• 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

植物可给性和植物多样性共同决定了重金属从土壤中的生物累积风险,本研究以中国珠江三角洲地区受镉污染的蔬菜农场为例展开。

Phytoavailability and phytovariety codetermine the bioaccumulation risk of heavy metal from soils, focusing on Cd-contaminated vegetable farms around the Pearl River Delta, China.

机构信息

Croucher Institute for Environmental Sciences, and Department of Biology, Hong Kong Baptist University, Kowloon Tong, Hong Kong SAR, PR China.

出版信息

Ecotoxicol Environ Saf. 2013 May;91:18-24. doi: 10.1016/j.ecoenv.2013.01.001. Epub 2013 Feb 9.

DOI:10.1016/j.ecoenv.2013.01.001
PMID:23399100
Abstract

Five random vegetable farms were selected to investigate the bioaccumulation risk of heavy metals (HMs) by different type of vegetables around the Pearl River Delta (PRD), China. The concentration order of four major HMs in the surface soil samples was Cd<Cu<Pb<Zn, with only Cd concentrations (1.4-1.8mgkg(-1)) significantly higher than the permissible limit (≤0.3mgkg(-1)) for agricultural soils. Soil DTPA-extractable (phytoavailable) Cd concentrations differed markedly amongst the five farms, and varied within 0.017-0.17mgkg(-1). Meanwhile, 28.0% of vegetable samples collected from these five farms were contaminated with Cd according to the permissible limit (≤0.05mgkg(-1)), and 71.4% of these polluted samples belonged to stem/leaf vegetables. The average bioaccumulation factors of Cd from cultivated soil to stem/leaf vegetables and melon/fruit/bean vegetables varied within 0.021-0.050 and 0.005-0.020 (soil total Cd basis), and 0.50-2.01 and 0.13-0.53 (soil DTPA-extractable Cd basis), respectively. Redundancy analysis (RDA) showed that DTPA-extractable Cd, which negatively but significantly correlated (P<0.05) to soil pH, was the key factor in influencing vegetable Cd accumulation, notably stem/leaf vegetables. The results show that Cd was the primary metal of risk in vegetable farms around the PRD region, and stem/leaf vegetables posed about 2.2 times higher health risks associated with exposure to Cd than melon/fruit/bean vegetables.

摘要

随机选取了珠三角地区的 5 个蔬菜农场,调查了不同类型蔬菜对重金属(HM)的生物蓄积风险。表层土壤样品中四种主要 HM 的浓度顺序为 Cd<Cu<Pb<Zn,只有 Cd 浓度(1.4-1.8mgkg(-1)))明显高于农业土壤的允许限值(≤0.3mgkg(-1))。五个农场之间的土壤 DTPA 可提取(植物可利用)Cd 浓度差异显著,范围在 0.017-0.17mgkg(-1)之间。同时,根据允许限值(≤0.05mgkg(-1)),从这五个农场采集的 28.0%的蔬菜样本受到 Cd 污染,其中 71.4%的污染样本属于茎/叶类蔬菜。从耕作土壤到茎/叶类蔬菜和瓜果/豆类蔬菜的 Cd 平均生物积累因子在 0.021-0.050 和 0.005-0.020(土壤总 Cd 基准)之间,而在 0.50-2.01 和 0.13-0.53(土壤 DTPA 可提取 Cd 基准)之间,分别。冗余分析(RDA)表明,与土壤 pH 呈负相关(P<0.05)但显著相关的 DTPA 可提取 Cd 是影响蔬菜 Cd 积累的关键因素,特别是茎/叶类蔬菜。结果表明,Cd 是珠三角地区蔬菜农场的主要风险金属,与瓜果/豆类蔬菜相比,茎/叶类蔬菜因接触 Cd 而产生的健康风险高约 2.2 倍。

相似文献

1
Phytoavailability and phytovariety codetermine the bioaccumulation risk of heavy metal from soils, focusing on Cd-contaminated vegetable farms around the Pearl River Delta, China.植物可给性和植物多样性共同决定了重金属从土壤中的生物累积风险,本研究以中国珠江三角洲地区受镉污染的蔬菜农场为例展开。
Ecotoxicol Environ Saf. 2013 May;91:18-24. doi: 10.1016/j.ecoenv.2013.01.001. Epub 2013 Feb 9.
2
The accumulation and health risk of heavy metals in vegetables around a zinc smelter in northeastern China.中国东北某锌冶炼厂周边蔬菜中重金属的积累及健康风险
Environ Sci Pollut Res Int. 2016 Dec;23(24):25114-25126. doi: 10.1007/s11356-016-7342-5. Epub 2016 Sep 28.
3
Heavy metals and lead isotopes in soils, road dust and leafy vegetables and health risks via vegetable consumption in the industrial areas of Shanghai, China.中国上海工业区土壤、道路灰尘和叶类蔬菜中的重金属和铅同位素,以及通过食用蔬菜带来的健康风险。
Sci Total Environ. 2018 Apr 1;619-620:1349-1357. doi: 10.1016/j.scitotenv.2017.11.177. Epub 2017 Nov 23.
4
Heavy metal accumulation in balsam pear and cowpea related to the geochemical factors of variable-charge soils in the Pearl River Delta, South China.重金属在苦瓜和豇豆中的积累与珠江三角洲可变电荷土壤的地球化学因素有关。
Environ Sci Process Impacts. 2014 Jul;16(7):1790-8. doi: 10.1039/c3em00637a.
5
Assessment of trace metal bioavailability in garden soils and health risks via consumption of vegetables in the vicinity of Tongling mining area, China.中国铜陵矿区附近蔬菜中痕量金属生物可给性评估及健康风险。
Ecotoxicol Environ Saf. 2013 Apr;90:103-11. doi: 10.1016/j.ecoenv.2012.12.018. Epub 2013 Jan 17.
6
Health risk from heavy metals via consumption of food crops in the vicinity of Dabaoshan mine, South China.中国南方大宝山矿附近通过食用粮食作物产生的重金属健康风险。
Sci Total Environ. 2009 Feb 15;407(5):1551-61. doi: 10.1016/j.scitotenv.2008.10.061. Epub 2008 Dec 9.
7
Accumulation of heavy metals in leaf vegetables from agricultural soils and associated potential health risks in the Pearl River Delta, South China.叶菜类蔬菜中重金属的积累及其在珠江三角洲地区的潜在健康风险。
Environ Monit Assess. 2014 Mar;186(3):1547-60. doi: 10.1007/s10661-013-3472-0. Epub 2013 Nov 3.
8
Toxicological assessment of heavy metals accumulated in vegetables and fruits grown in Ginfel river near Sheba Tannery, Tigray, Northern Ethiopia.在埃塞俄比亚提格雷地区的 Sheba 皮革厂附近的 Ginfel 河种植的蔬菜和水果中积累的重金属的毒理学评估。
Ecotoxicol Environ Saf. 2013 Sep;95:171-8. doi: 10.1016/j.ecoenv.2013.05.035. Epub 2013 Jun 20.
9
The impact of greenhouse vegetable farming duration and soil types on phytoavailability of heavy metals and their health risk in eastern China.温室蔬菜种植年限和土壤类型对中国东部重金属植物可给性及其健康风险的影响。
Chemosphere. 2014 May;103:121-30. doi: 10.1016/j.chemosphere.2013.11.047. Epub 2013 Dec 11.
10
Source identification and exchangeability of heavy metals accumulated in vegetable soils in the coastal plain of eastern Zhejiang province, China.中国浙江东部沿海平原蔬菜土壤中重金属的来源识别与可交换性
Ecotoxicol Environ Saf. 2017 Aug;142:410-416. doi: 10.1016/j.ecoenv.2017.03.035. Epub 2017 Apr 28.

引用本文的文献

1
Fertilizers and Human Health-A Systematic Review of the Epidemiological Evidence.肥料与人类健康——流行病学证据的系统综述
Toxics. 2024 Sep 26;12(10):694. doi: 10.3390/toxics12100694.
2
Comparing the Effects of Lime Soil and Yellow Soil on Cadmium Accumulation in Rice during Grain-Filling and Maturation Periods.比较石灰土和黄壤对水稻灌浆成熟期镉积累的影响。
Plants (Basel). 2024 Jul 23;13(15):2018. doi: 10.3390/plants13152018.
3
Differences in the response mechanism of cadmium uptake, transfer, and accumulation of different rice varieties after foliar silicon spraying under cadmium-stressed soil.
镉胁迫土壤下叶面喷施硅后不同水稻品种镉吸收、转运及积累响应机制的差异
Front Plant Sci. 2023 Jan 10;13:1064359. doi: 10.3389/fpls.2022.1064359. eCollection 2022.
4
Geochemical Baseline Establishment and Source-Oriented Ecological Risk Assessment of Heavy Metals in Lime Concretion Black Soil from a Typical Agricultural Area.典型农业区石灰结核黑土重金属的地球化学基准值建立及来源导向生态风险评估
Int J Environ Res Public Health. 2021 Jun 26;18(13):6859. doi: 10.3390/ijerph18136859.
5
The compound effects of biochar and iron on watercress in a Cd/Pb-contaminated soil.生物炭和铁对 Cd/Pb 污染土壤中豆瓣菜的复合效应。
Environ Sci Pollut Res Int. 2020 Feb;27(6):6312-6325. doi: 10.1007/s11356-019-07353-7. Epub 2019 Dec 21.
6
The impact of fertilizers on the uptake of manganese in Cherry Belle radish plants: implications for human health.肥料对樱桃萝卜植物锰吸收的影响:对人类健康的影响。
Environ Sci Pollut Res Int. 2019 Apr;26(10):10414-10428. doi: 10.1007/s11356-019-04574-8. Epub 2019 Feb 27.
7
Soil amendments for cadmium phytostabilization by five marigold cultivars.五种万寿菊品种对镉的植物稳定作用的土壤改良。
Environ Sci Pollut Res Int. 2019 Mar;26(9):8737-8747. doi: 10.1007/s11356-019-04233-y. Epub 2019 Feb 2.
8
Bioavailability evaluation, uptake of heavy metals and potential health risks via dietary exposure in urban-industrial areas.城市工业区通过饮食摄入的重金属的生物利用度评估、吸收和潜在健康风险。
Environ Sci Pollut Res Int. 2016 Nov;23(22):22443-22453. doi: 10.1007/s11356-016-7449-8. Epub 2016 Aug 22.
9
Transfer of cadmium from soil to vegetable in the Pearl River Delta area, South China.中国南方珠江三角洲地区土壤中镉向蔬菜的转移
PLoS One. 2014 Sep 23;9(9):e108572. doi: 10.1371/journal.pone.0108572. eCollection 2014.
10
Biochar and Glomus caledonium influence Cd accumulation of upland kangkong (Ipomoea aquatica Forsk.) intercropped with Alfred stonecrop (Sedum alfredii Hance).生物炭和喀里多尼亚球囊霉对与东南景天间作的蕹菜镉积累的影响。
Sci Rep. 2014 Apr 14;4:4671. doi: 10.1038/srep04671.