• 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

入侵杂草作为潜在毒性金属的生物监测和植物修复剂:马来西亚半岛的案例研究。

Invasive Weed as a Potential Biomonitor and a Phytoremediator of Potentially Toxic Metals: A Case Study in Peninsular Malaysia.

机构信息

Department of Biology, Faculty of Science, Universiti Putra Malaysia, UPM, Serdang 43400, Malaysia.

Department of Biology, Faculty of Science, University of Tabuk, Tabuk 741, Saudi Arabia.

出版信息

Int J Environ Res Public Health. 2021 Apr 28;18(9):4682. doi: 10.3390/ijerph18094682.

DOI:10.3390/ijerph18094682
PMID:33924835
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC8124176/
Abstract

The invasive weed was investigated for its potential as a biomonitor and as a phytoremediator of potentially toxic metals (PTMs) (Cd, Cu, Ni, Pb, and Zn) in Peninsular Malaysia owing to its ecological resistance towards unfavourable environments. The biomonitoring potential of PTMs was determined based on the correlation analysis of the metals in the different parts of the plant (leaves, stems, and roots) and its habitat topsoils. In the roots, the concentrations (mg/kg dry weight) of Cd, Cu, Ni, Pb, and Zn ranged from 0.03 to 2.18, 9.22 to 139, 0.63 to 5.47, 2.43 to 10.5, and 50.7 to 300, respectively. In the leaves, the concentrations (mg/kg dry weight) of Cd, Cu, Ni, Pb, and Zn ranged from 0.03 to 1.16, 7.94 to 20.2, 0.03 to 6.13, 2.10 to 21.8, and 18.8 to 160, respectively. In the stems, the concentrations (mg/kg dry weight) of Cd, Cu, Ni, Pb, and Zn ranged from 0.03 to 1.25, 5.57 to 11.8, 0.23 to 3.69, 0.01 to 7.79, and 26.4 to 246, respectively. On the other hand, the phytoremediation potential of the five metals was estimated based on the bioconcentration factor (BCF) and the translocation factor (TF) values. Correlation analysis revealed that the roots and stems could be used as biomonitors of Cu, the stems as biomonitors of Ni, the roots and leaves as biomonitors of Pb, and all three parts of the plant as biomonitors of Zn. According to the BCF values, in the topsoil, the "easily, freely, leachable, or exchangeable" geochemical fractions of the five metals could be more easily transferred to the roots, leaves, and stems when compared with total concentrations. Based on the TF values of Cd, Ni, and Pb, the metal transfer to the stems (or leaves) from the roots was efficient (>1.0) at most sampling sites. The results of BCF and TF showed that was a good phytoextractor for Cd and Ni, and a good phytostabilizer for Cu, Pb, and Zn. Therefore, is a good candidate as a biomonitor and a phytoremediator of Ni, Pb, and Zn for sustainable contaminant remediation subject to suitable field management strategies.

摘要

由于其对不利环境的生态抗性,入侵杂草被调查为生物监测器和潜在有毒金属(PTM)(Cd、Cu、Ni、Pb 和 Zn)的植物修复剂,在马来西亚半岛。基于金属在植物不同部位(叶、茎和根)及其生境表土中的相关性分析,确定了 PTM 的生物监测潜力。在根部,Cd、Cu、Ni、Pb 和 Zn 的浓度(mg/kg 干重)分别为 0.03 至 2.18、9.22 至 139、0.63 至 5.47、2.43 至 10.5 和 50.7 至 300。在叶片中,Cd、Cu、Ni、Pb 和 Zn 的浓度(mg/kg 干重)分别为 0.03 至 1.16、7.94 至 20.2、0.03 至 6.13、2.10 至 21.8 和 18.8 至 160。在茎中,Cd、Cu、Ni、Pb 和 Zn 的浓度(mg/kg 干重)分别为 0.03 至 1.25、5.57 至 11.8、0.23 至 3.69、0.01 至 7.79 和 26.4 至 246。另一方面,根据生物浓缩因子(BCF)和迁移因子(TF)值,估算了这五种金属的植物修复潜力。相关分析表明,根和茎可作为 Cu 的生物监测器,茎可作为 Ni 的生物监测器,根和叶可作为 Pb 的生物监测器,植物的所有三个部分都可作为 Zn 的生物监测器。根据 BCF 值,在表土中,与总浓度相比,五种金属的“易、自由、可浸提或可交换”地球化学形态更容易转移到根、叶和茎中。根据 Cd、Ni 和 Pb 的 TF 值,在大多数采样点,金属从根部向茎(或叶)的转移效率(>1.0)较高。BCF 和 TF 的结果表明,对于 Cd 和 Ni, 是一种很好的植物提取剂,对于 Cu、Pb 和 Zn,是一种很好的植物稳定剂。因此, 是一种很好的生物监测器和 Ni、Pb 和 Zn 的植物修复剂,适用于可持续污染物修复,受适当的田间管理策略的影响。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/f570b6421494/ijerph-18-04682-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/7e52c7d30be0/ijerph-18-04682-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/7e6cae274482/ijerph-18-04682-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/0ab0f879be58/ijerph-18-04682-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/f6476491447c/ijerph-18-04682-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/2909856f874b/ijerph-18-04682-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/85f0f7f6132c/ijerph-18-04682-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/976082cbecd5/ijerph-18-04682-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/64cb41ff7257/ijerph-18-04682-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/9f8b2a7cbc5a/ijerph-18-04682-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/413d72acdd25/ijerph-18-04682-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/f570b6421494/ijerph-18-04682-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/7e52c7d30be0/ijerph-18-04682-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/7e6cae274482/ijerph-18-04682-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/0ab0f879be58/ijerph-18-04682-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/f6476491447c/ijerph-18-04682-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/2909856f874b/ijerph-18-04682-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/85f0f7f6132c/ijerph-18-04682-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/976082cbecd5/ijerph-18-04682-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/64cb41ff7257/ijerph-18-04682-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/9f8b2a7cbc5a/ijerph-18-04682-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/413d72acdd25/ijerph-18-04682-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/fc24/8124176/f570b6421494/ijerph-18-04682-g011.jpg

相似文献

1
Invasive Weed as a Potential Biomonitor and a Phytoremediator of Potentially Toxic Metals: A Case Study in Peninsular Malaysia.入侵杂草作为潜在毒性金属的生物监测和植物修复剂:马来西亚半岛的案例研究。
Int J Environ Res Public Health. 2021 Apr 28;18(9):4682. doi: 10.3390/ijerph18094682.
2
Potentially Toxic Metals in the High-Biomass Non-Hyperaccumulating Plant : Human Health Risks and Phytoremediation Potentials.高生物量非超积累植物中的潜在有毒金属:对人类健康的风险及植物修复潜力
Biology (Basel). 2022 Mar 1;11(3):389. doi: 10.3390/biology11030389.
3
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.
4
Monitoring the Efficiency of L. Plants in Phytoremediation of Heavy Metal-Contaminated Soil.监测李氏植物对重金属污染土壤进行植物修复的效率。
Plants (Basel). 2020 Aug 19;9(9):1057. doi: 10.3390/plants9091057.
5
[Spatial Variation of Heavy Metals in Soils and Its Ecological Risk Evaluation in a Typical Production Area].[典型产区土壤重金属空间变异及其生态风险评价]
Huan Jing Ke Xue. 2018 Jun 8;39(6):2893-2903. doi: 10.13227/j.hjkx.201707115.
6
Phytoremediation potential of Arundo donax (Giant Reed) in contaminated soil by heavy metals.芦竹(巨型芦苇)对重金属污染土壤的植物修复潜力。
Environ Res. 2020 Jun;185:109427. doi: 10.1016/j.envres.2020.109427. Epub 2020 Mar 22.
7
Risk Assessment and Source Identification of Toxic Metals in the Agricultural Soil around a Pb/Zn Mining and Smelting Area in Southwest China.中国西南某铅锌矿采冶区周边农田土壤中有毒金属的风险评估与来源识别。
Int J Environ Res Public Health. 2018 Aug 25;15(9):1838. doi: 10.3390/ijerph15091838.
8
Translocation of metal ions from soil to tobacco roots and their concentration in the plant parts.金属离子从土壤到烟草根系的转运及其在植物各部位的浓度。
Environ Monit Assess. 2016 Dec;188(12):663. doi: 10.1007/s10661-016-5679-3. Epub 2016 Nov 11.
9
Heavy metals in the soils and plants from a typical restored coal-mining area of Huainan coalfield, China.中国淮南煤田一个典型的恢复采煤区土壤和植物中的重金属。
Environ Monit Assess. 2017 Sep 3;189(10):484. doi: 10.1007/s10661-017-6207-9.
10
Heavy Metal Contamination and Accumulation in Soil and Plant from Mining Area of Mitrovica, Kosovo.米特罗维察矿区土壤和植物中的重金属污染与积累。
Bull Environ Contam Toxicol. 2021 Sep;107(3):537-543. doi: 10.1007/s00128-021-03223-6. Epub 2021 Apr 9.

本文引用的文献

1
Synergistic effects of EDDS and ALA on phytoextraction of cadmium as revealed by biochemical and ultrastructural changes in sunflower (Helianthus annuus L.) tissues.EDDS 和 ALA 对向日葵(Helianthus annuus L.)组织中镉的植物提取的协同作用:生化和超微结构变化的揭示。
J Hazard Mater. 2021 Apr 5;407:124764. doi: 10.1016/j.jhazmat.2020.124764. Epub 2020 Dec 8.
2
Cadmium phytoextraction by Helianthus annuus (sunflower), Brassica napus cv Wichita (rapeseed), and Chyrsopogon zizanioides (vetiver).超积累植物向日葵、油菜和香根草对镉的植物提取。
Chemosphere. 2021 Feb;265:129086. doi: 10.1016/j.chemosphere.2020.129086. Epub 2020 Nov 24.
3
Phytoextraction of cadmium-contaminated soil by Celosia argentea Linn.: A long-term field study.
紫葳属植物对镉污染土壤的植物萃取:一项长期田间研究。
Environ Pollut. 2020 Nov;266(Pt 1):115408. doi: 10.1016/j.envpol.2020.115408. Epub 2020 Aug 15.
4
Chemometric characterization of heavy metals in soils and shoots of the two pioneer species sampled near the polluted water bodies in the close vicinity of the copper mining and metallurgical complex in Bor (Serbia): Phytoextraction and biomonitoring contexts.土壤和两种先锋物种茎叶中重金属的化学计量特征研究,这些样本采集自塞尔维亚博尔(Bor)铜矿区及冶金厂附近受污染水体的近岸地区:植物萃取和生物监测背景。
Chemosphere. 2021 Jan;262:127808. doi: 10.1016/j.chemosphere.2020.127808. Epub 2020 Jul 27.
5
Comparative study on the bioaccumulation of lead, cadmium and nickel and their toxic effects on the growth and enzyme defence strategies of a heavy metal accumulator, Hydrilla verticillata (L.f.) Royle.重金属积累植物水鳖(Hydrilla verticillata(L.f.)Royle.)对铅、镉、镍的生物积累及其对生长和酶防御策略毒性效应的比较研究。
Environ Sci Pollut Res Int. 2020 Mar;27(9):9853-9865. doi: 10.1007/s11356-019-06968-0. Epub 2020 Jan 11.
6
The potential of elm trees (Ulmus glabra Huds.) for the phytostabilisation of potentially toxic elements in the riparian zone of the Sava River.河岸带中糙叶榆树(Ulmus glabra Huds.)对潜在有毒元素的植物稳定潜力。
Environ Sci Pollut Res Int. 2020 Feb;27(4):4309-4324. doi: 10.1007/s11356-019-07173-9. Epub 2019 Dec 12.
7
Phytoremediation: Environmentally sustainable way for reclamation of heavy metal polluted soils.植物修复:重金属污染土壤修复的环境可持续方法。
Ecotoxicol Environ Saf. 2019 Jun 15;174:714-727. doi: 10.1016/j.ecoenv.2019.02.068. Epub 2019 Mar 14.
8
Chromium bioaccumulation, oxidative stress metabolism and oil content in lemon grass Cymbopogon flexuosus (Nees ex Steud.) W. Watson grown in chromium rich over burden soil of Sukinda chromite mine, India.印度 Sukinda 铬铁矿富含铬的废石场上生长的柠檬草 Cymbopogon flexuosus(Nees ex Steud.)W. Watson 的铬生物积累、氧化应激代谢和油含量。
Chemosphere. 2019 Mar;218:1082-1088. doi: 10.1016/j.chemosphere.2018.11.211. Epub 2018 Nov 30.
9
Formation of iron plaque in the roots of Spartina alterniflora and its effect on the immobilization of wastewater-borne pollutants.在互花米草根部形成的铁斑及其对废水中污染物固定的影响。
Ecotoxicol Environ Saf. 2019 Jan 30;168:212-220. doi: 10.1016/j.ecoenv.2018.10.072. Epub 2018 Oct 30.
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.