BUTYLATED HYDROXYTOLUENE (BHT)
First draft prepared by
Ms Elizabeth Vavasour
Toxicological Evaluation Division, Bureau of Chemical Safety
Food Directorate, Health Protection Branch, Health Canada
Ottawa, Ontario, Canada
Absorption, distribution, and excretion
Effects on enzymes and other biochemical parameters
Acute toxicity studies
Short-term toxicity studies
Long-term toxicity/carcinogenicity studies
Reproductive toxicity studies
Special studies on teratogenicity
Special studies on genotoxicity
Special studies on hepatotoxicity
Special studies on nephrotoxicity
Special studies oil pulmonary toxicity
Special studies on haemorrhagic effects
Special studies on effects on the thyroid
Special studies on effects on the immmune system
Special studies on potentiation or inhibition of cancer
Special studies on other effect
Observations in human
Butylated hydroxytoluene (BHT) was previously evaluated by the
Committee at its sixth, eighth, ninth, seventeenth, twentieth,
twenty-fourth, twenty-seventh, thirtieth, and thirty-seventh meetings
(Annex 1, references 6, 8, 11, 32, 41, 53, 62, 73, and 94). At the
thirty-seventh meeting, the temporary ADI of 0 - 0.125 mg/kg bw,
established at the thirtieth meeting, was extended pending the results
of a study designed to elucidate the role of hepatic changes in the
development of hepatic carcinomas observed in Wistar rats following
in utero and lifetime exposure to BHT.
The results of the above study were reviewed at the present
meeting. In addition, new data relating to the previously-noted
effects of BHT on the lung, liver, kidney, clotting mechanisms and
promotion/inhibition of carcinogenesis, new long-term and reproductive
toxicity studies, genotoxicity assays and human observations were
The following consolidated monograph is a compilation of studies
from the previous monographs and monograph addenda and those reviewed
for the first time at the present meeting.
2. BIOLOGICAL DATA
2.1 Biochemical aspects
2.1.1 Absorption, distribution, and excretion
A single oral dose of 14C-BHT given to male and female mice
resulted in rapid absorption and distribution of 14C to the tissues.
Excretion of 14C was mainly in the faeces (41-65%) and urine
(26-50%), with lesser amounts in expired air (6-9%). The half-life for
a single dose in the major tissues studied (stomach, intestines,
liver, and kidney) was 9-11 h. When daily doses were given for 10
days, the half-life for 14C in the tissues examined was 5-15 days.
Metabolism was characterized by oxidation at one or both of the
tert-butyl groups, followed by formation of the glucuronide
conjugate, and excretion in the urine, or by excretion of the free
acid in the faeces. More than 43 metabolites were present in the urine
and faeces of mice (Matsuo et al., 1984).
When 14C-BHT was administered to rats, 80-90% of the 14C was
excreted in the urine and faeces within 96 h, and less than 0.3% of
the 14C was in expired air. Most of the 14C-BHT was excreted as
the free acid in faeces with lesser amounts in the urine. More than 43
metabolites were present in the urine and faeces of rats
(Matsuo et al., 1984).
Male F344 rats were fed BHA/BHT mixtures at levels of 0/0,
0.5/0.05, 1.0/0.1, or 2.0/0.2% in the diet and the levels of the
compounds were determined in adipose tissue after 1, 2, or 4 months.
The BHT levels found in adipose tissue were 1.4, 2.9, or 7.8 mg/kg,
respectively, in the dosed animals. On an equivalent dose basis, BHT
accumulated to ten times the level of BHA. However, neither showed any
progressive accumulation with time. Considering the rat adipose tissue
data, the mean intake of BHT by humans and the corresponding level of
BHT found in adipose tissue from 6 humans (0.12 mg/kg), previous
observations that accumulation of BHT in the adipose tissue on a
dose/body weight basis is greater in humans than in rats were
confirmed (Conacher et al., 1986).
Groups of male and female rats were maintained on diets
containing 0 or 0.5% BHT for a period of 35 days, and then for a
period on diets free of BHT. During the period on the test diets,
groups of rats were killed at 5-day intervals and fat and liver
removed for BHT analysis. During the period on BHT-free diets, rats
were killed at 2-day intervals to measure loss of BHT from the fat and
liver. There was no clear evidence of progressive accumulation of BHT
in fat during the period of administration of the test compound. BHT
levels in the fat reached a maximum level (55 mg/kg in males, 65 mg/kg
in females) within 10 days of exposure to BHT. Thereafter there was
considerable fluctuation in the observed levels. The levels of BHT in
liver were very low, the maximum BHT levels being about 5 mg/kg in
males, and 1.5 mg/kg in females. The biological half-life of BHT in
fat and liver was estimated to be 7 to 10 days (Gage, 1964).
Groups of two rats (one male, one female) were given 1 to 5 oral
doses of 44 mg/kg bw BHT on alternate days and rats in each group were
killed 24 h after the final dose. The range of the total dose
accounted for was 92 to 104% in males and 93 to 99% in females. There
was an indication of sex difference in the route of excretion, females
excreting 19-43% of the radioactivity in urine and males only 3-15%.
Eight days after administration of 5 doses, 92% of the radioactivity
had been excreted by males and 97% by females. Subcutaneous
administration of graded doses of BHT to female rats revealed
substantial faecal excretion but the rate of excretion decreased with
increasing dose. There was no evidence of accumulation of 14C-BHT in
the body under the conditions of repeated oral dosage (Tye et al.,
Rats were given single oral doses (1-100 mg/rat) of 14C-BHT and
approximately 80 to 90% of the dose was recovered within four days in
the urine and faeces. Of the total radioactivity, 40% and 25% appeared
in the urine of females and males, respectively. After 4 days,
approximately 3.8% of the dose was retained, mainly in the alimentary
tract. A substantial portion of the radioactivity was found in the
bile collected from two rats (one male, one female) over a period of
40 h. The relatively slow excretion of BHT is probably attributable to
enterohepatic circulation rather than to tissue retention (Daniel &
The liver and body fat of rats fed a diet containing 0.5% BHT for
35 days were analyzed. The concentration of BHT in the liver never
rose above 5 mg/kg in males and 1.5 mg/kg in females. In the body fat,
the level fluctuated around 30 mg/kg in males and 45 mg/kg in females.
Fat from rats returned to BHT-free diet showed a progressive fall in
the concentration of BHT, the half-life being about 7 to 10 days.
The daily excretion of radioactivity in urine and faeces was
studied in rats given an oral dose of 14C-labelled BHT (12 mg/kg
bw). Excretion became negligible by the sixth day after administration
when about 70% of the injected dose had been recovered. Less than 1%
was excreted as carbon dioxide in the expired air. About 50% of the
radioactivity was excreted in the bile during the 24-hour period
following the oral dose (Daniel & Gage, 1965).
The BHT content of fat and liver of rats given diets containing
0.5 or 1% BHT for periods up to 35 and 50 days, respectively, were
analyzed. With 0.5% BHT in the diet, a level of approximately 30 mg/kg
in the fat was reached in males and 45 mg/kg in females, with
approximately 1-3 mg/kg in the liver. With 1% BHT, the level in the
fat was 50 mg/kg in males and 30 mg/kg in females. On cessation of
treatment, the level of BHT in fat fell with a half-life of 7 to 10
days (Daniel & Gage, 1965).
The level of BHT in the fat reached a plateau at approximately
100 mg/kg after 3 to 4 days when daily doses of 500 mg/kg bw were
given by intubation. A daily dose of 200 mg/kg bw for one week
produced a level of about 50 mg/kg (Gilbert & Golberg, 1965).
Rats were given doses of 100 µg of 3H-labelled BHT
intraperitoneally and the urinary output of radioactivity was measured
for 4 consecutive days. After 4 days of dosing, 34.5% of the injected
radioactivity was recovered in urine (Ladomery et al., 1963). The
same dose of BHT (100/µg) labelled with 14C was given to rats, and
34% of the radioactivity was excreted in the urine in the first four
days, in close agreement with the previous result using tritiated BHT
(Ladomery et al., 1967a).
After a single parenteral dose (100 µg) of 14C-BHT, rats
excreted 3235% of the radioactivity in the urine, and 35-37% in the
faeces, in a 4-day period. The intestinal contents together with the
gut wall contained most of the remaining activity. Biliary excretion
was rapid, and the radioactive material in bile was readily absorbed
from the gut, suggesting a rapid enterohepatic circulation
(Ladomery et al., 1967b).
White male Wistar rats (290-350 g) were administered
[14C]-labelled BHT, or its alcohol [BHT-CH2OH] or its aldehyde
[BHT-CHO] or acid [BHT-COOH] derivative by i.v. or i.p. injection. The
overall excretion of BHT and its related compounds excreted in urine
and faeces was studied for a 5-day period, and biliary excretion
monitored for 120426 h after i.p. injection. For the low doses of the
compounds tested (100 µg), there were no significant differences in
the total recovery of 14C during the 5 days urinary and faecal
excretion and 120-126 h biliary excretion. However, there were
differences in ratio of urinary to faecal excretion of 14C. The
major metabolite present in early bile after i.p. injection of the
labelled compounds was BHT-COOH or its ester glucuronide. Late bile
after acid hydrolysis showed BHT-COOH to be the major 14C component
(Holder et al., 1970a).
Temporal concentration changes in BHT and BHT-quinone methide
were studied following a single oral dose of 800 mg BHT/kg bw in rats,
which were monitored in plasma, the GI tract, and some adipose tissues
over a 48-hour period using GLC. Groups of 4 or 5 male Sprague-Dawley
rats were sacrificed at 0.5, 1, 3, 6, 12, 18, 24, 30, 36 or 48 h after
administration of BHT. The amount of BHT in the gastric contents
stayed constant for 12 h, then declined rapidly to 24 h, followed by a
gradual decline to 48 h. BHT was not detected in the plasma at any of
the time points, while BHT-quinone methide showed a rapid rise between
12 and 18 h after administration, followed by a gradual decline to
48 h. BHT was detected in epididymal, subcutaneous, perirenal and
brown dorsal adipose tissue soon after administration. A peak
concentration was noted in epididymal and subcutaneous fat at 18 h,
but did not show this trend in perirenal or brown dorsal fat.
In a second experiment, in which groups of 5 or 6 rats were
sacrificed 4-7 or 24-27 h after administration of BHT, a single oral
dose of 800 mg/kg bw resulted in a significant increase in the weight
of stomach contents in both fasted and non-fasted rats at 4-7 h. By
24-27 h after administration, there was no difference in the weight of
stomach contents between non-fasted treated animals and controls. This
study suggested that high single doses of BHT caused a delay in
gastric emptying which was reflected in the delay in plasma levels of
In another experiment, 800 mg/kg bw BHT was instilled
intraduodenally to 5 anaesthetized rats and 30 minutes later the
concentrations of BHT and its metabolites were measured in blood from
the portal vein and descending aorta, and in liver and epididymal
adipose tissue. BHT and/or BHT radical was detected in all but the
descending aorta, while BHT-quinone methide was not present in any of
the samples collected at 30 minutes after administration (Takahashi,
One-day old chicks were given 14C-BHT at a level of 200 mg/kg
in the feed for 10 weeks. At broiler age, edible portions had residues
amounting to 1-3 mg/kg of BHT and metabolites. Similar diets given to
laying hens produced residues in eggs of 2 mg/kg after 7 days, the
level thereafter remaining constant (Frawley et al., 1965a).
When feed containing 500 or 100 mg/kg BHT was given to laying
hens, residues of 20 and <5 mg/kg were found in the fat fraction of
eggs, respectively. In the broiler chicken, over a period of 21 weeks,
the residues in body fat were 55 mg/kg on the 500 mg/kg diet and
< 5 mg/kg on the 100 mg/kg diet (Van Stratum & Vos, 1965).
Four human male subjects were administered a single dose of
approximately 40 mg 14C-labelled BHT. About 75% of the administered
radioactivity was excreted in the urine. About 50% of the dose
appeared in the urine in the first 24 h, followed by a slower phase
which probably represented the release of the compounds or their
metabolites stored in tissues. In humans, the bulk of the
radioactivity was excreted as the ether insoluble glucuronide of a
metabolite in which the ring methyl group and one tert-butyl methyl
group were oxidized to carboxyl groups, and a methyl group on the
other tert-butyl group was also oxidized, probably to an aldehyde
group. BHT-acid, free and conjugated, was a minor component of the
urine and the mercapturic acid was virtually absent. The rapidity of
the first phase of the urinary excretion in humans suggested that
there was no considerable enterohepatic circulation as had been
observed in the rat (Daniel et al., 1967).
Reported values of BHT in body fat were 0.23 ± 0.15 mg/kg
(11 individuals, residents of the United Kingdom) and 1.30 ±
0.82 mg/kg (12 individuals, residents of the United States of America)
(Collings & Sharratt, 1970).
Based on reported BHT levels in human fat in Japan, United
Kingdom and USA and the calculated dietary intakes of BHT, a
bioconcentration factor in humans (BCF, wet weight basis) of 0.36 was
calculated for BHT. This BCF was 45 times higher than that calculated
for the rat. In comparison, the BCF for total DDT was calculated at
1279 (Geyer et al., 1986).
The disposition of single oral doses of BHT was compared in
humans and rats. A single oral dose of 0.5 mg/kg bw of BHT was
ingested by 7 healthy male volunteers after fasting overnight. Blood
samples were taken after 0, 15, 30, 45, 60, 75, 90, 120, 150, 180 and
240 minutes. Total urine and faeces were collected for 2 days. In
another experiment, 5 healthy female volunteers ingested 0.25 mg/kg bw
of BHA and one week later 0.25 mg/kg bw of BHT. After another week,
0.25 mg/kg bw of BHT plus 0.25 mg/kg bw of BHA were given
simultaneously. After each dosing, blood samples were taken as
described above. Similar experiments were conducted in male Wistar
rats, except that the doses used were 20, 63, or 200 mg/kg bw of BHT.
In rats, peak plasma concentrations of BHT (0.2, 0.3, and 2.3 µg/ml)
were seen after 2.6 h. Simultaneous administration of BHA produced
significantly lower plasma concentrations between 0.5 and 3 h. Large
variations were seen in humans in plasma levels of BHT. The mean peak
plasma level was 0.09/µg/ml, reached after 1.5 h. The plasma
concentrations were not influenced by simultaneous administration of
BHA. In the rat, approximately 2% of the dose was excreted as BHT-COOH
in the urine (equal amounts of conjugated and unconjugated compound)
and 10% as BHT in the faeces in 4 days. In humans, 2.8% of the dose
was found in the urine as BHT-COOH (mainly conjugated) and no BHT
could be detected in the faeces. On a comparative dose basis, it seems
that BHT in plasma reaches a higher level in humans than in rats
(Verhagen et al., 1989).
The oxidative metabolism of BHT by liver microsomes from 3 inbred
mouse strains, NGP/N, A/J and MA/MyJ was compared. The strain order
shown is the order of increasing susceptibility of these mice to BHT
lung tumour promotion which correlates with their increasing ability
to produce BHT-BuOH, by hydroxylation of BHT at one of the
tert-butyl groups. Four weekly i.p. injections of BHT selectively
induced the BHT oxidation pathway leading to formation of BHT-BuOH
(Thompson et al., 1989).
The metabolism of BHTOOH was examined to assess the role of
reactive intermediates in mediating tumour promotion in mouse skin.
Incubation of BHTOOH with either isolated neonatal mouse keratinocytes
or a cell-free haematin system resulted in the generation of
the BHT-phenoxyl radical. Only one non-radical metabolite of
BHTOOH-BHT-quinol was detected in keratinocytes, while incubation of
BHTOOH with haematin produced several metabolites: oxacyclopentenone,
BHT-quinone, BHT, BHT-stilbene quinone, and BHT-quinone methide. In
contrast to the action of BHTOOH, topical application of epidermal
doses of BHT-quinol, BHT-quinone, BHT-stilbene quinone, as well as BHT
itself to mouse skin, did not induce epidermal ornithine decarboxylase
activity (Taffe et al., 1989).
Co-administration of BHA (200 mg/kg bw) with a subtoxic dose of
BHT (200 mg/kg bw) enhanced the lung toxicity of BHT in male mice. BHA
co-administration significantly increased the radioactivity covalently
bound to lung macromolecules at 4-8 h after [14C]-BHT. The
pretreatment also reduced the rate of in vitro metabolism of BHT in
mouse liver supernatant. The co-administration of BHA and BHT caused a
decrease in metabolism of BHT in the liver with the result that the
lung was exposed to a larger amount of BHT (Yamamoto et al., 1988).
Examination of the biliary metabolites from i.v. and i.p. doses
of small amounts of 14C-BHT, showed the presence of four principal
metabolites. Some 34 to 53% of the 14C-label in the bile was
identified as 3-5-di- t-butyl-4-hydroxy-benzoic acid, which was
probably present as the ester glucuronide. The other metabolites
present were 3,5-di- t-butyl-4-hydroxybenzaldehyde, 3-5-di- t-butyl-
4-hydroxybenzyl alcohol, and 1,2-bis (3,5-di- t-butyl-4-hydroxyphenyl)
ethane (Ladomery et al., 1967b).
Rats were given a single dose of 14C-BHT and urine and
bile collected for periods ranging from 48 to 96 h. Faeces were
also collected during this same period. About 19% to 59% of the
radioactivity appeared in the urine during this period, and 26% to 36%
in the bile. The major metabolites in the urine were 3,5-di- tert-
butyl-4-hydroxybenzoic acid, both free (9% of the dose), as well as
glucuronide (15%) and S-(3,5-di- tert-butyl-4-hydroxybenzyl)-
N-acetylcysteine. The ester glucuronide and mercaptic acid were also
the major metabolites in rat bile. Free 3,5-di- tert-butyl-4-
hydroxybenzoic acid was the major metabolite in faeces (Daniel
et al., 1968).
Male Wistar rats were dosed intraperitoneally with 200 mg/kg bw
BHT-acid or 2,6-di- tert-butyl phenol (DBP). Faeces and urine were
collected for 5 days after administration of BHT-acid and for 3 days
after administration of DBP. Bile was collected from rats treated with
BHT-acid for 24 h after administration. Following administration of
BHT-acid, the metabolites DBP, 2,6-di- tert-butyl- p-benzoquinone
(BBQ), 2,6-di- tert-butylhydroquinone (BHQ) glucuronide and BHT-acid
glucuronide were identified in the faeces and bile. This suggested
that BHT-acid, considered as a main metabolic end-product of BHT,
was metabolized to the quinone and hydroquinone following its
decarboxylation to form the di-substituted phenol, DBP. An alternative
route for formation of the quinone, BBQ, was a homolysis reaction of
the O-O bond of the hydroperoxide which is catalyzed by rat liver
cytochrome P-450 (Yamamoto et al., 1991).
Rabbits were given single or repeated doses of BHT in the range
of 400-800 mg/kg bw. About 16% of the dose was excreted as ester
glucuronide and 19% as ether glucuronide. Unconjugated phenol (8%),
ethereal sulfate (8%) and a glycine conjugate (2%) were also excreted.
Excretion of all detectable metabolites was essentially complete 3 to
4 days after administration of the compound and about 54% of the dose
was accounted for as identified metabolites (Dacre, 1961).
The metabolism of butylated hydroxytoluene (BHT) orally
administered to rabbits in single doses of 500 mg/kg bw was studied.
The metabolites 2,6-di- tert-butyl-4-hydroxymethylphenol
(BHT-alcohol), 3,5-di- tert-butyl-4-hydroxy-benzoic acid (BHT-acid)
and 4,4'-ethylene- bis-(2,6-di-tert-butylphenol) were identified. The
urinary metabolites of BHT comprised 37.5% as glucuronides, 16.7%
as ethereal sulfates and 6.8% as free phenols; unchanged BHT was
present only in the faeces (Akagi & Aoki, 1962a); 3,5-di- tert-butyl-
4-hydroxybenzaldehyde (BHT-aldehyde) was also isolated from rabbit
urine (Aoki, 1962). The main metabolic pathway was confirmed by
administering BHT-alcohol to rabbits and isolating BHT-aldehyde,
BHT-acid, the ethylene- bis derivative and unchanged BHT-alcohol in
the urine (Akagi & Aoki, 1962b).
When [14C]BHT was activated in vitro by the prostaglandin H
synthase system in microsomes from ram seminal vesicles or by
horseradish peroxidase, significant covalent binding to protein could
be detected. BHT-quinone methide was detected at only minor
concentrations, therefore an intermediate free radical was suggested
as an active metabolite. Addition of BHA to the medium greatly
increased the formation of BHT-quinone methide and covalent binding to
proteins (Thompson et al., 1986).
A group of 8 men each received 100 mg of BHT on two occasions
separated by a 4-day interval. Urine was collected for 24 h after BHT
administration. The metabolites were identified as BHT-COOH and
benzoyl-glycine. In another study in which two adults were given 1.0 g
of BHT, BHT-COOH and its ester glucuronide were the only major
metabolites identified in urine (Holder et al., 1970b).
126.96.36.199 Combined species
The metabolism of BHT was studied with liver and lung microsomes
from rats and mice. Two main metabolic processes occurred,
hydroxylation of alkyl substituents and oxidation of the aromatic ¼
electron system. The former led to the 4-hydroxymethyl product
(BHT-CH2OH) and a primary alcohol resulting from hydroxylation of a
t-butyl group (BHT- tBuOH). Additional metabolites were produced by
oxidation of BHT-CH2OH to the corresponding benzaldehyde and benzoic
acid derivatives. Hydroxylation of BHT- tBuOH occurred at the
benzylic methyl position, and the resulting diol was oxidized further
to the hydroxybenzaldehyde derivative. Oxidation of the ¼ system led
to BHT-quinol (2,6-di- t-butyl-4-hydroxy-4-methyl-2,5-cyclo-
hexadienone), BHT-quinone (2,6-di- t-butyl-4-benzoquinone), and
BHT-quinone methide (2,6-di- t-butyl-4-methylene-2,5-cyclohexa-
dienone) probably via the hydroperoxide (BHTOOH). Derivatives of the
quinol and quinone with a hydroxylated t-butyl group were also
formed. Quantitative data demonstrated that BHT-CH2OH was the
principal metabolite in rat liver and lung microsomes. The mouse
produced large amounts of both BHT-CH2OH and BHT- tBuOH in these
tissues. The metabolite profile was similar in rat liver and lung.
Mouse lung, however, produced more quinone relative to other
metabolites than mouse liver (Thompson et al., 1987).
The in vitro peroxidase-catalyzed covalent binding of BHT to
microsomal protein and the formation of BHT-quinone methide was
enhanced by addition of BHA. Several other phenolic compounds commonly
used in food also enhanced the metabolic activation of BHT. Microsomes
from lung, bladder, kidney medulla and small intestine of various
animal species, including humans, were also able to support this
interaction of BHA and BHT using either hydrogen peroxide or
arachidonic acid as the substrate (Annex 1, reference 95).
Phenobarbital (PB) pretreatment of Sprague-Dawley rats and A/J
mice had little or no effect on respective quinone methide formation
from BHT or BHT-BuOH in pulmonary microsome preparations, but resulted
in a 6-37 fold induction of this activity in hepatic microsomes from
these species. PB administration had little effect on the two-step
oxidation of BHT to QM-OH in pulmonary microsomes of the mouse, while
in hepatic microsomes, PB pre-treatment resulted in a greater than
100-fold increase in this activity. This was found to be mainly due to
a greater than 100-fold increase in the initial tert-butyl
hydroxylation step in mouse liver microsomes. The enhancement was
somewhat higher than for 7-pentoxyresorufin O-dealkylase activity,
demonstrating that tert-butyl hydroxylation could serve as a
specific marker for the enzyme. The results also showed that pulmonary
microsomes from mice, but not rats, had a relatively high constitutive
P-450 activity for tert-butyl hydroxylation of BHT, supporting
the proposal that this metabolite was involved in BHT-induced
pneumotoxicity. Two cytochrome P-450 inhibitors, SKF 525-A and
metapyrone, inhibited the conversions of BHT to QM and QM-OH to a
similar extent in PB-treated mouse liver microsomes; the terpenoid
alcohol cedrol was found to selectively inhibit BHT conversion to
QM-OH. This compound has been found previously to inhibit
pneumotoxicity when administered to mice prior to treatment with BHT.
In untreated mouse liver microsomes, BHT hydroxylation to BHT-MeOH
showed the greatest activity, with oxidation to QM second and
hydroxylation to BHT-BuOH last (Bolton & Thompson, 1991).
2.1.3 Effects on enzymes and other biochemical parameters
Mice (BALB/c strain) were maintained on a diet containing 7.5 g
BHT/kg of feed. After 3 weeks on the test diet, there was an enhanced
activity in plasma esterases which persisted throughout the
experimental period of 20 weeks. Following electrophoretic separation
of the esterases, the increased enzyme activity was shown to be
located in two specific bands (Tyndall et al., 1975).
Dietary administration of BHT to male Swiss Webster mice resulted
in a marked increase in hepatic microsomal epoxide hydrolase and
glutathione-S-transferase (Hammock & Ota, 1983).
Feeding experiments were carried out on 45 pairs of weanling male
rats for 5 to 8 weeks with diets containing 0, 10 or 20% lard
supplements to which 0.01, 1 or 5 g BHT/kg had been added. At
0.01 g/kg, no changes were observed in any of the serum constituents
studied, while at 5 g/kg an increase in the serum cholesterol level
was seen within 5 weeks. Female rats fed for 8 months a diet
containing a 10% lard supplement with 1 g BHT/kg showed increased
serum cholesterol levels, but no other significant changes. Diets
containing 5 g BHT/kg in 10% and 20% lard supplements fed to female
rats for the same period increased serum cholesterol, phospholipid and
mucoprotein levels (Day et al., 1959).
In further work with rats, it was found that increased output of
urinary ascorbic acid accompanied liver enlargement induced by BHA or
BHT in onset, degree and duration, being rapid but transient with BHA,
and slower in onset but more prolonged with BHT (Gaunt et al.,
1965a). The simultaneous stimulation of processing enzyme activity,
increase in urinary ascorbic acid output, and increase in relative
liver weight brought about by BHT was unaffected by 14 days of dietary
restriction, and all these changes except liver weight were reversible
during 14 days' recovery on normal diet (Gaunt et al., 1965b).
Rats given BHT by daily intubation showed increased activity of
some liver microsomal enzymes. Stimulation of enzyme activity
correlated with an increase in relative liver weight. The threshold
dose for these changes in enzyme activity in female rats was below
25-75 mg BHT/kg bw/day. The storage of BHT in fat appeared to be
influenced by the activity of the processing enzymes. In rats given
500 mg/kg bw/day, the level of BHT in fat attained values of 230 mg/kg
in females and 162 mg/kg in males by the second day, by which time the
relative liver weight and processing enzyme activities had become
elevated. Thereafter, liver weight and enzyme activity continued to
rise but the BHT content of fat fell to a plateau of about 100 mg/kg
in both sexes (Gilbert & Golberg, 1965).
Groups of 12 SPF Carworth rats equally divided by sex were
administered BHT dissolved in arachis oil daily for one week, at dose
levels of 50, 100, 200 or 500 mg/kg bw. A group of 8 rats served as
control. The animals were killed 24 h after the final dose, and
histological and biochemical studies (glucose-6-phosphatase: and
glucose-6-phosphate dehydrogenase) made on the livers of all animals.
A histochemical assessment of the livers of test animals was also
carried out. BHT caused an increase in liver weight in males at dose
levels of 100 mg/kg bw and greater, and in females at 200 mg/kg bw and
greater. BHT caused a decrease in glucose-6-phosphatase activity in
females at dose levels greater than 100 mg/kg bw, and an increase in
glucose-6-phosphate dehydrogenase in both males and females at the
highest dose tested. In another study, rats were dosed according to
the above schedule and then maintained for 14 to 28 days following the
final dosing. By day 28, no biochemical changes were observed, and
relative liver weights returned to normal by day 14 (Feuer et al.,
Rats fed diets containing BHT at levels of 100 to 5000 mg/kg for
12 days showed liver enlargement, as well as increased activity of
liver microsomal biphenyl-4-hydroxylase, at all levels except the
lowest level of 100 mg/kg. Enzyme activity was not significantly
altered at 5000 mg/kg BHT fed for one day (Creaven et al., 1966).
Rats (male and female Carworth Farm SPF) were given an oral dose
of BHT equivalent to 500 mg/kg bw. Dosing was from 1 to 5 days, and
rats varying in size from 100-400 g body weight were used. Microsomal
preparations from the livers of treated rats were assayed for BHT
oxidase, an enzyme that metabolizes BHT to the BHT alcohol
(2,6-di- tert-butyl-4-methylphenol to 2,6-di- tert-butyl-4-hydroxy
methylphenol). Treatment of female rats with BHT (500 mg/kg bw/day for
5 days) caused a six fold increase in the activity of the enzyme/gram
of liver and a 35% increase in relative liver weight, both being
prevented by actinomycin D. The induction was more pronounced in males
than in females, and the induction of the enzyme, low in rats in the
100 g body-weight range, reached a maximum in rats in the 200 g
body-weight range, and fell in larger animals (300-400 g range)
(Gilbert & Golberg, 1967).
Groups of female Alderly Park SPF rats were maintained on diets
containing 0%, 0.01%, 0.1%, 1% or 5% BHT for periods up to 28 days,
and then on diets free of BHT for 56 days. Animals were killed in
groups of four, 2 being used for enzyme assay (aminopyrene
demethylase) and 2 for electron microscopy. The increase in enzyme
activity was directly related to the dietary level of BHT. No
detectable increase was observed at the lowest level over the 28-day
feeding period. Following withdrawal of BHT from the diet, the enzyme
level returned to normal in all test animals. The degree of
endoplasmic reticulum proliferation was proportional to the amount of
BHT in the diet and the duration of feeding at the 5% and 1% level. At
the 0.1% level, there was a transient rise in smooth endoplasmic
reticulum. No proliferation was observed at the 0.01% level. Following
removal of BHT from the diet, there was a rapid disappearance of the
proliferated smooth endoplasmic reticulum.
In a second study, groups of rats were fed diets containing 1%
BHT for 10 days, and then for a second period of 10 days after an
interval of 20 days on a normal diet. The animals were killed in
groups of five at 10, 30, 40, 42 or 47 days. Livers were removed for
aminopyrene demethylase assay and electron microscopy. Enzyme activity
did not differ significantly following both 10-day periods of
administration of BHT. Electron microscopy showed similar smooth
endoplasmic reticulum response during both these periods (Botham
et al., 1970).
Microsomal preparations from livers of rats, dosed daily with
450 mg/kg bw BHT for up to 7 days, showed an increased capacity to
incorporate labelled amino acids, when compared to preparations from
controls. BHT also stimulated the in vivo incorporation of amino
acids, mainly into the proteins of the endoplasmic reticulum
A group of 23 female SPF rats (Wistar strain) was administered
500 mg/kg BHT dissolved in rape-seed oil, for 11 days. The control
group was administered rape-seed oil alone. Groups of 7 rats were
killed following administration of the final dosing. The remaining
rats were maintained without further exposure to BHT, and killed on
days 28 or 63 of the study. Livers of the rats were examined for
weight, DNA content and number of cell nuclei. Treatment with BHT
resulted in enlargement of the liver, with a concomitant increase in
its DNA content, and in the number and ploidy of its nuclei. The liver
mass returned to normal within two weeks. However, the DNA content of
the liver of BHT-treated animals remained elevated up to the time of
termination of this study, and there was no reduction in the total
number of nuclei or the degree of ploidy (Hermann et al., 1971).
Two groups of 10 male and 10 female rats (Alderly Park, SPF
Wistar strain) were dosed by stomach tube with 200 mg/kg bw/day of BHT
dissolved in maize oil for 7 days. Four rats/sex dosed with an
equivalent amount of maize oil served as controls. Urinary ascorbic
acid excretion was measured in urine samples collected following 5
days on the test compound. The animals were killed 24 h after the
final dose and the livers removed for biochemical assays (aminopyrine
demethylase-AMPM, hexobarbitone oxidase-HO, cytochrome P-450, and
glucose-6-phosphatase), and electron microscopy. Another group of
treated rats was maintained for a 7-day recovery period, and a similar
battery of liver studies was carried out. Administration of BHT
resulted in an increase of urinary excretion of ascorbic acid which
remained constant throughout the treatment period. Following cessation
of BHT treatment there was a gradual return towards control values.
There were significant sex differences in some of the biochemical
responses to BHT, with the exception of the glucose-6-phosphatase
activity. Female rats showed a marked increase in APDM and HO
activity, which was not observed in male rats. Cytochrome P-450 levels
were increased in both males and females. The biochemical parameters,
with the exception of APDM activity in female rats, returned to normal
following the 7-day recovery period. Electron microscopy showed
significant proliferation of the smooth endoplasmic reticulum of the
hepatic cells. No other morphological changes were detected
(Burrows et al., 1972).
BHT (500 mg/kg bw/day) was administered by gavage to groups of
young Wistar male and female rats for 7 days and the animals were
housed in metabolism cages. Control animals received corn oil vehicle
only. They were then sacrificed and liver enzymes (aniline-
4-hydroxylase, biphenyl-4-hydroxylase, ethyl morphine N-demethylase,
and 4-methyl umbelliferone glucuronyl transferase) were assayed and the
cytochrome P-450-CO interaction spectrum evaluated. Urinalysis using
GC was conducted to assay for D-glucaric acid, D-glucuronic acid,
1-gulonic acid, xylitol and L-ascorbic acid. Administration of BHT
enhanced all the parameters measured with the exception of the hepatic
microsomal protein content. BHT was a more potent inducer of
xenobiotic metabolism in female rats (Lake et al., 1976).
BHT in the diet of Sprague-Dawley rats resulted in a marked
decrease in the NADPH-cytochrome P450 reductase activity of isolated
liver microsomal preparations. This effect was not observed when BHT
was added in vitro to liver microsomes (Rikans et al., 1981).
Dietary BHT was also shown to affect the carboxylation process in
the conversion of rat liver microsomal protein to prothrombin
(Takahashi & Hiraga, 1981a).
Rats fed a diet containing 0.4% BHT showed an increase in GSH-S
transferase activity in the liver, but not in lungs and kidneys.
GSH-reductase levels were increased in liver and lungs
(Partridge et al., 1982).
BHT at 300-6000 mg/kg in the diet caused a dose-dependent
increase in gamma-glutamyl transpeptidase in normal F344 male rats.
However, cytosolic glutathione S-transferase was only enhanced at
dietary concentrations of 3000 or 6000 mg/kg (Furukawa et al.,
Groups of 4 male F344 rats were pretreated with buthionine
sulfoximine, a glutathione-depleting agent (900 mg/kg bw), and after
1 h given intraperitoneal injections of BHT (100, 250, 400, or
500 mg/kg bw). A dose-related elevation of serum GOT and GPT
activities was observed. BHT or buthionine sulfoximine alone had no
effect. In contrast, pretreatment with cysteine (100-200 mg/kg bw)
inhibited the elevation of serum enzyme activities at a toxic dose of
BHT (1000 mg/kg bw) (Nakagawa, 1987).
Supplementation of AAF-containing diets with 0.3% BHT, which
affords protection against AAF hepatocarcinogenesis in high-fat fed
Sprague-Dawley rats, protected and/or induced total hepatic nuclear
envelope cytochrome P-450 content. Short-term feeding with AAF without
BHT resulted in a marked loss of total hepatic nuclear envelope P-450
(Carubelli & McCay, 1987). Immunological studies showed that BHT
enhanced the AAF-dependent induction of P-450c, but not P-450d. BHT by
itself had no effect on these nuclear envelope enzymes
(Friedman et al., 1989).
Administration of 0.5% BHT in the diet of male Wistar rats for 2
weeks increased UDP-glucuronosyl transferase activity in liver
microsomes for several substrates to 236-269% of controls. The amounts
of UDP-glucuronosyl transferase protein and associated mRNA in liver
microsomes were also increased, paralleling the increases in enzyme
activity. In addition to induction of hepatic activity, BHT treatment
resulted in increased activity in microsomes from the kidney and small
intestine (Kashfi et al., 1994).
Acute effects on electrolyte excretion, similar to those
described for large doses of BHA were also obtained following
administration of BHT at doses of 500-700 mg/kg bw. No such effects
were observed at lower dosage levels (Denz & Llaurado, 1957).
Groups of 2-4 juvenile rhesus monkeys (Macaca mulatta) were fed
BHT dissolved in corn oil at dose levels of 0, 50, or 500 mg/kg bw for
4 weeks. Blood samples were taken prior to treatment and then at
weekly intervals from the control and test animals in the high-dose
group, and from test animals in the low-dose group at the end of the
4-week period, for determination of total plasma cholesterol, lipid
phosphorus and triglyceride. Liver biopsies were taken from the test
animals in the high group at two weeks. At the end of the test period
all animals were fasted for 24 h and sacrificed, and liver and blood
samples obtained. Liver samples were analyzed for succinic
dehydrogenase and susceptibility to peroxidation. Extracted liver
lipids were analyzed for total cholesterol, lipid phosphorus and
triglycerides. Total cholesterol levels in plasma and liver were
significantly lowered. Lipid phosphorus levels in the plasma were
increased at the high-dose level, as were cholesterol:lipid phosphorus
ratios in the plasma and liver. The susceptibility of liver lipids to
oxidation was reduced in the high-dose group (Branen et al., 1973).
2.2 Toxicological studies
2.2.1 Acute toxicity studies
The results of acute toxicity studies with BHT are summarized in
Acute oral, intraperitoneal (mice) and eye irritation (rabbits)
and skin irritation (rats) were measured for 7 breakdown products of
BHT. All compounds tested were less toxic than the parent compound
(Conning et al., 1969).
Table 1. Acute toxicity studies with BHT
Animal Route LD50 Approximate Reference
(mg/kg bw) lethal dose
Rat oral > 1700-1970 - Deichmann et al., 1955
Cat oral - 940-2100 Deichmann et al., 1955
Rabbit oral - 2100-3200 Deichmann et al., 1955
Guinea-pig oral - 10 700 Deichmann et al., 1955
Rat oral 2450 Karplyuk, 1959
Mouse oral 2000 Karplyuk, 1959
As shown in Table 2, the LD50 (i.p.) for BHT showed
considerable differences for strains of inbred and non-inbred male
mice. In all cases death occurred 4 to 6 days after administration of
BHT, and was accompanied by massive edema and haemorrhage in the lung
(Kawano et al., 1981).
Table 2. Variation in LD50 with strains of mice (Kawano et al., 1981)
Strain LD50 (mg/kg bw)
DBA/2N (inbred) 138
BALB/cNnN (inbred) 1739
C57BL/6N (inbred) 917
ICR-JCL (non-inbred) 1243
2.2.2 Short-term toxicity studies
In order to estimate the MTD for BHT in mice, groups of 5/sex
B6C3F1 mice, 6-week old, were fed diets containing 0, 3100, 6200,
12 500, 25 000 or 50 000 mg BHT/kg of feed for 7 weeks. Each animal was
weighed twice weekly. Gross necropsy was performed on all animals. One
female mouse in the 25 000 mg/kg group, and 1 male and 4 female mice
in the 50 000 mg/kg group died before the end of the study.
Body-weight decrements, mostly dose-related, were noted in all
treatment groups compared with controls. Histopathologic examination
of male mice receiving 25 000 mg/kg revealed a very small amount of
centrilobular cytoplasmic vacuolization of hepatocytes which was not
observed in females receiving 12 500 mg/kg (high-dose females were not
examined) (NCI, 1979).
A similar study was conducted to establish the dose levels for a
subsequent carcinogenicity study. Groups of B6C3F1 mice (10/sex)
received BHT in the diet at concentrations of 0.25%, 0.5%, 1%, 2%, or
4% for 10 weeks. Twenty mice/sex were used for the control group. Both
male and female mice receiving the highest dose of BHT experienced a
retardation of body-weight gain which exceeded 10% of control values.
In addition, histopathological examination of mice in the 4% group,
revealed marked starvation atrophy of the spleen, heart and kidneys.
None of these changes were noted in mice at the next lower dose level
(2% diet) or any of the other groups. The MTD was considered to be 2%
diet (Inai et al., 1988).
Groups of male and female C3H mice (17-39 mice/group), 6-10
weeks old, were maintained for 10 months on a semi-synthetic diet
containing 0.05 or 0.5% BHT. Control groups were maintained on
BHT-free semi-synthetic diet or commercial lab chow. At the end of the
test period, the liver and lungs were excised and inspected grossly
for proliferative lesions. Of the proliferative lesions considered to
be clearly identifiable as tumours, approximately 50% were examined
microscopically. Mice maintained on diets containing BHT had lower
body weights than controls. Male mice fed BHT showed an increase in
liver tumours, compared to controls. Histologically, the tumours were
identified as hepatocellular adenomas. No increase was observed in
female mice. The reported incidence of liver tumours in male C3H
mice was 38% (10/26) in the 0.5% BHT group, 58% (15/26) in the 0.05%
BHT group, 5% (2/37) in the control semi-synthetic diet group, and 18%
(7/38) in the control lab chow group.
In a study in which C3H mice were maintained on diets
containing 0.5% BHT for one month followed by lab chow for 10 months,
or control diet (BHT-free) for one month followed by lab chow for 10
months, the incidence of liver tumours in the two groups of male mice
were 9% (3/35) and 17% (5/29), respectively. Dietary BHT did not
result in an increased incidence of lung tumours in either male or
In another study in which male BALB/c mice were maintained for
one year on a BHT-free diet, or diets containing 0.05% BHT or 0.5%
BHT, the incidence of liver tumours were 13% (4/30), 14% (6/43), and
7% (2/28) for the respective groups (Lindenschmidt et al., 1986).
It has previously been demonstrated that the incidence of
spontaneously-occurring hepatic tumours in C3H mice is modified by
sex, population density, level of dietary protein, and caloric intake.
Historical dam were not available for a 10-month study. The incidence
of hepatic tumours in a 12-month study in this strain ranged from
6-13% for females, and 41-68% for males (Peraino et al., 1973).
Thus, the reported incidence of hepatocellular tumours was not
significantly different from other controls of similar age in studies
with the same inbred strain.
Feeding experiments conducted for 20 or 90 days indicated that
rats did not find food containing respectively 0.5 or 1% BHT
palatable. However, the animals ingested food so treated more readily
if these concentrations were attained gradually. Paired feeding
experiments with groups of 5 or 10 rats for 25 days demonstrated that
diets containing 0.8 and 1% BHT reduced the daily intake of food below
control values. A level of 1% in the diet retarded weight gain
BHT (0.3%) in the diet of pregnant rats that had been kept for 5
weeks on a diet deficient in vitamin E produced no toxic symptoms,
while 1.6% caused drastic loss of weight and fetal death (Ames
et al., 1956).
BHT was fed to rats (12/group) for 7 weeks at a level of 0.1% BHT
in diets containing 20% or 10% lard supplement. With the 20% lard
supplement diet, significant reduction of the initial growth rate and
mature weight of male rats was observed. No effect was noted in female
or male rats receiving the 10% lard supplement diet. A paired feeding
experiment showed that this inhibition of growth was a direct toxic
effect of BHT and could not be explained by a reduction in the
palatability of the diet. At this level BHT produced a significant
increase in the weight of the liver, both absolute and relative to
body weight. Rats under increased stress showed significant loss of
hair from the top of the head. The toxic effect of BHT was greater if
the fat load in the diet was increased. Anophthalmia occurred in 10%
of the litters (Brown et al., 1959).
BHT administered to rats at 250 mg/kg bw/day for 68 to 82 days
caused fatty infiltration of the liver and reduction in body-weight
gain (Karplyuk, 1959).
Groups of 6 weanling rats (3/sex) were fed diets containing a 20%
lard supplement and BHT at levels of 0, 0.1, 0.2, 0.3, 0.4 or 0.5% for
6 weeks. BHT reduced the growth rate, especially in males, the effect
becoming significant at 0.3% BHT. It also increased the absolute liver
weight and the ratio of liver weight to body weight in both sexes, the
latter effect becoming significant at 0.2% BHT. BHT increased the
ratio of left adrenal weight to body weight in male rats but had no
consistent effect in females. There were no histological changes in
the adrenal attributable to treatment. All dietary levels of BHT
increased the serum cholesterol and the concentration of cholesterol
was directly proportional to the BHT level. There was also a
significant increase in the concentration of adrenal cholesterol. BHT
produced no significant changes in the concentration of total or
percentage esterified liver cholesterol, total liver lipid or
concentration of total polyunsaturated fatty acids in the liver
(Johnson & Hewgill, 1961).
Rats fed diets supplemented with 20% lard, and containing 0, 0.2,
0.3, 0.4 or 0.5% (dry weight) BHT for 6 weeks, showed an increase in
serum cholesterol that was directly related to the level of dietary
BHT. BHT increased the relative weight of the male adrenal and also
caused a significantly greater decrease in growth rate of male as
compared to the female. Increased liver weight in test animals was
paralleled by increased absolute lipid content of the liver (Johnson &
In another study, rats were maintained on diets containing 0.5%
dietary BHT in the presence or absence of a 20% lard supplement. BHT
increased the basic metabolic rate, the concentration of body
cholesterol and the rate of synthesis of body and liver cholesterol,
and reduced the total fatty acid content of the body, irrespective of
the presence or absence of dietary lard. In the animals fed BHT
without lard, BHT increased the rate of synthesis and turnover of body
and liver fatty acids and reduced the growth rate. These effect
occurred to a greater extent in animals fed BHT with lard (Johnson &
Groups of 8 young rats were fed diets containing 19.9% casein and
0, 0.02 or 0.2% BHT for 8 weeks. The experiment was repeated with
16.6% casein in the diet of further groups for 4 weeks and again with
9.6% casein (and no added choline) for 7 weeks. In all three instances
BHT caused stimulation of growth and improved protein efficiency. The
nitrogen content of the liver was, however, greatly reduced in
BHT-treated animals, except when the level of BHT was reduced to
0.02%. Recovery of hepatic protein after fasting (details not given)
was also impaired in rats on 0.2% BHT. Liver lipid content was
increased at 0.2%, but not at 0.02% BHT. A dietary level of 0.2% BHT
also increased the adrenal weight and ascorbic acid content, although
if recalculated on the basis of weight of gland, there was no
significant difference. The increase in adrenal ascorbic acid was
interpreted as indicating a stress imposed on the organism by BHT
(Sporn & Schöbesch, 1961).
Groups of 20 male and 20 female rats fed 1% BHT in the diet for
10 weeks showed recovery both in liver to body weight ratios and in
morphological appearance of the liver cells within a few weeks after
restoring the animals to a normal diet (Goater et al., 1964).
Groups of 48 weanling rats (24/sex) were given diets containing 0
or 0.1% BHT for periods of up to 16 weeks. Measurements of growth
rate, food consumption, weight and micropathological examination of
organs at autopsy revealed no difference between treated and control
groups. However, increase in relative liver weight and in the weight
of the adrenals was produced without histopathological evidence of
damage. Biochemical measurements and histochemical assessments of
liver glucose phosphatase and glucose 6-phosphate dehydrogenase
activities revealed no difference from the control group
(Gaunt et al., 1965a).
Groups of rats (16/sex) were fed diets containing 20% fat and BHT
levels of 0, 0, 0.03, 0.1 or 0.3% BHT for 10 weeks. No definite effect
on body weight was observed at any level in females and there was only
a slight depression in males at the 0.3% level. There was no
significant effect on blood cholesterol level in either sex after
feeding BHT at any of the levels. Four males at the 0.3% and two at
the 0.1% level died during the experiment. Two deaths occurred among
females at 0.3%. Only one male rat died in both control groups
(Frawley et al., 1965b).
In order to determine the MTD for BHT in rats, groups of F344
rats (5/sex) were given diets containing 0, 6200, 12 500, 25 000 or
50 000 mg BHT/kg diet for 7 weeks. Body weights were determined twice
weekly. Gross necropsy was performed on all animals in the study. All
of the male and female rats in the 50 000 mg/kg group died before the
end of the study. With the exception of one male in the 12 500 mg/kg
group, all of the animals in the other treatment groups and control
groups survived to the end of the study. Body weights at week 7 of the
study showed a dose-related decrement, with animals in the 25000 mg/kg
group weighing only 38% to 44% of control values. At dietary levels of
12 500 mg/kg, there was a slight increase in haematopoiesis in both
sexes (NCI, 1979).
Mild to moderately severe diarrhoea was induced in a group of
4 dogs fed BHT at doses of 1.4-4.7 g/kg bw every 2 to 4 days for
4 weeks. Postmortem examination revealed no significant gross
pathological changes. No signs of intoxication and no gross or
histopathological changes were observed in dogs fed doses of
0.17-0.94 g/kg bw, 5 days/week for a 12-month period (Deichmann
et al., 1955).
Groups of 3 infant or juvenile monkeys (Macaca mulatta)
received BHT at doses of 0, 50 or 500 mg/kg bw/day for 4 weeks. Blood
analysis (complete cell count, serum sodium and potassium, bilirubin,
cholesterol and GOT) was carried out weekly, as was a complete
urinalysis. Liver biopsies were taken from the juvenile monkey at 2
weeks, following a 24-h fast. At the end of the test period, all
animals were fasted 24 h and sacrificed. Tissues from all major organs
were prepared for light and electron microscopy. Liver tissue was
also analyzed for protein, RNA and cytochrome P-450. Microsomal
preparations prepared from the livers were used to measure
nitroanisole demethylase and glucose-6-phosphatase activity. Urine and
blood values of test and control animals were similar. Histological
evaluation of all organs other than the liver from either infant or
juvenile monkeys did not indicate any compound-related changes. Test
animals receiving BHT showed hepatocytomegaly and enlargement of
hepatic cell nuclei. The hepatocytes of treated animals showed
moderate proliferation of the endoplasmic reticulum. Lipid droplets
were also prominent in cytoplasm of these hepatic cells. There was
fragmentation of the nucleolus in 15% of the hepatic cells in the test
animals in the high-dose group. DNA, RNA and cytochrome P-450 levels
in the liver of test and control animals were similar. BHT-treated
juveniles showed an increase in nitroanisole demethylase activity
which increased with time. The enzyme activity was unaffected in
infant monkeys. Glucose-6-phosphatase activity declined in juvenile
monkeys but was unchanged in infant monkeys (Allen & Engblom, 1972).
2.2.3 Long-term toxicity/carcinogenicity studies
Groups of 60 FAF male mice were maintained on semi-synthetic
diets containing 0, 0.25 or 0.5% BHT. The mean life-span of the test
animals was significantly greater than controls, being 17.0 ± 5.0 and
20.9 ± 4.7 months respectively for the 0.25% and 0.5% BHT, as compared
to 14.5 ± 4.6 months for controls (Harman, 1968).
A group of 18, 8-week old male BALB/C mice fed BHT at a level of
0.75% for a period of 12 months, developed marked hyperplasia of the
hepatic bile ducts with an associated subacute cholangitis (Clapp
et al., 1973).
Eleven mice (BALB/C strain) were maintained on a diet containing
0.75% BHT for a period of 16 months. The incidence of lung tumours in
the test group was 63.6%, compared with 24% in controls (Clapp
et al., 1974). However, a repeat of this study using a larger group
of test animals, showed that BHT had no effect on the incidence of
lung tumours in either sex (Clapp et al., 1975).
Groups of 48 mice (CFI strain) equally divided by sex were
maintained on diets containing 1000 mg/kg BHT. At week 4, one group
was then fed a diet containing 2500 mg/kg BHT, and at week 8, another
group was fed a diet containing 5000 mg/kg BHT. The animals were
maintained on these diets until 100 weeks of age. There was no
statistically significant reduction in survival of animals on the BHT
diet, although survival was poorer in males at the high-dose level
during the last quarter of the study. Animals dying or sacrificed
during the course of the study showed greater centrilobular cytomegaly
and karyomegaly than controls. Bile duct hyperplasia was only observed
in 3/141 test animals. There was no significant difference in the
incidence of malignant tumours in the high-dose group and control.
However, there was an increased incidence of lung neoplasia in treated
mice (75%, 74%, 53% and 47% in the 5000, 2500, 1000 mg/kg and control
groups, respectively). There were no morphological features to
distinguish the lung tumours in treated mice from those in controls.
There was also an apparent increase in benign ovarian tumours in
BHT-treated female mice, since none were observed in control animals
(Brooks et al., 1976).
BHT was administered in the diet at levels of 0, 3000, or
6000 mg/kg to groups of 20 (control) or 50 (treated) male and female
B6C3F1 mice for 107108 weeks. The mice were observed twice daily for
signs of ill-health. Physical examinations were performed each month
and body weights were recorded at least once a month. Gross and
microscopic examination of 28 major organs, tissues and gross lesions
including the liver, thyroid and forestomach, was performed on all
animals at the end of the study and all animals dying on test where
possible. Peripheral blood smears were made for all animals where
possible. The body weights of treated male and female mice were lower
than the control mice throughout the study [numerical data not
provided]. The magnitude of the body-weight decrements was
dose-related. Administration of BHT in the diet resulted in similar or
improved survival in the treated groups compared with controls. At
termination, survival in male mice was 60%, 86% and 92% and in females
85%, 82% and 90%, for the control, low-and high-dose groups,
respectively. There was a marked dose-related increase in the
incidence of hepatocytomegaly and non-neoplastic lesions of the liver
(peliosis, hepatocellular degeneration/necrosis and cytoplasmic
vacuolation) in males but not in females. The incidence of
hepatocellular adenoma or carcinoma was not significantly increased in
either treated male or female mice, although there was a small
increase in the incidence of combined adenomas and carcinomas in the
treated females (1/20, 4/46 and 5/49 for the control, low- and
high-dose females, respectively) which was not statistically
significant. The historical control incidence for hepatocellular
neoplasms was not provided. The incidence of alveolar/bronchiolar
carcinomas or adenomas in female mice was significantly higher than
controls (5%) in the low dose (35%), but not the high dose (14%). The
historical control incidence was 4.7% for alveolar/bronchiolar
adenomas or carcinomas. Chronic ingestion of BHT in the diet was
related to a significant reduction in the incidence of sarcomas of
multiple organs in female mice. Four adenomas of the eye/lacrimal
gland were observed in high-dose males (8%) and in 2 low-dose females
but not in corresponding controls. The historical incidence of this
tumour in male mice was 1.2%. Since the lacrimal gland was only
examined microscopically in animals with grossly apparent lesions, the
report states that the lacrimal gland tumours could not be clearly
related to BHT administration (NCI, 1979).
Groups of B6C3F1 mice (100/sex), were fed diets containing 0,
200, 1000 or 5000 mg/kg BHT for 96 weeks, followed by a basal diet for
8 weeks. At the end of the test period the surviving animals were
killed. A complete autopsy was carried out, and the principal organs
and tissues were examined microscopically. Mice that died during the
course of the study were also autopsied. In addition, terminal blood
samples were collected for haematological examination and serum
clinical biochemistry. Urine samples were also examined. During the
course of the study, food consumption was similar for test and control
groups. Body weights of females in the 1000 and 5000 mg/kg groups were
lower than controls, as was the body weight of males in the 5000 mg/kg
group. There were minor changes in the absolute weight of some organs
in the high-dose groups (salivary glands, heart and kidney). In males,
the serum GOT and GPT levels in the 5000 mg/kg group were higher than
controls. No other compound-related effects were observed in the
haematological, serum and urine analysis. Neoplastic lesions were
reported in both test and control animals. The tumours that occurred
with greatest frequency were adenomas of the lungs, hyperplastic
nodules and hepatocellular carcinomas of the liver and malignant
lymphomas. However, there was no statistically significant difference
between the BHT-treated and control groups for the incidence of any
type of tumour (Shirai et al., 1982).
BHT was administered in the diet at concentrations of 0, 1% or 2%
to groups of B6C3F1 mice (50/sex) for 104 weeks. After the treatment
period, all the surviving mice were given basal diet for an additional
16 weeks. Treated animals underwent a 16-week recovery period prior to
pathological examination. Mean body weights of the treated male and
female mice were lower than those of controls. The body-weight
decrements were dose-related in both sexes and were more marked in
female mice. Treatment with BHT was found to improve survival in a
dose-related manner in both males and females. At the end of treatment
(104 weeks), the percent survival for male/female mice was 40%/58%
(control), 64%/81% (1% diet) and 74%/89% (2% diet). In male mice
administered BHT, there was a statistically significant increase in
the incidence of either a hepatocellular adenoma (19%, 38% and 53% in
control, low- and high-dose groups, respectively) or a focus of
hepatocellular alteration, showing a clear dose-response relationship.
No increases in the number of female mice with hepatocellular adenomas
or foci of altered hepatocytes were noted. The incidence of male mice
with other tumours and the incidence of female mice with any
tumour were not significantly increased as a consequence of BHT
administration. There was a dose-related tendency to lower incidence
of lymphoma and leukemia in both males and females (Inai et al.,
Groups of rats (15/sex) given diets containing 1% lard and
0.2, 0.5 or 0.8% BHT for 24 months showed no specific signs of
intoxication, and micropathological studies were negative. For the
group given a diet containing 0.5% BHT, the BHT was dissolved in lard
and then heated for 30 minutes at 150°C before incorporation in the
diet. There were no effects on weight gain or blood constituents and
micropathological studies of the main organs were negative. The
feeding of 0.8% BHT was followed in both male and female rats by a
subnormal weight gain and by an increase in the weight of the brain
and liver and some other organs in relation to body weight.
Micropathological studies were negative in this group also. BHT had no
specific effect on the number of erythrocytes and leucocytes, or on
the concentration of haemoglobin in the peripheral blood. A number of
rats of both sexes died during this experiment, but the fatalities
were not treatment-related. Micropathological studies supported this
observation. At 0.5%, BHT had no effect on the rat reproductive cycle,
the histology of the spleen, kidney, liver and skin, or on the weight
of the heart, spleen or kidney. There was no significant increase in
mortality of rats fed a diet containing 0.1% BHT and 10% hydrogenated
coconut oil for a period of two years (Deichmann et al., 1955).
Groups of JCL strain rats (20/sex/group), reared under a barrier
system and 4 weeks of age at the start of the study, received BHT at
0, 0.005, 0.062 or 0.32% in the diet. Of each group of 40, 15 received
compound for a "lifetime", 10 for 24 months, and 5 each for 3, 6 or 12
months. At the interim and final kills, liver, kidney, heart, spleen,
thyroid and caecum weight were determined as were haematology, serum
biochemistry, urinalysis, and histological investigation of the
tissues. At 24 months, heart, liver, kidney, spleen, pituitary,
thyroid, adrenal, testes, prostate and brain were weighed,
haematological and biochemical measurements conducted, and
histopathology done. There was an increase in liver weight, serum
cholesterol, serum K+ and histological changes in liver and kidney
at the 0.32% dietary level. There was no change in quantity of food
intake, body-weight gain, mortality during feeding or mean life span
and no finding suspicious of tumour induction. There was no indication
of a dose-related trend in tumour prevalence in either 24-month or
"lifetime" groups. The tumours found were said to be typical of those
described in aged rats. It is to be noted that the number of surviving
rats was small and that tumour data included both lifetime groups and
animals dead or sacrificed moribund during the 6, 12 and 24-month
feeding. The available data do not list the number of each of the
individual tissues examined, although the number of rats is listed.
The data show a tendency for a decreased number of tumours per rat at
higher BHT levels (Hiraga, 1978).
Groups of Fischer 344 rats (50/sex) received 3000 mg/kg or
6000 mg/ kg BHT in the diet for 105 weeks. The compound was mixed with
autoclaved lab meal containing 4% fat. A control group of 20
animals/sex received lab meal only. The animals were observed twice
daily for signs of ill-health. Physical examinations were performed
each month and body weights were recorded at least once a month. Gross
and microscopic examination of 28 major organs, tissues and gross
lesions including the liver, kidney, thyroid and forestomach, were
performed on all animals at the end of the study and all animals dying
on test where possible. Peripheral blood smears were made for all
animals where possible. There was a dose-related decrease in body
weights of treated male and female rats throughout the study. There
was no significant effect of BHT on mortality and no difference in the
incidence of various neoplasms between treated and control groups. The
incidence of adenomas of the pituitary was significantly reduced in
female rats with BHT administration. The incidence of focal alveolar
histiocytosis was elevated in treated male and female rats in a
dose-related manner compared with controls. The effect was more
pronounced in females than in males (NCI, 1979).
Groups of 7-week old Wistar rats (57/sex/group) were maintained
on diets containing 0.25 or 1% of BHT for 104 weeks. Control groups
consisted of 36 rats/sex. At the end of the test period, the surviving
animals were killed and a complete autopsy was carried out and the
weights of liver, spleen and kidneys were taken. The principal organs
and tissues were examined microscopically. Terminal blood samples were
collected for haematological examination and serum clinical
biochemistry. Survival in test groups was between 40% and 68%. A
significant increase in the mortality of the high-dose males was noted
after week 96 of the study. Food intake was similar for test and
control animals, but body-weight gain was significantly reduced in
high-dose males up to week 60 and in high-dose females for most of the
study. Increases in the mean absolute and relative liver weights were
observed in all treated animals, and decreases in the absolute and
relative spleen weights were observed in the treated females.
Dose-related changes in serum triglyceride (reduction) and GGT
(increase) in treated males and in total blood cholesterol (increase)
in treated females were noted. No significant morphological changes
were observed in the liver which were attributable to BHT treatment. A
variety of tumours were noted on histopathological examination at the
end of the study, with no dose-related response in either type of
tumour or total number as compared to controls. The incidence of
hyperplastic nodules in the liver and of pancreatic carcinomas in
female rats and of pituitary adenomas and adeno-carcinomas in both
sexes of test animals was higher than in controls. However, with the
exception of the incidence of pituitary adenomas in the low-dose
females, these differences were not significantly different from
controls. Since this effect was not dose-related, it was concluded
that BHT, under the conditions of this test. was not carcinogenic
(Shibata et al., 1979; Hirose et al., 1981).
Groups of 60, 40, 40, or 60 Wistar rats of each sex (F0
generation) were fed BHT in the diet at doses of 0, 25, 100, or
500 mg/kg bw/day, respectively. The F0 rats were mated after 13
weeks of dosing. The F1 groups consisted of 100, 80, 80, and 100
F1 rats, respectively, of each sex from the offspring from each
group. Because of an adverse effect on the kidney in the parents, the
concentration of BHT in the highest dose group was lowered to
250 mg/kg bw/day in the F1 generation. The study was terminated when
rats in the F1 generation were 144 weeks of age. Parameters studied
were food consumption (weekly), body weight, appearance, and
mortality. Autopsy and complete histopathological examinations were
performed on all animals dying during the study, or sacrificed
in extremis or at termination.
All animals consuming BHT experienced a dose-related increase in
survival. In both sexes differences (p <0.001) in longevity were
seen. The average body weights of the F1 pups at birth in the mid-
and high-dose groups were slightly lower than those in the control
group. Body weights of all dosed animals from weaning through the
entire experiment were lower than those of control animals. In the
low-, mid-, and high-dose groups, the reductions in body weight were
for males/females 7%/5%, 11%/10%, and 21%/16%. Food intake was
comparable for all groups. Clinical appearance and behaviour were
reported to be normal for all animals. The high-dose males voided a
slightly reddish urine. Haematological parameters were reported to be
unchanged by BHT treatment, but no data were given. Serum triglycerides
were reduced in both sexes and cholesterol was somewhat elevated in
Histological studies indicated an increase in hepatocellular
carcinomas in male rats and an increase in hepatocellular adenomas in
both male and female rats. Most liver tumours were found during
terminal sacrifice at 141-144 weeks. One hepatocellular carcinoma was
found in a control male at 117 weeks and one in a high-dose male at
132 weeks. The remainder of the carcinomas occurred at terminal
sacrifice. The first adenoma was noted in a high-dose male at 115
weeks. Tables 3 and 4 summarize the data on mortality and the
appearance of adenomas and carcinomas of the liver. Data on mortality
and tumour incidence in different groups were analyzed using the
procedure of Peto et al. (1980). The dose-related increases in the
number of hepatocellular adenomas were statistically significant
(at p < 0.05) in male F1 rats, when all groups were tested for
heterogenicity or analysis of trend. The increase in hepatocellular
adenomas and carcinomas in treated female F1 rats was statistically
significant only for adenomas (at p <0.05) in the analysis for trend.
Reports on the spontaneous incidence of hepatocellular neoplasms in
Wistar rats from the laboratory performing this study, as well as
other European laboratories, indicated that it was usually less than
3% (Solleveld et al., 1984; Deerberg et al., 1980; Olsen et al.,
1984). The median life-span for animals in these studies ranged from
28-36 months for males and 28-33 months for females. Other sites
reported to have a slight but not statistically significant increase
in neoplastic lesions were as follows: thyroid, pancreas, ovary,
uterus, thymus, reticuloendothelium system, and mammary gland.
Non-neoplastic lesions occurred incidentally and showed no
relationship to BHT treatment, with the exception of lesions of the
liver, which showed a dose-related increased incidence of bile duct
proliferation and cysts in males, and focal cellular enlargement in
females. At the highest dose (250 mg/kg bw/day), there was no adverse
effect on the kidney (Olsen et al., 1986).
A long-term study was initiated in order to investigate the role
of hepatic changes in the development of hepatocellular carcinomas in
rats following in utero/lifetime exposure to BHT. The dosing regimen
of the study and strain of rat used were similar to those in the
two-generation study conducted by Olsen et al. (1986). Groups of
6 male and 48 female Wistar rats, aged 13 weeks and 9 weeks,
respectively, were fed BHT in the diet at doses of 0, 25, 100 or
500 mg/kg bw/day for 3 weeks prior to mating (13 weeks in Olsen
study). The rats were then mated on a 1:8 ratio for up to 21 days.
When pregnancy had been established by abdominal palpation, dams were
removed to individual cages. On day 20 of gestation, 5 pregnant rats
were sacrificed for assessment of body and liver weights and liver
histopathology. The pups were delivered by Caesarian section and
retained for assessment of a number of parameters. The remaining
females (20 dams in the control and high-dose groups; 24 dams in the
low- and mid-dose groups) were allowed to deliver normally. On day 6
post-partum, litters were either culled or augmented to comprise 8
pups, at the same time maximizing the number of robust males in each
litter. At weaning (3 weeks), 4 pups from each of 5 litters per group
were selected randomly, maximizing the numbers of males, for
assessment of a number of parameters. The male pups from the remaining
litters (approximately 60/group) were selected to continue in the
study and were placed in one of 4 groups corresponding to the diets
fed to their parents, with the exception that the high dose was
reduced to 250 mg/kg bw/day as in the Olsen study. Interim kills were
conducted at 1, 6, 11, or 16 months. The study was terminated 22
months after the F1 male rats were placed on test diets. All animals
were observed daily throughout the study for clinical or behavioural
signs of toxicity. F0 females were palpated from pregnancy to
weaning and F1 males were palpated from 15 months to termination.
Body weights were recorded approximately every 2 weeks and food
consumption monitored every few days. Animals dying during the study
or at scheduled sacrifices were subjected to gross necropsy. At each
of the scheduled sacrifices the following parameters were measured in
all groups of F1 fetuses and weanlings and F1 male rats: body and
liver weights; hepatic enzyme activities for glucose-6-phosphatase,
epoxide hydrolase, glutathione-S-transferase, ethoxyresorufin
O-deethylase and pentoxyresorufin O-depentylase; hepatic content of
total cytochrome P-450, total glutathione, total microsomal and
cytosolic protein; and histopathological changes in the liver. In
addition, immunochemical staining of liver sections for cytochrome
P-450 1A and 2B and epoxide hydrolase was performed in the control and
high-dose groups at all scheduled sacrifices. Cellular proliferation
in the liver was measured in 5 animals per dose group at 4 weeks and
all subsequent sacrifices using pulse labelling techniques with
bromodeoxyuridine (only control and high-dose results were reported).
At the 11, 16 and 22-month sacrifices, a number of parameters in
addition to those listed above were monitored: histopathological
changes in the adrenal, kidney and thyroid; assessment of distribution
of hepatic glucose-6-phosphatase and gamma-glutamyl transferase by
histochemical staining; and serum thyroxine concentration (presented
for 16 and 22 months only).
In the first 5 weeks of BHT administration, a reduction in
body-weight gain was noted in the high-dose males. This trend started
prior to BHT administration and continued after BHT administration was
initiated. Body-weight gain in all other treatment groups was similar
to that in controls. No treatment-related effects on the health of the
animals were noted. During pregnancy and lactation, there was no
difference in food consumption between treated and control female
rats, and body weights of the dams were similar at weaning. At the
sacrifice on day 20 of gestation, both absolute and relative liver
weights of the dams were increased in a dose-related manner,
statistically significant at the high dose. The body weights of the
females, both including and excluding their litters, were similar in
all groups. Histopathological examination of the liver revealed mild
enlargement of centrilobular hepatocytes and eosinophilia in 4/5
high-dose (500 mg/kg bw/day) animals, and 1/5 low-dose (25 mg/kg
bw/day) animals, consistent with induction of mixed function oxidase
activity. A decrease in the mitotic index of hepatocytes from dams
receiving 100 and 500 mg/kg bw/day was noted; the significance of this
result was unclear.
Table 3. Mortality (and combined adenomas and carcinomas of the liver) in F1 rats (Olsen et al., 1986)
(mg/kg number Number of deaths during weeksa
bw/day) of rats
0-90 91-104 105-113 114-118 119-126 127-132 133-140 141-144 Total
0 100 20 10 13 (1)/8 11 10 (1)/12 16 (2)/100
25 80 8 11 6 3 (1)/13 11 8 20 (1)/80
100 90 8 12 3 2 10 7 (2)/11 (4)/27 (6)/80
250 99 7 7 6 (1)/4 (2)/8 (2)/13 (1)/10 (20)/44 (26)/99
0 100 16 15 18 (2)/8 11 7 8 17 (2)/100
25 79 10 9 4 6 13 (1)/10 (1)/8 (1)/19 (3)/79
100 80 5 17 5 5 (1)/7 (1)/9 (1)/11 (3)/21 (6)/80
250 99 9 5 11 12 8 5 (2)/10 (12)/39 (14)/99
a Figures in parenthesis are combined adenomas and carcinomas occurring during that period.
Table 4. Incidence of hepatocellular nodular hyperplasia, adenomas,
and carcinomas (Olsen et al., 1986)
BHT Effective No. Nodular
(mg/kg bw/day) of rats hyperplasia Adenomas Carcinomas
0 100 2 1 1
25 80 0 1 0
100 90 2 5 1
250 99 2 18a 8b
0 100 2 2 0
25 79 0 3 0
100 80 4 6 0
250 99 5 12c 2d
a Over-all test for heterogeneity, p< 0.001, chi-square
18.17, 3 df.
Test lot trend, p< 0.001, chi-square = 17.97, 1 df.
b Over-all test for heterogeneity, p < 0,05. chi-square
11.12, 3 df.
Test for trend, p< 0.01, chi-square = 9.40. 1 df.
c Over-all test for heterogeneity, not significant, chi-square =
5.20, 3 df.
Test for trend, p< 0.05, chi-square = 4.99, 1 df
d Over-all test for heterogeneity, not significant, chi-square =
2.87, 3 df.
Test for trend, not significant, chi-square = 2.59, 1 df.
Reproductive parameters were as follows: mating index was in the
range 54-65%; gestation index, 93-96%; viability index (birth to
day 6), 93-96%. No effect of treatment was evident in these
parameters. The absolute numbers of resorptions/dam were also similar
in treated and control groups. There was a slight decrease in the
numbers of pups/litter in the low- and high-dose groups, but a
dose-related trend was not evident. Body weights of the pups from the
high-dose group were significantly lower than controls at birth (10%),
and at days 6 (12%) and 21 (21%) of lactation. Mortality of the pups
remaining after culling, to day 21 of lactation was 2%, 8%, 12% and
15%, in order of ascending dose. Since the culling of pups at day 6
was non-random, these data could not be used for an unbiased
evaluation of reproductive function in BHT-treated animals.
Body weights of the F1 males which continued in the study were
lower in the high-dose group, compared with controls, throughout the
22-month treatment period. During the first year of the study, the
difference was in the range of 10-20%. Lower body weights which
differed from controls by about 5% were also noted in the mid-dose
animals during the first half of the treatment period. No adverse
reactions to treatment or effects on food consumption were noted.
Subjective assessment of the coats of rats indicated that there was
less age-related deterioration in the 100 and 250 mg/kg bw/day groups
than in controls. At the scheduled sacrifices, consistent dose-related
increases in relative, but not absolute liver weights were observed,
which were statistically significant at the high dose.
A dose-related incidence of enlargement and eosinophilia of the
centrilobular hepatocytes was observed consistently at the scheduled
sacrifices, starting at 6 months. This was indicative of proliferation
of the SER, consistent with an induction of mixed function oxidases.
Immunohistochemical staining of liver sections from control and
high-dose rats revealed a marked increase in hepatocellular content
and distribution of cytochrome P-450 2B with BHT treatment which
persisted throughout the study. No such alteration was seen in the
staining patterns for cytochrome P-450 1A or epoxide hydrolase.
Histochemical staining revealed a marked induction of gamma-glutamyl
trans-peptidase activity in the periportal hepatocytes of nearly all
of the high-dose rats, starting at 11 months of treatment. This effect
was noted to a lesser extent in the mid-dose group. The distribution
of glucose-6-phosphatase activity in the treated rats was normal.
There was no evidence of treatment-related bile duct hyperplasia or
inflammatory cell infiltrate in the portal tract. Some rats with
altered hepatocellular foci (AHF) were noted in treated groups at 11
months and in all groups at 16 and 22 months. There was no treatment
relationship in the incidence of specific types of foci. At 22 months,
there was a higher incidence of eosinophilic and basophilic foci in
the high-dose group. Histochemical staining of liver sections revealed
a small number of high-dose animals with glucose-6-phosphatase-
deficient AHF which was statistically significant. No treatment-
related increase was noted in the incidence of AHF staining positive
for GGT At 22 months, there was also a significant increase in the
number of rats with hepatic nodules in the high-dose group (6/19
animals compared with none in the other groups).
No increases in the rate of hepatocellular proliferation were
detected as a result of BHT administration at any point in the study
commencing from 4 weeks post-weaning. It is of interest to note that
Clayson et al. (1993) observed an increase in hepatocellular
proliferation between 2 and 4 days after initiation of treatment of
male Wistar rats with 0.5% dietary BHT. Such a transient increase
would be difficult to detect with the widely spaced sampling times
used in this study.
A number of hepatic enzyme activities and other parameters
related to xenobiotic metabolism were altered as a result of BHT
treatment. Total cytochrome P-450 content was increased by 30-60% in
the high-dose animals starting at 21 days of age. Dose-related
increases were noted in epoxide hydrolase, glutathione-S-transferase
and pentoxyresorufin O-depentylase (PROD) activities, starting at 21
days of age, which were statistically significant in the mid- and
high-dose groups. The increases in PROD activity were very large,
10-25 fold in the mid-dose, and 20-80 fold in the high-dose groups.
Modest dose-related increases in ethoxyresomfin O-deethylase
activities were noted which were not statistically different from
controls. No effects on hepatic glutathione levels or glucose
6-phosphatase activity were noted throughout the study.
Histopathological examination of the kidneys revealed a reduction
in severity of chronic progressive nephropathy which affected the rats
in all groups from 11 months. No effects on the adrenal were noted,
although in a nearly identical, but invalidated study conducted in the
same laboratory (Robens Institute, 1989) cytomegaly of cells of the
zona fasciculata was observed in the mid- and high-dose groups at
weaning and at 4 weeks post-weaning, but not at subsequent time
points. In the present study, histopathology of the adrenal was
conducted starting at 11 months post-weaning. Evidence of thyroid
hyper-activity, characterized by reduction of follicular size, absence
or reduction of colloid, irregularities in the follicular outline,
hyperaemia and increase in the number of follicular cells was noted
starting at 11 months in both the mid-dose group (mild changes
affecting 75-82% of the rats) and the high-dose group (marked changes
affecting 100% of the rats). This effect was probably secondary to the
effects of BHT on the liver. Serum thyroxine levels in treated rats
did not differ from controls.
The demonstrated effects on hepatic enzyme induction and
consequent thyroid hyperactivity in the mid- and high-dose groups
together with the tumour data from the Olsen study suggested a NOEL of
25 mg/kg bw/day (Price, 1994).
BHT was added to the diet of male F344 rats for periods of up to
110 weeks. In the first experiment, a group of 36 male F344 rats
received basal NIH-07 diet only, while groups of 21 rats received
diets containing 300, 1000, 3000 or 6000 mg/kg BHT. Four animals were
randomly selected from each group for measurement of altered
hepatocellular foci at 12, 36, 48 or 76 weeks.
The remaining animals were sacrificed at 76 weeks. In a second
experiment, groups of 27 male F344 rats were fed basal diet, or diets
containing 12 000 mg/kg BHT or 12 000 mg/kg BHA for 110 weeks, at
which time all surviving animals were sacrificed. In both experiments,
body weights were recorded every four weeks. Gross necropsy was
performed on all animals. The livers were weighed and submitted for
histopathology along with tumours and gross lesions from other organs.
All the rats in experiment 1 survived the entire treatment period
(76 weeks). In experiment 2, the survival of rats in control and
treated groups started to decline after 84 weeks, but no
treatment-related trend was evident. At the end of the treatment
periods, rats fed 3000, 6000 or 12000 mg/kg BHT had significantly
lower body weights compared with respective controls. The body-weight
decrement for these three groups was approximately 10%. Rats fed
6000 mg/kg BHT for 76 weeks had significantly increased absolute and
relative liver weights compared with controls. In rats fed 12000 mg/kg
BHT for 110 weeks, the absolute liver weights were significantly
decreased and relative liver weights were comparable to controls. The
density of iron storage deficient hepatocellular foci in the one
affected rat per group was slightly but not significantly increased in
BHT-treated animals at 48 and 76 weeks; the incidence and size of foci
were slightly decreased at 110 weeks in rats receiving 12000 mg/kg
BHT. No hepatocellular carcinomas were detected in any of the groups.
Hepatocellular adenomas were detected in all groups, including
controls, with no treatment-related trend in incidence. There was also
no treatment-related effect of BHT on the incidence of grossly
observable tumours in specific organs (Williams et al., 1990a).
2.2.4 Reproductive toxicity studies
Diets containing 0.1 or 0.5% BHT together with two dietary levels
of lard (10 or 20%) were given to mice. The 05% level of BHT produced
slight but significant reduction in mean pup weight and total litter
weight at 12 days of age. The 0.1% level of BHT had no such effect.
Out of 7754 mice born throughout the reproductive life span of the
mothers, none showed anophthalmia, although 12 out of the 144 mothers
were selected from an established anophthalmic strain (Johnson, 1965).
The chronic ingestion of 05% BHT by pregnant mice and their
offspring resulted in a variety of behavioural changes. Compared to
controls, BHA-treated pregnant mice showed increased exploration,
decreased sleeping, decreased self-grooming, slower learning, and a
decreased orientation reflex. BHT-treated offspring showed decreased
sleeping, increased social and isolation-induced aggression, and a
severe deficit in learning (Stokes & Scudder, 1974).
A 3-generation study was performed in mice for the evaluation of
reproductive, developmental, and behavioural effects. Groups of 10
Crj:CD-1 mice/sex received BHT in the diet at concentrations of 0,
0.015%, 0.045%, 0.135%, or 0.405% (equivalent to 0, 20, 70, 200 or
610 mg/kg bw/day) starting at 5 weeks of age. At 9 weeks of age, the
mice were mated on a 1:1 basis for a period of 5 days. The pups
resulting from these matings were weaned at 4 weeks of age and 10
mice/sex/group were randomly selected to continue in the study. Males
and females were mated at 9 weeks as in the previous generation.
Reproductive parameters measured for each of the F1 and F2 groups
were: number of litters and pups, litter size and weight, sex ratio,
pup weights on lactation days 0, 4, 7, 14, and 21, and survival to day
21. Neurobehavioural parameters measured at various times during
the lactation period were: surface righting, negative geotaxis,
cliff avoidance, swimming behaviour and olfactory orientation.
Administration of BHT in the diet to mice adversely affected only
one of the measured reproductive parameters. Body-weight gain was
consistently reduced from day 7 to day 21 of lactation in the F1
high-dose pups, but no body weight differences were noted in the F2
pups compared with controls. In the F2 males, lower scores were
assigned to the treated groups for the 180° turn in the open field
trial but this effect was not apparent in the F2 female pups.
Consequently, no toxicologically significant effects of treatment were
apparent with BHT at the dietary concentrations tested in this study
(Tanaka et al., 1993).
Weanling rats (16/sex) were fed a diet containing 20% lard and 0,
300, 1000 or 3000 mg/kg BHT and mated at 100 days of age (79 days on
test). Ten days after weaning of the first litter, the animals were
again mated to produce a second litter. The offspring (16 females and
8 males) were mated at 100 days of age. Numerous function and clinical
tests including serum cholesterols and lipids were performed on the
parents and the first filial generation up to 28 weeks and gross and
microscopical examination at 42 weeks. At the 3000 mg/kg dietary
level, 10-20% reduction in growth rate of parents and offspring was
observed. A 20% elevation of serum cholesterol levels was observed
after 28 weeks, but no cholesterol elevation after 10 weeks. A 10-20%
increase in relative liver weight was also observed upon killing after
42 weeks on diet. All other observations at 3000 mg/kg and all
observations at 1000 mg/kg and 300 mg/kg were comparable with control.
All criteria of reproduction were normal. No teratogenic effects were
detected (Frawley et al., 1965b).
Similar results to those obtained with the parental and first
filial generations were also obtained with the second filial
generation. Examination of two litters obtained from the latter at 100
days of age revealed no effects except a reduction of mean body weight
at the 3000 mg/kg level. The offspring were examined for litter size,
mean body weight, occurrence of stillbirth, survival rate and gross
and microscopic pathology (Kennedy et al., 1966).
Breeding pairs of Sprague-Dawley rats (200-220 g) received Purina
chow supplemented with 0.125%, 0.25% or 0.5% BHT ad libitum
beginning from the week before mating and continuing in females
through lactation and weaning of the pups. Growth rates and survival
were adversely affected. Pre-weaning pups born of mothers at the
highest dose level weighed significantly less than controls at ages 7,
14 and 21 days. The total number of pups dying on study, born of dams
receiving 0.25 or 0.5% BHT, was significantly higher than controls.
Behavioural tests were conducted, consisting of righting reflex,
pivoting, cliff avoidance, startle response, swimming, open field,
running, wheel activity, roto-rod, active avoidance, position
discrimination and passive avoidance. For pre-weaning testing, no
differences were noted at the low- or mid-dose groups. At the
high-dose level, there was significant increase in surface righting
time, delayed forelimb swimming development and a trend to less
activity in open field tests. In post-weaning tests, males in the
0.25% BHT group showed an effect on passive avoidance, with more
partial re-entries into compartments where shocked. For all other
tests, there were no statistical differences, suggesting that BHT had
no effect on basic motor coordination, active avoidance acquisition,
or extinction performance (Brunner et al., 1978).
Groups of 46 rats, 6-week old (Wistar outbred, SPF) were fed
diets containing 0, or 0.5 to 0.9% BHT so that the dietary intake of
BHT was equivalent to 500 mg/kg bw/day during the course of the study.
At week 19, the F0 generation was mated. Twenty-four hours after
birth of F1 rats, the size of the litters was reduced to 8, and
half of the litters were cross-fostered. The body weight of parents
and offspring and the developmental events of offspring were
monitored during the course of the study, as well as the reproductive
performance of the F0 rats. Auditory and visual function and
locomotive coordination tests were carried out on tile F1
generation. The F1 animals were autopsied at day 25 of age, and a
histological examination made of the brains. Body weights and weight
gain of test animals were reduced when compared to controls, and this
persisted during gestation. The duration of pregnancy, average body
weight, and litter size were similar for test and control animals. The
average body weight and weight gain of the F1 offspring were
significantly reduced in pups nursed by dosed mothers. Pups exposed
in utero to BHT also showed a relatively slower development than
controls when fostered with non-dosed mothers. Pups exposed to BHT
in utero and/or mothers milk showed alterations in the behavioural
patterns examined as well as higher incidence in average number of
dead cells in the brain (Meyer & Hansen, 1980).
Detailed comments were submitted by the Chemical Manufacturers
Association (CMA) (1983) on studies of the effect of BHT on
reproduction and teratogenicity. The major comments were concerned
with the studies of Brunner et al. (1978) and Vorhees et al.
(1981) previously reviewed by JECFA in 1980 (Annex 1, reference 54) as
well as the study by Meyer & Hansen (1980).
In the case of the Brunner et al. and Vorhees et al. studies,
it was concluded that the study showed normal pup survival and
development in pups raised by dams on diets containing 0.125% BHT.
Normal post-weaning development was observed in pups raised by dams
on diets containing 0.25% BHT, although increased post-weaning
mortality occurred in pups raised by dams on the 0.25% and 0.5% diet;
developmental delays occurred in pups in the 0.5% group. In the case
of the Meyer and Hansen (1980) study, developmental delays were seen
in rats raised by dams on diets containing 0.5% BHT. At the 0.25% and
0.5% level, the effect may be due either to toxic effects of BHT on
the dam, or direct toxicity during lactation. A number of questions
were also raised about the design of the Brunner and Vorhees study.
These are: (i) the pup selection, in which all litters of fewer than 8
live pups were discarded; and (ii) the excess mortality was reported
in terms of pup count rather than affected litters. The data from this
study have been audited by the U.S. FDA (1983). It was concluded that
the raw data support the authors' observations of increased mortality
in the mid-dose and high-dose BHT offspring. However, excess mortality
occurred in a limited number of litters. For example, in the 0.5%
group, of the 60 deaths reported in 19 litters, 49 of the deaths
occurred in 5 litters; in the 0.25% group, of the 42 deaths, 21
occurred in 2 litters, and at the 0.125% level, of the 12 deaths, 11
occurred in 1 litter. It was also noted that in the high dose-group,
there was an increased number of litters with 8 pups or less, and no
litters larger than 12 pups. In the other dose groups, the litter size
was comparable to controls.
In the case of the Meyer & Hansen (1980) study, the CMA comments
noted that the level of BHT used in the study caused toxicity in the
dams, which appeared to affect the pups directly or indirectly.
Reports of teratogenicity studies and/or 1-generation reproductive
toxicity studies in several strains of mice and rats as well as a
3-generation reproductive toxicity study in rats were also submitted
in the comments to support a "no effect" level of 0.1% BHT in the
Groups of 60, 40, 40, or 60 Wistar rats of each sex, 7 weeks of
age, were fed a semi-synthetic diet containing BHT so that the dietary
intake was equivalent to 0, 25, 100, or 500 mg/kg bw/day, respectively.
After 13 weeks on the test diet the rats were mated.
Food consumption was similar in all groups. Male and female rats
in the high-dose group showed a significant decrease in body weight
which persisted throughout the study. Gestation rate was similar for
all test groups. The litter size and number of males per litter were
significantly lower in the 500 mg/kg bw/day group than in the
controls. Viability was similar in test groups and in the control
group during the lactation period. The average birth weight of the
pups in the 500 and 100 mg/kg bw/day groups was slightly lower than in
the controls. During the lactation period, BHT caused a significantly
lower dose-related body-weight gain (5%, 7%, and 41% lower body weight
for the 25, 100, and 500 mg/kg bw/day groups, respectively, as
compared to controls) (Olsen et al., 1986).
A study was initiated to determine the maximum dietary dose of
BHT tolerated by female rats exposed prior to and through pregnancy,
and by pups similarly exposed in utero and until weaning. Groups of
3 male and 16 female Wistar rats were administered BHT in the diet
corresponding to 0, 500, 750, or 1000 mg/kg bw/day for 3 weeks before
mating. At least 8 females per group were dosed during the pregnancy,
and until weaning (21 days after the delivery). After mating, the
males and the remaining females were autopsied. No effect of treatment
was seen on blood-clotting times in these animals. Food consumption of
treated females was considerably higher than controls from the fourth
week of the study onwards. No significant effect was seen on body
weight although a dose-related trend to reduction was apparent. No
effects were seen on general health except for fur discoloration in
Successful mating occurred less frequently in rats pretreated
with 1000 mg/kg bw/day of BHT than in the other groups. No major
differences were observed between the groups of pregnant females. The
weight gain in rats treated with the two highest doses appeared to be
inhibited in the last week of the pregnancy. There was no significant
difference between litter number or litter weight between pups born of
control or treated animals, although a dose-related trend towards
reduction in litter size was seen. No evidence of teratogenic effects
of BHT was provided.
Litter sizes were standardized to 8 pups if possible. At weaning,
the dams treated with 1000 mg/kg bw/day of BHT had lower body weights
and very little body fat was observed at autopsy. Pups from the dams
treated with the lowest BHT dose were markedly stunted in their
growth, but appeared healthy. Pups from dams treated with the two
highest doses were severely stunted, showed poor fur condition, and
were less active. It was noted that in BHT-treated animals, where the
litter size was less than 8, the average pup weight was generally
considerably greater. This implies that the reduced weight gains in
litters of normal size were associated with poor milk production
rather than BHT toxicity. Pups from two litters from each dose group
were maintained on control diet for 4 weeks after weaning. Pups born
to dams receiving BHT-containing diets remained of lower body weight
than control pups. Pups from the two highest dose groups continued to
show poor condition. Treatment with BHT caused a marked increase in
liver weight in all dams. The liver weights were almost 10% of the
body weights, the maximum degree of enlargement possible in rats. The
relative liver weights of pups from BHT treated dams were not
different from controls (Robens Institute, 1989).
When BHT was fed at a level of 0.125% for 34 weeks to a group of
10 pullets, no differences in fertility, hatchability of eggs or
health of chicks in comparison with a similar control group were
found. The eggs of the antioxidant-treated birds contained more
carotenoids and vitamin A than those of the controls (Shellenberger
et al., 1957).
A group of 6 adult female rhesus monkeys were maintained on a
test diet containing a mixture of BHT and BHA that provided an intake
equivalent to 50 mg BHT/kg bw/day and 50 mg BHA/kg bw/day. Another
group of 6 adult female rhesus monkeys were used as controls. The
monkeys were fed the diet for one year prior to breeding and then for
an additional year, including a 165-day gestation period. Haematologic
studies including haemoglobin, haematocrit, total and differential
WBC, cholesterol, Na+, K+, total protein, serum GPT, and GOT, were
carried out at monthly intervals. Body weights were taken at monthly
intervals. Records of menstrual cycles were maintained through the
After one year the females were bred to rhesus males not
receiving test diets. During pregnancy complete blood counts were done
on days 40, 80, 120 and 160 of gestation and on days 30 and 60
post-partum. A total of 5 infants were born to the experiment monkeys
and 6 to the control monkeys. Haematological evaluations were made on
infants of the test and control monkeys at days 1, 5, 15, 30 and 60,
and observations of the infants were continued through two years of
age. Two experimental and 2 control infants, 3 months of age, were
removed from their mothers for 1 month of psychological home cage
No clinical abnormalities were observed in parent or offspring
during the period of study. The gestation of test animals was free of
complications and normal infants were delivered. Adult females
continued to have normal infants. Infants born during the exposure
period remained healthy, with the exception of one infant that died
from unrelated causes. Home cage observations at the third month of
life did not reveal any behavioural abnormalities (Allen, 1976).
2.2.5 Special studies on teratogenicity
In a study on the embryotoxicity of BHT, 3 dosing schedules were
employed: single doses (1000 mg/kg bw) on a specific day of gestation,
repeated daily doses (750 mg/kg bw) from the time of mating throughout
pregnancy, and daily doses (250-500 mg/kg bw for mice and 500 and
700 mg/kg bw for rats) during a 7- to 10-week period before mating,
continuing through mating and gestation up to the time the animals
were killed. No significant embryotoxic effects were observed on
examination of the skeletal and soft tissues of the fully developed
fetuses as well as by other criteria. Reproduction and postnatal
development were also unaffected (Clegg, 1965).
2.2.6 Special studies on genotoxicity
The results of genotoxicity studies with BHT are summarized in
At a concentration as low as 10 µg/ml (optimal 50-100/µg/ml), BHT
exerted a strong inhibitory effect on cell-to-cell dye transfer
(lucifer yellow transfer) in cultures of SV-40-transformed Djungarian
hamster fibroblasts. The effect was reversible. BHT shared this effect
with a series of well known tumour promoters (Budunova et al.,
An extensive database of genotoxicity studies for BHT, including
those documented above, were reviewed in a paper by Bombard et al.
(1992). The authors concluded that the majority of evidence indicated
a lack of potential for BHT to induce point mutations, chromosomal
aberrations, or to interact with or damage DNA, and that BHT does not
represent a genotoxic risk to humans.
The ability of BHT and its metabolites to induce cleavage of
supercoiled plasmid DNA was studied in pUC18 by agarose gel
electrophoresis. Dose-related cleavage of DNA was noted with
BHT-quinone in the range 106-10-3M, and to a lesser extent using
higher doses of BHT-aldehyde and BHT-peroxyquinone. BHT, BHT- quinone
methide and other BHT metabolites had no effect on the plasmid DNA.
Free radical scavengers were effective against the effects of
BHT-quinone and -peroxyquinone, but not against BHT-aldehyde.
Formation of superoxide radical as measured by a reduction in
cytochrome c, was noted only with BHT-quinone (Nagai et al., 1993).
The addition of BHT (5 to 20 µg/plate) caused a two-fold increase
in the mutagenic potency of aflatoxin B1 using Salmonella
typhimurium strains TA98 and TA100, with and without activation
(Shelef & Chin, 1980).
The addition of 50-250 µg of BHT/plate inhibited 3,2'-dimethyl-
4-aminobiphenyl-induced mutagenicity in Salmonella typhimurium
strains TA98 and TA100 in the presence of rat liver S-9 fraction
(Reddy et al., 1983a).
Table 5. Results of genotoxicity assays with BHT
Test System Test Object Concentration of Results Reference
Ames test1 S. typhimurium 0.015-0.6% Negative Brusick 1975
Ames test1 S. typhimurium Negative Hageman et al.
TA97, TA102 1988
Ames test1 S. typhimurium 100-10 000 Negative Williams et al.
TA98, TA100 µg/plate 1990b
Ames test1 S. typhimurium 100-1000 µg/plate Negative Yoshida 1990
Ames test1 S. typhimurium 10 µg/plate Negative Detringer et al.
TA 98 1993
Host-mediated assay ICR Swiss mouse/ 30-1400 mg/kg - Negative SRI 1972
S. typhimurium acute
G46, TA1530 30-500 mg/kg -
Mammalian cell rat liver epithelial 60-90 µg/ml Negative Williams et al.
gene mutation cell (line 18), 1990b
Table 5 (cont'd)
Test System Test Object Concentration of Results Reference
Sex-linked recessive Drosophila 2.0 × 10-6 µg Negative2 Prasad &
lethal melanogaster Kamra 1974
Sex-linked Drosophila 5% diet Negative Brusick 1975
recessive lethal melanogaster
Clastogenic effects and chromosomal aberrations
Chromosomal human WI-38 2.5-250 µg/ml Positive2 SRI 1972
aberration assay (embryonic lung
Sex chromosome loss Drosophila 2.0 × 10-6 Negative2 Prasad &
melanogaster Kamra 1974
Micronucleus assay rat bone marrow 30, 90, 1400 Negative SRI 1972
mg/kg (acute and
Dominant lethal assay Sprague-Dawley rat 30, 900, 1400 Negative Brusick 1975
mg/kg bw (acute)
30, 250, 500 Positive
Dominant lethal assay male Sprague-Dawley 50, 150, 500 Positive2 Sheu et al.
rats mg/kg bw/day 1986
1% diet Negative
Table 5 (cont'd)
Test System Test Object Concentration of Results Reference
Heritable male mice 1% diet Negative Sheu et al.
translocation assay 1986
Mitotic recombination Saccharomyces 0.6-2.4% Negative Brusick 1975
Mitotic recombination Saccharomyces 30, 900, 1400 Negative SRI 1972
- Host-mediated cerevisiae D3/ICR mg/kg bw (acute
Swiss mouse 30, 250, 500 Negative
Sister chromatid CHO cells 1 - 1000 µg/ml Negative Williams et al.
DNA excision repair UV-irradiated human ? Positive Daugherty
synthesis lymphocytes 1978
DNA repair test hepatocyte primary 0.01 - 10 µg/ml Negative Williams et al.
1 Both with and without rat liver S9 metabolic activation.
2 A discussion of this result is contained in Bombard et al. (1992).
The addition of 100-250/µg of BHT/plate was shown to inhibit
3,2'-dimethyl-4-aminobiphenyl-induced mutagenicity in Salmonella
typhimurium strains TA98 and TA100 Mutagenicity was further
inhibited by use of S-9 preparations from rats fed dietary BHT (0.6%)
as compared to S-9 preparation from rats fed BHT-free diets
(Reddy et al., 1983b).
BHT was a moderately effective inhibitor of benzidine-induced
mutagenicity in Salmonella typhimurium strain TA98, activated with a
hamster liver S-9 fraction (Josephy et al., 1985).
BHT (0.11-11 /µM) protected against DNA damage induced in rat
hepatocytes by AAF or N-hydroxy AAF as shown by a marked reduction of
unscheduled DNA synthesis. BHT also inhibited AAF-induced DNA damage
in human hepatocytes. In addition, rats pre-treated with 0.5% BHT in
the diet for 10 days provided hepatocytes which exhibited less
unscheduled DNA synthesis than did hepatocytes from control rats when
these cells were exposed to either AAF or N-hydroxy AAF (Chipman &
2.2.7 Special studies on hepatotoxicity
Groups of male ddY mice treated perorally with BHT (200-800 mg/kg
bw) in combination with an inhibitor of GSH synthesis, buthionine
sulfoximine (BSO, 1 h before and 2 h after BHT, 4 mmol/kg bw/dose,
i.p.) developed hepatotoxicity characterized by an increase in SGPT
activity and centrilobular necrosis of hepatocytes. The hepatotoxic
response was both time- and dose-dependent. BHT (up to 800 mg/kg bw)
alone produced no evidence of liver injury. Drug metabolism inhibitors
such as SKF-525A, piperonyl butoxide, and carbon disulfide prevented
the hepatotoxic effect of BHT given in combination with BSO while
inducers of drug metabolism such as phenobarbital tended to increase
hepatic injury. The results suggested that BHT was activated by a
cytochrome-P-450-dependent metabolic reaction and that the hepatotoxic
effect was caused by inadequate rates of detoxification of the
reactive metabolite in mice depleted of hepatic GSH by BSO
administration. Based on studies with structural BHT analogues, the
authors suggested that a BHT-quinone methide may play a role in the
hepatotoxicity in mice (Mizutani et al., 1987).
Female (albino Wistar) rats, initial body weight 120-130 g, were
maintained on a diet containing 0 or 0.4% BHT, for 80 weeks. After one
week on the test diet, significant increases were observed in liver
weight, microsomal protein, cytochrome P-450, cytochrome b5,
NADPH-cytochrome c reductase, biphenyl-4-hydroxylase and ethyl
morphine N-demethylase but not aniline-4-hydroxylase. Total liver
protein, succinic dehydrogenase and glucose-6-phosphatase were
slightly decreased. There was little change in this pattern during the
period of the study. Rats removed from the BHT test diet at the end of
the test period and maintained on BHT free diet for 18 days, showed a
return to normal for many liver parameters except for cytochrome b5,
cytochrome c reductase and ethylmorphine N-demethylase. Histological
changes at the end of 80 weeks feeding consisted of centrilobular cell
enlargement, which was reversible following 18 days on a BHT-free
diet. The only ultrastructural change was a prolileration of smooth
endoplasmic reticulum (Gray et al., 1972).
Groups of female rats (80-100 g) received 0.4% BHT with corn oil
mixed in ground lab chow and were sacrificed at intervals of 1, 8, 16,
32, or 80 weeks, and compared with controls. Samples of liver were
taken for biochemical, histochemical, and morphological studies. To
examine for reversibility of hepatic changes, control diet was
administered for 18 days to a group of 4 rats following 80 weeks of
BHT administration. After one week on BHT, there was a marked liver
enlargement with relative liver weight increased up to 35% and with an
increase in drug metabolizing activities and NADP cytochrome c
reductase activity. After 18 days of removal from the 80-week
treatment, there was only a slight increase in liver weight. The
effect was therefore reversible. Histologically, after BHT treatment
the liver was characterized by enlarged centrilobular hepatocytes,
with a heterogenous appearance of this zone. Ultrastructurally, there
was a proliferation of smooth endoplasmic reticulum. The authors noted
that although the evidence of liver injury was equivocal, there were
two features that were also seen with many hepatotoxins and
hepatocarcinogens: depression of glucose-6-phosphatase activity and
cell enlargement. However, there were no lysosomal changes
characteristic of cytologic injury, and effects were reversible
(Crampton et al., 1977).
Groups of 8 male Wistar rats were given diets containing 0, 0.1,
0.25, 0.5, or 0.75% BHT for 30 days. BHT did not induce cellular
proliferation in the liver, urinary bladder or thyroid after 30 days
as measured by the [3H]thymidine labelling index or mitotic index.
In a second experiment, groups of 8 rats were treated with 0.5%
dietary BHT for 2, 4, 8, 10, or 14 days. This treatment led to a
time-limited increase in liver cell [3H]thymidine-labelling index
that subsided to control values within 8 days. This increase in
[3H]thymidine labelling in the liver was accompanied by an
unexpectedly large increase in the mitotic index (Briggs et al.,
Groups of female Sprague-Dawley rats were given 700 mg BHT/kg bw
and selected hepatic biochemical effects were determined after 4 and
21 h. Ornithine decarboxylase (ODC) activity and cytochrome P-450
content were increased 190 and 30% respectively. No effect was seen on
hepatic glutathione content or serum alanine aminotransferase
activity. Indication of hepatic DNA damage was obtained as measured by
an increased alkaline DNA elution. No effects on these parameters
could be detected when the BHT dose was 140 mg/kg bw. It was concluded
that BHT in high doses may have a DNA damaging effect (Kitchin &
BHT was administered to male Wistar rats by savage at doses of
0, 25, 250 or 500 mg/kg bw/day for 7 days (5 rats/group), or 28 days
(10/group) and also at daily doses of 1000 or 1250 mg BHT/kg bw/day
(5 rats/group) for up to 4 days (sublethal doses). The sublethal doses
induced centrilobular necrosis within 48 h, whereas administration of
250 or 500 mg/kg bw/day BHT for 7 or 28 days caused dose-related
hepatomegaly and, at the highest dose level, induced progressive
periportal hepatocyte necrosis. The periportal lesions were associated
with proliferation of bile ducts, persistent fibrous and inflammatory
cell reactions, hepatocyte hyperplasia and hepatocellular and nuclear
hypertrophy. Evidence of mild cell damage was also obtained at
250 mg/kg bw/day, while there was no evidence that BHT caused liver
damage at 25 mg/kg bw/day. Biochemical changes consisted of
dose-related induction of epoxide hydrolase, dose-related changes in
the ratio of cytochrome P-450 isoenzymes and depression of
glucose-6-phosphatase. Measurement of BHT demonstrated a dose-related
accumulation in fat but not in the liver (Powell et al., 1986).
The acute effects of a single oral administration of 500 mg/kg bw
BHT to rats were investigated in combination with phenobarbitone (PB),
a microsomal enzyme inducing agent, and buthionine sulfoximine (BSO),
a glutathione-depleting agent. Groups of 10 male Sprague-Dawley rats
received BHT in corn oil by gavage, BHT with 3 days prior
administration of 80 mg/kg bw/day PB in saline i.p., BHT with 1 h
prior administration of 900 mg/kg bw BSO in saline i.p., or corn
oil/saline alone. Thirty-six hours after administration of BHT, the
animals were sacrificed and blood was collected for assay of serum
enzyme activities (ALT, AST, alkaline phosphatase, lactate
dehydrogenase), albumin, APTT and clotting factors II, VII, X and
IX. Samples of liver (from each of 4 lobes), lung and kidney were
processed for histopathological examination which included
immunochemical staining of liver lot visualization of cytochrome P-450
1A and 2B distribution. Liver homogenates were also assayed for
reduced glutathione concentration, microsomal cytochrome P-450,
ethoxyresorufin- O-deethylase (EROD) activity, ethoxycoumarin- O-
deethylase (ECOD) activity, epoxide hydrolase activity and malondi-
The results showed that a single oral dose of 500 mg/kg bw BHT
was below the threshold for acute hepatotoxicity. BHT administration
had no effect on any of the serum parameters, with the exception of a
slight reduction in the levels of clotting factor IX. There was no
evidence that BHT induced hepato-cellular necrosis, and hepatic
malondialdehyde concentration, an indicator of lipid peroxidation, was
reduced from controls. A single dose of BHT was also associated with
an increase in mitotic activity of hepatocytes in 8/10 animals,
increased hepatic activity of ECOD without affecting microsomal
protein content or EROD activity, and a marked increase in hepatic
epoxide hydrolase activity. The last was postulated to be related to
BHT-induced inhibition of phylloquinone epoxide reductase activity.
There was no effect on hepatic GSH levels, no clear treatment-related
change in immunochemical staining of hepatocytes for the cytochrome
P-450 1A or 2B isoenzyme families and no histopathological changes in
the lung or kidney. Prior administration of PB or BSO resulted in
unequivocal liver damage (hepatocyte degeneration or coagulative
necrosis), mostly in the centrilobular areas, in about half the rats,
without affecting serum parameters which are commonly used indices for
tissue damage (ALT, AST, lactate dehydrogenase). Since neither of
these treatments duplicated the periportal cell damage observed with
repeated administration of BHT, the results could not be used as a
model for investigation of alterations in enzyme profiles induced by
repeated administration of BHT (Powell & Connolly 1991).
2.2.8 Special studies on nephrotoxicity
A single large dose of BHT (1000 mg/kg bw) in male F344 rats
produced some renal damage, as measured by reduced accumulation of
p-aminohippuric acid in renal slices, proteinuria and enzymuria, in
addition to hepatic damage. Administration of phenobarbital (80 mg/kg
bw, i.p., daily for 4 days) prior to BHT treatment of male rats
produced renal damage accompanied by slight tubular necrosis and more
pronounced biochemical changes. Female rats were less susceptible to
BHT-induced renal and hepatic damage than male rats (Nakagawa &
The nephrocalcinogenic effect of BHT was studied in groups of
10-20 female Wistar rats (5 weeks old) fed 1% BHT for 13-48 days in
semi purified diets using sodium caseinate or lactalbumin as the only
protein source. BHT induced nephropathy in female rats irrespective of
the diet used. Pronounced nephrocalcinosis was only found in rats fed
the sodium caseinate diet. Thus a connection between the development
of nephropathy and nephrocalcinosis after BHT was not established
(Meyer et al., 1989).
Groups of 10 male ddY mice received 0, 1.35%, 1.75%, 2.28%,
2.96%, 3.85% or 5.00% BHT in a purified diet, (equal to 0, 1570, 1980,
2630, 3370, 4980 or 5470 mg/kg bw/day, respectively) for 30 days.
Terminal body weights in all groups of treated mice were lower than
those of controls, the difference ranging from 15% at the lowest dose
to 30% at the highest dose, statistically significant at the highest
three doses. Absolute and relative kidney weights exhibited
dose-related decreases and increases, respectively, which were related
to reduced body-weight gain. Results from gross pathology of the
kidney showed 7/10 of the high-dose animals with "misshapen kidney"
compared with none in any of the other treated or control groups.
Histopathology of the kidney revealed a dramatic dose-related increase
in the incidence and severity of toxic nephrosis (0, 2, 3, 6, 8, 10,
and 10 out of 10 mice/group) as indicated by a number of tubular
lesions (distal and proximal tubular degeneration, distal tubular
necrosis, distal tubular regeneration, tubular dilatation and cysts).
No pathological changes were noted in the liver of these same mice
which could be related to treatment. The ED50 for toxic nephrosis in
the tidy male mouse following 30 days of administration of BHT in the
diet was calculated to be 2300 mg/kg bw/day (Takahashi, 1992).
2.2.9 Special studies on pulmonary toxicity
Young male Swiss Webster mice were injected i.p. with BHT at dose
levels ranging from 63 to 500 mg/kg bw BHT. The animals were killed 1,
3 or 5 days after BHT administration. Histopathological changes were
well-developed 3 days after administration of 500 mg/kg bw, and
consisted of a proliferation of many alveolar cells, formation of
giant cells and macrophage proliferation. These changes were
accompanied by an increase in lung weight and total amounts of DNA and
RNA. The changes were dose dependent, the smaller effective dose being
250 mg/kg bw (Saheb & Witschi, 1975).
Sixty male Swiss mice were given i.p. injections of 400 mg/kg bw
BHT dissolved in corn oil. Six experimental animals and 6 controls
were sacrificed daily for 9 days. Two hours before sacrifice, each
animal received 2 µCi/g of tritiated thymidine. No animals died during
the study and none showed signs of respiratory distress. Two days
after dosing, cellular lesions were noticed in the type I alveolar
epithelium. Abnormal giant type II cells were observed in mitosis and
many had an accumulation of tritiated thymidine. Labelled endothelial
cells were seen after day 6 in small vessels and capillaries, and
there was an increase in fibroblastic cells in the interstitium and
capillaries. There was an increase in thymidine-labelled pulmonary
cells from days 2 through 5, after which labelling dropped off and
approached control levels by day 9. Levels of lung thymidine kinase
activity rose sharply on days 1-4 after dosing and then dropped off
rapidly (Adamson et al., 1977).
Groups of NMRI mice (25-35 g) and Wistar rats (160-320 g)
received BHT as a single dose of 500 mg/kg bw dissolved in soya bean
oil, either i.p. or by gavage. Four days later, radiolabelled 14C
thymidine was given. After 90 minutes, the animals were sacrificed,
lungs removed and DNA levels were measured. In mice, DNA synthesis was
equally increased in males and females by oral or i.p. administration.
Although lung weight was increased, the concentration of DNA was not
affected. No effect was seen in male rats and only a slight increase
in females (Larsen & Tarding, 1978).
Groups of 16-24 Swiss male mice (25-30 g) received a single i.p.
injection of BHT in corn oil (63, 215, or 500 mg/kg bw) or corn oil
only (Tocopherol stripped 0.5 ml). Three days later the mice were
sacrificed. After BHT treatment, wet lung weights were increased to
120% of control, as were dry lung weights. There were significant
increases in DNA content and level of non-protein sulfhydryl (133-156%
of control). Superoxide dismutase and other oxidative enzyme levels
were increased. The authors concluded that BHT apparently increased
inflammatory and reparative-proliferative processes of the lung
(Omaye et al., 1977).
Following acute exposure to BHT, the initial sequence of events
involved infiltration of type I (squamous) epithelial cells followed
by multifocal necrosis and destruction of the blood barrier. A
detailed discussion of the sequence of tissue changes and repair
mechanisms was given. It was stated that the susceptibility of the
squamous epithelium to injury was similar to that seen after oxygen
exposure, radiation exposure, and treatment with blood-borne
bleomycin, but the recovery pattern was quite different. BHT was
thought to cause cell lysis and death as a result of interaction with
the cell membrane (BIBRA, 1977).
The increase in lung weight and increase in thymidine
incorporation into lung DNA observed in mice following BHT injection
was inhibited by treatment with cedar terpenes. No increase in lung
weight was observed in animals treated with BHT alone if they were
less than 3-week old. This may result from the inability of infant
mice to metabolize BHT (Malkinson, 1979).
In a study of lung toxicity of BHT analogues in mice, it was
established that the structural feature essential for toxic activity
is a phenolic ring structure having a methyl group at the 4-position
and ortho-alkyl group(s) which can result in a moderate hindering
effect of the hydroxyl group (Mizutani et al., 1982).
In another study, the toxic potency of BHT in mice was decreased
by deuteration of the 4-methyl group, suggesting that lung damage
following administration of BHT was caused by the metabolite
2,6-di- tert-butyl-4-methylene-2,5-cyclohexadienone (Mizutani et al.,
Male mice given a single dose of BHT showed ultrastructural
changes of the lung, which were characterized by selective destruction
of type I epithelial cells, which were replaced by type II cuboidal
cells. These changes were accompanied by a marked decrease in the
number of peroxisomes, as well as catalase activity (Hirai et al.,
Subcutaneous injections of BHA significantly enhanced the
lung/body weight ratio of mice given intraperitoneal injections of
subthreshold doses of BHT (Thompson et al., 1986).
The ability of BHA to modify BHT-induced changes in lung weight
was studied in male CD-1 mice. BHA alone had no effect on lung weight
up to a dose of 500 mg/kg bw (s.c.). When injected 30 minutes prior to
sub-threshold doses of BHT (0-250 mg/kg bw, J.p.), BHA significantly
enhanced lung weight in a dose-dependent manner. The ability of BHA to
enhance BHT-induced changes in lung weight was dependent on both the
time and the route of administration of BHA relative to BHT (Thompson
& Trush, 1988a).
In experiments with mouse lung slices, BHA enhanced the covalent
binding of BHT to protein. Subcutaneous administration of either BHA
(250 mg/kg bw) or diethyl maleate (DEM, 1 ml/kg bw) to male CD-1 mice
produced a similar enhancement of BHT-induced lung toxicity. In
contrast to DEM, the administration of BHA (250 or 1500 mg/kg bw) did
not decrease mouse lung glutathione levels. In vitro results
suggested that BHA facilitates the activation of BHT in the lung as a
result of increased formation of hydrogen peroxide and subsequent
peroxidase-dependent formation of BHT-quinone methide (Thompson &
BHT administration lowered cytosolic Ca++ -activated neutral
protease (calpain) activity in the lungs of male and female A/J mice.
The altered proteolytic activity occurred earlier (day 1) and at a
close lower than that which caused observable lung toxicity as
assessed by the lung weight/body weight ratio (day 4) (Blumenthal &
A range of doses from 10-200 mg/kg bw of BHT or BHT-BuOH, a
metabolite of BHT, were administered i.p. to groups of 2-3 inbred,
C57BL/6J mice. BHT-BuOH had a 4- to 20-fold greater potency than
BHT in increasing the relative lung weight, decreasing lung
cytosolic Ca++-dependent protease activity, and causing pulmonary
histopathology. Nature of damage (type I cell death) and regenerative
response (type II cell hyperplasia and differentiation) were identical
with the two compounds. BHT-BuOH also caused damage to liver, kidney
or heart. The authors suggested that BHT-BuOH formation may be an
essential step in the conversion of BHT to the ultimate pneumotoxin,
which might be the corresponding BHT-BuOH-quinone methide (Maikinson
et al., 1989).
The synthetic corticosteroid methylprednisolone (MP; 30 mg/kg bw,
s.c. given twice daily for 3 days) partially protected male C57BL/6N
mice from the pulmonary toxicity of BHT when administered 0, 24 or
48 h after BHT treatment (Okine et al., 1986).
The activity of a metabolite of BHT hydroxylated on one
tert-butyl group, (BHT-BuOH) in inducing pneumotoxicity was
investigated in the mouse on the basis that pneumotoxicity had been
observed following administration of BHT in all inbred strains of mice
tested, but not in rats, and BHT-BuOH was a major product of mouse
liver and lung microsomes and formed only in traces in rat microsomes.
Lung damage was assessed by determining lung/body weight ratios,
Ca2+-dependent protease (calpain) activity and by histopathological
examinations of the lungs. The liver, heart and kidneys were
investigated for histopathological changes resulting from i.p.
injection of BHT-BuOH. BHT-BuOH induced nearly a doubling of lung/body
weight ratios 4 days after an i.p. injection of 50 mg/kg bw. By
comparison, doses of 200 mg/kg bw BHT or greater were required to
produce consistent increases in this parameter. Other BHT metabolites,
DBQ, BHT-MeOH, BHT-OOH and BHT-OH, had no effect at i.p. doses of
200 mg/kg bw. Pulmonary calpain activity was significantly decreased
in mice which received 50 mg/kg bw BHT-BuOH, reaching a maximal loss
at 3-4 days after administration. This effect was similar in time
course and extent to that induced by 400 mg/kg bw BHT. A dose of
10 mg/kg bw BHT-BuOH also resulted in a significant decrease in
calpain activity which was less marked than the higher dose. Alveolar
deterioration and compensatory Type II cell hyperplasia, inflammatory
response and bronchiolar cell hyperplasia were observed in response to
i.p. doses of 50 mg/kg bw BHT-BuOH. Less extensive effects were noted
with doses of 10 mg/kg bw and these effects were considered comparable
to those induced with doses of 400 mg/kg bw BHT. On the basis of the
qualitative similarity in the effects of BHT and BHT-BuOH on the
mouse lung, the higher potency of the metabolite, and the species
correlation of formation of BHT-BuOH and pneumotoxicity, the authors
concluded that BHT-BuOH was an intermediate in the biotransformation
of BHT to a toxic metabolite in the mouse (Malkinson et al., 1989).
A quinone methide metabolite of BHT which is formed subsequent to
hydroxylation of the tert-butyl side group (QM-OH) was investigated
as the metabolite responsible for pulmonary toxicity in mice. QM-OH
was more strongly electrophilic than BHT-quinone methide as indicated
by a reaction time with GSH which was 6 times faster. Liver and lung
microsomes from both rats and mice produced quinone methide from BHT,
but only microsomes from the mouse produced QM-OH readily from BHT.
Microsomes from rat liver produced traces of QM-OH and lung microsomes
produced none. These results were used to reconcile previous results
linking pulmonary toxicity in the mouse to quinone methide formation
with species specificity of this effect. The authors postulated that
the organ specificity of BHT toxicity in mice was due to lower
concentrations of GSH in the lung compared with the liver for
inactivation of toxic metabolites (Bolton et al., 1990).
The time course for repair of BHT-induced lung injury was
investigated in four strains of mice with i.p. LD50s ranging from
350-1700 mg/kg bw. The four strains of mice tested developed similar
levels of injury at equivalent doses and no correlation could be made
between lung injury and lethality (Kehrer & DiGiovanni, 1990).
A number of compounds which modify the activity of specific
cytochrome P-450 isoenzymes were used to identify the isoenzymes
involved in bioactivation of some compounds, including BHT, to
pulmonary toxins. Pretreatment of mice with O,O,S-trimethylphosphoro-
dithioate, bromophos, p-xylene, ß-naphthoflavone or pyrazole all
produced a reduction of pneumotoxicity in MF1 outbred mice induced by
a single i.p. dose of 400 mg/ kg bw BHT as indicated by a lowering of
lung/body weight ratios measured 3 days after administration of BHT.
The first three agents greatly reduced lethality of BHT in mice as
indicated by an increase in LD50 values. The prevention of lung
toxicity by these agents was proportional to the reduction in
lethality of BHT. These three agents also markedly inhibited
pentoxyresomfin (PROD) activity, an action attributed to CYP 2B1 in
rat lung microsomes. ß-Naphthofiavone exerted a less marked effect on
these LD50 values and PROD activity, and pyrazole-induced PROD
activity. The authors concluded that since the three agents which
prevented the pneumotoxicity of BHT in mice also inhibited PROD
activity in rat lung microsomes, CYP 2B1 was the most likely candidate
for the bioactivation of BHT in mouse lung. However, since BHT is not
toxic to the rat lung, results obtained with rat lung microsomes would
not necessarily be relevant to the mouse. In addition, the authors did
not mention that pretreatment of mice with pyrazole, while reducing
the lung/body weight ratio increase induced by BHT, also induced PROD
activity in rat lung microsomes (Verschoyle et al., 1993).
The ability of isolated Clara (non-ciliated bronchiolar
epithelial) cells from mouse lung to metabolize BHT to the putative
toxic quinone methide QM-OH was investigated as well as comparison of
the toxic effects of BHT and BHT-BuOH on these cells. These cells
contain most of the monooxygenase activity of the lung, mainly as CYP
2B1/2B2. Analysis of quantitative metabolite data revealed that
hydroxylation of BHT occurred 5 times more readily at a tert-butyl
group, producing BHT-BuOH, than at the 4-methyl position to produce
BHT-MeOH in mouse Clara cells. The data also suggested that QM-OH was
more readily produced from BHT-BuOH than was BHT-QM from BHT. BHT-BuOH
more effectively reduced the viability of Clara cells in culture than
did BHT. Concentrations of 5 and 10 µM BHT-BuOH reduced viability in a
comparable manner to 75 and 100 µM BHT. Inhibition of cytochrome P-450
with SKF 525-A reduced damage to Clara cells induced by both BHT and
BHT-BuOH. The authors concluded that BHT-BuOH is an intermediate in
P-450-catalyzed oxidation of BHT to a cytotoxic species which they
propose is QM-OH (Bolton et al., 1993).
Groups of 20 male Swiss albino mice received BHT in olive oil or
olive oil alone by a single i.p. injection at doses of 0, 200, 400 or
800 mg/kg bw. Five animals from each group were sacrificed at 24 h,
48 h or 7 days after exposure. Lavage fluid was collected from the
lungs and assayed for total protein content and lactate dehydrogenase
(LDH) activity. Cells in the sediment were counted. Histopathological
examination of the lungs was performed. A time- and dose-dependent
increase in the number of cells in the bronchoalveolar lavage fluid
and in the total protein content and LDH activity was noted at 48 h
and 7 days. The severity of histopathological lesions, described as
congestion of capillaries and small blood vessels, and increased
cellularity and diffuse thickening of alveolar septa, was also
increased in a time- and dose-dependent manner (Waseem & Kaw, 1994).
2.2.10 Special studies on haemorrhagic effects
See Combined species, section 188.8.131.52
Groups of male Sprague-Dawley rats (6 weeks of age) received BHT
in a semi-synthetic diet at concentrations ranging from 0.6% to 1.4%
or control diet only. Deaths occurred within 40 days, at levels of
0.7% or greater. Spontaneous massive bleeding to the pleural and
peritoneal cavities, or as external haemorrhage, was observed in all
dead or dying animals. The prothrombin index was decreased as the
daily dose of BHT was increased. Mild diarrhoea was noted after 4
days. Rough hair coat, and redness of urine was noted. Death was due
to haemorrhage and was classified by the authors as a secondary type
of toxicity, probably due to a decrease in prothrombin concentration.
According to the authors, the effect seemed to depend on strain of
rats and dietary concentration (Takahashi & Hiraga, 1978a).
Groups of 10 male Sprague-Dawley CLEA rats were fed diets
containing 0.6, 0.7, 0.8, 1.0, 1.2, or 1.4% BHT for 40 days. A
dose-related effect on mortality (21 death/50 rats) was observed with
rats given 0.7% or more BHT during the period from 9 to 37 days.
Spontaneous massive haemorrhages were observed in these animals. The
prothrombin index of survivors was decreased, which was dependent on
the BHT dose. At the lowest level, the decrease was approximately 65%
(Takahashi & Hiraga, 1978b).
Male Sprague-Dawley CLEA rats were maintained on diets containing
levels of 85, 170, 330, 650, 1300, 2500, or 5000 mg/kg BHT for 1 to 4
weeks. A significant decrease in the prothrombin index was observed at
week 1 in all groups fed BHT at levels of 170 mg/kg or higher.
However, when the rats were maintained on the test diets for 4 weeks,
a significant decrease in the prothrombin index was observed only in
the 5000 mg/kg group. This was the only group which showed an increase
in relative liver weights compared to those of the control group. In
another study, haemorrhagic death, haemorrhage, and a decrease in
prothrombin index in male Sprague-Dawley rats caused by 1.2% BHT were
prevented by the simultaneous addition of 0.68 mole phylloquinone/kg
bw/day. Phylloquinone oxide also prevented hypoprothrombinemia due to
BHT (Takahashi & Hiraga, 1979).
Male Sprague-Dawley rats were fed diets containing 0 or 1.2% BHT
for one week. BHT-treated rats showed haemorrhages in most organs.
There was a significantly increased leakage of Evans Blue into the
epididymis. In addition, inhibition of ADP-induced platelet
aggregation and decreased platelet factor 3 availability were
observed. Plasma prothrombin factors were decreased, but fibrinolytic
activity was unchanged (Takahashi & Hiraga, 1981b).
Male albino rats (CRL COB CD(SD) BR) given 3 consecutive daily
doses of 380, 760, or 1520 mg BHT/kg bw/day showed no evidence of
haemorrhage. However, BHT produced a dose-dependent increase in
prothrombin time, with no effect on prothrombin time seen in the
380 mg/kg bw/day group (Krasavage, 1984).
Male rats receiving 0.25% dietary BHT for 2 weeks showed
decreased concentrations of vitamin K in the liver and increased
faecal excretion of vitamin K (Suzuki et al., 1983).
Dietary BHT at a level of 1.2% was shown to affect platelet
morphology (distribution width), and to cause changes in the fatty
acid composition of the platelet lipids (Takahashi & Hiraga, 1984).
Groups of 4-5 male Sprague-Dawley rats (5-6 weeks old) were fed a
diet containing 1.2% BHT for 1-7 days, and blood coagulation factors
II(prothrombin), VII, VIII, IX and X, and platelet aggregation were
measured. The average dose of BHT was about 1000 mg/kg bw/day. The
plasma concentrations of factors II, VII, IX and X were significantly
reduced in a time-dependent fashion when BHT was administered for 2-7
days and haemorrhages in epididymis were found in rats given BHT for
4-7 days. On the contrary, thrombin-induced and calcium-required
aggregation of washed platelets was unchanged throughout the
experiment. These results suggest that factors II, VII, IX and X
rapidly decrease immediately after the administration of BHT, but
hypoaggregability of platelets may be a secondary effect caused by
bleeding (Takahashi, 1986).
Groups of 4-10 male Sprague-Dawley rats (5-6 weeks old) were
given single oral doses of 800 mg BHT/kg bw and 0.5-72 h later, plasma
concentrations of blood coagulation factors II (prothrombin), VII, IX
and X and hepatic levels of BHT and BHT-quinone methide were
determined. Levels of the coagulation factors were reduced 36-60 h
after BHT treatment, but by 72 h some recovery had occurred. Hepatic
levels of BHT reached maxima at 3 h (a major peak) and 24 h after BHT
dosing and BHT-quinone methide reached maxima at 6 and 24 h (a major
peak). When BHT was given in doses of 200, 400 or 800 mg/kg bw,
factors II, VII and X decreased after 48 h only in rats given the
highest dose, but factor IX was more susceptible to BHT and showed a
dose-dependent decrease. Neither pretreatment with phenobarbital for 3
days nor the feeding of 1% cysteine in the diet throughout the
experiment prevented the decrease in vitamin-K-dependent factors at
800 mg/kg bw. In contrast, pretreatment with cobaltous chloride or SKF
525A partially prevented the decrease in the blood coagulation
factors. The results indicate that the anticoagulant effect may
require the metabolic activation of BHT (Takahashi, 1987).
The diets used in the above mentioned studies, and in previous
studies from the same laboratory contained no added vitamin K, and the
animals apparently were marginally vitamin K deficient (Faber, 1990).
BHT was less efficient than synthetic retinoids in elevating
the prothrombin times and causing haemorrhagic deaths in male
Sprague-Dawley rats maintained on a diet devoid of vitamin K (McCarthy
et al., 1989).
The effects of BHT on platelet aggregation were examined.
In vitro experiments indicated that BHT, at concentrations greater
than about 10-3M, inhibited both ADP- and collagen-induced platelet
aggregations, but not those induced by arachidonic acid. BHT-quinone
methide also inhibited ADP- and collagen-induced aggregations to a
lesser extent. In another experiment, male Sprague-Dawley rats were
fed a diet containing 1.2% BHT (650-740 mg/kg bw/day) for 4 or 7 days.
The treated animals showed marked decreases in body-weight gain
compared with controls. Haemorrhage was detected in epididymal adipose
tissues of all animals receiving BHT in the diet. Platelet aggregation
capacity induced by ADP or collagen in platelet-rich plasma collected
from these rats was considered to be normal. Although aggregation
induced by 3.9 mM arachidonic acid was markedly inhibited in platelets
from the rats fed 1.2% BHT for 7 days, platelet aggregation induced by
the optimal concentration of arachidonate (2.0 mM) was normal. These
results suggested a difference in plasma or platelet properties
between the BHT-treated and control rats. The authors concluded that
BHT-induced haemorrhage in rats was not due to a direct effect of BHT
on platelet aggregation. The differences between in vitro and
in vivo results were attributed to the low plasma concentrations of
BHT or BHT-quinone methide which were present in vivo (Takahashi,
This study reported on the effect of BHT on vitamin K-dependent
clotting factors in rats receiving vitamin K-sufficient and vitamin
K-supplemented diets. Groups of 5-6 male Wistar rats received diets
with BHT added to give a nominal intake of: (1) 0, 3000 mg/kg bw/day
or 3000 mg/kg bw/day plus 250 mg vitamin K3/kg of feed for 7, 14 or
21 days; (2) the same regimen for 7 or 14 days with a 250 mg/kg
Vitamin K control group added; (3) 0, 12.5, 125 or 600 mg/kg bw/day or
600 mg/kg bw/day plus 3 mg/kg vitamin K3 for 28 days. The basic diet
(SDS Ltd., Witham, Essex, UK) was found to contain a minimum of
3 mg/kg vitamin K3 which was considered more than adequate to supply
the recommended intake of this vitamin. In the first experiment,
prothrombin time (PT) was measured as well as specific vitamin
K-dependent factor deficiencies. The results showed that 3000 mg/kg
bw/day BHT had no effect on PT, but specifically decreased the levels
of vitamin K-dependent clotting factors II, VII, X and IX in rats
receiving a diet containing adequate vitamin K. In experiments 2 and
3, a Thrombotest optimized for rodents was used in addition to
different assay methods for PT and APTT. Serum fibrinogen levels were
measured in experiment 2 only. Thrombotest time, PT and APTT were
significantly increased from controls within 7 days at a close of
3000 mg/kg bw/day. Vitamin K3 supplementation at 250 mg/kg in the
diet prevented the BHT-induced increases in Thrombotest time and APTT
and reduced the effects of BHT on PT. BHT administration had no effect
on serum fibrinogen concentrations. Thrombotest time, but not PT or
APTT, was significantly increased from controls after administration
of 600 mg BHT/kg bw/day for 28 days. The effect was prevented by
concurrent dietary supplementation with 3 mg vitamin K3/kg of feed.
This study confirmed an antagonistic effect of BHT on vitamin K in
rats, which resulted in a reduction in blood-clotting factors even
when the diets contained adequate vitamin K. The authors pointed out
that this was a high-dose phenomenon with a threshold and a steep
dose-response curve (Cottrell et al., 1994).
184.108.40.206 Combined species
A number of strains of rats (Sprague-Dawley, Wistar, Donryu and
Fischer), mice OCR, ddY, DBA/c, C3H/HBe, BALB/CaAn and C57BL/6), New
Zealand White-Sat rabbits, beagle dogs, and Japanese quail were fed
diets containing BHT (1.2% in the diet for rats and mice; 1% for
quail; 170 or 700 mg/kg bw/day for rabbits; and 173,400, or 760 mg/kg
bw/day for dogs) for a period of 14-17 days. Haemorrbagic deaths
occurred among male rats of all strains and female rats of the Fischer
strain. Female rats of the Donryu and Sprague-Dawley strains showed no
obvious haemorrhaging. No haemorrhagic effects were noted in quails,
rabbits or dogs (Takahashi et al., 1980).
Administration of 0.5%, 1.0% or 2.0% BHT in a purified diet
(equal to 660, 1390 or 2860 mg/kg bw/day) for 21 days resulted in a
dose-related increase in the mortality due to massive haemorrhage of
the lungs in male ddY mice housed in wire-bottomed cages. The
surviving animals exhibited a dose-related increase in both absolute
and relative lung and liver weights at termination. Haemorrhagic
deaths and increased absolute lung and liver weights were not observed
in ddY male mice fed diets containing 1.35% 5.0% BHT for 30 days and
housed in cages with soft-wood chip bedding, or in Hartley guinea-pigs
fed 0.125% - 2.0% BHT in the diet for 14-17 days. The prothrombin
times were significantly increased in all groups of ddY mice receiving
BHT in the diet at levels of 1.0% or higher (with the exception of the
2.0% wire-caged group). The effect was of a similar magnitude
(approximately 25%) in treated groups housed on soft-wood bedding,
regardless of the dose. Results for kaolin-activated partial
thromboplastin time were similar. Effects on coagulation in
guinea-pigs were equivocal. The authors suggested that the coagulation
defect in mice in the absence of a dose-response relationship might be
due to minor damage to hepatobiliary function and/or fatty liver and
the haemorrhages in the lungs to injury to that organ. The haemorrhage
and coagulation defect would consequently not have the same cause as
that observed in rats. BHT was detected in the livers of mice and
guinea-pigs in dose-related concentrations (0.2-4/µg/g tissue).
BHT-quinone methide was not detected in these species although it has
been detected in the livers of rats (7-40 µg/g tissue) in a study by
Takahashi et al. (1980) (Takahashi, 1992).
2.2.11 Special studies on effects on the thyroid
Male MOL/WIST SPF rats, outbred strain (approximately 200 g) were
used for the study. BHT was added to a semi-synthetic diet in which
the iodine content was controlled at about 12/µg/100 g (nutritional
requirement for the rat is 15 µg/100 g). In one study, rats were fed
0, 500 or 5000 mg BHT/kg of feed for 8, 26 or 90 days, and the uptake
of 125I by the thyroid was determined. The presence of BHT in the
diet resulted in a marked increase in the uptake of 125I at all time
periods studied. When rats were fed BHT in diets containing varying
amounts of iodine (12, 150 or 300/µg/100 g) for 30 days, there was a
significant increase in thyroid weight in BHT-treated animals when
compared to controls. BHT in the diet of rats increased liver and
thyroid weights at 5000 mg/kg of the diet, but only thyroid weight at
500 mg/kg. BHT did not change levels of T3 and T4 in the blood.
The biological half-life of thyroxine was increased after 13 days on a
BHT diet but returned to normal after 75 days. Electron microscopy of
the thyroid glands of rats exposed to 5000 mg/kg BHT for 28 days
showed an increase in the number of follicle cells (Sondergaard &
2.2.12 Special studies on effects on the immune system
In vitro, BHT (50 /µg/culture) suppressed the plaque-forming cell
response of mouse spleen cell cultures as measured by the method of
Mishell & Dulton (Archer et al., 1978).
Addition of cyclic GMP (cGMP added as the dibutyl or 8-bromo
form) to BHT suppressed Mishell-Dulton cultures and effected a
reversal of the BHT suppression of antibody production (Wess & Archer,
2.2.13 Special studies on potentiation or inhibition of cancer
Male Strain A mice were injected i.p. with 500 mg/kg bw urethan,
then one week later received repeated injections (1/week for 8 weeks)
of either 300 mg/kg bw BHT, or 500 mg/kg bw BHA, or 1000 mg/kg bw
Vitamin E all dissolved in corn oil. At the termination of the study,
only BHT was shown to produce a significant increase in tumour yield.
Although the number of tumours produced by BHA treatment was greater
than usual, it was not statistically significant. A/J mice treated
with 3-methylcholanthrene or dimethylnitrosamine, followed by
treatment with BHT (i.p.), resulted in an increase in tumour yield
(Witschi et al., 1981).
Groups of Charles River rats (20/sex) were fed diets (males 24
weeks, females 36 weeks) containing 6600 mg BHT/kg of feed and/or
carcinogen (N-2-fluorenylacetamide or N-hydroxy-N-2-fluorenyl-
acetamide) in the molar ratio of 30:1, then continued on control diets
for another 12 weeks. The N-2-fluorenylacetamide alone resulted in
hepatomas in 70% of the male rats, and mammary adenocarcinoma in 20%
of the females. With N-hydroxy-N-2-fluorenylacetamide, 60% of the
males had hepatomas and 70% of the females had mammary adenocarcinoma.
BHT reduced the incidence of hepatomas in males to 20% when the
carcinogen was N-2-fluorenylacetamide, and to 15% when N-hydroxyl-
N-2-fluorenylacetamide was the test compound. Similar results were
obtained with Fischer strain rats. Liver and oesophageal tumour
production with diethylnitrosamines at 55 mg/litre in drinking-water
for 24 weeks was not affected by BHT (Ulland et al., 1973).
Groups of 20 male F344 rats were given a single intragastric
administration of 100 mg/kg bw MNNG or 750 mg/kg bw EHEN, 2 s.c.
injections of 0.5 mg/kg bw MBN or 4 s.c. injections of 40 mg/kg bw
DMH. At the same time, the rats received 0.1% DBN for 4 weeks,
followed by 0.1% DHPN for 2 weeks in drinking-water for a total
carcinogen exposure period of 6 weeks. Three days after completion of
these treatments, the rats received 0 or 0.7% BHT in the diet for 36
weeks. Control groups of 10 or 11 animals received 0.7% BHT alone or
basal diet alone. Final body weights of both BHT-treated groups were
significantly lower than those of respective controls (by 7% compared
with carcinogen-treated control and by 13% compared with basal diet
control) and this was reflected in higher relative kidney weights.
Relative liver weights were increased by about 60-75%. Dietary BHT
following carcinogen treatment eliminated the appearance of colon
carcinomas and reduced the incidence and multiplicity of some
preneoplastic and neoplastic lesions of the kidney. BHT administration
increased the incidence of hyperplasia, adenomas and carcinomas of the
thyroid gland and had no effect on tongue, oesophagus, forestomach,
glandular stomach, duodenum, small intestine, liver, lung or urinary
bladder (Hirose et al., 1993).
Male F344 rats were treated with 0.01 or 0.05% N-butyl-N
(4-hydroxy-butyl) nitrosamine (BBN) in drinking-water for 4 weeks, then
fed diets containing 0 or 1% BHT for 32 weeks. BHT in the diet was
associated with a significant increase in the incidence of cancer and
papilloma of the bladder of rats treated with 005%, but not 0.01% BBN
(Imaida et al., 1983).
Rats were administered 200 mg/kg N-2-fluorenylacetamide (FAA) in
the diet alone or with 6000 mg/kg BHT for 25 weeks. No bladder
neoplasms resulted from feeding FAA alone, but the combination of FAA
and BHT resulted in 17/41 papillomas and 3/41 carcinomas in the
bladder (Williams et al., 1983).
Four dietary levels of BHT (300, 1000, 3000, or 6000 mg/kg)
were simultaneously fed with 200 mg/kg FAA for 25 weeks. FAA
feeding alone produced no neoplasms, but when combined with BHT at
3000 or 6000 mg/kg, the incidence of bladder tumours were 18% and
44%, respectively. The incidence of bladder tumours in the 300 and
1000 mg/kg BHT groups was low and not significantly different from the
incidence with FAA alone (see also effects on liver) (Maeura &
Male F344 rats were given injections of methylnitrosourea (MNU)
twice a week for 4 weeks, and then a basal diet containing 1% BHT for
32 weeks. BHT significantly increased the incidence of papilloma and
papillary or nodular hyperplasia of the urinary bladder, and the
incidence of adenoma (but not adenocarcinoma) of the thyroid (Imaida
et al., 1984).
Groups of 20 male F344 rats (6-week old) were pretreated with
0.05% N-butyl-N-(4-hydroxybutyl)nitrosamine in the drinking-water for
2 weeks and thereafter given diets containing 0, 0.25, 0.5, or 1% BHT.
On day 22 of the experiment, the lower section of the left ureter of
each rat was ligated. Animals were killed at week 24 of the
experiment. BHT increased dose-dependently the incidence and number of
preneoplastic lesions, papillary or nodular hyperplasia of the urinary
bladder. The incidence of bladder lesions was increased particularly
at 1% BHT (Fukushima et al., 1987a).
Groups of 20 male F344 rats (6-week old) were given 0.05%
N,N-dibutylnitrosamine in their drinking-water for 16 weeks,
and simultaneously administered 0 or 0.7% BHT in the diet. The
simultaneous administration of BHT led to increased incidence in liver
lesions. The incidence of transitional cell carcinomas or papillary
or nodular hyperplasia of the urinary bladder and papillomas or
carcinomas of oesophagus was not altered. A decrease in hyperplastic
nodules in the forestomach was observed (Imaida et al., 1988).
Groups of 20 male F344 rats (6-week old) were pretreated with
0.05% N-butyl-N-(4-hydroxybutyl)nitrosamine in the drinking-water for
4 weeks and thereafter maintained on diets containing 0, 0.4% BHA +
0.4% BHT + 0.4% TBHQ, or 0.8% BHT. The study was terminated after 36
weeks. An increase in urinary crystals and incidence and density of
papillary or nodular hyperplasia of urinary bladder epithelium was
observed in all groups fed BHT-containing diets. The incidence of
papillomas and carcinomas of the bladder was not increased and
no proliferative changes were seen in renal pelvis. Hepatocyte
hypertrophy was induced in the group administered 0.8% BHT (Hagiwara
et al., 1989).
Ten male F344 rats (6-week old) were given a diet containing 1%
BHT with 7 mg/kg vitamin K. A decrease in body weight was observed.
DNA synthesis in the urinary bladder epithelium was increased after 4
weeks while no morphological changes were seen after 8 weeks using
light microscopy. Using electron microscopy, morphologic surface
alterations such as formation of pleomorphic or short, uniform
microvilli and ropy or leafy microridges were seen (Shibata et al.,
A study was performed to investigate early proliferation-related
responses of the renal pelvic epithelium in response to bladder tumour
promoters. Groups of 10 male F344 rats received 0 or 1% BHT. At week
4, the DNA-labelling index of the renal pelvic epithelial cells was
determined from 1000 cells in 5 rats/group. At week 8, kidney sections
were prepared for SEM examination. Body weights of the treated animals
were significantly lower than for controls, 18% at 4 weeks and 25% at
8 weeks (Shibata et al., 1989). The mean DNA labelling index in the
renal pelvic epithelium after 4 weeks treatment was slightly higher
than in controls, but without statistical significance. No cell
surface alterations were observed by SEM after 8 weeks of treatment
(Shibata et al., 1991).
Groups of 20 F344 rats, 4 or 54 weeks of age, were injected s.c.
with 50 mg/kg bw of 3,2'-dimethyl-4-aminobiophenyl (DMAB), a
multi-organ carcinogen, once a week for 10 weeks. At the same time,
the animals received 1% BHT in the diet for 11 weeks. The study was
terminated 55 weeks after initiation of treatment. Combined treatment
with DMAB and BHT resulted in the development of urinary bladder
papillomas and carcinomas in more than 95% of both young and old rats.
The induction of liver foci and pancreatic acinar cell foci by DMAB
was inhibited by concurrent treatment with BHT. Increased formation of
DMAB-DNA adducts, detected by immunohistochemical staining was
demonstrated in urinary bladder epithelial cells from the BHT-treated
rats. BHT treatment suppressed the formation of these adducts in the
liver and had no effect on formation of adducts in the colon, pancreas
or prostate. The authors suggested that these effects of BHT were
related to its ability to induce a number of drug-metabolizing
enzymes, thus altering the quantity of active metabolites in a
particular tissue (Shirai et al., 1991).
Simultaneous feeding for 76 weeks of 6000 mg/kg BHT with 50 mg/kg
AAF, a minimally effective carcinogenic dose of this compound in F344
rats, resulted in an increase in the incidence and multiplicity of
urinary bladder neoplasms, including carcinomas. Feeding of both 3000
and 6000 mg/kg BHT in conjunction with AAF resulted in an increase in
the incidence of nodular hyperplasia of the urinary bladder, and a
positive trend in the incidence of this lesion was noted down to
dietary levels of 300 mg/kg BHT. In the same study, dietary
administration of 100 - 6000 mg/kg BHT resulted in a dose-related
decrease in induction of altered hepatic foci (iron-storage deficient
and GGT-positive) and a decrease in the multiplicity of AAF-induced
adenomas and carcinomas of the liver and the incidence of carcinomas
(Williams et al., 1991).
220.127.116.11 GI tract
Groups of male BALB/c mice treated intrarectally with
methyl-nitrosurea, and then maintained on diets containing BHT, showed
a marked increase in the incidence and multiplicity of GI tract
tumours when compared to treated mice maintained on BHT-free diets. In
another study, BALB/c mice were injected with dimethylhydrazine (6
weekly injections) and then maintained on control (BHT-free) diets or
on diets containing 0.05% or 0.5% BHT. The colon tumour incidence were
10%, 0%, and 32%, in the respective groups (Lindenschmidt et al.,
The observed increase in tumour-specific antigen activity in the
colon chromatin of rats treated with 1,2-dimethylhydrazine was
eliminated by simultaneous treatment with BHT (Gabryelak et al.,
Male F344 rats were treated with a single dose of N-methyl-
N'-nitro-N-nitrosoguanidine, and then maintained on diets containing
no BHT, 1.0% BHT, 5% NaCl, or 5% NaCl + 1.0% BHT for 51 weeks. The
incidence of squamous cell carcinomas of the forestomach were 11%,
16%, 3%, and 53% in the respective groups (Shirai et al., 1984).
When rats were given 0.5% BHT in the diet for 36 weeks following
4 injections (1 per week) of 1,2-dimethylhydrazine, BHT did not affect
the number of rats with colon tumours, but the number of tumours per
rat occurring in the distal colon was significantly decreased (Shirai
et al., 1985).
Wistar rats fed 1.0% BHT in the diet during treatment with
N-methyl-N'-nitro-N-nitrosoguanidine (administered in drinking-water
at a concentration of 1.0 mg/ml) for 25 weeks, and then maintained on
the test diet for another 14 weeks, showed a significant reduction in
the incidence of gastric cancer, when compared to rats receiving
BHT-free diets (82% versus 37%) (Tatsuta et al., 1983).
Seven-week old male Wistar rats (20/group) were given
N-methyl-N'-nitro-N-nitrosoguanidine in the drinking-water
(100 mg/litre) for 8 weeks, and were also fed a diet supplemented with
10% sodium chloride. Thereafter, they were maintained on a diet
containing 1% BHT for 32 weeks. A carcinogen control group was fed the
basal diet without BHT supplementation. The experiment was terminated
40 weeks after the beginning of administration of MNNG. BHT did not
increase the incidence of tumours in the glandular stomach or in the
forestomach (Takahashi et al., 1986).
Groups of 21 male F344 rats were given 0.5 g/litre N,N-dibutyl-
nitrosamine in drinking-water for 4 weeks and then treated with a
basal diet containing 1% BHT with 7 mg/kg vitamin K for 32 weeks. BHT
enhanced oesophageal carcinogenesis (papillomas: 16/21 versus 3/21;
carcinomas 9/21 versus 0/21) but did not enhance forestomach
carcinogenesis. BHT induced an increased incidence of papillary or
nodular hyperplasia and papilloma in the bladder, while no
statistically significant increase was seen in liver lesions
(Fukushima et al., 1987b).
Groups of 5 male F344 rats were given diets containing 0 or 0.7%
BHT for 4 weeks. Histological examination of the forestomach showed
that BHT did not induce hyperplasia in the forestomach epithelium
(Hirose et al., 1987).
When male Fischer 344 rats were fed diets containing 0, 0.5% or
1.0% BHT for 5 or 6 months immediately following initiation with 2 or
4 s.c. injections of DMH (40 mg/kg bw), a significantly higher
incidence of colon tumours (5-month study) and a significantly
increased incidence of small intestinal tumours (duodenum, jejunum,
and ileum) were seen in the BHT-treated animals than in the animals
fed a BHT-free control diet. Administration of N-nitroso-N-methylurea
(NMU; 90 mg/kg bw given orally) produced stomach and colon tumours;
0.5% BHT in the diet did not affect tumour incidence. It was concluded
that dietary BHT may enhance development of gastrointestinal tumours
produced by DMH, but not by NMU, provided exposure to BHT occurs after
exposure to the carcinogen (Lindenschmidt et al., 1987).
Male Syrian golden hamsters were given a diet containing 1% BHT.
Induction of hyperplasia and neoplastic lesions of the forestomach
were examined histopathologically and autoradiographically at weeks 1,
2, 3, 4, and 16. Mild hyperplasia occurred slightly more often in
hamsters fed the BHT diet than in the control group. BHT induced no
severe hyperplasia or papillomatous lesions. No significant increase
in the labelling index was observed at any time during the experiment
(Hirose et al., 1986).
Groups of 93 rats (22-day old) received 0 or 0.5% BHT diets for
407 days following 18 days of administration of AAF (0.02%). Prolonged
feeding of BHT diet after AAF produced a significant increase of liver
tumours (Peraino et al., 1977).
Rats were administered 200 mg/kg AAF in the diet, alone or with
6000 mg/kg BHT for 25 weeks. AAF alone induced a 100% incidence of
liver neoplasms. Simultaneous administration of BHT resulted in a
decreased frequency of benign neoplasms, neoplastic nodules and
malignant neoplasms, and hepatocellular carcinomas (Williams et al.,
BHT at concentrations of 300, 1000, 3000, or 6000 mg/kg was fed
simultaneously with 200 mg/kg AAF for 6, 12, 18, or 25 weeks. BHT
produced a reduction in the incidence of tumours in a dose-dependent
manner (100% incidence in the absence of BHT to 56% at 6000 mg/kg BHT)
(see also effects on the bladder) (Maeura et al., 1984).
Rats were fed 200 mg/kg AAF for 8 weeks, then diets containing
BHT at levels of 300, 1000, 3000, or 6000 mg/kg for up to 22 weeks.
The area of altered hepatocellular foci, identified by iron exclusion
and gamma-glutamyl transferase (GGT) activity, that was induced by
feeding the AAF, showed increased development at the highest level of
BHT (the number of foci, the area occupied by GGT-positive
preneoplastic and neoplastic lesions, and the neoplasm incidence were
increased). These parameters were unaffected at the lower BHT levels
(Maeura & Williams, 19841.
Rats were given a single i.p. injection of 200 mg/kg bw of
diethylnitrosamine, and then maintained on a diet containing 1% BHT
for 6 weeks. At week 3 the rats were subjected to partial hepatectomy.
The number of gamma-glutamyl transpeptidase positive foci in the liver
of BHT-fed rats was significantly decreased when compared to controls
(Imaida et al., 1983).
BHT was compared to phenobarbital (PB) and DDT with respect to
its effect on liver carcinogenesis in male Wistar rats using an
initiation-selection-promotion protocol. The rats were initiated with
a single dose of diethylnitrosamine (DEN; 200 mg/kg bw). Two weeks
later, selection was carried out by feeding AAF for 2 weeks and giving
a necrogenic dose of carbon tetrachloride after 1 week. After another
week the rats were maintained on a diet with the promoters, or BHT at
a level of 0.5%. Groups of 8-10 animals were examined after 3, 6, 14,
or 22 weeks on the diet. BHT, as PB and DDT, had strongly increased
the frequency of GGT-positive lesions in the liver at week 14, but in
contrast to PB and DDT, BHT did not enhance the development of
hepatocellular carcinomas at week 22. It was suggested that BHT was
not a promoter of liver carcinomas in male Wistar rats when given
after initiation (Préat et al., 1986).
Initiation of liver carcinogenesis with a single dose of
diethylnitrosamine (DEN), and selection with AAF combined with a
proliferative stimulus (CCl4 administration), was followed by a
treatment with PB or BHT (0.5% in the diet) for periods up to 22
weeks. Control animals received no treatment after the initiation and
selection procedure. An increase in the amount of 2N nuclei was found
in the putative preneoplastic lesions of animals that received
initiation and selection (I-S) and 3 weeks basal diet. When the diet
was supplemented with PB (after I-S), the increase in diploid nuclei
started earlier. At the time carcinomas appeared (22 weeks PB
treatment) a decrease in the frequency of 2N nuclei was found.
BHT-treated animals which develop no carcinoma within the considered
time span showed a clear increased amount of 2N nuclei in the
precancerous lesions only after 14 weeks treatment (Haesen et al.,
Dietary administration of 1% BHT for 26 weeks was commenced
during or immediately after 2 weekly i.p. injections of azaserine
(30 mg/kg bw) to male Wistar rats. Administration of BHT after
azaserine enhanced the frequency of GST-A positive focal pancreatic
acinar lesions, while GST-P positive hepatocellular lesions were
significantly reduced. When BHT was given together with azaserine, no
effect was seen in the liver, while the frequency of preneoplastic
lesions in the pancreas was significantly reduced (Thornton et al.,
A study was conducted to establish whether the modulating effect
of dietary fats and BHT on AAF-induced hepatocarcinogenesis was
related to the levels of cytochrome P-450 in the nuclear envelope
(NE). Treatment of weanling rats with 0.3% dietary BHT for 2 weeks was
followed by up to 16 weeks of treatment with 0.05% AAF in the diet.
Prior treatment with BHT protected against the AAF-induced reduction
in the NE cytochrome P-450 content of liver cells for 9 weeks in rats
fed a diet with a high saturated fat content, compared with 3 weeks in
rats fed a diet with a high polyunsaturated fat content. The magnitude
of this effect of BHT on cytochrome P-450 content was apparently
correlated with its tumour reduction effect in rats fed AAF in
high-fat diets. The results from rats fed low-fat diets, in which BHT
apparently does not exert a significant effect on AAF-induced
carcinogenesis, were different from those in rats fed the high-dose
diets. In rats fed low-fat diets, AAF did not reduce cytochrome P-450
content until 9 weeks of feeding, at which point prior treatment with
BHT resulted in a partial reversal of this effect. In the first 3
weeks when AAF-treated rats had cytochrome P-450 content similar to
control animals, prior treatment with BHT resulted in its induction in
the AAF-treated animals (Carubelli & McCay 1989).
BHT at concentrations of 1-14 mM in the presence of a rat liver
microsomal preparation reduced the binding of AAF to calf thymus DNA
to 20% of control values. When N-hydroxylated 2-AAF, a cytochrome
P-450 activated oxidation product of AAF was used, BHT (0.1-8.0 mM)
reduced its binding to DNA to only 80% of control levels. In rat
hepatocyte cultures, BHT concentrations of 0.01-0.10 mM resulted in a
reduction of AAF binding to DNA to about 85% of control levels. These
results showed that mechanisms in addition to those demonstrated
in vivo (i.e. induction of detoxifying enzymes) may be involved in
the anticarcinogenic effects of BHT (Richer et al., 1989).
Male B6C3F1 mice were injected i.p. with 100 or 200 µmol/kg bw
of diethylnitrosamine (DEN) once a week for 10 weeks. After a recovery
interval of 4 weeks, the mice were fed diets containing 5000 mg/kg BHT
or 500 mg/kg phenobarbital (positive control) for 24 weeks. At the end
of this time, DEN alone induced a dose-related incidence of altered
hepatic foci and hepatocellular adenomas. Treatment with BHT following
DEN administration had no effect on the incidence or multiplicity of
these lesions, whereas phenobarbital administration potentiated the
effects of DEN 2 to 3 fold (Tokumo et al., 1991).
Dietary administration of 50 mg/kg AAF was found to induce a 100%
incidence of liver neoplasms after 76 weeks. Concurrent administration
of BHT at levels of 100 - 6000 mg/kg of feed inhibited the induction
of altered hepatic foci and reduced the multiplicity of hepatocellular
adenomas and carcinomas and the incidence of carcinomas (Williams
et al., 1991).
Concurrent administration of BHT in the diet at 5, 25 or
125 mg/kg of feed for 42 weeks with gavage administration of aflatoxin
B1 (5 µg/kg bw, 3 times a week) for the final 40 weeks resulted in a
reduction in the density of hepatic foci staining positive for the
placental form of glutathione S-transferase at the highest dose of BHT
(Iatropoulos et al., 1994).
The tumorigenic potency of a single i.p. injection of 1000 mg/kg
bw of urethane to male Swiss-Webster mice was significantly increased
if followed by repeated weekly injections with 250 mg/kg bw BHT. The
number of animals/group ranged from 9 to 22 and the animals were
treated for 9 to 13 weeks. Only tumours on the lung surface itself
were counted. About 90% of the animals treated with urethane alone
developed lung tumours. There was a significant increase in the number
of tumours/mouse after 11 or more weeks of treatment with BHT. Animals
treated with BHT alone did not develop lung tumours. A/J strain mice
were also given the same treatment with 10 weekly injections of BHT
The number of lung tumours/mouse significantly increased in those
receiving BHT in addition to urethane in comparison with those
receiving urethane alone. With both strains of mice, repeated
injection of BHT without prior urethane treatment did not result in an
increased number of animals with lung tumours or tumours/mouse as
compared to controls dosed with corn oil. With both mouse strains,
there were fewer lung tumours in the animals given BHT as compared to
the corn oil controls. In contrast to the above results, injection of
animals with BHT for 0-7 days before urethane injection did not
increase the number of animals with tumours or number of tumours/mouse
(Witschi & Cote. 1976).
Groups of Swiss mice were given 50, 250, or 1000 mg/kg bw
urethane or 0.9% NaCl. After 7 days, half the urethane-treated
animals and half the controls received 300 mg/kg bw BHT i.p., the
remaining animals receiving corn oil alone. The animals received 13
injections/week. The number of tumours/lung found 14-24 weeks after
the initial urethane doses was significantly increased in the
In another study, when the interval between injection of the
urethane and the first treatment with BHT was delayed for 6 weeks, BHT
treatment produced more tumours. When the number of BHT injections
commencing 1 week after urethane treatment was reduced from 13 to 4,
the same significant increase in tumour yield was observed as in the
13-dose study. However, 1 or 2 doses of BHT had no significant effect.
When the mice were pretreated with 13 injections of BHT, and then
treated with urethane 1 week later, there was no enhancement of tumour
yield. Simultaneous administration of BHT and urethane resulted in
fewer tumours compared to animals treated with urethane alone. When
mouse strains (C57BL, C3H and BALB/C) which have a low naturally
occurring incidence of lung adenoma were treated with urethane and
then with multiple injections of BHT, the BHT treatment did not
significantly increase tumour incidence or average numbers of lung
tumours (Witschi & Lock, 1979).
Male A/J mice were injected i.p. with a single dose of urethane
and then fed 0.75% of either BHT, BHA, or ethoxyquin in the diet, once
a week or continuously for 8 weeks. Lung tumour yield was scored 4
months after the urethane treatment. Dietary BHT, but not BHA or
ethoxyquin, under both test conditions, enhanced lung tumour
Mice were fed diets containing BHA or BHT for 2 weeks prior to
urethane treatment, and then maintained on conventional laboratory
diets for 4 months. The BHT diet had no effect on tumour yield, but
the BHA treatment significantly decreased the average number of
tumours (Witschi, 1981).
A/J mice were given a single dose of BHT i.p. (400 mg/kg bw),
sufficient to cause acute lung damage and produce cell proliferation
in the lung for 6 to 7 days. Urethane was administered continuously by
implanted mini pumps during this period. Continuous presence of
urethane during the period of cell division did not result in an
enhanced number of the tumours. When urethane-injected mice were dosed
i.p. with SKF525A (2-diethylaminoethyl-2-,2-di-phenylvalerate
hydrochloride) and BHT (SKF inhibits lung cell division normally seen
following BHT administration), or BHT alone, both treatment gave a
very significant increase in lung tumour yield compared to
urethane-treated controls. Repeated pulmonary cell division brought
about by other treatment e.g., 95-100% oxygen, were also shown not to
enhance tumour development (Witschi & Kehrer, 1982).
BHT was shown to enhance the lung tumour incidence in mice
treated with doses of urethane greater than 50 mg/kg bw. At lower
doses of urethane (subcarcinogenic doses) BHT did not enhance tumour
development. In another study, it was shown that following treatment
of mice with urethane, a two-week exposure to 0.75% BHT in the diet
was sufficient to enhance tumour development, and that 0.1% BHT was an
effective enhancer when fed for 8 weeks.
BHT, administered within 24 h post-treatment and fed for 8
weeks, enhanced tumour development in mice treated once with
3-methylcholanthrene, benzo(a)pyrene, or N-nitrosodimethylamine.
When mice were injected weekly with BHT, there was a rapid
increase in cell proliferation, and in both the cumulative labelling
index (incorporation of 3H-thymidine) and the number of labelled
type II cells. These effects were smaller after each injection, and by
the fifth injection, no increase was observed (Witschi & Morse, 1985).
A single i.p. injection of BHT (200 mg/kg bw) 6 h before a single
urethane injection (1000 mg/kg bw) had varying effects on lung
tumorigenesis in mice of different strains and ages. Strains
exhibiting both high (A/J, SWR/J) and low (BALB/cByJ, 129/J, C57BL/6J)
susceptibility to urethane tumorigenesis were tested. BHT treatment
decreased tumour multiplicity by an average of 32% in adult A/J mice
but acted as a cocarcinogen by increasing tumour number 48% in adult
SWR/J mice, 240% in adult C57BL/6J mice, 655% in adult 129/J mice, and
38% in 14-day old A/J mice. The numbers of both alveolar type 2
cell-derived and bronchiolar Clara cell-derived lung adenomas were
similarly affected by these BHT treatments. BHT pre-treatment had no
effect on adenoma multiplicity in either young or adult BALB/cByJ
mice. Multiplicity in young BALB cByJ mice was also unaffected by
chronic BHT administration (6 injections/week) following urethane,
while multiplicities increased several-fold with such treatment in
adult mice of this strain (Malkinson & Thaete, 1986).
A/J mice given 1000 mg/kg bw urethane followed by 400 mg/kg bw
BHT by injection, developed 40% more lung tumours than mice treated
with urethane alone. In mice treated with 3-methylcholanthrene,
repeated injections of BHT (300 mg/kg bw) increased tumour
multiplicity by a much larger factor (500-800). Pretreatment of mice
with BHT reduced the number of tumours produced by methylcholanthrene.
The enhancing effect of BHT on lung tumour development was not due to
the production of diffuse alveolar cell hyperplasia (Witschi, 1986).
Lung tumour promotion by BHT and 3 of its metabolites was
compared in the inbred mouse strain MA/MyJ. MA/MyJ mice were given a
single injection of urethane (50 mg/kg bw) followed by 6 weekly i.p.
injections of 50 or 200 mg/kg bw BHT, BHT-BuOH, 2,6-di- tert-butyl-
4-hydroxymethyl phenol (BHT-MeOH) or 2,6-di- tert-butyl-1,4-benzo-
quinone (DBQ). The only metabolite that enhanced lung tumour formation
was BHT-BuOH, and it was effective at one-fourth the effective dose of
BHT. The study implicates BHT-BuOH formation as an important step in
the chain of events leading to promotion of lung tumours (Thompson
et al., 1989).
The susceptibility of different strains of mouse to the lung
tumour-promoting effects of BHT was correlated with ability of hepatic
microsomal preparations from each strain to produce a metabolite of
BHT, BHT-BuOH, which is hydroxylated on one tert-butyl group. No
correlation existed between tumour promotion and microsomal production
of BHT-MeOH (hydroxylated on the methyl group) or DBQ (the quinone
metabolite). In the MA/MyJ strain, which was found to be the most
sensitive to promotion of urethane-induced lung tumours by BHT, 6
weekly i.p. injections of 50 mg/kg bw of the BHT metabolite, BHT-BuOH,
resulted in a similar promotional effect to 200 mg/kg bw BHT, while
200 mg/kg bw of the BHT metabolites, BHT-MeOH or DBQ, had no
promotional effect. The authors cited other evidence which implicated
the tert-butyl hydroxylation pathway in lung-tumour promotion by
BHT: preferential in vitro formation of this metabolite relative to
other metabolic products of BHT was correlated with species (rat
versus mouse) and strain susceptibility to lung tumour promotion by
BHT; the repeat-dose administration regimen of BHT associated with
lung tumour formation was also associated with induction of
hydroxylation on the tert-butyl group; and this pathway is a major
route of metabolism in the mouse lung (Thompson et al., 1989).
Evidence was cited to show that the genes which regulate
sensitivity to the lung tumour-promoting effects of BHT are distinct
from the pas (pulmonary adenoma susceptibility) genes which
predispose some inbred strains of mice to the development of lung
tumours. It was suggested that strain differences in response to the
effects of BHT are mediated through genes which regulate the ability
to metabolize BHT along specific pathways (Malkinson, 1991).
18.104.22.168 Mammary gland
Groups of female Sprague-Dawley rats were treated with
7,12-dimethylbenz[a]anthracene (DMBA) or nitrosomethylurea (NMU), and
then fed diets containing 0 or 0.3% BHT for 30 weeks. Rats treated
with DMBA and maintained on the control diet developed 100% tumour
incidence (mammary gland) by week 27, whereas those maintained on the
BHT supplemented diet had an incidence of 54% by the end of the study.
Dietary BHT had no effect on the incidence of tumours induced by NMU
treatment (King et al., 1981).
Female rats were fed diets containing 0, 0.25, or 0.5% BHT. The
test diets were administered either (a) 2 weeks before until 1 week
after DMBA administration or (b) 1 week after DMBA administration to
the end of the study (30 weeks). The DMBA was administered as a single
dose of 8 mg. BHT was an effective inhibitor of mammary carcinogenesis
when administered during either of these time frames (20% inhibition
by regime (a) and 50% by regime (b)) (McCormick et al., 1984).
Dietary BHT was shown to decrease the incidence of mammary
tumours induced in female Sprague-Dawley rats by DMBA but had no
effect on animals treated with MNU (King et al., 1981).
The inhibitory effect of BHT was strongly influenced by the dose
of initiating carcinogen and the type of diet in which BHT was fed.
Administration of BHT in the AIN-76A diet, showed a markedly different
effect from BHT in the NIH-07 diet. In the AIN-76A diet, 6000 mg/kg
BHT had no effect on the incidence of mammary tumours induced by 15 mg
DMBA, whereas a similar level of BHT in the NIH-07 diet resulted in a
40% inhibition of tumour development (Cohen et al., 1984).
A dose-related inhibition of DMBA-induced mammary tumorigenesis
in female Sprague-Dawley rats was seen after long-term exposure to
dietary BHT. BHT was given from 14 days before carcinogen
administration to termination at 210 days. In animals fed the
cereal-based NIH-07 diet and receiving a low dose (5 mg/rat) of DMBA,
there was a significant overall inhibitory trend in tumour incidence
observed among those receiving 300, 1000, 3000, or 6000 mg BHT/kg of
feed. Maximal inhibition was approximately 50% at the highest
concentration of BHT. The inhibitory effect of BHT on mammary tumour
incidence was less pronounced when BHT was administered to rats
initiated with a high carcinogen dose. At 15 mg DMBA/rat, maximal
inhibition was only 20% at the highest concentration of BHT. Similar
results were obtained when BHT was fed in the casein-based AIN-76A
diet. The inhibition seen in this study was less pronounced than that
seen in an earlier study using short-term exposure to BHT (Cohen
et al., 1986).
Retinyl acetate (RA) and BHT had additive effects in inhibiting
mammary carcinogenesis in female Sprague-Dawley rats. Chronic exposure
to RA plus BHT induced a high incidence of hepatic fibrosis and bile
duct hyperplasia; these changes were not observed in controls and were
seen in low incidence in animals exposed to RA only or BHT only
(McCormick et al., 1986).
The effect of dietary administration of BHT on the formation of
DNA adducts in the mammary gland by DMBA was investigated in female
Sprague-Dawley rats using 32P post-labelling techniques. Diets
containing 0.4% or 0.8% BHT were fed to 39-day old rats for 2 weeks
followed by oral administration of 32 mg/kg bw DMBA. BHT treatment
resulted in a 42% or 36% reduction in the formation of all types of
DMBA-derived DNA adducts 22 h later compared with DMBA-treated
controls. Dietary BHT selectively inhibited the formation of adducts
derived from the anti diastereomer of DMBA as opposed to the syn
diastereomer. Dietary concentrations of BHT within the range used in
this study have been reported to significantly inhibit the initiation
of DMBA-induced carcinogenesis (Singletary & Nelshoppen, 1991).
In this study, the effects of BHT and its metabolites BHT-MeOH
and DBQ (BHT-quinone) on DMBA-induced rat mammary carcinogenesis and
the in vivo formation of rat mammary DMBA-DNA adducts were tested.
The selection of these metabolites was based on the observation that
they were the major metabolites detected following incubation of BHT
with rat liver microsomes and that no metabolites were detected
following inhibition with rat mammary microsomes. Each of the
compounds were administered 2 weeks before and 1 week after oral
administration of 33 mg/kg bw DMBA. The i.p. administration of
200 mg/kg bw BHT and DBQ (but not BHT-MeOH) resulted in 39% and 25%
inhibition of mammary tumour formation, respectively. There was a good
quantitative correlation between inhibition of mammary tumorigenesis
by BHT and DBQ and the inhibition of DMBA-DNA adduct formation. Doses
of 100 and 200 mg/kg bw BHT inhibited DMBA-DNA binding to a similar
degree. BHT and DBQ differed in their selectivity of inhibition of
specific adducts. A decrease in the formation of the anti-dihydro-
diolepoxide adduct of DMBA to deoxyguanosine was most closely
correlated with the abilities of BHT and DBQ to inhibit mammary
tumorigenesis (Singletary et al., 1992).
Male LEW inbred rats were given an injection of 30 mg azaserine
once a week for 3 weeks, and then maintained on diets containing
0 or 0.45% BHT for 4 months. BHT treatment reduced the number of
acidophilic foci per pancreas by 32%, but was without effect on focal
size. BHT had no effect on the occurrence of basophilic foci (Roebuck
et al., 1984).
BHT had no tumour-initiating activity when tested in a two-stage
mouse skin carcinogenesis model using 12-O-tetradecanoyl phorbol-13-
acetate (TPA) as a promoter. BHT was applied twice weekly for 5 weeks
at a total dose of 100 mg (Sato et al, 1987a).
The hydroperoxide metabolite of BHT, BHTOOH (2,6-di- tert-butyl-
4-hydroperoxyl-2,5-cyclohexadienone), was an effective inducer of
epidermal ODC activity in SENCAR mice. Maximal induction of ODC
activity was observed 12 h after a single application of BHTOOH.
Papilloma and carcinoma formation was observed when BHTOOH was applied
twice weekly for 50 weeks to mice previously initiated with DMBA.
Doses of 2, 8, and 20 µmol BHTOOH gave maximal papilloma responses.
Progression of papillomas to carcinomas occurred after 60 weeks. The
data suggest that BHTOOH, unlike BHT, is an effective tumour promoter
in mouse skin. No papillomas or carcinomas were observed in
uninitiated mice treated with BHTOOH only (Taffe & Kensler, 1988).
2.2.14 Special studies on other effects
Young adult BALB/c mice of both sexes were maintained on diets
containing 0.75% BHT for 1 month, and then irradiated with 525-750 R
of X-ray. Radiation protection was observed at all doses below that
which produced 100% lethality (Clapp & Satterfield, 1975).
Hybrid (C31F1 male mice, 10-12 weeks of age, were maintained
on diets containing 0 or 0.75% BHT, for a period of 30 days, and then
injected i.p. with alkylating materials. There was a marked reduction
in the 30-day mortality in mice fed BHT Males were protected against
ethyl methane-sulphonate, n-propyl or isopropyl methanesulphonate,
ethyl dibromide, diethylnitrosamine and cyclophosphamide, but not
against methyl methane-sulphonate, N-methyl-N'-nitro-N-nitroso-
guaridine or dipropylnitrosamine (Cumming & Walton, 1973).
Rats dosed with 14C-aflatoxin B1 and fed BHT (0.5% in the
diet) showed an enhanced excretion of water-soluble metabolites of
14C-aflatoxin B1 in the urine and faeces. In addition, BHT
pretreatment was shown to decrease the amount of 14C bound to
hepatic nuclear DNA (Fukayama & Hsieh, 1985).
2.3 Observations in humans
Double-blind, placebo-controlled challenge tests with a 1:1
mixture of BHT and BHA (50 mg) were carried out in 44 cases of chronic
urticaria, 91 cases of atopic dermatitis, and 123 cases of contact
dermatitis. No positive reactions were seen (Hannuksela & Lahti,
Support bandages containing BHT were found to induce allergic
contact dermatitis in two leg ulcer patients. The lesions showed
improvement when use of the bandages in question was discontinued.
Both patients gave a positive response to skin patch testing with BHT
(Dissanayake & Powell, 1989).
A study was conducted to evaluate the sensitizing risk of BHT
based on patch testing of 1336 eczema patients and estimates of
exposure derived from a data base on chemical products. During a
2-year period in which the patients were tested, BHT produced no
positive reactions. It was concluded that these results, together with
the frequent use of BHT in industrial settings and consumer products,
suggested that concentrations of BHT encountered in normal use would
not induce allergic contact dermatitis (Flyvholm & Menné, 1990).
Two patients with chronic idiopathic urticaria were subjected to
double-blind, placebo-controlled, oral challenges with a series of
food additives. During testing, BHT and BHA were identified as
causative agents. Avoidance of foods containing BHT and BHA resulted
in long-term reduction in severity and frequency of urticarial
episodes (Goodman et al., 1990).
Using platelets from healthy volunteers, the basis for the
inhibitory effects of BHT on thrombin-induced platelet activation was
investigated. Concentrations of 20-300 µM BHT in incubation mixtures
of platelets resulted in a dose-dependent activation of protein kinase
C. The authors indicated that this action desensitizes platelets
against subsequent phospholipase C activation associated with platelet
activation by the physiological agonists thrombin and collagen
(Ruzzene et al., 1991).
BHT concentrations of 100 µg/ml were cytotoxic to human
peripheral lymphocytes in culture. Concentrations up to 60 µg/ml had
no effect on tritiated thymidine uptake in phytohaemagglutinin-
stimulated lymphocytes, although a dose-related synergistic inhibition
with cortisol or prednisolone was noted. The mixed lymphocyte reaction
(MLR) was suppressed by concentrations of 50 µg/ml BHT. There was a
linear relationship between the stimulation ratio for lymphocytes from
each pair of subjects and the extent of inhibition of the MLR by
50 µg/ml BHT. The concentrations of BHT used in lymphocyte cultures in
this study were not considered by the authors to be relevant to plasma
concentrations achieved with dietary exposures (Klein & Bruser, 1992).
The effects of long-term BHT administration have been adequately
documented in a number of rodent studies, in only one of these
studies (Olsen et al., 1986) conducted in the Wistar rat, was a
hepatocarcinogenic effect evident. This study differed from those
conducted previously in that the rats were exposed to BHT in utero,
during the lactation period, and for a further 40 weeks after the
standard 2-year exposure period. The dose levels employed were 25, 100
or 500 mg/kg bw/day. It was necessary to reduce the highest dose from
500 mg/kg bw/day in the reproduction segment to 250 mg/kg bw/day in the
long-term feeding portion of the study. A statistically significant
increase in the survival-adjusted incidence of hepatocellular
neoplasms was observed in both male and female rats at the highest
dose tested. The majority of these tumours were not malignant;
however, the incidence of hepatocarcinomas was significantly higher in
male rats in the high-dose group than in untreated males. The tumours
were detected very late in the study, in most cases when the animals
were killed following 141-144 weeks of treatment. The NOEL was
25 mg/kg bw/day, based on effects on litter size, sex ratio, and pup
body-weight gain during the lactation period in the reproduction
segment of the study.
The Committee was aware that the above study had been reviewed by
the International Agency for Research on Cancer (IARC, 1986), and
concluded that it was difficult to draw conclusions about the observed
incidence of liver lesions in the treated groups because of the large
differences in survival between treatment and control groups. The
carcinogenicity of BHT to humans could not be evaluated.
The protocol employed in the new study (Price, 1994), the purpose
of which was to investigate the hepatic changes in male Wistar rats
that occur following in utero and lifetime exposure to BHT for up to
22 months, was almost identical to that of the Olsen et al., 1986
study. In the new study, hepatomegaly was observed in the F0 dams
receiving the highest dose (500 mg/kg bw/day), while toxicologically
significant liver enlargement was not observed in any F1 dose group
up to 250 mg/kg bw/day, the highest dose tested. The body weights of
the pups from the highest dose group were significantly lower than
those of control pups throughout the lactation period, and mortality
was increased in the treated pups in a dose-related manner between
days 6 and 21 of lactation. In the F1 males, BHT administration
resulted in a persistent, marked induction of cytochrome P-450 2B and
gamma-glutamyl transpeptidase activity in the centrilobular and
periportal hepatocytes in the highest dose group throughout the study,
commencing at a very early stage (21 days of age); gamma-glutamyl
transpeptidase activity was also increased, but to a lesser extent, at
the middle dose (cytochrome P-450 2B activity was not determined).
Total cytochrome P450 content and epoxide hydrolase, ethoxyresorufin
O-deethylase, and glutathione S-transferase activities were
also consistently elevated in a dose-related manner in the mid- and
highest dose groups. In a separate study, uridine diphosphate
(UDP)-glucuronosyl transferase activity was induced in the liver of
male Wistar rats receiving BHT at a dose level of 5 g/kg (equivalent
to 500 mg/kg bw/day). Consistent enlargement of the centrilobular
hepatocytes was evident starting at 6 months in rats receiving the
highest dose of 250 mg/kg bw/day, indicative of proliferation of the
smooth endoplasmic reticulum consistent with the induction of
mixed-function oxidases. However, histopathological examination failed
to reveal any signs of hepatocellular necrosis in this group. In
addition, no evidence of hepatoxicity as indicated by a decrease in
glucose 6-phosphatase activity and intracellular glutathione content
in the treated groups, was seen. There was no indication of sustained
hepatocellular proliferation during the study. A small, but
significant, number of altered hepatic foci deficient in glucose-6-
phosphatase were found in the highest dose group (250 mg/kg bw/day) at
22 months. In this same group, lesions described as hepatic nodules
were detected in 6/19 animals as compared with none in the lower-dose
groups and controls. Evidence of thyroid enlargement with follicular
hyperplasia, in the absence of elevated serum thyroxine levels, was
noted in the groups receiving 100 and 250 mg/kg bw/day. There was
evidence in the mid- and highest dose groups of an early, transient
effect on the adrenal cortex before sexual maturation of the F1
males, which took the form of cytomegaly of the cells of the zona
BHT has been shown to induce hepatocellular necrosis and
proliferation in male Wistar rats at doses higher than those used in
either of these long-term studies and which exceeded the maximum
tolerated dose. Sublethal oral doses of 1000 or 1250 mg/kg bw/day for
4 days induced hepatocellular necrosis in the centrliobular region
within 48 hours. When a lower dose of BHT (500 mg/kg bw/day) was
administered for periods of 1 to 4 weeks, allowing for enzyme
induction to occur, bile duct proliferation, hepatocellular
hyperplasia, and persistent fibrous and inflammatory cell reactions
were observed in the periportal region. The shift in the localization
of the damage from one area of the liver to another suggested the
involvement of inducible hepatic drug-metabolizing enzymes in the
production of reactive metabolites.
In view of the probable involvement of hepatic enzyme induction
in the development of the hepatocellular damage associated with
repeated doses of BHT, the Committee concluded that, in this case,
enzyme induction was the most sensitive index of effects on the liver.
A well-defined threshold was demonstrated at 100 mg/kg bw/day in the
long-term study reviewed for the first time at this meeting, giving a
NOEL of 25 mg/kg bw/day. Effects observed in the reproduction segments
of the in utero/lifetime exposure studies were also taken into
account in the derivation of this NOEL. The Committee used a safety
factor of 100 to allocate an ADI of 0-0.3 mg/kg bw for BHT.
ADAMSON, I.Y.R., BOWDEN, D.H., COTE, M.G. & WITSHI, H. (1977).
Lung injury induced by butylated hydroxytoluene: cytodynamic and
biochemical studies in mice. Lab. Invest., 36: 26-32.
AKAGI, M. & AOKI, I. (1962a). Chem. Pharm. Bull. (Tokyo), 10: 101.
AKAGI, M. & AOKI, I. (1962b). Studies on food additives. VIII
metabolism of alpha-hydroxy-2,6-di- tert-butyl-p-cresol. Isolation of
metabolites. Chem. Pharm. Bull. (Tokyo), 10: 200-204.
ALLEN, J.R. (1976). Long-term antioxidant exposure effects on female
primates. Arch. Environ. Health, 31: 47-50.
ALLEN, I.R. & ENGBLOM, J.F. (1972). Ultrastructural and biochemical
changes in the liver of monkeys given butylated hydroxytoluene and
butylated hydroxyanisole. Food Cosmet. Toxicol., 10: 769-779.
AMES, SR., LUDWIG, M.I, SWANSON, W.J. & HARRIS, P.L. (1956). Proc.
Soc. Exp. Biol. (N.Y.), 93: 39.
AOKI, I. (1962). Chem. Pharm. Bull. (Tokyo), 10: 105.
ARCHER, D.L., SMITH, B.G. & BUKOVIC-WESS, J.A. (1978). Use of an
in vitro antibody-producing system for recognizing potentially
immunosuppressive compounds, Int. Arch. Allergy Appl. Immunol.,
BIBRA. (1977). British Industrial Biological Research Association. BHT
and lung tumours. BIBRA information Bulletin, 17(2): 88.
BLUMENTHAL, E.J., & MALKINSON, A.M. (1987). Changes in pulmonary
calpain activity following treatment of mice with butylated
hydroxytoluene. Arch. Biochem. Biophys., 256(1): 19-28.
BOLTON, J.L. & THOMPSON, J.A. ( 1991). Oxidation of butylated
hydroxytoluene to toxic metabolites. Factors influencing hydroxylation
and quinone methide formation by hepatic and pulmonary microsomes.
Drug Metab. Dispos., 19(2): 467-472.
BOLTON, J.L., SEVESTRE, H., IBE, B.O. & THOMPSON, J.A. (1990).
Formation and reactivity of alternative quinone methides from buylated
hydroxytoluene: Possible explanation for species-specific
pneumotoxicity. Chem. Res. Toxicol., 3: 65-70.
BOLTON, J.L., THOMPSON, J.A., ALLENTOFF, A.J., MILEY, F.B. & MALINSON,
A.M. (1993). Metabolic activation of butylated hydroxytoluene by mouse
bronchiolar Clara cells. Toxicol. Appl. Pharmacol., 123: 43-49.
BOMHARD, E.M., BREMMER, J.N. & HERBOLD, B.A. (1992). Review of the
mutagenicity/genotoxicity of butylated hydroxytoluene. Mutat. Res.,
BOTHAM, C.M., CONNING, D.M., HAYES, J., LITCHFIELD, M.H. & McELLIGOTT,
T.F. (1970). Effects of butylated hydroxytoluene on the enzyme
activity and ultrastructure of rat hepatocytes. Food Cosmet.
Toxicol., 8: 1-8.
BRANEN, A.L., RICHARDSON, T., GOEL, M.C. & ALLEN, J. R. (1973). Lipid
and enzyme changes in the blood and liver of monkeys given butylated
hydroxytoluene and butylated hydroxyanisole. Food Cosmet. Toxicol.,
BRIGGS, D., LOK, E., NERA, E.A., KARPINSKI, K. & CLAYSON, D.B. (1989).
Short-term effects of butylated hydroxytoluene on the Wistar rat
liver, urinary bladder and thyroid gland. Cancer Letters, 46: 31-36.
BROOKS, T.M., HUNT, P.F., THORPE, E. & WALKER, A.I.T. (1976). Effects
of prolonged exposure of mice to butylated hydroxytoluene. Unpublished
report from Shell Research, Ltd., Tunstell Lab., Sittingbourne, Kent,
U.K submitted to the World Health Organization by the authors.
BROWN, W.D., JOHNSON, A.R. & O'HALLORAN, M.W. (1959). Aust. J. Exp.
Biol. Med. Sci., 37: 533.
BRUNNER, R., VORHEES, C. & BUTCHER, K. (1978). Psychotoxicity of
selected food additives and related compounds. Report prepared under
FDA contract 223-75-2030.
BRUSICK, D. (1975). Mutagenic evaluation of compound FDA 71-25:
butylated hydroxytoluene (IONOL). Unpublished report from Litton
Biometrics, Inc., Kensington, Md., U.S. submitted to the World Health
Organization by the U.S. Food and Drug Administration.
BUDUNOVA, I.V., MITTELMAN, L.A. & BELITSKY, G.A. (1989).
Identification of tumor promoters by their inhibitory effect on
intercellular transfer of lucifer yellow. Cell. Biol. Toxicol.,
BURROWS, C.M., CUMMING, D.M., GARTLAND, C.J. & LITCHFIELD, M.H.
(1972). Topanol(R) 354 (BHT and BHA): Comparison of biochemical and
ultrastructural effects on rat hepatocytes. Unpublished report
(HO/IH/P49) from ICI Special Centre, Toxicology Bureau, submitted to
the World Health Organization by the Imperial Chemical Industries
Ltd., Alderley Park, Cheshire, U.K.
CARUBELLI, R. & McCAY, P.B. (1987). Dietary butylated hydroxytoluene
protects cytochrome P-450 in hepatic nuclear membranes of rats fed
2-acetylaminofluorene. Nutr. Cancer, 10: 145-148.
CARUBELLI, R. & McCAY, P.B. (1989). Hepatic nuclear envelope
cytochrome P-450 in rats fed 2-acetylaminofluorene. Effect of dietary
fats and butylated hydroxytoluene. Cancer Lett., 47: 83-89.
CHIPMAN, J.K, & DAVIES, J.E. (1988). Reduction of 2-acetylamino-
fluorene-induced unscheduled DNA synthesis in human and rat
hepatocytes by butylated hydroxytoluene. Mutat. Res.,
CLAPP, N.K. & SATTERFIELD, L.C. (1975). Modification of radiation
lethality by previous treatment with butylated hydroxytoluene.
Radiation Res., 64: 388-392.
CLAPP, N.K., TYNDALL, R.L. & CUMMING, R.B. (1973). Hyperplasia of
hepatic bile ducts in mice following long-term administration of
butylated hydroxytoluene. Food Cosmet. Toxicol., 11: 847.
CLAPP, N.K., TYNDALL, R.L. CUMMING, R.B. & OTTEN J.A. (1974). Effects
of butylated hydroxytoluene alone or with diethylnitrosamine in mice.
Food Cosmet. Toxicol., 12: 367-371.
CLAPP, N.K., SATTERFIELD, L.C. & KLIMA, W.C. (1975). Modification of
diethylnitrosamine lung tumorigenesis by concomitant treatment with
butylated hydroxytoluene. Unpublished report from Oak Ridge National
Lab., Oak Ridge, Tenn., USA, submitted to the World Health
Organization by Eastman Chemical Product, Inc., Kingsport, Tenn., USA.
CLAYSON, D.B., IVERSON, F., NERA, E.A. & LOK, E. (1993). The
importance of cellular proliferation induced by BHA and BHT. Toxicol.
Industr. Health, 9(1-2): 231-242.
CLEGG, D.J. (1965). Absence of teratogenic effect of butylated
hydroxyanisole (BHA) and butylated hydroxytoluene (BHT) in rats and
mice. Food Cosmet. Toxicol., 3: 387-403.
COHEN, L.A., POLANSKY, M., FURUYA, K., REDDY, M., BERKE, B.
& WEISBURGER, J.H. (1984). Inhibition of chemically induced
mammary carcinogenesis in rats by short-term exposure to BHT:
Interrelationships among BHT concentration, carcinogen dose, and diet.
J. Natl. Cancer Inst., 72: 165-174.
COHEN, L.A., CHOI, K., NUMOTO, S., REDDY, M., BERKE, B. & WEISBURGER,
J.H. (1986). Inhibition of chemically induced mammary carcinogenesis
in rats by long-term exposure to butylated hydroxytoluene (BHT):
interrelations among BHT concentration, carcinogen dose, and diet.
J. Natl. Cancer Inst., 76(4): 721-730.
COLLINGS, A.J. & SHARRATT, M. (1970). The BHT content of human adipose
tissue. Food Cosmet. Toxicol., 8: 409-412.
CONACHER, H.B., IVERSON, F., LAU, P.Y., & PAGE, B.D. (1986). Levels
of BHA and BHT in human and animal adipose tissue: interspecies
extrapolation. Food Chem. Toxicol., 24: 1159-1162.
CONNING, D.M., KIRCH, D.A. & STYLES, J.A. (1969). The toxicity of BHT
and several oxidation products in vivo and in vitro. Unpublished
report (IHR/260) from the Industrial Hygiene Research Labs., Alderley
Park, Cheshire, U.K., submitted to the World Health Organization by
the Imperial Chemical Industries, Ltd.
COTTRELL, S., ANDREWS, C.M., CLAYTON, D. & POWELL, C.J. (1994). The
dose-dependent effect of BHT (butylated hydroxytoluene) on vitamin
K-dependent blood coagulation in rats. Food Chem. Toxicol.,
CRAMPTON, R.F., GRAY, T.J., GRASSO, P. & PARKE, D.V. (1977). Long-term
studies on chemically induced liver enlargement in the rat. I.
Sustained induction of microsomal enzymes with absence of liver damage
on feeding phenobarbitone or butylated hydroxytoluene. Toxicology,
CREAVEN, P.J., DAVIES, W.H. & WILLIAMS, R.T. (1966). The effect of
butylated hydroxytoluene, butylated hydroxyanisole and octyl gallate
upon liver weight and biphenyl 4-hydroxylate activity in the rat.
J. Pharm Pharmacol., 18: 485.
CUMMING, R.B. & WALTON, M.F. (1973). Modification of the acute
toxicity of mutagenic and carcinogenic chemicals in the mouse by
prfeeding with antioxidants. Food Cosmet. Toxicol., 11: 547-553.
DACRE, J.C. (1961). Biochem. J., 78: 758.
DANIEL, J.W. & GAGE, J.C. (1965). The absorption and excretion of
butylated hydroxytoluene (BHT) in the rat. Food Cosmet. Toxicol.,
DANIEL, J.W., GAGE, J.C., JONES, D.I. & STEVENS, M.A. (1967).
Excretion of butylated hydroxyoluene (BHT) and butylated
hydroxyanisole (BHA) by man. Food Cosmet. Toxicol., 5: 475-479.
DANIEL, J.W., GAGE, I.C. & JONES, D.I. (1968). The metabolism of
3,5-di- tert-butyl-4-hydroxytoluene in the rat and in man.
Biochem. J., 106: 783-790.
DAUGHERTY, J.P., DAVIS, S. & YIELDING, K.L. (1978). Inhibition
by butylated hydroxytoluene of excision repair synthesis and
semiconservative DNA synthesis. Biochem. Biophys. Res. Commun.,
DAY, A.J., JOHNSON, A.R., O'HALLORAN, M.W & SCHWARTZ, C.J. (1959).
Aust. J. Exp. Biol. Med. Sci., 37: 295.
DEERBERG, F., RAPP, K.G., PITTERMANN, W. & REHM, S. (1980). Zum
tumorspektrum der Han: Wis-Ratte. [Tumour spectrum of the Han:WIST
rat] Z. Versuchstierk, 22: 267-280.
DEICHMANN, W.B., CLEMMER, J.J., RAKOCZY, R. & BIANCHINE, J. (1955).
A.M.A. Arch. Industr. Hlth., 11: 93.
DENZ, F.A. & LLAURADO, I.G. (1957). Brit. J. Exp. Path., 38: 515.
DERTINGER, S.D., TOROUS, D.K. & TOMETSKO, A.M. (1993). In vitro
system for detecting non-genotoxic carcinogens. Environ. Molecular
Mutagen., 21: 332-338.
DISSANAYAKE, M. & POWELL, S.M. (1989). Allergic contact dermatitis
from BHT in leg ulcer patients. Contact Dermatitis, 21: 195.
FABER, W. (1990). Hemorrhagic effects of butylated hydroxytoluene
(BHT). Unpublished report. Submitted to WHO by the BHT Special Program
Panel, Chemical Manufacturers Association, Washington, D.C., USA.
FEUER, G., GAUNT, I.F., GOLBERG, L. & FAIRWEATHER, F.A. (1965). Liver
response tests. VI Application to comparative study of food
antioxidants and hepatotoxic agents. Food Cosmet. Toxicol.,
FLYVHOLM, M.-A. & MENNÉ, T. (1990). Sensitizing risk of butylated
hydroxytoluene based on exposure and effect data. Contact Dermatitis,
FRAWLEY, J.P., KAY, J.H. & CALANDRA, J.C. (1965a). The residue of
butylated hydroxytoluene (BHT) and metabolites in tissue and eggs of
chickens fed diets containing radioactive BHT. Food Cosmet. Toxicol.,
FRAWLEY, J.P., KOHN. F.E., KAY, J.H. & CALANDRA, J.C. (1965b).
Progress report n multigeneration reproduction studies in rats fed
butylated hydroxytoluene (BHT). Food Cosmet. Toxicol., 3: 377-386.
FRIEDMAN, F.K., MILLER, H., PARK, S.S., GRAHAM, S.A., GELBOIN, H.V. &
CARUBELLI, R. (1989). Induction of rat liver microsomal and nuclear
cytochrome P-450 by dietary 2-acetylaminofluorene and butylated
hydroxytoluene. Biochem. Pharmacol., 38(18): 3075-3081.
FUKAYAMA, M.Y. & HSIEH, D.P. (1985). Effect of butylated
hydroxytoluene pretreatment on the excretion, tissue distribution and
DNA binding of [14C]aflatoxin B1 in the rat. Food Chem. Toxicol.,
FUKUSHIMA, S., OGISO, T., KURATA, Y., HIROSE, M. & ITO, N. (1987a).
Dose-dependent effects of butylated hydroxyanisole, butylated
hydroxytoluene and ethoxyquin for promotion of bladder carcinogenesis
in N-butyl-N-(4-hydroxybutyl)nitrosamine-initiated, unilaterally
ureter-ligated rats. Cancer Lett., 34: 83-90.
FUKUSHIMA, S., SAKATA, T., TAGAWA, Y., SHIBATA, M-A., HIROSE, M. &
ITO, N. (1987b). Different modifying response of butylated
hydroxyanisole, butylated hydroxytoluene, and other antioxidants in
N,N-dibutylnitrosamine esophagus and forestomach carcinogenesis of
rats. Cancer Res., 4., 47:2113-2116.
FURUKAWA, K., MAEURA, Y., FURUKAWA, N.T., & WILLIAMS, G.M. (1984).
Induction by butylated hydroxytoluene of rat liver y-glutamyl
transpeptidase activity in comparison to expression in
carcinogen-induced altered lesions. Chem Biol. Interact.,
GABRYELAK, T., PUMO, D.E. & CHIU, J.F. (1981). Changes in
tumor-specific nuclear antigen activity in carcinogen-treated colon
by tumor promotor and carcinogen inhibitors, Cancer Res.,
GAGE, J.C. (1964). The tissue retention of 3,5-Di-t-butyl-4-hydroxy-
toluene (butylated hydroxytoluene, BHT). Unpublished report
(No. IHR/157) from the Industrial Hygiene Research Labs., Alderley
Park, Cheshire, U.K., submitted to the World Health Organization by
the Imperial Chemical Industries, Ltd., U.K.
GAUNT, I.F., FEUER, G., FAIRWEATHER, F.A. & GILBERT, D. (1965a). Liver
response tests. IV. Application to short-term feeding studies with
butylated hydroxytoluene (BHT) and butylated hydroxyanisole (BHA).
Food Cosmet. Toxicol., 3: 433-443.
GAUNT, I.F., GILBERT, D. & MARTIN, D. (1965b). Liver response tests.
V. Effect of dietary restriction on a short-term feeding study with
butylated hydroxytoluene (BHT). Food Cosmet. Toxicol., 3: 445-456.
GEYER, H., SCHEUNERT, I. & KORTE, F. (1986). Bioconcentration
potential of organic environmental chemicals in humans. Regul.
Toxicol. Pharmacol., 6(4): 313-347.
GILBERT, D. & GOLBERG, L. (1965). Food Cosmet. Toxicol., 3: 417.
GILBERT, D. & GOLBERG, L. (1967). BHT oxidase. A liver-microsomal
enzyme induced by the treatment of rats with butylated hydroxytoluene.
Food Cosmet. Toxicol., 5: 481-490.
GOATER, T.O., KENYON, A.J. & & HURST, E.W. (1964). The subacute
toxicity of Topanol(R) BHT. Unpublished report from the Industrial
Hygiene Research Labs., Alderley Park, Cheshire, U.K., submitted to
the World Health Organization by the Imperial Chemical Industries
GOODMAN, D.L., McDONNELL, J.T., NELSON, H.S., VAUGHAN, T.R. &
WEBER, R.W. (1990). Chronic urticaria exacerbated by the antioxidant
food preservatives, butylated hydroxyanisoie (BHA) and butylated
hydroxytoluene (BHT). J. Allergy Clin. Immunol., 86: 570-575.
GRAY, T.J., PARKE, D.V., GRASSO, P.. CRAMPTON, RF (1972). Biochemical
and pathological differences in hepatic response to chronic feeding of
safrole and butylated hydroxytoluene to rats. Biochem. J.,
HAESEN, S., DERIJCKE, T., DELEENER, A., CASTELAIN, P., ALEXANDRE, H.,
PRÉAT, V. & KIRSCH-VOLDERS, M. (1988). The influence of phenobarbital
and butylated hydroxytoluene on the ploidy rate in rat hepato-
carcinogenesis. Carcinogenesis, 9(10): 1755-1761.
HAGEMAN, G.J., VERHAGEN, H. & KLEINJANS, J.C. (1988). Butylated
hydroxyanisole, butylated hydroxytoluene and tert-butylhydroquinone
are not mutagenic in the Salmonella/microsome assay using new tester
strains. Mutat. Res., 208:207-211.
HAGIWARA, A., HIROSE, M., MIYATA, Y., FUKUSHIMA, S. & ITO, N. (1989).
Modulation of N-butyl-N-(4-hydroxybutyl)nitrosamine-induced rat
urinary bladder carcinogenesis by post-treatment with combinations of
three phenolic antioxidants. J. Toxicol. Pathol., 2: 33-39.
HAMMOCK, B.D. & OTA, K. (1983). Differential induction of cytosolic
epoxide hydrolase, microsomal epoxide hydrolase and glutathione
S-transferase activities. Tox. Appl. Pharmacol., 71: 254-265.
HANNUKSELA, M. & LAHTI, A. (1986). Peroral challenge tests with food
additives in urticaria and atopic dermatitis, Int. J. Dermatol.,
HARMAN, D. (1968). Free radical theory of aging: effect of free
radical reaction inhibitors on the mortality rate of male LAF mice.
J. Gerontol., 23: 476-482.
HERMANN, R.S, KORANSKY, W., LEBERL, C. & NOACK, G. (1971). Hyperplasia
and hypertrophy of rat liver induced by hexachloro-cyclohexane and
butylhydroxytoluene. Retention of the hyperplasia during involution of
the enlarged organ. Virchows Arch. B. Zellpath., 9: 125-134.
HIRAGA, K. (1978). Life-span oral toxicity study of 3,5-di- tert-
hydroxytoluene (BHT) in rats. Ann. Rep. Tokyo Metropolitan Research
Lab. Public Health, 32: 83.
HIRAI, K., YAMAUCHI, M., WITSCHI, H, & COTE, M.G. (1983).
Disintegration of lung peroxisomes during differentiation of type II
cells to type I cells in butylated hydroxytoluene-administered mice.
Exper. Mol. Pathal., 39: 129-138.
HIROSE, M., SHIBATA, M., HAGIWARA, A., IMAIDA, K & ITO, N. (1981).
Chronic toxicity of butylated hydroxytoluene in Wistar rats.
Food Cosmet. Toxicol., 19: 147-151.
HIROSE, M., MASUDA, A., KURATA, Y., IKAWA, E., MERA, Y. & ITO, N.
(1986). Histologic and autoradiographic studies on the forestomach of
hamsters treated with 2- tert-butylated hydroxyanisole, 3- tert-
butylated hydroxyanisole, crude butylated hydroxyanisole, or butylated
hydroxytoluene. J. Natl. Cancer Inst., 76(1): 143-147.
HIROSE, M., MASUDA, A., IMAIDA, K., KAGAWA, M., TSUDA, H. & ITO, N.
(1987). Induction of forestomach lesions in rats by oral
administrations of naturally occurring antioxidants for 4 weeks.
Jpn. J. Cancer. Res., 78(4): 317-321.
HIROSE, M., YADA, H., HAKOI, K. TAKAHASHI, S. & ITO, N. (1993).
Modification of carcinogenesis by alpha-tocopherol, t-butylhydro-
quinone, propyl gallate and butylated hydroxytoluene in a rat
multi-organ carcinogenesis model. Carcinogenesis, 14(11): 2359-2364.
HOLDER, G.M., RYAN, A.J., WATSON, T.R. & WIEBE, L.I. (1970a). The
biliary metabolism of butylated hydroxytoluene and its derivatives in
the rat. J. Pharm. Pharmacol., 22: 832-838.
HOLDER, G.M., RYAN, A.J., WATSON, T.R. & WIEBE, L.I. (1970b). The
metabolism of butylated hydroxytoluene in man. J. Pharm. Pharmacol.,
INTERNATIONAL AGENCY FOR RESEARCH ON CANCER (1986). Some naturally
occuring and synthetic food components, furocoumarins and ultraviolet
radiation. Lyon, (IARC Monographs on the Evaluation of Carcinogenic
Risks to Humans, Vol 40, 161-206.
IATROPOULOS, M.J., WILLIAMS, G.M., CONAWAY. C.C. (1994). Inhibition of
the action of the food-borne carcinogen aflatoxin B1 by butylated
hydroxyanisole and butylated hydroxytoluene in male rats. Unpublished
report to ILSI Research Foundation, 77 pp.
IMAIDA, K., FUKUSHIMA, S., SHIRAI, T., OHTANI, M., NAKANISHI, K. &
ITO, N. (1983). Promoting activities of BHA and BHT on 2-stage urinary
bladder carcinogenesis and inhibition of gamma-glutamyl transpeptidase-
positive foci development in the liver of rats. Carcinogenesis,
IMAIDA, K., FUKUSHIMA, S., SHIRAI, T., MASUI, T., OGISO, T. & ITO, N.
(1984). Promoting activities of BHA, BHT and sodium-L-ascorbate on
forestomach and urinary bladder carcinogenesis initiated with
methylnitrosourea in F-344 male rats. Gann, 75: 769-775.
IMAIDA, K., FUKUSHIMA, S., INOUE, K., MASUI, T., HIROSE, M. & ITO, N.
(1988). Modifying effects of concomitant treatment with butylated
hydroxyanisole or butylated hydroxytoluene on N,N-dibutylnitrosamine-
induced liver, forestomach and urinary bladder carcinogenesis in F344
male rats. Cancer Lett., 43: 167-172.
INAI, K., KOBUKE, T., NAMBU, S., TAKEMOTO, T., KOU, E., NISHINA, H.,
FUJIHARA, M., YONEHARA, S., SUEHIRO, S. & TSUYA, T. (1988).
Hepatocellular tumorigenicity of butylated hydroxytoluene administered
orally to B6C3F1 mice. Jpn. J. Cancer Res., 79(1): 49-58.
JOHNSON, A.R. & HEWGILL, F.R. (1961). Aust. J. Exp. Biol. Med. Sci.,
JOHNSON, A.R. & HOLDSWORTH, E.S (1968). J. Nutr. & Diet., 5: 147.
JOHNSON, A.R, (1965). A re-examination of the possible teratogenic
effects of butylated hydroxytoluene (BHT) and its effect on the
reproductive capacity of the mouse. Food Cosmet. Toxicol.,
JOSEPHY, P.D., CARTER, M.H., & GOLDBERG, M.T. (1985). Inhibition of
benzidine mutagenesis by nucleophiles: a study using the Ames test
with hamster hepatic S9 activation. Mut. Res., 143: 5-10.
KASHFI, K., YANG, E.K., CHOWDHURY, J.R., CHOWDHURY, N.R., DANNENBERG,
A.J. (1994). Regulation of uridine diphosphate glucuronosyltransferase
expression by phenolic antioxidants. Cancer Res., 54: 5856-5859.
KARPLYUK, I.A. (1959). Vop. Pitan., 18: 24.
KAWANO, S., NAKAO, T & HIRAGA, K. (1981). Strain differences in
butylated hydroxytoluene-induced deaths in male mice. Tox. Appl.
Pharmacol., 61: 475-479.
KEHRER, J.P. & DIGIOVANNI, J. (1990). Comparison of lung injury
induced in 4 strains of mice by butylated hydroxytoluene. Taxicol.
Lett., 52: 55-61.
KENNEDY, G., FANCHET, O.E. & CALANDRA, J.C. (1966). Three-generation
reproduction study in albino rats. Butylated Hydroxytoluene. Final
Report. Unpublished report from Bio-Test Labs., Inc., Northbrook,
Ill., USA, submitted to the World Health Organization by Hercules,
Inc., Wilmington, Delaware, USA.
KING, M.M., MCCAY, P.B. & KOSANKE, S.D. (1981). Comparison of the
effects of butylated hydroxytoluene on N-nitrosomethylurea and
7,12-dimethylbenz[a]-anthracene-induced mammary tumours, Cancer
Letters, 14: 219-226.
KITCHIN, K.T. & BROWN, J.L. (1987). Biochemical effects of two
promoters of hepatocarcinogenesis in rats Food Chem. Toxic.,
KLEIN, A. & BRUSER, B. (1992). The effect of butylated hydroxytoluene
with and without cortisol, on stimulated lymphocytes. Life Sciences,
KRASAVAGE, W.J. (1984). The lack of effect of tertiary butylhydro-
quinone on prothrombin time in male rats. Drug Chem Toxicol.,
LADOMERY, L.G., RYAN, A.J. & WRIGHT, S.E. (1963). J. Pharm.
Pharmacol., 15: 771
LADOMERY, L.G., RYAN, A.J. & WRIGHT, S.E. (1967a). The excretion of
[14C] butylated hydroxytoluene in the rat. J. Pharm. Pharmacol.,
LADOMERY, L.G., RYAN, A.J. & WRIGHT, S.E. (1967b). The biliary
metabolite of butylated hydroxytoluene in the rat. J. Pharm.
Pharmacol., 19: 388-394.
LAKE, B.G., LONGLAND, R.C., GANGOLLI, S.D. & LLOYD, A.G. (1976). The
influence of some foreign compounds on hepatic xenobiotic metabolism
and the urinary excretion of D-glucuronic acid metabolites in the rat.
Toxicol. Appl. Pharmacol., 35:113-122.
LARSEN, J.C. & TARDING, F. (1978). Stimulation of DNA synthesis in
mouse and rat lung following administration of butylated
hydroxytoluene. Archives of Toxicol. Suppl., 1: 147-150.
LINDENSCHMIDT, R.C., TRYKA. A.F, GOAD, M.E., & WITSCHI, H.P. (1986).
The effects of dietary BHT on liver and colon tumor development in
mice. Toxicology, 38:151-160.
LINDENSCHMIDT, R.C., TRYKA, A.F. & WITSCHI, H. (1987). Modification of
gastrointestinal tumor development in rats by dietary butylated
hydroxytoluene. Fundam. Appl. Toxicol., 8(4): 474-481.
MAEURA, Y. & WILLIAMS, G.M. (1984). Enhancing effect of butylated
hydroxytoluene on the development of liver altered foci and neoplasms
induced by N-2-fluorenylacetamide in rats. Food Chem. Toxicol.,
MAEURA, Y., WEISBURGER, J.H. & WILLIAMS, G.M. (1984). Dose-dependent
reduction of N-2-fluorenylacetamide-induced liver cancer and
enhancement of bladder cancer in rats by butylated hydroxytoluene.
Cancer Res., 44: 1604-1610.
MALKINSON, A.M. (1979). Prevention of butylated hydroxytoluene-induced
lung damage in mice by cedar terpene administration. Pre-print of
paper accepted for publication in Toxicol. Appl. Pharmacol.,
MALKINSON, A.M. (1991). Genetic studies on lung tumor susceptibility
and histogenesis in mice. Environ. Health Perspect., 93: 149-159.
MALKINSON, A.M. & THAETE, L.G. (1986). Effects of strain and age on
prophylaxis and co-carcinogenesis of urethane-induced mouse lung
adenomas by butylated hydroxytoluene. Cancer. Res., 46: 1694-1697.
MALKINSON, A.M., THAETE, L.G., BLUMENTHAL, E.J. & THOMPSON, J.A.
(1989). Evidence for a role of tert-butyl hydroxylation in the
induction of pneumotoxicity in mice by butylated hydroxytoluene.
Toxicol. Appl. Pharmacol., 101: 196-204.
MATSUO, M., MIHARA, K., OKUNO, M., OHKAWA, B., & MIYAMOTO, J. (1984).
Comparative metabolism of 3,5-di- tert-butyl-4-hydroxytoluene (BHT)
in mice and rats. Food Chem. Toxicol., 22: 345-354.
McCARTHY, D.J., LINDAMOOD, C., GUNDBERG, C.M. & HILL, D.L. (1989).
Retinoid-induced hemorrhaging and bone toxicity in rats fed diets
deficient in vitamin K. Toxicol. Appl. Pharmacol., 97: 300-310.
McCORMICK, D.L., MAJOR, N., & MOON, R.C. (1984). Inhibition of
7,12-dimethylbenz(a)anthracene-induced rat mammary carcinogenesis by
concomitant or postcarcinogen antioxidant exposure. Cancer Res.,
McCORMICK, D.L., MAY, C.M., THOMAS, C.F. & DETRISAC, C.J. (1986).
Anticarcinogenic and hepatotoxic interactions between retinyl acetate
and butylated hydroxytoluene in rats. Cancer Res., 46: 5264-5269.
MEYER, O. & HANSEN, E. (1980). Behavioural and developmental effects
of butylated hydroxytoluene dosed to rats in utero and in the
lactation period. Toxicology, 16: 247-258.
MEYER, O.A., KRISTIANSEN, E. & WURTZEN, G. (1989). Effects of dietary
protein and butylated hydroxytoluene on the kidneys of rats.
Lab. Anim., 23: 175-179.
MIZUTANI, T., ISHIDA, I., YAMANOTOK, K. & TAJIMA, K. (1982). Pulmonary
toxicity of butylated hydroxytoluene and related alkylphenols:
Structural requirements for toxic potency in mice. Toxicol. Appl.
Pharmacol., 62: 273-281.
MIZUTANI, T., YAMAMOTO, K. & TAJIMA, K. (1983). Isotope effects on the
metabolism and pulmonary toxicity of butylated hydroxytoluene in mice
by deuteration of the 4-methyl group. Toxicol. Appl. Pharmacol.,
MIZUTANI, T., NOMURA, H., NAKANISHI, K. & FUJITA, S. (1987).
Hepatotoxicity of butylated hydroxytoluene and its analogs in mice
depleted of hepatic glutathione. Toxicol. Appl. Pharmacol.,
NAGAI, F., USHIYAMA, K. & KANO, I. (1993). DNA cleavage by metabolites
of butylated hydroxytoluene. Arch. Toxicol., 67: 552-557.
NAKAGAWA, Y. (1987). Effects of buthionine sulfoximine and cysteine on
the hepatotoxicity of butylated hydroxytoluene in rats. Toxicol.
Lett., 37: 251-256.
NAKAGAWA, Y. & TAYAMA, K. (1988). Nephrotoxicity of butylated
hydroxytoluene in phenobarbital-pretreated male rats. Arch. Toxicol.,
NCI (1979) National Cancer Institute. Bioassay of butylated
hydroxytoluene (BHT) for possible carcinogenicity. DHEW Report
No. NIH 79-1706. Technical Report Series No. 150.
NIEVEL, J.G. (1969). Effect of coumarin, BHT and phenobarbitone on
protein synthesis in the rat liver. Food Cosmet. Toxicol.,
OKINE, L.K., LOWE, M.C., MIMNAUGH, E.G., GOOCHEE, J.M. & GRAM, T.E.
(1986). Protection by methylprednisolone against butylated
hydroxytoluene-induced pulmonary damage and impairment of microsomal
monooxygenase activities in the mouse: lack of effect on fibrosis.
Exp. Lung Res., 10: 1-22.
OLSEN, P., GRY, J., KNUDSEN, L., MEYER, O, & POULSEN, E. (1984).
Animal feeding study with nitrite-treated meat. In: N-nitroso
compounds; Occurrence, biological effects, and relevance to human
cancer. O'Neill, I.K., von Borstel, R.C., Miller, C.T., Long, J., &
Bartsch, B. (eds.), IARC Scient. Publ. No.57: pp. 667-675.
International Agency for Research on Cancer, Lyon.
OLSEN, P., MEYER, O., BILLE, N. & WURTZEN, G. (1986). Carcinogenicity
study on butylated hydroxytoluene (BHT) in Wistar rats exposed
in utero. Food Chem. Toxicol., 24: 112.
OMAYE, S.T., REDDY, K.A. & CROSS, C.E. (1977). Effect of butylated
hydroxytoluene and other antioxidants on mouse lung metabolism.
J. Toxicol. Environ. Health, 3: 829-836.
PARTRIDGE, C.A., DAO, D.D. & AWASTHI, Y.C. (1982). Induction of
glutathione-linked detoxification system by dietary antioxidants,
Fed. Proc., 41: Abstract 2152.
PERAINO, C., FRY, R.J., & STAFFELDT, E. (1973). Enhancement of
spontaneous hepatic tumorigenesis in C3H mice by dietary
phenolbarbital. J. Natl. Cancer Inst., 51: 1349-1350.
PERAINO, C., FRY, R.J., STAFFELDT, E. & CHRISTOPHER, J.P. (1977).
Enhancing effects of phenobarbitone and butylated hydroxytoluene on
2-acetylaminofluorene-induced hepatic tumorigenesis in the rat.
Food and Cosmetics Toxicol., 15: 93-96.
PETO, R., PIKE, M.C., DAY, N.E., GRAY, R.G., LEE, P.N., PARISH, S.,
PETO, J., RICHARDS, S., & WAHRENDORF, J. (1980). Guidelines for
simple, sensitive significance tests for carcinogenic effects in
long-term animal experiments. In: Long-term and Short-term Screening
Assays for Carcinogens: A Critical Appraisal. IARC Monographs on the
Evaluation of the Carcinogenic Risk of Chemicals to Humans, Suppl. 2,
pp. 311-426. International Agency for Research on Cancer, Lyon.
POWELL, C.J. & CONNOLLY, A.K. (1991). The site specificity and
sensitivity of the rat liver to butylated hydroxytoluene-induced
damage. Toxicol. Appl. Pharmacol., 108: 67-77.
POWELL, C.J., CONNELLY, J.C., JONES, S.M., GRASSO, P., BRIDGES, J.W.
(1986). Hepatic responses to the administration of high doses of BHT
to the rat: their relevance to hepatocarcinogenicity. Food. Chem.
Toxicol., 24: 1131-1143
PRASAD, O. & KAMRA O.P. (1974). Radiosensitization of Drosophila
sperm by commonly used food additives-butylated hydroxyanisole and
butylated hydroxytoluene, Int. J. Radiat. Biol., 25: 67-72.
PRÉAT, V., GERLACHE, J. DE, LANS, M., TAPER, H. & ROBERFROID, M.
(1986). Comparative analysis of the effect of phenobarbital,
dichlorodiphenyltrichloroethane, butylated hydroxytoluene and
nafenopin on rat hepatocarcinogenesis. Carcinogenesis,
PRICE, S.C. (1994). The role of hepatocellular injury in the chronic
toxicity of BHT: Two generation Wistar albino rat study. Robens
Institute, U. of Surrey, Guildford, Surrey, U.K. Study No: 1/91/Tx.
Final Report No: R193/TOX/0020. Vol. 1-8. Submitted to WHO by Robens
REDDY, B.S., HANSEN, D., MATHEWS, L., & SHARMA, C. (1983a). Effect of
micronutrients, antioxidants and related compounds on the mutagenicity
of 3,2'-dimethyl-4-aminobiphenyl, a colon and breast carcinogen
Food Chem. Toxicol., 21: 129-132.
REDDY, B.S., SHARMA, C., & MATHEWS, L. (1983b). Effect of butylated
hydroxytoluene and butylated hydroxyanisole on the mutagenicity of
3,2'-dimethyl-4-aminobiphenyl. Nutr. Cancer, 5: 153-158.
RICHER, N., MARION, M. & DENIZEAU, F. (1989) Inhibition of binding of
2-acetylaminofluorene to DNA by butylated hydroxytoluene and butylated
hydroxyanisole in vitro. Cancer Lett., 47: 211-216.
RIKANS, L.E., GIBSON, D.D., McCAY, P.B., KING, M.M. (1981). Effects of
butylated hydroxytoluene and acetylaminofluorene on NADPH-cytochrome
P-450 reductase activity in rat liver microsome, Food Cosmet.
Toxicol., 19: 89-92.
ROBENS INSTITUTE (1989). Dose ranging experiment on the role of
hepatocellular injury in the chronic toxicity of BHT. Final report
7/88/TX, Robens Institute of Health and Safety, University of Surrey,
Guildford, Surrey, United Kingdom. Unpublished report. Submitted to
WHO by European BHT Manufacturers Association (EBMA). CEFIC,
ROEBUCK, B.D., MACMILLAN, D.L., BUSH, D.M. & KENSLER, T.W. (1984).
Modulation of azaserine-induced pancreatic foci by phenolic
antioxidants in rats. J. Natl. Cancer Inst., 72: 1405-1409.
RUZZENE, M., DONELLA-DEANA, A, ALEXANDRE, A., FRANCESCONI, M.A. &
DEANA, R. (1991). The antioxidant butylated hydroxytoluene stimulates
platelet protein kinase C and inhibits subsequent protein
phosphorylation induced by thrombin. Biochim. Biophys. Acta,
SAHEB, W. & WITSCHI, H. (1975). Lung growth in mice after a single
dose of butylated hydroxytoluene. Toxicol. & Appl. Pharm.,
SATO, H., TAKAHASHI, M., FURUKAWA, F., MIYAKAWA, Y., HASEGAWA, R.,
TOYODA, K., HAYASHI, Y. (1987). Initiating potential of 2-(2-furyl)-
3-(5-nitro-2- furyl)acrylamide (AF-2), butylated hydroxyanisole (BHA),
butylated hydroxytoluene (BHT) and 3,3',4',5,7-pentahydroxyflavone
(quercetin) in two-stage mouse skin carcinogenesis. Cancer Lett.,
SHELEF, L.A. & CHIN, B. (1980) Effect of phenolic antioxidants on the
mutagenicity of aflatoxins B1. Appl. Environ. Microbiol.,
SHELLENBERGER, T.E., PARRISH, D.B. & SANFORD, P.E. (1957). Poultry
Sci., 36: 1313.
SHEU, C.W., CAIN, K.T., RUSHBROOK, C.J., JORGENSON, T.A. & GENEROSO,
W.M. (1986). Tests for mutagenic effects of ammoniated glycyrrhizin,
butylated hydroxytoluene, and gum Arabic in rodent germ cells.
Environ. Mutagen., 8(3): 357-367.
SHIBATA, M., HAGIWARA, A., MIYATA, Y., IMAIDA, K., ARAI, M. & ITO, N.
(1979). Experimental study on carcinogenicity of butylated
hydroxytoluene (BHT) in rats. Translation of the Proceedings of the
38th Annual Meeting of the Japanese Cancer Assoc., Tokyo, September
SHIBATA, M.A., YAMADA, M., TANAKA, H., KAGAWA, M. & FUKUSHIMA, S.
(1989). Changes in urine composition, bladder epithelial morphology,
and DNA synthesis in male F344 rats in response to ingestion of
bladder tumour promoters. Toxicol. Appl. Pharmacol., 99: 37-49.
SHIBATA, M.-A., ASAKAWA, E.. HAGIWARA, A., KURATA, Y. & FUKUSHIMA, S.
(1991). DNA synthesis and scanning electron microscopic lesions in
renal pelvic epithelium of rats treated with bladder cancer promoters.
Toxicol. Lett., 55: 263-272.
SHIRAI, T., HAGIWARA, A., KURATA, Y., SHIBATA, M., FUKUSHIMA, S.,
ITO, N. (1982). Lack of carcinogenicity of butylated hydroxytoluene on
long-term administration to B6C3FI mice. Food. Chem. Tox.,
SHIRAI, T., FUKUSHIMA, S., OHSHIMA, M., MASUDA, A., & ITO, N. (1984).
Effects of BHA, BHT and NaCl on gastric carcinogenesis initiated with
N-methyl-N'-nitro-N-nitrosoguanidine in F-344 rats. J. Natl. Cancer
Inst., 72: 1189-1198.
SHIRAI, T., IKAWA, E., HIROSE. M., THAMAVIT, W., & ITO, N. (1985).
Modification by five antioxidants of 1,2-dimethylhydrazine-initiated
colon carcinogenesis in F-344 rats. Carcinogenesis, 6: 637-639.
SHIRAI, T., FUKUSHIMA, S., KAWABE, M., SHIBATA, M.-A., IWASAKI, S.,
TADA, M. & ITO, N. (1991). Selective induction of rat urinary bladder
tumors by simultaneous administration of 3,2'-dimethyl-4-aminobiphenyl
(DMAB) and butylated hydroxyanisole or butylated hydroxytoluene is
associated with increased DMAB-DNA adduct formation. Carcinogenesis,
SINGLETARY, K.W. & NELSHOPPEN, J.M. (1991). Selective in vivo
inhibition of rat mammary 7,12-dimethylbenz[alpha]anthracene - DNA
adduct formation by dietary butylated hydroxytoluene. Carcinogenesis,
SINGLETARY, K.W., NELSHOPPEN, L.M., SCARDEFIELD, S. & WALLIG, M.
(1992). Inhibition by butylated hydroxytoluene and its oxidative
metabolites of DMBA-induced mammary tumorigenesis and of mammary
DMBA-DNA adduct formation in vivo in the female rat. Food Chem.
Toxicol., 30(6): 455-465.
SOLLEVELD, H.A., HASEMAN, J.K., & MCCONNELL, E.E. (1984). Natural
history of body weight gain, survival and neoplasia in the F344 rat.
J. Natl. Cancer Inst., 72: 929-940.
SONDERGAARD, D. & OLSEN, P (1982). The effect of butylated
hydroxytoluene (BHT) on the rat thyroid. Toxicology Letters,
SPORN, A. & SCHOBESCH, O. (1961). Igiena (Bucharest), 9: 113.
S.R.I. Stanford Research Institute (1972). Report 14 submitted to U.S.
Food and Drug Administration.
STOKES, J.D. & SCUDDER, C.L. (1974). The effect of butylated
hydroxyanisole and butylated hydroxytoluene on behavioral development
of mice. Devel. Psychobiol., 7: 343-350.
SUZUKI, H., NAKAO, T. & HIRAGA, K. (1983). Vitamin K content of liver
and faeces from vitamin K-deficient and butylated hydroxytoluene
(BHT)-treated male rats. Toxicol. Appl. Pharmacol., 67: 152-155.
TAFFE, B.G. & KENSLER, T.W. (1988). Tumor promotion by a hydroperoxide
metabolite of butylated hydroxytoluene, 2,6-di- tert-butyl-4-
hydroperoxy-4-methyl-2,5-cyclohexadienone, in mouse skin. Res. Commun.
Chem. Pathol. Pharmacol., 61(3): 291-303.
TAFFE, B.G., ZWEIER, J.L., PANNELL, L.K. & KENSLER, T.W. (1989).
Generation of reactive intermediates from the tumor promoter butylated
hydroxytoluene hydroperoxide in isolated murine keratinocytes or by
hematin. Carcinogenesis, 10(7): 1261-1268.
TAKAHASHI, O. (1986). Feeding of butylated hydroxytoluene to rats
caused a rapid decrease in blood coagulation factors II (prothrombin),
VII, IX and X. Arch. Toxicol., 58(3): 177-181.
TAKAHASHI, O. (1987). Decrease in blood coagulation factors II
(prothrombin), VII, IX and X in the rat after a single oral dose of
butylated hydroxytoluene. Fd. Chem. Toxicol., 25(3): 219-224.
TAKAHASHI, O.(1990). Gastric retention and delayed absorption of a
large dose of butylated hydroxytoluene in the rat. Xenobiotica,
TAKAHASHI, O. (1991). Some properties of rat platelet aggregation and
effects of butylated hydroxytoluene, warfarin and aspirin. Food Chem.
Toxicol., 29(3): 173-183.
TAKAHASHI, O. (1992). Haemorrhages due to defective blood coagulation
do not occur in mice and guinea-pigs fed butylated hydroxytoluene, but
nephrotoxicity is found in mice. Food Chem. Toxicol., 30(2): 89-97.
TAKAHASHI, O. & HIRAGA, K. (1978a). Dose-response study of hemorrhagic
death by dietary butylated hydroxytoluene (BHT) m male rats. Tox.
Appl. Pharm., 43: 399-406.
TAKAHASHI, O. & HIRAGA, K. (1978b). Effects of low levels of butylated
hydroxytoluene on the prothrombin index of male rats. Food Cosmet.
Toxicol., 24: 16, 475-477.
TAKAHASHI, O. & HIRAGA, K. (1979). Preventive effects of phylloquinone
on hemorrhagic death induced by butylated hydroxytoluene in male rats.
J. Nutr., 109: 453-457.
TAKAHASHI, O. & HIRAGA, K (1981a). Inhibition of phylloquinone
expoxide-dependent carboxylation of microsomal proteins from rat liver
by 2,6-di- tert-butyl-4-methylene-2,5-cyclohexadienone. Food Cosmet.
Toxicol., 19: 701-706.
TAKAHASHI, O. & HIRAGA, K. (1981b). Haemorrhagic toxicosis in rats
given butylated hydroxytoluene, Acta Pharmacol. Toxicol., 49: 14-20.
TAKAHASHI, O. & HIRAGA, K. (1984). Effects of dietary butylated
hydroxytoluene on functional and biochemical properties of platelets
and plasma preceeding the occurrence of haemorrhage in rats.
Food Chem. Toxicol., 22: 97-103.
TAKAHASHI, O., HAYASHIDA, S., & HIRAGA, K. (1980). Species differences
in the haemorrhagic response to butylated hydroxytoluene.
Food Cosmet. Toxicol., 18: 229-235.
TAKAHASHI M., FURUKAWA F., TOYODA, K., SATO, H., HASEGAWA, R. &
HAYASHI, Y. (1986). Effects of four antioxidants on N-methyl-N'-nitro-
N-nitrosoguanidine initiated gastric tumour development in rats.
Cancer Lett., 30(2): 161-168.
TANAKA, T., OISHI, S. & TAKAHASHI, O. (1993). Three generation
toxicity study of butylated hydroxytoluene administered to mice.
Toxicol. Lett., 66: 295-304.
TATSUTA, M., MIKUNI, T., & TANIGUCHI, H. (1983). Protective effect of
butylated hydroxytoluene against induction of gastric cancer by
N-methyl-N'-nitro-N-nitrosoguanidine in Wistar rats. Int. J. Cancer,
THOMPSON, D.C. & TRUSH, M.A. (1988a). Enhancement of butylated
hydroxytoluene-induced mouse lung damage by butylated hydroxyanisole.
Toxicol. Appl. Pharmacol., 96(1): 115-121.
THOMPSON, D.C. & TRUSH, M.A, (1988b). Studies on the mechanism of
enhancement of butylated hydroxytoluene-induced mouse lung toxicity by
butylated hydroxyanisole. Toxicol. Appl. Pharmacol., 96(1): 122-131.
THOMPSON, D.C., CHA, Y.N. & TRUSH, M.A (1986). The peroxidative
activation of butylated hydroxytoluene to BHT-quinone methide and
stilbenequinone. Adv. Exp. Med. Biol., 197: 301-309.
THOMPSON, J.A., MALKINSON, A.M., WAND, M.D., MASTOVICH, S.L.,
MEAD, E.W., SCHULLEK, K.M. & LAUDENSCHLAGER, W.G. (1987). Oxidative
metabolism of butylated hydroxytoluene by hepatic and pulmonary
microsomes from rats and mice. Drug Metab. Dispos., 5: 833-840.
THOMPSON, J.A., SCHULLEK, K.M., FERNANDEZ, C.A. & MALKINSON, A.M.
(1989). A metabolite of butylated hydroxytoluene with potent
tumor-promoting activity in mouse lung. Carcinogenesis,
THORNTON, M., MOORE, M.A. & ITO, N. (1989). Modifying influence of
dehydroepiandrosterone or butylated hydroxytoluene treatment on
initiation and development stages of azaserine-induced acinar
pancreatic preneoplastic lesions in the rat. Carcinogenesis,
TOKUMO, K., IATROPOULOS, M.J. & WILLIAMS, G.M. (1991). Butylated
hydroxytoluene lacks the activity of phenobarbital in enhancing
diethylnitrosamine-induced mouse liver carcinogenesis. Cancer Lett.,
TYE, R., ENGEL, J.D. & RAPIEN, I. (1965). Summary of toxicological
data. Disposition of butylated hydroxytoluene (BHT) in the rat.
Food Cosmet Toxicol., 3: 547-551.
TYNDALL, R.L., COLYER, S. & CLAPP, N. (1975). Early alterations in
plasma esterases with associated pathology following oral
administration of diethylnitrosamine and butylated hydroxytoluene
singly or in combination, Int. J. Cancer, 16: 184-191.
ULLAND, B.M., WEISBURGER, J.H., YAMAMOTO, R.S., WEISBURGER, E.K.
(1973). Antioxidants and carcinogenesis: butylated hydroxytoluene, but
not diphenyl-p-phenyl-enediamine, inhibits cancer induction by
N-2-fluorenylacetamide and by N-hydroxy-N-2-fluorenyl acctamide in
rats Food Cosmet. Toxicol., 11: 199-207.
VAN STRATUM, P.G. & VOS, H.J. (1965). The transfer of dietary
butylated hydroxytoluene (BHT) into the body and egg fat of laying
hens. Food Cosmet. Toxicol., 3: 475-477.
VERHAGEN, H., BECKER, H.H.G., COMUTH, P.A.W.V., MAAS, L.M., HOOR,
F.TEN, HENDERSON, P.T. & KLEINJANS, J.C.S. (1989). Disposition of
single oral doses of butylated hydroxytoluenc in man and in rat.
Fd. Chem. Toxicol., 27(12): 765-772.
VERSCHOYLE, R.D., WOLF, C.R. & DINSDALE, D. (1993). Cytochrome P450
2B isoenzymes are responsible for the pulmonary bioactivation and
toxicity of butylated hydroxytoluene, O,O,S-trimethylphosphorothioate
and methylcyclopentadienyl manganese tricarbonyl. J. Pharmacol. Exp.
Ther., 266(2): 958-963.
VORHEES, C.V., BUTCHER, R.E., BRUNNER, R.L., SOBOTKA, T.J. (1981).
Developmental neurobehavioral toxicity of butylated hydroxytoluene in
rats. Food Cosmet. Toxicol., 19: 153-162.
WASEEM, M. & KAW, J.L. (1994). Pulmonary effects of butylated
hydroxytoluene in mice. Food Addit. Contain., 11(1): 33-38.
WESS, J.A. & ARCHER, D.L. (1982). Evidence from in vitro murine
immunologic assays that some phenolic food additives may function as
antipromotors by lowering intracellular cyclic GMP levels. Proc. Soc.
Exp. Biol. Med., 170: 427-430.
WILLIAMS, G.M., MAEURA, Y., & WEISBURGER, J.H. (1983). Simultaneous
inhibition of liver carcinogenicity and enhancement of bladder
carcinogenicity of N-2-fluorenylacetamide by butylated hydroxytoluene.
Cancer Lett., 19: 55-60.
WILLIAMS, G.M., SHIMADA, T., McQUEEN, C., TONG, C., & VED BRAT, S.
(1984). Lack of genotoxicity of butylated hydroxyanisole (BHA) and
butylated hydroxytoluene (BHT). The Toxicologist, 4: 104.
WILLIAMS, G.M., WANG, C.X. & IATROPOULOS, M.J. (1990a). Toxicity
studies of butylated hydroxyanisole and butylated hydroxytoluene. II.
Chronic feeding studies. Food Chem. Toxicol., 28(12): 799-806.
WILLIAMS, G.M., MCQUEEN, C.A. & TONG, C (1990b). Toxicity studies of
butylated hydroxyanisole and butylated hydroxytoluene. I. Genetic and
cellular effects. Food Chem. Toxicol., 28(12): 793-798.
WILLIAMS, G.M., TANAKA, T., MARUYAMA, H., MAEURA, Y., WEISBURGER, J.H.
& ZANG, E. (1991). Modulation by butylated hydroxytoluene of liver and
bladder carcinogenesis induced by chronic low-level exposure to
2-acetylaminofluorene. Cancer Res., 51: 6224-6230.
WITSCHI, H. P. (1981). Enhancement of tumor formation in mouse lung by
dietary butylated hydroxytoluene. Toxicology, 21: 95-104.
WITSCHI, H.P. (1986). Separation of early diffuse alveolar cell
proliferation from enhanced tumour development in mouse lung. Cancer
Res., 46(6): 2675-2679.
WITSCHI, H. & COTE, M. G. (19761. Biochemical pathology of lung damage
produced by chemicals. Fed. Proc., 35(1): 89-94.
WITSCHI H.P. & KEHRER, J.P. (19821. Adenoma development in mouse lung
following treatment with possible promoting agents. J. Am. Coll.
Toxicology, 1: 171.
WITSCHI, H.P. & LOCK, S. (19791. Enhancement of adenoma formation in
mouse lung by butylated hydroxytoluene. Tox. Appl Pharm., 50: 391-400.
WlTSCHI H.P. & MORSE, C.C. (19851. Cell kinetics in mouse lung
following administration of carcinogens and butylated hydroxytoluene.
Tox. Appl. Pharm., 78: 464-472.
WITSCHI H.P., HAKKINEN, P.J. & KEHRER, J.P. (19811. Modification of
lung tumor development in A/J mice, Toxicology, 21: 37-45.
YAMAMOTO, K., TAJIMA, K, OKINO, N. & MIZUTANI, T. (19881. Enhanced
lung toxicity of butylated hydroxytoluene in mice by coadministration
of butylated hydroxyanisole. Res. Commun. Chem Pathol. Pharmacol.,
YAMAMOTO, K., TAJIMA, K., TAKEMURA, M. & MIZUTANI, T. (1991). Further
metabolism of 3,5-di- tert-butyl-4-hydroxybenzoic acid, a major
metabolite of butylated hydroxytoluene, in rats. Chem. Pharm. Bull.,
YOSHIDA, Y. (1990). Study on mutagenicity and antimutagenicity of BHT
and its derivatives in a bacterial assay. Mutation Res.,