特别是在受到工业污染影响的地区。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/a04a3ee62e4c/12870_2024_5068_Fig14_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/a0b5389dc488/12870_2024_5068_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/8a33e1ac35c9/12870_2024_5068_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/e9261a338192/12870_2024_5068_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/23e598ed080a/12870_2024_5068_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/f7a80415c6d3/12870_2024_5068_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/eecc82cd8cd9/12870_2024_5068_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/3e39e17e65d0/12870_2024_5068_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/3cf612acfb54/12870_2024_5068_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/c9f7b04c7aba/12870_2024_5068_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/6cc57b80cc8a/12870_2024_5068_Fig10_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/1e324cfe8ca7/12870_2024_5068_Fig11_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/3d0ad1e1c459/12870_2024_5068_Fig12_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/5e2b67bc4c12/12870_2024_5068_Fig13_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/a04a3ee62e4c/12870_2024_5068_Fig14_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/a0b5389dc488/12870_2024_5068_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/8a33e1ac35c9/12870_2024_5068_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/e9261a338192/12870_2024_5068_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/23e598ed080a/12870_2024_5068_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/f7a80415c6d3/12870_2024_5068_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/eecc82cd8cd9/12870_2024_5068_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/3e39e17e65d0/12870_2024_5068_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/3cf612acfb54/12870_2024_5068_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/c9f7b04c7aba/12870_2024_5068_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/6cc57b80cc8a/12870_2024_5068_Fig10_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/1e324cfe8ca7/12870_2024_5068_Fig11_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/3d0ad1e1c459/12870_2024_5068_Fig12_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/5e2b67bc4c12/12870_2024_5068_Fig13_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/301a/11067082/a04a3ee62e4c/12870_2024_5068_Fig14_HTML.jpg

相似文献

1
Modified diatomite for soil remediation and its implications for heavy metal absorption in Calendula officinalis.改性硅藻土用于土壤修复及其对金盏花中重金属吸收的影响。
BMC Plant Biol. 2024 May 3;24(1):357. doi: 10.1186/s12870-024-05068-7.
2
Nano silica's role in regulating heavy metal uptake in Calendula officinalis.纳米二氧化硅在调节金盏花中重金属吸收的作用。
BMC Plant Biol. 2024 Jun 25;24(1):598. doi: 10.1186/s12870-024-05311-1.
3
Modified natural diatomite and its enhanced immobilization of lead, copper and cadmium in simulated contaminated soils.改性天然硅藻土及其对模拟污染土壤中铅、铜和镉的增强固定化作用。
J Hazard Mater. 2015 May 30;289:210-218. doi: 10.1016/j.jhazmat.2015.02.052. Epub 2015 Feb 20.
4
Effect of Arbuscular Mycorrhizal Fungi On Yield and Phytoremediation Performance of Pot Marigold (Calendula officinalis L.) Under Heavy Metals Stress.丛枝菌根真菌对重金属胁迫下金盏菊(Calendula officinalis L.)产量及植物修复性能的影响
Int J Phytoremediation. 2015;17(12):1244-52. doi: 10.1080/15226514.2015.1045131.
5
Phytoremediation of Heavy Metal-Contaminated Soil by Switchgrass: A Comparative Study Utilizing Different Composts and Coir Fiber on Pollution Remediation, Plant Productivity, and Nutrient Leaching.利用不同堆肥和椰糠纤维对污染修复、植物生产力和养分淋溶的影响比较研究:柳枝稷修复重金属污染土壤
Int J Environ Res Public Health. 2019 Apr 9;16(7):1261. doi: 10.3390/ijerph16071261.
6
Hyperaccumulator oilcake manure as an alternative for chelate-induced phytoremediation of heavy metals contaminated alluvial soils.超富集植物油饼肥作为螯合剂诱导修复重金属污染冲积土的替代物。
Int J Phytoremediation. 2015;17(1-6):256-63. doi: 10.1080/15226514.2014.883497.
7
The rotation of white lupin (Lupinus albus L.) with metal-accumulating plant crops: a strategy to increase the benefits of soil phytoremediation.白羽扇豆(Lupinus albus L.)与金属积累型作物轮作:一种提高土壤植物修复效益的策略。
J Environ Manage. 2014 Dec 1;145:35-42. doi: 10.1016/j.jenvman.2014.06.001. Epub 2014 Jul 1.
8
A field trial for remediation of multi-metal contaminated soils using the combination of fly ash stabilization and Zanthoxylumbungeanum- Lolium perenne intercropping system.利用粉煤灰稳定化和花椒-黑麦草间作系统修复多金属污染土壤的田间试验。
J Environ Manage. 2024 Jun;361:121231. doi: 10.1016/j.jenvman.2024.121231. Epub 2024 May 28.
9
Effect of bamboo and rice straw biochars on the mobility and redistribution of heavy metals (Cd, Cu, Pb and Zn) in contaminated soil.竹炭和稻草生物炭对污染土壤中重金属(镉、铜、铅和锌)迁移性及再分布的影响。
J Environ Manage. 2017 Jan 15;186(Pt 2):285-292. doi: 10.1016/j.jenvman.2016.05.068. Epub 2016 Jun 2.
10
Accumulation of heavy metals in native Andean plants: potential tools for soil phytoremediation in Ancash (Peru).本土安第斯植物中重金属的积累:秘鲁安卡什地区土壤植物修复的潜在工具。
Environ Sci Pollut Res Int. 2018 Dec;25(34):33957-33966. doi: 10.1007/s11356-018-3325-z. Epub 2018 Oct 2.

引用本文的文献

1
The Use of Diatomite-Based Composites for the Immobilization of Toxic Heavy Metals in Industrial Wastes Using Post-Flotation Sediment as an Example.以浮选后沉积物为例,利用硅藻土基复合材料固定工业废物中的有毒重金属
Materials (Basel). 2024 Dec 17;17(24):6174. doi: 10.3390/ma17246174.

本文引用的文献

1
Thermal Hydrolysis Pretreatment-Anaerobic Digestion Promotes Plant-Growth Biostimulants Production from Sewage Sludge by Upregulating Aromatic Amino Acids Transformation and Quinones Supply.热水解预处理-厌氧消化通过上调芳香族氨基酸转化和醌类供应促进污水污泥中植物生长生物刺激素的生产。
Environ Sci Technol. 2022 Feb 1;56(3):1938-1950. doi: 10.1021/acs.est.1c06506. Epub 2022 Jan 10.
2
Soil amendments for immobilization of potentially toxic elements in contaminated soils: A critical review.土壤改良剂在污染土壤中固定潜在有毒元素的研究进展。
Environ Int. 2020 Jan;134:105046. doi: 10.1016/j.envint.2019.105046. Epub 2019 Nov 12.
3
Fractionation, Mobility, and Contamination Assessment of Potentially Toxic Metals in Urban Soils in Four Industrial Serbian Cities.
城市土壤中潜在有毒金属的分馏、迁移和污染评估。
Arch Environ Contam Toxicol. 2018 Oct;75(3):335-350. doi: 10.1007/s00244-018-0518-x. Epub 2018 Mar 5.
4
Phytoremediation strategies for soils contaminated with heavy metals: Modifications and future perspectives.重金属污染土壤的植物修复策略:改良与未来展望。
Chemosphere. 2017 Mar;171:710-721. doi: 10.1016/j.chemosphere.2016.12.116. Epub 2016 Dec 23.
5
Silicon occurrence, uptake, transport and mechanisms of heavy metals, minerals and salinity enhanced tolerance in plants with future prospects: A review.硅在植物中的存在、吸收、运输以及重金属、矿物质和盐分增强植物耐受性的机制及未来展望:综述
J Environ Manage. 2016 Dec 1;183(Pt 3):521-529. doi: 10.1016/j.jenvman.2016.09.009. Epub 2016 Sep 9.
6
Cadmium, lead, and zinc mobility and plant uptake in a mine soil amended with sugarcane straw biochar.在添加甘蔗秸秆生物炭的矿区土壤中,镉、铅和锌的迁移性和植物吸收。
Environ Sci Pollut Res Int. 2015 Nov;22(22):17606-14. doi: 10.1007/s11356-015-4977-6. Epub 2015 Jul 7.
7
The effect of excess copper on growth and physiology of important food crops: a review.过量铜对重要粮食作物生长和生理的影响:综述
Environ Sci Pollut Res Int. 2015 Jun;22(11):8148-62. doi: 10.1007/s11356-015-4496-5. Epub 2015 Apr 15.
8
Modified natural diatomite and its enhanced immobilization of lead, copper and cadmium in simulated contaminated soils.改性天然硅藻土及其对模拟污染土壤中铅、铜和镉的增强固定化作用。
J Hazard Mater. 2015 May 30;289:210-218. doi: 10.1016/j.jhazmat.2015.02.052. Epub 2015 Feb 20.
9
Suppression of cadmium concentration in wheat grains by silicon is related to its application rate and cadmium accumulating abilities of cultivars.硅对小麦籽粒中镉浓度的抑制作用与其施用量及品种的镉积累能力有关。
J Sci Food Agric. 2015 Sep;95(12):2467-72. doi: 10.1002/jsfa.6976. Epub 2014 Nov 25.
10
Role of phosphate fertilizers in heavy metal uptake and detoxification of toxic metals.磷酸盐肥料在重金属吸收和解毒中的作用。
Chemosphere. 2014 Aug;108:134-44. doi: 10.1016/j.chemosphere.2014.01.030. Epub 2014 Feb 18.