Page last updated: 2024-11-04

dibutyl phthalate

Description Research Excerpts Clinical Trials Roles Classes Pathways Study Profile Bioassays Related Drugs Related Conditions Protein Interactions Research Growth Market Indicators

Description

Dibutyl phthalate (DBP) is a plasticizer, a substance added to plastics to increase their flexibility and durability. It is a synthetic compound produced by the reaction of phthalic anhydride with butanol. DBP has been widely used in a variety of applications, including PVC flooring, wall coverings, clothing, and toys. However, concerns about its potential health effects have led to its phasing out in many countries. DBP is known to be an endocrine disruptor, meaning it can interfere with the body's hormonal system. Exposure to DBP can occur through ingestion, inhalation, and skin contact. Studies have linked DBP exposure to various health problems, including reproductive abnormalities, developmental delays, and cancer. Due to these concerns, DBP has been restricted or banned in many countries. Its replacement with safer alternatives is an active area of research. The study of DBP is important to understand its potential risks and to develop safer alternatives for use in various products.'

6-((3-cyclobutyl-2,3,4,5-tetrahydro-1H-3-benzazepin-7-yl)oxy)-N-methyl-3-pyridinecarboxamide: GSK-189254 is the HCl salt; an H3 receptor antagonist; putative cognitive enhancer; structure in first source [Medical Subject Headings (MeSH), National Library of Medicine, extracted Dec-2023]

Dibutyl Phthalate: A plasticizer used in most plastics and found in water, air, soil, plants and animals. It may have some adverse effects with long-term exposure. [Medical Subject Headings (MeSH), National Library of Medicine, extracted Dec-2023]

dibutyl phthalate : A phthalate ester that is the diester obtained by the formal condensation of the carboxy groups of phthalic acid with two molecules of butan-1-ol. Although used extensively as a plasticiser, it is a ubiquitous environmental contaminant that poses a risk to humans. [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]

Cross-References

ID SourceID
PubMed CID9798547
CHEMBL ID517140
SCHEMBL ID169579
MeSH IDM0006258
PubMed CID3026
CHEMBL ID272485
CHEBI ID34687
SCHEMBL ID24051
MeSH IDM0006258

Synonyms (244)

Synonym
bdbm50247054
6-(3-cyclobutyl-2,3,4,5-tetrahydro-1h-benzo[d]azepin-7-yloxy)-n-methylnicotinamide
CHEMBL517140 ,
gsk189254
6-((3-cyclobutyl-2,3,4,5-tetrahydro-1h-3-benzazepin-7-yl)oxy)-n-methyl-3-pyridinecarboxamide
BCP9000737
gsk-189,254
unii-5t4tx6co53
5t4tx6co53 ,
gsk 189254a
3-pyridinecarboxamide, 6-((3-cyclobutyl-2,3,4,5-tetrahydro-1h-3-benzazepin-7-yl)oxy)-n-methyl-
gsk-189254a
720690-73-3
gsk-189254 free base
SCHEMBL169579
6-(3-cyclobutyl-2,3,4,5-tetrahydro-1h-benzo[d]azepin-7-yloxy)-n-methyl-nicotinamide
WROHEWWOCPRMIA-UHFFFAOYSA-N ,
CS-6206
HY-14111
gsk189254a
6-((3-cyclobutyl-2,3,4,5-tetrahydro-1h-benzo[d]azepin-7-yl)oxy)-n-methylnicotinamide
AKOS032944981
Q5514566
720690-73-3 (free base)
E77309
6-[(3-cyclobutyl-2,3,4,5-tetrahydro-1h-3-benzazepin-7-yl)oxy]-n-methylpyridine-3-carboxamide
gsk 189254a; gsk-189254a;gsk189254;gsk-189254;gsk 189254
BCP29549
6-[(3-cyclobutyl-1,2,4,5-tetrahydro-3-benzazepin-8-yl)oxy]-n-methylpyridine-3-carboxamide
gtpl10736
HMS3748C15
EX-A1905
MS-25443
DTXSID801005982
gsk189254gsk189254
6-[(3-cyclobutyl-1,2,4,5-tetrahydro-3-benzazepin-7-yl)oxy]-n-methylpyridine-3-carboxamide
VDB69073
A935062
AC-36239
EN300-36038
Z281777806
BIDD:ER0641
MLS002177802
smr000777923
BRD-K73477617-001-01-0
staflex dbp
84-74-2
elaol
di-n-butyl phthalate
dibutyl-o-phthalate
nsc-6370
px 104
genoplast b
celluflex dpb
hexaplas m/b
benzene-o-dicarboxylic acid, di-n-butyl ester
o-benzenedicarboxylic acid, dibutyl ester
dibutyl 1,2-benzenedicarboxylate
unimoll db
phthalic acid, dibutyl ester
wln: 4ovr bvo2
witcizer 300
n-butyl phthalate
dibutyl phthalate
palatinol c
nsc6370
butyl phthalate
1,2-benzenedicarboxylic acid, dibutyl ester
DIVK1C_006724
di-n-butylorthophthalate
SPECTRUM_001975
BSPBIO_002547
NCGC00090769-01
ai-3-00283
phthalate, di-n-butyl
nsc 6370
n-butylphthalate
dbp (ester)
ersoplast fda
kodaflex dbp
einecs 201-557-4
caswell no. 292
hatcol dbp
epa pesticide chemical code 028001
ccris 2676
benzene-o-dicarboxylic acid di-n-butyl ester
phthalate, dibutyl-
uniflex dbp
brn 1914064
di-n-butylester kyseliny ftalove [czech]
ergoplast fdb
rc plasticizer dbp
rcra waste number u069
rcra waste no. u069
hsdb 922
ortho-dibutyl phthalate
dibutyl phthalate, 99%
dibutyl phthalate, reagentplus(r), >=99%
NCGC00090769-02
NCGC00090769-03
KBIO1_001668
KBIO2_007668
KBIO2_005100
KBIOGR_001267
KBIO3_002047
KBIO2_002532
KBIOSS_002541
SPECPLUS_000628
SPECTRUM3_000874
SPECTRUM4_000714
SPECTRUM330086
di-n-butyl phthalate (dbup)
SPECTRUM5_002068
NCGC00090769-04
NCGC00090769-05
NCGC00090769-06
dibutylphthatlate
di n butyl phthalate
phthalate, dibutyl
phthalate, butyl
dibutyl-phthalate
HMS2091E09
hatco dbp
ruifeng vp 201
plasthall dbp
yh-1bd2
monocizer dbp
corflex 440
vp-201
CHEMBL272485 ,
dibutylphthalate
vestinol c
phthalic acid di-n-butyl ester
o-benzenedicarboxylic acid dibutyl ester
CHEBI:34687 ,
benzenedicarboxylic acid dibutyl ester
1,2-benzenedicarboxylic acid dibutyl ester
phthalic acid dibutyl ester
dibutyl benzene-1,2-dicarboxylate
dibutyl o-phthalate
dibutyl-1,2-benzenedicarboxylate
rapidcelltrade markp
P0292
NCGC00090769-07
NCGC00090769-09
NCGC00090769-08
AKOS005720807
ec 201-557-4
1,2-benzenedicarboxylic acid, 1,2-dibutyl ester
2286e5r2ke ,
di-n-butylester kyseliny ftalove
dibutyl phthalate [nf]
unii-2286e5r2ke
HMS3041E18
dtxsid2021781 ,
tox21_201729
tox21_300980
cas-84-74-2
dtxcid301781
NCGC00259278-01
NCGC00254882-01
BBL011532
nsc-755894
nsc755894
pharmakon1600-00330086
bdbm50371946
STL146650
benzenedicarboxylic acid, dibutyl ester
FT-0624680
EPITOPE ID:138714
nutyl phthalate
gtpl6295
dibutyl phthalate [mi]
dibutyl phthalate [usp-rs]
butyl phthalate [who-dd]
dibutyl phthalate [ep monograph]
dibutyl phthalate [inci]
dibutyl phthalate [hsdb]
dibutyl phthalate [mart.]
dibutyl phthalate [ii]
SCHEMBL24051
J-503795
dibutyl ester of 1,2-benzenedicarboxylic acid
uniplex 150
morflex 240
palatinol dbp
mfcd00009441
1,2-dibutyl benzene-1,2-dicarboxylate
CCG-230933
dibutyl phthalate, selectophore(tm)
dibutyl phthalate, pestanal(r), analytical standard
dibutyl phthalate, saj special grade, >=98.0%
dibutyl phthalate, certified reference material, tracecert(r)
dibutyl phthalate, united states pharmacopeia (usp) reference standard
dibutyl phthalate, >=99%
dibutyl phthalate, european pharmacopoeia (ep) reference standard
sr-05000001549
SR-05000001549-1
SR-05000001549-3
dibutyl phthalate, ar, >=99%
dibutyl phthalate, pharmaceutical secondary standard; certified reference material
dibutyl phthalate, lr, >=98%
phthalic acid, bis-butyl ester
dibutyll phthalate
bufa
dibutyl 1, 2-benzenedicarboxylate
dibutyl phthalate (dbp)
dibutyl 1,2-benzene-dicarboxylate
SBI-0052568.P002
CS-0013564
Z277540112
F0001-2134
BCP24796
Q415612
HY-Y0304
DB13716
BRD-K73477617-001-04-4
di(1-butyl) phthalate
S5377
EN300-77394
synolate md
dibutyl phthalate (ep monograph)
witicizer 300
induflex dbp
di(n-butyl) 1,2-benzenedicarboxylate
phthalsauredibutylester
dibutyl-1,2-benzene-dicarboxylate
usepa/opp pesticide code: 028001
ersoplast fda.
dibutyl phthalate (mart.)
phthalsaeure dibutylester
r!c. plasticizer dbp
ergoplast fob
1,2 benzenedicarboxylic acid, di-n-butyl ester
bisoflex dbp
dibutyl phthalate (ii)
bis-n-butyl phthalate
benzol-1,2-dicarbonsauredibutylester
hatcp dbp
sicol 140
dibutyl phthalate (usp-rs)
1,2 benzenedicarboxylic acid, bis(n-butyl) ester
mollan b
ftalato di n-butanolo

Research Excerpts

Overview

Dibutyl phthalate (DBP) is a phthalic acid ester (PAE) that has posed a health hazard to the organisms. It is a plasticizer widely used in daily production, which causes serious environmental pollution. At certain levels, it can be harmful to human health.

ExcerptReferenceRelevance
"Dibutyl phthalate (DBP) is a phthalic acid ester (PAE) that has posed a health hazard to the organisms. "( Dibutyl phthalate-induced oxidative stress and apoptosis in swine testis cells and therapy of naringenin via PTEN/PI3K/AKT signaling pathway.
Chen, H; Huang, X; Sun, X; Xu, S; Zhang, Y; Zou, M, 2022
)
3.61
"Dibutyl phthalate (DBP) is an environmental hormone disrupter. "( Reproductive toxicity of dibutyl phthalate adsorbed on carbon nanotubes in male Balb/C mice.
Ding, S; He, S; Qin, Y; Ye, X; Zhang, H; Zhou, T, 2022
)
2.47
"Dibutyl phthalate (DBP) is an endocrine disruptor, which causes male reproductive dysfunction in rodents. "( Preconception exposure to dibutyl phthalate (DBP) impairs spermatogenesis by activating NF-κB/COX-2/RANKL signaling in Sertoli cells.
Hua, S; Jiang, J; Liu, S; Shi, F; Wu, L; Xie, Z; Zhang, Y; Zhu, Y, 2022
)
2.46
"Dibutyl phthalate (DBP) is a plasticizer widely used in daily production, which causes serious environmental pollution, and damage to brain, liver, kidney, and lung by producing excessive reactive oxygen species (ROS) after entering the body. "( Dibutyl phthalate causes MC3T3-E1 cell damage by increasing ROS to promote the PINK1/Parkin-mediated mitophagy.
Cui, Y; Du, J; Huo, S; Li, B; Li, Y; Shao, B; Song, M; Wang, B, 2022
)
3.61
"Dibutyl phthalate (DBP) is a typical phthalate (PAEs). "( Dibutyl phthalate affects insulin synthesis and secretion by regulating the mitochondrial apoptotic pathway and oxidative stress in rat insulinoma cells.
Chen, B; Dong, R; Du, J; Gu, Y; Li, S; Liu, S; Liu, X; Qin, J; Yang, R; Yang, S; Zheng, J, 2023
)
3.8
"Dibutyl phthalate (DBP) is a typical plasticizer and is widely used in industrial manufacturing. "( Dibutyl phthalate causes heart damage by disrupting Ca
Du, J; Huo, S; Li, B; Li, Y; Song, M; Wang, Q; Zhang, J; Zhang, X, 2023
)
3.8
"Dibutyl phthalate (DBP) is a frequently detected farmland contaminant that is harmful to the environment and human health. "( Use of Bacillus-siamensis-inoculated biochar to decrease uptake of dibutyl phthalate in leafy vegetables.
Chen, X; Cheng, J; Feng, F; Long, L; Nabil El-Masry, G; Wan, Q; Wang, Q; Xu, W; Yan, H; Yu, X, 2020
)
2.24
"Dibutyl phthalate (DBP) is a ubiquitous environmental contaminant that at certain levels can be harmful to human health. "( Dibutyl phthalate-mediated oxidative stress induces splenic injury in mice and the attenuating effects of vitamin E and curcumin.
Ma, P; Wang, J; Wang, X; Wu, Y; Yan, B; Yan, X; Yang, W; Yang, Y; Ye, D; Zhang, Y, 2020
)
3.44
"Dibutyl phthalate (DBP) is a commonly used additive in plastic products, so it may potentially coexist with microplastics (MPs) in marine environment. "( Acute and chronic combined effect of polystyrene microplastics and dibutyl phthalate on the marine copepod Tigriopus japonicus.
Li, W; Li, Z; Liu, Y; Yang, K; Yi, X; Zhan, J; Zhou, H, 2020
)
2.24
"Dibutyl phthalate (DBP) is an environmental pollutant that can threaten human health. "( Combined genomic and transcriptomic analysis of the dibutyl phthalate metabolic pathway in Arthrobacter sp. ZJUTW.
Li, J; Linhardt, RJ; Liu, T; Qiu, L; Zhang, F; Zhong, W, 2020
)
2.25
"Dibutyl phthalate (DBP) is an environmental endocrine disruptor detected in water, soil, and other environmental media frequently. "( Paternal exposure to di-n-butyl-phthalate induced developmental toxicity in zebrafish (Danio rerio).
Ding, X; Hu, J; Li, W; Sun, B; Tian, F; Wang, Y; Xia, M; Xu, H; Yang, M; Yang, W, 2021
)
2.06
"Dibutyl phthalate is an endocrine disruptor used in a wide range of industrial and agriculture applications. "( Effects of Subacute Exposure of Dibutyl Phthalate on the Homeostatic Model Assessment, Thyroid Function, and Redox Status in Rats.
Khan, AR; Khan, S; Majeed, KA; Rehman, H; Saeed, AA; Tahir, MS; Yousaf, MS, 2021
)
2.35
"Dibutyl phthalate is an important phthalate ester extensively used in various products like plastics, adhesives, inks, pharmaceuticals, lacquers, varnishes, paper coatings, safety glasses, and cosmetics. "( Sub-chronic exposure to low concentration of dibutyl phthalate affects anthropometric parameters and markers of obesity in rats.
Majeed, KA; Rabbani, I; Rashid, MA; Tahir, SK; Ur Rehman, H; Yousaf, MS; Zaneb, H, 2017
)
2.16
"Dibutyl phthalate (DBP) is a plasticizer used for many consumer products including cosmetics. "( Dibutyl Phthalate Rather than Monobutyl Phthalate Facilitates Contact Hypersensitivity to Fluorescein Isothiocyanate in a Mouse Model.
Imai, Y; Kurohane, K; Ogawa, E; Sekiguchi, K; Tsutsumi, M, 2017
)
3.34
"Dibutyl phthalate (DBP) is a plasticizer that has male reproductive toxicity."( ZnSO
Ao, L; Cao, J; Cui, Z; Liu, J; Liu, T; Mo, M; Wang, X; Zhang, X, 2018
)
1.2
"Dibutyl phthalate (DBP) is a type of phthalate, found in high concentrations in indoor air, which appears to have a high inflammatory potential."( Dibutyl phthalate modulates phenotype of granulocytes in human blood in response to inflammatory stimuli.
Bølling, AK; Carlsten, C; Huff, RD; Maestre-Batlle, D; Pena, OM; Randhawa, A, 2018
)
2.64
"Dibutyl phthalate (DBP) is a plasticizer, whose presence in the environment as a pollutant has attained a great deal of attention due to its reported association with endocrine system disturbances on animals. "( Kinetics and pathway of biodegradation of dibutyl phthalate by Pleurotus ostreatus.
Ahuactzin-Pérez, M; García-Dávila, J; González-Pérez, M; Gutiérrez-Ruíz, MC; Sánchez, C; Santacruz-Juárez, E; Tlécuitl-Beristain, S, 2018
)
2.19
"Dibutyl phthalate (DBP) is a typical soil contaminant that is widely used as plasticizer in modern agricultural production. "( Dibutyl phthalate contamination remolded the fungal community in agro-environmental system.
Deng, Y; Duan, G; Jia, M; Jin, D; Kong, X; Liu, H; Wang, X; Zhang, F, 2019
)
3.4
"Dibutyl phthalate (DBP) is a phthalate ester used as a plasticizer, and solvent. "( Use of the Adverse Outcome Pathway (AOP) framework to evaluate species concordance and human relevance of Dibutyl phthalate (DBP)-induced male reproductive toxicity.
Arzuaga, X; Hotchkiss, AK; Radke, EG; Walker, T; Yost, EE, 2020
)
2.21
"Dibutyl phthalate (DBP) is a commonly used plasticizer and additive to adhesives, printing inks and nail polishes. "( A dibutyl phthalate sensor based on a nanofiber polyaniline coated quartz crystal monitor.
Ding, P; Hu, R; Li, G; Luo, Z; Ma, X; Wang, Y; Zhang, J, 2013
)
2.55
"Dibutyl phthalate (DBP) is a peroxisome proliferator which can lead to germ cell loss from Sertoli cells. "( Inhibition of PPARα attenuates vimentin phosphorylation on Ser-83 and collapse of vimentin filaments during exposure of rat Sertoli cells in vitro to DBP.
Ao, L; Cao, J; Cui, Z; Liu, J; Liu, W; Tan, L; Yang, H; Zhang, X, 2014
)
1.85
"Dibutyl phthalate (DBP) is a ubiquitous contaminant in the marine environment, and relatively little is known about the toxicological mechanisms of this compound at the metabolite level. "( Metabolomics-based approach for assessing the toxicity mechanisms of dibutyl phthalate to abalone (Haliotis diversicolor supertexta).
Cai, Z; Chen, B; Zhou, J, 2015
)
2.09
"Dibutyl phthalate (DBP) is a widely used plasticizer that has been shown to induce germ cell apoptosis-related testicular atrophy and cause reproductive toxicity. "( The p-eIF2α/ATF4 pathway links endoplasmic reticulum stress to autophagy following the production of reactive oxygen species in mouse spermatocyte-derived cells exposed to dibutyl phthalate.
Ao, L; Cao, J; Gao, J; Ling, X; Liu, K; Wang, Z; Zhang, G; Zou, P, 2016
)
2.07
"Dibutyl phthalate (DBP) is a widely used synthetic phthalic diester and monobutyl phthalate (MBP) is its main metabolite. "( Comparison of the Effects of Dibutyl and Monobutyl Phthalates on the Steroidogenesis of Rat Immature Leydig Cells.
Chen, X; Ge, RS; Hu, G; Li, L; Li, X; Lian, QQ; Wang, M; Wang, S; Xu, R; Zhu, Q, 2016
)
1.88

Effects

Dibutyl phthalate has a certain inhibitory effect on the activity, diversity, and heterogeneity of microorganisms in soil. It has a wide variety of manufacturing applications and is used in both commercial and consumer products.

Dibutyl phthalate (DBP) has been widely detected in municipal and industrial wastewater. It can indirectly inhibit pollutant removals, especially degradation of dissolved organic matter (DOM) DBP has been illegally used in beverages and directly affects the human health.

ExcerptReferenceRelevance
"Dibutyl phthalate has a certain inhibitory effect on the activity, diversity, and heterogeneity of microorganisms in soil."( Effect of dibutyl phthalate on microbial function diversity and enzyme activity in wheat rhizosphere and non-rhizosphere soils.
Dong, Y; Gao, M; Song, Z; Zhang, Z, 2020
)
1.68
"Dibutyl phthalate (DBP) has a wide variety of manufacturing applications and is used in both commercial and consumer products. "( Subungual penetration of dibutyl phthalate in human fingernails.
Jackson, EM, 2008
)
2.09
"The dibutyl phthalate (DBP) has been detected in fetuses and infants and can cause damage to the reproductive system in adulthood, but the exact mechanism remains unclear. "( DNA methylation-mediated inhibition of MGARP is involved in impaired progeny testosterone synthesis in mice exposed to DBP in utero.
Feng, X; Jiang, Y; Li, H; Liu, M; Sun, X; Wang, H; Xu, X; Yu, J; Yu, Y; Zhang, J, 2023
)
1.47
"Dibutyl phthalate (DBP) has been widely detected in municipal and industrial wastewater, which could indirectly inhibit pollutant removals, especially degradation of dissolved organic matter (DOM). "( Insight into suppression of dibutyl phthalate on DOM removal during municipal sewage treatment using fluorescence spectroscopy with PARAFAC and moving-window 2D-COS.
Liu, D; Song, Y; Wang, J; Yu, H, 2023
)
2.65
"Dibutyl phthalate has been illegally used in beverages and directly affects the human health. "( Elucidation of binding mechanism of dibutyl phthalate on bovine serum albumin by spectroscopic analysis and molecular docking method.
Dong, J; Kong, J; Li, L; Li, R; Wang, L; Zhao, P, 2020
)
2.28
"Dibutyl phthalate has a certain inhibitory effect on the activity, diversity, and heterogeneity of microorganisms in soil."( Effect of dibutyl phthalate on microbial function diversity and enzyme activity in wheat rhizosphere and non-rhizosphere soils.
Dong, Y; Gao, M; Song, Z; Zhang, Z, 2020
)
1.68
"Dibutyl phthalate (DBP) has significant male reproductive toxicity, and the Sertoli cells are the target cells of DBP. "( Role of PI3K/AKT/mTOR signaling pathway in DBP-induced apoptosis of testicular sertoli cells in vitro.
Jin, S; Li, H; Wang, H; Wang, J; Zhang, J, 2017
)
1.9
"Dibutyl phthalate (DBP) has been extensively used as a plasticizer in many daily products, which is highly toxic to human, notably affecting the reproductive and developmental function. "( An ultra-sensitive monoclonal antibody-based enzyme-linked immunosobent assay for dibutyl phthalate in human urinary.
Ahmed, S; Chen, S; Lei, Y; Zhang, D; Zhou, L, 2016
)
2.1
"Dibutyl phthalate (DBP) has a wide variety of manufacturing applications and is used in both commercial and consumer products. "( Subungual penetration of dibutyl phthalate in human fingernails.
Jackson, EM, 2008
)
2.09

Actions

ExcerptReferenceRelevance
"dibutyl phthalate) produce testicular dysgenesis."( Impact of environmental pollutants on the male: effects on germ cell differentiation.
Veeramachaneni, DN, 2008
)
1.07

Toxicity

Dibutyl phthalate (DBP) is one of the most commonly used and toxicphthalate esters. It has a variety of harmful effects on aquatic animals. The objective of this study was to determine the adverse effects of MBuP, a major metabolite of DBP.

ExcerptReferenceRelevance
" These data indicate that the dibutyl phthalate separation technique offers the advantage of monitoring only viable hepatocytes for changes in membrane integrity or metabolic performance during a toxic chemical insult."( Mechanism of chemical-induced toxicity. I. Use of a rapid centrifugation technique for the separation of viable and nonviable hepatocytes.
Brown, MK; Fariss, MW; Reed, DJ; Schmitz, JA, 1985
)
0.56
"n-Butyl benzyl phthalate (BBP) and di-n-butyl phthalate (DBP) were evaluated and compared for their developmental toxic potential."( Comparative developmental toxicity of n-butyl benzyl phthalate and di-n-butyl phthalate in rats.
Amano, H; Ema, M; Kurosaka, R; Ogawa, Y, 1995
)
0.29
" In conclusion, this study showed that DBP is a reproductive/developmental toxicant in Sprague-Dawley rats exposed both as adults and during development; it also indicates that the adverse reproductive/developmental effects of DBP on the second generation were greater than on the first generation."( Reproductive toxicity of di-n-butylphthalate in a continuous breeding protocol in Sprague-Dawley rats.
Barnes, LH; Chapin, RE; Gulati, DK; Li, LH; Wine, RN, 1997
)
0.3
" It was concluded that DBP administered during the second half of pregnancy produced adverse effects on the reproductive development in male fetuses."( Further evaluation of developmental toxicity of di-n-butyl phthalate following administration during late pregnancy in rats.
Ema, M; Kawashima, K; Miyawaki, E, 1998
)
0.3
"The objective of this study was to determine the susceptible days for the adverse effects of di-n-butyl phthalate (DBP) on development of reproductive system in male offspring following maternal administration on successive 3-day period during late pregnancy."( Critical period for adverse effects on development of reproductive system in male offspring of rats given di-n-butyl phthalate during late pregnancy.
Ema, M; Kawashima, K; Miyawaki, E, 2000
)
0.31
"The objective of this study was to determine the adverse effects of monobutyl phthalate (MBuP), a major metabolite of dibutyl phthalate (DBP), on development of the reproductive system in offspring following maternal administration during late pregnancy, and to assess the role of MBuP in the antiandrogenic effects of DBP."( Adverse effects on development of the reproductive system in male offspring of rats given monobutyl phthalate, a metabolite of dibutyl phthalate, during late pregnancy.
Ema, M; Miyawaki, E,
)
0.55
" However, MBuP elicited a toxic effect at higher concentrations than DBP."( Effects of dibutyl phthalate and monobutyl phthalate on cytotoxicity and differentiation in cultured rat embryonic limb bud cells; protection by antioxidants.
Choi, YW; Han, SY; Kim, SH; Kim, SS; Kwack, SJ; Kwon, O; Lee, MK; Park, KL; Sohn, KH, 2002
)
0.7
" In the whole embryo culture assay, ESBO (83, 250 and 750 microg/ml) exerted no toxic effect on growth and development of the embryo, whereas phthalate esters (1, 10, 100 microg/ml for DEHP, 10, 100, 1,000 microg/ml for BBP and DBP) inhibited growth and development dose dependently."( Comparison of embryotoxicity of ESBO and phthalate esters using an in vitro battery system.
Hee Kim, S; Hee Sohn, K; Ho Kim, B; Jun Kwack, S; Lea Park, K; Seek Rhee, G; Sun Kim, S, 2002
)
0.31
" The NOAEL (no observable adverse effect level) for developmental toxicity of DBP was established based on pup body weight and male reproductive lesions at 50 mg/kg BW/day."( Reproductive and developmental toxicity in F1 Sprague-Dawley male rats exposed to di-n-butyl phthalate in utero and during lactation and determination of its NOAEL.
Chen, B; Jiang, X; Zhang, Y, 2004
)
0.32
" The adverse effects of DBP on testes of F(1) male rats in different developmental period (PND14, 21 and 70) were observed by anatomy and pathological methods."( [Reversibility of adverse effects of di-n-butyl phthalate on F1 generation rat testes].
Chen, BH; Jiang, XZ; Zhang, YH, 2004
)
0.32
"These results suggest that adverse effects of DBP on young rat testes should be reversibility."( [Reversibility of adverse effects of di-n-butyl phthalate on F1 generation rat testes].
Chen, BH; Jiang, XZ; Zhang, YH, 2004
)
0.32
" Butyl methyl phthalate, the major product of degradation by the esterase, was an oxidative toxic hazard that damaged protein synthesis."( Enzymatic degradation of dibutyl phthalate and toxicity of its degradation products.
Kim, YH; Lee, J, 2005
)
0.63
" In conclusion, DIBP administered by gavage is embryotoxic and teratogenic, and affects the developing male reproductive tract, at maternal toxic doses."( Developmental toxic effects of diisobutyl phthalate, the methyl-branched analogue of di-n-butyl phthalate, administered by gavage to rats.
Gallissot, F; Sabaté, JP; Saillenfait, AM, 2006
)
0.33
" Overall, the dose level of DBP in the present study produced a few adverse effects on the neurobehavioral parameters, and it may alter cognitive abilities of the male rodent."( Neurobehavioral toxicity study of dibutyl phthalate on rats following in utero and lactational exposure.
Li, T; Li, Y; Shi, N; Zhuang, M, 2009
)
0.63
" Monobutyl phthalate, the developmentally toxic metabolite of DBP, and its glucuronide conjugate were found in maternal and fetal plasma, amniotic fluid, and maternal urine."( Reproductive toxicity and pharmacokinetics of di-n-butyl phthalate (DBP) following dietary exposure of pregnant rats.
Dorman, DC; Gaido, KW; Hensley, JB; Lehmann, KP; Ross, SM; Sochaski, MA; Struve, MF; Willson, GA, 2009
)
0.35
"The purposes of this review are to (1) evaluate human and experimental evidence for adverse effects on reproduction and development in humans, produced by exposure to phthalates, and (2) identify knowledge gaps as for future studies."( Reproductive and developmental toxicity of phthalates.
Bergman, A; Eriksen, GS; Gutleb, AC; Lyche, JL; Murk, AJ; Ropstad, E; Saunders, M; Skaare, JU, 2009
)
0.35
" The differences observed in the cytotoxicity of these compounds, along with other properties, may assist the dental practitioners in the selection of reline materials with improved service life performance and low risk of adverse reactions in patients who wear relined dentures."( Cytotoxicity of monomers, plasticizer and degradation by-products released from dental hard chairside reline resins.
Carlos, IZ; Chaves, CA; Giampaolo, ET; Machado, AL; Pavarina, AC; Vergani, CE, 2010
)
0.36
" Significant adverse effects were observed on the reproductive system, including decreased sperm count, increased production of abnormal sperm, changes in serum testosterone levels and irregular arrangements of the seminiferous epithelium."( The combined toxicity of dibutyl phthalate and benzo(a)pyrene on the reproductive system of male Sprague Dawley rats in vivo.
An, H; Ao, L; Cao, J; Chen, X; Liu, W; Sun, L; Wang, Y; Zhou, Z, 2011
)
0.67
"To study the toxic effects of phthalate esters on the aquatic creatures, carps were exposed to dibutyl phthalate (DBP) and di-2-ethylhexyl phthalate (DEHP) of six different concentrations for 96 h-LC50 measurements."( Toxicity of phthalate esters exposure to carp (Cyprinus carpio) and antioxidant response by biomarker.
Gao, Y; Qi, M; Zhao, X, 2014
)
0.62
" Our data indicate an urgent need for LS waste management guidelines and for adequate information regarding toxic outcomes that may arise from human exposure."( Luminescent threat: toxicity of light stick attractors used in pelagic fishery.
Bagattini, R; Barretto, FP; Bechara, EJ; da Silva, AL; de Arruda Campos, IP; de Medeiros, MH; de Moura, RA; de Oliveira, AA; de Oliveira, TF; Di Mascio, P; Loureiro, AP, 2014
)
0.4
" cordifolia fruit and it indicates that the LD50 value is higher than 1000 mg/kg body weight."( Toxicity study of dibutyl phthalate of Rubia cordifolia fruits: in vivo and in silico analysis.
Akella, S; Anantharaman, A; Fulzele, DP; Ganesh, J; Hemachandran, H; Priya, RR; Rajasekaran, C; Siva, R, 2016
)
0.77
" In particular, the diethyl (DEP), di-n-propyl (DnPP), and di-n-butyl (DBP) phthalates were found to exert detrimental effects in both mammalian and non-mammalian studies, with toxic effects varying according to alkyl chain length."( Assessing differences in toxicity and teratogenicity of three phthalates, Diethyl phthalate, Di-n-propyl phthalate, and Di-n-butyl phthalate, using Xenopus laevis embryos.
Burnham, N; Gardner, ST; Lester, R; Onkst, PE; Perygin, DH; Rayburn, J; Wood, AT, 2016
)
0.43
" In conclusion oral DBP administration for 14 days may cause some neurobehavioral adverse effects in mice."( Determination of dibutyl phthalate neurobehavioral toxicity in mice.
Faizi, M; Farzanehfar, V; Kobarfard, F; Naderi, N, 2016
)
0.77
" Antagonism effects were found in the joint toxicity of Cu(II) combined with DBP or DEHP using the toxic unit method."( Joint Toxicity of Two Phthalates with Waterborne Copper to Daphnia magna and Photobacterium phosphoreum.
Huang, B; Li, D; Yang, Y, 2016
)
0.43
" This study demonstrated the toxic and apoptotic effects of DBP in mouse neocortical neurons in primary cultures."( Dibutyl Phthalate (DBP)-Induced Apoptosis and Neurotoxicity are Mediated via the Aryl Hydrocarbon Receptor (AhR) but not by Estrogen Receptor Alpha (ERα), Estrogen Receptor Beta (ERβ), or Peroxisome Proliferator-Activated Receptor Gamma (PPARγ) in Mouse C
Kajta, M; Szychowski, KA; Wnuk, A; Wójtowicz, AK, 2017
)
1.9
"5 weeks were exposed to DBP by gavage for 8 weeks, 3 days per week to doses of 1/16 LD50 or 1/4 LD50 each time."( Three generation study of reproductive and developmental toxicity following exposure of pubescent F0 male mice to di-n-butyl phthalate.
Dobrzynska, MM; Gajowik, A; Tyrkiel, EJ, 2017
)
0.46
" In the present study, we investigated the toxicity of DBP in zebrafish embryo development, especially adverse effects on cardiac development."( Exposure to DBP induces the toxicity in early development and adverse effects on cardiac development in zebrafish (Danio rerio).
Li, Y; Sun, G, 2019
)
0.51
" The Adverse Outcome Pathway (AOP) framework was used to evaluate the available evidence for DBP-induced toxicity to the male reproductive system."( Use of the Adverse Outcome Pathway (AOP) framework to evaluate species concordance and human relevance of Dibutyl phthalate (DBP)-induced male reproductive toxicity.
Arzuaga, X; Hotchkiss, AK; Radke, EG; Walker, T; Yost, EE, 2020
)
0.77
" The overall findings revealed that Pb and DBP co-exposure greatly influenced the developmental nervous system and accompanied with synergistic toxic effect."( Evaluation of combined developmental neurological toxicity of di (n-butyl) phthalates and lead using immature mice.
Chen, H; Ding, Y; Feng, W; Liu, H; Mao, G; Wu, X; Yang, L; Zhang, W; Zhao, T, 2020
)
0.56
" Here we endeavored to address for the first time whether MPs could transport and release phthalate esters (PAEs) into mouse gut and the consequential toxic effects."( Microplastics release phthalate esters and cause aggravated adverse effects in the mouse gut.
Deng, Y; Huang, Y; Lemos, B; Ren, H; Shen, R; Wang, M; Yan, Z; Zhang, Y, 2020
)
0.56
" This study investigated the toxic effects of small polystyrene (SPS, 100-1000 nm) and large polystyrene (LPS, >10,000 nm) microplastics, on lettuce under di-butyl phthalate (DBP) stress."( Effect of polystyrene on di-butyl phthalate (DBP) bioavailability and DBP-induced phytotoxicity in lettuce.
Dong, Y; Gao, M; Liu, Y; Song, Z; Wang, C; Wang, S; Xu, Y, 2021
)
0.62
" Additionally, lower doses cause more adverse effects than the highest dose, which is an important fact because of the widespread environmental exposure to DBP."( The overview of current evidence on the reproductive toxicity of dibutyl phthalate.
Czerczak, S; Czubacka, E; Kupczewska-Dobecka, MM, 2021
)
0.86
" When co-exposed, 20 μg NPs/mL increased viabilities of cells exposed to either DBP or DEHP and the modulation of toxic potency of DEHP was greater than that of DBP, while the 200 μg NPs/mL resulted in lesser viability of cells."( Combined cytotoxicity of polystyrene nanoplastics and phthalate esters on human lung epithelial A549 cells and its mechanism.
Giesy, JP; Liu, R; Shi, Q; Tang, J; Wang, L, 2021
)
0.62
"Dibutyl phthalate (DBP) is one of the most commonly used and toxic phthalate esters and has a variety of harmful effects on aquatic animals."( Accumulation, detoxification, and toxicity of dibutyl phthalate in the swimming crab.
He, Y; Li, R; Lin, W; Mu, C; Shi, C; Wang, C; Ye, Y, 2022
)
2.42
"To comprehensively understand the toxic risks of phthalates to aquatic ecosystems, we examined the acute toxicity of di-(2-ethylhexyl) phthalate (DEHP) and di-butyl phthalate (DBP) on multiple trophic models, including algae (Chlorella vulgaris), Daphnia magna and fish (Danio rerio, Pseudorasbora parva)."( Integrated toxicity assessment of DEHP and DBP toward aquatic ecosystem based on multiple trophic model assays.
Huang, Y; Li, Y; Liu, J; Mu, X; Pang, S; Shen, G; Wang, C; Yuan, L, 2022
)
0.72
" Overall, the findings of this study suggested that PR can degrade DBP in liquid fermentation without generating toxic byproducts."( Biodegradation of dibutyl phthalate in liquid fermentation by endophytic Penicillium species and the toxicity evaluation of the by-product.
Choi, HB; Naveen, KV; Sathiyaseelan, A; Wang, MH; Zhang, X, 2023
)
1.24
" Here we show that the toxic effects of single and combined exposure to DBP (0."( Multi-walled carbon nanotubes enhance the toxicity effects of dibutyl phthalate on early life stages of zebrafish (Danio rerio): Research in physiological, biochemical and molecular aspects.
Chen, H; Li, Y; Liang, H; Ren, B; Zhao, T; Zhao, Y, 2023
)
1.15

Pharmacokinetics

ExcerptReferenceRelevance
" This study provides direct pharmacokinetic analysis for MBP and MBP-G in pregnant rats during fetal male reproductive development, and indicates that future pharmacokinetic or toxicology studies can reliably utilize oral dosing with DBP."( Pharmacokinetics of monobutylphthalate, the active metabolite of di-n-butylphthalate, in pregnant rats.
Borghoff, SJ; Kremer, JJ; Parkinson, HD; Williams, CC, 2005
)
0.33
" The pharmacokinetic results demonstrate that DBP appeared to have a two-compartment model in the rats; the area under concentration versus time (AUC) was 57."( Pharmacokinetics of dibutyl phthalate (DBP) in the rat determined by UPLC-MS/MS.
Chang, LW; Hou, ML; Tsai, TH, 2013
)
0.71
" Data from this study were used to structure and calibrate simple pharmacokinetic (PK) models for these two phthalates, which predict urine and blood metabolite concentrations with a given phthalate intake scenario (times and quantities)."( Development and application of simple pharmacokinetic models to study human exposure to di-n-butyl phthalate (DnBP) and diisobutyl phthalate (DiBP).
Koch, HM; Lorber, M, 2013
)
0.39
" The data for DnBP were used in a modeling exercise linking dose models for inhalation and transdermal permeation with a simple pharmacokinetic model that predicted timing and mass of metabolite excretions."( Linking a dermal permeation and an inhalation model to a simple pharmacokinetic model to study airborne exposure to di(n-butyl) phthalate.
Bekö, G; Clausen, G; Gong, M; Koch, HM; Lorber, M; Morrison, G; Salthammer, T; Schripp, T; Toftum, J; Weschler, CJ, 2017
)
0.46
" To evaluate the human risk of DBP, forward and reverse dosimetry was conducted using in silico simplified physiologically based pharmacokinetic (PBPK) modeling based on in vivo experimental pharmacokinetic data in humanized-liver mice (HL-mice) obtained after an oral dose of 100 mg/kg."( Steady-State Human Pharmacokinetics of Monobutyl Phthalate Predicted by Physiologically Based Pharmacokinetic Modeling Using Single-Dose Data from Humanized-Liver Mice Orally Administered with Dibutyl Phthalate.
Kamiya, Y; Miura, T; Mizuno, S; Murayama, N; Shimizu, M; Suemizu, H; Uehara, S; Yamazaki, H; Yoshizawa, M, 2019
)
0.7

Compound-Compound Interactions

A highly sensitive and selective. molecularly imprinted (MIP) sensor combined with magnetic molecularly. imprinted solid phase extraction (MMISPE) was developed for the determination of dibutyl phthalate (DBP) in complex matrixes.

ExcerptReferenceRelevance
"To evaluate the toxic and carcinogenic potential of ozone alone or in combination with 4-(N-methyl-N-nitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and/or dibutyl phthalate (DBP)."( Toxicity and carcinogenicity of ozone in combination with 4-(N-methyl-N-nitrosamino)-1-(3-pyridyl)-1-butanone and dibutyl phthalate in B6C3F1 mice for 16 and 32 weeks.
Cho, MY; Kim, MY, 2009
)
0.76
" Oviductal carcinomas were observed in female mice exposed to ozone or DBP alone for 16 weeks and ozone in combination with NNK and DBP for 32 weeks."( Toxicity and carcinogenicity of ozone in combination with 4-(N-methyl-N-nitrosamino)-1-(3-pyridyl)-1-butanone and dibutyl phthalate in B6C3F1 mice for 16 and 32 weeks.
Cho, MY; Kim, MY, 2009
)
0.56
"A highly sensitive and selective molecularly imprinted (MIP) sensor combined with magnetic molecularly imprinted solid phase extraction (MMISPE) was developed for the determination of dibutyl phthalate (DBP) in complex matrixes."( A sensitive and selective molecularly imprinted sensor combined with magnetic molecularly imprinted solid phase extraction for determination of dibutyl phthalate.
Cai, R; Chen, H; Luo, L; Zhang, Z, 2013
)
0.78
" Our results point to a low risk of increased genotoxic effects of AgNP when used in combination with aluminium salts, butylparaben or di-n-butylphthalate in consumer products."( Genotoxic effects in transformed and non-transformed human breast cell lines after exposure to silver nanoparticles in combination with aluminium chloride, butylparaben or di-n-butylphthalate.
Cieślak, M; Domeradzka-Gajda, K; Grobelny, J; Kozajda, A; Puchowicz, D; Ranoszek-Soliwoda, K; Roszak, J; Smok-Pieniążek, A; Spryszyńska, S; Stępnik, M; Tomaszewska, E, 2017
)
0.46

Bioavailability

Dibutyl phthalate (DBP) is one of the most ubiquitous EDCs because of its bioavailability in water, soil, and atmosphere. DBP and di-(2-ethylhcxyl) phthalATE (DEHP) polluted fluvo-aquic soils.

ExcerptReferenceRelevance
" As the esters became more lipophilic and less hydrophilic, the rate of absorption was reduced."( In vitro absorption of some o-phthalate diesters through human and rat skin.
Dugard, PH; Ramsey, JD; Rhodes, C; Scott, RC, 1987
)
0.27
" When DBP-amended soil had been aged for three months, decreases in bioavailability were observed but the effect varied tremendously between different organisms."( Degradation of di-butyl-phthalate by soil bacteria.
Chao, WL; Kuo, YL; Lin, CM; Shiung, II, 2006
)
0.33
" The results highlight the importance of shunt pathways when evaluating the bioavailability of skin sensitizers."( The pilosebaceous unit--a phthalate-induced pathway to skin sensitization.
Ericson, MB; Jonsson, CA; Karlberg, AT; Simonsson, C; Stenfeldt, AL, 2012
)
0.38
", coarse and fine sands) with higher bioavailability displayed higher bioconcentration factors compared to finer soil fractions (i."( Variation in accumulation, transport, and distribution of phthalic acid esters (PAEs) in soil columns grown with low- and high-PAE accumulating rice cultivars.
Cai, QY; Chen, XH; Chen, XX; Li, X; Li, YW; Mo, CH; Wong, MH; Wu, Y; Zhu, TK, 2018
)
0.48
" The results indicated that the changes in DBP degradation percentage were related to both DBP bioavailability and the total relative abundances of dominant DBP-degraders."( Impact of microplastic addition on degradation of dibutyl phthalate in offshore sediments.
Chi, J; Zhang, H; Zhao, D, 2021
)
0.87
"0% biochar (BC) or iron-manganese oxide modified biochar (FMBC) additions on the biomass, enzyme activity, and grain quality of wheat plants grown in dibutyl phthalate (DBP) and di-(2-ethylhcxyl) phthalate (DEHP) polluted fluvo-aquic soils, as well as the bioavailability of DBP and DEHP."( Fe-Mn oxide modified biochar decreases phthalate uptake and improves grain quality of wheat grown in phthalate-contaminated fluvo-aquic soil.
Chang, X; Gao, M; Song, Z; Xu, Y, 2021
)
0.82
" Thus, it is important to explore strategies to reduce the bioavailability of phthalate esters."( Effects of Fe-Mn oxide-modified biochar composite applications on phthalate esters (PAEs) accumulation in wheat grains and grain quality under PAEs-polluted brown soil.
Chang, X; Gao, M; Guo, Z; Song, Z; Xu, Y, 2021
)
0.62
"Awareness of risks posed by widespread presence of nanoplastics (NPs) and bioavailability and potential to interact with organic pollutants has been increasing."( Combined cytotoxicity of polystyrene nanoplastics and phthalate esters on human lung epithelial A549 cells and its mechanism.
Giesy, JP; Liu, R; Shi, Q; Tang, J; Wang, L, 2021
)
0.62
" The results clearly indicated that PS reduced the bioavailability of DBP while causing a decrease in the photosynthetic parameters as well as the total chorophyll content compared to DBP alone by affecting the crystalline structure of the water-soluble chlorophyll protein."( Polystyrene particles combined with di-butyl phthalate cause significant decrease in photosynthesis and red lettuce quality.
Dong, Y; Gao, M; Liu, Y; Song, Z, 2021
)
0.62
", Tenax, hydroxypropyl[β]cyclodextrin (HPCD), n-butanol and low-molecular-weight-organic-acids (LMWOA), for predicting the bioavailability and phytotoxicity of soil phthalic acid esters to the green vegetable Shanghaiqing (SHQ)."( Comparison of Different Chemical Extraction Methods for Predicting the Bioavailability and Phytotoxicity of Soil PAEs to Green Vegetables (Brassica Rapa Var. Chinensis).
Chen, X; Cheng, J; Tian, L; Wan, Q; Yu, X, 2022
)
0.72
" Unarguably, dibutyl phthalate (DBP) is one of the most ubiquitous EDCs because of its bioavailability in water, soil, and atmosphere."( Enhanced removal of dibutyl phthalate in a laccase-mediator system: Optimized process parameters, kinetics, and environmental impact.
Adebajo, SO; Bankole, PO; Mulla, SI; Omoni, VT; Tennison-Omovoh, CA, 2023
)
1.6

Dosage Studied

ExcerptRelevanceReference
" These agents can increase wakefulness (W) in cats and rodents following acute administration, but their effects after repeat dosing have not been reported previously."( Differential effects of acute and repeat dosing with the H3 antagonist GSK189254 on the sleep-wake cycle and narcoleptic episodes in Ox-/- mice.
Anaclet, C; Brown, SH; Buda, C; Feng, JQ; Franco, P; Guidon, G; Guo, RX; Lin, JS; Medhurst, AD; Parmentier, R; Roberts, JC; Sastre, JP; Upton, N; Zhang, M, 2009
)
0.35
" After twice daily dosing for 8 days, the effect of GSK189254 (10 mg x kg(-1)) on W in both Ox+/+ and Ox-/- mice was significantly reduced, while the effect on narcoleptic episodes in Ox-/- mice was significantly increased."( Differential effects of acute and repeat dosing with the H3 antagonist GSK189254 on the sleep-wake cycle and narcoleptic episodes in Ox-/- mice.
Anaclet, C; Brown, SH; Buda, C; Feng, JQ; Franco, P; Guidon, G; Guo, RX; Lin, JS; Medhurst, AD; Parmentier, R; Roberts, JC; Sastre, JP; Upton, N; Zhang, M, 2009
)
0.35
" Moreover, the differential effects observed on W and narcoleptic episodes following repeat dosing could have important implications in clinical studies."( Differential effects of acute and repeat dosing with the H3 antagonist GSK189254 on the sleep-wake cycle and narcoleptic episodes in Ox-/- mice.
Anaclet, C; Brown, SH; Buda, C; Feng, JQ; Franco, P; Guidon, G; Guo, RX; Lin, JS; Medhurst, AD; Parmentier, R; Roberts, JC; Sastre, JP; Upton, N; Zhang, M, 2009
)
0.35
" Additional data on plasma pharmacokinetics after oral dosing and the plasma free fraction gave a corresponding estimate of the free concentration of GSK189254 required to occupy 50% of the available receptor sites (EC(50)) (0."( Evaluation of 11C-GSK189254 as a novel radioligand for the H3 receptor in humans using PET.
Ashworth, S; Comley, RA; Cunningham, VJ; Gee, AD; Gunn, RN; Lai, RY; Laruelle, M; Plisson, C; Rabiner, EA; Wilson, AA, 2010
)
0.36
" These binding characteristics and the pharmacokinetic profile of AZD5213 indicate that high daytime and low night-time H3RO could be achieved following once daily oral dosing of AZD5213."( AZD5213: a novel histamine H3 receptor antagonist permitting high daytime and low nocturnal H3 receptor occupancy, a PET study in human subjects.
Boström, E; Halldin, C; Jostell, KG; Jucaite, A; Nyberg, S; Segerdahl, M; Stenkrona, P; Takano, A, 2013
)
0.39
" Indeed, histamine elicited a sigmoid dose-response curve for IP3 production, shifted to the right by chlorpheniramine maleate, and elicited a double bell-shaped curve for cAMP production, partially suppressed by the selective H2R, H3R and H4R antagonists when each added alone, and completely ablated when combined together."( Histamine receptor expression in human renal tubules: a comparative pharmacological evaluation.
Camussi, G; Chazot, PL; Grange, C; Lanzi, C; Moggio, A; Pini, A; Rosa, AC; Veglia, E, 2015
)
0.42
" MBP is incorporated into the lumen at a maximum rate between 1 and 3 h after dosing with DBP."( Mechanisms of testicular atrophy induced by di-n-butyl phthalate in rats. Part 3. Changes in the activity of some enzymes in the Sertoli and germ cells, and in the levels of metal ions.
Fukuoka, M; Tanaka, A; Zhou, Y, 1990
)
0.28
" In our studies rats were dosed from weaning through puberty , gestation, and lactation."( The development of a protocol to assess reproductive effects of toxicants in the rat.
Cooper, R; Ferrell, J; Goldman, J; Gray, LE; Laskey, J; Linder, R; Ostby, J; Rehnberg, G; Sigmon, R, 1988
)
0.27
" The liver microsomal metabolism of n-hexane increased to about the same extent at all dosage levels."( Phthalate esters: effects of orally administered dibutylphthalate on cytochrome P-450 mediated metabolism in rat liver and lung.
Nilsen, OG; Walseth, F, 1986
)
0.27
" Both male and female CD-1 mice were dosed for 7 days prior to and during a 98-day cohabitation period."( Reproductive effects of four phthalic acid esters in the mouse.
Chapin, RE; Lamb, JC; Lawton, AD; Reel, JR; Teague, J, 1987
)
0.27
" Long-term dosing studies indicating reduced fertility in the rat suggested a maternal effect of the compound."( Dibutyl phthalate: maternal effects versus fetotoxicity.
Cummings, AM; Gray, LE, 1987
)
1.72
" Peak blood levels of 14C occurred 2 hr after dosing in both groups of rats."( The effect of intestinal esterase inhibition on the in vivo absorption and toxicity of Di-n-butyl phthalate.
Carter, DE; Earnest, DL; White, RD, 1983
)
0.27
"0% DBP in the diet were selected, and this dosing design yielded average daily DBP intakes of 52, 256, and 509 mg/kg for males and 80, 385, and 794 mg/kg for females, respectively."( Reproductive toxicity of di-n-butylphthalate in a continuous breeding protocol in Sprague-Dawley rats.
Barnes, LH; Chapin, RE; Gulati, DK; Li, LH; Wine, RN, 1997
)
0.3
" Significant increases in the incidences of fetuses with skeletal malformations, of fetuses with skeletal and internal malformations and of fetuses with external and skeletal malformations were noted after a single dosing of DBP on day 8, on day 9 and on day 15, respectively."( Developmental effects of di-n-butyl phthalate after a single administration in rats.
Ema, M; Harazono, A; Miyawaki, E; Ogawa, Y,
)
0.13
" Maternal body weights throughout the dosing period were comparable in all groups."( Male reproductive tract malformations in rats following gestational and lactational exposure to Di(n-butyl) phthalate: an antiandrogenic mechanism?
Cattley, RC; Foster, PM; Mylchreest, E, 1998
)
0.3
"The nature of products of contamination intake were investigated in cattle dosed with [14C]di-n-butylphthalate (DBP)."( Analysis of di-n-butylphthalate biotransformation in cattle by liquid chromatography/ion trap mass spectrometry/mass spectrometry.
Coldham, NG; Dave, M; Sauer, MJ, 1998
)
0.3
" Male offsprings display a higher incidence of epididymal and testicular lesions than generally seen with flutamide, P, or V even at high dosage levels."( Administration of potentially antiandrogenic pesticides (procymidone, linuron, iprodione, chlozolinate, p,p'-DDE, and ketoconazole) and toxic substances (dibutyl- and diethylhexyl phthalate, PCB 169, and ethane dimethane sulphonate) during sexual differen
Cooper, RL; Gray, LE; Lambright, C; Mann, P; Ostby, J; Price, M; Wolf, C,
)
0.13
" In a study conducted at CIIT, the majority of these adverse changes could be reproduced over a similar dose range, but with a much shorter dosing regimen covering a critical window of development (gestation days 12-20)."( Effects of di-n-butyl phthalate (DBP) on male reproductive development in the rat: implications for human risk assessment.
Cattley, RC; Foster, PM; Mylchreest, E, 2000
)
0.31
" Since previous, limited dose-response studies with DBP that reported alterations in male reproductive development and function failed to establish a NOAEL (no-observed-adverse-effect level), an extensive dose-response study was conducted."( Dose-dependent alterations in androgen-regulated male reproductive development in rats exposed to Di(n-butyl) phthalate during late gestation.
Cattley, RC; Foster, PM; Mylchreest, E; Wallace, DG, 2000
)
0.31
" These concentrations are far less than the toxic dosage reported so far, so that CAPD is unlikely to contaminate patients seriously."( Endocrine-disrupting chemicals in CAPD dialysate and effluent.
Kakiya, Y; Kishimoto, T; Naganuma, T; Okada, C; Sugimura, K; Sugimura, T, 2001
)
0.31
" Adjuvant effect was accepted to be present if a statistical increase in antibody production occurred in a test group as compared to an ovalbumin control group together with the fulfillment of dose-response relationships."( Adjuvant effect of di-n-butyl-, di-n-octyl-, di-iso-nonyl- and di-iso-decyl phthalate in a subcutaneous injection model using BALB/c mice.
Larsen, ST; Lund, RM; Nielsen, GD; Poulsen, OM; Thygesen, P, 2002
)
0.31
" As the animals were only dosed in utero, these findings indicate that DBP can initiate fetal testicular and epididymal changes that may not manifest as clear malformations until adulthood."( Pathogenesis of male reproductive tract lesions from gestation through adulthood following in utero exposure to Di(n-butyl) phthalate.
Barlow, NJ; Foster, PM,
)
0.13
" In another experiment, pregnant dams were treated with DBP until gd 19, with the start of DBP treatment moved 1 d later into gestation for each treatment group, with the final group dosed only on gd 19."( Di(n-butyl) phthalate impairs cholesterol transport and steroidogenesis in the fetal rat testis through a rapid and reversible mechanism.
Gaido, KW; Ross, SM; Thompson, CJ, 2004
)
0.32
" To determine the dose-response relationship for the effect of DBP on steroidogenesis in fetal rat testes, pregnant Sprague-Dawley rats received corn oil (vehicle control) or DBP (0."( Dose-dependent alterations in gene expression and testosterone synthesis in the fetal testes of male rats exposed to di (n-butyl) phthalate.
Foster, PM; Gaido, KW; Lehmann, KP; Phillips, S; Sar, M, 2004
)
0.32
" DBP dissolved in peanut oil was administered by gavage at dosage of 0, 250, 500, 1,000 mg/(kg."( [Effects of di-butyl phthalate on sperm motility and oxidative stress in rats].
Chen, J; He, J; Liu, R; Song, L; Wang, X; Wang, Y; Zhu, Z, 2004
)
0.32
"01), while the testis organ body weight ratios were lower at dosage of 1,000 mg/(kg."( [Effects of di-butyl phthalate on sperm motility and oxidative stress in rats].
Chen, J; He, J; Liu, R; Song, L; Wang, X; Wang, Y; Zhu, Z, 2004
)
0.32
" Pregnant Sprague-Dawley rats were orally dosed with DBP at levels of 10, 50, or 500 mg/kg/day from gestation days 12 to 19; maternal and fetal liver samples were collected on day 19 for analyses."( Di-n-butyl phthalate activates constitutive androstane receptor and pregnane X receptor and enhances the expression of steroid-metabolizing enzymes in the liver of rat fetuses.
Bartolucci-Page, E; Gaido, KW; Hoffman, HB; Kirwan, SE; Laughter, A; Wyde, ME; Yan, B; You, L; Zhang, F, 2005
)
0.33
"Timed-pregnant Sprague-Dawley rats were dosed with DBP at 500 mg/kg/day on gestation day (GD) 14 and 15, 15 and 16, 16 and 17, 17 and 18, 18 and 19, or 19 and 20 (GD 0=plug day)."( Critical window of male reproductive tract development in rats following gestational exposure to di-n-butyl phthalate.
Carruthers, CM; Foster, PM, 2005
)
0.33
") dosing with MBP."( Pharmacokinetics of monobutylphthalate, the active metabolite of di-n-butylphthalate, in pregnant rats.
Borghoff, SJ; Kremer, JJ; Parkinson, HD; Williams, CC, 2005
)
0.33
" The growth and morphology of Bok choy showed a significant dose-response relationship upon treatment with DBP in a hydroponic culture medium."( Effects of endocrine disruptor di-n-butyl phthalate on the growth of Bok choy (Brassica rapa subsp. chinensis).
Liao, CS; Wang, YS; Yen, JH, 2006
)
0.33
" Key impact factors such as pH, temperature, ionic strength, ozone dosage and initial DBP concentration were investigated."( Removal of a type of endocrine disruptors--di-n-butyl phthalate from water by ozonation.
Li, HY; Liu, HJ; Qu, JH, 2006
)
0.33
" With exposed dose increasing, the serum testosterone (T) levels of male rats inversely decreased, and in the same dosage group the serum T levels of hypospadiac rats were significantly lower than the levels of nonhypospadiac counterparts."( Study on developmental abnormalities in hypospadiac male rats induced by maternal exposure to di-n-butyl phthalate (DBP).
Jiang, J; Ma, L; Wang, X; Yuan, L; Zhang, W, 2007
)
0.34
" Pregnant rats and neonatal male marmosets were dosed with 500 mg/kg/day DBP or MBP."( Effects of monobutyl and di(n-butyl) phthalate in vitro on steroidogenesis and Leydig cell aggregation in fetal testis explants from the rat: comparison with effects in vivo in the fetal rat and neonatal marmoset and in vitro in the human.
Anderson, RA; Bayne, R; Coutts, S; Greig, I; Hallmark, N; Mahood, IK; McKinnell, C; Morris, K; Scott, H; Sharpe, RM; Walker, M, 2007
)
0.34
" In the equal effect dosage joint treatment of PP and BP, uterus proliferation effects were observed at the doses of 1 and 1/2 LOEL, but the effect was not observed at the doses of 1/4 LOEL."( [Enhancement of di-n-butyl phthalate on the estrogenic activities of esters of p-hydroxybenzoic acid].
Chang, B; Ge, J; Liang, Y, 2007
)
0.34
" We characterized the dose-response effects of six individual phthalates (BBP, DBP, DEHP, diethyl phthalate [DEP], diisobutyl phthalate [DiBP], and dipentyl phthalate [DPP]) on gestation day (GD) 18 testicular testosterone production following exposure of Sprague-Dawley rats on GD 8-18."( A mixture of five phthalate esters inhibits fetal testicular testosterone production in the sprague-dawley rat in a cumulative, dose-additive manner.
Blystone, CR; Furr, J; Gray, LE; Hotchkiss, AK; Howdeshell, KL; Lambright, CR; Rider, CV; Wilson, VS, 2008
)
0.35
" In order to gain a better understanding of the effect of repeated dosing on maternal and fetal metabolism and distribution, pregnant Sprague-Dawley rats were given a single dose of 500 mg/kg DBP on GD 19 or daily doses of 50, 100, and 500 mg/(kg day) from GD 12 to 19 via corn oil gavage."( Kinetics of selected di-n-butyl phthalate metabolites and fetal testosterone following repeated and single administration in pregnant rats.
Andersen, ME; Borghoff, SJ; Campbell, JL; Clewell, RA; Kremer, JJ; Sochaski, MA; Williams, CC, 2009
)
0.35
" Rats were dosed during pregnancy with antiandrogens singly or in pairs at dosage levels equivalent to about one half of the ED50 for hypospadias or epididymal agenesis."( Cumulative effects of in utero administration of mixtures of "antiandrogens" on male rat reproductive development.
Furr, JR; Gray, LE; Hotchkiss, AK; Howdeshell, KL; Lambright, CR; Rider, CV; Wilson, VS, 2009
)
0.35
" In all binary mixture studies, rats were dosed during pregnancy with chemicals, singly or in pairs, at dosage levels equivalent to approximately one-half of the ED50 for hypospadias or epididymal agenesis."( Cumulative effects of in utero administration of mixtures of reproductive toxicants that disrupt common target tissues via diverse mechanisms of toxicity.
Furr, JR; Gray, LE; Rider, CV; Wilson, VS, 2010
)
0.36
"Metabolite profiles (metabolomics) of plasma samples of Wistar rats dosed with di(2-ethylhexyl)phthalate (DEHP - 3000ppm) and dibutylphthalate (DBP - 150, 1000 and 7000ppm) were individually determined in 28 days dietary studies."( The individual and combined metabolite profiles (metabolomics) of dibutylphthalate and di(2-ethylhexyl)phthalate following a 28-day dietary exposure in rats.
Coelho-Palermo Cunha, G; Fabian, E; Herold, M; Kamp, H; Krennrich, G; Leibold, E; Looser, R; Mellert, W; Prokoudine, A; Strauss, V; van Ravenzwaay, B; Walk, T; Wiemer, J, 2010
)
0.36
" The control group and 4 DiBP groups, group I, II, III and IV, were given DiBP in corn oil by gavages at the dosage of 0, 50, 250, 500 and 1000 mg/kg respectively."( [Effect of diisobutyl phthalate on antioxidase activity and DNA damage in mice].
Feng, Y; Ma, N; Xu, H; Zhang, W, 2010
)
0.36
" The exercise focused on qualitative evaluation, based on a lack of available dose-response data, of the DBP toxicogenomic data set to postulate modes and mechanisms of action for the male reproductive developmental outcomes, which occur in the lower dose range."( Use of genomic data in risk assessment case study: II. Evaluation of the dibutyl phthalate toxicogenomic data set.
Androulakis, IP; Euling, SY; Gaido, KW; Hester, S; Ierapetritou, MG; Keshava, C; Keshava, N; Kim, AS; Ovacik, MA; Sen, B; White, LD; Wilson, VS, 2013
)
0.62
"The knowledge on the dose-response relationships between cumulative phthalate exposure and reproductive hormones in human are lacking."( Associations between hazard indices of di-n-butylphthalate and di-2-ethylhexylphthalate exposure and serum reproductive hormone levels among occupationally exposed and unexposed Chinese men.
Feng, Y; Hanaoka, T; Hara, K; Ichiba, M; Kishi, R; Na, J; Nakadate, T; Pan, G; Wang, P; Yamano, Y; Yin, H; Yu, L; Zhang, S, 2011
)
0.37
" Two parameters such as sodium hydroxide (NaOH) dosage and sonication time were considered by the central composite design (CCD) program to investigate the effect on the degradation of phthalate acid esters (PAEs) and solubilization of soluble chemical oxygen demand (SCOD)."( Sono-alkalization pretreatment of sewage sludge containing phthalate acid esters.
Lin, JG; Ma, YS, 2011
)
0.37
"In a published controlled dosing experiment, a single individual consumed 5mg each of labeled di-n-butyl phthalate (DnBP) and diisobutyl phthalate (DiBP) on separate occasions and tracked metabolites in his blood and urine over 48h."( Development and application of simple pharmacokinetic models to study human exposure to di-n-butyl phthalate (DnBP) and diisobutyl phthalate (DiBP).
Koch, HM; Lorber, M, 2013
)
0.39
" Catalyst dosage of 10 mg L(-1) led to approximately 25% of increase in DBP (initial concentration 2 mg L(-1)) removal in 60 min as compared with ozone alone, and when catalyst dosage increased to 100 mg L(-1), the DBP removal was further improved by 46%."( Heterogeneous catalytic ozonation of dibutyl phthalate in aqueous solution in the presence of iron-loaded activated carbon.
Cui, C; Huang, Y; Li, L; Pan, D; Zhang, D, 2015
)
0.69
" Therefore, long-term exposure to phthalate esters affected development and function of the primate testis in a time and dosage dependent manner."( Phthalate esters affect maturation and function of primate testis tissue ectopically grafted in mice.
Alpaugh, W; Avelar, GF; Bondareva, A; Conley, A; Coyle, KM; Dobrinski, I; França, LR; Meyers, S; Modelski, M; Rodriguez-Sosa, JR; Tang, L; Wynne-Edwards, K, 2014
)
0.4
" A dose-response relationship existed between DNA damage and total soil DBP levels."( Evaluation of DNA damage and antioxidant system induced by di-n-butyl phthalates exposure in earthworms (Eisenia fetida).
Du, L; Li, G; Li, Y; Liu, M; Yin, S; Zhang, X; Zhao, J, 2015
)
0.42
" The dose-response curves obtained were verified using the Weibull fitting function."( Eco-toxicological bioassay of atmospheric fine particulate matter (PM2.5) with Photobacterium Phosphoreum T3.
Shi, C; Wang, W; Yan, Y; Yang, Y; Zhou, B, 2016
)
0.43
", one week) based on suggested consumption dosage and phthalate concentrations."( Occurrence of phthalate esters in over-the-counter medicines from China and its implications for human exposure.
Guo, Y; Jia, LL; Leung, KS; Lou, XY; Zeng, EY, 2017
)
0.46
" Pregnant CD-1 dams were orally dosed with vehicle (tocopherol-stripped corn oil) or a phthalate mixture (20 and 200 µg/kg/d, 200 and 500 mg/kg/d) daily from gestational day 10 to birth."( Exposure to an Environmentally Relevant Phthalate Mixture Causes Transgenerational Effects on Female Reproduction in Mice.
Flaws, JA; Gao, L; Zhou, C, 2017
)
0.46
" Six to seven males from each dosage group were sacrificed at 4, 8 and 12 weeks after the start of exposure for examination of sperm count and quality."( Three generation study of reproductive and developmental toxicity following exposure of pubescent F0 male mice to di-n-butyl phthalate.
Dobrzynska, MM; Gajowik, A; Tyrkiel, EJ, 2017
)
0.46
" In conclusion, we have developed a reliable image analysis method that can be used to facilitate dose-response studies for the reproducible induction of MNGs by in utero phthalate exposure."( Validation of an automated counting procedure for phthalate-induced testicular multinucleated germ cells.
Bai, CY; Boekelheide, K; Conley, JM; Gray, LE; Lambright, C; Spade, DJ, 2018
)
0.48
" The results indicated that there was a competitive interaction between As(III) and DBP removal, and 40 mg/kg of Mn(II) dosage and 20%-30% soil moisture content were recommended for optimal and simultaneous removal of As(III) and DBP."( Simultaneous remediation of As(III) and dibutyl phthalate (DBP) in soil by a manganese-oxidizing bacterium and its mechanisms.
Duo, J; He, Z; Li, Z; Pan, X; Wei, Z; Zhang, Q, 2019
)
0.78
" For statistical purposes, the PS is defined as a single endpoint and one dose-response analysis is conducted, rather than conducting multiple analyses on each individual endpoint."( Ordinal dose-response modeling approach for the phthalate syndrome.
Blessinger, TD; Cai, C; Euling, SY; Hogan, KA; Klinefelter, G; Saillenfait, AM; Wang, L, 2020
)
0.56
"To improve dose-response modeling approaches for the PS and other syndromes of effects by accounting for differing severity levels among the endpoints."( Ordinal dose-response modeling approach for the phthalate syndrome.
Blessinger, TD; Cai, C; Euling, SY; Hogan, KA; Klinefelter, G; Saillenfait, AM; Wang, L, 2020
)
0.56
"Ordinal dose-response modeling was performed on PS data from a published study of diisobutyl phthalate (DIBP) gestational exposure to male Sprague-Dawley rats."( Ordinal dose-response modeling approach for the phthalate syndrome.
Blessinger, TD; Cai, C; Euling, SY; Hogan, KA; Klinefelter, G; Saillenfait, AM; Wang, L, 2020
)
0.56
"The ordinal dose-response modeling method accounts for severity differences among dichotomous PS endpoints, can be expanded in the future to include more severity levels, and can be used in both single and cumulative phthalate risk assessments."( Ordinal dose-response modeling approach for the phthalate syndrome.
Blessinger, TD; Cai, C; Euling, SY; Hogan, KA; Klinefelter, G; Saillenfait, AM; Wang, L, 2020
)
0.56
" Exposure to these chemicals (100-1000 μM) can significantly reduce the viability of H295R cells in a dose-response manner, and these plasticizers and their metabolites that migrated into oily foods at high temperatures (0."( Effects of fast food packaging plasticizers and their metabolites on steroid hormone synthesis in H295R cells.
Bai, J; Duan, C; Fang, Y; Gao, Z; Li, Z; Liang, J; Peng, H; Sun, J; Wang, Q, 2020
)
0.56
" A dose-response of auxin (IAA) was observed after a 2 d exposure."( Effects of dibutyl phthalate contamination on physiology, phytohormone homeostasis, rhizospheric and endophytic bacterial communities of Brassica rapa var. chinensis.
Cheng, J; Ge, J; Li, QX; Li, Y; Yu, X, 2020
)
0.95
" Pre-pubertal quail (n = 25) 4 weeks post-hatching were dosed orally with 10, 50, 200 and 400 mg DBP/kg/d, for 30 days and control birds were administered corn-oil only (n = 5 per group)."( Dose-related morphological changes in the epididymal region of sexually active adult male Japanese quail treated with di-n-butyl phthalate (DBP) commencing during the pre-pubertal stage.
Botha, CJ; Ibrahim, MIA; Williams, J, 2021
)
0.62
" The birds were randomly divided into five dosage groups at the age of 4 weeks."( Structural observations on spermatogenic cells of Japanese quail (Coturnix coturnix japonica) pre-pubertally exposed to dibutyl phthalate: A light and transmission electron microscopy study.
Ibrahim, MIA; Mahdy, MAA; McGaw, LJ; Molele, RA; Zakariah, M, 2022
)
0.93
" Rats were orally dosed from gestation days 14-18 with dilutions of PFQ and DBP at 0%, 12."( In Utero Exposure to a Mixture of the Perfluoroalkyl-Isopropyl Pesticide Pyrifluquinazon With Dibutyl Phthalate Cumulatively Disrupts Male Rat Reproductive Development via Different Mechanisms of Action.
Conley, JM; Furr, JR; Gray, LE; Lambright, CS, 2022
)
0.94
" Together, our findings suggest that DBP at present dosage may potentiate LPO generation and Sertoli cell immaturity via downregulation of Sox9 and disruption of the Pou4f1-Prnd gene network in post-meiotic germ cells without visible changes in spermatogenesis or testosterone level."( Phthalate plasticizer decreases the prion-like protein doppel essential for structural integrity and function of spermatozoa.
Gye, MC; Lee, JH; Park, SH; Ryou, C, 2022
)
0.72
[information is derived through text-mining from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Roles (5)

RoleDescription
environmental contaminantAny minor or unwanted substance introduced into the environment that can have undesired effects.
teratogenic agentA role played by a chemical compound in biological systems with adverse consequences in embryo developments, leading to birth defects, embryo death or altered development, growth retardation and functional defect.
plasticiserAny compound that is used as an additive to increase the plasticity or fluidity of a substance, particularly but not exclusively to synthetic polymers.
metaboliteAny intermediate or product resulting from metabolism. The term 'metabolite' subsumes the classes commonly known as primary and secondary metabolites.
EC 3.2.1.20 (alpha-glucosidase) inhibitorAn EC 3.2.1.* (glycosidase) inhibitor that interferes with the action of alpha-glucosidase (EC 3.2.1.20).
[role 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]

Drug Classes (2)

ClassDescription
phthalate ester
diesterA diester is a compound containing two ester groups.
[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 Targets (30)

Potency Measurements

ProteinTaxonomyMeasurementAverage (µ)Min (ref.)Avg (ref.)Max (ref.)Bioassay(s)
Chain A, TYROSYL-DNA PHOSPHODIESTERASEHomo sapiens (human)Potency56.23410.004023.8416100.0000AID485290
Chain A, JmjC domain-containing histone demethylation protein 3AHomo sapiens (human)Potency70.79460.631035.7641100.0000AID504339
glp-1 receptor, partialHomo sapiens (human)Potency28.18380.01846.806014.1254AID624417
RAR-related orphan receptor gammaMus musculus (house mouse)Potency48.55770.006038.004119,952.5996AID1159521
USP1 protein, partialHomo sapiens (human)Potency50.11870.031637.5844354.8130AID504865
GLI family zinc finger 3Homo sapiens (human)Potency27.89990.000714.592883.7951AID1259369; AID1259392
thyroid stimulating hormone receptorHomo sapiens (human)Potency12.58930.001318.074339.8107AID926; AID938
nuclear receptor subfamily 1, group I, member 3Homo sapiens (human)Potency61.13060.001022.650876.6163AID1224839
progesterone receptorHomo sapiens (human)Potency54.48270.000417.946075.1148AID1346795
glucocorticoid receptor [Homo sapiens]Homo sapiens (human)Potency35.48130.000214.376460.0339AID588533
pregnane X nuclear receptorHomo sapiens (human)Potency68.58960.005428.02631,258.9301AID1346982
estrogen nuclear receptor alphaHomo sapiens (human)Potency60.64680.000229.305416,493.5996AID743069; AID743075; AID743077; AID743079
67.9K proteinVaccinia virusPotency10.00000.00018.4406100.0000AID720579
bromodomain adjacent to zinc finger domain 2BHomo sapiens (human)Potency50.11870.707936.904389.1251AID504333
peroxisome proliferator-activated receptor deltaHomo sapiens (human)Potency5.01420.001024.504861.6448AID588535; AID743212
vitamin D (1,25- dihydroxyvitamin D3) receptorHomo sapiens (human)Potency0.00390.023723.228263.5986AID743223
thyroid stimulating hormone receptorHomo sapiens (human)Potency13.78950.001628.015177.1139AID1224843
v-jun sarcoma virus 17 oncogene homolog (avian)Homo sapiens (human)Potency27.06390.057821.109761.2679AID1159526; AID1159528
chromobox protein homolog 1Homo sapiens (human)Potency56.23410.006026.168889.1251AID540317
potassium voltage-gated channel subfamily H member 2 isoform dHomo sapiens (human)Potency79.43280.01789.637444.6684AID588834
lethal(3)malignant brain tumor-like protein 1 isoform IHomo sapiens (human)Potency28.18380.075215.225339.8107AID485360
Nuclear receptor ROR-gammaHomo sapiens (human)Potency6.68240.026622.448266.8242AID651802
Rap guanine nucleotide exchange factor 4Homo sapiens (human)Potency31.62283.981146.7448112.2020AID720708
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023]

Inhibition Measurements

ProteinTaxonomyMeasurementAverageMin (ref.)Avg (ref.)Max (ref.)Bioassay(s)
Histamine H2 receptorHomo sapiens (human)Ki3.16230.00062.197310.0000AID1059539
Histamine H1 receptorHomo sapiens (human)Ki2.51190.00000.511010.0000AID1059538
Histamine H4 receptorHomo sapiens (human)Ki3.16230.00060.478710.0000AID1059537
Histamine H3 receptorRattus norvegicus (Norway rat)Ki0.00130.00010.29638.5110AID1059540; AID1059552; AID692493
Histamine H3 receptorHomo sapiens (human)IC50 (µMol)0.00050.00050.46685.9000AID389212
Histamine H3 receptorHomo sapiens (human)Ki0.00020.00010.33998.5110AID1059541; AID1059543; AID1059553; AID375418; AID537545; AID692494
Cathepsin BHomo sapiens (human)IC50 (µMol)420.00000.00021.845310.0000AID316335
Cathepsin BMus musculus (house mouse)IC50 (µMol)230.00000.54001.43332.9800AID316337
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023]

Biological Processes (50)

Processvia Protein(s)Taxonomy
gastric acid secretionHistamine H2 receptorHomo sapiens (human)
immune responseHistamine H2 receptorHomo sapiens (human)
positive regulation of vasoconstrictionHistamine H2 receptorHomo sapiens (human)
G protein-coupled serotonin receptor signaling pathwayHistamine H2 receptorHomo sapiens (human)
chemical synaptic transmissionHistamine H2 receptorHomo sapiens (human)
G protein-coupled receptor signaling pathway, coupled to cyclic nucleotide second messengerHistamine H2 receptorHomo sapiens (human)
inflammatory responseHistamine H1 receptorHomo sapiens (human)
G protein-coupled receptor signaling pathwayHistamine H1 receptorHomo sapiens (human)
phospholipase C-activating G protein-coupled receptor signaling pathwayHistamine H1 receptorHomo sapiens (human)
memoryHistamine H1 receptorHomo sapiens (human)
visual learningHistamine H1 receptorHomo sapiens (human)
regulation of vascular permeabilityHistamine H1 receptorHomo sapiens (human)
positive regulation of vasoconstrictionHistamine H1 receptorHomo sapiens (human)
regulation of synaptic plasticityHistamine H1 receptorHomo sapiens (human)
cellular response to histamineHistamine H1 receptorHomo sapiens (human)
G protein-coupled serotonin receptor signaling pathwayHistamine H1 receptorHomo sapiens (human)
G protein-coupled receptor signaling pathway, coupled to cyclic nucleotide second messengerHistamine H1 receptorHomo sapiens (human)
chemical synaptic transmissionHistamine H1 receptorHomo sapiens (human)
inflammatory responseHistamine H4 receptorHomo sapiens (human)
positive regulation of cytosolic calcium ion concentrationHistamine H4 receptorHomo sapiens (human)
biological_processHistamine H4 receptorHomo sapiens (human)
regulation of MAPK cascadeHistamine H4 receptorHomo sapiens (human)
G protein-coupled serotonin receptor signaling pathwayHistamine H4 receptorHomo sapiens (human)
adenylate cyclase-inhibiting G protein-coupled acetylcholine receptor signaling pathwayHistamine H4 receptorHomo sapiens (human)
G protein-coupled receptor signaling pathway, coupled to cyclic nucleotide second messengerHistamine H4 receptorHomo sapiens (human)
chemical synaptic transmissionHistamine H4 receptorHomo sapiens (human)
neurotransmitter secretionHistamine H3 receptorHomo sapiens (human)
G protein-coupled serotonin receptor signaling pathwayHistamine H3 receptorHomo sapiens (human)
G protein-coupled receptor signaling pathway, coupled to cyclic nucleotide second messengerHistamine H3 receptorHomo sapiens (human)
chemical synaptic transmissionHistamine H3 receptorHomo sapiens (human)
adenylate cyclase-inhibiting G protein-coupled acetylcholine receptor signaling pathwayHistamine H3 receptorHomo sapiens (human)
proteolysisCathepsin BHomo sapiens (human)
thyroid hormone generationCathepsin BHomo sapiens (human)
collagen catabolic processCathepsin BHomo sapiens (human)
epithelial cell differentiationCathepsin BHomo sapiens (human)
regulation of apoptotic processCathepsin BHomo sapiens (human)
decidualizationCathepsin BHomo sapiens (human)
symbiont entry into host cellCathepsin BHomo sapiens (human)
proteolysis involved in protein catabolic processCathepsin BHomo sapiens (human)
cellular response to thyroid hormone stimulusCathepsin BHomo sapiens (human)
negative regulation of transcription by RNA polymerase IINuclear receptor ROR-gammaHomo sapiens (human)
xenobiotic metabolic processNuclear receptor ROR-gammaHomo sapiens (human)
regulation of glucose metabolic processNuclear receptor ROR-gammaHomo sapiens (human)
regulation of steroid metabolic processNuclear receptor ROR-gammaHomo sapiens (human)
intracellular receptor signaling pathwayNuclear receptor ROR-gammaHomo sapiens (human)
circadian regulation of gene expressionNuclear receptor ROR-gammaHomo sapiens (human)
cellular response to sterolNuclear receptor ROR-gammaHomo sapiens (human)
positive regulation of circadian rhythmNuclear receptor ROR-gammaHomo sapiens (human)
regulation of fat cell differentiationNuclear receptor ROR-gammaHomo sapiens (human)
positive regulation of DNA-templated transcriptionNuclear receptor ROR-gammaHomo sapiens (human)
adipose tissue developmentNuclear receptor ROR-gammaHomo sapiens (human)
T-helper 17 cell differentiationNuclear receptor ROR-gammaHomo sapiens (human)
regulation of transcription by RNA polymerase IINuclear receptor ROR-gammaHomo sapiens (human)
adaptive immune responseRap guanine nucleotide exchange factor 4Homo sapiens (human)
G protein-coupled receptor signaling pathwayRap guanine nucleotide exchange factor 4Homo sapiens (human)
adenylate cyclase-activating G protein-coupled receptor signaling pathwayRap guanine nucleotide exchange factor 4Homo sapiens (human)
calcium-ion regulated exocytosisRap guanine nucleotide exchange factor 4Homo sapiens (human)
regulation of exocytosisRap guanine nucleotide exchange factor 4Homo sapiens (human)
insulin secretionRap guanine nucleotide exchange factor 4Homo sapiens (human)
positive regulation of insulin secretionRap guanine nucleotide exchange factor 4Homo sapiens (human)
regulation of synaptic vesicle cycleRap guanine nucleotide exchange factor 4Homo sapiens (human)
Ras protein signal transductionRap guanine nucleotide exchange factor 4Homo sapiens (human)
regulation of insulin secretionRap guanine nucleotide exchange factor 4Homo sapiens (human)
[Information is prepared from geneontology information from the June-17-2024 release]

Molecular Functions (23)

Processvia Protein(s)Taxonomy
histamine receptor activityHistamine H2 receptorHomo sapiens (human)
G protein-coupled serotonin receptor activityHistamine H2 receptorHomo sapiens (human)
neurotransmitter receptor activityHistamine H2 receptorHomo sapiens (human)
histamine receptor activityHistamine H1 receptorHomo sapiens (human)
G protein-coupled serotonin receptor activityHistamine H1 receptorHomo sapiens (human)
neurotransmitter receptor activityHistamine H1 receptorHomo sapiens (human)
histamine receptor activityHistamine H4 receptorHomo sapiens (human)
G protein-coupled serotonin receptor activityHistamine H4 receptorHomo sapiens (human)
G protein-coupled acetylcholine receptor activityHistamine H4 receptorHomo sapiens (human)
histamine receptor activityHistamine H3 receptorHomo sapiens (human)
G protein-coupled acetylcholine receptor activityHistamine H3 receptorHomo sapiens (human)
G protein-coupled serotonin receptor activityHistamine H3 receptorHomo sapiens (human)
cysteine-type endopeptidase activityCathepsin BHomo sapiens (human)
protein bindingCathepsin BHomo sapiens (human)
collagen bindingCathepsin BHomo sapiens (human)
peptidase activityCathepsin BHomo sapiens (human)
cysteine-type peptidase activityCathepsin BHomo sapiens (human)
proteoglycan bindingCathepsin BHomo sapiens (human)
RNA polymerase II cis-regulatory region sequence-specific DNA bindingNuclear receptor ROR-gammaHomo sapiens (human)
DNA-binding transcription factor activity, RNA polymerase II-specificNuclear receptor ROR-gammaHomo sapiens (human)
DNA-binding transcription repressor activity, RNA polymerase II-specificNuclear receptor ROR-gammaHomo sapiens (human)
DNA-binding transcription factor activityNuclear receptor ROR-gammaHomo sapiens (human)
protein bindingNuclear receptor ROR-gammaHomo sapiens (human)
oxysterol bindingNuclear receptor ROR-gammaHomo sapiens (human)
zinc ion bindingNuclear receptor ROR-gammaHomo sapiens (human)
ligand-activated transcription factor activityNuclear receptor ROR-gammaHomo sapiens (human)
sequence-specific double-stranded DNA bindingNuclear receptor ROR-gammaHomo sapiens (human)
nuclear receptor activityNuclear receptor ROR-gammaHomo sapiens (human)
guanyl-nucleotide exchange factor activityRap guanine nucleotide exchange factor 4Homo sapiens (human)
protein bindingRap guanine nucleotide exchange factor 4Homo sapiens (human)
cAMP bindingRap guanine nucleotide exchange factor 4Homo sapiens (human)
protein-macromolecule adaptor activityRap guanine nucleotide exchange factor 4Homo sapiens (human)
small GTPase bindingRap guanine nucleotide exchange factor 4Homo sapiens (human)
[Information is prepared from geneontology information from the June-17-2024 release]

Ceullar Components (23)

Processvia Protein(s)Taxonomy
plasma membraneHistamine H2 receptorHomo sapiens (human)
synapseHistamine H2 receptorHomo sapiens (human)
plasma membraneHistamine H2 receptorHomo sapiens (human)
dendriteHistamine H2 receptorHomo sapiens (human)
cytosolHistamine H1 receptorHomo sapiens (human)
plasma membraneHistamine H1 receptorHomo sapiens (human)
synapseHistamine H1 receptorHomo sapiens (human)
dendriteHistamine H1 receptorHomo sapiens (human)
plasma membraneHistamine H1 receptorHomo sapiens (human)
plasma membraneHistamine H4 receptorHomo sapiens (human)
plasma membraneHistamine H4 receptorHomo sapiens (human)
dendriteHistamine H4 receptorHomo sapiens (human)
synapseHistamine H4 receptorHomo sapiens (human)
plasma membraneHistamine H3 receptorHomo sapiens (human)
presynapseHistamine H3 receptorHomo sapiens (human)
plasma membraneHistamine H3 receptorHomo sapiens (human)
synapseHistamine H3 receptorHomo sapiens (human)
dendriteHistamine H3 receptorHomo sapiens (human)
collagen-containing extracellular matrixCathepsin BHomo sapiens (human)
extracellular regionCathepsin BHomo sapiens (human)
extracellular spaceCathepsin BHomo sapiens (human)
lysosomeCathepsin BHomo sapiens (human)
external side of plasma membraneCathepsin BHomo sapiens (human)
apical plasma membraneCathepsin BHomo sapiens (human)
endolysosome lumenCathepsin BHomo sapiens (human)
melanosomeCathepsin BHomo sapiens (human)
perinuclear region of cytoplasmCathepsin BHomo sapiens (human)
collagen-containing extracellular matrixCathepsin BHomo sapiens (human)
extracellular exosomeCathepsin BHomo sapiens (human)
peptidase inhibitor complexCathepsin BHomo sapiens (human)
ficolin-1-rich granule lumenCathepsin BHomo sapiens (human)
extracellular spaceCathepsin BHomo sapiens (human)
lysosomeCathepsin BHomo sapiens (human)
nucleusNuclear receptor ROR-gammaHomo sapiens (human)
nucleoplasmNuclear receptor ROR-gammaHomo sapiens (human)
nuclear bodyNuclear receptor ROR-gammaHomo sapiens (human)
chromatinNuclear receptor ROR-gammaHomo sapiens (human)
nucleusNuclear receptor ROR-gammaHomo sapiens (human)
cytosolRap guanine nucleotide exchange factor 4Homo sapiens (human)
plasma membraneRap guanine nucleotide exchange factor 4Homo sapiens (human)
membraneRap guanine nucleotide exchange factor 4Homo sapiens (human)
hippocampal mossy fiber to CA3 synapseRap guanine nucleotide exchange factor 4Homo sapiens (human)
plasma membraneRap guanine nucleotide exchange factor 4Homo sapiens (human)
[Information is prepared from geneontology information from the June-17-2024 release]

Bioassays (52)

Assay IDTitleYearJournalArticle
AID1059533Binding affinity to human serum albumin by HPLC analysis2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID617163Ratio of drug level in brain to plasma in ip dosed rat2011Bioorganic & medicinal chemistry letters, Sep-15, Volume: 21, Issue:18
Amine-constrained pyridazinone histamine H₃ receptor antagonists.
AID1059552Displacement of [3H]-R-alpha-ethylhistamine from histamine H3 receptor in rat cerebral cortical tissue membranes after 45 mins by liquid scintillation spectrometry2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID692493Binding affinity to rat cortical histamine H3 receptor2011Journal of medicinal chemistry, Jan-13, Volume: 54, Issue:1
Histamine H3 receptor as a drug discovery target.
AID375418Binding affinity to histamine H3 receptor2009Journal of medicinal chemistry, Jul-09, Volume: 52, Issue:13
5-hydroxyindole-2-carboxylic acid amides: novel histamine-3 receptor inverse agonists for the treatment of obesity.
AID617159Cmax in po dosed rat2011Bioorganic & medicinal chemistry letters, Sep-15, Volume: 21, Issue:18
Amine-constrained pyridazinone histamine H₃ receptor antagonists.
AID409909Binding affinity to human recombinant histamine H3 receptor by GTPgammaS binding assay2008Bioorganic & medicinal chemistry, Sep-15, Volume: 16, Issue:18
Piperidine variations in search for non-imidazole histamine H(3) receptor ligands.
AID1059536Aqueous solubility of the compound2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059534Time dependent inhibition of CYP450 (unknown origin)2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059537Binding affinity to human histamine H4 receptor2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059551Ex vivo binding affinity to histamine H3 receptor in po dosed rat cerebral cortex using [3H]-R-alpha-ethylhistamine after 2 hrs by HPLC analysis2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID389212Antagonist activity at human cloned histamine H3 receptor expressed in CHO-K1 cells assessed as inhibition of R-alpha-methylhistamine-induced [35S]GTPgammaS binding2008Journal of medicinal chemistry, Nov-13, Volume: 51, Issue:21
Synthesis and evaluation of structurally constrained quinazolinone derivatives as potent and selective histamine H3 receptor inverse agonists.
AID1059546Reversal of RAMH-induced dipsogenia in Lister Hooded rat at 3 mg/kg, po treated 2 hrs before RAMH challenge measured after 1 hr2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059541Displacement of [3H]-R-alpha-ethylhistamine from human histamine H3 receptor expressed in HEK293 cells after 45 mins by liquid scintillation spectrometry2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID617161Oral bioavailability in rat2011Bioorganic & medicinal chemistry letters, Sep-15, Volume: 21, Issue:18
Amine-constrained pyridazinone histamine H₃ receptor antagonists.
AID780101Awakening activity in rat assessed as increased wakefulness at 10 mg/kg, po after 1 hr2013Bioorganic & medicinal chemistry letters, Nov-15, Volume: 23, Issue:22
Discovery of a potent, selective, and orally bioavailable histamine H3 receptor antagonist SAR110068 for the treatment of sleep-wake disorders.
AID537545Displacement of [3H]N-R-methylhistamine from human H3 receptor isolated from C6 cells2010Journal of medicinal chemistry, Nov-11, Volume: 53, Issue:21
Diaryldiamines with dual inhibition of the histamine H(3) receptor and the norepinephrine transporter and the efficacy of 4-(3-(methylamino)-1-phenylpropyl)-6-(2-(pyrrolidin-1-yl)ethoxy)naphthalen-1-ol in pain.
AID1059538Binding affinity to human histamine H1 receptor2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059540Displacement of [3H]-R-alpha-ethylhistamine from rat histamine H3 receptor expressed in HEK293 cells after 45 mins by liquid scintillation spectrometry2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059547Drug level in rat blood at 3 mg/kg, po2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059532Intrinsic clearance in human liver microsomes2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID692494Binding affinity to human histamine H3 receptor2011Journal of medicinal chemistry, Jan-13, Volume: 54, Issue:1
Histamine H3 receptor as a drug discovery target.
AID1059550Ex vivo binding affinity to histamine H3 receptor in rat cerebral cortex using [3H]-R-alpha-ethylhistamine at 3 mg/kg, po after 3 hrs by HPLC analysis2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059544Reversal of RAMH-induced dipsogenia in po dosed Lister Hooded rat treated 2 hrs before RAMH challenge measured after 1 hr2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059539Binding affinity to human histamine H2 receptor2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059535Inhibition of human ERG at 10 uM by patch clamp experiment2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059548Ratio of drug level in brain to blood in rat at 3 mg/kg, po after 1 hr2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059543Displacement of [3H]-R-alpha-ethylhistamine from histamine H3 receptor in human cerebral cortical tissue membranes after 45 mins by liquid scintillation spectrometry2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1059542Intrinsic clearance in rat liver microsomes2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID617160AUC (0 to 6 hrs) in po dosed rat2011Bioorganic & medicinal chemistry letters, Sep-15, Volume: 21, Issue:18
Amine-constrained pyridazinone histamine H₃ receptor antagonists.
AID617162Drug uptake in ip dosed rat brain after 1 hr2011Bioorganic & medicinal chemistry letters, Sep-15, Volume: 21, Issue:18
Amine-constrained pyridazinone histamine H₃ receptor antagonists.
AID1059553Antagonist activity at human histamine H3 receptor expressed in CHOK1 cells assessed as inhibition of GTPgammaS binding2013Bioorganic & medicinal chemistry letters, Dec-15, Volume: 23, Issue:24
Identification of clinical candidates from the benzazepine class of histamine H3 receptor antagonists.
AID1159607Screen for inhibitors of RMI FANCM (MM2) intereaction2016Journal of biomolecular screening, Jul, Volume: 21, Issue:6
A High-Throughput Screening Strategy to Identify Protein-Protein Interaction Inhibitors That Block the Fanconi Anemia DNA Repair Pathway.
AID588501High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Lethal Factor Protease, MLPCN compound set2010Current protocols in cytometry, Oct, Volume: Chapter 13Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening.
AID588501High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Lethal Factor Protease, MLPCN compound set2006Cytometry. 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.
AID588501High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Lethal Factor Protease, MLPCN compound set2010Assay and drug development technologies, Feb, Volume: 8, Issue:1
High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors.
AID651635Viability Counterscreen for Primary qHTS for Inhibitors of ATXN expression
AID504812Inverse Agonists of the Thyroid Stimulating Hormone Receptor: HTS campaign2010Endocrinology, Jul, Volume: 151, Issue:7
A small molecule inverse agonist for the human thyroid-stimulating hormone receptor.
AID504810Antagonists of the Thyroid Stimulating Hormone Receptor: HTS campaign2010Endocrinology, Jul, Volume: 151, Issue:7
A small molecule inverse agonist for the human thyroid-stimulating hormone receptor.
AID588497High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set2010Current protocols in cytometry, Oct, Volume: Chapter 13Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening.
AID588497High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set2006Cytometry. 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.
AID588497High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set2010Assay and drug development technologies, Feb, Volume: 8, Issue:1
High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors.
AID588499High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set2010Current protocols in cytometry, Oct, Volume: Chapter 13Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening.
AID588499High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set2006Cytometry. 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.
AID588499High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set2010Assay and drug development technologies, Feb, Volume: 8, Issue:1
High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors.
AID977602Inhibition of sodium fluorescein uptake in OATP1B3-transfected CHO cells at an equimolar substrate-inhibitor concentration of 10 uM2013Molecular pharmacology, Jun, Volume: 83, Issue:6
Structure-based identification of OATP1B1/3 inhibitors.
AID977599Inhibition of sodium fluorescein uptake in OATP1B1-transfected CHO cells at an equimolar substrate-inhibitor concentration of 10 uM2013Molecular pharmacology, Jun, Volume: 83, Issue:6
Structure-based identification of OATP1B1/3 inhibitors.
AID316336Cytotoxicity against mouse B16F10 cells by MTT assay2008Bioorganic & medicinal chemistry letters, Mar-15, Volume: 18, Issue:6
Cathepsin B inhibitory activities of phthalates isolated from a marine Pseudomonas strain.
AID316337Inhibition of cathepsin B in mouse B16F10 cells2008Bioorganic & medicinal chemistry letters, Mar-15, Volume: 18, Issue:6
Cathepsin B inhibitory activities of phthalates isolated from a marine Pseudomonas strain.
AID316335Inhibition of cathepsin B2008Bioorganic & medicinal chemistry letters, Mar-15, Volume: 18, Issue:6
Cathepsin B inhibitory activities of phthalates isolated from a marine Pseudomonas strain.
AID1159550Human Phosphogluconate dehydrogenase (6PGD) Inhibitor Screening2015Nature cell biology, Nov, Volume: 17, Issue:11
6-Phosphogluconate dehydrogenase links oxidative PPP, lipogenesis and tumour growth by inhibiting LKB1-AMPK signalling.
AID1346556Human TRPA1 (Transient Receptor Potential channels)2009Journal of neuroimmunology, Feb-15, Volume: 207, Issue:1-2
TRPA1 and TRPV1 activation is a novel adjuvant effect mechanism in contact hypersensitivity.
[information is prepared from bioassay data collected from National Library of Medicine (NLM), extracted Dec-2023]

Research

Studies (1,569)

TimeframeStudies, This Drug (%)All Drugs %
pre-199086 (5.48)18.7374
1990's71 (4.53)18.2507
2000's319 (20.33)29.6817
2010's630 (40.15)24.3611
2020's463 (29.51)2.80
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Market Indicators

Research Demand Index: 89.25

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 very strong demand-to-supply ratio for research on this compound.

MetricThis Compound (vs All)
Research Demand Index89.25 (24.57)
Research Supply Index7.37 (2.92)
Research Growth Index5.16 (4.65)
Search Engine Demand Index161.83 (26.88)
Search Engine Supply Index2.00 (0.95)

This Compound (89.25)

All Compounds (24.57)

Study Types

Publication TypeThis drug (%)All Drugs (%)
Trials2 (6.45%)5.53%
Trials11 (0.70%)5.53%
Reviews1 (3.23%)6.00%
Reviews45 (2.84%)6.00%
Case Studies0 (0.00%)4.05%
Case Studies7 (0.44%)4.05%
Observational0 (0.00%)0.25%
Observational0 (0.00%)0.25%
Other28 (90.32%)84.16%
Other1,519 (96.02%)84.16%
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]