tetrabromobisphenol A: a brominated flame retardant
3,3',5,5'-tetrabromobisphenol A : A bromobisphenol that is 4,4'-methanediyldiphenol in which the methylene hydrogens are replaced by two methyl groups and the phenyl rings are substituted by bromo groups at positions 2, 2', 6 and 6'. It is a brominated flame retardant.
ID Source | ID |
---|---|
PubMed CID | 6618 |
CHEMBL ID | 184450 |
CHEBI ID | 33217 |
SCHEMBL ID | 18647 |
MeSH ID | M0074958 |
Synonym |
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BIDD:ER0631 |
MLS002152878 |
smr001224492 |
4,4''-(propane-2,2-diyl)bis(2,6-dibromophenol) |
bdbm50150793 |
2,2'',6,6''-tetrabromobisphenol a |
4,4''-isopropylidenebis(2,6-dibromophenol) |
4,4''-(1-methylethylidene)bis(2,6-dibromophenol) |
3,3'',5,5''-tetrabromobisphenol a |
4,4''-(2,2-propanediyl) bis[2,6-dibromo]phenol |
phenol, 4,4'-(1-methylethylidene)bis[2,6-dibromo- |
phenol, 4,4'-isopropylidenebis[2,6-dibromo- |
fire guard 2000 |
firemaster bp 4a |
saytex rb-100 |
tetrabromodian: tetrabromodihydroxy diphenylpropane |
great lakes ba-59p |
4,4'-isopropylidene-bis(2,6-dibromophenol) |
phenol, 4,4'-isopropylidenebis (dibromo-) |
4,4'-(1-methylethylidene)bis(2,6-dibromophenol) |
CHEBI:33217 , |
4,4'-isopropylidenebis(2,6-dibromophenol) |
saytex rb-100 abs |
4,4'-(2,2-propanediyl) bis[2,6-dibromo]phenol |
4,4'-(propane-2,2-diyl)bis(2,6-dibromophenol) |
fr-1524 |
2,2',6,6'-tetrabromobisphenol a |
C0763 |
2,2-bis(3,5-dibromo-4-hydroxyphenyl)propane |
4,4'-propane-2,2-diylbis(2,6-dibromophenol) |
2,6-dibromo-4-[1-(3,5-dibromo-4-hydroxyphenyl)-1-methylethyl]phenol |
2,5-dibromophenyl)propane |
3,3',5'-tetrabromobisphenol a |
firemaster bp4a |
phenol,4'-isopropylidenebis[2,6-dibromo- |
nsc-59775 |
4,6-dibromophenol) |
fg 2000 |
2,6,6'-tetrabromobisphenol a |
2,5-dibromo-4-hydroxyphenyl)propane |
bromdian |
phenol,4'-(1-methylethylidene)bis[2,6-dibromo- |
nsc59775 |
tetrabromo-4,4'-isopropylidenediphenol |
OPREA1_822733 |
79-94-7 |
tetrabromobisphenol a |
3,3',5,5'-tetrabromobisphenol a |
NCGC00091463-01 |
NCGC00091463-02 |
4,4'-isopropylylidenebis(2,6-dibromophenol) |
ccris 6274 |
hsdb 5232 |
3,5,3',5'-tetrabromobisphenol a |
2,2',6,6'-tetrabromo-4,4'-isopropylidenediphenol |
einecs 201-236-9 |
ba 59 |
phenol, 4,4'-(1-methylethylidene)bis(2,6-dibromo- |
saytex rb 100pc |
phenol, 4,4'-isopropylidenebis(2,6-dibromo- |
tetrabromodian |
4,4'-(1-methylethylidene)bis(2,6-dibromophenol)2,2-bis(3,5-dibromo-4-hydroxyphenyl)propane |
2,2-bis(4-hydroxy-3,5-dibromophenyl)propane |
tetrabromodiphenylopropane |
nsc 59775 |
inchi=1/c15h12br4o2/c1-15(2,7-3-9(16)13(20)10(17)4-7)8-5-11(18)14(21)12(19)6-8/h3-6,20-21h,1-2h |
330396_ALDRICH , |
3,3',5,5'-tetrabromobisphenol a, 97% |
NCGC00091463-03 |
3,3',5,5'-tetrabromo bisphenol a |
tetrabromo bisphenol a |
tbbpa |
STK048486 |
AC-11719 |
AKOS000491577 |
2,6-dibromo-4-[2-(3,5-dibromo-4-hydroxyphenyl)propan-2-yl]phenol |
zinc01689786 |
BMSE000567 |
CHEMBL184450 , |
T0032 |
NCGC00091463-04 |
NCGC00091463-06 |
NCGC00091463-05 |
xdi , |
4,4'-(2,2-propanediyl)bis(2,6-dibromophenol) |
tox21_300561 |
dtxsid1026081 , |
NCGC00259530-01 |
tox21_201981 |
NCGC00254356-01 |
cas-79-94-7 |
dtxcid406081 |
tox21_201182 |
NCGC00258734-01 |
FT-0682679 |
ec 201-236-9 |
unii-fqi02rfc3a |
flame cut 120g |
fqi02rfc3a , |
FT-0617111 |
2,2,6,6-tetrabromo-4,4-isopropylidene phenol |
S12384 |
tetrabromobisphenol a [mi] |
tetrabromobisphenol a [iarc] |
tetrabromobisphenol a, 3,3',5,5'- |
cp-2000 |
2,2',6,6'-tetrabromobisphenol a [hsdb] |
SCHEMBL18647 |
3OSW |
2,6-dibromo-4-[1-(3,5-dibromo-4-hydroxy-phenyl)-1-methyl-ethyl]phenol |
2,2-bis-(3,5-dibromo-4-hydroxyphenyl)propane |
2,2-bis(3,5dibromo-4-hydroxyphenyl)propane |
2,2-bis-(3,5-dibromo-4-hydroxyphenyl)-propane |
2,2-bis-(4'-hydroxy-3',5'-dibromophenyl)-propane |
2,2-bis(3,5-dibromo-4-hydroxyphenyl)-propane |
W-104257 |
3,3',5,5'-tetrabromobisphenol a, certified reference material, tracecert(r) |
3,3',5,5'-tetrabromo-4,4-dihydroxy-2,2-diphenylpropane |
2,2',6,6'-tetrabromo-4,4'-isopropylidene bisphenol |
tetrabromobisphenol ''a'' |
4,4'-(1-methylethylidene)bis[2,6-dibromophenol] |
mfcd00013962 |
SR-01000596914-1 |
sr-01000596914 |
3,3',5,5'-tetrabromobisphenol a, analytical standard |
bp_15 |
tbbp-a |
Q425246 |
AS-12834 |
33'55'-tetrabromobisphenol a |
3,3',5,5'-tetrabromo-4,4'-dihydroxy-diphenyl-dimethyl-methane |
A864777 |
BR1202 |
tetrabromobisphenol a 50 microg/ml in methanol |
EN300-64638 |
CS-W013812 |
tbba/tbbpa |
Tetrabromobisphenol A (TBBPA) is used in a variety of consumer products such as electronic equipment, fire extinguishers, furniture, plastics, textiles, and kitchen hoods. It is a flame retardant that can contaminate the environment and human being, acting as an endocrine disruptor.
Tetrabromobisphenol A (TBBPA) has become a ubiquitous indoor contaminant due to its widespread use as an additive flame retardant in consumer products. The pollutant has aroused widespread pollution in industrial wastewater.
Excerpt | Reference | Relevance |
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"Tetrabromobisphenol A (TBBPA) can cause diverse adverse effects including neurotoxicity. " | ( The potential neurotoxicity of emerging tetrabromobisphenol A derivatives based on rat pheochromocytoma cells. Hu, L; Jiang, G; Liu, Q; Long, Y; Qu, G; Ren, X; Zhou, Q, 2016) | 2.14 |
Tetrabromobisphenol A (TBBPA) is a brominated flame retardant. It can cause diverse adverse effects including neurotoxicity. The molecular mechanisms are unclear, and related metabolomics studies are limited.
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" Half the rats in each dose group were sacrificed for a full gross necropsy and a histopathology on the organs and the tissues at 22 days of age and the remaining rats were reared without any treatment from post-weaning until 84 days of age to examine the recovery and the delayed occurrence of toxic effects." | ( Unexpected nephrotoxicity induced by tetrabromobisphenol A in newborn rats. Ema, M; Fukuda, N; Hasegawa, R; Ito, Y; Kamata, E; Koizumi, M; Mitumori, K; Yamaguchi, M, 2004) | 0.6 |
" Tetrabromobisphenol A (TBBPA) was quite toxic to enchytraeids, with significant effects on reproduction detected already at the 10 mgkg(-1) exposure level (EC(10)=2." | ( Toxicity of three halogenated flame retardants to nitrifying bacteria, red clover (Trifolium pratense), and a soil invertebrate (Enchytraeus crypticus). Hartnik, T; Jensen, J; Mariussen, E; Sverdrup, LE, 2006) | 1.24 |
" Our studies on acute and sub-acute toxic effects with established cell lines demonstrate that TBBPA interferes with cellular signaling pathways." | ( Cytotoxicity of TBBPA and effects on proliferation, cell cycle and MAPK pathways in mammalian cells. Detzel, T; Krug, HF; Kuch, B; Strack, S; Wahl, M, 2007) | 0.34 |
"In most toxicity studies single housing is still preferred, as social stress is believed to have an effect on experimental outcome through interaction with the toxic compound or by increasing variation." | ( Effects of housing condition on experimental outcome in a reproduction toxicity study. Hendriksen, CF; van den Bos, R; van der Ven, LT; Verwer, CM, 2007) | 0.34 |
" TBBPA at a weakly toxic level (0." | ( Biotransformation and cytotoxicity of a brominated flame retardant, tetrabromobisphenol A, and its analogues in rat hepatocytes. Ishii, H; Nakagawa, Y; Ogata, A; Suzuki, T, 2007) | 0.58 |
"Using the indoor simulating method of dynamic and static exposure respectively, the toxic effects of TBBPA on the antioxidant enzyme defense systems and Glutathione-S-transferase (GST) activity of tubifex Monopylephorus limosus were examined." | ( [Oxidation stress and toxicity of TBBPA pollution on polychaete tubifex (Monopylephorus limosus)]. Hu, XG; Li, YN; Luo, Y; Zhou, QX, 2008) | 0.35 |
" Endpoint values showed that B(4)BPA was significantly less toxic than the other chemicals when tested with the Microtox and algal asssays." | ( Ecotoxicity of a brominated flame retardant (tetrabromobisphenol A) and its derivatives to aquatic organisms. André, C; Blaise, C; Debenest, T; Gagné, F; Kohli, M; Petit, AN, 2010) | 0.62 |
" The purpose of the study was to develop a multispecies microalgae test in order to determine the impact of species interactions on the cytoxicity of an emergent toxic contaminant: the tetrabromobisphenol A (TBBPA)." | ( Comparative toxicity of a brominated flame retardant (tetrabromobisphenol A) on microalgae with single and multi-species bioassays. Blaise, C; Debenest, T; Gagné, F; Kohli, M; Nguyen, N; Petit, AN, 2011) | 0.81 |
" The use of vtg1 mRNA induction in zebrafish embryos and larvae was found to be a sensitive biomarker of exposure to these organic compounds, and was helpful in elucidating their adverse effects and setting water quality guidelines." | ( Toxicity assessment and vitellogenin expression in zebrafish (Danio rerio) embryos and larvae acutely exposed to bisphenol A, endosulfan, heptachlor, methoxychlor and tetrabromobisphenol A. Chan, KM; Chan, WK; Chow, WS, 2013) | 0.58 |
" Our in vitro studies thus demonstrate that TBBPA exerts several adverse effects on functional neurotransmission endpoints with effect concentrations that are only two orders of magnitude below the highest cord serum concentrations." | ( Multiple novel modes of action involved in the in vitro neurotoxic effects of tetrabromobisphenol-A. Hendriks, HS; van den Berg, M; van Kleef, RG; Westerink, RH, 2012) | 0.38 |
"Tetrabromobisphenol A (TBBPA) is a toxic brominated flame retardant." | ( Synergistic neurotoxicity of oxygen-glucose deprivation and tetrabromobisphenol A in vitro: role of oxidative stress. Lazarewicz, JW; Stafiej, A; Toczyłowska, B; Ziemińska, E, 2012) | 2.06 |
"5 μM TBBPA for 45 min to normoxic and glucose-containing incubation medium did not reduce the viability of cultured CGC, but this compound exacerbated the toxic effects of OGD in a concentration-dependent way." | ( Synergistic neurotoxicity of oxygen-glucose deprivation and tetrabromobisphenol A in vitro: role of oxidative stress. Lazarewicz, JW; Stafiej, A; Toczyłowska, B; Ziemińska, E, 2012) | 0.62 |
"Tetrabromobisphenol A (TBBPA), a brominated flame retardant, is detected commonly in aquatic environments, where it is thought to be highly toxic to the development of aquatic life." | ( Protective effects of puerarin against tetrabromobisphenol a-induced apoptosis and cardiac developmental toxicity in zebrafish embryo-larvae. Ding, Z; Sun, F; Wang, S; Wu, F; Xu, F; Yang, S; Zhang, M, 2015) | 2.13 |
" The results have demonstrated some notable toxic effects due to long-term exposure to either or both contaminants." | ( Toxic effects of the joint exposure of decabromodiphenyl ether (BDE209) and tetrabromobisphenol A (TBBPA) on soil microorganism and enzyme activity. An, S; Chen, L; Lin, K; Liu, K; Zhang, W; Zhao, L, 2014) | 0.63 |
"The toxic effects of three polybrominated diphenyl ether (PBDE) congeners (BDE-47, -99, and -209), tetrabromobisphenol A (TBBPA) and bisphenol A (BPA), were evaluated by determining their 24h and 96 h median lethal concentrations using a zebrafish liver cell line, ZFL." | ( Evaluation of the toxic effects of brominated compounds (BDE-47, 99, 209, TBBPA) and bisphenol A (BPA) using a zebrafish liver cell line, ZFL. Chan, KM; Yang, J, 2015) | 0.63 |
" It concludes that the potential modes of action for thyroid changes induced by TBBPA are expected to exhibit a threshold for adverse effects due to the ability of the mammalian organism to compensate small changes in thyroid hormone levels." | ( Tetrabromobisphenol A (TBBPA): Possible modes of action of toxicity and carcinogenicity in rodents. Dekant, W; Kacew, S; Lai, DY, 2015) | 1.86 |
" Whether 1:1 concentration or 1:1 toxic level, the research showed synergy effect relative to single exposure conditions." | ( Lethal and Sublethal Toxicity Comparison of BFRs to Three Marine Planktonic Copepods: Effects on Survival, Metabolism and Ingestion. Gong, W; Hao, Y; Zhu, L, 2016) | 0.43 |
"Tetrabromobisphenol A (TBBPA) can cause diverse adverse effects including neurotoxicity." | ( The potential neurotoxicity of emerging tetrabromobisphenol A derivatives based on rat pheochromocytoma cells. Hu, L; Jiang, G; Liu, Q; Long, Y; Qu, G; Ren, X; Zhou, Q, 2016) | 2.14 |
"Tetrabromobisphenol A and tetrachlorobisphenol A are halogenated bisphenol A (H-BPA), and has raised concerns about their adverse effects on the development of fetuses and infants, however, the molecular mechanisms are unclear, and related metabolomics studies are limited." | ( Metabolomics approach reveals metabolic disorders and potential biomarkers associated with the developmental toxicity of tetrabromobisphenol A and tetrachlorobisphenol A. Chen, Y; Chi, Y; Dong, S; Huang, Q; Lin, Y; Wang, HO; Ye, G; Ye, T, 2016) | 2.08 |
" Tetrabromobisphenol A is classified as hazard statements (H) H400/H410, which means that it is toxic to aquatic biota, causing long-term changes in these organisms." | ( [Tetrabromobisphenol A - Toxicity, environmental and occupational exposures]. Bukowska, B; Jarosiewicz, M, 2017) | 2.28 |
" Due to the hazardous effects of many of these chemicals, manufacturers are developing next generation potential less toxic alternatives." | ( Acute mixture toxicity of halogenated chemicals and their next generation counterparts on zebrafish embryos. Abdel-Moneim, A; Godfrey, A; Sepúlveda, MS, 2017) | 0.46 |
" The results of toxicity testing showed that ferrate (VI) could effectively control the toxicity of the treated samples, although the toxicity increased in the initial reaction stage due to the accumulation and destruction of more toxic intermediates." | ( Degradation of tetrabromobisphenol A by ferrate(VI) oxidation: Performance, inorganic and organic products, pathway and toxicity control. Dong, W; Han, Q; Liu, T; Song, X; Tian, Y; Wang, H, 2018) | 0.83 |
"Tetrabromobisphenol A (TBBPA) and tetrachlorobisphenol A (TCBPA) are persistent toxic environmental pollutants that cause severe reproductive toxicity in animals." | ( Differences in reproductive toxicity of TBBPA and TCBPA exposure in male Rana nigromaculata. Chen, B; Chen, F; Du, Q; He, J; Jia, X; Li, N; Liu, W; Shan, X; Tang, J; Zhang, H, 2018) | 1.92 |
" The results of toxicity testing showed that ozonation could effectively control the acute and chronic toxicity of the water samples, although the toxicity increased in the initial reaction stage due to the accumulation of more toxic intermediates." | ( Degradation of tetrabromobisphenol a by ozonation: Performance, products, mechanism and toxicity. Dong, W; Fan, H; Gu, Y; Han, Q; Liu, P; Ma, H; Song, X; Wang, H, 2019) | 0.87 |
" Recently, we developed a novel in vitro three-dimensional (3D) testicular cell co-culture model, enabling the classification of reproductive toxic substances." | ( High-Content Image-Based Single-Cell Phenotypic Analysis for the Testicular Toxicity Prediction Induced by Bisphenol A and Its Analogs Bisphenol S, Bisphenol AF, and Tetrabromobisphenol A in a Three-Dimensional Testicular Cell Co-culture Model. Edenfield, C; Guan, X; Liang, S; Measel, E; Siracusa, JS; Yin, L; Yu, X, 2020) | 0.75 |
" Compound 2,6-dibromo-4-[3,5-dibromo-4-(2-hydroxyethoxy)benzene-1-sulfonyl]phenol was more toxic than other compounds in various cells, and the sensitivity of this compound to the normal hepatocytes and cancer cells was inconsistent." | ( Synthesis and Toxicity of Halogenated Bisphenol Monosubstituted-Ethers: Establishing a Library for Potential Environmental Transformation Products of Emerging Contaminant. Cao, M; Deng, W; Gao, Y; Guo, R; Hu, M; Shi, J; Ye, S; Zhang, W; Zhou, W, 2020) | 0.56 |
" This study confirmed that environmentally relevant levels of TBBPA and TBBPA-BDBPE are toxic to the liver." | ( Toxicity of Tetrabromobisphenol A and Its Derivative in the Mouse Liver Following Oral Exposure at Environmentally Relevant Levels. Fu, J; Guo, H; Jiang, G; Li, D; Li, Z; Liu, Y; Luo, Q; Ma, J; Qu, G; Shi, J; Wang, Y; Wang, Z; Yang, X; Yao, L; Zhang, Q, 2021) | 1 |
" Although several experiments were performed in vitro and in vivo, human data are lacking, and thus, chronic toxic effects of TBBPA on humans are not well known, particularly in sensitive populations including pregnant women, newborns, children, and the elderly." | ( Toxic Effects of Tetrabromobisphenol A: Focus on Endocrine Disruption. Balci, A; Chao, MW; Erkekoglu, P; Oral, D, 2021) | 0.96 |
" Previous studies have shown that TBBPA and its derivative cause a lot of toxic effects." | ( Review of the environmental occurrence, analytical techniques, degradation and toxicity of TBBPA and its derivatives. Bin, H; Guanghua, M; Sunday, OE; Weiwei, F; Xian, Q; Xiangyang, W; Yao, C; Zhengjia, Z, 2022) | 0.72 |
" The toxic effects of TBBPA on three model aquatic organisms (Chlorella pyrenoidosa, Daphnia magna, and Danio rerio), in the absence and presence of DOM were investigated." | ( Dissolved organic matter heightens the toxicity of tetrabromobisphenol A to aquatic organisms. Jin, S; Luo, T; Song, L; Wang, DG; Wang, Z; Ye, N; Zhang, F, 2022) | 0.97 |
" These observed changes in developmental endpoints, hormonal level, and alteration in mRNA expression of component genes involved in neurodevelopmental pathways could be part of the possible mechanism of the observed toxic effects of TBBPA-DHEE exposure on zebrafish." | ( Transcriptomic sequencing reveals the potential molecular mechanism by which Tetrabromobisphenol A bis (2-hydroxyethyl ether) exposure exerts developmental neurotoxicity in developing zebrafish (Danio rerio). Che, J; Chen, Y; Ding, Y; Feng, W; Mao, G; Okeke, ES; Qian, X; Wu, X; Xu, H; Zeng, Z, 2022) | 0.95 |
" Therefore, in this study, we focused on the early stages of human liver development to explore the toxic effects of those HFRs, by using a human embryonic stem cell liver differentiation model." | ( Developmental toxicity assessments for TBBPA and its commonly used analogs with a human embryonic stem cell liver differentiation model. Faiola, F; Li, S; Yang, R; Yin, N; Zhang, S; Zhao, M, 2023) | 0.91 |
" This compound is persistent in the environment and accumulates in living organisms through the food chain, and is toxic to animals and human beings." | ( Apigenin attenuates tetrabromobisphenol A-induced cytotoxicity in neuronal SK-N-MC cells. Choi, EM; Chon, S; Park, SY; Suh, KS, 2023) | 1.23 |
" In this review, we aimed to summarize published scientific evidence on human biomonitoring, toxic effects and mode of action of TBBPA in humans." | ( A Review on Tetrabromobisphenol A: Human Biomonitoring, Toxicity, Detection and Treatment in the Environment. Adams, M; Issaka, E; Miao, B; Yakubu, S; Zhang, Y; Zhu, Q, 2023) | 1.29 |
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"A method of ultrasound-dispersive liquid-liquid microextraction (US-DLLME) combined with high-performance liquid chromatography/variable wavelength detection (HPLC-VWD) has been developed for rapid measuring tetrabromobisphenol A and its five derivatives in water." | ( Rapid determination of tetrabromobisphenol A and its main derivatives in aqueous samples by ultrasound-dispersive liquid-liquid microextraction combined with high-performance liquid chromatography. Du, X; Jiang, G; Liu, J; Liu, Q; Wang, X, 2013) | 0.89 |
Excerpt | Reference | Relevance |
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" The obtained results suggest absorption of TBBPA from the gastrointestinal tract and rapid metabolism of the absorbed TBBPA by conjugation resulting in a low systemic bioavailability of TBBPA." | ( Toxicokinetics of tetrabromobisphenol a in humans and rats after oral administration. Dekant, W; Schauer, UM; Völkel, W, 2006) | 0.67 |
" Although readily absorbed from the gut, systemic bioavailability of TBBPA is low (<2%)." | ( The effects of dose, route, and repeated dosing on the disposition and kinetics of tetrabromobisphenol A in male F-344 rats. Kuester, RK; Rodriguez, VP; Sipes, IG; Sólyom, AM, 2007) | 0.56 |
" However, nearly 50% of initial HBCDs recovered in mixed cabbage-radish treatments, which suggested that interspecific plant interactions might enhance the bioavailability of HBCDs." | ( Fate of tetrabromobisphenol A and hexabromocyclododecane brominated flame retardants in soil and uptake by plants. Li, Y; Wang, Y; Xie, X; Zhou, Q, 2011) | 0.8 |
" The flame retardants could not be measured in significant amounts in the brains, suggesting low bioavailability and/or rapid elimination/metabolism." | ( Effects of neonatal exposure to the flame retardant tetrabromobisphenol-A, aluminum diethylphosphinate or zinc stannate on long-term potentiation and synaptic protein levels in mice. Dingemans, MM; Hendriks, HS; Koolen, LA; Lee, I; Leonards, PE; Ramakers, GM; Viberg, H; Westerink, RH, 2015) | 0.42 |
"Ethical and technical difficulties inherent to studies in human tissues are impeding assessment of the dermal bioavailability of brominated flame retardants (BFRs)." | ( Evaluation of 3D-human skin equivalents for assessment of human dermal absorption of some brominated flame retardants. Abdallah, MA; Harrad, S; Pawar, G, 2015) | 0.42 |
" Subsequent key events in the AOP, including increased bioavailability of unconjugated estrogens in uterine tissue, would occur as a result of decreased sulfation, leading to a disruption in estrogen homeostasis, increased expression of estrogen responsive genes, cell proliferation, and hyperplasia." | ( A high dose mode of action for tetrabromobisphenol A-induced uterine adenocarcinomas in Wistar Han rats: A critical evaluation of key events in an adverse outcome pathway framework. Borghoff, SJ; Haws, LC; Rager, JE; Wikoff, DS, 2016) | 0.72 |
Class | Description |
---|---|
bromobisphenol | A bisphenol substituted by at least one bromo group and its derivatives. |
brominated flame retardant | Any organobromine compound that is used as a flame retardant. These chemicals are widely incorporated as additives in consumer products such as electronics, vehicles, polyurethane foams etc, to make them less flammable. |
[compound class information is derived from Chemical Entities of Biological Interest (ChEBI), Hastings J, Owen G, Dekker A, Ennis M, Kale N, Muthukrishnan V, Turner S, Swainston N, Mendes P, Steinbeck C. (2016). ChEBI in 2016: Improved services and an expanding collection of metabolites. Nucleic Acids Res] |
Protein | Taxonomy | Measurement | Average (µ) | Min (ref.) | Avg (ref.) | Max (ref.) | Bioassay(s) |
---|---|---|---|---|---|---|---|
Chain A, TYROSYL-DNA PHOSPHODIESTERASE | Homo sapiens (human) | Potency | 28.1838 | 0.0040 | 23.8416 | 100.0000 | AID485290 |
Chain A, HADH2 protein | Homo sapiens (human) | Potency | 15.3632 | 0.0251 | 20.2376 | 39.8107 | AID886; AID893 |
Chain B, HADH2 protein | Homo sapiens (human) | Potency | 15.3632 | 0.0251 | 20.2376 | 39.8107 | AID886; AID893 |
Chain A, JmjC domain-containing histone demethylation protein 3A | Homo sapiens (human) | Potency | 89.1251 | 0.6310 | 35.7641 | 100.0000 | AID504339 |
Chain A, ATP-DEPENDENT DNA HELICASE Q1 | Homo sapiens (human) | Potency | 22.3872 | 0.1259 | 19.1169 | 125.8920 | AID2549 |
Luciferase | Photinus pyralis (common eastern firefly) | Potency | 84.2603 | 0.0072 | 15.7588 | 89.3584 | AID1224835 |
interleukin 8 | Homo sapiens (human) | Potency | 74.9780 | 0.0473 | 49.4806 | 74.9780 | AID651758 |
acetylcholinesterase | Homo sapiens (human) | Potency | 70.9259 | 0.0025 | 41.7960 | 15,848.9004 | AID1347395; AID1347397; AID1347398 |
15-lipoxygenase, partial | Homo sapiens (human) | Potency | 9.1804 | 0.0126 | 10.6917 | 88.5700 | AID887 |
WRN | Homo sapiens (human) | Potency | 50.1187 | 0.1683 | 31.2583 | 100.0000 | AID651768 |
hypoxia-inducible factor 1 alpha subunit | Homo sapiens (human) | Potency | 54.9139 | 3.1890 | 29.8841 | 59.4836 | AID1224846; AID1224894 |
RAR-related orphan receptor gamma | Mus musculus (house mouse) | Potency | 57.2962 | 0.0060 | 38.0041 | 19,952.5996 | AID1159521; AID1159523 |
GLS protein | Homo sapiens (human) | Potency | 17.7828 | 0.3548 | 7.9355 | 39.8107 | AID624170 |
GLI family zinc finger 3 | Homo sapiens (human) | Potency | 49.6096 | 0.0007 | 14.5928 | 83.7951 | AID1259369; AID1259392 |
AR protein | Homo sapiens (human) | Potency | 54.6706 | 0.0002 | 21.2231 | 8,912.5098 | AID1259243; AID1259247; AID588516; AID743035; AID743036; AID743042; AID743054; AID743063 |
Smad3 | Homo sapiens (human) | Potency | 35.4813 | 0.0052 | 7.8098 | 29.0929 | AID588855 |
aldehyde dehydrogenase 1 family, member A1 | Homo sapiens (human) | Potency | 0.0238 | 0.0112 | 12.4002 | 100.0000 | AID1030 |
hypoxia-inducible factor 1, alpha subunit (basic helix-loop-helix transcription factor) | Homo sapiens (human) | Potency | 44.9647 | 0.0013 | 7.7625 | 44.6684 | AID2120 |
thyroid stimulating hormone receptor | Homo sapiens (human) | Potency | 35.7168 | 0.0013 | 18.0743 | 39.8107 | AID926; AID938 |
estrogen receptor 2 (ER beta) | Homo sapiens (human) | Potency | 11.1514 | 0.0006 | 57.9133 | 22,387.1992 | AID1259377; AID1259378 |
hypothetical protein, conserved | Trypanosoma brucei | Potency | 39.8107 | 0.2239 | 11.2451 | 35.4813 | AID624173 |
progesterone receptor | Homo sapiens (human) | Potency | 37.4442 | 0.0004 | 17.9460 | 75.1148 | AID1346784; AID1346795 |
glucocorticoid receptor [Homo sapiens] | Homo sapiens (human) | Potency | 52.9961 | 0.0002 | 14.3764 | 60.0339 | AID588533; AID720691; AID720692; AID720719 |
retinoic acid nuclear receptor alpha variant 1 | Homo sapiens (human) | Potency | 55.5083 | 0.0030 | 41.6115 | 22,387.1992 | AID1159552; AID1159555 |
retinoid X nuclear receptor alpha | Homo sapiens (human) | Potency | 26.8171 | 0.0008 | 17.5051 | 59.3239 | AID1159527; AID1159531 |
estrogen-related nuclear receptor alpha | Homo sapiens (human) | Potency | 62.9081 | 0.0015 | 30.6073 | 15,848.9004 | AID1224841; AID1224848; AID1224849; AID1259401; AID1259403 |
farnesoid X nuclear receptor | Homo sapiens (human) | Potency | 50.8273 | 0.3758 | 27.4851 | 61.6524 | AID588526; AID743217 |
pregnane X nuclear receptor | Homo sapiens (human) | Potency | 50.2865 | 0.0054 | 28.0263 | 1,258.9301 | AID1346982; AID720659 |
estrogen nuclear receptor alpha | Homo sapiens (human) | Potency | 43.7132 | 0.0002 | 29.3054 | 16,493.5996 | AID1259244; AID1259248; AID588513; AID588514; AID743069; AID743075; AID743077; AID743078; AID743079 |
glucocerebrosidase | Homo sapiens (human) | Potency | 11.2202 | 0.0126 | 8.1569 | 44.6684 | AID2101 |
bromodomain adjacent to zinc finger domain 2B | Homo sapiens (human) | Potency | 56.2341 | 0.7079 | 36.9043 | 89.1251 | AID504333 |
peroxisome proliferator-activated receptor delta | Homo sapiens (human) | Potency | 58.3195 | 0.0010 | 24.5048 | 61.6448 | AID743212; AID743215 |
peroxisome proliferator activated receptor gamma | Homo sapiens (human) | Potency | 20.0102 | 0.0010 | 19.4141 | 70.9645 | AID588536; AID588537; AID743094; AID743140; AID743191 |
vitamin D (1,25- dihydroxyvitamin D3) receptor | Homo sapiens (human) | Potency | 49.8233 | 0.0237 | 23.2282 | 63.5986 | AID588541; AID588543; AID743222; AID743223 |
cytochrome P450, family 19, subfamily A, polypeptide 1, isoform CRA_a | Homo sapiens (human) | Potency | 62.3710 | 0.0017 | 23.8393 | 78.1014 | AID743083 |
activating transcription factor 6 | Homo sapiens (human) | Potency | 58.9195 | 0.1434 | 27.6121 | 59.8106 | AID1159516; AID1159519 |
thyrotropin-releasing hormone receptor | Homo sapiens (human) | Potency | 34.7308 | 0.1549 | 17.8702 | 43.6557 | AID1346877; AID1346891 |
nuclear factor of kappa light polypeptide gene enhancer in B-cells 1 (p105), isoform CRA_a | Homo sapiens (human) | Potency | 53.8566 | 19.7391 | 45.9784 | 64.9432 | AID1159509 |
v-jun sarcoma virus 17 oncogene homolog (avian) | Homo sapiens (human) | Potency | 31.9626 | 0.0578 | 21.1097 | 61.2679 | AID1159526; AID1159528 |
Histone H2A.x | Cricetulus griseus (Chinese hamster) | Potency | 110.7973 | 0.0391 | 47.5451 | 146.8240 | AID1224845; AID1224896 |
Caspase-7 | Cricetulus griseus (Chinese hamster) | Potency | 51.1280 | 0.0067 | 23.4960 | 68.5896 | AID1346980 |
15-hydroxyprostaglandin dehydrogenase [NAD(+)] isoform 1 | Homo sapiens (human) | Potency | 10.0000 | 0.0018 | 15.6638 | 39.8107 | AID894 |
runt-related transcription factor 1 isoform AML1b | Homo sapiens (human) | Potency | 8.8659 | 0.0200 | 7.9858 | 39.8107 | AID504374; AID504375 |
thyroid hormone receptor beta isoform a | Homo sapiens (human) | Potency | 36.5327 | 0.0100 | 39.5371 | 1,122.0200 | AID588547 |
potassium voltage-gated channel subfamily H member 2 isoform d | Homo sapiens (human) | Potency | 39.8107 | 0.0178 | 9.6374 | 44.6684 | AID588834 |
caspase-3 | Cricetulus griseus (Chinese hamster) | Potency | 51.1280 | 0.0067 | 23.4960 | 68.5896 | AID1346980 |
thyroid hormone receptor beta isoform 2 | Rattus norvegicus (Norway rat) | Potency | 38.0081 | 0.0003 | 23.4451 | 159.6830 | AID743065; AID743067 |
heat shock protein beta-1 | Homo sapiens (human) | Potency | 46.2874 | 0.0420 | 27.3789 | 61.6448 | AID743210; AID743228 |
core-binding factor subunit beta isoform 2 | Homo sapiens (human) | Potency | 8.8659 | 0.0200 | 7.9858 | 39.8107 | AID504374; AID504375 |
flap endonuclease 1 | Homo sapiens (human) | Potency | 44.6684 | 0.1337 | 25.4129 | 89.1251 | AID588795 |
serine/threonine-protein kinase PLK1 | Homo sapiens (human) | Potency | 26.6795 | 0.1683 | 16.4040 | 67.0158 | AID720504 |
nuclear factor erythroid 2-related factor 2 isoform 1 | Homo sapiens (human) | Potency | 40.2978 | 0.0006 | 27.2152 | 1,122.0200 | AID651741; AID720636; AID743202; AID743219 |
DNA polymerase eta isoform 1 | Homo sapiens (human) | Potency | 89.1251 | 0.1000 | 28.9256 | 213.3130 | AID588591 |
DNA polymerase iota isoform a (long) | Homo sapiens (human) | Potency | 35.4813 | 0.0501 | 27.0736 | 89.1251 | AID588590 |
geminin | Homo sapiens (human) | Potency | 5.1735 | 0.0046 | 11.3741 | 33.4983 | AID624296 |
Vpr | Human immunodeficiency virus 1 | Potency | 56.2341 | 1.5849 | 19.6264 | 63.0957 | AID651644 |
cytochrome P450 3A4 isoform 1 | Homo sapiens (human) | Potency | 15.8489 | 0.0316 | 10.2792 | 39.8107 | AID884; AID885 |
histone acetyltransferase KAT2A isoform 1 | Homo sapiens (human) | Potency | 25.1189 | 0.2512 | 15.8432 | 39.8107 | AID504327 |
caspase-1 isoform alpha precursor | Homo sapiens (human) | Potency | 39.8107 | 0.0003 | 11.4484 | 31.6228 | AID900 |
lethal factor (plasmid) | Bacillus anthracis str. A2012 | Potency | 20.4839 | 0.0200 | 10.7869 | 31.6228 | AID912 |
Gamma-aminobutyric acid receptor subunit pi | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Polyunsaturated fatty acid lipoxygenase ALOX15B | Homo sapiens (human) | Potency | 20.4839 | 0.3162 | 12.7657 | 31.6228 | AID881 |
Voltage-dependent calcium channel gamma-2 subunit | Mus musculus (house mouse) | Potency | 68.3804 | 0.0015 | 57.7890 | 15,848.9004 | AID1259244 |
Rap guanine nucleotide exchange factor 3 | Homo sapiens (human) | Potency | 79.4328 | 6.3096 | 60.2008 | 112.2020 | AID720709 |
Cellular tumor antigen p53 | Homo sapiens (human) | Potency | 47.6258 | 0.0023 | 19.5956 | 74.0614 | AID651631; AID651743; AID720552 |
Gamma-aminobutyric acid receptor subunit beta-1 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit delta | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit gamma-2 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Glutamate receptor 2 | Rattus norvegicus (Norway rat) | Potency | 68.3804 | 0.0015 | 51.7393 | 15,848.9004 | AID1259244 |
Gamma-aminobutyric acid receptor subunit alpha-5 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit alpha-3 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit gamma-1 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit alpha-2 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit alpha-4 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit gamma-3 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit alpha-6 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Alpha-synuclein | Homo sapiens (human) | Potency | 8.9125 | 0.5623 | 9.3985 | 25.1189 | AID652106 |
Histamine H2 receptor | Cavia porcellus (domestic guinea pig) | Potency | 20.4839 | 0.0063 | 8.2350 | 39.8107 | AID881 |
Nuclear receptor ROR-gamma | Homo sapiens (human) | Potency | 35.5347 | 0.0266 | 22.4482 | 66.8242 | AID651802 |
Gamma-aminobutyric acid receptor subunit alpha-1 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit beta-3 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
Gamma-aminobutyric acid receptor subunit beta-2 | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
TAR DNA-binding protein 43 | Homo sapiens (human) | Potency | 22.3872 | 1.7783 | 16.2081 | 35.4813 | AID652104 |
Rap guanine nucleotide exchange factor 4 | Homo sapiens (human) | Potency | 35.4813 | 3.9811 | 46.7448 | 112.2020 | AID720708 |
GABA theta subunit | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
ATPase family AAA domain-containing protein 5 | Homo sapiens (human) | Potency | 57.8507 | 0.0119 | 17.9420 | 71.5630 | AID651632 |
Ataxin-2 | Homo sapiens (human) | Potency | 57.8507 | 0.0119 | 12.2221 | 68.7989 | AID651632 |
Gamma-aminobutyric acid receptor subunit epsilon | Rattus norvegicus (Norway rat) | Potency | 15.8489 | 1.0000 | 12.2248 | 31.6228 | AID885 |
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023] |
Protein | Taxonomy | Measurement | Average | Min (ref.) | Avg (ref.) | Max (ref.) | Bioassay(s) |
---|---|---|---|---|---|---|---|
Chain A, Peroxisome proliferator-activated receptor gamma | Homo sapiens (human) | IC50 (µMol) | 0.7000 | 0.7000 | 3.3500 | 6.0000 | AID977608 |
Chain A, Peroxisome proliferator-activated receptor gamma | Homo sapiens (human) | IC50 (µMol) | 0.7000 | 0.7000 | 3.3500 | 6.0000 | AID977608 |
Sarcoplasmic/endoplasmic reticulum calcium ATPase 1 | Oryctolagus cuniculus (rabbit) | IC50 (µMol) | 0.5000 | 0.0002 | 2.8167 | 9.0000 | AID1605047 |
Polyunsaturated fatty acid lipoxygenase ALOX15 | Homo sapiens (human) | IC50 (µMol) | 4.0000 | 0.0400 | 2.0998 | 10.0000 | AID241374 |
Polyunsaturated fatty acid lipoxygenase ALOX12 | Homo sapiens (human) | IC50 (µMol) | 10.0000 | 0.1000 | 2.4523 | 10.0000 | AID241245 |
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023] |
Protein | Taxonomy | Measurement | Average | Min (ref.) | Avg (ref.) | Max (ref.) | Bioassay(s) |
---|---|---|---|---|---|---|---|
Skn7p | Saccharomyces cerevisiae (brewer's yeast) | AbsAC40_uM | 1.2600 | 0.6600 | 5.2696 | 18.2300 | AID624258 |
HSP40, subfamily A [Plasmodium falciparum 3D7] | Plasmodium falciparum 3D7 | AbsAC1000_uM | 8.1300 | 0.1290 | 4.1169 | 11.3160 | AID540271 |
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023] |
Assay ID | Title | Year | Journal | Article |
---|---|---|---|---|
AID588501 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Lethal Factor Protease, MLPCN compound set | 2010 | Current protocols in cytometry, Oct, Volume: Chapter 13 | Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening. |
AID588501 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Lethal Factor Protease, MLPCN compound set | 2006 | Cytometry. Part A : the journal of the International Society for Analytical Cytology, May, Volume: 69, Issue:5 | Microsphere-based protease assays and screening application for lethal factor and factor Xa. |
AID588501 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Lethal Factor Protease, MLPCN compound set | 2010 | Assay and drug development technologies, Feb, Volume: 8, Issue:1 | High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors. |
AID588499 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set | 2010 | Current protocols in cytometry, Oct, Volume: Chapter 13 | Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening. |
AID588499 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set | 2006 | Cytometry. Part A : the journal of the International Society for Analytical Cytology, May, Volume: 69, Issue:5 | Microsphere-based protease assays and screening application for lethal factor and factor Xa. |
AID588499 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set | 2010 | Assay and drug development technologies, Feb, Volume: 8, Issue:1 | High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors. |
AID651635 | Viability Counterscreen for Primary qHTS for Inhibitors of ATXN expression | |||
AID588497 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set | 2010 | Current protocols in cytometry, Oct, Volume: Chapter 13 | Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening. |
AID588497 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set | 2006 | Cytometry. Part A : the journal of the International Society for Analytical Cytology, May, Volume: 69, Issue:5 | Microsphere-based protease assays and screening application for lethal factor and factor Xa. |
AID588497 | High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set | 2010 | Assay and drug development technologies, Feb, Volume: 8, Issue:1 | High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors. |
AID504812 | Inverse Agonists of the Thyroid Stimulating Hormone Receptor: HTS campaign | 2010 | Endocrinology, Jul, Volume: 151, Issue:7 | A small molecule inverse agonist for the human thyroid-stimulating hormone receptor. |
AID1745845 | Primary qHTS for Inhibitors of ATXN expression | |||
AID504810 | Antagonists of the Thyroid Stimulating Hormone Receptor: HTS campaign | 2010 | Endocrinology, Jul, Volume: 151, Issue:7 | A small molecule inverse agonist for the human thyroid-stimulating hormone receptor. |
AID1508627 | Counterscreen qHTS for small molecule stabilizers of the endoplasmic reticulum resident proteome: GLuc-NoTag assay | 2021 | Cell reports, 04-27, Volume: 35, Issue:4 | A target-agnostic screen identifies approved drugs to stabilize the endoplasmic reticulum-resident proteome. |
AID1508629 | Cell Viability qHTS for small molecule stabilizers of the endoplasmic reticulum resident proteome | 2021 | Cell reports, 04-27, Volume: 35, Issue:4 | A target-agnostic screen identifies approved drugs to stabilize the endoplasmic reticulum-resident proteome. |
AID1508628 | Confirmatory qHTS for small molecule stabilizers of the endoplasmic reticulum resident proteome: Secreted ER Calcium Modulated Protein (SERCaMP) assay | 2021 | Cell reports, 04-27, Volume: 35, Issue:4 | A target-agnostic screen identifies approved drugs to stabilize the endoplasmic reticulum-resident proteome. |
AID1605048 | Inhibition of porcine cerebellar microsomes SERCA2b by enzyme-coupled method | 2020 | Journal of medicinal chemistry, 03-12, Volume: 63, Issue:5 | Sarco/Endoplasmic Reticulum Calcium ATPase Inhibitors: Beyond Anticancer Perspective. |
AID274424 | Displacement of androgen fluormone from androgen receptor at 100 uM | 2006 | Journal of medicinal chemistry, Dec-14, Volume: 49, Issue:25 | Identification of the brominated flame retardant 1,2-dibromo-4-(1,2-dibromoethyl)cyclohexane as an androgen agonist. |
AID1605047 | Inhibition of rabbit skeletal muscle microsomes SERCA1a by enzyme-coupled method | 2020 | Journal of medicinal chemistry, 03-12, Volume: 63, Issue:5 | Sarco/Endoplasmic Reticulum Calcium ATPase Inhibitors: Beyond Anticancer Perspective. |
AID241036 | Inhibitory effect on soybean 15-lipoxygenase | 2004 | Journal of medicinal chemistry, Jul-29, Volume: 47, Issue:16 | Probing the activity differences of simple and complex brominated aryl compounds against 15-soybean, 15-human, and 12-human lipoxygenase. |
AID752865 | Inhibition of sarco/endoplasmic reticulum calcium ATPase in human GM08333 cells assessed as inhibition of calcium ion uptake at 50 uM measured for 1 min by Fura-2AM staining assay | 2013 | Bioorganic & medicinal chemistry, Jul-01, Volume: 21, Issue:13 | Structural requirements for inhibitory effects of bisphenols on the activity of the sarco/endoplasmic reticulum calcium ATPase. |
AID237340 | Calculated octanol-water partition coefficient (ClogP) | 2004 | Journal of medicinal chemistry, Jul-29, Volume: 47, Issue:16 | Probing the activity differences of simple and complex brominated aryl compounds against 15-soybean, 15-human, and 12-human lipoxygenase. |
AID274429 | Activity against human androgen receptor expressed in HepG2 cells assessed as renilla reporter gene activation in presence of 1 nM DHT at 1 uM after 40 hrs | 2006 | Journal of medicinal chemistry, Dec-14, Volume: 49, Issue:25 | Identification of the brominated flame retardant 1,2-dibromo-4-(1,2-dibromoethyl)cyclohexane as an androgen agonist. |
AID241245 | Inhibitory effect on human platelet 12-lipoxygenase | 2004 | Journal of medicinal chemistry, Jul-29, Volume: 47, Issue:16 | Probing the activity differences of simple and complex brominated aryl compounds against 15-soybean, 15-human, and 12-human lipoxygenase. |
AID752867 | Inhibition of rabbit skeletal muscle sarco/endoplasmic reticulum calcium ATPase assessed as inhibition of ATP hydrolysis by spectrophotometric analysis | 2013 | Bioorganic & medicinal chemistry, Jul-01, Volume: 21, Issue:13 | Structural requirements for inhibitory effects of bisphenols on the activity of the sarco/endoplasmic reticulum calcium ATPase. |
AID752864 | Drug uptake in human serum | 2013 | Bioorganic & medicinal chemistry, Jul-01, Volume: 21, Issue:13 | Structural requirements for inhibitory effects of bisphenols on the activity of the sarco/endoplasmic reticulum calcium ATPase. |
AID241374 | Inhibitory effect on human reticulocyte 15-lipoxygenase | 2004 | Journal of medicinal chemistry, Jul-29, Volume: 47, Issue:16 | Probing the activity differences of simple and complex brominated aryl compounds against 15-soybean, 15-human, and 12-human lipoxygenase. |
AID977608 | Experimentally measured binding affinity data (IC50) for protein-ligand complexes derived from PDB | 2011 | Environmental health perspectives, Sep, Volume: 119, Issue:9 | Peroxisome proliferator-activated receptor γ is a target for halogenated analogs of bisphenol A. |
[information is prepared from bioassay data collected from National Library of Medicine (NLM), extracted Dec-2023] |
Timeframe | Studies, This Drug (%) | All Drugs % |
---|---|---|
pre-1990 | 3 (0.41) | 18.7374 |
1990's | 0 (0.00) | 18.2507 |
2000's | 122 (16.85) | 29.6817 |
2010's | 414 (57.18) | 24.3611 |
2020's | 185 (25.55) | 2.80 |
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023] |
According to the monthly volume, diversity, and competition of internet searches for this compound, as well the volume and growth of publications, there is estimated to be strong demand-to-supply ratio for research on this compound.
| This Compound (48.11) All Compounds (24.57) |
Publication Type | This drug (%) | All Drugs (%) |
---|---|---|
Trials | 0 (0.00%) | 5.53% |
Reviews | 31 (4.25%) | 6.00% |
Case Studies | 0 (0.00%) | 4.05% |
Observational | 0 (0.00%) | 0.25% |
Other | 698 (95.75%) | 84.16% |
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023] |