• 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

芬兰鱼鹰蛋中持久性卤代芳烃的时间趋势(1972-2017 年)和空间差异。

Temporal trends (1972-2017) and spatial differences of persistent halogenated aromatic hydrocarbons in osprey eggs in Finland.

机构信息

Finnish Institute for Health and Welfare, Environmental Health Unit, Kuopio, Finland.

School of Pharmacy (Toxicology) and Department of Environmental and Biological Sciences, University of Eastern Finland, Kuopio, Finland.

出版信息

PLoS One. 2024 Sep 3;19(9):e0308227. doi: 10.1371/journal.pone.0308227. eCollection 2024.

DOI:10.1371/journal.pone.0308227
PMID:39226334
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11371234/
Abstract

Time trends and regional differences of polychlorinated dibenzo-p-dioxins and -furans (PCDD/Fs), polychlorinated biphenyls (PCBs), polychlorinated naphthalenes (PCNs), DDTs, polybrominated biphenyls (PBBs) and polybrominated diphenylethers (BDEs) were studied in unhatched osprey eggs collected by bird ringers in 1972-2017 from four areas in Finland. Two study areas were from Baltic Sea, Northern Quark and Finnish Archipelago Sea, while the two others were inland lake areas, eutrophicated Lake Vanajanselkä affected by industrial emissions, and Pristine SW Lake Area. The highest concentrations of most compound groups were in Lake Vanajanselkä consistent with high emissions, the predominance of bream as a prey, and higher concentrations in bream compared to other prey fish. Concentrations of all chlorinated compounds decreased significantly in all study areas. Average annual decreases were ∑PCDD/F 2.3-4.9%, ∑PCB 2.2-4.2%, ∑PCN 2.6-7.0% and ∑DDT 7.1-9.5%, primarily in line with decreased levels in prey fish. From 1972 PBBs and BDEs increased significantly until 1990s declining rapidly thereafter. PCDD/F congener profile was dominated by 2,3,4,7,8-PeCDF, except in Lake Vanajanselkä by 1,2,3,6,7,8-HxCDD. PCB congener profile was dominated by PCB 153 in all study areas, followed by PCB 180 and PCB 138. Among dioxin-like compounds PCBs contributed 82%, PCDDs 14% and PCDFs 4% to toxic equivalent quantity (∑TEQ). PCB 126 contributed most to ∑TEQ, followed by 1,2,3,7,8-PeCDD. BDE 47 being the dominant BDE congener, followed by BDE 100. ∑DDT concentrations were relatively similar across all study areas, with DDE contributing about 90%. Productivity of chicks per active nest was significantly decreased in Lake Vanajanselkä, and the likely explanation is embryotoxicity of dioxin-like compounds. It is plausible that dioxin-like compounds influenced embryonic survival among highly exposed ospreys prior to 2010, especially in Lake Vanajanselkä and Northern Quark. However, decreased survival due to DDE-induced eggshell thinning seems unlikely after 1985, and BDE levels were below those potentially causing adverse effects.

摘要

1972 年至 2017 年间,鸟类环志者在芬兰的四个地区收集了未孵化的鱼鹰卵,研究了多氯二苯并对二恶英和呋喃(PCDD/Fs)、多氯联苯(PCBs)、多氯萘(PCNs)、滴滴涕、多溴联苯(PBBs)和多溴联苯醚(BDEs)的时间趋势和区域差异。两个研究区域位于波罗的海、北夸克和芬兰群岛海,而另外两个是内陆湖泊地区,富营养化的瓦纳扬塞勒卡湖受工业排放影响,以及原始的西南湖地区。与高排放量一致,最高浓度的大多数化合物组都在瓦纳扬塞勒卡湖中,主要是鲤鱼作为猎物,与其他猎物鱼相比,鲤鱼中的浓度更高。所有氯化化合物的浓度在所有研究区域均显著下降。∑PCDD/F 的年均降幅为 2.3-4.9%,∑PCB 为 2.2-4.2%,∑PCN 为 2.6-7.0%,∑DDT 为 7.1-9.5%,主要与猎物鱼中的水平下降一致。自 1972 年以来,PBBs 和 BDEs 显著增加,直到 20 世纪 90 年代才迅速下降。PCDD/F 同系物的特征是 2,3,4,7,8-PeCDF 占主导地位,除了瓦纳扬塞勒卡湖是 1,2,3,6,7,8-HxCDD 占主导地位。所有研究区域中,PCB 同系物的特征均以 PCB 153 为主,其次是 PCB 180 和 PCB 138。在二恶英类化合物中,PCBs 占毒性当量(∑TEQ)的 82%,PCDDs 占 14%,PCDFs 占 4%。PCB 126 对∑TEQ 的贡献最大,其次是 1,2,3,7,8-PeCDD。BDE 47 是最主要的 BDE 同系物,其次是 BDE 100。∑DDT 浓度在所有研究区域都相对相似,其中 DDE 占约 90%。在瓦纳扬塞勒卡湖中,每窝活跃巢穴的雏鸟生产力明显下降,可能的解释是二恶英类化合物的胚胎毒性。在 2010 年之前,高度暴露的鱼鹰中,二恶英类化合物可能影响了胚胎的存活率,尤其是在瓦纳扬塞勒卡湖和北夸克。然而,自 1985 年以来,由于滴滴涕诱导的蛋壳变薄导致的存活率下降似乎不太可能,而且 BDE 水平低于可能产生不利影响的水平。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/4b04ce445ee5/pone.0308227.g017.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/117944833eab/pone.0308227.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/683bffb1c20a/pone.0308227.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/7d9a0377dd9f/pone.0308227.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/9b63a06d02c8/pone.0308227.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/a7c206162e4b/pone.0308227.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/8f2c68a02de8/pone.0308227.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/22a26a6fce93/pone.0308227.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/31fd8864f563/pone.0308227.g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/59bdd8ce23cb/pone.0308227.g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/8971bc1b1ee2/pone.0308227.g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/88e7f4c74cf3/pone.0308227.g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/9f345c37f9d2/pone.0308227.g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/142eda0ccd99/pone.0308227.g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/184cae7d50df/pone.0308227.g014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/f6ee6916c612/pone.0308227.g015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/9df3faf06190/pone.0308227.g016.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/4b04ce445ee5/pone.0308227.g017.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/117944833eab/pone.0308227.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/683bffb1c20a/pone.0308227.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/7d9a0377dd9f/pone.0308227.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/9b63a06d02c8/pone.0308227.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/a7c206162e4b/pone.0308227.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/8f2c68a02de8/pone.0308227.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/22a26a6fce93/pone.0308227.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/31fd8864f563/pone.0308227.g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/59bdd8ce23cb/pone.0308227.g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/8971bc1b1ee2/pone.0308227.g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/88e7f4c74cf3/pone.0308227.g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/9f345c37f9d2/pone.0308227.g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/142eda0ccd99/pone.0308227.g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/184cae7d50df/pone.0308227.g014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/f6ee6916c612/pone.0308227.g015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/9df3faf06190/pone.0308227.g016.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/12b4/11371234/4b04ce445ee5/pone.0308227.g017.jpg

相似文献

1
Temporal trends (1972-2017) and spatial differences of persistent halogenated aromatic hydrocarbons in osprey eggs in Finland.芬兰鱼鹰蛋中持久性卤代芳烃的时间趋势(1972-2017 年)和空间差异。
PLoS One. 2024 Sep 3;19(9):e0308227. doi: 10.1371/journal.pone.0308227. eCollection 2024.
2
Occurrence of PCDD/PCDFs, dioxin-like PCBs, and PBDEs in surface sediments from the Neva River and the Eastern Gulf of Finland (Russia).涅瓦河和芬兰湾东部(俄罗斯)表层沉积物中 PCDD/PCDFs、类二恶英多氯联苯和 PBDEs 的出现情况。
Environ Sci Pollut Res Int. 2019 Mar;26(8):7375-7389. doi: 10.1007/s11356-018-1945-y. Epub 2018 May 28.
3
PCDD/Fs, PCBs and PBDEs in zooplankton in the Baltic Sea - spatial and temporal shifts in the congener-specific concentrations.波罗的海浮游动物中的多氯二苯并对二噁英/多氯二苯并呋喃、多氯联苯和多溴二苯醚——同族体特定浓度的时空变化
Chemosphere. 2014 Nov;114:172-80. doi: 10.1016/j.chemosphere.2014.04.026. Epub 2014 May 14.
4
Temporal trends of PBDD/Fs, PCDD/Fs, PBDEs and PCBs in ringed seals from the Baltic Sea (Pusa hispida botnica) between 1974 and 2015.1974 年至 2015 年间波罗的海(环斑海豹)中 PBDD/Fs、PCDD/Fs、PBDEs 和 PCBs 的时间趋势。
Sci Total Environ. 2018 Mar;616-617:1374-1383. doi: 10.1016/j.scitotenv.2017.10.178. Epub 2017 Oct 21.
5
PCDDs, PCDFs, PCBs, OC pesticides and mercury in fish and osprey eggs from Willamette River, Oregon (1993, 2001 and 2006) with calculated biomagnification factors.俄勒冈州威拉米特河鱼类和鹗蛋中的多氯二苯并对二噁英、多氯二苯并呋喃、多氯联苯、有机氯农药及汞(1993年、2001年和2006年)以及计算得出的生物放大因子。
Ecotoxicology. 2009 Feb;18(2):151-73. doi: 10.1007/s10646-008-0268-z. Epub 2008 Oct 2.
6
Distribution, seasonal variation and inhalation risks of polychlorinated dibenzo-p-dioxins and dibenzofurans, polychlorinated biphenyls and polybrominated diphenyl ethers in the atmosphere of Beijing, China.中国北京大气中多氯二苯并对二恶英和二苯并呋喃、多氯联苯和多溴二苯醚的分布、季节变化及吸入风险。
Environ Geochem Health. 2018 Oct;40(5):1907-1918. doi: 10.1007/s10653-017-9961-2. Epub 2017 Apr 26.
7
Polychlorinated dibenzo-p-dioxins/furans (PCDD/Fs), polychlorinated biphenyls (PCBs), and polybrominated diphenyl ethers (PBDEs) in breast milk from Zhejiang, China.中国浙江母乳中的多氯二苯并对二恶英/呋喃(PCDD/Fs)、多氯联苯(PCBs)和多溴二苯醚(PBDEs)。
Environ Int. 2012 Jul;42:84-90. doi: 10.1016/j.envint.2011.04.004. Epub 2011 May 14.
8
Comparison of organohalogen compounds in a white-tailed sea eagle egg laid in 1941 with five eggs from 1996 to 2001.比较 1941 年一只白头海雕产下的一枚卵与 1996 年至 2001 年的五枚卵中的有机卤化物化合物。
Chemosphere. 2012 Jul;88(3):286-91. doi: 10.1016/j.chemosphere.2012.02.039. Epub 2012 Mar 6.
9
Polychlorinated dibenzo-p-dioxins, dibenzofurans, biphenyls, naphthalenes and polybrominated diphenyl ethers in the edible fish caught from the Baltic Sea and lakes in Finland.从芬兰波罗的海和湖泊捕获的食用鱼中的多氯二苯并对二恶英、二苯并呋喃、联苯、萘和多溴二苯醚。
Environ Pollut. 2006 May;141(2):213-25. doi: 10.1016/j.envpol.2005.08.055. Epub 2005 Oct 13.
10
Halogenated organic compounds in the eggs of aquatic birds from the Gulf of Gdansk and Wloclawek Dam (Poland).卤代有机化合物在波兰格但斯克湾和弗罗茨瓦夫大坝(波兰)水鸟蛋中的分布情况。
Chemosphere. 2019 Dec;237:124463. doi: 10.1016/j.chemosphere.2019.124463. Epub 2019 Jul 26.

本文引用的文献

1
The toxicological profile of polychlorinated naphthalenes (PCNs).多氯萘的毒理学特征。
Sci Total Environ. 2022 Sep 1;837:155764. doi: 10.1016/j.scitotenv.2022.155764. Epub 2022 May 8.
2
A time-trend guided non-target screening study of organic contaminants in Baltic Sea harbor porpoise (1988-2019), guillemot (1986-2019), and white-tailed sea eagle (1965-2017) using gas chromatography-high-resolution mass spectrometry.使用气相色谱-高分辨质谱法对波罗的海港湾鼠海豚(1988-2019 年)、海雀(1986-2019 年)和白尾海雕(1965-2017 年)进行的时间趋势引导的非靶向筛选研究。
Sci Total Environ. 2022 Jul 10;829:154620. doi: 10.1016/j.scitotenv.2022.154620. Epub 2022 Mar 17.
3
Endocrine, metabolic and apical effects of in utero and lactational exposure to non-dioxin-like 2,2',3,4,4',5,5'-heptachlorobiphenyl (PCB 180): A postnatal follow-up study in rats.
宫内和哺乳期暴露于非二恶英样 2,2',3,4,4',5,5'-七氯联苯(PCB 180)对内分泌、代谢和顶端的影响:大鼠的一项产后随访研究。
Reprod Toxicol. 2021 Jun;102:109-127. doi: 10.1016/j.reprotox.2021.04.004. Epub 2021 May 13.
4
Sources of polychlorinated dibenzo-p-dioxins and dibenzofurans to Baltic Sea herring.波罗的海鲱鱼中多氯二苯并对二恶英和多氯二苯并呋喃的来源。
Chemosphere. 2019 Mar;218:493-500. doi: 10.1016/j.chemosphere.2018.11.051. Epub 2018 Nov 19.
5
Perfluoroalkyl substances (PFASs) and polychlorinated naphthalenes (PCNs) add to the chemical cocktail in peregrine falcon eggs.全氟烷基物质(PFASs)和多氯萘(PCNs)增加了游隼蛋中的化学鸡尾酒。
Sci Total Environ. 2019 Jan 15;648:894-901. doi: 10.1016/j.scitotenv.2018.08.090. Epub 2018 Aug 7.
6
Polychlorinated Biphenyls and Polybrominated Biphenyls.多氯联苯和多溴联苯
IARC Monogr Eval Carcinog Risks Hum. 2016;107:9-500.
7
Brominated flame retardants (BFRs) in eggs from birds of prey from Southern Germany, 2014.2014 年德国南部猛禽蛋中的溴化阻燃剂(BFRs)。
Environ Pollut. 2017 Dec;231(Pt 1):569-577. doi: 10.1016/j.envpol.2017.08.047. Epub 2017 Aug 29.
8
Polychlorinated naphthalenes (PCNs) in food and humans.食品和人体内的多氯萘(PCNs)。
Environ Int. 2017 Jul;104:1-13. doi: 10.1016/j.envint.2017.02.015. Epub 2017 Apr 7.
9
Declining Trends of Polychlorinated Naphthalenes in Seabird Eggs from the Canadian Arctic, 1975-2014.1975-2014 年加拿大北极海鸟蛋中多氯萘的下降趋势。
Environ Sci Technol. 2017 Apr 4;51(7):3802-3808. doi: 10.1021/acs.est.7b00431. Epub 2017 Mar 23.
10
Declining trends of polychlorinated dibenzo-p-dioxins, dibenzofurans and non-ortho PCBs in Canadian Arctic seabirds.加拿大北极海鸟体内多氯二苯并对二噁英、二苯并呋喃和非邻位多氯联苯的下降趋势。
Environ Pollut. 2017 Jan;220(Pt A):557-566. doi: 10.1016/j.envpol.2016.10.003. Epub 2016 Oct 11.