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越南北方一个二级钢铁回收工艺村河流沉积物中二噁英和呋喃存在情况的综合评估。

A Comprehensive Evaluation of Dioxins and Furans Occurrence in River Sediments from a Secondary Steel Recycling Craft Village in Northern Vietnam.

作者信息

Nguyen Hung Xuan, Nguyen Xuyen Thi, Mai Hang Thi Hong, Nguyen Huong Thi, Vu Nam Duc, Pham Thao Thi Phuong, Nguyen Trung Quang, Nguyen Dat Tien, Duong Nam Thanh, Hoang Anh Le Tuan, Nguyen Tung Ngoc, Le Nhan Van, Dao Ha Viet, Ngoc Minh Truong, Bui Minh Quang

机构信息

Faculty of Chemistry, Graduate University of Science and Technology, Vietnam Academy of Science and Technology, 18 Hoang Quoc Viet Street, Cau Giay, Hanoi 11353, Vietnam.

Center for High Technology Research and Development, Vietnam Academy of Science and Technology, 18 Hoang Quoc Viet Street, Cau Giay, Hanoi 11353, Vietnam.

出版信息

Molecules. 2024 Apr 15;29(8):1788. doi: 10.3390/molecules29081788.

DOI:10.3390/molecules29081788
PMID:38675609
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11052440/
Abstract

This first study investigated the presence of dioxins and furans in river sediments around a craft village in Vietnam, focusing on Secondary Steel Recycling. Sediment samples were collected from various locations along the riverbed near the Da Hoi Secondary Steel Recycling village in Bac Ninh province. The analysis was conducted using a HRGC/HRMS-DFS device, detecting a total of 17 dioxin/furan isomers in all samples, with an average total concentration of 288.86 ng/kg d.w. The concentrations of dioxin/furan congeners showed minimal variation among sediment samples, ranging from 253.9 to 344.2 ng/kg d.w. The predominant compounds in the dioxin group were OCDD, while in the furan group, they were 1,2,3,4,6,7,8-HpCDF and OCDF. The chlorine content in the molecule appeared to be closely related to the concentration of dioxins and their percentage distribution. However, the levels of furan isomers did not vary significantly. The distribution of these compounds was not dependent on the flow direction, as they were mainly found in solid waste and are not water-soluble. Although the hepta and octa congeners had high concentrations, when converted to TEQ values, the tetra and penta groups (for dioxins) and the penta and hexa groups (for furans) contributed more to toxicity. Furthermore, the source of dioxins in sediments at Da Hoi does not only originate from steel recycling production activities but also from other combustion sites. The average total toxicity was 10.92 ng TEQ/kg d.w, ranging from 4.99 to 17.88 ng TEQ/kg d.w, which did not exceed the threshold specified in QCVN 43:2017/BTNMT, the National Technical Regulation on Sediment Quality. Nonetheless, these levels are still concerning. The presence of these toxic substances not only impacts aquatic organisms in the sampled water environment but also poses potential health risks to residents living nearby.

摘要

第一项研究调查了越南一个手工艺村周围河流沉积物中二噁英和呋喃的存在情况,重点关注二级钢铁回收。沉积物样本是从北宁省大回二级钢铁回收村附近河床的不同位置采集的。使用高分辨率气相色谱/高分辨率质谱-双聚焦扇形磁场质谱仪进行分析,在所有样本中共检测到17种二噁英/呋喃异构体,平均总浓度为288.86纳克/千克干重。二噁英/呋喃同系物的浓度在沉积物样本中变化极小,范围为253.9至344.2纳克/千克干重。二噁英组中的主要化合物是八氯二苯并二噁英,而呋喃组中的主要化合物是1,2,3,4,6,7,8-七氯代二苯并呋喃和八氯代二苯并呋喃。分子中的氯含量似乎与二噁英的浓度及其百分比分布密切相关。然而,呋喃异构体的含量变化不显著。这些化合物的分布不依赖于水流方向,因为它们主要存在于固体废物中,且不溶于水。尽管七氯和八氯同系物浓度较高,但换算成毒性当量值时,四氯和五氯组(对于二噁英)以及五氯和六氯组(对于呋喃)对毒性的贡献更大。此外,大回沉积物中的二噁英来源不仅源于钢铁回收生产活动,还来自其他燃烧场所。平均总毒性为10.92纳克毒性当量/千克干重,范围为4.99至17.88纳克毒性当量/千克干重,未超过越南国家沉积物质量技术法规QCVN 43:2017/BTNMT规定的阈值。尽管如此,这些水平仍令人担忧。这些有毒物质的存在不仅影响采样水环境中的水生生物,还对附近居民构成潜在的健康风险。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/bf6b6b3bb84f/molecules-29-01788-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/34d9e57a46e4/molecules-29-01788-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/ba2d1d88631a/molecules-29-01788-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/bfb4a28f2935/molecules-29-01788-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/a573c8525539/molecules-29-01788-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/30a34ada04bb/molecules-29-01788-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/391cf5c5d343/molecules-29-01788-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/e2a3d4329ad8/molecules-29-01788-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/bf6b6b3bb84f/molecules-29-01788-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/34d9e57a46e4/molecules-29-01788-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/ba2d1d88631a/molecules-29-01788-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/bfb4a28f2935/molecules-29-01788-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/a573c8525539/molecules-29-01788-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/30a34ada04bb/molecules-29-01788-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/391cf5c5d343/molecules-29-01788-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/e2a3d4329ad8/molecules-29-01788-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4e49/11052440/bf6b6b3bb84f/molecules-29-01788-g008.jpg

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