• 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

Immunosuppressive activity of polychlorinated biphenyl mixtures and congeners: nonadditive (antagonistic) interactions.

作者信息

Harper N, Connor K, Steinberg M, Safe S

机构信息

Texas A & M University, College Station 77843-4466, USA.

出版信息

Fundam Appl Toxicol. 1995 Aug;27(1):131-9. doi: 10.1006/faat.1995.1116.

DOI:10.1006/faat.1995.1116
PMID:7589923
Abstract

The dose-response inhibition of the splenic plaque-forming cell (PFC) response and serum IgM units to the antigen, trinitrophenyl-lipopolysaccharide, was determined for several polychlorinated biphenyl (PCB) mixtures and congeners in female B3C3F1 mice. The ED50 values for Aroclor 1260-, 1254-, 1248-, and 1242-induced immunotoxicity varied by less than twofold from 355 to 699 mg/kg. The range of ED50 values for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 3,3',4,4'-tetrachlorobiphenyl, 3,3',4,4',5-pentaCB, 3,3',4,4',5,5'-hexaCB, 2,3,3',4,4'-pentaCB, 2,3',4,4',5-pentaCB, 2,3,3',4,4',5-hexaCB, 2,3,3',4,4',5,5'-heptaCB, 2,2',3,3',4,4',5-heptaCB, and 2,2',3,4,4',5,5'-heptaCB were 4.6 to 4.9, 134 to 245, 4.7 to 7.0, 6.9 to 11.1, 88,000 to 121,000, 122,000 to 132,000, 99,000 to 157,000, 89,000 to 129,000, 117,000 to 240,000, and 132,000 to 238,000 micrograms/kg, respectively. The immunotoxicity-derived toxic equivalency factors (TEFs) for these congeners could be calculated from the ED50 (TCDD)/ED50 (congener) ratios and the TEF values were within the range of those previously determined for other aryl hydrocarbon receptor-mediated responses. Based on the known concentrations of these congeners in the PCB mixtures, TCDD or toxic equivalents (TEQs) in the mixture were calculated [i.e., TEQ = sigma (PCBcongener x TEF)] using the immunotoxicity-derived TEFs (plaque-forming cells/10(6) viable cells). TEQ values for Aroclors 1260, 1254, 1248, and 1242 were 16.0, 54.4, 260.4, and 197 ppm, respectively. Based on the ED50 value for the immunosuppressive activity of TCDD (4.8 micrograms/kg), the calculated ED50 values for immune suppression by Aroclors 1260, 1254, 1248, and 1242 were 300, 88, 18, and 24 mg/kg, respectively. The ED50 (observed)/ED50 (calculated) ratios were 1.2, 5.9, 21, and 22.0 for Aroclors 1260, 1254, 1248 and 1242, respectively.(ABSTRACT TRUNCATED AT 250 WORDS)

摘要

相似文献

1
Immunosuppressive activity of polychlorinated biphenyl mixtures and congeners: nonadditive (antagonistic) interactions.
Fundam Appl Toxicol. 1995 Aug;27(1):131-9. doi: 10.1006/faat.1995.1116.
2
Polychlorinated biphenyls (PCBs): environmental impact, biochemical and toxic responses, and implications for risk assessment.多氯联苯(PCBs):环境影响、生化与毒性反应及风险评估的意义
Crit Rev Toxicol. 1994;24(2):87-149. doi: 10.3109/10408449409049308.
3
Immunotoxic potencies of polychlorinated biphenyl (PCB), dibenzofuran (PCDF) and dibenzo-p-dioxin (PCDD) congeners in C57BL/6 and DBA/2 mice.
Toxicology. 1993 Jun 11;80(2-3):217-27. doi: 10.1016/0300-483x(93)90183-s.
4
Teratogenicity and immunotoxicity of 3,3',4,4',5-pentachlorobiphenyl in C57BL/6 mice.
Toxicology. 1993 Jan 29;77(1-2):123-31. doi: 10.1016/0300-483x(93)90143-g.
5
Comparative potencies of Aroclors 1232, 1242, 1248, 1254, and 1260 in male Wistar rats--assessment of the toxic equivalency factor (TEF) approach for polychlorinated biphenyls (PCBs).
Fundam Appl Toxicol. 1993 May;20(4):456-63. doi: 10.1006/faat.1993.1056.
6
Toxicology and carcinogenesis studies of a mixture of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (Cas No. 1746-01-6), 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) (Cas No. 57117-31-4), and 3,3',4,4',5-pentachlorobiphenyl (PCB 126) (Cas No. 57465-28-8) in female Harlan Sprague-Dawley rats (gavage studies).2,3,7,8-四氯二苯并-对-二噁英(TCDD)(化学物质登记号1746-01-6)、2,3,4,7,8-五氯二苯并呋喃(PeCDF)(化学物质登记号57117-31-4)和3,3',4,4',5-五氯联苯(多氯联苯126)(化学物质登记号57465-28-8)混合物对雌性Harlan Sprague-Dawley大鼠的毒理学和致癌性研究(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 Sep(526):1-180.
7
Structure-dependent induction of CYP2B by polychlorinated biphenyl congeners in female Sprague-Dawley rats.多氯联苯同系物对雌性斯普拉格-道利大鼠CYP2B的结构依赖性诱导作用。
Biochem Pharmacol. 1995 Nov 27;50(11):1913-20. doi: 10.1016/0006-2952(95)02087-x.
8
Toxicology and carcinogenesis studies of a binary mixture of 3,3',4,4',5-pentachlorobiphenyl (PCB 126) (Cas No. 57465-28-8) and 2,3',4,4',5-pentachlorobiphenyl (PCB 118) (Cas No. 31508-00-6) in female Harlan Sprague-Dawley rats (gavage studies).3,3',4,4',5-五氯联苯(PCB 126)(化学物质登记号:57465-28-8)与2,3',4,4',5-五氯联苯(PCB 118)(化学物质登记号:31508-00-6)二元混合物对雌性哈兰·斯普拉格-道利大鼠的毒理学和致癌性研究(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 Nov(531):1-218.
9
Inhibition of 3,3',4,4',5-pentachlorobiphenyl-induced fetal cleft palate and immunotoxicity in C57BL/6 mice by 2,2',4,4',5,5'-hexachlorobiphenyl.2,2',4,4',5,5'-六氯联苯对3,3',4,4',5-五氯联苯诱导的C57BL/6小鼠胎儿腭裂和免疫毒性的抑制作用
Chemosphere. 1997 Mar-Apr;34(5-7):1605-13. doi: 10.1016/s0045-6535(97)00456-6.
10
Dose-response immunotoxicities of commercial polychlorinated biphenyls (PCBs) and their interaction with 2,3,7,8-tetrachlorodibenzo-p-dioxin.
Toxicol Lett. 1989 Jul;48(1):35-43. doi: 10.1016/0378-4274(89)90183-5.

引用本文的文献

1
The role of epidemiology studies in human health risk assessment of polychlorinated biphenyls.流行病学研究在多氯联苯的人类健康风险评估中的作用。
Environ Res. 2021 Mar;194:110662. doi: 10.1016/j.envres.2020.110662. Epub 2020 Dec 30.
2
Exercise influences the impact of polychlorinated biphenyl exposure on immune function.运动影响多氯联苯暴露对免疫功能的影响。
PLoS One. 2020 Aug 24;15(8):e0237705. doi: 10.1371/journal.pone.0237705. eCollection 2020.
3
Identification of Sex-Specific Transcriptome Responses to Polychlorinated Biphenyls (PCBs).
鉴定多氯联苯(PCBs)对性别特异性转录组的响应。
Sci Rep. 2019 Jan 24;9(1):746. doi: 10.1038/s41598-018-37449-y.
4
Potential effects of polychlorinated biphenyls (PCBs) and selected organochlorine pesticides (OCPs) on immune cells and blood biochemistry measures: a cross-sectional assessment of the NHANES 2003-2004 data.多氯联苯(PCBs)和特定有机氯农药(OCPs)对免疫细胞及血液生化指标的潜在影响:基于2003 - 2004年美国国家健康与营养检查调查(NHANES)数据的横断面评估
Environ Health. 2014 Dec 16;13:114. doi: 10.1186/1476-069X-13-114.
5
Inhalation and dietary exposure to PCBs in urban and rural cohorts via congener-specific measurements.通过特定同系物测量,对城市和农村队列中多氯联苯的吸入和膳食暴露情况进行研究。
Environ Sci Technol. 2015 Jan 20;49(2):1156-64. doi: 10.1021/es5048039.
6
Evaluating health risks from inhaled polychlorinated biphenyls: research needs for addressing uncertainty.评估吸入多氯联苯对健康的风险:应对不确定性的研究需求。
Environ Health Perspect. 2015 Feb;123(2):109-13. doi: 10.1289/ehp.1408564. Epub 2014 Oct 10.
7
Direct assessment of cumulative aryl hydrocarbon receptor agonist activity in sera from experimentally exposed mice and environmentally exposed humans.直接评估实验暴露小鼠和环境暴露人体血清中的累积芳香烃受体激动剂活性。
Environ Health Perspect. 2010 May;118(5):693-8. doi: 10.1289/ehp.0901113.
8
Generalized concentration addition predicts joint effects of aryl hydrocarbon receptor agonists with partial agonists and competitive antagonists.广义浓度加和预测了芳香烃受体激动剂与部分激动剂和竞争性拮抗剂的联合效应。
Environ Health Perspect. 2010 May;118(5):666-72. doi: 10.1289/ehp.0901312.
9
Residential exposure to polychlorinated biphenyls and organochlorine pesticides and risk of childhood leukemia.居家接触多氯联苯和有机氯农药与儿童白血病风险
Environ Health Perspect. 2009 Jun;117(6):1007-13. doi: 10.1289/ehp.0900583. Epub 2009 Jan 27.
10
The 2005 World Health Organization reevaluation of human and Mammalian toxic equivalency factors for dioxins and dioxin-like compounds.2005年世界卫生组织对二噁英及二噁英类化合物的人类和哺乳动物毒性当量因子的重新评估。
Toxicol Sci. 2006 Oct;93(2):223-41. doi: 10.1093/toxsci/kfl055. Epub 2006 Jul 7.