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diethylhexyl phthalate

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Description

Diethylhexyl phthalate (DEHP) is a plasticizer commonly used to increase the flexibility and durability of plastics. It is synthesized by reacting phthalic anhydride with 2-ethylhexanol. DEHP is widely studied due to concerns about its potential health effects. Research has linked DEHP exposure to various health issues, including reproductive problems, liver damage, and endocrine disruption. It has been classified as a possible human carcinogen by the International Agency for Research on Cancer. While DEHP is still widely used, its production and use are being phased out in many countries due to safety concerns. The importance of DEHP research lies in understanding its potential risks to human health and the environment, as well as exploring safer alternatives for plasticizers.'

Diethylhexyl Phthalate: An ester of phthalic acid. It appears as a light-colored, odorless liquid and is used as a plasticizer for many resins and elastomers. [Medical Subject Headings (MeSH), National Library of Medicine, extracted Dec-2023]

bis(2-ethylhexyl) phthalate : A phthalate ester that is the bis(2-ethylhexyl) ester of benzene-1,2-dicarboxylic acid. [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 CID8343
CHEMBL ID1242017
CHEBI ID17747
SCHEMBL ID20271
SCHEMBL ID21733281
MeSH IDM0006353

Synonyms (185)

Synonym
1,2-benzenedicarboxylic acid, bis-(1-ethylhexyl) ester
di-sec-octyl phthalate
phthalic acid di(2-ethylhexyl) ester
diethylhexyl phthalate
CHEBI:17747 ,
bis(2-ethylhexyl) benzene-1,2-dicarboxylate
di(2-ethylhexyl)orthophthalate
bis(2-ethylhexyl) o-phthalate
1,2-benzenedicarboxylic acid bis(2-ethylhexyl) ester
phthalic acid bis(2-ethylhexyl) ester
dioctylphthalate
inchi=1/c24h38o4/c1-5-9-13-19(7-3)17-27-23(25)21-15-11-12-16-22(21)24(26)28-18-20(8-4)14-10-6-2/h11-12,15-16,19-20h,5-10,13-14,17-18h2,1-4h
15495-94-0
bis(2-ethylhexyl) phthalate
wln: 4y2 & 1ovr bvo1y4 & 2
nci-c52733
1, bis(ethylhexyl) ester
rc plasticizer dop
fleximel
octyl phthalate
octoil
vestinol ah
di(2-ethylhexyl) phthalate
flexol dop
bis(2-ethylhexyl) 1,2-benzenedicarboxylate
di(ethylhexyl) phthalate
phthalic acid, bis(2-ethylhexyl) ester
pittsburgh px-138
truflex dop
staflex dop
compound 889
di(2-ethylhexyl) o-phthalate
eviplast 81
nsc17069
flexol plasticizer dop
bisoflex dop
sicol 150
phthalic acid dioctyl ester
hercoflex 260
witcizer 312
vinicizer 80
bisoflex 81
eviplast 80
palatinol ah
wln: 8ovr bvo8
bis(ethylhexyl) phthalate
ethylhexyl phthalate
kodaflex dop
nsc-17069
1,2-benzenedicarboxylic acid bis-(1-ethylhexyl) ester
1,2-benzenedicarboxylic acid, bis(2-ethylhexyl) ester
NCGC00091499-01
union carbide flexol 380
caswell no. 392k
plasthall dop
ergoplast fdo
hsdb 339
etalon (plasticizer)
sansocizer r 8000
sconamoll dop
nsc 17069
sansocizer dop
platinol dop
brn 1890696
diacizer dop
reomol dop
rcra waste no. u028
einecs 204-211-0
ccris 237
platinol ah
nuoplaz dop
jayflex dop
etalon
dof [russian plasticizer]
ethyl hexyl phthalate
kodaflex dehp
benzenedicarboxylic acid, bis(2-ethylhexyl) ester
good-rite gp 264
ergoplast fdo-s
hatcol dop
di(2-ethylhexyl) orthophthalate
di-2-ethylhexyl phthalate
behp
monocizer dop
di-2-ethylhexylphthalate
mollan o
rcra waste number u028
reomol d 79p
ai3-04273
bis-(2-ethylhexyl)ester kyseliny ftalove [czech]
daf 68
epa pesticide chemical code 295200
di-(2-ethylhexyl) phthalate
bis(2-ethylhexyl)phthalate
117-81-7
DOP ,
dehp ,
di(2-ethylhexyl)phthalate
2-ethylhexyl phthalate
C03690
dioctyl phthalate, 99%
dioctyl phthalate, >=99.5%
NCGC00091499-02
di(2-ethylhexyl)phthalate (dehp)
di(2-ethylhexyl phthalate)
NCGC00091499-04
smr000777878
MLS001333173
bis-(2-ethylhexyl) phthalate
MLS001333174
bis(2-ethylhexyl) 1, 2-benzenedicarboxylate
MLS002454397
FT-0663286
P0297
82208-43-3
BRD-A89471977-001-05-2
NCGC00091499-07
NCGC00091499-06
NCGC00091499-05
c42k0ph13c ,
ec 204-211-0
bis-(2-ethylhexyl)ester kyseliny ftalove
unii-c42k0ph13c
1,2-benzenedicarboxylic acid, 1,2-bis(2-ethylhexyl) ester
dtxcid70607
cas-117-81-7
dtxsid5020607 ,
tox21_400084
CHEMBL1242017
AKOS024318875
14c -dehp
1,2-benzenedicarboxylic acid, bis(2-ethylhexyl) ester, labeled with carbon-14
HMS2233C15
S3360
FT-0624576
EPITOPE ID:140107
HMS3374J09
SCHEMBL20271
bis(2-ethylhexyl)phthalate [hsdb]
plastic additive 14
diethylhexyl phthalate [inci]
dehp [mi]
plastic additive 14 [usp-rs]
bis(2-ethylhexyl phthalate)-
di(2-ethylhexyl)phthalate [iarc]
dioctylphthalate [ii]
phthalic acid bis(2-ethylhexyl ester)
vinycizer 80
palatinol dop
merrol dop
bis-(2-ethylhexyl)ester kyseliny ftalove (czech)
corflex 400
hatco dop
bis(2-ethylhexyl)ester phthalic acid
palatinol ah-l
8033-53-2
352431-42-6
diplast o; esbo-d 82; ergoplast fdo; ergoplast fdo-s; etalon
benzene-1,2-dicarboxylic acid bis(2-ethylhexyl) ester
bis(2-ethylhexyl) phthalate, certified reference material, tracecert(r)
bis(2-ethylhexyl) phthalate, selectophore(tm)
bis(2-ethylhexyl) phthalate, saj first grade, >=98.0%
plastic additive 14, united states pharmacopeia (usp) reference standard
bis(2-ethylhexyl) phthalate, pestanal(r), analytical standard
mfcd00009493
plastic additive 01, european pharmacopoeia (ep) reference standard
diethylhexylphthalate; bis-(2-ethylhexyl) phthalate; plastic additive 01; dehp
diethylhexylphthalate (bis-(2-ethylhexyl) phthalate)
phthalic acid, bis-2-ethylhexyl ester 10 microg/ml in cyclohexane
phthalic acid, bis-2-ethylhexyl ester
bis(2-ethylhexyl) phthalate-d38
F0001-0292
HY-B1945
Q418492
50885-87-5
bis(2-ethylhexyl) phthalate 100 microg/ml in methanol
bis(2-ethylhexyl) phthalate 5000 microg/ml in methanol
AMY40790
CS-0014050
SCHEMBL21733281
A937603
bis(2-ethylhexyl)phthalate-13c6
1,2-bis(2-ethylhexyl) benzene-1,2-dicarboxylate
EN300-93410
Z1267670415

Research Excerpts

Overview

Diethylhexyl phthalate (DEHP) is an estrogen-like compound widely used as a commercial plasticizer. It is present in medical devices, tubing, food containers and packaging. It has been identified as a probable obesogen.

ExcerptReferenceRelevance
"Diethylhexyl phthalate (DEHP) is a common chemical plasticizer found in medical supplies, food packaging, and polyvinyl materials, and has been identified as a probable obesogen."( Impacts of diethylhexyl phthalate and overfeeding on physical fitness and lipid mobilization in Danio rerio (zebrafish).
Bisesi, JH; Buerger, AN; Harris, JP; Parente, CE; Watts, EG; Wormington, AM, 2022
)
1.83
"Diethylhexyl phthalate (DEHP) is an estrogen-like compound widely used as a commercial plasticizer and present in medical devices, tubing, food containers and packaging. "( Diethylhexyl phthalate exposure impairs follicular development and affects oocyte maturation in the mouse.
Chen, B; De Felici, M; Feng, YN; Huynh, E; Li, L; Ma, JM; Shen, W; Shi, QH; Zhang, LJ; Zhang, XF, 2013
)
3.28
"Diethylhexyl phthalate (DEHP) is an estrogen-like compound widely used as a plasticizer in commercial products and is present in medical devices, and common household items. "( Exposure to diethylhexyl phthalate (DEHP) results in a heritable modification of imprint genes DNA methylation in mouse oocytes.
Chen, H; Chen, P; Ge, W; Hou, ZM; Li, L; Ma, HG; Qin, GQ; Qin, XS; Shen, W; Sun, LL; Zhang, T; Zhang, XF, 2014
)
2.22
"Diethylhexyl phthalate (DEHP) is a widely used industrial additive for increasing plastic flexibility. "( Transgenerational inheritance of ovarian development deficiency induced by maternal diethylhexyl phthalate exposure.
Han, Z; Li, L; Liu, JC; Liu, YP; Ma, JY; Shen, W; Zhang, T; Zhang, XF, 2015
)
2.08
"Diethylhexyl phthalate (DEHP) is a widely used industrial plasticizer to which humans are widely exposed."( The pollutant diethylhexyl phthalate regulates hepatic energy metabolism via species-specific PPARalpha-dependent mechanisms.
Auwerx, J; Bedu, E; Bueno, M; Casals-Casas, C; Desvergne, B; Feige, JN; Gelman, L; Gerber, A; Gonzalez, FJ; Winkler, C; Yang, Q, 2010
)
1.44
"Diethylhexyl phthalate (DEHP) is a widely used plasticizer that induces peroxisome proliferation in rodents. "( A glucose-regulated protein, GRP58, is down-regulated in C57B6 mouse liver after diethylhexyl phthalate exposure.
Gill, SS; Muhlenkamp, CR, 1998
)
1.97

Toxicity

ExcerptReferenceRelevance
" Although the oral LD50 in the rat, mouse and rabbit is about 30 g/kg, its toxicology reveals problematic features such as high toxicity to some invertebrates, specific effects on the nervous system of fish and teratogenic effects in rats."( [Toxicity of the PVC-plasticizer di(2-ethylhexyl)phthalate (author's transl)].
Brevik, EM,
)
0.13
" In contrast, only DEHP and BBS induced toxic renal lesions."( The chronic hepatic or renal toxicity of di(2-ethylhexyl) phthalate, acetaminophen, sodium barbital, and phenobarbital in male B6C3F1 mice: autoradiographic, immunohistochemical, and biochemical evidence for levels of DNA synthesis not associated with car
Anderson, LM; Diwan, BA; Hagiwara, A; Lindsey, K; Ward, JM, 1988
)
0.27
" Except for transient ataxia and sedation, no adverse effects were observed among neonates that received 3:1 medium- and long-chain triglyceride emulsion for 9 consecutive days beginning on day 3 postpartum."( Assessment of the safety of chemicals administered intravenously in the neonatal rat.
Gillies, B; Greener, Y; Schmitt, D; Wienckowski, D; Woods, E; Youkilis, E, 1987
)
0.27
"The effects of DEHP on sperm morphology and on peripheral blood micronuclei were studied for 12 weeks following five subacute IP injections of DEHP at 1/6, 1/12, and 1/60 of the LD50 per day."( Genetic toxicology of phthalate esters: mutagenic and other genotoxic effects.
Blakey, DH; Douglas, GR; Hugenholtz, AP, 1986
)
0.27
" The LD50 and the nonfetolethal maximum dosage of DEHP in its single, oral administration was 592 mg/kg and 64 mg/kg, respectively."( Teratogenicity/fetotoxicity of DEHP in mice.
Nakamura, Y; Tomita, I; Tutikawa, K; Yagi, Y, 1982
)
0.26
" For all chemicals except carbon tetrachloride, the lowest effective dose for systemic toxicity was within the range of 3-56% of the LD50 for acute dosing, and 1-30% of the LD50 for repeated administration."( A multidisciplinary approach to toxicological screening: I. Systemic toxicity.
Berman, E; MacPhail, RC; Moser, VC; Schlicht, M, 1995
)
0.29
" The pesticides, CAR, TDM, HEP, and CDN, displayed the most acute neurotoxicity and were active at lower proportions of their respective acute LD50 values than were the solvents or the industrial chemicals."( A multidisciplinary approach to toxicological screening: III. Neurobehavioral toxicity.
Cheek, BM; MacPhail, RC; Moser, VC, 1995
)
0.29
" To determine if the toxic effects of di(2-ethylhexyl)phthalate (DEHP) are mediated by PPAR alpha, we examined its effect in PPAR alpha-null mice."( Receptor and nonreceptor-mediated organ-specific toxicity of di(2-ethylhexyl)phthalate (DEHP) in peroxisome proliferator-activated receptor alpha-null mice.
Gonzalez, FJ; Perella, CM; Peters, JM; Ward, JM,
)
0.13
" The results obtained indicate no serious toxic effects for DEHP at the level present in blood stored in DEHP plasticized blood bags as evidenced by the lack of any significant alteration in most of the biochemical parameters studied."( Toxic effect of systemic administration of low doses of the plasticizer di-(2-ethyl hexyl) phthalate [DEHP] in rats.
Arun, P; Deepadevi, KV; Kumar, VM; Kurup, PA; Lekshmi, LR; Nair, KG; Santhosh, A, 1998
)
0.3
" Results for high-molecular-weight PEs (log Kow>6) indicate that these chemicals are not acutely or chronically toxic to freshwater or marine organisms due to the combined role of low water solubility and limited bioconcentration potential which precludes attainment of internal concentrations that are required to elicit adverse effects."( Application of quantitative structure--activity relationships for assessing the aquatic toxicity of phthalate esters.
Konkel, WJ; Parkerton, TF, 2000
)
0.31
" Methyl clofenapate was not toxic up to a dose that produced precipitate, so cannot be directly compared with WY, which induced aberrations only at toxic dose levels."( The genetic toxicity of the peroxisome proliferator class of rodent hepatocarcinogen.
Armstrong, MJ; Ashby, J; Galloway, SM; Johnson, TE, 2000
)
0.31
" Thus, DEHP might exert its toxic effects on the testis by altering the expression of ZnT-1."( Testicular toxicity of di-(2-ethylhexyl)phthalate in young Sprague-Dawley rats.
Habeebu, SS; Klaassen, CD; Park, JD, 2002
)
0.31
" Three representative compounds, N-ethyl-N-nitrosourea (ENU), adriamycin (ADR), and mono-(2-ethylhexyl)phthalate (MEHP), toxic to different targets and known to affect germ cell development and impair fertility, were tested on PGCs in culture using three different experimental protocols."( A comparative study of cytotoxic effects of N-ethyl-N-nitrosourea, adriamycin, and mono-(2-ethylhexyl)phthalate on mouse primordial germ cells.
Ciccalese, R; De Felici, M; Iona, S; Klinger, FG; Nunziata, A; Sisti, R, 2002
)
0.31
" 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
" There were no adverse effects of DEHP on either litter size, litter weight or sex ratio at birth."( Reproductive and neurobehavioural toxicity study of bis(2-ethylhexyl) phthalate (DEHP) administered to mice in the diet.
Tanaka, T, 2002
)
0.31
" These results are similar to the toxic effects of long chain fatty acids on sludge digestion, suggesting that DEHP or its degradation products affect all the microbial populations in the anaerobic bioreactor."( Toxicity of di-(2-ethylhexyl) phthalate on the anaerobic digestion of wastewater sludge.
Ahring, BK; Alatriste-Mondragon, F; Iranpour, R, 2003
)
0.32
" To evaluate the possible toxic liver risk resulting from exposure to DEHP and TOTM, isolated rat hepatocytes were incubated with either DEHP, TOTM, MEHP or their common metabolite (2-EH) for 3 hours."( Evaluation of the direct toxicity of trioctyltrimellitate (TOTM), di(2-ethylhexyl) phthalate (DEHP) and their hydrolysis products on isolated rat hepatocytes.
Brunet, C; Dine, T; Dupin-Spriet, T; Gressier, B; Kambia, K; Luyckx, M, 2004
)
0.32
" There were no adverse effects of DEHP on either litter size, litter weight and sex ratio at birth."( Reproductive and neurobehavioural effects of bis(2-ethylhexyl) phthalate (DEHP) in a cross-mating toxicity study of mice.
Tanaka, T, 2005
)
0.33
" The toxic effects of the final degradation products were investigated using various recombinant bioluminescent bacteria."( Biodegradation of dipropyl phthalate and toxicity of its degradation products: a comparison of Fusarium oxysporum f. sp. pisi cutinase and Candida cylindracea esterase.
Bae, KD; Gu, MB; Kim, YH; Lee, J; Min, J, 2005
)
0.33
" The goal of this research was to investigate a threshold dose-response model with random effects (RE) to model the variability that exists between litters of animals in studies of toxic agents."( A new threshold dose-response model including random effects for data from developmental toxicity studies.
Hunt, DL; Rai, SN,
)
0.13
" Information from these animal studies of ambient substances that are noncarcinogenic, yet potentially toxic, to humans is used by federal protection agencies (Environmental Protection Agency, Occupational Safety and Health Administration, Food and Drug Administration) to determine safe exposure levels, such as no observed adverse effects level and benchmark dose."( A regression spline model for developmental toxicity data.
Hunt, DL; Li, CS, 2006
)
0.33
"In this study, di(2-ethylhexyl)phthalate (DEHP) toxicities to Caenorhabditis elegans were investigated using multiple toxic endpoints, such as mortality, growth, reproduction and stress-related gene expression, focusing on the identification of chemical-induced gene expression as a sensitive biomarker for DEHP monitoring."( Toxic effects of di(2-ethylhexyl)phthalate on mortality, growth, reproduction and stress-related gene expression in the soil nematode Caenorhabditis elegans.
Choi, J; Jung, IH; Lee, JY; Roh, JY, 2007
)
0.34
"These studies were conducted to evaluate the potential adverse effects of di-2-ethylhexyl terephthalate (DEHT) exposure on in utero development in mice and rats."( Developmental toxicity and uterotrophic studies with di-2-ethylhexyl terephthalate.
Deyo, JA; Faber, WD; Knapp, J; Navarro, L; Ruble, K; Stump, DG, 2007
)
0.34
"The lack of adverse developmental effects with DEHT exposure are in contrast to the adverse developmental effects noted after di-2-ethylhexyl phthalate (DEHP) exposure."( Developmental toxicity and uterotrophic studies with di-2-ethylhexyl terephthalate.
Deyo, JA; Faber, WD; Knapp, J; Navarro, L; Ruble, K; Stump, DG, 2007
)
0.34
"The main purpose of this collaborative work is to determine the optimal administration period required to detect toxic effects in evaluation of ovarian morphological changes in repeated-dose toxicity studies."( Collaborative work on evaluation of ovarian toxicity. 10) Two- or four-week repeated dose studies and fertility study of di-(2-ethylhexyl) phthalate (DEHP) in female rats.
Chiba, S; Deki, T; Hayashi, S; Iwata, Y; Kiyokawa, J; Matsuo, S; Mizoguchi, K; Suzuki, M; Takai, R, 2009
)
0.35
" Therefore, much effort was undertaken to reduce the potential risk of adverse effects of DEHP on humans by diminishing environmental exposure to this chemical."( Risk reduction of adverse effects due to di-(2-ethylhexyl) phthalate (DEHP) by utilizing microbial degradation.
Baek, JH; Gu, MB; Kim, KB; Kwack, SJ; Lee, BM; Sang, BI, 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 objective of this study was to investigate the cytotoxicity and genotoxicity potentials of di(2-ethylhexyl)phthalate (DEHP), the most widely used phthalate and its primary toxic metabolite mono(2-ethylhexyl)phthalate (MEHP), and their effects on the antioxidant balance in the LNCaP human prostate adenocarcinoma cell line."( Protective effect of selenium supplementation on the genotoxicity of di(2-ethylhexyl)phthalate and mono(2-ethylhexyl)phthalate treatment in LNCaP cells.
De Rosa, V; Erkekoğlu, P; Favier, A; Giray, B; Hincal, F; Rachidi, W, 2010
)
0.36
" Furthermore, our data suggest that the adverse effects caused by exposure to DEHP are likely to occur preferentially via PPAR signalling pathways in the testis and oestrogen signalling pathways in the liver."( Mechanisms of toxicity of di(2-ethylhexyl) phthalate on the reproductive health of male zebrafish.
Filby, AL; Lewis, C; Paull, GC; Santos, EM; Uren-Webster, TM, 2010
)
0.36
"Maternal exposure to di(2-ethylhexyl)phthalate (DEHP) is associated with adverse effects on offspring, and the metabolites are agonists of peroxisome proliferator-activated receptor (PPAR) α, which exhibits species differences in expression and function."( Hepatic peroxisome proliferator-activated receptor α may have an important role in the toxic effects of di(2-ethylhexyl)phthalate on offspring of mice.
Gonzales, FJ; Harada, Y; Hayashi, Y; Ito, Y; Kamijima, M; Naito, H; Nakajima, T; Ramdhan, DH; Tamada, H; Wang, D; Yamagishi, N; Yanagiba, Y, 2011
)
0.37
" Although the evidences are limited, it seems reasonable that DEHP may have a potential for similar adverse effects in humans."( Reproductive toxicity of di(2-ethylhexyl) phthalate in selenium-supplemented and selenium-deficient rats.
Arnaud, J; Asan, E; Erkekoglu, P; Giray, B; Hincal, F; Zeybek, ND, 2011
)
0.37
"Mono-(2-ethylhexyl) phthalate (MEHP) is the most toxic metabolite of di-(2-ethylhexyl) phthalate (DEHP)."( Evaluation of ovarian toxicity of mono-(2-ethylhexyl) phthalate (MEHP) using cultured rat ovarian follicles.
Chihara, K; Fukuda, C; Funabashi, H; Inada, H; Kimura, J; Kunimatsu, T; Miyano, T; Miyawaki, I; Tateishi, Y; Yamashita, A, 2012
)
0.38
"To investigate the separate and combined toxic effects of di-2-ethylhexylphthalate (DEHP) and cypermethrin (CYP) on prepubertal male rats."( [Single and combined toxic effects of di-2-ethylhexyl phthalate and cypermethrin on fertility and development in the the prepubertal male rats].
Cai, D; Li, X, 2012
)
0.38
" Rats exposed to DEHP alone showed main toxic effect."( [Single and combined toxic effects of di-2-ethylhexyl phthalate and cypermethrin on fertility and development in the the prepubertal male rats].
Cai, D; Li, X, 2012
)
0.38
"Mono-(2-ethylhexyl) phthalate (MEHP), the metabolite of di-(2-ethylhexyl) phthalate (DEHP), was suspected to be toxic to human embryos."( Cytotoxic effects of mono-(2-ethylhexyl) phthalate on human embryonic stem cells.
Cai, XH; Chen, X; Liang, R; Lu, Q; Shen, H; Shi, C; Yu, WD, 2013
)
0.39
"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
)
0.4
" In response, astrocyte proliferation (gliosis) was initiated, serving as a mechanism to maintain a homeostatic environment for neurons and protect neurons from toxic chemicals."( Primary neuronal-astrocytic co-culture platform for neurotoxicity assessment of di-(2-ethylhexyl) phthalate.
Li, K; Sun, Y; Wu, Y; Yang, X; Yuan, Y; Zuo, H, 2014
)
0.4
" In conclusion, in male rats, DEHP had adverse effects on the testis including inhibition of androgen production."( Celery oil modulates DEHP-induced reproductive toxicity in male rats.
Helal, MA, 2014
)
0.4
"Perfluorooctane sulfonate (PFOS) and di(2-ethylhexyl) phthalate (DEHP) have both been reported to induce adverse effects including immunotoxicity."( Immunotoxic effects of perfluorooctane sulfonate and di(2-ethylhexyl) phthalate on the marine fish Oryzias melastigma.
Chen, Y; Chi, Y; Dong, S; Fang, C; Huang, Q; Lin, Y; Zhang, H, 2015
)
0.42
" 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 article reviews the evidence, with particular reference to our own findings, that DEHP may actually exert a variety of adverse effects on mammalian folliculogenesis from early to final stages of oogenesis, including altered development of the primordial germ cells, impaired fetal oocyte survival and meiotic progression, reduced oocyte nest breakdown, acceleration of primordial follicle activation, altered follicle steroidogenesis and increased follicle atresia."( Di(2-ethylhexyl)phthalate: Adverse effects on folliculogenesis that cannot be neglected.
De Felici, M; Shen, W; Zhang, T; Zhang, XF, 2016
)
0.43
" These results suggested that DEHP exposure caused the toxic effects of quail cerebellum."( A novel nuclear xenobiotic receptors (AhR/PXR/CAR)-mediated mechanism of DEHP-induced cerebellar toxicity in quails (Coturnix japonica) via disrupting CYP enzyme system homeostasis.
Du, ZH; Li, JL; Li, XN; Sun, XC; Xia, J; Zhang, C; Zhao, HS; Zhu, SY, 2017
)
0.46
" In this study we investigated the multigenerational toxic effects including locomotive behaviors and reproduction upon prolonged DEHP exposure (from larval L1 to adult) and the underlying mechanisms in the nematode Caenorhabditis elegans."( Prolonged exposure of di(2-ethylhexyl) phthalate induces multigenerational toxic effects in Caenorhabditis elegans.
How, CM; Li, SW; Liao, VH, 2018
)
0.48
" The results confirm the reprotoxicity of DEHP and BPA as endocrine disruptors and indicate that ginseng could be used to alleviate the toxic effects of these chemicals."( Ameliorative effect of ginseng extract on phthalate and bisphenol A reprotoxicity during pregnancy in rats.
Abdel-Aziz Swelum, A; Abohassan, MG; Ahmed, MM; Hussein, MA; Moumen, AF; Moustafa, AA; Saadeldin, IM; Suleiman, AH, 2018
)
0.48
" The heat-shock response (HSR) comprising heat-shock protein (HSPs) and heat-shock transcription factor (HSFs) plays a pivotal role in various toxic stress conditions."( Modulation of heat-shock response is associated with Di (2-ethylhexyl) phthalate (DEHP)-induced cardiotoxicity in quail (Coturnix japonica).
Du, ZH; Li, JL; Li, PC; Li, XN; Liu, W; Wang, H, 2019
)
0.51
" However, there were adverse effects on soil algae, Collembola, and nematodes."( Soil ecotoxicity study of DEHP with respect to multiple soil species.
An, YJ; Cui, R; Kim, D; Kwak, JI; Moon, J, 2019
)
0.51
" Phthalates exert adverse effects on the development of seminiferous cords in the fetal testis through unknown toxicity pathways."( All-trans Retinoic Acid Disrupts Development in Ex Vivo Cultured Fetal Rat Testes. II: Modulation of Mono-(2-ethylhexyl) Phthalate Toxicity.
Boekelheide, K; Hall, SJ; Reyes, G; Spade, DJ; Wortzel, JD, 2019
)
0.51
" The results of the OECD TG407 subacute repeated dosing toxicity test indicate ATEC is less toxic compared to ATHC or DEHP and could be recommended as an alternative to phthalate plasticizers."( Effects of citrate ester plasticizers and bis (2-ethylhexyl) phthalate in the OECD 28-day repeated-dose toxicity test (OECD TG 407).
Gye, MC; Park, SH; Park, SJ; Xu, Y; Yoon, KN, 2019
)
0.51
" The results indicated that DEHP exerted metabolic toxic effects and increased insulin resistance through interfering with glucose metabolism and insulin signaling transduction pathway."( Study on the metabolism toxicity, susceptibility and mechanism of di-(2-ethylhexyl) phthalate on rat liver BRL cells with insulin resistance in vitro.
Ding, Y; Fei, F; Feng, W; Liu, Y; Mao, G; Wu, X; Yan, M; Yang, L; Zhang, Z; Zhao, T, 2019
)
0.51
" Our results showed that ICA reversed the adverse effect of DEHP on Leydig cell proliferation, and decreased ROS levels and elevated Δψm levels."( Icariin protects mouse Leydig cell testosterone synthesis from the adverse effects of di(2-ethylhexyl) phthalate.
Lian, X; Lin, J; Liu, Y; Lv, R; Mo, K; Sun, J; Wang, D; Wang, S; Xie, M; Xu, L; Xu, S, 2019
)
0.51
" Recent research on the adverse effects of DEHP has focused on reproductive and developmental toxicity in rodents and/or humans."( Di(2-ethylhexyl) phthalate-induced toxicity and peroxisome proliferator-activated receptor alpha: a review.
Ito, Y; Kamijima, M; Nakajima, T, 2019
)
0.51
" Based on our findings, DEHP significantly reduced the production and count of sperms; these toxic effects were associated with alterations in the serum hormone levels."( Protective effect of alpha-lipoic acid on di-(2-ethylhexyl) phthalate-induced testicular toxicity in mice.
Goudarzi, M; Haghi Karamallah, M; Kalantar, H; Kalantar, M; Malayeri, A; Mansouri, E, 2020
)
0.56
" In the current study, we addressed toxic effects of MEHP and DEHP on embryonic human kidney cells (HEK-293 cell line) and kidney tissue of rats, respectively."( The implication of mitochondrial dysfunction and mitochondrial oxidative damage in di (2-ethylhexyl) phthalate induced nephrotoxicity in both
Ashari, S; Dashti, A; Ghandadi, M; Ghassemi-Barghi, N; Karami, M; Mohammadi, H; Ranaee, M; Shokrzadeh, M, 2020
)
0.56
"Both di(2-ethylhexyl)phthalate (DEHP) and ethanol have toxic effects on the liver, and the oral exposure to DEHP in combination with ethanol may exist in the alcohol consumers, however, current food safety risk assessments based solely on the toxicity data of DEHP may underestimate the health impacts of phthalates, especially in population that continually consume alcoholic beverages."( Hepatotoxicity study of combined exposure of DEHP and ethanol: A comprehensive analysis of transcriptomics and metabolomics.
Fang, J; Geng, X; Jia, X; Li, Y; Ma, N; Xu, M; Yang, H; Zhang, Q, 2020
)
0.56
" The results of this study suggested that DEHP exposure could affect the male reproductive system and the degree of adverse effect depended on the dose and extent of exposure."( The dynamic assessment of toxicity and pathological process of DEHP in germ cells of male Sprague Dawley rats.
Dong, Q; Fang, K; Liu, S; Lu, D; Peng, Z; Ren, Z; Wang, L; Yang, B; Yang, L; Zhou, J, 2020
)
0.56
" The major and toxic metabolic derivative of DEHP, mono-2-ethylhexyl phthalate (MEHP), is capable of interfering with mitochondrial function, but its mechanism of action on mitophagy remains elusive."( Mono-2-ethylhexyl phthalate drives progression of PINK1-parkin-mediated mitophagy via increasing mitochondrial ROS to exacerbate cytotoxicity.
Héroux, P; Leng, J; Shen, HM; Wang, F; Wang, K; Wang, L; Wu, Y; Xia, D; Xu, J; Zhang, L; Zheng, F, 2021
)
0.62
" 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
"It has been revealed that di(2-ethylhexyl)phthalate (DEHP) has toxic impacts on the male reproductive system."( Taurine ameliorates cytotoxic effects of Di(2-ethylhexyl) phthalate on Leydig cells.
Khorsandi, L; Saki, G; Valizadeh, A; Yahyavy, S, 2021
)
0.62
" elegans, induces changes in gene expression levels, and activates the autophagy signal transduction pathway and that siRNA@SPION complexes suppress such toxic effects by silencing the expression of genes involved in the autophagy signal transduction pathway."( siRNA@superparamagnetic iron oxide nanoparticles attenuate physiological toxicity of DEHP by suppressing autophagy pathway activities in Caenorhabditis elegans.
Du, X; Huang, Y; Liu, Q; Liu, T, 2022
)
0.72
"Di-(2-ethylhexyl) phthalate (DEHP) is a plasticiser that, if absorbed into the human body, can cause various adverse effects including reproductive toxicity, liver toxicity and gut microbiota dysbiosis."( Lactic acid bacteria alleviate di-(2-ethylhexyl) phthalate-induced liver and testis toxicity via their bio-binding capacity, antioxidant capacity and regulation of the gut microbiota.
Chen, Q; Chen, W; He, Y; Kong, Q; Tian, P; Wang, G; Zhang, H; Zhao, J, 2022
)
0.72
" This study revealed that exposure to DEHP can be injurious to male reproductive health and aqueous garlic extract can decrease the toxic effects of DEHP in male mice."( Effect of aqueous garlic (Allium sativum) extract against di-(2-ethylhexyl) phthalate induced reproductive toxicity in male mice.
Aslam, I; Aziz, R; Batool, S; Iram, F; Shaheen, M; Shameem, S, 2022
)
0.72
"Emerging evidence indicates that nanoplastics (NPs) can transport organic pollutants such as di-(2-ethylhexyl) phthalate (DEHP) into organisms and induce adverse health effects."( Polystyrene nanoparticles aggravate the adverse effects of di-(2-ethylhexyl) phthalate on different segments of intestine in mice.
Chen, C; Cheng, S; Jiang, X; Luo, S; Mao, L; Qiu, J; Sun, W; Tang, S; Xia, Y; Yu, Z; Zhou, L; Zou, Z, 2022
)
0.72
" In particular, during early pregnancy, any adverse exposure may cause abnormal fetal growth or inhibit the development of embryogenic organs."( Prenatal di-(2-ethylhexyl) phthalate exposure induced myocardial cytotoxicity via the regulation of the NRG1-dependent ErbB2/ErbB4-PI3K/AKT signaling pathway in fetal mice.
Ji, Y; Li, B; Li, J; Lu, P; Wang, X; Yu, D; Zhu, D, 2022
)
0.72
" This approach can enable better understanding of the toxic mechanism of DEHP-induced human female reproductive toxicity and reveal potential novel DEHP female reproductive targets for experimental studies."( Mapping DEHP to the adverse outcome pathway network for human female reproductive toxicity.
Andric, N; Fa Nedeljkovic, S; Kokai, D; Pogrmic-Majkic, K; Samardzija Nenadov, D; Stanic, B; Tesic, B, 2022
)
0.72
"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
"Microplastics (MPs) have the characteristics of large specific surface area, high hydrophobicity and surface charge, so they are easy to combine with other pollutants and cause toxic effects on aquatic organisms."( The combined toxic effects of polyvinyl chloride microplastics and di(2-ethylhexyl) phthalate on the juvenile zebrafish (Danio rerio).
Chen, L; Han, X; Ji, Y; Lv, M; Wang, H; Wang, Q; Wang, X; Wang, Y; Zhao, X, 2022
)
0.72
" VA and VC supplementation attenuated the toxic effects of DEHP on the testicular functions, morphology, and semen characterization of the experimental adult male Wistar rats."( Vanillic acid and vitamin C attenuated di-2-ethylhexyl phthalate-induced testicular toxicity in adult male rats.
Adedotun, OA; Adejayi, J; Gbotolorun, SC; Iteire, K; Ogunlade, B, 2022
)
0.72
" Here, we reviewed relevant published studies, summarized the occurrence and major metabolic pathways of six typical PAEs (DMP, DEP, DBP, BBP, DEHP, and DOP) in water, soil, and the atmosphere, degradation and metabolic pathways under aerobic and anaerobic conditions, and explored the molecular mechanisms of the toxic effects of eleven PAEs (DEHP, DPP, DPrP, DHP, DEP, DBP, MBP, MBzP, BBP, DiNP, and DMP) on the immune system of different organisms at the gene, protein, and cellular levels."( Health risks of phthalates: A review of immunotoxicity.
Chen, J; Ju, H; Lyu, L; Tao, Y; Zhang, Y, 2022
)
0.72
" This study aimed to investigate the toxic effects on the male reproductive system upon coexposure to NPs and DEHP."( Polystyrene nanoparticles enhance the adverse effects of di-(2-ethylhexyl) phthalate on male reproductive system in mice.
Chen, C; Cheng, S; Jiang, X; Li, D; Luo, S; Mao, L; Qiu, J; Sun, W; Tang, S; Xia, Y; Xu, S; Yu, Z; Zhou, L; Zou, Z, 2022
)
0.72
" However, DEHP is known as an endocrine-disrupting chemical, causing cancers and adverse effects on human health."( Biodegradation of high di-(2-Ethylhexyl) phthalate (DEHP) concentration by food waste composting and its toxicity assessment using seed germination test.
Bui, XT; Chen, PH; Hoang, HG; Lam, SS; Le, TH; Lin, C; Rene, ER; Tran, HT, 2023
)
0.91
"The plasticizer di- (2-ethylhexyl) phthalate (DEHP) is considered a risk factor for allergic diseases and has attracted public attention for its adverse effects on health."( Multi-omics reveals the mechanisms of DEHP driven pulmonary toxicity in ovalbumin-sensitized mice.
Chen, Y; Li, N; Liu, P; Quan, X; Wang, X; Xu, C; Zhang, Q, 2023
)
0.91
"Considering that research of adverse effects of mono(2-ethylhexyl) phthalate (MEHP) and monobutyl phthalate (MBP), two key metabolites of the most common phthalates used as plasticisers in various daily-life products, has been scattered and limited, the aim of our study was to provide a more comprehensive analysis by focusing on major organ systems, including blood, liver, kidney, and pancreas in 66 male pubertal rats randomised into eleven groups of six."( Endocrine adverse effects of mono(2-ethylhexyl) phthalate and monobutyl phthalate in male pubertal rats.
Barlas, N; Karabulut, G, 2022
)
0.72
" Several PEs, however, were found to have adverse effects on the health of animals."( Evaluation of the 52-week chronic toxicity of a novel phthalate-free plasticizer, Eco-DEHCH (bis(2-ethylhexyl) cyclohexane-1,4-dicarboxylate), in Han Wistar rats.
Cha, HJ; Han, HJ; Jeong, DS; Kang, J; Ko, SM; Lee, DH; Lee, JY; Son, WC, 2023
)
0.91
" As an environmental endocrine disruptor, it induces adverse effects on brain development and function."( MiR-93 alleviates DEHP plasticizer-induced neurotoxicity by negatively regulating TNFAIP1 and inhibiting ubiquitin-mediated degradation of CK2β.
Dai, S; He, S; Hu, X; Li, Z; Liu, N; Qiu, F; Wang, J; Wei, C; Xiang, S; Zhang, Z, 2023
)
0.91

Pharmacokinetics

ExcerptReferenceRelevance
" Values of biological half-life and area under the concentration-time curve (AUC) of mono(2-ethylhexyl)phthalate, the main metabolite of DEHP, in testes after a single co-administration of DEHP (p."( Effects of co-administration of di(2-ethylhexyl)phthalate and testosterone on several parameters in the testis and pharmacokinetics of its mono-de-esterified metabolite.
Oishi, S, 1989
)
0.28
"A pharmacokinetic model for the accumulation of di-2-ethylhexyl phthalate (DEHP) by sheepshead minnow predicted a significant increase in the bioconcentration factor (BCF) of DEHP if its metabolism were inhibited."( Metabolic inhibition and di-2-ethylhexyl phthalate pharmacokinetics in fish.
Hayton, WL; Karara, AH,
)
0.13
" The pharmacokinetic differences between these two species indicate that the tissues of the marmoset are exposed to a level of DEHP metabolites equivalent to the complete absorption of a dose of Ca."( Comparative pharmacokinetics and subacute toxicity of di(2-ethylhexyl) phthalate (DEHP) in rats and marmosets: extrapolation of effects in rodents to man.
Batten, PL; Bratt, H; Elcombe, CR; Jackson, SJ; Orton, TC; Pratt, IS; Rhodes, C, 1986
)
0.27
"21/kg), and terminal half-life (approximately 50 min) were unchanged in two dogs following bilateral ureteral ligation."( Liquid chromatographic analysis of di(2-ethylhexyl) phthalate: application to pharmacokinetic studies in the mongrel dog.
Breutzmann, DA; Constantini, EG; Elmquist, WF; Haughey, DB; Hemphill, DG, 1988
)
0.27
" Both the terminal elimination half-life and the mean residence time increased exponentially with increasing temperature; the half-life increased from 79."( Temperature dependence of di-2-ethylhexyl phthalate (DEHP) pharmacokinetics in rainbow trout.
Barron, MG; Hayton, WL; Tarr, BD, 1987
)
0.27
" We do not have sufficient pharmacokinetic data in mice to evaluate the dose relationships as yet."( Pharmacokinetics, interactions with macromolecules and species differences in metabolism of DEHP.
Albro, PW; Corbett, JT; Jordan, S; Matthews, HB; Schroeder, JL, 1982
)
0.26
" To explain the increasing concentration of DEHP during treatment of renal failure using plasticized tubing, we propose a pharmacokinetic compartmental model in order to fit raw data obtained from dialysed patients and to get the amount of DEHP which enters the body by AUC calculations."( A pharmacokinetic interpretation of increasing concentrations of DEHP in haemodialysed patients.
Brunet, C; Courbon, F; Dine, T; Gressier, B; Houin, G; Luyckx, M; Nogarede, S; Plusquellec, Y; Souhait, J; Vanpoucke, J, 2000
)
0.31
"A simple pharmacokinetic model to predict concentrations of metabolites of di-2-ethylhexyl phthalate, DEHP, in humans starting from intakes of DEHP was developed and applied."( A simple pharmacokinetic model to characterize exposure of Americans to di-2-ethylhexyl phthalate.
Angerer, J; Koch, HM; Lorber, M, 2010
)
0.36
"To better understand the timing and extent of DEHP exposure, we used a simple pharmacokinetic model to "reconstruct" the DEHP dose responsible for the presence of DEHP metabolites in urine."( Dose reconstruction of di(2-ethylhexyl) phthalate using a simple pharmacokinetic model.
Calafat, AM; Lorber, M, 2012
)
0.38
"Dose reconstruction using pharmacokinetic models-in conjunction with biomonitoring data, diary information, and other related data-can provide a powerful means to define timing, magnitude, and possible sources of exposure to a given contaminant."( Dose reconstruction of di(2-ethylhexyl) phthalate using a simple pharmacokinetic model.
Calafat, AM; Lorber, M, 2012
)
0.38
" Adjusted animal biomonitoring equivalents from chimeric mice studies were scaled to human biomonitoring equivalents using known species allometric scaling factors and in vitro metabolic clearance data with a simple physiologically based pharmacokinetic (PBPK) model."( Human biofluid concentrations of mono(2-ethylhexyl)phthalate extrapolated from pharmacokinetics in chimeric mice with humanized liver administered with di(2-ethylhexyl)phthalate and physiologically based pharmacokinetic modeling.
Adachi, K; Murayama, N; Shimizu, M; Suemizu, H; Yamazaki, H, 2015
)
0.42
" We developed, evaluated, and demonstrated a modeling framework that integrates exposure and pharmacokinetic models to convert product phthalate concentrations into population-scale risks for phthalates and their substitutes."( An integrated exposure and pharmacokinetic modeling framework for assessing population-scale risks of phthalates and their substitutes.
Li, H; Little, JC; Song, Z; Wu, Y; Xu, Y; Zhong, M, 2021
)
0.62

Compound-Compound Interactions

ExcerptReferenceRelevance
" The group exposed to DEHP in combination with acetone was more affected."( Toxicity study of di(2-ethylhexyl)phthalate (DEHP) in combination with acetone in rats.
Dalgaard, M; Hansen, EV; Ladefoged, O; Lam, HR; Ostergaard, G, 2000
)
0.31
" Wistar rats were gavaged during gestation and lactation with vehicle, DEHP (300 or 750 mg/kg/day), or DEHP (750 mg/kg/day) in combination with DEHA (400mg/kg/day), and male offspring were examined at gestation day (GD) 21, postnatal day (PND) 22, 26 and 190."( Early testicular effects in rats perinatally exposed to DEHP in combination with DEHA--apoptosis assessment and immunohistochemical studies.
Borch, J; Dalgaard, M; Ladefoged, O,
)
0.13
" This research illustrates how chimeric mice transplanted with human hepatocytes in combination with a simple PBPK model can assist evaluations of pharmacokinetics or toxicokinetics of the primary or secondary metabolites of DEHP."( Human biofluid concentrations of mono(2-ethylhexyl)phthalate extrapolated from pharmacokinetics in chimeric mice with humanized liver administered with di(2-ethylhexyl)phthalate and physiologically based pharmacokinetic modeling.
Adachi, K; Murayama, N; Shimizu, M; Suemizu, H; Yamazaki, H, 2015
)
0.42

Bioavailability

ExcerptReferenceRelevance
" These data indicate that the bioavailability of selenium is decreased by DEHP."( Selenium metabolism in isolated hepatocytes: inhibition of incorporation in proteins by mono(2-ethylhexyl)phthalate, a metabolite of the peroxisome proliferator di(2-ethylhexyl)phthalate.
Garberg, P; Högberg, J, 1991
)
0.28
" 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
" Hence, the low po systemic availability of DEHP may be largely attributed to presystemic hydrolysis of DEHP to MEHP in the gut, whereas slow and/or incomplete absorption is the likely cause of the poor bioavailability of DEHP after ip administration."( Effects of route of administration and repetitive dosing on the disposition kinetics of di(2-ethylhexyl) phthalate and its mono-de-esterified metabolite in rats.
Ermer, JC; Li, RC; Pollack, GM; Shen, DD, 1985
)
0.27
" MEHP seems to be well absorbed by the peritoneal membrane."( The fate of leached di(2-ethylhexyl)phthalate in patients undergoing CAPD treatment.
Fischer, FP; Kiefer, T; Kuhlmann, U; Mettang, T; Rettenmeier, AW; Thomas, S; Wodarz, R,
)
0.13
" Incubations of LDEA with liver slices from rats and humans showed that the compound is well absorbed by hepatic tissue from both species."( Lauramide diethanolamine absorption, metabolism, and disposition in rats and mice after oral, intravenous, and dermal administration.
deCosta, K; Mathews, JM; Thomas, BF, 1996
)
0.29
" The spiking experiment suggested that SBRs had the potential to remove DEHP biologically from reject water but that the removal was restricted by the poor bioavailability of DEHP as a result of sorption to solids."( Removal of bis (2-ethylhexyl) phthalate from reject water in a nitrogen-removing sequencing batch reactor.
Marttinen, SK; Rintala, JA; Ruissalo, M, 2004
)
0.32
" This was partly attributed to low bioavailability and microbial toxicity of the xenobiotics."( Toxicity of xenobiotics during sulfate, iron, and nitrate reduction in primary sewage sludge suspensions.
Elsgaard, L, 2010
)
0.36
" Ultrasonication and Fenton oxidation pre-treatment was applied to improve biodegradability of WWS and bioavailability of the target compounds for digestion and fermentation."( Effect of ultrasonication and Fenton oxidation on biodegradation of bis(2-ethylhexyl) phthalate (DEHP) in wastewater sludge.
Brar, SK; Pham, TT; Surampalli, RY; Tyagi, RD, 2011
)
0.37
" The bioavailability of DEHP-D(4) was surprisingly high with an area under the concentration-time curve until 24h (AUC) amounting to 50% of that of free MEHP-D(4)."( Kinetics of di(2-ethylhexyl) phthalate (DEHP) and mono(2-ethylhexyl) phthalate in blood and of DEHP metabolites in urine of male volunteers after single ingestion of ring-deuterated DEHP.
Csanády, GA; Filser, JG; Fromme, H; Kessler, W; Klein, D; Numtip, W; Pütz, C; Seckin, E; Völkel, W, 2012
)
0.38
" It is important to determine the bioavailability of EEDCs in soil to inform risk assessment concerning their environmental presence; Eisenia fetida (earthworms) are typically used in traditional in vivo bioavailability experiments."( Development of an in vitro thin-film solid-phase microextraction method to determine the bioavailability of xenoestrogens in soil.
Engler, KN; Lemley, AT, 2013
)
0.39
" In order to assess the exact extent of the absorption of DEHP via the oral route, the aim of this study is to develop a reliable and validated ultra performance liquid chromatography with tandem mass spectrometry (UPLC-MS/MS) method to evaluate the oral bioavailability of DEHP in rats."( Determination and pharmacokinetics of di-(2-ethylhexyl) phthalate in rats by ultra performance liquid chromatography with tandem mass spectrometry.
Chang, LW; Chang-Liao, WL; Hou, ML; Lee, CJ; Lin, LC; Tsai, TH; Tsai, YM, 2013
)
0.39
" We established the high-performance liquid chromatography (HPLC) method for detecting DEHP and its major metabolite, mono-ethylhexyl phthalate (MEHP) in rat plasma, and then examined the toxicokinetic and bioavailability of DEHP with or without polysorbate 80 in rats."( Food emulsifier polysorbate 80 increases intestinal absorption of di-(2-ethylhexyl) phthalate in rats.
Gao, HT; Lu, Y; Rong, WT; Wang, YY; Xu, Q; Yang, N; Yu, SQ; Zhang, D; Zhang, FY, 2014
)
0.4
" Interestingly, curcumin despite its very low bioavailability showed protective activity against many organ lesions."( Curcumin influences semen quality parameters and reverses the di(2-ethylhexyl)phthalate (DEHP)-induced testicular damage in mice.
Basta-Kaim, A; Głombik, K; Kubera, M; Sikora-Polaczek, M; Starowicz, G; Styrna, J, 2014
)
0.4
" In male germ cells in vivo the protective effect was seen despite the low bioavailability of curcumin."( Curcumin influences semen quality parameters and reverses the di(2-ethylhexyl)phthalate (DEHP)-induced testicular damage in mice.
Basta-Kaim, A; Głombik, K; Kubera, M; Sikora-Polaczek, M; Starowicz, G; Styrna, J, 2014
)
0.4
"5 g) × the number of diapers used per day (12 sheets) × skin absorption rate (0."( Investigation of the amount of transdermal exposure of newborn babies to phthalates in paper diapers and certification of the safety of paper diapers.
Imai, S; Ishii, S; Katagiri, R; Kuribara, I; Minobe, Y; Wada, M; Wada, T, 2015
)
0.42
" Later, the operating conditions were optimized for removal of DEHP, COD, NH4(+) and PO4(3-), and finally the effect of bioavailability was examined by introduction of different concentrations of humic acid into the influent."( Effect of bioavailability on the fate of hydrophobic organic compounds and metal in treatment of young landfill leachate by membrane bioreactor.
Brar, SK; Buelna, G; Droguia, P; Dubé, R; Zolfaghari, M, 2016
)
0.43
" We hypothesized that DEHP might increase the bioavailability of BPA in tissues by competing for metabolic enzymes."( Diethylhexyl phthalate magnifies deposition of
Borman, ED; deCatanzaro, D; Pollock, T; Vecchi, N, 2017
)
1.9
" These observations suggest that ROS generation by MEHP leads to activation of HSL and increase in STAR which, together, result in increased free-cholesterol bioavailability and progesterone formation."( Redox regulation of hormone sensitive lipase: Potential role in the mechanism of MEHP-induced stimulation of basal steroid synthesis in MA-10 Leydig cells.
Li, Y; Martinez-Arguelles, DB; Papadopoulos, V; Traore, K; Zaman, N; Zhou, C; Zirkin, B, 2019
)
0.51
" orientalis biochar and pig biochar application on the bioavailability of cadmium (Cd) and di-(2-ethylhexyl) phthalate (DEHP) and on plant physiological parameters (malondialdehyde, proline and soluble sugars)."( Effect of biochars on the bioavailability of cadmium and di-(2-ethylhexyl) phthalate to Brassica chinensis L. in contaminated soils.
Che, L; Chen, H; Gielen, G; Guo, J; Mandal, S; Rinklebe, J; Shaheen, SM; Wang, H; Xu, S; Yang, X, 2019
)
0.51
"The ATP-binding cassette transporter P-glycoprotein (P-gp) is known to limit both brain penetration and oral bioavailability of many chemotherapy drugs."( A High-Throughput Screen of a Library of Therapeutics Identifies Cytotoxic Substrates of P-glycoprotein.
Ambudkar, SV; Brimacombe, KR; Chen, L; Gottesman, MM; Guha, R; Hall, MD; Klumpp-Thomas, C; Lee, OW; Lee, TD; Lusvarghi, S; Robey, RW; Shen, M; Tebase, BG, 2019
)
0.51
" Toxicity data on intravenous exposure are lacking and these are essential to conclude on hazard characteristics of alternatives that are poorly absorbed via the oral exposure route."( An update on the hazard of and exposure to diethyl hexyl phthalate (DEHP) alternatives used in medical devices.
Den Braver-Sewradj, SP; Hessel, EVS; Piersma, A, 2020
)
0.56
"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
)
0.62
" 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
" First of all, we verified that P80 promoted the bioavailability of MEHP-AF in the long-term and low-dose exposure of MEHP-AF with P80 as a result of increasing the intestinal absorption of MEHP-AF."( Food emulsifier polysorbate 80 promotes the intestinal absorption of mono-2-ethylhexyl phthalate by disturbing intestinal barrier.
Feng, QP; Hu, MY; Li, WJ; Wu, X; Xiang, SY; Yu, SQ; Yuan, YZ; Zhu, YT, 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
" As accurate as possible exposure assessment data of the oral bioavailability of these compounds are necessary, however only one in vivo study with piglets is available so far."( The oral bioavailability of di-2-ethylhexyl phthalate (DEHP), di-isononyl phthalate (DiNP) and di-(isononyl)-cyclohexane-1,2-dicarboxylate (DINCH®) in house dust.
Fembacher, L; Fromme, H; Nowak, D; Plichta, V; Völkel, W; Wöckner, M, 2022
)
0.72
", 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
"Organic pollutants such as di-(2-ethylhexyl) phthalate (DEHP) interact with nanoplastics (NPs) and change their bioavailability and toxicity to aquatic organisms."( Di-(2-ethylhexyl) phthalate exacerbated the toxicity of polystyrene nanoplastics through histological damage and intestinal microbiota dysbiosis in freshwater Micropterus salmoides.
Ai, W; Chen, G; Gao, D; Junaid, M; Liao, H; Liu, S; Wang, J, 2022
)
0.72
" Compared with REV, RBE exhibits higher bioavailability and better antioxidant effects."( Resveratrol Butyrate Ester Supplementation Blunts the Development of Offspring Hypertension in a Maternal Di-2-ethylhexyl Phthalate Exposure Rat Model.
Chang-Chien, GP; Hou, CY; Hsu, CN; Lin, S; Tain, YL, 2023
)
0.91

Dosage Studied

ExcerptRelevanceReference
" The acute toxicity of DEHP is very low (greater than 20 g/kg as LD50 in rats), and the ester is rapidly metabolised to products which are excreted in the urine and bile; chronic toxicity from the levels of dosage obtaining is thus very improbable."( Diethylhexyl phthalate as a factor in blood transfusion and haemodialysis.
Baker, RW, 1978
)
1.7
" After oral dosing no significant retention was found in organs and tissues."( Biochemical studies on phthalic esters I. Elimination, distribution and metabolism of di-(2-ethylhexyl)phthalate in rats.
Adachi, T; Takahashi, T; Tanaka, A; Yamaha, T, 1975
)
0.25
" These findings represent the first report assessing the in-vivo interaction potential of structurally similar and dissimilar peroxisome proliferators and provides insight into the dose-response nature of joint exposures to certain non-genotoxic carcinogens."( Effects of joint exposures to selected peroxisome proliferators on hepatic acyl-CoA oxidase activity in male B6C3F1 mice.
Baldwin, LA; Calabrese, EJ; Leonard, DA; Ochs, JB, 1992
)
0.28
" Furthermore, a reasonable estimate of intake of individual chemicals can be achieved provided that dosing solutions are prepared fresh at frequent intervals (e."( Toxicology studies of a chemical mixture of 25 groundwater contaminants. I. Chemistry development.
Arneson, DW; Brown, RD; Buchanan, RC; Chatham, AT; Goehl, TJ; Harris, RK; Yang, RS, 1989
)
0.28
" Each antimicrobial agent was diluted with sterile water for injection to a concentration representative of the most common dosage when administered via a portable infusion pump."( Stability of cefazolin sodium, cefoxitin sodium, ceftazidime, and penicillin G sodium in portable pump reservoirs.
Allen, LV; Stiles, ML; Tu, YH, 1989
)
0.28
"The Rai and Van Ryzin dose-response model proposed for teratology experiments has been characterized for its appropriateness and applicability in modeling the dichotomous response data from developmental toxicity studies."( Characterization of a developmental toxicity dose-response model.
Faustman, EM; Kimmel, CA; Smith, WP; Wellington, DG, 1989
)
0.28
" DEHP dosing during lactation also caused a decrease in mammary gland weight and a decrease in mammary gland RNA content which reflects synthetic activity."( Transfer of di(2-ethylhexyl) phthalate through rat milk and effects on milk composition and the mammary gland.
Dostal, LA; Schwetz, BA; Weaver, RP, 1987
)
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
" The administration of DEHP at dosage of 164."( Assessment of the safety of chemicals administered intravenously in the neonatal rat.
Gillies, B; Greener, Y; Schmitt, D; Wienckowski, D; Woods, E; Youkilis, E, 1987
)
0.27
" However, DEHP was negative for promotional activity when tested using the same sex and strain of rat and dosing regimen that resulted in hepatocarcinogenicity."( Di(2-ethylhexyl)phthalate: lack of initiating activity in the liver of female F-344 rats.
Garvey, LK; Hamm, TE; Popp, JA; Swenberg, JA, 1987
)
0.27
" The recovery of radioactivity from the urine of rats dosed with [14C]DEHP was examined by solvent extraction and XAD-2 resin absorption procedures."( Methods for measuring mutagenicity in urine of rats dosed with [14C]di(2-ethylhexyl)phthalate.
Barber, ED; DiVincenzo, GD; Donish, WH; Hamilton, ML; Mueller, KR, 1985
)
0.27
" Multiple dosing with DEHP (2."( Disposition of orally administered di-(2-ethylhexyl) phthalate and mono-(2-ethylhexyl) phthalate in the rat.
Belpaire, F; Teirlynck, OA, 1985
)
0.27
" In our dose-response study in rats it was shown that at the lowest dose (50 mg/kg body weight/day, approximately equivalent to a dietary level of 1000 ppm) several effects seen with higher doses were not apparent and others differed only slightly from normal control values."( Genotoxicity studies on di-(2-ethylhexyl) phthalate and adipate and toxicity studies on di-(2-ethylhexyl) phthalate in the rat and marmoset.
Carter, JT; Grasso, P; Jäckh, R; Rhodes, C, 1984
)
0.27
") at 4 weeks of age with N-nitrosodiethylamine (DEN) at a dosage of 80 mg/kg."( Di(2-ethylhexyl)phthalate but not phenobarbital promotes N-nitrosodiethylamine-initiated hepatocellular proliferative lesions after short-term exposure in male B6C3F1 mice.
Lynch, P; Ohshima, M; Riggs, C; Ward, JM, 1984
)
0.27
" The LD50 and the nonfetolethal maximum dosage of DEHP in its single, oral administration was 592 mg/kg and 64 mg/kg, respectively."( Teratogenicity/fetotoxicity of DEHP in mice.
Nakamura, Y; Tomita, I; Tutikawa, K; Yagi, Y, 1982
)
0.26
" Acute DEHP (150 mg/kg) increased mitotic figures in hepatocytes, which were replaced by hepatocellular cytomegaly after 14 d of dosing at the same level."( A multidisciplinary approach to toxicological screening: I. Systemic toxicity.
Berman, E; MacPhail, RC; Moser, VC; Schlicht, M, 1995
)
0.29
" Repeated dosing produced little or no effect with TCE or PER, marked physiological changes with CCl4, and cumulative toxicity and lethality with DCM."( A multidisciplinary approach to toxicological screening: III. Neurobehavioral toxicity.
Cheek, BM; MacPhail, RC; Moser, VC, 1995
)
0.29
" Differences in the pattern of systemic and neurological effects were also obtained that depended on dosing duration."( A multidisciplinary approach to toxicological screening: IV. Comparison of results.
Berman, E; Elder, JA; Kavlock, RJ; MacPhail, RC; Moser, VC; Narotsky, MG; Schlicht, M, 1995
)
0.29
" Adult, regularly cycling Sprague-Dawley rats were dosed daily with 2 g/kg DEHP in corn oil by gavage for 1 to 12 days."( Di-(2-ethylhexyl) phthalate suppresses estradiol and ovulation in cycling rats.
Davis, BJ; Heindel, JJ; Maronpot, RR, 1994
)
0.29
" Rats were dosed by oral gavage with 2 g phthalate diester/kg/day in corn oil vehicle for 2 days, while Leydig cell primary cultures were incubated with 1,000 microM monoester for 2 hr."( The influence of phthalate esters on Leydig cell structure and function in vitro and in vivo.
Garside, DA; Jones, HB; Liu, R; Roberts, JC, 1993
)
0.29
" The results provide support for a unified receptor-based mechanism controlling the main PP response, but demonstrate that individual responsive genes can show quite different dose-response curves."( The effects of peroxisome proliferators on protein abundances in mouse liver.
Anderson, NL; Eacho, P; Esquer-Blasco, R; Foxworthy, P; Richardson, F, 1996
)
0.29
" The animals were sacrificed at 6 hr, 24 hr, 48 hr, 7 days or 14 days after dosing to harvest skin specimens for the determination of radioactivity by autoradiographic and liquid scintillation methods, and to determine the dose that remained in the body."( Skin reservoir formation and bioavailability of dermally administered chemicals in hairless guinea pigs.
Bronaugh, R; Chu, I; Dick, D; Tryphonas, L, 1996
)
0.29
" Contrary to the infusion pump with the keyboard system, the infusion pump with a rotor in an occlusive pathway and a microstep motor (12,800 microsteps per revolution) was significantly more accurate as regards dosage (evaluated as the difference between the required and actually achieved value of flow)."( [Clinical use of infusion pumps with rotors in occlusive tracts].
Gajdůsková, V; Havlát, F; Havránková, V; Jarosová, A; Krifta, P; Sevela, K, 1996
)
0.29
" In this article, we consider statistical tests for increasing trend in mutant frequency with increasing dose, along with statistical models that may be used to describe the observed dose-response relationships."( Statistical analysis of the lacI transgenic mouse mutagenicity assay.
Fung, KY; Krewski, D; Lutz, WK; Shephard, S; Zhu, Y, 1997
)
0.3
" Using the definition of additivity as proposed by Berenbaum, some authors have instead used an experimental design necessary to estimate coefficients in an additivity model where only dose-response (concentration-effect) information of single compounds is required."( Economical designs for detecting and characterizing departure from additivity in mixtures of many chemicals.
Gennings, C,
)
0.13
" Dosing was for 7 days at the dose and route employed previously in the NTP cancer bioassays."( Hepatic ploidy, nuclearity, and distribution of DNA synthesis: a comparison of nongenotoxic hepatocarcinogens with noncarcinogenic liver mitogens.
Hasmall, SC; Roberts, RA, 1997
)
0.3
" Analysis of dose-response exposures to DEHP by reverse transcription (RT)-PCR confirm these results and also shows that GRP58 is not altered in kidney or testis."( A glucose-regulated protein, GRP58, is down-regulated in C57B6 mouse liver after diethylhexyl phthalate exposure.
Gill, SS; Muhlenkamp, CR, 1998
)
0.53
" The skin surface was not protected during the absorption dosing period."( Percutaneous absorption of salicylic acid, theophylline, 2, 4-dimethylamine, diethyl hexyl phthalic acid, and p-aminobenzoic acid in the isolated perfused porcine skin flap compared to man in vivo.
Maibach, H; Melendres, J; Riviere, JE; Sedik, L; Wester, RC, 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,
)
0.33
" Recent studies of DEHP clearly indicate a nonlinear dose-response curve that strongly suggests the existence of a dose threshold below which tumors in rodents are not induced."( A cancer risk assessment of di(2-ethylhexyl)phthalate: application of the new U.S. EPA Risk Assessment Guidelines.
Cattley, R; Doull, J; Elcombe, C; Lake, BG; Swenberg, J; van Gemert, M; Wilkinson, C; Williams, G, 1999
)
0.3
" A fifth group received clofibrate at a dosage of 500 mg/kg/day to provide a positive Control for liver peroxisome activity."( Effects of di-isononyl phthalate (DINP) on peroxisomal markers in the marmoset-DINP is not a peroxisome proliferator.
Hall, M; Harling, R; Matthews, A; Webley, L, 1999
)
0.3
" The compound is pharmaceutically formulated as a lyophilized product containing 500 microg active substance per dosage unit."( Compatibility and stability of aplidine, a novel marine-derived depsipeptide antitumor agent, in infusion devices, and its hemolytic and precipitation potential upon i.v. administration.
Beijnen, JH; Bouma, M; Bult, A; Henrar, RE; Manada, C; Nuijen, B, 1999
)
0.3
"In two separate studies with exposure duration 9 weeks or 4 weeks, male Wistar rats were dosed with di(2-ethylhexyl)phthalate (DEHP) by gavage and exposed to drinking water with or without acetone (0."( Toxicity study of di(2-ethylhexyl)phthalate (DEHP) in combination with acetone in rats.
Dalgaard, M; Hansen, EV; Ladefoged, O; Lam, HR; Ostergaard, G, 2000
)
0.31
" We also assessed the rate of Sertoli cell proliferation in pups at intervals after dosage with either chemical or vehicle by administering bromodeoxy uridine (BrdU) 3 h before euthanasia."( A single dose of Di-(2-ethylhexyl) phthalate in neonatal rats alters gonocytes, reduces sertoli cell proliferation, and decreases cyclin D2 expression.
Jester, WF; Laslett, AL; Li, LH; Orth, JM, 2000
)
0.31
" We have reported previously that 7-day dosing with DEHP induced a higher bromodeoxyuridine labeling index (LI) in binuclear octoploid (2x4N) rat hepatocytes than did DCB, suggesting that induction of DNA synthesis in 2x4N hepatocytes might represent a more substantial carcinogenic risk."( The nongenotoxic hepatocarcinogens diethylhexylphthalate and methylclofenapate induce DNA synthesis preferentially in octoploid rat hepatocytes.
Hasmall, SC; Roberts, RA,
)
0.13
" While only DEHP treatment reduced maternal weight gain during the entire dosing period by about 15 g, both DEHP and DINP reduced pregnancy weight gain to GD 21 by 24 g and 14 g, respectively."( Perinatal exposure to the phthalates DEHP, BBP, and DINP, but not DEP, DMP, or DOTP, alters sexual differentiation of the male rat.
Furr, J; Gray, LE; Ostby, J; Parks, L; Price, M; Veeramachaneni, DN, 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
" To illustrate this method, we fit a nonlinear dose-response model with nonnegative mixed bound constraints to clustered binary data from a developmental toxicity study."( Fitting nonlinear and constrained generalized estimating equations with optimization software.
Contreras, M; Ryan, LM, 2000
)
0.31
"Modeling of developmental toxicity studies often requires simple parametric analyses of the dose-response relationship between exposure and probability of a birth defect but poses challenges because of nonstandard distributions of birth defects for a fixed level of exposure."( Bayesian semiparametric analysis of developmental toxicology data.
Dominici, F; Parmigiani, G, 2001
)
0.31
" Sprague-Dawley rats were dosed with corn oil or DEHP (0, 375, 750, or 1,500 mg/kg/day, per os) from gestation day 3 through postnatal day (PND) 21."( Abnormalities of sexual development in male rats with in utero and lactational exposure to the antiandrogenic plasticizer Di(2-ethylhexyl) phthalate.
Ko, K; Lin, TM; Moore, RW; Peterson, RE; Rudy, TA, 2001
)
0.31
" Both laboratories found genotoxicity with a positive dose-response relationship for maleic hydrazide and acridine."( Genotoxicity of maleic hydrazide, acridine and DEHP in Allium cepa root cells performed by two different laboratories.
Lopez, LC; Moretton, J; Nielsen, MH; Rank, J, 2002
)
0.31
" For the current studies, male rats were dosed for 15 days via oral gavage and euthanized on the morning of test day 15."( Evaluation of a 15-day screening assay using intact male rats for identifying antiandrogens.
Frame, SR; Ladics, GS; O'Connor, JC, 2002
)
0.31
" It is pharmaceutically formulated as a lyophilized product containing 200 mg platinum per dosage unit."( Stability and compatibility of the investigational polymer-conjugated platinum anticancer agent AP 5280 in infusion systems and its hemolytic potential.
Beijnen, JH; Bouma, M; Bult, A; Jansen, BA; Nuijen, B; Reedijk, J; Rice, JR; Stewart, DR, 2002
)
0.31
" In dose-response experiments trend of decreasing amount of DNA synthesis was observed, but no statistical differences were found."( The effects of mono-2-ethylhexyl phathalate, adriamycin and N-ethyl-N-nitrosourea on stage-specific apoptosis and DNA synthesis in the mouse spermatogenesis.
Hakovirta, H; Linderborg, J; Nikula, H; Parvinen, M; Suominen, JS; Toppari, J, 2003
)
0.32
" Histopathological evaluation and organ weight measurements were performed on some animals after 21 days of dosing (primary group) and later on the recovery group animals that were held without further treatment until sexual maturity at approximately 90 days of age."( Evaluation of reproductive development following intravenous and oral exposure to DEHP in male neonatal rats.
Bruen, US; Cammack, JN; Conine, D; Echols, C; Friedman, M; Gass, J; Gordon, D; Hecker, L; White, RD; Wilson, DM; Yeh, TY,
)
0.13
" The results showed that DEHP could cause damage to embryonic development and there was a significant dose-response and dose-effect relationship between concentration of DEHP and its embryonic developmental toxicity."( [Effects of Di(2-ethylhexyl) phthalate(DEHP) on mouse embryos development in vitro].
Chen, X; Gao, L; Li, Y; Pei, X, 2003
)
0.32
"Risk assessment of chemicals is essential for the estimation of chemical safety, and animal toxicity data are typically used in the evaluation process, which consists of hazard identification, dose-response assessment, exposure assessment, and risk characterization."( Principles of risk assessment for determining the safety of chemicals: recent assessment of residual solvents in drugs and di(2-ethylhexyl) phthalate.
Hasegawa, R; Hirose, A; Koizumi, M, 2004
)
0.32
" To examine dose-response relationships, the experiment was repeated for DEHP exposures of 50, 200 and 800 mg/kg."( Altered expression of genes related to zinc homeostasis in early mouse embryos exposed to di-2-ethylhexyl phthalate.
Jang, B; Knudsen, TB; Lee, J; Park, J, 2004
)
0.32
" Because skin absorption of high molecular weight phthalates is limited, liver weight increase, a measure of peroxisomal proliferation, was monitored to assure that internal dosing had been achieved."( Phthalate treatment does not influence levels of IgE or Th2 cytokines in B6C3F1 mice.
Butala, JH; David, RM; Gans, G; Guo, TL; McKee, RH; Peachee, VL; White, KL, 2004
)
0.32
" Up-regulation of bcl-2, inhibitor of Apaf-1/caspase-9/caspase-2 cascade of apoptosis, may be related to the fact that no morphological apoptotic change was induced after dosing of 20 mg/kg DEHP."( Gene expression analysis of the rat testis after treatment with di(2-ethylhexyl) phthalate using cDNA microarray and real-time RT-PCR.
Adachi, T; Kijima, K; Komiyama, M; Matsuoka, N; Mori, C; Toyosawa, K; Yasuba, M, 2004
)
0.32
" Currently, scant data exist on the exact dosage to this population."( Infusion of di-2-ethylhexylphthalate for neonates: a review of potential health risk.
Brown, K; Jaeger, RJ; Weiss, AL,
)
0.13
"Here we describe a random effects threshold dose-response model for clustered binary-response data from developmental toxicity studies."( Testing threshold and hormesis in a random effects dose-response model applied to developmental toxicity data.
Hunt, D; Rai, SN, 2005
)
0.33
" The goal of this research was to investigate a threshold dose-response model with random effects (RE) to model the variability that exists between litters of animals in studies of toxic agents."( A new threshold dose-response model including random effects for data from developmental toxicity studies.
Hunt, DL; Rai, SN,
)
0.13
"In animal studies using oral dosing for short periods, di (2-ethylhexyl) phthalate (DEHP) is well known for its reproductive toxicity, especially for its testicular toxicity."( The effects of subacute inhalation of di (2-ethylhexyl) phthalate (DEHP) on the testes of prepubertal Wistar rats.
Kishi, R; Kondo, T; Kurahashi, N; Ma, M; Omura, M; Umemura, T, 2005
)
0.33
" The assay of amodiaquine hydrochloride in pharmaceutical dosage forms using one of the proposed sensors gave average recoveries of 104."( Amodiaquine polymeric membrane electrode.
Amighi, K; Blankert, B; Kambu, O; Kauffmann, JM; Malongo, TK; Nsangu, J, 2006
)
0.33
" We performed an extensive dose-response study following developmental exposure to DEHP and evaluated the effects on female reproductive development."( A dose-response study following in utero and lactational exposure to di(2-ethylhexyl)phthalate: effects on female rat reproductive development.
Andrade, AJ; Chahoud, I; Grande, SW; Grote, K; Talsness, CE, 2006
)
0.33
"Observed dose-response patterns of data from several developmental toxicity experiments appear to be nonlinear and should be characterized by an appropriate model to adequately fit this observed pattern."( A regression spline model for developmental toxicity data.
Hunt, DL; Li, CS, 2006
)
0.33
" Superovulation was induced by injections of equine chorionic gonadotropin (eCG) and human chorionic gonadotropin (hCG) in rats dosed with 125, 250, 500, 1,000 or 2,000 mg/kg body weight of DEHP for 4 consecutive days."( Involvement of thyroxine in ovarian toxicity of di-(2-ethylhexyl) phthalate.
Honma, T; Ito, S; Sekiguchi, S; Suda, M, 2006
)
0.33
"An extensive dose-response study following in utero and lactational exposure to di-(2-ethylhexyl) phthalate (DEHP) was conducted."( A dose-response study following in utero and lactational exposure to di-(2-ethylhexyl) phthalate (DEHP): effects on androgenic status, developmental landmarks and testicular histology in male offspring rats.
Andrade, AJ; Chahoud, I; Golombiewski, A; Grande, SW; Grote, K; Sterner-Kock, A; Talsness, CE, 2006
)
0.33
" Using quantitative PCR (qPCR), the dose-response of 24 genes was determined after a single MEHP exposure of 10, 100, or 1000 mg/kg."( Testicular gene expression profiling following prepubertal rat mono-(2-ethylhexyl) phthalate exposure suggests a common initial genetic response at fetal and prepubertal ages.
Gaido, KW; Johnson, KJ; Lahousse, SA; Liu, D; Wallace, DG, 2006
)
0.33
" For females, increased ovarian and uterine weights and elevated blood estradiol level were observed in higher dosage groups, 500 and 2500 mg/kg."( Effect of di(2-ethylhexyl) phthalate (DEHP) on genital organs from juvenile common marmosets: I. Morphological and biochemical investigation in 65-week toxicity study.
David, RM; Gans, G; Katoh, M; Kawasuso, T; Kurata, Y; Tomonari, Y, 2006
)
0.33
" In males on PND 1, aromatase activity was inhibited at low doses and increased at high doses resulting in a non-monotonic dose-response profile which resembled a J-shaped curve."( A dose-response study following in utero and lactational exposure to di-(2-ethylhexyl)-phthalate (DEHP): non-monotonic dose-response and low dose effects on rat brain aromatase activity.
Andrade, AJ; Chahoud, I; Grande, SW; Grote, K; Talsness, CE, 2006
)
0.33
" Previously, we reported dose-response associations of decreased semen quality with urinary concentrations of monobutyl phthalate (MBP) and monobenzyl (MBzP) phthalate, which are metabolites of dibutyl phthalate and butylbenzyl phthalate, respectively."( Altered semen quality in relation to urinary concentrations of phthalate monoester and oxidative metabolites.
Calafat, AM; Duty, S; Hauser, R; Meeker, JD; Silva, MJ, 2006
)
0.33
" We performed an extensive dose-response study following developmental exposure to DEHP and evaluated the effects on adult female reproductive function."( A dose-response study following in utero and lactational exposure to di-(2-ethylhexyl) phthalate (DEHP): reproductive effects on adult female offspring rats.
Andrade, AJ; Chahoud, I; Golombiewski, A; Grande, SW; Grote, K; Sterner-Kock, A; Talsness, CE, 2007
)
0.34
" The regression coefficients and the parameters from the dose-response model are simultaneously estimated using a penalized alternating least-squares method."( Joint detection of important biomarkers and optimal dose-response model using penalties.
Eilers, P; Ledent, E; Renard, D; Tibaldi, F; Vandenhende, F, 2007
)
0.34
" The present study investigates dose-response relationships for these classic Sertoli cell toxicants using histopathology endpoints."( Dose-dependent effects of sertoli cell toxicants 2,5-hexanedione, carbendazim, and mono-(2-ethylhexyl) phthalate in adult rat testis.
Boekelheide, K; Bryant, BH; Hall, SJ; Moffit, JS, 2007
)
0.34
" A slight reduction in rate of body weight gain was noted on the first day of dosing in the high dose group, but no other indications of toxicity were evident."( Developmental toxicity and uterotrophic studies with di-2-ethylhexyl terephthalate.
Deyo, JA; Faber, WD; Knapp, J; Navarro, L; Ruble, K; Stump, DG, 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
" The luc induction was determined in different tissues 8h after dosing the ER-luc male mice intraperitoneally (IP) or 14h after oral dosing."( Food-associated estrogenic compounds induce estrogen receptor-mediated luciferase gene expression in transgenic male mice.
Murk, AJ; Rietjens, IM; Ter Veld, MG; van den Berg, JH; van der Saag, PT; Zawadzka, E, 2008
)
0.35
" The daily dosage is between 71 and 104 microg x kg(-1) x day(-1)."( Extraction of diethylhexylphthalate by home total parenteral nutrition from polyvinyl chloride infusion lines commonly used in the home.
Brade, J; Hannmann, T; Loff, S; Reinecke, FM; Subotic, U; Wischmann, H, 2008
)
0.35
" Whereas the discussion of leaching of plasticizers is focussed on the toxicological properties of a drug packaging system, the sorption of drug formulation compounds has an influence on the dosage of the active pharmaceutical ingredient resulting in a reduced drug delivery to the patient."( Investigation into the sorption of nitroglycerin and diazepam into PVC tubes and alternative tube materials during application.
Brandsch, R; Treleano, A; Welle, F; Wolz, G, 2009
)
0.35
" The model was calibrated using data from an individual who dosed himself with 48."( A simple pharmacokinetic model to characterize exposure of Americans to di-2-ethylhexyl phthalate.
Angerer, J; Koch, HM; Lorber, M, 2010
)
0.36
" 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
" The bioassay was applied for a dose-response study of mono(2-ethylhexyl)phthalate (MEHP), a chemical known to disrupt several steroidogenic enzymes."( Steroidogenesis-disrupting compounds can be effectively studied for major fertility-related endpoints using in vitro cultured mouse follicles.
Lenie, S; Smitz, J, 2009
)
0.35
" Nevertheless, their path of action, dose-response character, and cellular target(s) within the fetal testis are not known."( Time- and dose-related effects of di-(2-ethylhexyl) phthalate and its main metabolites on the function of the rat fetal testis in vitro.
Angerer, J; Chagnon, MC; Chauvigné, F; Chevrier, C; Jégou, B; Lesné, L; Menuet, A; Regnier, JF, 2009
)
0.35
"In the rat, some phthalates alter sexual differentiation at relatively low dosage levels by altering fetal Leydig cell development and hormone synthesis, thereby inducing abnormalities of the testis, gubernacular ligaments, epididymis, and other androgen-dependent tissues."( Transgenerational effects of Di (2-ethylhexyl) phthalate in the male CRL:CD(SD) rat: added value of assessing multiple offspring per litter.
Barlow, NJ; Furr, JR; Gray, CL; Gray, LE; Howdeshell, KL; Ostby, JS, 2009
)
0.35
"Although is clear that exposure to high dosage levels of some phthalates delays the onset of puberty in the male rat, it has been hypothesized that low levels of di(2-ethylhexyl) phthalate (DEHP) accelerate puberty by enhancing testicular androgen synthesis."( Pubertal administration of DEHP delays puberty, suppresses testosterone production, and inhibits reproductive tract development in male Sprague-Dawley and Long-Evans rats.
Furr, J; Gray, LE; Howdeshell, KL; Lambright, CR; Noriega, NC; Wilson, VS, 2009
)
0.35
" From GD 12 through GD 17 each dam was dosed daily by gavage with either corn oil (vehicle control, 1 mgxkg(-1)xd(-1)) or DEHP (1, 250, 750 and 1000 mgxkg(-1)xd(-1))."( [Effects of in utero exposure to di(2-ethylhexyl) phthalate on sexual development in female offspring].
Ding, Y; Gao, Y; Shi, R; Tian, Y; Zhou, YJ, 2010
)
0.36
" These doses covered the whole dose-response curve for the demasculinizing effects of DEHP including low-dose effects."( Low-dose perinatal exposure to di(2-ethylhexyl) phthalate induces anti-androgenic effects in male rats.
Axelstad, M; Boberg, J; Christiansen, S; Dalgaard, M; Hass, U; Metzdorff, SB; Vinggaard, AM, 2010
)
0.36
" In order to define the di-(2-ethylhexyl) phthalate (DEHP) dose-response curve for reproductive malformations, we retained more offspring to adulthood to improve detection of these malformations in the reproductive assessment by continuous breeding study design."( Determination of the di-(2-ethylhexyl) phthalate NOAEL for reproductive development in the rat: importance of the retention of extra animals to adulthood.
Bishop, JB; Blystone, CR; Chapin, RE; Foster, PM; Kissling, GE; Wolfe, GW, 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
" Both parent compounds, TBB and TBPH, were detected in tissues at approximately 1% of daily dosage along with brominated metabolites."( Accumulation and DNA damage in fathead minnows (Pimephales promelas) exposed to 2 brominated flame-retardant mixtures, Firemaster 550 and Firemaster BZ-54.
Bearr, JS; Mitchelmore, CL; Stapleton, HM, 2010
)
0.36
" The dosed substances were deuterated di-2-ethylhexylphthalate (D(4)-DEHP) and di-isononylphthalate (D(4)-DINP) at two dose levels."( A twenty-volunteer study using deuterium labelling to determine the kinetics and fractional excretion of primary and secondary urinary metabolites of di-2-ethylhexylphthalate and di-iso-nonylphthalate.
Anderson, WA; Castle, L; Hird, S; Jeffery, J; Scotter, MJ, 2011
)
0.37
"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
" Male wistar rats were dosed with corn oil or DEHP by gavage from postnatal day (PND) 10-50 or PND 50-90 at doses between 1 and 1000 mg/kg/day."( Relative sensitivity of developmental and immune parameters in juvenile versus adult male rats after exposure to di(2-ethylhexyl) phthalate.
Gremmer, ER; Piersma, AH; Tonk, EC; van Loveren, H; Verhoef, A, 2012
)
0.38
" A significant decrease in protein levels of cyclin D1 and CDK-2 was found at high dosage of DEHP (100 μM) after 24h treatment."( Di 2-ethyl hexyl phthalate affects differentiation and matrix mineralization of rat calvarial osteoblasts--in vitro.
Arunakaran, J; Balasubramanian, K; Bhat, FA; Karthikeyan, GD; Karthikeyan, S; Parameswari, S; Ramajayam, G; Senthilkumar, K; Srinivasan, N; Vignesh, RC, 2013
)
0.39
" Sixty ICR female mice were randomized into four groups dosed with 0, 125, 500, or 2 000 mg/kg DEHP by gavage for 16 weeks, 6 days/week."( Di-(2-ethylhcxyl) phthalate reduces progesterone levels and induces apoptosis of ovarian granulosa cell in adult female ICR mice.
He, J; Li, N; Liu, T; Ye, L; Zhou, L, 2012
)
0.38
" We assessed non-monotonic dose-response by adding a quadratic term to a simple linear regression model."( Non-monotonic dose effects of in utero exposure to di(2-ethylhexyl) phthalate (DEHP) on testicular and serum testosterone and anogenital distance in male mouse fetuses.
Do, RP; Ponzi, D; Stahlhut, RW; Taylor, JA; Vom Saal, FS, 2012
)
0.38
" Pregnant dams were dosed orally from gestation day (GD) 13-19 with 0, 10, or 100 mg diethylhexyl phthalate (DEHP)/kg body weight per day."( Novel molecular targets associated with testicular dysgenesis induced by gestational exposure to diethylhexyl phthalate in the rat: a role for estradiol.
Klinefelter, GR; Laskey, JW; Riffle, BW; Roberts, NL; Strader, LF; Suarez, JD; Veeramachaneni, DN; Winnik, WM, 2012
)
0.82
" The hypospadias was observed and the incidence in three DEHP dosage levels was 10."( Dose-related effect by maternal exposure to di-(2-ethylhexyl) phthalate plasticizer on inducing hypospadiac male rats.
He, Y; Hua, Y; Li, M; Qiu, L; Tu, S; Wang, Q; Wei, G; Wen, S; Zhang, Y, 2013
)
0.39
" This study was designed to evaluate the dose-response relationship for the effects of DnHP on the synthesis and production of testosterone in the fetal rat testis."( Dose-dependent alterations in gene expression and testosterone production in fetal rat testis after exposure to di-n-hexyl phthalate.
Denis, F; Moison, D; Robert, A; Roudot, AC; Rouiller-Fabre, V; Sabaté, JP; Saillenfait, AM, 2013
)
0.39
" The cells were dosed either with neat DEHP or emulsified in aqueous solution (166 μg/ml)."( Skin permeation and metabolism of di(2-ethylhexyl) phthalate (DEHP).
Berthet, A; Gaudin, R; Hopf, NB; Langard, E; Spring, P; Vernez, D, 2014
)
0.4
" Chemical-specific and mechanistic data support concordance of temporal and dose-response relationships for the key events associated with many PPARα activators including a phthalate ester plasticizer di(2-ethylhexyl) phthalate (DEHP) and the drug gemfibrozil."( Mode of action framework analysis for receptor-mediated toxicity: The peroxisome proliferator-activated receptor alpha (PPARα) as a case study.
Corton, JC; Cunningham, ML; Hummer, BT; Klaunig, JE; Lau, C; Meek, B; Peters, JM; Popp, JA; Rhomberg, L; Seed, J, 2014
)
0.4
"The aim of this study was to investigate the association between di(2-ethylhexyl) phthalate (DEHP) exposure and atopic dermatitis (AD) in Korean children, focusing on the potential dose-response relationship."( Potential nonmonotonous association between di(2-ethylhexyl) phthalate exposure and atopic dermatitis in Korean children.
Choi, WJ; Hong, S; Kim, C; Kim, H; Kim, J; Kim, KS; Kwon, HJ; Lim, WR, 2014
)
0.4
" Adult CD-1 mice were orally dosed with DEHP (20 μg/kg/day-750 mg/kg/day) daily for 10 and 30 days."( Daily exposure to Di(2-ethylhexyl) phthalate alters estrous cyclicity and accelerates primordial follicle recruitment potentially via dysregulation of the phosphatidylinositol 3-kinase signaling pathway in adult mice.
Flaws, JA; Hannon, PR; Peretz, J, 2014
)
0.4
" Pregnant Sprague Dawley rats were gavaged from Gestational Day 14 to birth with corn oil, genistein, DEHP, or their mixture at 10 mg/kg/day, a dose selected from previous dose-response studies using single chemicals for its lack of long-term testicular effects."( Disruption of rat testis development following combined in utero exposure to the phytoestrogen genistein and antiandrogenic plasticizer di-(2-ethylhexyl) phthalate.
Boisvert, A; Culty, M; Duong, TB; Francois, S; Jones, S; Thrane, P, 2014
)
0.4
" 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
" To test this hypothesis, pregnant female CD-1 mice were orally dosed daily with tocopherol-stripped corn oil (vehicle control) or DEHP (20 μg/kg/day-750 mg/kg/day) from gestation day 11-birth."( Prenatal exposure to di-(2-ethylhexyl) phthalate (DEHP) affects reproductive outcomes in female mice.
Brehm, E; Flaws, JA; Niermann, S; Rattan, S, 2015
)
0.42
" In order to elucidate potential mechanisms by which DEHP disturbs thyroid hormone homeostasis, Sprague-Dawley (SD) rats were dosed with DEHP by gavage at 0, 250, 500, and 750 mg/kg/day for 30 days and sacrificed within 24 h after the last dose."( DEHP reduces thyroid hormones via interacting with hormone synthesis-related proteins, deiodinases, transthyretin, receptors, and hepatic enzymes in rats.
Li, L; Liu, C; Wei, L; Zhao, L, 2015
)
0.42
"We found that urinary PAE metabolite concentrations (specifically, metabolites of DEP, DnBP, DiBP, and DEHP) were positively associated with the APs for abdominal obesity (including skinfold thickness, waist circumference, waist-to-height ratio, and waist-to-hip) and indicated a dose-response relationship."( The effects of phthalate and nonylphenol exposure on body size and secondary sexual characteristics during puberty.
Chang, CH; Chen, BH; Chen, CC; Chen, ML; Hou, JW; Hsiung, CA; Huang, PC; Lee, CC; Lee, MC; Lee, MJ; Liao, KW; Lin, CL; Lin, FR; Pan, WH; Sun, CW; Tsai, YA; Wang, SL; Wang, YH; Wu, MT; Wu, WC; Yang, W; Yu, CJ, 2015
)
0.42
"As a part of the Japanese Center for the Validation of Alternative Methods (JaCVAM)-initiative international validation study of the in vivo alkaline comet assay (comet assay), we examined DNA damage in the liver, stomach, and bone marrow of rats dosed orally three times with up to 2000 mg/kg of benzene, di(2-ethylhexyl) phthalate, and trisodium ethylenediamine tetraacetic acid monohydrate."( Genotoxicity evaluation of benzene, di(2-ethylhexyl) phthalate, and trisodium ethylenediamine tetraacetic acid monohydrate using a combined rat comet/micronucleus assays.
Funabashi, H; Kimura, J; Kitamoto, S; Matsuyama, R; Miyata, K; Ogata, K; Ota, M; Saito, K; Uematsu, Y; Yamada, T, 2015
)
0.42
" The notion that these EDs do not follow classical dose-response effects and involve different mechanisms of toxicity from perinatal ages to adulthood highlights the importance of assessing impacts across a range of doses and ages."( In utero exposure to di-(2-ethylhexyl) phthalate induces testicular effects in neonatal rats that are antagonized by genistein cotreatment.
Boisvert, A; Culty, M; Francois, S; Jones, S; Zhang, L, 2015
)
0.42
" In order to clarify the roles of p53 in DEHP-induced hepatotoxicity, Sprague-Dawley (SD) rats were dosed daily with DEHP by gavage for 30 days; BRL cells (rat liver cell line) were treated with DEHP for 24 h after pretreatment with NAC or small interfering RNA (siRNA)."( p53-dependent apoptosis contributes to di-(2-ethylhexyl) phthalate-induced hepatotoxicity.
Guan, X; Ha, M; Li, L; Liu, C; Wei, L, 2016
)
0.43
" Adult CD-1 mice were orally dosed with vehicle or DEHP (20 μg/kg/day-500 mg/kg/day) daily for 10 days, and reproductive outcomes were assessed at 6 and 9 months postdosing."( Acute Exposure to Di(2-Ethylhexyl) Phthalate in Adulthood Causes Adverse Reproductive Outcomes Later in Life and Accelerates Reproductive Aging in Female Mice.
Flaws, JA; Hannon, PR; Niermann, S, 2016
)
0.43
" MEHP notably up-regulated the expression of PTCH with a dose-response relationship in the presence of cyclopamine, which indicate that MEHP might target on the downstream components of Hh pathway and advance the progression of PCa through activating the Hh pathway."( Mono-2-ethyhexyl phthalate advancing the progression of prostate cancer through activating the hedgehog pathway in LNCaP cells.
Jianhui, W; Jiao, C; Qi, P; Xiu, W; Yan, Z; Yong, W; Yunhui, Z; Zuyue, S, 2016
)
0.43
" Pregnant mice were exposed to DEHP by gavage, with the dosage regime beginning at human relevant exposure level."( Di(2-Ethylhexyl) Phthalate Exposure In Utero Damages Sertoli Cell Differentiation Via Disturbance of Sex Determination Pathway in Fetal and Postnatal Mice.
Cui, X; Liu, W; Wang, Y; Yang, Q; Yu, M; Zhang, Z, 2016
)
0.43
" Overall, this study determined that the kinetics of the phthalate monoesters MEHP and MnBP after oral dosage are comparable to the properties of their diesters."( Kinetics of the phthalate metabolites mono-2-ethylhexyl phthalate (MEHP) and mono-n-butyl phthalate (MnBP) in male subjects after a single oral dose.
Fromme, H; Mittermeier, A; Völkel, W, 2016
)
0.43
" In order to clarify adverse effects of DEHP on testicular physiology and testosterone production, Sprague-Dawley (SD) rats were dosed daily with DEHP by gavage for 30days; TM3 cells (mouse Leydig cell line) were treated with DEHP for 24h after pretreatment with vitamin C or U0126."( Di-(2-ethylhexyl) phthalate inhibits testosterone level through disturbed hypothalamic-pituitary-testis axis and ERK-mediated 5α-Reductase 2.
Guan, X; Ha, M; Li, P; Liu, C; Wei, L; Yang, M, 2016
)
0.43
" A strong dose-response relationship was observed between urinary metabolite levels and the odds of missed miscarriage."( A pilot study on association between phthalate exposure and missed miscarriage.
Chen, Y; Gu, H; Jin, Y; Wang, G; Yi, H; Yuan, W; Zhang, L; Zhao, H; Zhou, T, 2016
)
0.43
" 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
" Pregnant mice were exposed to DEHP by gavage, with the dosage regime beginning at human relevant exposure levels."( DEHP exposure in utero disturbs sex determination and is potentially linked with precocious puberty in female mice.
Cui, X; Liu, W; Wang, Y; Yang, Q; Yu, M; Zhang, Z, 2016
)
0.43
" The results acquired for determination of phenobarbitone in its dosage forms utilizing the proposed sensors are in good agreement with those obtained by the British Pharmacopoeial method."( Ionophore-based potentiometric PVC membrane sensors for determination of phenobarbitone in pharmaceutical formulations.
Abounassif, M; Al-Majed, A; Alrabiah, H; Mostafa, GA, 2016
)
0.43
" To explore the possible molecular mechanisms, 128 Wistar rats were dosed with DEHP by gavage at 0, 150, 300, and 600 mg/kg/day for 3 months (M) and 6 M, respectively."( Effects of Long-Term In Vivo Exposure to Di-2-Ethylhexylphthalate on Thyroid Hormones and the TSH/TSHR Signaling Pathways in Wistar Rats.
Dong, J; Dong, X; Guo, J; Liu, M; Na, X; Wang, Z; Zhang, Y; Zhao, Y, 2017
)
0.46
" In order to elucidate roles of the MAPK and PI3K/Akt pathways and hepatic enzymes in thyroid-disrupting effects of DEHP, Sprague-Dawley rats were dosed with DEHP by gavage for 30 consecutive days; Nthy-ori 3-1 cells were treated with DEHP with NAC, k-Ras siRNA or inhibitors (U0126 and wortmannin)."( Di2-ethylhexyl phthalate disrupts thyroid hormone homeostasis through activating the Ras/Akt/TRHr pathway and inducing hepatic enzymes.
Ha, M; Liu, C; Xie, Z; Yang, M; Ye, H; Yue, P, 2017
)
0.46
" Pregnant female CD-1 mice were orally dosed with vehicle control (tocopherol-stripped corn oil) or with 20 μg/kg/day, 200 μg/kg/day, 500 mg/kg/day, or 750 mg/kg/day of DEHP from gestational day 11 to birth."( Prenatal Exposure to DEHP Induces Premature Reproductive Senescence in Male Mice.
Abosalum, ME; Barakat, R; Brehm, E; Canisso, IF; Flaws, JA; Hess, R; Ko, C; Lin, PP; Rattan, S, 2017
)
0.46
" DEHP exposure significantly reduced the survival rate of fetuses in the 250 and 500 mg/kg dosage groups compared with the control and 5 mg/kg groups."( From the Cover: Teratogenic Effects of in Utero Exposure to Di-(2-Ethylhexyl)-Phthalate (DEHP) in B6:129S4 Mice.
Bantukul, T; Kawakami, Y; Kissling, GE; Rotgers, E; Ungewitter, E; Yao, HH, 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
" Dose-response relationships were determined in the parental AA8 cell line, its nucleotide repair-deficient UV5 and base repair-deficient EM9 subclones, and also in AS52 cells harboring the bacterial guanine-hypoxanthine phosphoribosyltransferase (gpt) gene and its derived AS52-XPD-knockdown and AS52-PARP-1-knockdown cells."( Acute exposure to DEHP metabolite, MEHP cause genotoxicity, mutagenesis and carcinogenicity in mammalian Chinese hamster ovary cells.
Chang, YJ; Chao, MW; Chuang, YC; Lin, PY; Tseng, CY, 2017
)
0.46
" Eleven genes were down-regulated in neonatal hypothalamus and showed non-monotonic dose-response relationships, that the 10 mg/kg DEHP dosage was associated with the greatest number of gene expression changes."( Specific effects of prenatal DEHP exposure on neuroendocrine gene expression in the developing hypothalamus of male rats.
Dao, L; Gao, N; Gore, AC; Hu, R; Huang, Y; Liu, Y; Sun, Z; Wang, X; Wu, L; Yin, W; Zhang, C, 2018
)
0.48
" Non-monotonic dose-response was observed for testosterone levels with a significant increase at 50μg/kgBW/d associated to a notable enhancement of Leydig cells number (35%)."( Male rat exposure to low dose of di(2-ethylhexyl) phthalate during pre-pubertal, pubertal and post-pubertal periods: Impact on sperm count, gonad histology and testosterone secretion.
Bendisari, K; Boudalia, S; Bouzid, B; Chader, H; Iguer-Ouada, M; Latreche, B; Oudir, M, 2018
)
0.48
" To test this hypothesis, pregnant CD-1 mice were orally dosed with corn oil (vehicle control) or DEHP (20 and 200 μg/kg/day and 200, 500, and 750 mg/kg/day) daily from gestation day 10."( Prenatal exposure to di(2-ethylhexyl) phthalate disrupts ovarian function in a transgenerational manner in female mice.
Brehm, E; Flaws, JA; Gao, L; Niermann, S; Rattan, S, 2018
)
0.48
" Chemical-specific and mechanistic data support concordance of temporal and dose-response relationships for the key events associated with many PPARα activators."( The PPARα-dependent rodent liver tumor response is not relevant to humans: addressing misconceptions.
Corton, JC; Klaunig, JE; Peters, JM, 2018
)
0.48
" Pregnant CD-1 mice were orally dosed with corn oil (vehicle control) or DEHP (20 and 200 µg/kg/d and 500 and 750 mg/kg/d) from gestational day 11 until birth."( Prenatal Exposure to Di(2-Ethylhexyl) Phthalate Causes Long-Term Transgenerational Effects on Female Reproduction in Mice.
Brehm, E; Flaws, JA; Gao, L; Rattan, S, 2018
)
0.48
" Adult female CD1 mice were orally dosed with DEHP (0, 20 μg/kg/day, 200 μg/kg/day, 20 mg/kg/day or 200 mg/kg/day) for 30 days."( Di (2-ethylhexyl) phthalate (DEHP) alters proliferation and uterine gland numbers in the uteri of adult exposed mice.
Flaws, JA; Hannon, PR; Johnson-Walker, YJ; Myint, MS; Nowak, RA; Richardson, KA, 2018
)
0.48
" Pregnant CD-1 mice were orally dosed with corn oil (vehicle control) or DEHP (20 and 200 µg/kg/day and 500 and 750 mg/kg/day) from gestation day 10."( Di(2-Ethylhexyl) Phthalate Exposure During Prenatal Development Causes Adverse Transgenerational Effects on Female Fertility in Mice.
Brehm, E; Flaws, JA; Gao, L; Rattan, S, 2018
)
0.48
" Therefore, prepubertal male rats were dosed with 0, 100, 200, and 400 mg/kg/day of DEHP."( Impact of the Di(2-Ethylhexyl) Phthalate Administration on Trace Element and Mineral Levels in Relation of Kidney and Liver Damage in Rats.
Aydemir, D; Barlas, N; Gok, M; Karabulut, G; Şimşek, G; Ulusu, NN, 2018
)
0.48
" Transcriptional expression of antioxidants such as superoxide dismutase, catalase, glutathione peroxidase, and glutathione S-transferase and peroxisome proliferation-activated receptor and retinoid X receptor genes was significantly suppressed with 21-day DEHP exposure (20-200 μg/L), with marginal alteration in reactive oxygen species levels and antioxidant activities within the dosing period."( Environmentally relevant concentrations of di(2-ethylhexyl)phthalate exposure alter larval growth and locomotion in medaka fish via multiple pathways.
Chen, PJ; Chiang, LF; Tan, SW; Yang, WK, 2018
)
0.48
" Then, the model was evaluated against the published independent data on different dosing scenarios."( Development of a human physiologically based pharmacokinetic (PBPK) model for phthalate (DEHP) and its metabolites: A bottom up modeling approach.
Kumar, V; Schuhmacher, M; Sharma, RP, 2018
)
0.48
" Adult female CD-1 mice (39-40 days) were orally dosed with vehicle control (corn oil), DEHP (20 µg/kg/day-200 mg/kg/day), or DiNP (20 µg/kg/day-200 mg/kg/day) for 10 days."( Subchronic Exposure to Di(2-ethylhexyl) Phthalate and Diisononyl Phthalate During Adulthood Has Immediate and Long-Term Reproductive Consequences in Female Mice.
Chiang, C; Flaws, JA, 2019
)
0.51
" Pregnant CD-1 mice (F0) were orally dosed with a vehicle or the phthalate mixtures (20 µg/kg/day, 200 µg/kg/day, 200 mg/kg/day, or 500 mg/kg/day) from gestational day 10."( Prenatal exposure to an environmentally relevant phthalate mixture disrupts testicular steroidogenesis in adult male mice.
Barakat, R; Ko, CJ; Lin, PP; Park, CJ; Seymore, T, 2019
)
0.51
" The results of the OECD TG407 subacute repeated dosing toxicity test indicate ATEC is less toxic compared to ATHC or DEHP and could be recommended as an alternative to phthalate plasticizers."( Effects of citrate ester plasticizers and bis (2-ethylhexyl) phthalate in the OECD 28-day repeated-dose toxicity test (OECD TG 407).
Gye, MC; Park, SH; Park, SJ; Xu, Y; Yoon, KN, 2019
)
0.51
" The pregnant mice were dosed with DEHP (20 μg/kg body weight/day) or vehicle control from E10."( Prenatal exposure to di-(2-ethylhexyl) phthalate and high-fat diet synergistically disrupts mouse fetal oogenesis and affects folliculogenesis†.
Gao, L; Mirihagalle, S; Patel, C; Qiao, H; Rattan, S; Suh, L; You, T, 2019
)
0.51
" Pregnant CD-1 mice were orally dosed daily with either tocopherol-stripped corn oil or DEHP (20 or 200 μg/kg/day; 500 or 750 mg/kg/day) from gestational day 10."( Exposure to di-(2-ethylhexyl) phthalate transgenerationally alters anxiety-like behavior and amygdala gene expression in adult male and female mice.
Chiang, C; Flaws, JA; Hatcher, KM; Mahoney, MM; Rattan, S; Willing, J, 2019
)
0.51
" To explore the DEHP-induced hepatotoxicity that occurs via regulation of HSR in birds, female quail were dosed with DEHP by oral gavage (0, 250, 500 and 1000 mg/kg) for 45 days."( Di-(2-ethylhexyl) phthalate (DEHP)-induced hepatotoxicity in quail (Coturnix japonica) via suppression of the heat shock response.
Fan, JH; Li, JL; Li, XN; Luo, Y; Talukder, M; Zhao, Y; Zuo, YZ, 2019
)
0.51
" Female CD1 mice were dosed orally with DEHP (0, 20, 200 and 2000 μg/kg/day) for 30 days."( Alterations in oocytes and early zygotes following oral exposure to di(2-ethylhexyl) phthalate in young adult female mice.
Alfaro-Pedraza, E; Hernández-Ochoa, I; Mojica-Villegas, MA; Parra-Forero, LY; Urióstegui-Acosta, M; Vargas-Marín, S; Veloz-Contreras, A, 2019
)
0.51
" Female CD-1 mice (age 39-40 days) were dosed with either vehicle control, DEHP (20 μg/kg/day-200 mg/kg/day), or DiNP (20 μg/kg/day-200 mg/kg/day) for 10 days and breeding trials were conducted at 12 and 15 months post-dosing."( Late-life consequences of short-term exposure to di(2-ethylhexyl) phthalate and diisononyl phthalate during adulthood in female mice.
Borkowski, G; Chiang, C; Flaws, JA; Lewis, LR, 2020
)
0.56
" DEHP was intragastrically administrated at the dosage of 0, 300, 1000 and 3000 mg/kg/d (body weight) for 4 weeks."( Role of the 17β-hydroxysteroid dehydrogenase signalling pathway in di-(2-ethylhexyl) phthalate-induced ovarian dysfunction: An in vivo study.
Li, N; Liu, T; Ye, L; Zhou, L; Zhu, J, 2020
)
0.56
" Female CD-1 mice aged 39-40 days were orally dosed with either vehicle control (corn oil), DEHP (20 μg/kg/day-200 mg/kg/day), or DiNP (20 μg/kg/day-200 mg/kg/day) for 10 days."( Exposure to di(2-ethylhexyl) phthalate and diisononyl phthalate during adulthood disrupts hormones and ovarian folliculogenesis throughout the prime reproductive life of the mouse.
Borkowski, G; Chiang, C; Flaws, JA; Lewis, LR, 2020
)
0.56
" Pregnant Sprague-Dawley rats (n = 3) were divided into four groups (control, BPA (50 mg/kg/day), DEHP (30 mg/kg/day), and BPA (50 mg/kg/day) + DEHP (30 mg/kg/day)) and dosed by oral gavage during pregnancy and lactation."( Histopathologic, apoptotic and autophagic, effects of prenatal bisphenol A and/or di(2-ethylhexyl) phthalate exposure on prepubertal rat testis.
Balci, A; Erkekoglu, P; Kocer-Gumusel, B; Ozkemahli, G; Yersal, N; Zeybek, ND, 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
" The present study followed the same dosing paradigm and included assessment of additional organs to evaluate the potential utility of this design for DEHP alternatives."( Effects of intravenous and oral di(2-ethylhexyl) phthalate (DEHP) and 20% Intralipid vehicle on neonatal rat testis, lung, liver, and kidney.
Camacho, L; Delclos, KB; Latendresse, JR; Law, CD; Muskhelishvili, L, 2020
)
0.56
" Results showed that DEHP exposed mice livers exhibited significant changes in global DNA methylation levels in all three generations, with the effect being different in F2 after high dosage exposure."( Multi and transgenerational epigenetic effects of di-(2-ethylhexyl) phthalate (DEHP) in liver.
Flaws, JA; Irudayaraj, J; Rattan, S; Wen, Y, 2020
)
0.56
" To investigate the impact of early life exposure to DEHP on the ovary and testes, newborn piglets were orally dosed with DEHP (20 or 200 mg/kg/day) or vehicle control (tocopherol-stripped corn oil) for 21 days."( Early postnatal exposure to di(2-ethylhexyl) phthalate causes sex-specific disruption of gonadal development in pigs.
Barakat, R; Cann, IK; De La Torre, KM; Donovan, SM; Flaws, JA; Inman, Z; Irudayaraj, JM; Ko, CJ; Lee, Y; Meling, DD; Monaco, MH; Rattan, S; Warner, GR, 2021
)
0.62
" To test this hypothesis, adult female mice were orally dosed with corn-oil vehicle control or doses of DiNP ranging from 20 µg/kg/d to 200 mg/kg/d for 10-14 days."( The Impact of Di-Isononyl Phthalate Exposure on Specialized Epithelial Cells in the Colon.
Bashir, ST; Chiu, J; Chiu, K; Flaws, JA; Nowak, RA, 2021
)
0.62
" Dose-response relationships between phthalate exposure and health outcomes were obtained by systematic review and meta-analysis."( Indoor exposure to phthalates and its burden of disease in China.
Bu, Z; Deng, F; Guo, J; Hou, J; Huang, C; Huo, X; Kan, H; Li, H; Liu, N; Liu, W; Mo, J; Qian, H; Su, C; Sun, C; Sun, Y; Zeng, X; Zhang, Y; Zhao, B; Zhao, Y; Zhao, Z; Zheng, X; Zou, Z, 2022
)
0.72
" Global and dose-response metabolomics tools were used to identify metabolic perturbations and sensitive markers associated with MEHP."( Dose-response mapping of MEHP exposure with metabolic changes of trophoblast cell and determination of sensitive markers.
Cao, R; Chen, J; Chen, Y; Chen, Z; Fang, Y; Liu, C; Wang, M; Zhang, H; Zhao, K; Zhou, M, 2023
)
0.91
" Adult C57BL/6 female mice were orally dosed with corn oil (control, n = 7) or DEHP (0."( Subchronic exposure to environmentally relevant concentrations of di-(2-ethylhexyl) phthalate differentially affects the colon and ileum in adult female mice.
Arcanjo, RB; Bashir, ST; Chiu, J; Chiu, K; Flaws, JA; Lai, NZE; Martinez, A; Nowak, RA; Raj, K; Stasiak, S; Zheng, E, 2022
)
0.72
" As expected with the low dosing scheme, the compounds induced a modest response on the transcriptome, as we identified changes in only mmu-miR-143-3p after DINP treatment and very few differentially expressed genes."( Investigation of the effects of phthalates on
Caiment, F; Carvalho, DJ; Costagliola, S; Giselbrecht, S; Hauser, D; Moroni, L; Nazzari, M; Romitti, M, 2023
)
0.91
[information is derived through text-mining from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Roles (3)

RoleDescription
apoptosis inhibitorAny substance that inhibits the process of apoptosis (programmed cell death) in multi-celled organisms.
androstane receptor agonistAn agonist that selectively binds to and activates androstane receptors.
plasticiserAny compound that is used as an additive to increase the plasticity or fluidity of a substance, particularly but not exclusively to synthetic polymers.
[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 (56)

Potency Measurements

ProteinTaxonomyMeasurementAverage (µ)Min (ref.)Avg (ref.)Max (ref.)Bioassay(s)
Chain A, JmjC domain-containing histone demethylation protein 3AHomo sapiens (human)Potency50.11870.631035.7641100.0000AID504339
interleukin 8Homo sapiens (human)Potency84.12670.047349.480674.9780AID651758
pregnane X receptorRattus norvegicus (Norway rat)Potency11.22020.025127.9203501.1870AID651751
RAR-related orphan receptor gammaMus musculus (house mouse)Potency0.86350.006038.004119,952.5996AID1159521
SMAD family member 2Homo sapiens (human)Potency21.87510.173734.304761.8120AID1346859
SMAD family member 3Homo sapiens (human)Potency21.87510.173734.304761.8120AID1346859
GLI family zinc finger 3Homo sapiens (human)Potency54.48270.000714.592883.7951AID1259369
AR proteinHomo sapiens (human)Potency29.51930.000221.22318,912.5098AID1259243; AID1259381; AID743035; AID743042; AID743054; AID743063
aldehyde dehydrogenase 1 family, member A1Homo sapiens (human)Potency22.38720.011212.4002100.0000AID1030
estrogen receptor 2 (ER beta)Homo sapiens (human)Potency27.30600.000657.913322,387.1992AID1259377; AID1259378
nuclear receptor subfamily 1, group I, member 3Homo sapiens (human)Potency14.73180.001022.650876.6163AID1224838; AID1224839; AID1224893
progesterone receptorHomo sapiens (human)Potency60.11800.000417.946075.1148AID1346784; AID1346795
cytochrome P450 family 3 subfamily A polypeptide 4Homo sapiens (human)Potency6.32610.01237.983543.2770AID1645841
glucocorticoid receptor [Homo sapiens]Homo sapiens (human)Potency6.16450.000214.376460.0339AID720692
retinoic acid nuclear receptor alpha variant 1Homo sapiens (human)Potency7.69590.003041.611522,387.1992AID1159552
retinoid X nuclear receptor alphaHomo sapiens (human)Potency2.75360.000817.505159.3239AID1159527
estrogen-related nuclear receptor alphaHomo sapiens (human)Potency17.68760.001530.607315,848.9004AID1224841; AID1224842
farnesoid X nuclear receptorHomo sapiens (human)Potency15.59390.375827.485161.6524AID743217; AID743220
pregnane X nuclear receptorHomo sapiens (human)Potency10.49220.005428.02631,258.9301AID1346982; AID720659
estrogen nuclear receptor alphaHomo sapiens (human)Potency31.48210.000229.305416,493.5996AID1259383; AID743069; AID743075
GVesicular stomatitis virusPotency17.82930.01238.964839.8107AID1645842
bromodomain adjacent to zinc finger domain 2BHomo sapiens (human)Potency50.11870.707936.904389.1251AID504333
peroxisome proliferator-activated receptor deltaHomo sapiens (human)Potency54.94100.001024.504861.6448AID743212
peroxisome proliferator activated receptor gammaHomo sapiens (human)Potency34.66540.001019.414170.9645AID743191
vitamin D (1,25- dihydroxyvitamin D3) receptorHomo sapiens (human)Potency7.76330.023723.228263.5986AID588543; AID743222; AID743223
euchromatic histone-lysine N-methyltransferase 2Homo sapiens (human)Potency31.62280.035520.977089.1251AID504332
thyroid stimulating hormone receptorHomo sapiens (human)Potency3.85710.001628.015177.1139AID1224843
nuclear factor of kappa light polypeptide gene enhancer in B-cells 1 (p105), isoform CRA_aHomo sapiens (human)Potency3.890019.739145.978464.9432AID1159509
chromobox protein homolog 1Homo sapiens (human)Potency89.12510.006026.168889.1251AID540317
thyroid hormone receptor beta isoform aHomo sapiens (human)Potency0.22390.010039.53711,122.0200AID588545
thyroid hormone receptor beta isoform 2Rattus norvegicus (Norway rat)Potency24.33650.000323.4451159.6830AID743065
nuclear factor erythroid 2-related factor 2 isoform 1Homo sapiens (human)Potency68.58960.000627.21521,122.0200AID651741; AID743202
cytochrome P450 3A4 isoform 1Homo sapiens (human)Potency15.84890.031610.279239.8107AID884; AID885
lethal factor (plasmid)Bacillus anthracis str. A2012Potency7.94330.020010.786931.6228AID912
Gamma-aminobutyric acid receptor subunit piRattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Interferon betaHomo sapiens (human)Potency17.82930.00339.158239.8107AID1645842
HLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)Potency17.82930.01238.964839.8107AID1645842
Cellular tumor antigen p53Homo sapiens (human)Potency13.68540.002319.595674.0614AID651631
Gamma-aminobutyric acid receptor subunit beta-1Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit deltaRattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit gamma-2Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-5Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-3Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit gamma-1Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-2Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-4Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit gamma-3Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-6Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Nuclear receptor ROR-gammaHomo sapiens (human)Potency74.97800.026622.448266.8242AID651802
Gamma-aminobutyric acid receptor subunit alpha-1Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit beta-3Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit beta-2Rattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
GABA theta subunitRattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
Inositol hexakisphosphate kinase 1Homo sapiens (human)Potency17.82930.01238.964839.8107AID1645842
Gamma-aminobutyric acid receptor subunit epsilonRattus norvegicus (Norway rat)Potency15.84891.000012.224831.6228AID885
cytochrome P450 2C9, partialHomo sapiens (human)Potency17.82930.01238.964839.8107AID1645842
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023]

Biological Processes (178)

Processvia Protein(s)Taxonomy
cell surface receptor signaling pathway via JAK-STATInterferon betaHomo sapiens (human)
response to exogenous dsRNAInterferon betaHomo sapiens (human)
B cell activation involved in immune responseInterferon betaHomo sapiens (human)
cell surface receptor signaling pathwayInterferon betaHomo sapiens (human)
cell surface receptor signaling pathway via JAK-STATInterferon betaHomo sapiens (human)
response to virusInterferon betaHomo sapiens (human)
positive regulation of autophagyInterferon betaHomo sapiens (human)
cytokine-mediated signaling pathwayInterferon betaHomo sapiens (human)
natural killer cell activationInterferon betaHomo sapiens (human)
positive regulation of peptidyl-serine phosphorylation of STAT proteinInterferon betaHomo sapiens (human)
cellular response to interferon-betaInterferon betaHomo sapiens (human)
B cell proliferationInterferon betaHomo sapiens (human)
negative regulation of viral genome replicationInterferon betaHomo sapiens (human)
innate immune responseInterferon betaHomo sapiens (human)
positive regulation of innate immune responseInterferon betaHomo sapiens (human)
regulation of MHC class I biosynthetic processInterferon betaHomo sapiens (human)
negative regulation of T cell differentiationInterferon betaHomo sapiens (human)
positive regulation of transcription by RNA polymerase IIInterferon betaHomo sapiens (human)
defense response to virusInterferon betaHomo sapiens (human)
type I interferon-mediated signaling pathwayInterferon betaHomo sapiens (human)
neuron cellular homeostasisInterferon betaHomo sapiens (human)
cellular response to exogenous dsRNAInterferon betaHomo sapiens (human)
cellular response to virusInterferon betaHomo sapiens (human)
negative regulation of Lewy body formationInterferon betaHomo sapiens (human)
negative regulation of T-helper 2 cell cytokine productionInterferon betaHomo sapiens (human)
positive regulation of apoptotic signaling pathwayInterferon betaHomo sapiens (human)
response to exogenous dsRNAInterferon betaHomo sapiens (human)
B cell differentiationInterferon betaHomo sapiens (human)
natural killer cell activation involved in immune responseInterferon betaHomo sapiens (human)
adaptive immune responseInterferon betaHomo sapiens (human)
T cell activation involved in immune responseInterferon betaHomo sapiens (human)
humoral immune responseInterferon betaHomo sapiens (human)
positive regulation of T cell mediated cytotoxicityHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
adaptive immune responseHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
antigen processing and presentation of endogenous peptide antigen via MHC class I via ER pathway, TAP-independentHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
regulation of T cell anergyHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
defense responseHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
immune responseHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
detection of bacteriumHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
regulation of interleukin-12 productionHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
regulation of interleukin-6 productionHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
protection from natural killer cell mediated cytotoxicityHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
innate immune responseHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
regulation of dendritic cell differentiationHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
antigen processing and presentation of endogenous peptide antigen via MHC class IbHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
negative regulation of cell population proliferationCellular tumor antigen p53Homo sapiens (human)
regulation of cell cycleCellular tumor antigen p53Homo sapiens (human)
regulation of cell cycle G2/M phase transitionCellular tumor antigen p53Homo sapiens (human)
DNA damage responseCellular tumor antigen p53Homo sapiens (human)
ER overload responseCellular tumor antigen p53Homo sapiens (human)
cellular response to glucose starvationCellular tumor antigen p53Homo sapiens (human)
intrinsic apoptotic signaling pathway in response to DNA damage by p53 class mediatorCellular tumor antigen p53Homo sapiens (human)
regulation of apoptotic processCellular tumor antigen p53Homo sapiens (human)
positive regulation of transcription by RNA polymerase IICellular tumor antigen p53Homo sapiens (human)
positive regulation of miRNA transcriptionCellular tumor antigen p53Homo sapiens (human)
negative regulation of transcription by RNA polymerase IICellular tumor antigen p53Homo sapiens (human)
mitophagyCellular tumor antigen p53Homo sapiens (human)
in utero embryonic developmentCellular tumor antigen p53Homo sapiens (human)
somitogenesisCellular tumor antigen p53Homo sapiens (human)
release of cytochrome c from mitochondriaCellular tumor antigen p53Homo sapiens (human)
hematopoietic progenitor cell differentiationCellular tumor antigen p53Homo sapiens (human)
T cell proliferation involved in immune responseCellular tumor antigen p53Homo sapiens (human)
B cell lineage commitmentCellular tumor antigen p53Homo sapiens (human)
T cell lineage commitmentCellular tumor antigen p53Homo sapiens (human)
response to ischemiaCellular tumor antigen p53Homo sapiens (human)
nucleotide-excision repairCellular tumor antigen p53Homo sapiens (human)
double-strand break repairCellular tumor antigen p53Homo sapiens (human)
regulation of DNA-templated transcriptionCellular tumor antigen p53Homo sapiens (human)
regulation of transcription by RNA polymerase IICellular tumor antigen p53Homo sapiens (human)
protein import into nucleusCellular tumor antigen p53Homo sapiens (human)
autophagyCellular tumor antigen p53Homo sapiens (human)
DNA damage responseCellular tumor antigen p53Homo sapiens (human)
DNA damage response, signal transduction by p53 class mediator resulting in cell cycle arrestCellular tumor antigen p53Homo sapiens (human)
DNA damage response, signal transduction by p53 class mediator resulting in transcription of p21 class mediatorCellular tumor antigen p53Homo sapiens (human)
transforming growth factor beta receptor signaling pathwayCellular tumor antigen p53Homo sapiens (human)
Ras protein signal transductionCellular tumor antigen p53Homo sapiens (human)
gastrulationCellular tumor antigen p53Homo sapiens (human)
neuroblast proliferationCellular tumor antigen p53Homo sapiens (human)
negative regulation of neuroblast proliferationCellular tumor antigen p53Homo sapiens (human)
protein localizationCellular tumor antigen p53Homo sapiens (human)
negative regulation of DNA replicationCellular tumor antigen p53Homo sapiens (human)
negative regulation of cell population proliferationCellular tumor antigen p53Homo sapiens (human)
determination of adult lifespanCellular tumor antigen p53Homo sapiens (human)
mRNA transcriptionCellular tumor antigen p53Homo sapiens (human)
rRNA transcriptionCellular tumor antigen p53Homo sapiens (human)
response to salt stressCellular tumor antigen p53Homo sapiens (human)
response to inorganic substanceCellular tumor antigen p53Homo sapiens (human)
response to X-rayCellular tumor antigen p53Homo sapiens (human)
response to gamma radiationCellular tumor antigen p53Homo sapiens (human)
positive regulation of gene expressionCellular tumor antigen p53Homo sapiens (human)
cardiac muscle cell apoptotic processCellular tumor antigen p53Homo sapiens (human)
positive regulation of cardiac muscle cell apoptotic processCellular tumor antigen p53Homo sapiens (human)
glial cell proliferationCellular tumor antigen p53Homo sapiens (human)
viral processCellular tumor antigen p53Homo sapiens (human)
glucose catabolic process to lactate via pyruvateCellular tumor antigen p53Homo sapiens (human)
cerebellum developmentCellular tumor antigen p53Homo sapiens (human)
negative regulation of cell growthCellular tumor antigen p53Homo sapiens (human)
DNA damage response, signal transduction by p53 class mediatorCellular tumor antigen p53Homo sapiens (human)
negative regulation of transforming growth factor beta receptor signaling pathwayCellular tumor antigen p53Homo sapiens (human)
mitotic G1 DNA damage checkpoint signalingCellular tumor antigen p53Homo sapiens (human)
negative regulation of telomere maintenance via telomeraseCellular tumor antigen p53Homo sapiens (human)
T cell differentiation in thymusCellular tumor antigen p53Homo sapiens (human)
tumor necrosis factor-mediated signaling pathwayCellular tumor antigen p53Homo sapiens (human)
regulation of tissue remodelingCellular tumor antigen p53Homo sapiens (human)
cellular response to UVCellular tumor antigen p53Homo sapiens (human)
multicellular organism growthCellular tumor antigen p53Homo sapiens (human)
positive regulation of mitochondrial membrane permeabilityCellular tumor antigen p53Homo sapiens (human)
cellular response to glucose starvationCellular tumor antigen p53Homo sapiens (human)
intrinsic apoptotic signaling pathway in response to DNA damage by p53 class mediatorCellular tumor antigen p53Homo sapiens (human)
positive regulation of apoptotic processCellular tumor antigen p53Homo sapiens (human)
negative regulation of apoptotic processCellular tumor antigen p53Homo sapiens (human)
entrainment of circadian clock by photoperiodCellular tumor antigen p53Homo sapiens (human)
mitochondrial DNA repairCellular tumor antigen p53Homo sapiens (human)
regulation of DNA damage response, signal transduction by p53 class mediatorCellular tumor antigen p53Homo sapiens (human)
positive regulation of neuron apoptotic processCellular tumor antigen p53Homo sapiens (human)
transcription initiation-coupled chromatin remodelingCellular tumor antigen p53Homo sapiens (human)
negative regulation of proteolysisCellular tumor antigen p53Homo sapiens (human)
negative regulation of DNA-templated transcriptionCellular tumor antigen p53Homo sapiens (human)
positive regulation of DNA-templated transcriptionCellular tumor antigen p53Homo sapiens (human)
positive regulation of RNA polymerase II transcription preinitiation complex assemblyCellular tumor antigen p53Homo sapiens (human)
positive regulation of transcription by RNA polymerase IICellular tumor antigen p53Homo sapiens (human)
response to antibioticCellular tumor antigen p53Homo sapiens (human)
fibroblast proliferationCellular tumor antigen p53Homo sapiens (human)
negative regulation of fibroblast proliferationCellular tumor antigen p53Homo sapiens (human)
circadian behaviorCellular tumor antigen p53Homo sapiens (human)
bone marrow developmentCellular tumor antigen p53Homo sapiens (human)
embryonic organ developmentCellular tumor antigen p53Homo sapiens (human)
positive regulation of peptidyl-tyrosine phosphorylationCellular tumor antigen p53Homo sapiens (human)
protein stabilizationCellular tumor antigen p53Homo sapiens (human)
negative regulation of helicase activityCellular tumor antigen p53Homo sapiens (human)
protein tetramerizationCellular tumor antigen p53Homo sapiens (human)
chromosome organizationCellular tumor antigen p53Homo sapiens (human)
neuron apoptotic processCellular tumor antigen p53Homo sapiens (human)
regulation of cell cycleCellular tumor antigen p53Homo sapiens (human)
hematopoietic stem cell differentiationCellular tumor antigen p53Homo sapiens (human)
negative regulation of glial cell proliferationCellular tumor antigen p53Homo sapiens (human)
type II interferon-mediated signaling pathwayCellular tumor antigen p53Homo sapiens (human)
cardiac septum morphogenesisCellular tumor antigen p53Homo sapiens (human)
positive regulation of programmed necrotic cell deathCellular tumor antigen p53Homo sapiens (human)
protein-containing complex assemblyCellular tumor antigen p53Homo sapiens (human)
intrinsic apoptotic signaling pathway in response to endoplasmic reticulum stressCellular tumor antigen p53Homo sapiens (human)
thymocyte apoptotic processCellular tumor antigen p53Homo sapiens (human)
positive regulation of thymocyte apoptotic processCellular tumor antigen p53Homo sapiens (human)
necroptotic processCellular tumor antigen p53Homo sapiens (human)
cellular response to hypoxiaCellular tumor antigen p53Homo sapiens (human)
cellular response to xenobiotic stimulusCellular tumor antigen p53Homo sapiens (human)
cellular response to ionizing radiationCellular tumor antigen p53Homo sapiens (human)
cellular response to gamma radiationCellular tumor antigen p53Homo sapiens (human)
cellular response to UV-CCellular tumor antigen p53Homo sapiens (human)
stem cell proliferationCellular tumor antigen p53Homo sapiens (human)
signal transduction by p53 class mediatorCellular tumor antigen p53Homo sapiens (human)
intrinsic apoptotic signaling pathway by p53 class mediatorCellular tumor antigen p53Homo sapiens (human)
reactive oxygen species metabolic processCellular tumor antigen p53Homo sapiens (human)
cellular response to actinomycin DCellular tumor antigen p53Homo sapiens (human)
positive regulation of release of cytochrome c from mitochondriaCellular tumor antigen p53Homo sapiens (human)
cellular senescenceCellular tumor antigen p53Homo sapiens (human)
replicative senescenceCellular tumor antigen p53Homo sapiens (human)
oxidative stress-induced premature senescenceCellular tumor antigen p53Homo sapiens (human)
intrinsic apoptotic signaling pathwayCellular tumor antigen p53Homo sapiens (human)
oligodendrocyte apoptotic processCellular tumor antigen p53Homo sapiens (human)
positive regulation of execution phase of apoptosisCellular tumor antigen p53Homo sapiens (human)
negative regulation of mitophagyCellular tumor antigen p53Homo sapiens (human)
regulation of mitochondrial membrane permeability involved in apoptotic processCellular tumor antigen p53Homo sapiens (human)
regulation of intrinsic apoptotic signaling pathway by p53 class mediatorCellular tumor antigen p53Homo sapiens (human)
positive regulation of miRNA transcriptionCellular tumor antigen p53Homo sapiens (human)
negative regulation of G1 to G0 transitionCellular tumor antigen p53Homo sapiens (human)
negative regulation of miRNA processingCellular tumor antigen p53Homo sapiens (human)
negative regulation of glucose catabolic process to lactate via pyruvateCellular tumor antigen p53Homo sapiens (human)
negative regulation of pentose-phosphate shuntCellular tumor antigen p53Homo sapiens (human)
intrinsic apoptotic signaling pathway in response to hypoxiaCellular tumor antigen p53Homo sapiens (human)
regulation of fibroblast apoptotic processCellular tumor antigen p53Homo sapiens (human)
negative regulation of reactive oxygen species metabolic processCellular tumor antigen p53Homo sapiens (human)
positive regulation of reactive oxygen species metabolic processCellular tumor antigen p53Homo sapiens (human)
negative regulation of stem cell proliferationCellular tumor antigen p53Homo sapiens (human)
positive regulation of cellular senescenceCellular tumor antigen p53Homo sapiens (human)
positive regulation of intrinsic apoptotic signaling pathwayCellular tumor antigen p53Homo 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)
inositol phosphate metabolic processInositol hexakisphosphate kinase 1Homo sapiens (human)
phosphatidylinositol phosphate biosynthetic processInositol hexakisphosphate kinase 1Homo sapiens (human)
negative regulation of cold-induced thermogenesisInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol phosphate biosynthetic processInositol hexakisphosphate kinase 1Homo sapiens (human)
[Information is prepared from geneontology information from the June-17-2024 release]

Molecular Functions (54)

Processvia Protein(s)Taxonomy
cytokine activityInterferon betaHomo sapiens (human)
cytokine receptor bindingInterferon betaHomo sapiens (human)
type I interferon receptor bindingInterferon betaHomo sapiens (human)
protein bindingInterferon betaHomo sapiens (human)
chloramphenicol O-acetyltransferase activityInterferon betaHomo sapiens (human)
TAP bindingHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
signaling receptor bindingHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
protein bindingHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
peptide antigen bindingHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
TAP bindingHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
protein-folding chaperone bindingHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
transcription cis-regulatory region bindingCellular tumor antigen p53Homo sapiens (human)
RNA polymerase II cis-regulatory region sequence-specific DNA bindingCellular tumor antigen p53Homo sapiens (human)
DNA-binding transcription factor activity, RNA polymerase II-specificCellular tumor antigen p53Homo sapiens (human)
cis-regulatory region sequence-specific DNA bindingCellular tumor antigen p53Homo sapiens (human)
core promoter sequence-specific DNA bindingCellular tumor antigen p53Homo sapiens (human)
TFIID-class transcription factor complex bindingCellular tumor antigen p53Homo sapiens (human)
DNA-binding transcription repressor activity, RNA polymerase II-specificCellular tumor antigen p53Homo sapiens (human)
DNA-binding transcription activator activity, RNA polymerase II-specificCellular tumor antigen p53Homo sapiens (human)
protease bindingCellular tumor antigen p53Homo sapiens (human)
p53 bindingCellular tumor antigen p53Homo sapiens (human)
DNA bindingCellular tumor antigen p53Homo sapiens (human)
chromatin bindingCellular tumor antigen p53Homo sapiens (human)
DNA-binding transcription factor activityCellular tumor antigen p53Homo sapiens (human)
mRNA 3'-UTR bindingCellular tumor antigen p53Homo sapiens (human)
copper ion bindingCellular tumor antigen p53Homo sapiens (human)
protein bindingCellular tumor antigen p53Homo sapiens (human)
zinc ion bindingCellular tumor antigen p53Homo sapiens (human)
enzyme bindingCellular tumor antigen p53Homo sapiens (human)
receptor tyrosine kinase bindingCellular tumor antigen p53Homo sapiens (human)
ubiquitin protein ligase bindingCellular tumor antigen p53Homo sapiens (human)
histone deacetylase regulator activityCellular tumor antigen p53Homo sapiens (human)
ATP-dependent DNA/DNA annealing activityCellular tumor antigen p53Homo sapiens (human)
identical protein bindingCellular tumor antigen p53Homo sapiens (human)
histone deacetylase bindingCellular tumor antigen p53Homo sapiens (human)
protein heterodimerization activityCellular tumor antigen p53Homo sapiens (human)
protein-folding chaperone bindingCellular tumor antigen p53Homo sapiens (human)
protein phosphatase 2A bindingCellular tumor antigen p53Homo sapiens (human)
RNA polymerase II-specific DNA-binding transcription factor bindingCellular tumor antigen p53Homo sapiens (human)
14-3-3 protein bindingCellular tumor antigen p53Homo sapiens (human)
MDM2/MDM4 family protein bindingCellular tumor antigen p53Homo sapiens (human)
disordered domain specific bindingCellular tumor antigen p53Homo sapiens (human)
general transcription initiation factor bindingCellular tumor antigen p53Homo sapiens (human)
molecular function activator activityCellular tumor antigen p53Homo sapiens (human)
promoter-specific chromatin bindingCellular tumor antigen p53Homo 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)
inositol-1,3,4,5,6-pentakisphosphate kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol hexakisphosphate kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol heptakisphosphate kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol hexakisphosphate 5-kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
protein bindingInositol hexakisphosphate kinase 1Homo sapiens (human)
ATP bindingInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol hexakisphosphate 1-kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol hexakisphosphate 3-kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol 5-diphosphate pentakisphosphate 5-kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
inositol diphosphate tetrakisphosphate kinase activityInositol hexakisphosphate kinase 1Homo sapiens (human)
[Information is prepared from geneontology information from the June-17-2024 release]

Ceullar Components (36)

Processvia Protein(s)Taxonomy
extracellular spaceInterferon betaHomo sapiens (human)
extracellular regionInterferon betaHomo sapiens (human)
Golgi membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
endoplasmic reticulumHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
Golgi apparatusHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
plasma membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
cell surfaceHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
ER to Golgi transport vesicle membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
secretory granule membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
phagocytic vesicle membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
early endosome membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
recycling endosome membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
extracellular exosomeHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
lumenal side of endoplasmic reticulum membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
MHC class I protein complexHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
extracellular spaceHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
external side of plasma membraneHLA class I histocompatibility antigen, B alpha chain Homo sapiens (human)
nuclear bodyCellular tumor antigen p53Homo sapiens (human)
nucleusCellular tumor antigen p53Homo sapiens (human)
nucleoplasmCellular tumor antigen p53Homo sapiens (human)
replication forkCellular tumor antigen p53Homo sapiens (human)
nucleolusCellular tumor antigen p53Homo sapiens (human)
cytoplasmCellular tumor antigen p53Homo sapiens (human)
mitochondrionCellular tumor antigen p53Homo sapiens (human)
mitochondrial matrixCellular tumor antigen p53Homo sapiens (human)
endoplasmic reticulumCellular tumor antigen p53Homo sapiens (human)
centrosomeCellular tumor antigen p53Homo sapiens (human)
cytosolCellular tumor antigen p53Homo sapiens (human)
nuclear matrixCellular tumor antigen p53Homo sapiens (human)
PML bodyCellular tumor antigen p53Homo sapiens (human)
transcription repressor complexCellular tumor antigen p53Homo sapiens (human)
site of double-strand breakCellular tumor antigen p53Homo sapiens (human)
germ cell nucleusCellular tumor antigen p53Homo sapiens (human)
chromatinCellular tumor antigen p53Homo sapiens (human)
transcription regulator complexCellular tumor antigen p53Homo sapiens (human)
protein-containing complexCellular tumor antigen p53Homo sapiens (human)
plasma membraneGamma-aminobutyric acid receptor subunit gamma-2Rattus norvegicus (Norway rat)
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)
plasma membraneGamma-aminobutyric acid receptor subunit alpha-1Rattus norvegicus (Norway rat)
plasma membraneGamma-aminobutyric acid receptor subunit beta-2Rattus norvegicus (Norway rat)
fibrillar centerInositol hexakisphosphate kinase 1Homo sapiens (human)
nucleoplasmInositol hexakisphosphate kinase 1Homo sapiens (human)
cytosolInositol hexakisphosphate kinase 1Homo sapiens (human)
nucleusInositol hexakisphosphate kinase 1Homo sapiens (human)
cytoplasmInositol hexakisphosphate kinase 1Homo sapiens (human)
[Information is prepared from geneontology information from the June-17-2024 release]

Bioassays (46)

Assay IDTitleYearJournalArticle
AID1296008Cytotoxic Profiling of Annotated Libraries Using Quantitative High-Throughput Screening2020SLAS discovery : advancing life sciences R & D, 01, Volume: 25, Issue:1
Cytotoxic Profiling of Annotated and Diverse Chemical Libraries Using Quantitative High-Throughput Screening.
AID1347083qHTS for Inhibitors of the Functional Ribonucleoprotein Complex (vRNP) of Lassa (LASV) Arenavirus: Viability assay - alamar blue signal for LASV Primary Screen2020Antiviral research, 01, Volume: 173A cell-based, infectious-free, platform to identify inhibitors of lassa virus ribonucleoprotein (vRNP) activity.
AID1347094qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for BT-37 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347092qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for A673 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1346987P-glycoprotein substrates identified in KB-8-5-11 adenocarcinoma cell line, qHTS therapeutic library screen2019Molecular pharmacology, 11, Volume: 96, Issue:5
A High-Throughput Screen of a Library of Therapeutics Identifies Cytotoxic Substrates of P-glycoprotein.
AID1347089qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for TC32 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347097qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for Saos-2 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347108qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for Rh41 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347424RapidFire Mass Spectrometry qHTS Assay for Modulators of WT P53-Induced Phosphatase 1 (WIP1)2019The Journal of biological chemistry, 11-15, Volume: 294, Issue:46
Physiologically relevant orthogonal assays for the discovery of small-molecule modulators of WIP1 phosphatase in high-throughput screens.
AID1347106qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for control Hh wild type fibroblast cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1346986P-glycoprotein substrates identified in KB-3-1 adenocarcinoma cell line, qHTS therapeutic library screen2019Molecular pharmacology, 11, Volume: 96, Issue:5
A High-Throughput Screen of a Library of Therapeutics Identifies Cytotoxic Substrates of P-glycoprotein.
AID1347407qHTS to identify inhibitors of the type 1 interferon - major histocompatibility complex class I in skeletal muscle: primary screen against the NCATS Pharmaceutical Collection2020ACS chemical biology, 07-17, Volume: 15, Issue:7
High-Throughput Screening to Identify Inhibitors of the Type I Interferon-Major Histocompatibility Complex Class I Pathway in Skeletal Muscle.
AID1347104qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for RD cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347082qHTS for Inhibitors of the Functional Ribonucleoprotein Complex (vRNP) of Lassa (LASV) Arenavirus: LASV Primary Screen - GLuc reporter signal2020Antiviral research, 01, Volume: 173A cell-based, infectious-free, platform to identify inhibitors of lassa virus ribonucleoprotein (vRNP) activity.
AID1347105qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for MG 63 (6-TG R) cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1745845Primary qHTS for Inhibitors of ATXN expression
AID1347101qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for BT-12 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347098qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for SK-N-SH cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347095qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for NB-EBc1 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1508630Primary qHTS for small molecule stabilizers of the endoplasmic reticulum resident proteome: Secreted ER Calcium Modulated Protein (SERCaMP) assay2021Cell reports, 04-27, Volume: 35, Issue:4
A target-agnostic screen identifies approved drugs to stabilize the endoplasmic reticulum-resident proteome.
AID1347102qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for Rh18 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347093qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for SK-N-MC cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347091qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for SJ-GBM2 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347154Primary screen GU AMC qHTS for Zika virus inhibitors2020Proceedings of the National Academy of Sciences of the United States of America, 12-08, Volume: 117, Issue:49
Therapeutic candidates for the Zika virus identified by a high-throughput screen for Zika protease inhibitors.
AID1347086qHTS for Inhibitors of the Functional Ribonucleoprotein Complex (vRNP) of Lymphocytic Choriomeningitis Arenaviruses (LCMV): LCMV Primary Screen - GLuc reporter signal2020Antiviral research, 01, Volume: 173A cell-based, infectious-free, platform to identify inhibitors of lassa virus ribonucleoprotein (vRNP) activity.
AID1347100qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for LAN-5 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347099qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for NB1643 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347090qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for DAOY cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347107qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for Rh30 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID651635Viability Counterscreen for Primary qHTS for Inhibitors of ATXN expression
AID1347096qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for U-2 OS cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
AID1347425Rhodamine-PBP qHTS Assay for Modulators of WT P53-Induced Phosphatase 1 (WIP1)2019The Journal of biological chemistry, 11-15, Volume: 294, Issue:46
Physiologically relevant orthogonal assays for the discovery of small-molecule modulators of WIP1 phosphatase in high-throughput screens.
AID1347103qHTS of pediatric cancer cell lines to identify multiple opportunities for drug repurposing: Primary screen for OHS-50 cells2018Oncotarget, Jan-12, Volume: 9, Issue:4
Quantitative high-throughput phenotypic screening of pediatric cancer cell lines identifies multiple opportunities for drug repurposing.
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.
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.
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.
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.
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.
AID513086Antiapoptotic activity against Caenorhabditis elegans ced-3(n2438) mutant assessed as number of extra cells in anterior pharynx at 50 to 250 mM dissolved in soybean oil2006Nature chemical biology, Jun, Volume: 2, Issue:6
The nongenotoxic carcinogens naphthalene and para-dichlorobenzene suppress apoptosis in Caenorhabditis elegans.
AID1454229Cytotoxicity against human NCI-H460 cells incubated for 24 hrs by MTT assay2017Bioorganic & medicinal chemistry letters, 08-01, Volume: 27, Issue:15
Novel phenanthrene and isocoumarin from the rhizomes of Dioscorea nipponica Makino subsp. rosthornii (Prain et Burkill) C. T. Ting (Dioscoreaceae).
[information is prepared from bioassay data collected from National Library of Medicine (NLM), extracted Dec-2023]

Research

Studies (3,272)

TimeframeStudies, This Drug (%)All Drugs %
pre-1990496 (15.16)18.7374
1990's294 (8.99)18.2507
2000's606 (18.52)29.6817
2010's1100 (33.62)24.3611
2020's776 (23.72)2.80
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Market Indicators

Research Demand Index: 57.88

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 Index57.88 (24.57)
Research Supply Index8.15 (2.92)
Research Growth Index4.90 (4.65)
Search Engine Demand Index95.32 (26.88)
Search Engine Supply Index2.00 (0.95)

This Compound (57.88)

All Compounds (24.57)

Study Types

Publication TypeThis drug (%)All Drugs (%)
Trials28 (0.81%)5.53%
Reviews172 (5.01%)6.00%
Case Studies7 (0.20%)4.05%
Observational1 (0.03%)0.25%
Other3,228 (93.95%)84.16%
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]