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dichlorodiphenyl dichloroethylene

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Description

Dichlorodiphenyl dichloroethylene (DDE) is a persistent organic pollutant (POP) that is formed as a breakdown product of the insecticide DDT. DDE is highly lipophilic and accumulates in the environment and in the fat tissues of animals. It is known to disrupt endocrine function, particularly by interfering with estrogen receptors. Studies have shown that DDE exposure is associated with adverse health effects, including reproductive problems, immune suppression, and cancer. It is of significant environmental concern due to its persistence, bioaccumulation, and long-range transport. DDE is a subject of ongoing research to understand its impact on human and animal health, as well as to develop strategies for remediation and prevention of its further accumulation in the environment.'

Dichlorodiphenyl Dichloroethylene: An organochlorine pesticide, it is the ethylene metabolite of DDT. [Medical Subject Headings (MeSH), National Library of Medicine, extracted Dec-2023]

Cross-References

ID SourceID
PubMed CID3035
CHEMBL ID363207
CHEBI ID16598
SCHEMBL ID177472
MeSH IDM0005687

Synonyms (131)

Synonym
BIDD:ER0615
BIDD:PXR0109
MLS002152918
smr001224518
p,p'-(dichlorodiphenyl)-2,2-dichloroethylene
CHEBI:16598 ,
1-chloro-4-[2,2-dichloro-1-(4-chlorophenyl)ethenyl]benzene
benzene, 1,1'-(dichloroethenylidene)bis[4-chloro-
dichlorodiphenyldichloroethylene
1-chloro-4-[2,2-dichloro-1-(4-chlorophenyl)vinyl]benzene
ethylene, 1,1-dichloro-2,2-bis(p-chlorophenyl)-
DIVK1C_006678
1,1-dichloro-2,2-bis(4'-chlorophenyl)ethylene (dde)
1,1'-(2,2-dichloroethene-1,1-diyl)bis(4-chlorobenzene)
SPECTRUM_001941
BSPBIO_002501
SPECTRUM5_002042
MLS001055473
p,p'-dde (p,p'-dichlorodiphenyldichloroethylene)
NCGC00090888-01
p,p'-dichlorodiphenyl dichloroethylene
NCGC00090888-02
1,1-dichloro-2,2-bis(p-chlorophenyl)ethene
brn 1913355
2,2-bis(4-chlorophenyl)-1,1-dichloroethylene
ai3-01715
dde (van)
dde, p,p'-
hsdb 1625
benzene, 1,1'-(dichloroethenylidene)bis(4-chloro-
2,2-bis(p-chlorophenyl)-1,1-dichloroethylene
1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene
1,1'-(dichloroethenylidene)bis(4-chlorobenzene)
nsc 1153
1,1-bis(p-chlorophenyl)-2,2-dichloroethylene
1,1-dichloro-2,2-bis(para-chlorophenyl) ethylene
2,2-bis(4-chlorophenyl)-1,1-dichloroethene
p,p'-dichlorodiphenoldichloroethylene
para,para'-dde
dichlorodiphenyl dichloroethene
ccris 193
einecs 200-784-6
1,1-dichloro-2,2-di(p-chlorophenyl)ethylene
72-55-9
1,2-bis(p-chlorophenyl)ethene
1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene
1,2-bis(p-chlorophenyl)ethylene
benzene,1'-(dichloroethenylidene)bis[4-chloro-
p,p'-(dichlorodiphenyl)dichloroethylene
wln: gyguyr dg&r dg
nsc1153
ddt dehydrochloride
ethylene,1-dichloro-2,2-bis(p-chlorophenyl)-
1,1-dichloro-2,2-bis(4'-chlorophenyl)ethylene
1,1'-(dichloroethenylidene)bis[4-chlorobenzene]
nci-c00555
p,p'-dde
4,4'-dde
1,2-di(p-chlorophenyl)ethylene
DDE ,
C04596
nsc-1153
p,2-dichloroethylene
1,1-dichloro-2,2-bis(4-chlorophenyl)ethene, 99%
NCGC00090888-05
NCGC00090888-04
NCGC00090888-03
KBIOSS_002495
KBIO3_002001
KBIO2_002487
KBIO1_001622
KBIO2_007623
KBIO2_005055
KBIOGR_001221
SPECPLUS_000582
SPBIO_001710
SPECTRUM4_000701
SPECTRUM3_000861
SPECTRUM2_001865
SPECTRUM330072
p,p'-dichlorodiphenyldichloroethylene
p,p' -dde
NCGC00090888-06
dichlorodiphenyl dichloroethylene
B0133
A19100
CHEMBL363207 ,
1,1-dichloro-2,2-bis(4-chlorophenyl)ethene
NCGC00090888-09
NCGC00090888-07
NCGC00090888-08
NCGC00090888-10
4m7fs82u08 ,
unii-4m7fs82u08
68679-99-2
NCGC00254155-01
NCGC00258812-01
tox21_201260
cas-72-55-9
dtxsid9020374 ,
dtxcid90374
tox21_300109
HMS2230C07
CCG-39403
bdbm50410512
FT-0609172
AKOS015902433
benzene, 1,1'-(2,2-dichloroethenylidene)bis(4-chloro-
1,1'-(2,2-dichloro-1,1-ethenediyl)bis(4-chlorobenzene)
dde [hsdb]
S5437
HMS3369G06
SCHEMBL177472
1-chloro-4-[2,2-dichloro-1-(4-chlorophenyl)vinyl]benzene #
dde(p,p')
mfcd00000837
6ws ,
1-[2,2-bis(chloranyl)-1-(4-chlorophenyl)ethenyl]-4-chloranyl-benzene
4,4'-dde, pestanal(r), analytical standard
4,4'-dde 10 microg/ml in acetonitrile
4,4'-dde 10 microg/ml in cyclohexane
4,4'-dde 100 microg/ml in cyclohexane
4,4'-dde d8
4.4-dde
Q409592
4,4'-dde 1000 microg/ml in toluene
dde; nsc 1153; p,p'-dde
CS-0014085
D88610
HY-B1986
BS-44129

Research Excerpts

Effects

POP accumulating in Antarctic krill (Euphausia superba), which is a key Southern Ocean species. Dichlorodiphenyl dichloroethylene has been shown to reduce the duration of breast feeding in two studies.

ExcerptReferenceRelevance
"p,p'-dichlorodiphenyl dichloroethylene (p,p'-DDE) has been identified as a dominant POP accumulating in Antarctic krill (Euphausia superba), which is a key Southern Ocean species."( Altered developmental timing in early life stages of Antarctic krill (Euphausia superba) exposed to p,p'-DDE.
Bengtson Nash, SM; Kawaguchi, S; Kukkonen, JV; Leppänen, MT; Poulsen, AH, 2011
)
0.82
"Dichlorodiphenyl dichloroethylene (DDE) has been shown to reduce the duration of breast feeding in two studies. "( Maternal concentration of dichlorodiphenyl dichloroethylene (DDE) and initiation and duration of breast feeding.
Brooks, K; Davis, S; Fussman, C; Karmaus, W, 2005
)
2.07

Toxicity

ExcerptReferenceRelevance
" This treatment also resulted in a higher level of radioactivity in the adrenals of the pups than in the maternal adrenals, both at a subtoxic and at a toxic dose."( Adrenocortical toxicity of 3-methylsulphonyl-DDE; 3: Studies in fetal and suckling mice.
Bergman, A; Brandt, I; Jönsson, CJ; Lund, BO, 1992
)
0.28
" DDT metabolism in a North American species of planarian leads to the formation of metabolites more toxic than the parent compound."( Comparative acute toxicity of DDT metabolites among American and European species of planarians.
Bonner, JC; Wells, MR, 1987
)
0.27
" Because the regulation of the lipid composition of the membrane is a common strategy in response to adverse growth conditions, we studied the effects of DDE on the lipid composition and the consequent alterations of membrane physical properties in comparison to the parental compound DDT."( Membrane lipid composition of Bacillus stearothermophilus as affected by lipophilic environmental pollutants: an approach to membrane toxicity assessment.
Antunes-Madeira, MC; Donato, MM; Jurado, AS; Madeira, VM, 2000
)
0.31
" Increases in the absolute and relative (ratio to body weight) liver weights were observed as a typical toxic response after a single or repeated exposure to DDT."( A comparative study on the reliablility of toxicokinetic parameters for predicting hepatotoxicity of DDT in rats receiving a single or repeated administration.
Harada, T; Kobayashi, H; Takeda, M; Tomiyama, N; Watanabe, M, 2003
)
0.32
" Furthermore, the temporal trend in the toxic response using body residue as the dose metric is steep and found to be similar to another chlorinated hydrocarbon, pentachlorobenzene, but was more potent than that found for polycyclic aromatic hydrocarbons (PAHs)."( Time-dependent toxicity of dichlorodiphenyldichloroethylene to Hyalella azteca.
Gossiaux, DC; Landrum, PF; Lewis, JS; McElroy, M; Robinson, SD; Steevens, JA, 2005
)
0.33
"The Quick Easy Cheap Effective Rugged and Safe multiresidue method (QuEChERS) has been validated for the extraction of 15 organochlorine pesticides (OCPs) in completely different matrices of traditional Chinese medicine (TCM)."( Analysis of pesticide residues using the Quick Easy Cheap Effective Rugged and Safe (QuEChERS) pesticide multiresidue method in traditional Chinese medicine by gas chromatography with electron capture detection.
Chen, B; Chen, J; Liu, Y; Wu, J; Xu, R; Yang, M; Zhao, R, 2011
)
0.37
"We investigated the usefulness of an integrated computational systems biology approach in a case study involving the isomers and metabolites of the pesticide dichlorodiphenyltrichloroethane (DDT) to ascertain their possible links to relevant adverse effects."( Application of computational systems biology to explore environmental toxicity hazards.
Audouze, K; Grandjean, P, 2011
)
0.37
" Compared with the reported DDT levels demonstrated to have toxic effects on frogs, DDTs in the present frogs are unlikely to constitute an immediate health risk."( DDTs in rice frogs (Rana limnocharis) from an agricultural site, South China: tissue distribution, biomagnification, and potential toxic effects assessment.
Chen, SJ; Luo, XJ; Mai, BX; Wu, JP; Zhang, Y, 2012
)
0.38
" It has been shown in the literature that equilibrium SPME fiber concentrations reflect the bioavailable concentrations of hydrophobic contaminants, so these fiber concentrations should be a useful metric for assessing toxic effects from the bioavailable contaminant providing a framework to expand the use of SPME fibers beyond estimation of bioaccumulation."( Use of solid phase microextraction to estimate toxicity: relating fiber concentrations to toxicity--part I.
Ding, Y; Harwood, AD; Landrum, PF; Lydy, MJ; You, J, 2012
)
0.38
" The present study extends the use of fiber concentrations to organism body residues to specifically address biotransformation and provide the link to toxic response."( Use of solid phase microextraction to estimate toxicity: relating fiber concentrations to body residues--part II.
Ding, Y; Harwood, AD; Landrum, PF; Lydy, MJ; You, J, 2012
)
0.38
" It is one of the most toxic compounds belonging to organochlorines."( The Crucial Involvement of Retinoid X Receptors in DDE Neurotoxicity.
Kajta, M; Krzeptowski, W; Lasoń, W; Litwa, E; Rzemieniec, J; Wnuk, A; Wójtowicz, AK, 2016
)
0.43
" Predicted toxic units of DDX in porewater were utilized to distinguish between toxicity from DDT and that of DDD and DDE."( Full-Life Cycle Toxicity Assessment of Sediment-Bound DDT and Its Degradation Products on Chironomus dilutus.
Li, H; Ma, P; You, J, 2019
)
0.51

Pharmacokinetics

ExcerptReferenceRelevance
"Physiologically based pharmacokinetic (PBPK) modeling in marine mammals is a challenge because of the lack of parameter information and the ban on exposure experiments."( Application of Bayesian population physiologically based pharmacokinetic (PBPK) modeling and Markov chain Monte Carlo simulations to pesticide kinetics studies in protected marine mammals: DDT, DDE, and DDD in harbor porpoises.
Blust, R; Covaci, A; Das, K; Weijs, L; Yang, RS, 2013
)
0.39
" Unique data from Australia provide an opportunity to study this finding using simple pharmacokinetic (PK) models."( Use of a simple pharmacokinetic model to study the impact of breast-feeding on infant and toddler body burdens of PCB 153, BDE 47, and DDE.
Lorber, M; Toms, LL, 2017
)
0.46
"To document serum p,p'-DDT/E levels in 47 mothers and children participating in the Venda Health Examination of Mothers, Babies and their Environment (VHEMBE), a study conducted in an area where IRS insecticides are used annually, and to evaluate the precision and accuracy of a published pharmacokinetic model for the estimation of children's p,p'-DDT/E levels."( Early-life exposure to p,p'-DDT and p,p'-DDE in South African children participating in the VHEMBE study: An assessment using repeated serum measurements and pharmacokinetic modeling.
Bornman, R; Chevrier, J; Eskenazi, B; Ngueta, G; Rauch, S; Verner, MA, 2018
)
0.48
" A pharmacokinetic model of gestational and lactational exposure was used to estimate children's p,p'-DDT/E levels during pregnancy and the first two years of life, and estimated levels were compared to measured levels."( Early-life exposure to p,p'-DDT and p,p'-DDE in South African children participating in the VHEMBE study: An assessment using repeated serum measurements and pharmacokinetic modeling.
Bornman, R; Chevrier, J; Eskenazi, B; Ngueta, G; Rauch, S; Verner, MA, 2018
)
0.48
" The pharmacokinetic model may be useful to estimate children's levels in the VHEMBE population."( Early-life exposure to p,p'-DDT and p,p'-DDE in South African children participating in the VHEMBE study: An assessment using repeated serum measurements and pharmacokinetic modeling.
Bornman, R; Chevrier, J; Eskenazi, B; Ngueta, G; Rauch, S; Verner, MA, 2018
)
0.48

Bioavailability

ExcerptReferenceRelevance
"Field experiments were conducted to assess the bioavailability of weathered p,p'-DDE in soil to plants in the Cucurbita (squash, pumpkin) and Cucumis (cucumber, melon) genera."( Differential bioavailability of field-weathered p,p'-DDE to plants of the Cucurbita and Cucumis genera.
White, JC, 2002
)
0.31
" The data indicate that the addition of low molecular weight organic acids causes the partial dissolution of the soil structure through the chelation of inorganic structural ions, potentially enhancing bioavailability and having implications for the phytoremediation of persistent organic pollutants in soil."( Role of organic acids in enhancing the desorption and uptake of weathered p,p'-DDE by Cucurbita pepo.
Eitzer, BD; Iannucci-Berger, W; Lee, WY; Mattina, MI; White, JC, 2003
)
0.32
" The data suggest that the prediction of contaminant bioavailability should consider interactions among species."( Multi-species interactions impact the accumulation of weathered 2,2-bis (p-chlorophenyl)-1,1-dichloroethylene (p,p'-DDE) from soil.
Kelsey, JW; White, JC, 2005
)
0.33
" Finally, no change in the bioavailability of the compound was observed in successive generations of plants grown in the same contaminated soil."( Growth conditions impact 2,2-bis(p-chlorophenyl)-1,1-dichloroethylene (p,p'-DDE) accumulation by Cucurbita pepo.
Colino, A; Kelsey, JW; Koberle, M; White, JC, 2006
)
0.33
" A green-house study was conducted to determine the bioavailability of p,p'-DDD and p,p'-DDE to grains of rice and the influences of traditional Chinese farming practices on their bioaccumulation."( Bioavailability to grains of rice of aged and fresh DDD and DDE in soils.
Bian, Y; Jiang, X; Wang, F; Yang, X; Yao, F; Yu, G, 2007
)
0.34
" Surfactant-mediated increases in contaminant bioavailability are an unexpectedly complex process and clearly present unanticipated concerns over pollutant exposure to nontarget organisms."( Surfactants differentially impact p,p'-DDE accumulation by plant and earthworm species.
Kelsey, JW; Peters, R; White, JC, 2007
)
0.34
" Such models are important to understand bioavailability and mobility limitations of these chemicals in the aquatic environment."( Triple domain in situ sorption modeling of organochlorine pesticides, polychlorobiphenyls, polyaromatic hydrocarbons, polychlorinated dibenzo-p-dioxins, and polychlorinated dibenzofurans in aquatic sediments.
Kaag, K; Koelmans, AA; Peeters, ET; Sneekes, A, 2009
)
0.35
"Laboratory experiments were conducted to assess the effects of soil sterilization on the bioavailability of spiked p,p'-DDE and anthracene to the earthworms Eisenia fetida and Lumbricus terrestris."( Sterilization affects soil organic matter chemistry and bioaccumulation of spiked p,p'-DDE and anthracene by earthworms.
Kelsey, JW; Melnick, AM; Peters, RD; Slizovskiy, IB, 2010
)
0.36
"The rapid-desorbing fraction plays an important role in the bioavailability of organic pollutants in soil."( Tenax TA extraction to assess the bioavailability of DDTs in cotton field soils.
Gu, C; Jiang, X; Wang, F; Yang, X, 2010
)
0.36
"Few studies have been conducted examining the distribution of different-sized particles in sediment and its potential impact on bioavailability of sediment-associated contaminants."( Bioavailability of hydrophobic organic contaminants in sediment with different particle-size distributions.
Li, H; Lydy, MJ; Mehler, WT; Pang, J; Sun, B; You, J, 2011
)
0.37
"The ability of polydimethlysiloxane coated solid phase microextraction (SPME) fibers to predict bioavailability has been documented for a number of species and compounds."( A comparison of exposure methods for SPME-based bioavailability estimates.
Harwood, AD; Landrum, PF; Lydy, MJ, 2012
)
0.38
" The bioavailability of p,p'-DDE, p,p'-DDT, As, Cd, Cu, and Pb from five field-aged New Zealand orchards and three grazing soils was assessed by using a 28-d bioassay with Aporrectodea caliginosa and chemical assays."( Comparison of earthworm and chemical assays of the bioavailability of aged 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene, 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane, and heavy metals in orchard soils.
Gaw, S; Jensen, J; Kim, N; Northcott, G; Wilkins, A, 2012
)
0.38
"05 for both regressions) between the PRC-calibrated equilibrium concentrations of 1,1-dichloro-2,2-bis-(chlorophenyl) ethylene (p,p'-DDE) and polychlorinated biphenyl (PCB)-153 and the lipid normalized levels in worms (Neanthes arenaceodentata) was obtained in co-exposure tests under simulating field conditions, probably resulting from slightly overestimated bioavailability because of the hysteretic desorption of PRCs and toxic effects."( Isotopic exchange on solid-phase micro extraction fiber in sediment under stagnant conditions: Implications for field application of performance reference compound calibration.
Bao, LJ; Gan, J; Jia, F; Wu, X; Zeng, EY, 2016
)
0.43
" Measuring contaminant bioavailability in a before-and-after manner lends to improved assessment of remediation effectiveness."( Comparing different methods for assessing contaminant bioavailability during sediment remediation.
Gan, J; Jia, F; Liao, C; Taylor, A; Xue, J, 2016
)
0.43
" Changes in the sorption and potential bioavailability of spiked and native p,p'-DDE were measured by supercritical fluid extraction (SFE), XAD-assisted extraction (XAD), and solid-phase microextraction (SPME) and linked to qualitative changes in soil organic matter (SOM) chemistry measured by diffuse reflectance infrared Fourier-transform (DRIFT) spectroscopy."( Influence of soil γ-irradiation and spiking on sorption of p,p'-DDE and soil organic matter chemistry.
Bielská, L; Chrást, L; Hofman, J; Scherr, KE; Škulcová, L, 2018
)
0.48
"Compared to the total chemical concentration, bioavailability is a better measurement of risks of hydrophobic organic contaminants (HOCs) to biota in contaminated soil or sediment."( Evaluation of different methods for assessing bioavailability of DDT residues during soil remediation.
Gan, J; Schlenk, D; Taylor, A; Wang, J; Xu, C, 2018
)
0.48

Dosage Studied

ExcerptRelevanceReference
" After 54 days of feeding, six dosed bats were frozen and the remaining 16 were starved to death."( Experimental feeding of DDE and PCB to female big brown bats (Eptesicus fuscus).
Clark, DR; Prouty, RM, 1977
)
0.26
" The changes noted after 2 days of DDMU diet were confirmed by measurements on birds 18 h after oral dosing the DDMU."( The effects of 1,1-di(p-chlorophenyl)-2-chloroethylene on plasma enzymes and blood constituents in the Japanese quail.
Bunyan, PJ; Stanley, PI; Walker, CH; Westlake, GE, 1979
)
0.26
" After 40 days on dosage, during which one dosed bat was killed accidentally, four dosed bats were frozen and the remaining 17 were starved to death."( Effects of DDE on experimentally poisoned free-tailed bats (Tadarida brasiliensis): lethal brain concentrations.
Clark, DR; Kroll, JC, 1977
)
0.26
"The effects of PCBs (polychlorinated biphenyls) or a combination of DDT (1,1,1-trichloro-2,2-bis (p-chlorophenyl) ethane), DDD (1,1-dichloro-2,2-bis (p-chlorophenyl) ethane) and DDE (1,1-dichloro-2,2,-bis (p-chlorophenyl ethylene) on organ weights, liver storage of vitamin A and carotene, selected blood chemistry parameters, and serum protein fractions were determined in penned white pelicans (Pelecanus erythrorhynchos) receiving a daily dosage of these compounds."( Physiological effects of polychlorinated biphenyls or a combination of DDT, DDD, and DDE in penned white pelicans.
Ammann, BM; Call, DJ; Greichus, YA, 1975
)
0.25
" Stoppage of DDE dosage resulted in progressively thicker shells, yet even after 2 years on untreated feed hens laid eggs with shells about 10% thinner than control hens."( Shell thinning and reproductive impairment in black ducks after cessation of DDE dosage.
Longcore, JR; Stendell, RC, 1977
)
0.26
" Residues were determined in milk at 5-day intervals during the 60-day dosing period and for 60 days after dosing was stopped."( Hexachlorobenzene retention and excretion by dairy cows.
Fries, GF; Marrow, GS, 1976
)
0.26
" Mealworms (Tenebrio molitor) containing organochlorine pollutants were fed to the bats as follows: 5 bats were dosed at 480 ppm DDE, 12 at 150 ppm DDE, 5 at 1000 ppm polychlorinated biphenyl (PCB; Aroclor 1260), and 12 at 15 ppm PCB."( Effects of DDE and PCB (Aroclor 1260) on experimentally poisoned female little brown bats (Myotis lucifugus): lethal brain concentrations.
Clark, DR; Stafford, CJ, 1981
)
0.26
" Dosed eggs were consequently incubated at two temperatures (27."( The environmental contaminant DDE fails to influence the outcome of sexual differentiation in the marine turtle Chelonia mydas.
Georges, A; Limpus, CJ; Maher, B; Podreka, S, 1998
)
0.3
" The chemical was dosed by gavage to pregnant dams at 10 or 100 mg/kg body wt from gestation day 14 to 18."( Impaired male sexual development in perinatal Sprague-Dawley and Long-Evans hooded rats exposed in utero and lactationally to p,p'-DDE.
Archibeque-Engle, S; Casanova, M; Fan, LQ; Heck, HA; Sar, M; You, L, 1998
)
0.3
" Male offsprings display a higher incidence of epididymal and testicular lesions than generally seen with flutamide, P, or V even at high dosage levels."( Administration of potentially antiandrogenic pesticides (procymidone, linuron, iprodione, chlozolinate, p,p'-DDE, and ketoconazole) and toxic substances (dibutyl- and diethylhexyl phthalate, PCB 169, and ethane dimethane sulphonate) during sexual differen
Cooper, RL; Gray, LE; Lambright, C; Mann, P; Ostby, J; Price, M; Wolf, C,
)
0.13
" Pregnant Sprague-Dawley rats were dosed by gavage in corn oil with either 10 or 100 mg DDE per kg body wt per day from Gestation Day (gd) 14 to 18."( Transplacental and lactational transfer of p,p'-DDE in Sprague-Dawley rats.
Archibeque-Engle, S; Casanova, M; Conolly, RB; Gazi, E; Heck, HA; You, L, 1999
)
0.3
" Pregnant Sprague-Dawley rats were dosed daily by gavage with DDE at 0, 10, or 100 mg/kg body weight or with flutamide at 40 mg/kg body weight from gestation day 14 to 18."( Modulation of testosterone-metabolizing hepatic cytochrome P-450 enzymes in developing Sprague-Dawley rats following in utero exposure to p,p'-DDE.
Archibeque-Engle, S; Bruce, JM; Casanova, M; Chan, SK; Corton, JC; Heck, H; You, L, 1999
)
0.3
" Pregnant Long-Evans rats were dosed by gavage from Gestation Day 14 to 18 at 0, 10 (low dose), or 100 (high dose) mg DDE, or 40 mg flutamide/kg body wt (bw)/day (in utero treatment)."( In utero exposure to antiandrogens alters the responsiveness of the prostate to p,p'-DDE in adult rats and may induce prostatic inflammation.
Brenneman, KA; Heck, H; You, L, 1999
)
0.3
") erections we assessed the dose-response effects of p,p-DDE in comparison to the known androgen receptor antagonist flutamide in acute (0."( Effects of an environmental anti-androgen on erectile function in an animal penile erection model.
Adams, MA; Brien, SE; Heaton, JP; Racz, WJ, 2000
)
0.31
" One gram of chromic oxide (Cr2O3) was administered as a digestion marker to dosed calves."( Uptake and excretion of organochlorine compounds in neonatal calves.
Borger, DC; Keller, HL; Willett, LB, 2001
)
0.31
" Eggs were also dosed in two sets."( Effects of binary mixtures of six xenobiotics on hormone concentrations and morphometric endpoints of northern bobwhite quail (Colinus virginianus).
Dickerson, RL; McMurry, CS,
)
0.13
" We found that hepatic aromatase protein in adult male rats was greatly increased after seven daily oral treatments of DDE at a dosage of 100 mg/kg wt."( Induction of hepatic aromatase by p,p'-DDE in adult male rats.
Bartolucci, E; Ploch, S; Sar, M; Whitt, M; You, L, 2001
)
0.31
" The objective of this work was to determine the dose-response relationship between DDE and its antiandrogenic effect in adult, male rats and to quantitate the concentration of DDE in tissues following oral exposures."( Lack of antiandrogenic effects in adult male rats following acute exposure to 2,2-bis(4-chlorophenyl)-1,1-dichloroethylene (p,p'-DDE).
Devito, MJ; Leavens, TL; Sparrow, BR, 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
" An S-shaped dose-response relationship was indicated between P and DDE."( The role of DDE, PCB, coplanar PCB and eggshell parameters for reproduction in the white-tailed sea eagle (Haliaeetus albicilla) in Sweden.
Asplund, L; Bignert, A; Helander, B; Litzén, K; Olsson, A, 2002
)
0.31
"Information about the endocrine effects of different levels of DDT/DDE in human subjects is scarce; dosage may be a determinant factor of the type of effect."( [DDT/DDE concentrations and risk of hypospadias. Pilot case-control study].
Cuevas-Alpuche, J; Dewailly, E; Farías, P; Flores-Luévano, S; Hernández, M; Romano-Riquer, P; Romieu, I; Weber, JP,
)
0.13
" Dose-response relationships of individual agents were characterized over a 6-log concentration range (1 X 10(-2) to 1 X 10(4) ppb)."( Interactive effects of p,p'-dichlorodiphenyldichloroethylene and methoxychlor on hormone synthesis in largemouth bass ovarian cultures.
Borgert, CJ; Gross, TS; Guiney, PD; Osimitz, TG; Price, B; Wells, C, 2004
)
0.32
" However, no consistent dose-response effect was apparent across low, medium, and high exposure categories."( Age at natural menopause and exposure to organochlorine pesticides in Hispanic women.
Akkina, J; Bachand, A; Keefe, T; Reif, J, 2004
)
0.32
" The main results of our study were as follows: (1) azinphos-methyl alone caused a dose-dependent inhibition of plasma and brain ChE activity; (2) p,p'-DDE in combination with azinphos-methyl did not change azinphos-methyl inhibition of ChE activity; and (3) there were suggestions of immunostimulation in birds dosed 1 year previously to p,p'-DDE and of anemia when p,p'-DDE was combined with azinphos-methyl; however, there was no dose-response for these parameters in birds subsequently dosed with p,p'-DDE."( Effects of azinphos-methyl on cholinergic responses and general health in zebra finches (Taeniopygia guttata) after previous treatment with p,p'-DDE.
Bishop, CA; Cheng, KM; Elliott, JE; Gill, H; Williams, TD, 2005
)
0.33
" Long-term breastfeeding leads to a dose-response increase of the concentrations in children's serum during the first year of life."( Breastfeeding and concentrations of HCB and p,p'-DDE at the age of 1 year.
Grimalt, JO; Marco, E; Mazón, C; Ribas-Fitó, N; Sala, M; Sunyer, J, 2005
)
0.33
" The mitogenic response of leukocytes of chinook salmon exposed to p,p'-DDE in vivo exhibited a biphasic dose-response relationship."( p,p'-DDE depresses the immune competence of chinook salmon (Oncorhynchus tshawytscha) leukocytes.
Leong, JA; Misumi, I; Nakanishi, T; Schreck, CB; Vella, AT, 2005
)
0.33
" To provide data useful for the risk assessment of postnatal exposure to POPs, mixtures containing 19 PCBs, DDT, and DDE were prepared according to their concentrations previously measured in the milk of Canadian women, and dose-response effects were tested on the proliferation of MCF7-E3 cells in vitro, and in vivo experiments."( Effects of postnatal exposure to a mixture of polychlorinated biphenyls, p,p'-dichlorodiphenyltrichloroethane, and p-p'-dichlorodiphenyldichloroethene in prepubertal and adult female Sprague-Dawley rats.
Cole, J; Cooke, GM; Desaulniers, D; Leingartner, K; Soumano, K; Wade, M; Yagminas, A; Yang, J,
)
0.13
" The concentrations of estradiol (E2) and progesterone (P) in sera of the dosed mice were determined by the Serozyme kits (Bio-Ekon biotechnology Co."( [Study on reproductive and developmental toxicity of the pregnant mice and their foetus co-administered by p, p'-DDE and beta-BHC].
Chen, L; Liu, GH; Mo, SX; Yang, KD, 2006
)
0.33
"(1) Reproductive effects: with increase of the administered p,p'-DDE and P-BHC,the organ coefficient of uterus and its intraluminal fluid increased, the unterine nidation quantity decreased, the anogenital distance (AGD) and ratio of female to male raised, the concentration of estradiol and progesterone in sera of the dosed mice went up, and the abundant expression of alpha-ER and GnRH mRNA rised while beta-EP dropped in placentae in a dose-dependant manner."( [Study on reproductive and developmental toxicity of the pregnant mice and their foetus co-administered by p, p'-DDE and beta-BHC].
Chen, L; Liu, GH; Mo, SX; Yang, KD, 2006
)
0.33
"There were striking dose-response relations between serum concentrations of six selected POPs and the prevalence of diabetes."( A strong dose-response relation between serum concentrations of persistent organic pollutants and diabetes: results from the National Health and Examination Survey 1999-2002.
Baker, BA; Jacobs, DR; Lee, DH; Lee, IK; Song, K; Steffes, M; Toscano, W, 2006
)
0.33
" It is concluded that although 3-MeSO2-DDE is an interesting candidate for therapeutic use due to its potential characteristics to specifically target adrenocortical tumour cells the slow elimination of the compound might make it challenging to design appropriate dosage regimes."( Pharmacokinetics of the adrenocorticolytic compounds 3-methylsulphonyl-DDE and o,p'-DDD (mitotane) in Minipigs.
Bergman, A; Brandt, I; Cantillana, T; Hermansson, V; Hovander, L; Ljungvall, K; Magnusson, U; Törneke, K, 2008
)
0.35
"We found that treatment with p,p'-DDE induced a dose-response increase in the proliferation of CAMA-1 cells when cultivated in the presence of physiological concentrations of estrogens and androgens, but not in the absence of sex steroids in the cell culture medium."( 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene (p,p'-DDE) disrupts the estrogen-androgen balance regulating the growth of hormone-dependent breast cancer cells.
Aubé, M; Ayotte, P; Larochelle, C, 2008
)
0.35
" VTG-1 and VTG-2 were recommended as the preferred biomarker for assessing anti-androgenic p,p'-DDE because they were the highest up-regulated among the genes and showed good dose-response relationship."( Effects of p,p'-DDE exposure on gonadal development and gene expression in Japanese medaka (Oryzias latipes).
Hu, J; Zhang, Z, 2008
)
0.35
" In addition, in this multivariate model, a non-linear dose-response curve was observed between Total DDT body burden (sum of the three DDT-derivatives measured: p,p'-DDT, p,p'-DDE, and p,p'-DDD) and IGF-I in pre-pubertal male children (6-15years; p=0."( Insulin-like growth factor-I (IGF-I) serum concentrations in healthy children and adolescents: relationship to level of contamination by DDT-derivative pesticides.
Alvarez-León, EE; Apolinario, R; Boada, LD; Lara, PC; Losada, A; Luzardo, OP; Serra-Majem, L; Zumbado, M, 2010
)
0.36
"All DDT metabolites tested revealed a clear dose-response relationship for cytotoxicity in RTG-2 cells, but no dioxin-like activities with RTL-W1 cells."( Toxicity, dioxin-like activities, and endocrine effects of DDT metabolites--DDA, DDMU, DDMS, and DDCN.
Braunbeck, T; Erdinger, L; Hallare, AV; Hollert, H; Otte, JC; Rastall, A; Ricking, M; Schwarzbauer, J; Wetterauer, B, 2012
)
0.38
" Application of the model was restricted by the current lack of quantitative dose-response relationships between non-toxic stress and survival and reproduction."( Modelling the impact of toxic and disturbance stress on white-tailed eagle (Haliaeetus albicilla) populations.
Foppen, RP; Hendriks, AJ; Korsman, JC; Lenders, HJ; Schipper, AM, 2012
)
0.38
" A significant log dose-response relationship was found between log fiber concentration and organism mortality."( Use of solid phase microextraction to estimate toxicity: relating fiber concentrations to toxicity--part I.
Ding, Y; Harwood, AD; Landrum, PF; Lydy, MJ; You, J, 2012
)
0.38
" Its pharmacokinetic properties are not fully elucidated and different dosing regimens have never been compared head to head."( Comparison of two mitotane starting dose regimens in patients with advanced adrenocortical carcinoma.
Allolio, B; Baudin, E; Chadarevian, R; Fassnacht, M; Haak, HR; Kerkhofs, TM; Leboulleux, S; Mantero, F; Mueller, HH; Skogseid, B; Terzolo, M, 2013
)
0.39
"The objective of the study was to investigate the relationship between mitotane dose and plasma concentration comparing two dosing regimens."( Comparison of two mitotane starting dose regimens in patients with advanced adrenocortical carcinoma.
Allolio, B; Baudin, E; Chadarevian, R; Fassnacht, M; Haak, HR; Kerkhofs, TM; Leboulleux, S; Mantero, F; Mueller, HH; Skogseid, B; Terzolo, M, 2013
)
0.39
" In order to elucidate effects of PCBs and DDT on thyroid hormone homeostasis, Sprague-Dawley rats were dosed with PCB153 and p,p'-DDE intraperitoneally (ip) for five consecutive days and sacrificed within 24 h after the last dose."( PCB153 and p,p'-DDE disorder thyroid hormones via thyroglobulin, deiodinase 2, transthyretin, hepatic enzymes and receptors.
Ha, M; Li, L; Liu, C; Yang, K, 2014
)
0.4
" To test the hypothesis that the PI3K/Akt and MAPK pathways would play significant roles in TH imbalance caused by PCBs and DDT, Sprague-Dawley rats were dosed with PCB153 and p,p'-DDE intraperitoneally for 5 consecutive days, and human thyroid follicular epithelial (Nthy-ori 3-1 cell line) were treated with PCB153 and p,p'-DDE for different time."( The PI3K/Akt and ERK pathways elevate thyroid hormone receptor β1 and TRH receptor to decrease thyroid hormones after exposure to PCB153 and p,p'-DDE.
Duan, P; Ha, M; Li, L; Liu, C; Qi, S; Yang, K, 2015
)
0.42
" In the second project, female ICR mice were implanted with silicone and dosed with p,p'-DDE and PCB118 by intraperitoneal injection."( In vivo contaminant partitioning to silicone implants: Implications for use in biomonitoring and body burden.
Anderson, KA; Carozza, S; Kerkvliet, NI; O'Connell, SG; Pennington, J; Rohlman, D, 2015
)
0.42
" After dosing for 104 days, histological assessments and reproductive-endpoints were assessed."( Effects of environmental endocrine disruptors, including insecticides used for malaria vector control on reproductive parameters of male rats.
Bornman, MS; de Jager, C; Joubert, AM; Naidoo, V; Patrick, SM; Pitts, N, 2016
)
0.43
" Difference in difference model results showed that persistent organic pollutant (POP) exposure was positively associated with T2D in a dose-response manner."( The Relationship between Persistent Organic Pollutants Exposure and Type 2 Diabetes among First Nations in Ontario and Manitoba, Canada: A Difference in Difference Analysis.
Batal, M; Chan, HM; Fediuk, K; Hu, X; Ing, A; Marushka, L; Sadik, T; Schwartz, H; Tikhonov, C, 2018
)
0.48
" After adjusting for potential confounding factors such as age, sex and body mass index, all six OCPs showed positive associations with type 2 diabetes in a linear dose-response manner."( Exposure to organochlorine pesticides and the risk of type 2 diabetes in the population of East China.
Han, X; Jiang, G; Li, A; Li, Y; Meng, L; Turyk, ME; Wang, P; Xu, Y; Yang, R; Zhang, F; Zhang, J; Zhang, Q, 2020
)
0.56
" The BART method found dose-response functions similar to the BKMR model."( Prenatal exposure to a mixture of persistent organic pollutants (POPs) and child reading skills at school age.
Braun, JM; Calafat, AM; Chen, A; Dietrich, KN; Jandarov, R; Lanphear, BP; McCandless, L; Sjödin, A; Vuong, AM; Xie, C; Yolton, K; Zhang, H, 2020
)
0.56
" Dose-response meta-analysis suggested a non-linear relation between p,p'-DDE and T2D."( Exposure to the pesticide DDT and risk of diabetes and hypertension: Systematic review and meta-analysis of prospective studies.
Baltazar-Reyes, MC; Cupul-Uicab, LA; Hernández-Mariano, JÁ; Salazar-Martínez, E, 2022
)
0.72
[information is derived through text-mining from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Roles (2)

RoleDescription
persistent organic pollutantAny environmental contaminant that is resistant to environmental degradation through photolytic, biological or chemical processes. Such substances can have significant impact on health and the environment, as they persist in the environment, bioaccumulate in animal tissue and so biomagnify in food chains.
human xenobiotic metaboliteAny human metabolite produced by metabolism of a xenobiotic compound in humans.
[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
chlorophenylethyleneA chlorohydrocarbon that is consists of ethylene in which one or more hydrogens are replaced by chlorophenyl groups.
monochlorobenzenesAny member of the class of chlorobenzenes containing a mono- or poly-substituted benzene ring in which only one substituent is chlorine.
[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, Beta-lactamaseEscherichia coli K-12Potency5.01190.044717.8581100.0000AID485294
Chain A, JmjC domain-containing histone demethylation protein 3AHomo sapiens (human)Potency39.81070.631035.7641100.0000AID504339
Chain A, Ferritin light chainEquus caballus (horse)Potency15.84895.623417.292931.6228AID485281
hypoxia-inducible factor 1 alpha subunitHomo sapiens (human)Potency58.08273.189029.884159.4836AID1224846; AID1224894
RAR-related orphan receptor gammaMus musculus (house mouse)Potency32.71810.006038.004119,952.5996AID1159521; AID1159523
AR proteinHomo sapiens (human)Potency24.52310.000221.22318,912.5098AID1259243; AID1259247; AID588516; AID743053; AID743063
thyroid stimulating hormone receptorHomo sapiens (human)Potency27.82980.001318.074339.8107AID926; AID938
estrogen receptor 2 (ER beta)Homo sapiens (human)Potency37.33210.000657.913322,387.1992AID1259378
nuclear receptor subfamily 1, group I, member 3Homo sapiens (human)Potency28.39220.001022.650876.6163AID1224838; AID1224839; AID1224893
progesterone receptorHomo sapiens (human)Potency6.26260.000417.946075.1148AID1346795
glucocorticoid receptor [Homo sapiens]Homo sapiens (human)Potency39.34440.000214.376460.0339AID588533; AID720691
retinoic acid nuclear receptor alpha variant 1Homo sapiens (human)Potency66.44630.003041.611522,387.1992AID1159552; AID1159553
retinoid X nuclear receptor alphaHomo sapiens (human)Potency6.88940.000817.505159.3239AID1159527; AID1159531
estrogen-related nuclear receptor alphaHomo sapiens (human)Potency52.86550.001530.607315,848.9004AID1224841; AID1224848; AID1224849; AID1259401; AID1259403
farnesoid X nuclear receptorHomo sapiens (human)Potency35.01470.375827.485161.6524AID588526; AID588527; AID743217
pregnane X nuclear receptorHomo sapiens (human)Potency44.52350.005428.02631,258.9301AID1346982; AID720659
estrogen nuclear receptor alphaHomo sapiens (human)Potency47.30100.000229.305416,493.5996AID1259383; AID743075; AID743079
bromodomain adjacent to zinc finger domain 2BHomo sapiens (human)Potency50.11870.707936.904389.1251AID504333
peroxisome proliferator-activated receptor deltaHomo sapiens (human)Potency50.11870.001024.504861.6448AID588535
peroxisome proliferator activated receptor gammaHomo sapiens (human)Potency37.45880.001019.414170.9645AID743191
euchromatic histone-lysine N-methyltransferase 2Homo sapiens (human)Potency25.11890.035520.977089.1251AID504332
thyroid stimulating hormone receptorHomo sapiens (human)Potency25.76150.001628.015177.1139AID1224843; AID1224895; AID1259385; AID1259395
activating transcription factor 6Homo sapiens (human)Potency52.61980.143427.612159.8106AID1159516; AID1159519
nuclear factor of kappa light polypeptide gene enhancer in B-cells 1 (p105), isoform CRA_aHomo sapiens (human)Potency56.855519.739145.978464.9432AID1159509; AID1159518
v-jun sarcoma virus 17 oncogene homolog (avian)Homo sapiens (human)Potency47.02000.057821.109761.2679AID1159526; AID1159528
Histone H2A.xCricetulus griseus (Chinese hamster)Potency123.73970.039147.5451146.8240AID1224845; AID1224896
serine-protein kinase ATM isoform aHomo sapiens (human)Potency39.81070.707925.111941.2351AID485349
chromobox protein homolog 1Homo sapiens (human)Potency44.66840.006026.168889.1251AID540317
potassium voltage-gated channel subfamily H member 2 isoform dHomo sapiens (human)Potency17.90080.01789.637444.6684AID588834
thyroid hormone receptor beta isoform 2Rattus norvegicus (Norway rat)Potency45.86090.000323.4451159.6830AID743065; AID743067
heat shock protein beta-1Homo sapiens (human)Potency49.97140.042027.378961.6448AID743210
mitogen-activated protein kinase 1Homo sapiens (human)Potency15.84890.039816.784239.8107AID995
nuclear factor erythroid 2-related factor 2 isoform 1Homo sapiens (human)Potency61.69700.000627.21521,122.0200AID651741; AID743202; AID743219
lethal(3)malignant brain tumor-like protein 1 isoform IHomo sapiens (human)Potency19.95260.075215.225339.8107AID485360
gemininHomo sapiens (human)Potency28.18380.004611.374133.4983AID624297
cytochrome P450 3A4 isoform 1Homo sapiens (human)Potency7.94330.031610.279239.8107AID884; AID885
lethal factor (plasmid)Bacillus anthracis str. A2012Potency3.57170.020010.786931.6228AID912
Gamma-aminobutyric acid receptor subunit piRattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Cellular tumor antigen p53Homo sapiens (human)Potency58.72330.002319.595674.0614AID651631; AID720552
Gamma-aminobutyric acid receptor subunit beta-1Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit deltaRattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit gamma-2Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-5Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-3Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit gamma-1Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-2Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-4Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit gamma-3Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit alpha-6Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Nuclear receptor ROR-gammaHomo sapiens (human)Potency35.53470.026622.448266.8242AID651802
Gamma-aminobutyric acid receptor subunit alpha-1Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit beta-3Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit beta-2Rattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
GABA theta subunitRattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
Gamma-aminobutyric acid receptor subunit epsilonRattus norvegicus (Norway rat)Potency7.94331.000012.224831.6228AID885
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023]

Inhibition Measurements

ProteinTaxonomyMeasurementAverageMin (ref.)Avg (ref.)Max (ref.)Bioassay(s)
Androgen receptorRattus norvegicus (Norway rat)IC50 (µMol)15.48820.00101.979414.1600AID255211
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023]

Biological Processes (134)

Processvia Protein(s)Taxonomy
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)
[Information is prepared from geneontology information from the June-17-2024 release]

Molecular Functions (38)

Processvia Protein(s)Taxonomy
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)
[Information is prepared from geneontology information from the June-17-2024 release]

Ceullar Components (20)

Processvia Protein(s)Taxonomy
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)
[Information is prepared from geneontology information from the June-17-2024 release]

Bioassays (33)

Assay IDTitleYearJournalArticle
AID255211Inhibitory concentration against recombinant rat androgen receptor expressed in Escherichia coli using [3H]methyltrienolone (R 1881)2005Journal of medicinal chemistry, Sep-08, Volume: 48, Issue:18
Impact of induced fit on ligand binding to the androgen receptor: a multidimensional QSAR study to predict endocrine-disrupting effects of environmental chemicals.
AID1102172Root bioconcentration factor assessed as compound concentration in tomato plant dry mass to compound concentration in soil dry mass after 1 to 15 days post germination2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102176Drug uptake in Solanum lycopersicum (tomato) root after 60 to 151 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102178Drug uptake in Solanum lycopersicum (tomato) root after 16 to 59 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102182Drug uptake in Solanum lycopersicum (tomato) leaves after 16 to 59 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102180Drug uptake in Solanum lycopersicum (tomato) stem after 16 to 59 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102177Drug uptake in Solanum lycopersicum (tomato) stem after 60 to 151 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102171Root bioconcentration factor assessed as compound concentration in tomato plant dry mass to compound concentration in soil dry mass after 16 to 59 days post germination2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102184Drug uptake in Solanum lycopersicum (tomato) leaves after 1 to 15 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102179Drug uptake in Solanum lycopersicum (tomato) leaves after 60 to 151 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102183Drug uptake in Solanum lycopersicum (tomato) stem after 1 to 15 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID433903Hepatotoxicity in mouse assessed as carcinogenic potency2009European journal of medicinal chemistry, Sep, Volume: 44, Issue:9
Development of QSAR models for predicting hepatocarcinogenic toxicity of chemicals.
AID977602Inhibition of sodium fluorescein uptake in OATP1B3-transfected CHO cells at an equimolar substrate-inhibitor concentration of 10 uM2013Molecular pharmacology, Jun, Volume: 83, Issue:6
Structure-based identification of OATP1B1/3 inhibitors.
AID1102181Drug uptake in Solanum lycopersicum (tomato) root after 1 to 15 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102170Root bioconcentration factor assessed as compound concentration in tomato plant dry mass to compound concentration in soil dry mass after 60 to 151 days post germination2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102174Drug uptake in Solanum lycopersicum (tomato) fruit flesh after 60 to 151 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID1102173Drug uptake in Solanum lycopersicum (tomato) fruit peel after 60 to 151 days post germination by GC-ECD analysis2003Journal of agricultural and food chemistry, Feb-26, Volume: 51, Issue:5
Occurrence and distribution of organochlorine pesticides (OCPs) in tomato (Lycopersicon esculentum) crops from organic production.
AID977599Inhibition of sodium fluorescein uptake in OATP1B1-transfected CHO cells at an equimolar substrate-inhibitor concentration of 10 uM2013Molecular pharmacology, Jun, Volume: 83, Issue:6
Structure-based identification of OATP1B1/3 inhibitors.
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.
AID588497High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set2010Current protocols in cytometry, Oct, Volume: Chapter 13Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening.
AID588497High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set2006Cytometry. Part A : the journal of the International Society for Analytical Cytology, May, Volume: 69, Issue:5
Microsphere-based protease assays and screening application for lethal factor and factor Xa.
AID588497High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain F protease, MLPCN compound set2010Assay and drug development technologies, Feb, Volume: 8, Issue:1
High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors.
AID588499High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set2010Current protocols in cytometry, Oct, Volume: Chapter 13Microsphere-based flow cytometry protease assays for use in protease activity detection and high-throughput screening.
AID588499High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set2006Cytometry. Part A : the journal of the International Society for Analytical Cytology, May, Volume: 69, Issue:5
Microsphere-based protease assays and screening application for lethal factor and factor Xa.
AID588499High-throughput multiplex microsphere screening for inhibitors of toxin protease, specifically Botulinum neurotoxin light chain A protease, MLPCN compound set2010Assay and drug development technologies, Feb, Volume: 8, Issue:1
High-throughput multiplex flow cytometry screening for botulinum neurotoxin type a light chain protease inhibitors.
AID1745845Primary qHTS for Inhibitors of ATXN expression
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.
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.
AID651635Viability Counterscreen for Primary qHTS for Inhibitors of ATXN expression
AID1159607Screen for inhibitors of RMI FANCM (MM2) intereaction2016Journal of biomolecular screening, Jul, Volume: 21, Issue:6
A High-Throughput Screening Strategy to Identify Protein-Protein Interaction Inhibitors That Block the Fanconi Anemia DNA Repair Pathway.
AID1159550Human Phosphogluconate dehydrogenase (6PGD) Inhibitor Screening2015Nature cell biology, Nov, Volume: 17, Issue:11
6-Phosphogluconate dehydrogenase links oxidative PPP, lipogenesis and tumour growth by inhibiting LKB1-AMPK signalling.
[information is prepared from bioassay data collected from National Library of Medicine (NLM), extracted Dec-2023]

Research

Studies (2,151)

TimeframeStudies, This Drug (%)All Drugs %
pre-1990557 (25.89)18.7374
1990's206 (9.58)18.2507
2000's594 (27.62)29.6817
2010's633 (29.43)24.3611
2020's161 (7.48)2.80
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Market Indicators

Research Demand Index: 6.99

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 weak demand-to-supply ratio for research on this compound.

MetricThis Compound (vs All)
Research Demand Index6.99 (24.57)
Research Supply Index7.73 (2.92)
Research Growth Index4.71 (4.65)
Search Engine Demand Index0.00 (26.88)
Search Engine Supply Index0.00 (0.95)

This Compound (6.99)

All Compounds (24.57)

Study Types

Publication TypeThis drug (%)All Drugs (%)
Trials13 (0.58%)5.53%
Reviews70 (3.10%)6.00%
Case Studies7 (0.31%)4.05%
Observational3 (0.13%)0.25%
Other2,166 (95.88%)84.16%
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]