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2D Structure
Also known as: Butacarb [iso], 2655-19-8, 3,5-di-tert-butylphenyl methylcarbamate, 48sle5y118, Butacarbe [french], Caswell no. 291b
Molecular Formula
C16H25NO2
Molecular Weight
263.37  g/mol
InChI Key
SLZWBCGZQRRUNG-UHFFFAOYSA-N
FDA UNII
48SLE5Y118

1 2D Structure

2D Structure

2 Identification
2.1 Computed Descriptors
2.1.1 IUPAC Name
(3,5-ditert-butylphenyl) N-methylcarbamate
2.1.2 InChI
InChI=1S/C16H25NO2/c1-15(2,3)11-8-12(16(4,5)6)10-13(9-11)19-14(18)17-7/h8-10H,1-7H3,(H,17,18)
2.1.3 InChI Key
SLZWBCGZQRRUNG-UHFFFAOYSA-N
2.1.4 Canonical SMILES
CC(C)(C)C1=CC(=CC(=C1)OC(=O)NC)C(C)(C)C
2.2 Other Identifiers
2.2.1 UNII
48SLE5Y118
2.3 Synonyms
2.3.1 Depositor-Supplied Synonyms

1. Butacarb [iso]

2. 2655-19-8

3. 3,5-di-tert-butylphenyl Methylcarbamate

4. 48sle5y118

5. Butacarbe [french]

6. Caswell No. 291b

7. Butacarb [iso:bsi]

8. Butacarbe

9. Hsdb 2799

10. 3,5-di-t-butylphenylmethylcarbamate

11. Bts 14639

12. Epa Pesticide Chemical Code 291300

13. Brn 1914596

14. Rd 14639

15. 3,5-di-tert-butylphenyl N-methylcarbamate

16. Unii-48sle5y118

17. 3,5-bis(1,1-dimethylethyl)phenol Methylcarbamate

18. Carbamic Acid, Methyl-, 3,5-di-tert-butylphenyl Ester

19. Phenol, 3,5-bis(1,1-dimethylethyl)-, Methylcarbamate

20. Butacarb [hsdb]

21. Schembl77964

22. Dtxsid0041690

23. Chebi:82089

24. C18949

25. Q27155741

26. 3,5-bis(1,1-dimethylethyl)phenyl N-methylcarbamate

2.4 Create Date
2005-08-08
3 Chemical and Physical Properties
Molecular Weight 263.37 g/mol
Molecular Formula C16H25NO2
XLogP34.7
Hydrogen Bond Donor Count1
Hydrogen Bond Acceptor Count2
Rotatable Bond Count4
Exact Mass263.188529040 g/mol
Monoisotopic Mass263.188529040 g/mol
Topological Polar Surface Area38.3 Ų
Heavy Atom Count19
Formal Charge0
Complexity290
Isotope Atom Count0
Defined Atom Stereocenter Count0
Undefined Atom Stereocenter Count0
Defined Bond Stereocenter Count0
Undefined Bond Stereocenter Count0
Covalently Bonded Unit Count1
4 Drug and Medication Information
4.1 Minimum/Potential Fatal Human Dose

3. 3= moderately toxic: probable oral lethal dose (human) 0.5-5 g/kg, between 1 oz & 1 pint (or 1 lb) for 70 kg person (150 lb).

Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984., p. II-305


5 Pharmacology and Biochemistry
5.1 Absorption, Distribution and Excretion

In vivo studies have shown that carbamates are almost completely absorbed during normal transit through the gastrointestinal tract. ...In mice, all carbamates were rapidly distributed to the tissues and organs. The half-life values of penetration ranged from 8-17 min for carbamates. ...In animals, oxidation of carbamates often, but not always, results in detoxification. Oxidative metabolism generally leads to products of greater polarity and water solubility, and these can be more readily eliminated through the urine and feces than the parent compound. /Carbamate pesticides/

WHO; Environ Health Criteria 64: Carbamate pesticides (1986). Available from, as of December 28, 2004: https://www.inchem.org/documents/ehc/ehc/ehc64.htm


Little information is available on the distribution of carbamates in the various organs and tissues in mammals following exposure by inhalation or the oral route. The organs in which residues have been reported are the liver, kidneys, brain, fat, and muscle. The half-life in the rat is of the order of 3-8 hr. It seems that the excretion of carbamates via urine is also rapid in man, and that the metabolic pathways in man are the same as those in the rat. /Carbamate pesticides/

WHO; Environ Health Criteria 64: Carbamate pesticides (1986). Available from, as of July 3,2003: https://www.inchem.org/pages/ehc.html


5.2 Metabolism/Metabolites

When butacarb was incubated with mouse liver 10,000xg supernatant, eleven metabolites were detected. Hydrolysis produced only 6 phenols. One of these, the major metabolite, was identified as 3,5-di-tert-butylphenol. Other metabolites were characterized but not all were completely identified: two acid metabolites containing a carboxyl & carbamoyl group; two containing a carbamoyl & two hydroxy groups (but not dihydroxybenzenoid); a hydroxybutylphenol; one containing a carbamoyl & hydroxy group; two dihydroxybutylphenols; n-hydroxymethyl butacarb; & n-hydroxymethyl hydroxybutyl analog. Studies with housefly (musca domestica), blowfly (lucilia sericata) & grass grubs (costelytra zealandica) gave results quant similar to those with mouse liver enzymes.

Menzie, C. M. Metabolism of Pesticides, An Update. U.S. Department of the Interior, Fish, Wild-life Service, Special Scientific Report - Wildlife No. 184, Washington, DC: U.S. Government Printing Office, l974., p. 66


...Butacarb.../is/ cleaved to phenolic products by enzyme system in liver microsomes, which requires nadph & is inhibited by carbon monoxide...it is likely that this...microsomal mono-oxygenation is very important in 'hydrolysis' of carbamates.

The Chemical Society. Foreign Compound Metabolism in Mammals. Volume 2: A Review of the Literature Published Between 1970 and 1971. London: The Chemical Society, 1972., p. 378


The principal route of metabolism of insecticidal carbamate esters is oxidative and is generally associated with the mixed-function oxidase (MFO) enzymes, which are present in several tissues. /Carbamate pesticides/

WHO; Environ Health Criteria 64: Carbamate pesticides (1986). Available from, as of December 28, 2004: https://www.inchem.org/documents/ehc/ehc/ehc64.htm


The metabolism of 3,5-di-tert-butylphenyl-N-methylcarbamate (butacarb) was studied in insects and mouse liver enzymes. Tritium (H-3) labeled butacarb was incubated with 10,000 times the force of gravity supernatants from mouse liver or housefly and blowfly enzyme preparations, obtained from their abdomens. The reaction mixtures were analyzed for metabolites. Eleven oxidation products were detected in each species. In-vivo, adult houseflies and blowflies were dosed topically with H-3 labeled butacarb. The insects were then extracted by grinding them with sand and ether. Ether extracts were examined for metabolites. The water soluble fraction was also examined. Both fractions consisted of complex mixtures. The ether fraction was hydrolyzed with sodium-hydroxide, and the water soluble portion was analyzed. Six phenolic metabolites were detected. The major phenolic product was 3,5-di-tert-butylphenol, which accounted for more than half of the dose.

PMID:5144737 Full text: https://www.ncbi.nlm.nih.gov/pmc/articles/PMC1178072 Douch PGC, Smith JN; Biochem J 125 (2): 395-400 (1971)


5.3 Mechanism of Action

The carbamates alone weakly activated estrogen- or progesterone-responsive reporter genes in breast and endometrial cancer cells. All of the carbamates decreased estradiol- or progesterone-induced reporter gene activity in the breast and endometrial cancer cells. In whole cell competition binding assays, the carbamates demonstrated a limited capacity to displace radiolabeled estrogen or progesterone from /estrogen receptor/ or /progesterone receptor/. /Carbamates/

PMID:9126867 Klotz D et al; Life Sciences 60 (17): 1467-1475 (1997)


Carbamates are effective insecticides by virtue of their ability to inhibit acetylcholinesterase (AChE) in the nervous system. They also inhibit other esterases. The carbamylation of the enzyme is unstable, and the regeneration of AChE is relatively rapid compared with that from a phosphorylated enzyme. Thus, carbamate pesticides are less dangerous with regard to human exposure than organophosphorus pesticides. The ratio between the dose required to produce death and the dose required to produce minimum symptoms of poisoning is substantially larger for carbamate compounds than for organophosphorus compounds. /Carbamate Pesticides/

WHO; Environ Health Criteria 64: Carbamate pesticides (1986). Available from, as of July 3,2003: https://www.inchem.org/pages/ehc.html


The carbamate insecticides are reversible cholinesterase-inhibitors. They cause this effect by reversible carbamylation of the enzyme acetylcholinesterase, allowing accum of acetylcholine, as with the organophosphate insecticides. ... While the organophosphate insecticides cause irreversible inhibition of the cholinesterase enzymes, the carbamyl-enzyme complex is reversible & dissociates far more readily than the organophosphate complex. The clinical syndrome is more benign & of much shorter duration with the carbamate insecticides. /Carbamate insecticides/

Haddad, L.M. and Winchester, J.F. Clinical Management of Poisoning and Drug Overdosage. Philadelphia, PA: W.B. Saunders Co., 1983., p. 711