• 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

使用莠去津和利谷隆进行体外和体内除草剂相互作用的细胞遗传学研究。

Cytogenetic studies of herbicide interactions in vitro and in vivo using atrazine and linuron.

作者信息

Roloff B D, Belluck D A, Meisner L F

机构信息

State Laboratory of Hygiene, University of Wisconsin, Madison 53706.

出版信息

Arch Environ Contam Toxicol. 1992 Apr;22(3):267-71. doi: 10.1007/BF00212084.

DOI:10.1007/BF00212084
PMID:1616310
Abstract

The herbicides atrazine and linuron, found in Wisconsin's groundwater, were tested alone and in combination, both in vivo and in vitro, to determine their individual and combined genotoxic effects. Human lymphocytes exposed in vitro to either 1 microgram/ml linuron or 0.001 microgram/ml atrazine showed little chromosome damage, whereas significant chromosome damage was observed in lymphocytes simultaneously exposed to 0.5 microgram/ml linuron and 0.0005 microgram/ml atrazine, suggesting at least an additive model. In another experiment, mice were fed 20 micrograms/ml atrazine, 10 micrograms/ml linuron, or a combination of 10 micrograms/ml atrazine and 5 micrograms/ml linuron in their drinking water for 90 days, after which bone marrow cells and cultured splenocytes were examined for chromosomal damage. None of the treatment groups showed chromosome damage in bone marrow, whereas the cultured splenocytes demonstrated damage in all treatment groups. These experiments suggest that, prior to assessing the risk of a herbicide, it may be necessary to test it in combinations which mimic the mixtures which would occur under field conditions, such as in contaminated groundwater.

摘要

在威斯康星州的地下水中发现的除草剂阿特拉津和利谷隆,分别进行了单独测试以及体内和体外的联合测试,以确定它们各自的和联合的遗传毒性作用。体外暴露于1微克/毫升利谷隆或0.001微克/毫升阿特拉津的人类淋巴细胞几乎没有染色体损伤,而同时暴露于0.5微克/毫升利谷隆和0.0005微克/毫升阿特拉津的淋巴细胞中观察到了明显的染色体损伤,这表明至少存在相加作用模式。在另一项实验中,给小鼠饮用含有20微克/毫升阿特拉津、10微克/毫升利谷隆或10微克/毫升阿特拉津与5微克/毫升利谷隆组合的水,持续90天,之后检查骨髓细胞和培养的脾细胞的染色体损伤情况。所有处理组的骨髓均未显示染色体损伤,而培养的脾细胞在所有处理组中均表现出损伤。这些实验表明,在评估除草剂的风险之前,可能有必要以模拟田间条件下(如受污染的地下水中)出现的混合物的组合形式对其进行测试。

相似文献

1
Cytogenetic studies of herbicide interactions in vitro and in vivo using atrazine and linuron.使用莠去津和利谷隆进行体外和体内除草剂相互作用的细胞遗传学研究。
Arch Environ Contam Toxicol. 1992 Apr;22(3):267-71. doi: 10.1007/BF00212084.
2
Cytogenetic effects of alachlor and/or atrazine in vivo and in vitro.甲草胺和/或莠去津在体内和体外的细胞遗传学效应。
Environ Mol Mutagen. 1992;19(1):77-82. doi: 10.1002/em.2850190110.
3
The clastogenic potential of triazine herbicide combinations found in potable water supplies.饮用水供应中发现的三嗪类除草剂组合的致断裂潜力。
Environ Health Perspect. 1998 Apr;106(4):197-201. doi: 10.1289/ehp.98106197.
4
In vitro effects of N-nitrosoatrazine on chromosome breakage.N-亚硝基莠去津对染色体断裂的体外效应
Arch Environ Contam Toxicol. 1993 Jan;24(1):108-12. doi: 10.1007/BF01061097.
5
Surfactant-enhanced desorption of atrazine and linuron residues as affected by aging of herbicides in soil.表面活性剂对土壤中老化莠去津和利谷隆残留的增强解吸作用
Arch Environ Contam Toxicol. 2006 Jan;50(1):128-37. doi: 10.1007/s00244-005-7036-3. Epub 2005 Oct 19.
6
Cytogenetic studies of three triazine herbicides. II. In vivo micronucleus studies in mouse bone marrow.三种三嗪类除草剂的细胞遗传学研究。II. 小鼠骨髓体内微核研究。
Mutat Res. 2000 Nov 20;471(1-2):107-12. doi: 10.1016/s1383-5718(00)00124-8.
7
Lack of genotoxicity of the herbicide atrazine in cultured human lymphocytes.除草剂阿特拉津对培养的人淋巴细胞无遗传毒性。
Mutat Res. 1998 Aug 7;416(1-2):93-9. doi: 10.1016/s1383-5718(98)00081-3.
8
Limited immunotoxic potential of technical formulation of the herbicide atrazine (AAtrex) in mice.除草剂莠去津(阿特拉津)技术制剂对小鼠的免疫毒性潜力有限。
Toxicol Lett. 1992 May;60(3):263-74. doi: 10.1016/0378-4274(92)90284-q.
9
The herbicide linuron inhibits cholesterol biosynthesis and induces cellular stress responses in brown trout.除草剂利谷隆抑制胆固醇生物合成并诱导褐鳟细胞应激反应。
Environ Sci Technol. 2015 Mar 3;49(5):3110-8. doi: 10.1021/es505498u. Epub 2015 Feb 12.
10
In vivo studies on genotoxicity of pure and commercial linuron.纯利谷隆和市售利谷隆遗传毒性的体内研究。
Mutat Res. 1997 May 23;390(3):207-21. doi: 10.1016/s1383-5718(97)00012-0.

引用本文的文献

1
Atrazine: cytotoxicity, oxidative stress, apoptosis, testicular effects and chemopreventive Interventions.莠去津:细胞毒性、氧化应激、细胞凋亡、对睾丸的影响及化学预防干预措施
Front Toxicol. 2023 Oct 9;5:1246708. doi: 10.3389/ftox.2023.1246708. eCollection 2023.
2
Zinc Ameliorate Oxidative Stress and Hormonal Disturbance Induced by Methomyl, Abamectin, and Their Mixture in Male Rats.锌可改善由灭多威、阿维菌素及其混合物诱导的雄性大鼠氧化应激和激素紊乱。
Toxics. 2017 Dec 3;5(4):37. doi: 10.3390/toxics5040037.
3
Atrazine exposure elicits copy number alterations in the zebrafish genome.

本文引用的文献

1
Evaluation of the mutagenic potential of corn (Zea mays L.) grown in untreated and atrazine (AAtrex) treated soil in the field.对在田间未处理土壤和莠去津(阿特拉津)处理土壤中种植的玉米(玉米属)致突变潜力的评估。
Drug Chem Toxicol. 1984;7(3):243-57. doi: 10.3109/01480548409035106.
2
Oral toxicity of linuron (3-(3,4-dichlorophenyl)-1-methoxy-1-methylurea) in rats and dogs.利谷隆(3-(3,4-二氯苯基)-1-甲氧基-1-甲基脲)对大鼠和犬的口服毒性
Food Cosmet Toxicol. 1968 Aug;6(2):171-83. doi: 10.1016/0015-6264(68)90199-5.
3
Cytogenetic studies with atrazine (2-chloro-4-ethyl-amino-6-isopropylamino-s-triazine) on plants.
阿特拉津暴露引发斑马鱼基因组的拷贝数改变。
Comp Biochem Physiol C Toxicol Pharmacol. 2017 Apr;194:1-8. doi: 10.1016/j.cbpc.2017.01.003. Epub 2017 Jan 19.
4
Atrazine Triggers DNA Damage Response and Induces DNA Double-Strand Breaks in MCF-10A Cells.阿特拉津引发DNA损伤反应并诱导MCF-10A细胞中的DNA双链断裂。
Int J Mol Sci. 2015 Jun 24;16(7):14353-68. doi: 10.3390/ijms160714353.
5
Disruptive environmental chemicals and cellular mechanisms that confer resistance to cell death.具有破坏作用的环境化学物质以及赋予细胞对死亡抗性的细胞机制。
Carcinogenesis. 2015 Jun;36 Suppl 1(Suppl 1):S89-110. doi: 10.1093/carcin/bgv032.
6
Effects of short term exposure of atrazine on the liver and kidney of normal and diabetic rats.短期暴露于莠去津对正常和糖尿病大鼠肝脏及肾脏的影响。
J Toxicol. 2014;2014:536759. doi: 10.1155/2014/536759. Epub 2014 Sep 29.
7
Determination of genotoxicity of the metabolites of the pesticides Guthion, Sencor, Lorox, Reglone, Daconil and Admire by 32P-postlabeling.采用32P后标记法测定农药谷硫磷、甲嘧磺隆、恶草酮、敌草快、百菌清和吡虫啉代谢产物的遗传毒性。
Mol Cell Biochem. 1997 Apr;169(1-2):177-84. doi: 10.1023/a:1006861621031.
8
Small area pesticides data: multiplicity and variability of pesticide usage on southern row crops.小区域农药数据:南方大田作物农药使用的多样性和变异性
Arch Environ Contam Toxicol. 1992 Oct;23(3):289-94. doi: 10.1007/BF00216235.
关于阿特拉津(2-氯-4-乙氨基-6-异丙氨基-s-三嗪)对植物的细胞遗传学研究。
Experientia. 1972 Jun 15;28(6):704-5. doi: 10.1007/BF01944990.
4
Detection and analysis of interactions between atrazine and sodium pentachlorophenate with single and multiple algal-bacterial populations.阿特拉津与五氯酚钠在单一和多个藻菌种群间相互作用的检测与分析
Arch Environ Contam Toxicol. 1985 Mar;14(2):167-77. doi: 10.1007/BF01055608.
5
Cancer and other causes of death among Wisconsin farmers.威斯康星州农民中的癌症及其他死因。
Am J Ind Med. 1987;11(2):119-29. doi: 10.1002/ajim.4700110202.
6
Agricultural herbicide use and risk of lymphoma and soft-tissue sarcoma.农业除草剂的使用与淋巴瘤和软组织肉瘤的风险
JAMA. 1986 Sep 5;256(9):1141-7.
7
The effect of exposure regimen and duration on benzene-induced bone marrow damage in mice. II. Strain comparisons involving B6C3F1, C57B1/6 and DBA/2 male mice.暴露方案和持续时间对苯诱导的小鼠骨髓损伤的影响。II. 涉及B6C3F1、C57B1/6和DBA/2雄性小鼠的品系比较。
Mutat Res. 1988 Aug;203(4):273-95. doi: 10.1016/0165-1161(88)90018-0.
8
The effect of exposure regimen and duration on benzene-induced bone-marrow damage in mice. I. Sex comparison in DBA/2 mice.暴露方案和持续时间对苯诱导的小鼠骨髓损伤的影响。I. DBA/2小鼠的性别比较。
Mutat Res. 1988 Aug;203(4):251-71. doi: 10.1016/0165-1161(88)90017-9.
9
On the mutagenic and recombinogenic activity of certain herbicides in Salmonella typhimurium and in Aspergillus nidulans.
Mutat Res. 1988 Apr;204(4):615-21. doi: 10.1016/0165-1218(88)90064-x.
10
Assessment of the mutagenicity of fractions from s-triazine-treated Zea mays.对经 s-三嗪处理的玉米各组分致突变性的评估。
Mutat Res. 1988 Feb;197(2):325-36. doi: 10.1016/0027-5107(88)90102-9.