这是一篇来自已证抗体库的有关人类 cdk7的综述,是根据44篇发表使用所有方法的文章归纳的。这综述旨在帮助来邦网的访客找到最适合cdk7 抗体。
cdk7 同义词: CAK; CAK1; CDKN7; HCAK; MO15; STK1; p39MO15; cyclin-dependent kinase 7; 39 KDa protein kinase; CDK-activating kinase 1; TFIIH basal transcription factor complex kinase subunit; cell division protein kinase 7; cyclin-dependent kinase 7 (MO15 homolog, Xenopus laevis, cdk-activating kinase); homolog of Xenopus MO15 Cdk-activating kinase; kinase subunit of CAK; serine/threonine kinase stk1; serine/threonine protein kinase 1; serine/threonine protein kinase MO15

赛默飞世尔
小鼠 单克隆(31TF2-1F8)
赛默飞世尔 cdk7抗体(Affinity Bioreagent, MA3-001)被用于. PLoS ONE (2016) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Artemia franciscana; 1:1250; 图 10
赛默飞世尔 cdk7抗体(Affinity BioReagents, MA3-001)被用于被用于免疫印迹在Artemia franciscana样品上浓度为1:1250 (图 10). Integr Comp Biol (2005) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Acartia tonsa; 1:2500; 图 7a
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Acartia tonsa样品上浓度为1:2500 (图 7a). J Exp Mar Bio Ecol (2009) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; 面包酵母; 1:2000; 图 3a
赛默飞世尔 cdk7抗体(Affinity BioReagents, MA3-001)被用于被用于免疫印迹在面包酵母样品上浓度为1:2000 (图 3a). Cell Mol Biol Lett (2008) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Chinook salmon; 1:500; 图 1a
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Chinook salmon样品上浓度为1:500 (图 1a). Ecotoxicol Environ Saf (2009) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; California mussel; 图 2
赛默飞世尔 cdk7抗体(Affinity Bioreagent, MA3-001)被用于被用于免疫印迹在California mussel样品上 (图 2). Oecologia (2008) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Austrofundulus limnaeus; 1:1000; 图 2a
赛默飞世尔 cdk7抗体(Affinity BioReagents, MA3-001)被用于被用于免疫印迹在Austrofundulus limnaeus样品上浓度为1:1000 (图 2a). Cell Stress Chaperones (2007) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Chinook salmon; 1:500; 图 2
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Chinook salmon样品上浓度为1:500 (图 2). Environ Toxicol Chem (2007) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Balanus glandula; 1:2500; 图 1
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Balanus glandula样品上浓度为1:2500 (图 1). Biol Bull (2007) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Artemia franciscana; 1:1250; 图 4
赛默飞世尔 cdk7抗体(Affinity BioReagents, MA3-001)被用于被用于免疫印迹在Artemia franciscana样品上浓度为1:1250 (图 4). Comp Biochem Physiol B Biochem Mol Biol (2006) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; long-jawed mudsucker; 1:2500
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在long-jawed mudsucker样品上浓度为1:2500. Comp Biochem Physiol A Mol Integr Physiol (2006) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; bay mussel; 1:500; 图 2
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在bay mussel样品上浓度为1:500 (图 2). Biomarkers (2005) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Maori chief; 图 1b
  • 免疫印迹; emerald rockcod; 图 1b
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Maori chief样品上 (图 1b) 和 被用于免疫印迹在emerald rockcod样品上 (图 1b). Cell Stress Chaperones (2005) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; 猪; 1:1000; 图 1
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在猪样品上浓度为1:1000 (图 1). Toxicol Lett (2005) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; 牛; 图 1d
  • 免疫印迹; emerald rockcod; 图 1d
  • 免疫印迹; Notocypraea angustata; 图 1d
  • 免疫印迹; bald rockcod; 图 1d
赛默飞世尔 cdk7抗体(Affinity Bioreagent, MA3-001)被用于被用于免疫印迹在牛样品上 (图 1d), 被用于免疫印迹在emerald rockcod样品上 (图 1d), 被用于免疫印迹在Notocypraea angustata样品上 (图 1d) 和 被用于免疫印迹在bald rockcod样品上 (图 1d). Am J Physiol Regul Integr Comp Physiol (2005) ncbi
小鼠 单克隆(31TF2-1F8)
赛默飞世尔 cdk7抗体(Affinity BioReagents, MA3-001)被用于. J Biosci (2004) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Sacramento splittail; 1:500; 图 4a
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Sacramento splittail样品上浓度为1:500 (图 4a). Mar Environ Res (2005) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; long-jawed mudsucker; 1:2500
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在long-jawed mudsucker样品上浓度为1:2500. Physiol Biochem Zool (2004) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Chinook salmon; 1:500; 图 1
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Chinook salmon样品上浓度为1:500 (图 1). Mar Environ Res (2004) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Corbula amurensis; 1:500; 图 1
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Corbula amurensis样品上浓度为1:500 (图 1). Mar Environ Res (2004) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Macoma nasuta; 1:500; 表 1
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Macoma nasuta样品上浓度为1:500 (表 1). Mar Environ Res (2004) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; brown tegula; 图 1b
赛默飞世尔 cdk7抗体(Affinity BioReagent, MA3-001)被用于被用于免疫印迹在brown tegula样品上 (图 1b). Biol Bull (2003) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Pacific oyster; 图 4
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Pacific oyster样品上 (图 4). Biol Bull (2003) ncbi
小鼠 单克隆(31TF2-1F8)
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于. Mar Environ Res (2002) ncbi
小鼠 单克隆(31TF2-1F8)
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于. J Exp Biol (2002) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫细胞化学; African green monkey; 图 2a
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫细胞化学在African green monkey样品上 (图 2a). J Virol (2002) ncbi
小鼠 单克隆(31TF2-1F8)
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于. J Exp Biol (2002) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Artemia franciscana; 1:1250; 图 3
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在Artemia franciscana样品上浓度为1:1250 (图 3). J Cell Biochem (2002) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; California mussel; 图 7
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在California mussel样品上 (图 7). Biol Bull (2001) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; bay mussel; 图 4
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在bay mussel样品上 (图 4). J Exp Biol (2001) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; long-jawed mudsucker; 图 2b
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在long-jawed mudsucker样品上 (图 2b). J Exp Biol (2001) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Corbula amurensis; 1:500; 图 2
赛默飞世尔 cdk7抗体(Anity Bioreagents, MA3-001)被用于被用于免疫印迹在Corbula amurensis样品上浓度为1:500 (图 2). Mar Environ Res (2000) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫组化; Corbula amurensis; 图 2
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫组化在Corbula amurensis样品上 (图 2). Mar Environ Res (2000) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; green sea urchin; 图 6
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在green sea urchin样品上 (图 6). J Exp Zool (2001) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; Artemia franciscana; 图 10
赛默飞世尔 cdk7抗体(Affinity BioReagents, MA3-001)被用于被用于免疫印迹在Artemia franciscana样品上 (图 10). Cell Tissue Res (2000) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; emerald rockcod; 图 4
赛默飞世尔 cdk7抗体(Affinity BioReagents, MA3-001)被用于被用于免疫印迹在emerald rockcod样品上 (图 4). J Exp Biol (2000) ncbi
小鼠 单克隆(31TF2-1F8)
  • 免疫印迹; emerald rockcod; 图 2
赛默飞世尔 cdk7抗体(Affinity Bioreagents, MA3-001)被用于被用于免疫印迹在emerald rockcod样品上 (图 2). Comp Biochem Physiol A Mol Integr Physiol (2000) ncbi
圣克鲁斯生物技术
小鼠 单克隆(C-4)
  • 免疫沉淀; 人类; 图 4b
圣克鲁斯生物技术 cdk7抗体(Santa Cruz, SC-7344)被用于被用于免疫沉淀在人类样品上 (图 4b). Nat Commun (2017) ncbi
小鼠 单克隆(C-4)
  • 免疫印迹; 人类; 图 3a
圣克鲁斯生物技术 cdk7抗体(Santa Cruz, C-4)被用于被用于免疫印迹在人类样品上 (图 3a). J Virol (2016) ncbi
小鼠 单克隆(MO-1)
  • 其他; 人类; 图 st1
圣克鲁斯生物技术 cdk7抗体(SCBT, MO-1)被用于被用于其他在人类样品上 (图 st1). Mol Cell Proteomics (2016) ncbi
小鼠 单克隆(C-5)
  • 免疫印迹; 小鼠; 图 s1h
  • 免疫印迹; 人类; 图 s1h
圣克鲁斯生物技术 cdk7抗体(Santa, sc-365075)被用于被用于免疫印迹在小鼠样品上 (图 s1h) 和 被用于免疫印迹在人类样品上 (图 s1h). Cell (2014) ncbi
小鼠 单克隆(C-4)
  • 免疫沉淀; 人类
  • 免疫印迹; 人类
圣克鲁斯生物技术 cdk7抗体(Santa, sc-7344)被用于被用于免疫沉淀在人类样品上 和 被用于免疫印迹在人类样品上. Mol Cell Biol (2014) ncbi
艾博抗(上海)贸易有限公司
兔 多克隆
  • 免疫印迹; 人类; 图 s2b
艾博抗(上海)贸易有限公司 cdk7抗体(Abcam, ab59987)被用于被用于免疫印迹在人类样品上 (图 s2b). Cell (2014) ncbi
赛信通(上海)生物试剂有限公司
小鼠 单克隆(MO1)
  • 免疫印迹; 人类; 图 1c
赛信通(上海)生物试剂有限公司 cdk7抗体(Cell Signaling, 2916P)被用于被用于免疫印迹在人类样品上 (图 1c). Mol Cell (2017) ncbi
小鼠 单克隆(MO1)
  • 免疫印迹; 人类
赛信通(上海)生物试剂有限公司 cdk7抗体(Cell Signaling, MO1)被用于被用于免疫印迹在人类样品上. J Virol (2014) ncbi
文章列表
  1. Liao P, Zeng S, Zhou X, Chen T, Zhou F, Cao B, et al. Mutant p53 Gains Its Function via c-Myc Activation upon CDK4 Phosphorylation at Serine 249 and Consequent PIN1 Binding. Mol Cell. 2017;68:1134-1146.e6 pubmed 出版商
  2. Cayrol F, Praditsuktavorn P, Fernando T, Kwiatkowski N, Marullo R, Calvo Vidal M, et al. THZ1 targeting CDK7 suppresses STAT transcriptional activity and sensitizes T-cell lymphomas to BCL2 inhibitors. Nat Commun. 2017;8:14290 pubmed 出版商
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  16. Berger M, Emlet R. Heat-shock response of the upper intertidal barnacle Balanus glandula: thermal stress and acclimation. Biol Bull. 2007;212:232-41 pubmed
  17. Clegg J, Campagna V. Comparisons of stress proteins and soluble carbohydrate in encysted embryos of Artemia franciscana and two species of Parartemia. Comp Biochem Physiol B Biochem Mol Biol. 2006;145:119-25 pubmed
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  19. La Porte P. Mytilus trossulus hsp70 as a biomarker for arsenic exposure in the marine environment: laboratory and real-world results. Biomarkers. 2005;10:417-28 pubmed
  20. Place S, Hofmann G. Temperature differentially affects adenosine triphosphatase activity in Hsc70 orthologs from Antarctic and New Zealand notothenioid fishes. Cell Stress Chaperones. 2005;10:104-13 pubmed
  21. Ryan P, Bedard K, Breining T, Cribb A. Disruption of the endoplasmic reticulum by cytotoxins in LLC-PK1 cells. Toxicol Lett. 2005;159:154-63 pubmed
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  24. Teh S, Deng D, Werner I, Teh F, Hung S. Sublethal toxicity of orchard stormwater runoff in Sacramento splittail (Pogonichthys macrolepidotus) larvae. Mar Environ Res. 2005;59:203-16 pubmed
  25. Buckley B, Hofmann G. Magnitude and duration of thermal stress determine kinetics of hsp gene regulation in the goby Gillichthys mirabilis. Physiol Biochem Zool. 2004;77:570-81 pubmed
  26. Eder K, Leutenegger C, Wilson B, Werner I. Molecular and cellular biomarker responses to pesticide exposure in juvenile chinook salmon (Oncorhynchus tshawytscha). Mar Environ Res. 2004;58:809-13 pubmed
  27. Werner I. The influence of salinity on the heat-shock protein response of Potamocorbula amurensis (Bivalvia). Mar Environ Res. 2004;58:803-7 pubmed
  28. Werner I, Teh S, Datta S, Lu X, Young T. Biomarker responses in Macoma nasuta (Bivalvia) exposed to sediments from northern San Francisco Bay. Mar Environ Res. 2004;58:299-304 pubmed
  29. Tomanek L, Sanford E. Heat-shock protein 70 (Hsp70) as a biochemical stress indicator: an experimental field test in two congeneric intertidal gastropods (genus: Tegula). Biol Bull. 2003;205:276-84 pubmed
  30. Hamdoun A, Cheney D, Cherr G. Phenotypic plasticity of HSP70 and HSP70 gene expression in the Pacific oyster (Crassostrea gigas): implications for thermal limits and induction of thermal tolerance. Biol Bull. 2003;205:160-9 pubmed
  31. Werner I, Geist J, Okihiro M, Rosenkranz P, Hinton D. Effects of dietary exposure to the pyrethroid pesticide esfenvalerate on medaka (Oryzias latipes). Mar Environ Res. 2002;54:609-14 pubmed
  32. Buckley B, Hofmann G. Thermal acclimation changes DNA-binding activity of heat shock factor 1 (HSF1) in the goby Gillichthys mirabilis: implications for plasticity in the heat-shock response in natural populations. J Exp Biol. 2002;205:3231-40 pubmed
  33. Guerrero C, Bouyssounade D, Zárate S, Isa P, López T, Espinosa R, et al. Heat shock cognate protein 70 is involved in rotavirus cell entry. J Virol. 2002;76:4096-102 pubmed
  34. Tomanek L, Somero G. Interspecific- and acclimation-induced variation in levels of heat-shock proteins 70 (hsp70) and 90 (hsp90) and heat-shock transcription factor-1 (HSF1) in congeneric marine snails (genus Tegula): implications for regulation of hsp gene expression. J Exp Biol. 2002;205:677-85 pubmed
  35. Willsie J, Clegg J. Small heat shock protein p26 associates with nuclear lamins and HSP70 in nuclei and nuclear matrix fractions from stressed cells. J Cell Biochem. 2002;84:601-14 pubmed
  36. Helmuth B, Hofmann G. Microhabitats, thermal heterogeneity, and patterns of physiological stress in the rocky intertidal zone. Biol Bull. 2001;201:374-84 pubmed
  37. Buckley B, Owen M, Hofmann G. Adjusting the thermostat: the threshold induction temperature for the heat-shock response in intertidal mussels (genus Mytilus) changes as a function of thermal history. J Exp Biol. 2001;204:3571-9 pubmed
  38. Place S, Hofmann G. Temperature interactions of the molecular chaperone Hsc70 from the eurythermal marine goby Gillichthys mirabilis. J Exp Biol. 2001;204:2675-82 pubmed
  39. Werner I, Hinton D. Spatial profiles of hsp70 proteins in Asian clam (Potamocorbula amurensis) in northern San Francisco Bay may be linked to natural rather than anthropogenic stressors. Mar Environ Res. 2000;50:379-84 pubmed
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