Page last updated: 2024-11-05

linuron

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

Description

Linuron is a phenylurea herbicide used for controlling weeds in a variety of crops, including corn, soybeans, and cotton. It is synthesized by the reaction of 3,4-dichlorophenyl isocyanate with N-methyl-N-(3-methoxypropyl)amine. Linuron works by inhibiting photosynthesis in plants, specifically by blocking the electron transport chain in photosystem II. This disrupts the plant's ability to produce energy and leads to its death. Linuron is commonly used for pre-emergence applications, meaning it is applied to the soil before the weeds germinate. Linuron has been shown to be effective at controlling a wide range of weeds, including broadleaf weeds and grasses. Studies on linuron have been conducted to assess its environmental impact, such as its persistence in soil and water, and its potential for bioaccumulation in organisms. Linuron is still used in agriculture, but its use has been restricted in some countries due to concerns about its potential environmental effects.'

Linuron: A selective pre- and post-emergence herbicide. (From Merck Index, 11th ed) [Medical Subject Headings (MeSH), National Library of Medicine, extracted Dec-2023]

linuron : A member of the class of phenylureas that is N-methyl urea substituted by a methoxy group at position 1 and a 3,4-dichlorophenyl group at position 3. [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 CID9502
CHEMBL ID448213
CHEBI ID6482
SCHEMBL ID56566
MeSH IDM0012534

Synonyms (104)

Synonym
BIDD:ER0455
urea, n'-(3,4-dichlorophenyl)-n-methoxy-n-methyl-
urea, 3-(3,4-dichlorophenyl)-1-methoxy-1-methyl-
lorox
linuron
330-55-2
NCGC00160429-01
NCGC00160429-02
laroks [polish]
rotalin
afalon inuron
linurex
sinuron
n-(3,4-dwuchlorofenylo)n'-metoksy-n'-metylomocznik [polish]
3-(3,4-dichloor-fenyl)-1-methoxy-1-methylureum [dutch]
hoe 02 810
hoe 2810
3-(3,4-dicloro-fenil)-1-metossi-1-metil-urea [italian]
3-(4,5-dichlorphenyl)-1-methoxy-1-methylharnstoff [german]
cephalon
certroli-lin
aphalon
afalon
profalon
lorox weed killer
garnitan
linuron (herbicide)
1-methoxy-1-methyl-3-(3,4-dichlorophenyl)urea
caswell no. 528
linex
brn 2128725
epa pesticide chemical code 035506
3-(3,4-dichloro-fenil)-1-metossi-1-metil-urea [italian]
einecs 206-356-5
hsdb 1733
3-(3,4-dichlorophenyl)-1-methoxy-1-methylurea
du pont herbicide 326
linuron [ansi:bsi:iso]
methoxydiuron
sarclex
herbicide 326
malurane
hoe 002810
linorox
linex 4l
1-(3,4-dichlorophenyl)3-methoxy-3-methyluree [french]
n-(3,4-dichlorophenyl)-n'-methyl-n'-methoxyurea
lorox linuron weed killer
3-(3,4-dichlor-phenyl)-1-methoxy-1-methyl-harnstoff [german]
soilcid
du pont 326
dupont herbicide 326
n'-(3,4-dichlorophenyl)-n-methoxy-n-methylurea
NCGC00160429-03
CHEMBL448213
chebi:6482 ,
xkjmbincvninca-uhfffaoysa-
inchi=1/c9h10cl2n2o2/c1-13(15-2)9(14)12-6-3-4-7(10)8(11)5-6/h3-5h,1-2h3,(h,12,14)
STK664290
NCGC00160429-05
NCGC00160429-04
NCGC00160429-06
n-(3,4-dwuchlorofenylo)n'-metoksy-n'-metylomocznik
3-(3,4-dichloro-fenil)-1-metossi-1-metil-urea
01xp1su59o ,
3-(4,5-dichlorphenyl)-1-methoxy-1-methylharnstoff
3-(3,4-dichlor-phenyl)-1-methoxy-1-methyl-harnstoff
1-(3,4-dichlorophenyl)3-methoxy-3-methyluree
3-(3,4-dicloro-fenil)-1-metossi-1-metil-urea
unii-01xp1su59o
laroks
3-(3,4-dichloor-fenyl)-1-methoxy-1-methylureum
tox21_201281
dtxcid604163
NCGC00258833-01
NCGC00254638-01
cas-330-55-2
tox21_300732
dtxsid2024163 ,
A821586
3-(3,4-dichlorophenyl)-1-methoxy-1-methyl-urea
alfalon
FT-0603379
AKOS015889915
SCHEMBL56566
linuron [hsdb]
linuron [mi]
linuron [iso]
atlas linuron
scarclex
norunil
n'-(3,4-dichlorophenyl)-n-methoxy-n-methyl urea
n-(3,4-dichlorophenyl)-n'-methoxy-n'-methylurea
linuron, pestanal(r), analytical standard
linuron 100 microg/ml in acetonitrile
linuron 10 microg/ml in acetonitrile
J-018993
Q421476
CS-0013933
MS-23524
HY-B1866
F88229
L0395
mfcd00055249

Research Excerpts

Overview

Linuron is a phenylurea herbicide used to control a wide variety of vegetative weeds in agriculture. Its endocrine disruptive toxicity has recently received public attention. Linuron alters sexual differentiation in an antiandrogenic manner.

ExcerptReferenceRelevance
"Linuron is a phenylurea herbicide used to control a wide variety of vegetative weeds in agriculture in addition to residential applications."( Sub-lethal toxicity assessment of the phenylurea herbicide linuron in developing zebrafish (Danio rerio) embryo/larvae.
El Ahmadie, N; El Chehouri, J; Maharaj, S; Martyniuk, CJ; Rheingold, S; Souders, CL; Yang, L,
)
1.1
"Linuron is a commonly used organic herbicide which is used in plant growth control. "( Conformational analysis and concentration detection of linuron: Spectroscopic NMR and SERS study.
Al-Saadi, AA; Haroon, M; Iali, W, 2021
)
2.31
"Linuron is a widely used herbicide; its toxicity on the male reproductive system has been recognized. "( Maternal linuron exposure alters testicular development in male offspring rats at the whole genome level.
Bai, J; Ding, H; Han, H; Hu, B; Hu, X; Li, H; Li, Y; Su, L; Wang, F; Zheng, W, 2017
)
2.31
"Linuron is a widely used herbicide to control grasses and annual broad leaf weeds. "( Evaluation of 8-hydroxy-2-deoxyguanosine and NFkB activation, oxidative stress response, acetylcholinesterase activity, and histopathological changes in rainbow trout brain exposed to linuron.
Alak, G; Altun, S; Atamanalp, M; Erol, HS; Topal, A, 2017
)
2.09
"Linuron is a widely used herbicide in agriculture; its endocrine disruptive toxicity has recently received public attention. "( Reproductive toxicity of linuron following gestational exposure in rats and underlying mechanisms.
Ding, H; Han, H; Hu, B; Hu, X; Li, H; Li, Y; Su, L; Wang, F; Zheng, W, 2017
)
2.2
"Linuron is a globally used phenylurea herbicide, and a large number of studies have been made on the microbial degradation of the herbicide. "( Mineralisation of the herbicide linuron by Variovorax sp. strain RA8 isolated from Japanese river sediment using an ecosystem model (microcosm).
Satsuma, K, 2010
)
2.09
"Linuron is a widely used urea-based herbicide that has anti-androgenic activity in both fish and rodents. "( The effects of the urea-based herbicide linuron on reproductive endpoints in the fathead minnow (Pimephales promelas).
Elphick, JR; Hogan, NS; Kennedy, CJ; Lo, BP; Marlatt, VL; Martyniuk, CJ; Ornostay, A, 2013
)
2.1
"Linuron is an herbicide with weak androgen receptor (AR) antagonist activity. "( Altered gene expression during rat Wolffian duct development in response to in utero exposure to the antiandrogen linuron.
Barlow, NJ; Bowman, CJ; Foster, PM; McIntyre, BS; Phillips, SL; Turner, KJ, 2003
)
1.97
"Linuron, which is a weak competitive inhibitor of AR binding (reported Ki of 100 microM), alters sexual differentiation in an antiandrogenic manner."( Cellular and molecular mechanisms of action of linuron: an antiandrogenic herbicide that produces reproductive malformations in male rats.
Bobseine, K; Gray, LE; Hotchkiss, AK; Lambright, C; Mann, PC; Ostby, J; Wilson, V, 2000
)
1.29
"Linuron is an herbicide that displays weak androgen receptor antagonist activity. "( Effects of in utero linuron exposure on rat Wolffian duct development.
Barlow, NJ; Foster, PM; McIntyre, BS; Sar, M; Wallace, DG,
)
1.9

Effects

ExcerptReferenceRelevance
"Linuron has been shown to be negative in a battery of six tests for genotoxicity; therefore, a nongenotoxic mechanism of tumorgenesis was investigated."( Investigation of a mechanism for Leydig cell tumorigenesis by linuron in rats.
Biegel, LB; Cook, JC; Frame, SR; Mullin, LS, 1993
)
1.25

Actions

ExcerptReferenceRelevance
"Linuron's ability to cause DNA damage and cytogenetic effects was also investigated after treating groups of rats once with different doses of pure or commercial linuron."( In vivo studies on genotoxicity of pure and commercial linuron.
Caderni, G; Dolara, P; Fatigoni, C; Kuchenmeister, F; Monarca, S; Moretti, M; Pasquini, R; Pool-Zobel, BL; Scassellati-Sforzolini, G; Schmezer, P; Villarini, M, 1997
)
1.27

Treatment

Linuron isolated treatment seems to have an estrogenic mode of action due to the observed induction of vtg1. Soil treated with linuron for more than 10 years showed high biodegradation activity towards methoxy-methyl urea herbicides.

ExcerptReferenceRelevance
"linuron-treated agricultural soil and on-farm biopurification systems (BPS) treating complex agricultural wastewater, as to non-treated controls."( Targeted metagenomics demonstrates the ecological role of IS1071 in bacterial community adaptation to pesticide degradation.
Bers, K; Dunon, V; Lavigne, R; Springael, D; Top, EM, 2018
)
1.2
"Linuron isolated treatment seems to have an estrogenic mode of action due to the observed induction of vtg1."( Endocrine and physiological effects of linuron and S-metolachlor in zebrafish developing embryos.
Monteiro, MS; Novais, SC; Patrício, D; Quintaneiro, C; Soares, AMVM, 2017
)
1.45
"Linuron treatment resulted in a decrease in biomass of the macrophyte Elodea nuttallii and a clear decrease in abundance of the algae Cocconeis, Chroomonas, and Phormidium foveolarum."( Sensitivity of macrophyte-dominated freshwater microcosms to chronic levels of the herbicide linuron. I. Primary producers.
Brock, TC; Crum, SJ; Fettweis, U; Hartgers, EM; Van den Brink, PJ; Van Donk, E, 1997
)
1.24
"Linuron treatment induced a level of external effects consistent with its low affinity for AR [reduced anogenital distance (AGD), retained nipples, and a low incidence of hypospadias]."( 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,
)
1.09
"Soil treated with linuron for more than 10 years showed high biodegradation activity towards methoxy-methyl urea herbicides. "( Enrichment and molecular characterization of a bacterial culture that degrades methoxy-methyl urea herbicides and their aniline derivatives.
El-Fantroussi, S; Top, EM; Verstraete, W, 2000
)
0.64

Toxicity

The acute LD50 in virginal NMRI-Mice was found to be 2528 mg/kg for monolinuron and 1791 mg/ kg for buturon. Linuron inhibited bacterial growth and NADH-supported respiration.

ExcerptReferenceRelevance
"The acute LD50 in virginal NMRI-Mice was found to be 2528 mg/kg for monolinuron and 1791 mg/kg for buturon."( [Studies on the embryotoxicity of monolinuron and buturon in NMRI-mice (author's transl)].
Matthiaschk, G; Roll, R, 1977
)
0.76
" Dose levels were determined in the base of the LD50 of each component."( Mixture of paraquat and linuron formulations examined for genotoxicity in Wistar rats by the in vivo micronucleus test--evaluation by different statistical tests.
Goumenou, M; Machera, K, 2004
)
0.63
" Linuron inhibited bacterial growth and NADH-supported respiration, similar IC₅₀ values being estimated for both toxic responses (74 and 98 μM, respectively)."( Toxicity of the herbicide linuron as assessed by bacterial and mitochondrial model systems.
Fernandes, MA; Jurado, AS; Moreno, AJ; Santos, MS; Santos, SM; Vicente, JA; Videira, RA, 2014
)
1.61
" In fish, although the acutely lethal effects of diuron in early life stages appear to be >1mg/L, recent studies measuring sub-lethal behavioural and developmental endpoints suggest that diuron causes adverse effects at lower concentrations (i."( Biological responses to phenylurea herbicides in fish and amphibians: New directions for characterizing mechanisms of toxicity.
Marlatt, VL; Martyniuk, CJ, 2017
)
0.46

Bioavailability

ExcerptReferenceRelevance
" To examine the bioavailability of these residues, rats were dosed by gavage (water vehicle) with unextracted tubers and extracted tubers."( Preliminary studies on the bioavailability and disposition of bioincurred carrot residues of [14C] linuron and [14C]3,4-dichloroaniline in rats.
Shields, JB; Worobey, BL,
)
0.35
" To show the importance of physicochemical properties, the classic QSAR and CoMFA of neonicotinoids and prediction of bioavailability of pesticides in terms of membrane permeability in comparison with drugs are described."( Importance of physicochemical properties for the design of new pesticides.
Akamatsu, M, 2011
)
0.37
" Adding these materials to soil requires understanding the process of pesticide sorption-desorption by wood-soils, as sorption capacity could increase, with changes in pesticide bioavailability and final fate."( Study of processes influencing bioavailability of pesticides in wood-soil systems: Effect of different factors.
Arienzo, M; Herrero-Hernández, E; Marín-Benito, JM; Rodríguez-Cruz, MS; Sánchez-Martín, MJ, 2017
)
0.46

Dosage Studied

Long-Evans hooded rats were dosed daily for 10 weeks with 0, 10 or 20 mg lindane or 10, 20 or 40 mg linuron/kg body weight beginning at weaning. After 7 days of exposure to linuron, log-logistic-based dose-response analysis revealed significant growth inhibition.

ExcerptRelevanceReference
" Long-Evans hooded rats were dosed daily for 10 weeks with 0, 10 or 20 mg lindane or 10, 20 or 40 mg linuron/kg body weight beginning at weaning."( The effects of lindane and linuron on calcium metabolism, bone morphometry and the kidney in rats.
Andrews, JE; Gray, LE,
)
0.64
" To examine the bioavailability of these residues, rats were dosed by gavage (water vehicle) with unextracted tubers and extracted tubers."( Preliminary studies on the bioavailability and disposition of bioincurred carrot residues of [14C] linuron and [14C]3,4-dichloroaniline in rats.
Shields, JB; Worobey, BL,
)
0.35
" 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,
)
0.37
" Furthermore, these data suggest that dose-response studies utilizing late gestational exposure to endocrine-active compounds may be more robust than the traditional or EPA-modified multigeneration protocols in identifying adverse effects."( Effects of in utero exposure to linuron on androgen-dependent reproductive development in the male Crl:CD(SD)BR rat.
Barlow, NJ; Foster, PM; Gaido, KW; Maness, SC; McIntyre, BS; Wallace, DG, 2000
)
0.59
" 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
" Whole-plant herbicide dose-response experiments revealed that, relative to the UniS population, atrazine resistances in the UniR and SegR populations were > 770-fold and 16-fold, respectively."( Triazine resistance in Amaranthus tuberculatus (Moq) Sauer that is not site-of-action mediated.
Dixon, BS; Patzoldt, WL; Tranel, PJ, 2003
)
0.32
" In general, consideration of the dose-response curves for the antiandrogenic effects suggests that these responses were dose additive rather than synergistic responses."( A mixture of the "antiandrogens" linuron and butyl benzyl phthalate alters sexual differentiation of the male rat in a cumulative fashion.
Furr, J; Gray, LE; Hotchkiss, AK; Lambright, C; Ostby, JS; Parks-Saldutti, LG; Vandenbergh, JG, 2004
)
0.6
" In all binary mixture studies, rats were dosed during pregnancy with chemicals, singly or in pairs, at dosage levels equivalent to approximately one-half of the ED50 for hypospadias or epididymal agenesis."( Cumulative effects of in utero administration of mixtures of reproductive toxicants that disrupt common target tissues via diverse mechanisms of toxicity.
Furr, JR; Gray, LE; Rider, CV; Wilson, VS, 2010
)
0.36
" Dams were orally exposed from gestational day 7 (dimethomorph and imazalil) or 13 (linuron) until birth, then until end of dosing at early postnatal life."( Exposure to the pesticides linuron, dimethomorph and imazalil alters steroid hormone profiles and gene expression in developing rat ovaries.
Boberg, J; Christiansen, S; Cramer, J; Draskau, MK; Franssen, D; Johansson, HKL; Parent, AS; Pedersen, M; Svingen, T, 2023
)
1.43
[information is derived through text-mining from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Roles (4)

RoleDescription
xenobioticA xenobiotic (Greek, xenos "foreign"; bios "life") is a compound that is foreign to a living organism. Principal xenobiotics include: drugs, carcinogens and various compounds that have been introduced into the environment by artificial means.
environmental contaminantAny minor or unwanted substance introduced into the environment that can have undesired effects.
herbicideA substance used to destroy plant pests.
agrochemicalAn agrochemical is a substance that is used in agriculture or horticulture.
[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
dichlorobenzeneAny member of the class of chlorobenzenes carrying two chloro groups at unspecified positions.
phenylureasAny member of the class of ureas in which at least one of the nitrogens of the urea moiety is substituted by a phenyl or substituted phenyl group.
[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]

Pathways (1)

PathwayProteinsCompounds
linuron degradation211

Protein Targets (20)

Potency Measurements

ProteinTaxonomyMeasurementAverage (µ)Min (ref.)Avg (ref.)Max (ref.)Bioassay(s)
LuciferasePhotinus pyralis (common eastern firefly)Potency51.74280.007215.758889.3584AID1224835
pregnane X receptorRattus norvegicus (Norway rat)Potency35.48130.025127.9203501.1870AID651751
RAR-related orphan receptor gammaMus musculus (house mouse)Potency6.09440.006038.004119,952.5996AID1159521; AID1159523
AR proteinHomo sapiens (human)Potency37.08560.000221.22318,912.5098AID1259243; AID1259247; AID743035; AID743042; AID743063
nuclear receptor subfamily 1, group I, member 3Homo sapiens (human)Potency38.84460.001022.650876.6163AID1224838; AID1224839; AID1224893
progesterone receptorHomo sapiens (human)Potency68.58960.000417.946075.1148AID1346795
retinoic acid nuclear receptor alpha variant 1Homo sapiens (human)Potency14.33620.003041.611522,387.1992AID1159552; AID1159553; AID1159555
estrogen-related nuclear receptor alphaHomo sapiens (human)Potency15.27320.001530.607315,848.9004AID1224841; AID1224842; AID1259401; AID1259403
pregnane X nuclear receptorHomo sapiens (human)Potency55.32690.005428.02631,258.9301AID1346982; AID720659
estrogen nuclear receptor alphaHomo sapiens (human)Potency34.35700.000229.305416,493.5996AID1259244; AID1259248; AID1259383; AID743080; AID743091
vitamin D (1,25- dihydroxyvitamin D3) receptorHomo sapiens (human)Potency50.11870.023723.228263.5986AID588543
aryl hydrocarbon receptorHomo sapiens (human)Potency25.63100.000723.06741,258.9301AID651777; AID743085; AID743122
cytochrome P450, family 19, subfamily A, polypeptide 1, isoform CRA_aHomo sapiens (human)Potency2.62260.001723.839378.1014AID743083
thyroid stimulating hormone receptorHomo sapiens (human)Potency68.58960.001628.015177.1139AID1224843; AID1224895
thyroid hormone receptor beta isoform aHomo sapiens (human)Potency0.39810.010039.53711,122.0200AID588547
thyroid hormone receptor beta isoform 2Rattus norvegicus (Norway rat)Potency57.06590.000323.4451159.6830AID743065; AID743067
histone deacetylase 9 isoform 3Homo sapiens (human)Potency24.36740.037617.082361.1927AID1259364; AID1259388
nuclear factor erythroid 2-related factor 2 isoform 1Homo sapiens (human)Potency52.25370.000627.21521,122.0200AID651741; AID720636; AID743219
Voltage-dependent calcium channel gamma-2 subunitMus musculus (house mouse)Potency77.27200.001557.789015,848.9004AID1259244
Glutamate receptor 2Rattus norvegicus (Norway rat)Potency77.27200.001551.739315,848.9004AID1259244
[prepared from compound, protein, and bioassay information from National Library of Medicine (NLM), extracted Dec-2023]

Ceullar Components (1)

Processvia Protein(s)Taxonomy
plasma membraneGlutamate receptor 2Rattus norvegicus (Norway rat)
[Information is prepared from geneontology information from the June-17-2024 release]

Bioassays (7)

Assay IDTitleYearJournalArticle
AID409959Inhibition of bovine liver MAOB2008Journal of medicinal chemistry, Nov-13, Volume: 51, Issue:21
Quantitative structure-activity relationship and complex network approach to monoamine oxidase A and B inhibitors.
AID537734Antifungal activity against yeast AD1-8u expressing Candida albicans CaMdr1p by agar disk diffusion assay2010European journal of medicinal chemistry, Nov, Volume: 45, Issue:11
Analysis of physico-chemical properties of substrates of ABC and MFS multidrug transporters of pathogenic Candida albicans.
AID409957Inhibition of bovine liver MAOA2008Journal of medicinal chemistry, Nov-13, Volume: 51, Issue:21
Quantitative structure-activity relationship and complex network approach to monoamine oxidase A and B inhibitors.
AID537735Binding affinity to Candida albicans CaMdr1p expressed in yeast AD1-8u2010European journal of medicinal chemistry, Nov, Volume: 45, Issue:11
Analysis of physico-chemical properties of substrates of ABC and MFS multidrug transporters of pathogenic Candida albicans.
AID1091958Hydrophobicity, log P of the compound in octanol-water by shaking-flask method2011Journal of agricultural and food chemistry, Apr-13, Volume: 59, Issue:7
Importance of physicochemical properties for the design of new pesticides.
AID537736Antifungal activity against yeast AD1-8u expressing Candida albicans CaCdr1p by agar disk diffusion assay2010European journal of medicinal chemistry, Nov, Volume: 45, Issue:11
Analysis of physico-chemical properties of substrates of ABC and MFS multidrug transporters of pathogenic Candida albicans.
AID537733Binding affinity to Candida albicans CaCdr1p expressed in yeast AD1-8u2010European journal of medicinal chemistry, Nov, Volume: 45, Issue:11
Analysis of physico-chemical properties of substrates of ABC and MFS multidrug transporters of pathogenic Candida albicans.
[information is prepared from bioassay data collected from National Library of Medicine (NLM), extracted Dec-2023]

Research

Studies (246)

TimeframeStudies, This Drug (%)All Drugs %
pre-199045 (18.29)18.7374
1990's23 (9.35)18.2507
2000's74 (30.08)29.6817
2010's84 (34.15)24.3611
2020's20 (8.13)2.80
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]

Market Indicators

Research Demand Index: 48.91

According to the monthly volume, diversity, and competition of internet searches for this compound, as well the volume and growth of publications, there is estimated to be strong demand-to-supply ratio for research on this compound.

MetricThis Compound (vs All)
Research Demand Index48.91 (24.57)
Research Supply Index5.63 (2.92)
Research Growth Index4.75 (4.65)
Search Engine Demand Index83.69 (26.88)
Search Engine Supply Index2.16 (0.95)

This Compound (48.91)

All Compounds (24.57)

Study Types

Publication TypeThis drug (%)All Drugs (%)
Trials0 (0.00%)5.53%
Reviews4 (1.44%)6.00%
Case Studies4 (1.44%)4.05%
Observational0 (0.00%)0.25%
Other270 (97.12%)84.16%
[information is prepared from research data collected from National Library of Medicine (NLM), extracted Dec-2023]