Vol. 28, Issue 1, 1-4, January 2000
SHORT COMMUNICATION
Short Communication
Metabolism and Disposition of
4-t-Butylcatechol in Rats and Mice
 |
Abstract |
4-t-Butylcatechol (TBC) is an antioxidant used
primarily as a polymerization inhibitor for reactive monomers. Annual
production and use of TBC in the United States is approximately 1.5 million pounds. The absorption, tissue distribution, metabolism, and
excretion of [14C]TBC, labeled in the methine carbon, was
investigated in male Fischer 344 rats and B6C3F1 mice after
i.v., oral, and dermal administration. Oral (2 and 200 mg/kg in rats; 3 and 300 mg/kg in mice) and dermal (0.6, 6, and 63 mg/kg in rats; 1.3 and 157 mg/kg in mice) doses of TBC were well absorbed, then rapidly
metabolized and excreted primarily in urine. Dermal absorption of the
highest dose in the rat (87% of the 63 mg/kg dose) was significantly
higher than that of the two lower doses (0.6 and 6 mg/kg, 44 and 57%, respectively). Dermally administered TBC was also well absorbed in the
mouse (72-86%). Polar metabolites of TBC comprise all of the
radioactivity in the urine of both species after all routes of
administration. These were shown to consist mostly of the sulfate conjugates (and lesser amounts of the glucuronides) of TBC and of a
less polar metabolite. The deconjugated metabolite was isolated and
determined by mass spectrometry and 1H-NMR to be
mono-O-methylated TBC.
 |
Introduction |
4-t-Butylcatechol
(TBC)1
(Fig. 1) is used
principally as an antioxidant, stabilizer, and polymerization inhibitor
for styrene, butadiene, neoprene, and other olefins and reactive
monomers. Annual production of TBC in the United States was estimated
to be 1.5 million pounds in 1989, and total consumption was predicted to increase (Chemical Marketing Reporter, 1989). Occupational and
consumer exposures to TBC by skin contact have been implicated in
numerous cases of allergic and depigmentation reactions. In some cases
the residual TBC present in products made from TBC-stabilized monomers
was sufficient to cause these reactions. TBC has been found a common
factor in the development of contact dermatitis and leukoderma (Gellin
et al., 1979
). TBC is biochemically active and has been reported to be
a substrate for tyrosinase and to inhibit the second step of
melanogenesis (Usami et al., 1980
). TBC-related leukoderma may be
caused by its melanocytotoxic effects (Usami et al., 1980
). The oral
LD50 for TBC in rat is 2820 mg/kg, and that for
i.v. administration in mouse is 32 mg/kg (Smyth et al., 1954
; Sax and
Lewis, 1989
). Some studies (Hirose et al., 1989
) have called attention
to the tumor-promoting ability of TBC, but this has not been confirmed
in a full 2-year carcinogenicity bioassay.

View larger version (14K):
[in this window]
[in a new window]
|
Fig. 1.
Structure of TBC and gas chromatography/mass
spectrometry and 1H-NMR of deconjugated metabolite of TBC.
Mass spectra were determined by gas chromatography/mass spectrometry
analysis on a HP-5989A mass spectrometer using electron impact
ionization. The 1H-NMR was obtained on a Bruker AMX-500 MHz
instrument. The sample was dissolved in a mixture of
d4-methanol and D2O but also contained some
CH3OH remaining from the purification procedure. The
resonances at 3.1 to 3.5 are from (nondeuterated) methanol.
|
|
The objective of the present study was to investigate the absorption,
disposition, metabolism, and excretion of TBC in rats and mice to
complement toxicology studies in those species planned by the National
Toxicology Program.
 |
Materials and Methods |
Chemicals.
TBC was supplied by Aldrich Chemical Co, Inc. (Milwaukee, WI).
[14C]TBC (15 mCi/mmol), labeled on the methine
carbon, was prepared by Wizard Laboratories (West Sacramento, CA). The
radiochemical purity of TBC was determined by reversed phase HPLC to be
94%.
Animal Studies.
Adult male Fischer 344 rats (87-100 days old, 240-280 g) and
B6C3F1 mice (57-67 days old, 21-27 g) were
purchased from Charles River Laboratories, Inc. (Raleigh, NC) and were
furnished Purina Rodent Chow (no. 5002) and water ad libitum.
Single oral dose formulations contained 15 to 20 µCi radiolabel, an
appropriate amount of unlabeled TBC, and either water (2- to 3-mg/kg
doses) or 20% Emulphor EL-620 (GAF Corporation, New York, NY) in water
(200- to 300-mg/kg doses) in a single dose volume of 5 ml/kg for gavage
doses. Intravenous doses were prepared in a mixture of 10% Emulphor
EL-620 in homologous plasma at a volume of 1 ml/kg for rat or 2 ml/kg
for mice, and were injected into a lateral tail vein. Dermal doses were
formulated in acetone in a single dose volume of 25 µl for mice or
200 µl for rats and were administered to a 1- or
4-cm2 area (for mice and rats, respectively) on
the animals' backs from which the hair had been clipped the previous
day. Dermal dose sites were covered by nonocclusive appliances. In
pharmacokinetic studies, rats were prepared with indwelling jugular
cannulas the day before dosing.
Collection of Biological Samples and Determination of
Radiochemical Content.
After dosing, rats and mice were housed in glass metabolism cages that
provided for the separate collection of excreta into round-bottom
flasks cooled with dry ice. In pharmacokinetic studies, blood (0.3 ml)
was collected from rats in heparinized tubes at 0 (predose), 0.25, 0.5, 1, 2, 4, 8, and 24 h postdosing. Plasma was prepared by
centrifugation for 10 min at 2500g. At the end of the
experiments, the animals were anesthetized and sacrificed by
exsanguination. Adipose tissues, muscle, and skin (from three locations
each), blood, as well as the liver, kidneys, adrenal glands, spleen,
lungs, prostate, seminal vesicles, testes, and brain were removed and
assayed for radiochemical content. Additionally, stomach, small
intestine, cecum, and large intestine were removed and assayed with
contents for radiochemical content in some cases. At the conclusion of
the dermal studies, the dose-site skin was excised, the appliance was
removed, and both were washed and assayed as described previously
(Mathews et al., 1998
). Samples were assayed for radioactivity content
as described previously (Mathews et al., 1998
).
Metabolite Isolation.
An initial purification of metabolites in urine collected 0 to 24 h
after dermal administration (63 mg/kg) of TBC was accomplished by
solid-phase extraction (SPE) using a Bond Elut
C18 SPE cartridge containing 500 mg of packing
material in a 6-cc syringe barrel (Varian). Salts were eluted with 2 ml
of water followed by 2 ml of 5% aqueous methanol before the
metabolites were eluted with 2 ml of methanol. The methanol was
evaporated and the sample was reconstituted and incubated with 20 to 30 µl of
-glucuronidase/sulfatase (Sigma, from Helix
pomatia) at 37°C overnight. The deconjugated metabolite (M3) was
isolated by HPLC. The eluant containing M3 was prepared for NMR
analysis by concentration by SPE, eluting with
d4-methanol.
 |
Results and Discussion |
Distribution and Excretion.
The excretion of i.v. and oral doses of TBC in male rats and mice is
shown in Table 1. Rats rapidly excreted
radiolabel in urine after an i.v. or oral dose, with
70% of the dose
recovered there in the first 24 h postdosing. High percentages
(ca. 90%) of oral and i.v. doses administered to mice were excreted in
urine and feces. The high recoveries in mouse feces were likely due to
contamination of feces with urine-soaked food particles. Less than 1%
of the dose remained in the tissues of both species sampled 72 h
postdosing, and there was no evidence of marked accumulation in any
particular tissue type (data not shown).
View this table:
[in this window]
[in a new window]
|
TABLE 1
Cumulative disposition of radioactivity after i.v., oral, or dermal
administration of [14C]TBC to male F-344 rats and
B6C3F1 micea
|
|
The disposition of radioactivity after dermal administration of
[14C]TBC to rats and mice is shown in Table 1.
The dermal dose levels for mice were chosen so as to apply the same mg
TBC/cm2 skin as in the high- and low-dose rat
dermal studies. The mean percentage of the dose absorbed showed a trend
to increase with increasing dose in both species. In rats, about
two-thirds of the high dose was absorbed and excreted (primarily in
urine) within the first 24 h after application, and ultimately
over 85% of this dose was absorbed. The lower two doses were
significantly less well absorbed (43-57% in 72 h,
P < .0001). Conversely, the percentage of radiolabel
retained in the skin of the dose site at 72 h postdosing decreased
as the dose increased. Mice absorbed a higher percentage (72%) of the
low dose than did rats (44%); this difference is probably due to the
fact that mouse skin is thinner than rat skin. Mice, like rats,
excreted TBC-derived radioactivity primarily in urine.
Plasma levels of TBC equivalents were determined in rats over the
24 h after a 200-mg/kg oral dose and after a 63-mg/kg dermal administration. Peak concentrations of equivalents were measured at
1 h postdosing in the oral study (48 µg-Eq./g plasma) and 2 h postdosing in the dermal study (27 µg-Eq./g plasma).
Extracts of plasma were analyzed by HPLC and only polar metabolites (no parent compound) were detected at any time point after either route of
administration (data not shown), indicating rapid and complete
metabolism of TBC once it is internalized.
Metabolism.
Only polar metabolites were excreted in urine after oral, i.v., or
dermal administration of TBC to rats. TBC, which elutes at a retention
time of ca. 13 min, was not excreted in urine. The HPLC
radiochromatogram of rat urine collected 0 to 6 h after a dermal
dose (63 mg/kg) is shown in Fig. 2a and
is representative of profiles observed after each route of
administration for both species. Radiochromatograms of urine after
treatment with purified
-glucuronidase or purified sulfatase are
shown in Fig. 2, b and c, respectively, and indicate that conjugates of
TBC and at least two other metabolites were excreted in urine, one of
which (M3) is less polar than TBC. These chromatograms were also
typical for all species and routes. A greater proportion of the polar metabolites was liberated by treatment with sulfatase, indicating that
the majority of the polar metabolites excreted were sulfate esters. The
early eluting metabolites (M1 and M2) that remained after treatment of
urine with sulfatase were isolated by SPE and HPLC techniques (similar
to those used for M3) and treated again with sulfatase. HPLC analysis
after enzyme incubation indicated that the radioactivity associated
with these peaks had mostly shifted to the retention time of TBC.

View larger version (14K):
[in this window]
[in a new window]
|
Fig. 2.
HPLC radiochromatograms of rat urine
collected 0 to 6 h after dermal administration of
[14C]TBC.
The chromatographic system consisted of a DuPont Zorbax Rx-C18 column
(250 × 4.6 mm, 5 µm; Mac-Mod Analytical, Chadds Ford, PA) and a
mobile phase of methanol/water, 55:45 (v/v); the flow rate was 1 ml/min. The column effluent was monitored by an Applied Biosystems 759a
(Bodman, Aston, PA) absorbance detector at a wavelength of 254 nm and
by a Ramona-5-LS radioactivity detector equipped with a 500-µl solid
scintillate flow cell. a, untreated urine; b, -glucuronidase-treated
urine. Urine (200-400 µl) was added to 1000 U -glucuronidase
(prepared from Escherichia coli) and the mixture was
incubated 4 to 18 h at 37°C before analysis. c,
sulfatase-treated urine. Sulfatase solution (10 µl, prepared
from Aerobacter aerogenes; containing 14.5 U/ml) was
added to 100 µl of urine and 300 µl of
tris(hydroxymethyl)aminomethane (TRIZMA) buffer (0.05 M, pH 7.6) and
incubated 2 to 4 h at 37°C.
|
|
The late eluting peak (M3) was collected and analyzed by GC/MS. The
mass spectrum (Fig. 1a) displayed ions at 180 (M+) and 165 (M-CH3), consistent with
mono-O-methylated TBC. The 1H-NMR of
the isolated deconjugated metabolite (Fig. 1b) is in agreement with
published data for O-methyl TBC (Beger and Meerbote, 1988
).
TBC is excreted in rat and mouse urine as sulfate conjugates and, to a
lesser extent, glucuronides of TBC and its O-methylated metabolite. This is in agreement with the metabolism of
tert-butylhydroquinone, which is excreted primarily as a
sulfate conjugate (Peters et al., 1996
). TBC, as is the case with other
catechols and catecholamines (Axelrod, 1966
; Creveling et al., 1972
),
is O-methylated by catechol O-methyltransferase. Although our spectrometric data
indicated a mono-O-methylated metabolite was formed, it was
not possible to assign a definitive structure.
In conclusion, the data show that TBC is well absorbed after oral or
dermal administration. TBC is rapidly metabolized to the
O-methylated compound and the sulfate and glucuronide
conjugates of that compound and parent are rapidly excreted primarily
in urine. There appears little potential for bioaccumulation of TBC with repeat exposure as very little (<1%) of dose remains in tissues 72 h postdosing.
Sherry R. Black
James M. Mathews
Center for Bioorganic
Chemistry,
Research Triangle
Institute,
Research Triangle Park,
North Carolina
 |
Acknowledgment |
We thank Dr. Brian Thomas and Dr. Jason Burgess for mass spectrometry
and NMR analysis, respectively, and Sherry A. Tallent for assistance in
the preparation of this manuscript.
 |
Footnotes |
Received March 8, 1999; accepted October 1, 1999.
This work was performed under National Institute of
Environmental Health Sciences contract no. NO1-ES-15329.
Send reprint requests to: Sherry R. Black, Research
Triangle Institute, 3040 Cornwallis Rd., Research Triangle Park, NC
27709. E-mail: sherryb{at}rti.org
 |
Abbreviations |
Abbreviations used are:
TBC, 4-t-butylcatechol;
SPE, solid-phase extraction.
 |
References |
-
Axelrod J
(1966)
Methylation reactions in the formation and metabolism of catecholamines and other biogenic amines.
Pharmacol Rev
18:
95-113[Free Full Text].
-
Beger J and
Meerbote M
(1988)
O-Methylation of tert-alkylpyrocatechols. Analytical method for determination of the content of product mixtures and way for preparation of 4-tert-alkylveratroles.
J Prakt Chem
330:
119-125.
-
Chemical Marketing Reporter, January 23, 1989.
-
Creveling CR,
Morris N,
Shimizu H,
Ong HH and
Daly J
(1972)
Catechol O-methyltransferase IV. Factors affecting m- and p-methylation of substituted catechols.
Mol Pharmacol
8:
398-409[Abstract/Free Full Text].
-
Gellin GA,
Maibach HI,
Misiaszek MH and
Ring M
(1979)
Detection of environmental depigmenting substances.
Contact Dermat
5:
201-213[Medline].
-
Hirose M,
Yamaguchi S,
Fukishima S,
Hasegawa R,
Takahashi S and
Ito N
(1989)
Promotion by dihydroxybenzene derivatives of N-methyl-N'-nitro-N-nitroso-guanidine-induced F344 rat forestomach and glandular stomach carcinogenesis.
Cancer Res
49:
5143-5147[Abstract/Free Full Text].
-
Mathews JM,
Black SR and
Burka LT
(1998)
Disposition of butanal oxime in rat following oral, intravenous and dermal administration.
Xenobiotica
28:
767-777[Medline].
-
Peters MMCG,
Lau SS,
Dulik D,
Murphy D,
van Ommen B,
van Bladeren PJ and
Monks TJ
(1996)
Metabolism of tert-butylhydroquinone to S-substituted conjugates in the male Fischer 344 rat.
Chem Res Toxicol
9:
133-139[Medline].
-
Sax NI and
Lewis RJ
(1989)
Dangerous Properties of Industrial Materials 7th ed. vol II, pp 651-6522,
Van Nostrand Reinhold Co., New York.
-
Smyth HF, Jr,
Carpenter CP,
Well CS and
Pozani VC
(1954)
Range-finding toxicity data list V.
Arch Ind Hyg Occup Med
10:
61-68.
-
Usami Y,
Landau AB,
Fukuyama K and
Gellin G
(1980)
Inhibition of tyrosinase activity by 4-tert-butylcatechol and other depigmenting agents.
J Tox Environ Health
6:
559-567.
0090-9556/0/2801-0001-0004$02.00/0
DRUG METABOLISM AND DISPOSITION
Copyright © 2000 by The American Society for Pharmacology and Experimental Therapeutics