WORLD HEALTH ORGANIZATION Toxicological evaluation of some food colours, thickening agents, and certain other substancse WHO FOOD ADDITIVES SERIES NO. 8 The evaluations contained in this publication were prepared by the Joint FAO/WHO Expert Committee on Food Additives which met in Geneva, 14-23 April 19751 World Health Organization, Geneva 1975 1 Nineteenth Report of the Joint FAO/WHO Expert Committee on Food Additives, Wld Hlth Org. techn. Rep. Ser., 1975, No. 576; FAO Nutrition Meetings Report Series, 1975, No. 55. The monographs contained in the present volume are also issued by the Food and Agriculture Organization of the United Nations, Rome, as FAO Nutrition Meetings Report Series, No. 55A ISBN 92 4 166008 2 (C) FAO and WHO 1975 TERTIARY BUTYL HYDROQUINONE (TBHQ) BIOLOGICAL DATA BIOCHEMICAL ASPECTS Metabolic studies in the rat Male and female rats, body weight 250 g, were given a single dose of TBHQ, dissolved in corn oil (10% w/w) by intubation at dose levels equivalent to 100, 200, 300, or 400 mg/kg. At the 400 mg/kg level there was a rapid onset of ataxia, followed by recovery in two or three hours. Urine samples were collected daily for three days before dosing and then for six days after dosing. At all dose levels excretion appeared to be complete in three or four days. About 66% of the dose was excreted as the o-sulfate conjugate and less than 10% as the glucuronide. At the 100 mg/kg level, urinary excretion accounted for almost all the dose. At higher levels about 33% could not be accounted for in the urine, nor be detected in the faeces. Excretion of the free TBHQ at the 100 mg/kg level was about 12% but this level decreased at the higher dose levels (2% at 400 mg/kg). No other major metabolites were detected (Astill et al., 1968). Urine samples were collected from two animals, from the 0, 0.16%, and 0.5% dietary TBHQ groups of a long-term feeding study at months 12 and 20. Sera samples were collected from groups of five rats at months six, 12, 20 and at autopsy. Samples of perirenal, omental and subcutaneous fat were removed at autopsy, pooled by sex and dose. At 12 months, males at both levels excreted about equal amounts of the conjugates in the urine (o-sulfate and o-glucuronide). About two- thirds of the excretory products in females was the o-sulfate form and the remainder the o-glucuronide. At 20 months in both male and female, most of the conjugate excreted was in the o-sulfate form with little evidence for glucuronide excretion. Only negligible amounts of TBHQ were detected in serum or fat (Astill et al., 1968). Portions of the fat of control animals and animals that had been maintained on 0.5% TBHQ were examined for stability by the active oxygen method (oxidative stability) and also for TBHQ content. There were no apparent differences in the oxidative stability of fats from treated and control animals, nor did polarographic and colorimetric methods of analysis (sensitive to 5 ppm) indicate the presence of TBHQ in the fat of test animals (Astill, 1968). In a single dose study, rats received a dose of C14-labelled TBHQ equivalent to 15, 48, 92, 383, 380, or 400 mg/kg. Urine and faeces were collected daily as was expired CO2. At the end of the test period the animals were sacrificed and blood, brain, kidneys, liver, GI tract and perirenal, omental and subcutaneous fat removed for assay. Seventy-eight to 88 per cent. of the administered radioactivity was recovered in the urine, the bulk of this being excreted within the first 24 hours (55-82.7% of the administered dose). Of the recovered radioactivity, 70-76% was in the form of the o-sulfate conjugate: 1-2% as the o-glucuronide. Faecal excretion was 2-6%. Only traces of radioactivity were detected in the tissues at the 92 mg/kg level; no values were given for the higher levels (Astill et al., 1967a). In another experiment, rats (body weight 200-250 g) were maintained on a daily diet which allowed an intake of 5.7 mg/kg (0.029% level), of TBHQ-C14 daily for 17 days. Urine and faeces were collected throughout the experiment. At the end of the test period the rats were starved overnight before sacrifice, and brain, liver, kidney, and fat samples collected. Tissue levels were as follows (mg TBHQ/g wet tissue): liver, 0.06-0.34; kidney, 0.09-0.38; brain, 0.06-0.56; fat, 0.06-0.37) (Astill et al., 1967a). Pregnant albino S-D rats 380-440 g body weight age 48 weeks were selected from the third litter of second generation females in a reproduction study and had received 0.5% of TBHQ in the diet since weaning. Animals were given one day before term an oral dose of TBHQ-C14 (40 mg/kg) as a 10% solution in corn oil. Urine and faeces were collected up to time of sacrifice (7.6-16.7 hours after dosing). Foetuses were removed by Caesarean section. The uterus, amniotic fluid, GI tract, liver, brain, kidneys, and fat specimens were collected for radioassay. About 74% of the dose was excreted in the urine in the 16.7 hour period. Only 10% of the dose was detected in the GI tract at 7.4 hours after dosing, and 8.5% at 17.6 hours. The level of radioactivity in foetuses was 0.2% of the dose at 7.6 hours and 0.02% at 16.7 hours. Similar small proportions of the dose were present in the uterus and amniotic fluid and other tissues examined. Based on these results, extrapolation to possible known exposures suggest that at the highest possible intake (0.1 mg/kg/day), the human foetus would be exposed to the order of 1% of the daily intake in the form of unchanged TBHQ and probably higher levels of the conjugate (Astill & Walton, 1968). Metabolic studies in the dog Male beagle dogs about 11 kg weight fed Purina Chow and TBHQ as a single 100 mg/kg oral dose, via ground meat capsule. Urine was collected three days before dosing and six days after dosing. Excretion was essentially complete within 48 hours. The major urinary excretory products were the o-sulfate, and o-glucuronide conjugates and a small amount of unchanged TBHQ. Total recoveries ranged from 77-98%. About two-thirds of this was as the o-sulfate and one-third as the o-glucuronide (Astill et al., 1967b). In another study, 26 male and female dogs were used. The dogs were maintained on diets containing TBHQ dissolved in corn oil at levels equivalent to 0, 0.05, 0.1, and 0.5%. Urine and serum samples were collected on day nine and one day before commencement of feeding TBHQ, and at months three, six, 12, 13 and 24 of the test period. Serum was collected 23 hours after feeding. At autopsy, performed on one dog of each sex at each dose level at 12 months, and the remaining at 24 months, samples of perirenal, omental and subcutaneous fat were removed. Chromatographic studies of the urine indicated excretion of both the o-sulfate and o-glucuronide conjugates, at all dose levels. In the case of males the o-sulfate/glucuronide ratios were 2/1, whereas in females the bulk of the conjugate was in the form of the o-sulfate. Only insignificant quantities of TBHQ were detected in the fat (in fat, maximum in males was 7 ppm, and in females 17 ppm, in most cases value was 0), and serum (0-0.7 ppm) (Astill et al., 1967). Portions of the fat from test animals and animals that had been maintained on the highest level of TBHQ (0.5%) for two years were examined for stability by the active oxygen method. There was no apparent difference in the oxidative stability of fats from treated or control animals (Anonymous, 1968a). In another study TBHQ residues were assayed in fat, brain, liver and kidney of dog and rats from the long-term feeding studies. Storage appeared to be negligible (Astill & Jones, 1969). Metabolic studies in human subjects Human subjects (male) received TBHQ under the following conditions: (1) gelatin capsule containing 150 mg TBHQ; (2) a mixture of TBHQ (2%) in corn oil and graham cracker crumbs, equivalent to a dose of 125 mg TBHQ; (3) 100 mg dissolved in cottonseed oil contained in a gelatin capsule; (4) 20 g of mixture containing TBHQ, 2% cottonseed oil and 2% confectioners sugar in graham cracker crumbs. Doses of TBHQ ranged from 20 to 70 mg. Subjects one, two and three drank milk immediately after ingesting test material, subject four ate doughnuts and drank coffee. Urine was collected from subjects 24 hours before dosing and during the 72-hour period after dosing. Blood was collected by venipuncture at three or five and 24 hour post-dosing. Clinical observations were made immediately before ingestion and three to six hours after and consisted of blood pressure, pulse response, condition of pharynx, conjunctivae and pupils and neurologic effects. Haematologic studies consisted of haemoglobin, cell volume, WBC, differentials, reticulocytes, platelets and total protein. Urinalysis consisted of SpGr, albumin, reducing sugars, ketone bodies, occult blood, pH and sediment. Levels of TBHQ in serum and metabolites of TBHQ in urine were also determined. There was no evidence of any systemic effect following ingestion of TBHQ. No significant changes were observed in haematological studies or urinalysis. Examination of urine indicated that TBHQ was excreted as the o-sulfate and o-glucuronide conjugates (ratio approximately 3:1). These were mainly recovered during the first 24 hours. No free TBHQ was detected at any time. The manner of ingestion had a marked effect on the proportion of the dose recovered from urine. TBHQ administered by methods one and three resulted in only 22-40% of the dose being recovered in the urine, whereas method two resulted in 90-100% recovery. In all cases, the same metabolic products were present in urine. High recoveries of TBHQ metabolites in urine were accompanied by a serum level of TBHQ 3.1-3.7 mg/100 ml at three hours for two, compared to 0.4-1.2 mg/100 ml at three hours (one and three). At 24 hours these levels had fallen to 1.5 mg/100 ml for two and 0.2-1.2 mg/100 ml for one and three (Astill et al., 1967c). TOXICOLOGICAL STUDIES Special studies on reproduction TBHQ was fed in the diet to groups of 15 male and 15 female S-D rats for three successive generations at levels of 0 and 0.5%. Pairs of rats were mated to produce two litters per generation, with the next generation selected from weanlings of the second titter. Data recorded in each were as follows: number of inseminations, number of pregnancies, gestation period, average litter size, mortality of young from birth to weaning, weaning to one week after weaning, one week and two weeks after weaning to sacrifice. The average body weight per pup at weaning, one week after weaning, and two weeks after weaning were also recorded. Tissues were collected from all breeders. Animals that were not used as breeders were sacrificed at seven weeks and those selected as possible breeders but not used, at 14 weeks. All of the pups in the b generation were sacrificed and autopsied at approximately seven weeks of age. All animals were examined for gross pathology, and micropathology was studied on at least four animals of each litter. Organs examined included: trachea, lung, heart, tongue, oesophagus, stomach, small and large intestines, liver, kidneys, urinary bladder, pituitary, adrenal, pancreas, thyroid, parathyroid, gonads, uterus, spleen, bone marrow, cerebrum, cerebellum, and eye. To terminate study F3b litters were delivered by uterotomy on the nineteenth day of gestation. Foetuses were examined for gross abnormalities. One-third were stained with alizarin red for skeletal defects, while the other two-thirds, after fixation, were sectioned freehand and examined for abnormalities. The percentage of inseminations and pregnancies, gestation and average litter size appeared normal for both matings of each generation. In the F1a and F2a test groups there were more deaths than in control in birth to weaning period. The effect was not observed in the subsequent F1b and F2b generations. The parent rats (Fo generation) of the test group ate less and showed lower weight gain than their respective controls. Body weight of pups from treated animals at various time periods from weaning were lower than those of the control. Deaths during the period, weaning to five weeks were always more frequent in treated group (deaths as percentage total number animals). Abnormalities were reported in 22 foetuses from the F3b generation but 13 of these were in control group. Minor skeletal changes were noted in two animals in the test group. No compound related histological abnormalities were observed (Terhaar & Krasavage, 1968a). In another study groups each of 20 male and 20 female rats (S-D) were maintained on diets containing TBHQ at concentrations of 0.015, 0.15, 0.5 and 0% along with Mazola Corn Oil at 5% (w/w) incorporated into a basic diet of Purina Chow. Diets were fed for 66 days prior to breeding. Rats of the same dose level were mated (1:1) to produce two groups of first generation litters (F1a and F1b). F1a litters were maintained on assigned diets. Data recorded included number of inseminations and pregnancies, gestation period, litter size, mortality of young at birth, birth to weaning, weaning to one week post-weaning and one week post-weaning to two weeks post-weaning. Litters of F1b generation were treated similarly to F1a litters up to the tenth day after birth. At day 10, litters and dams within test groups were paired, and one pair placed on control diet, while others remained on the test diet. Also half the litters and dams of control groups were allowed to remain on the control diet and half on high level TBHQ diet (0.5%). At five weeks of age pups were sacrificed and examined for gross pathology. A number of deaths of parent animals occurred during the study (one male high dose, one control group during first five days, and later three males, one low, one middle, one high dose level, and one female control). None of the deaths appeared to be compound related. Food intake of parent rats was similar to control except at the 0.5% level, where there was a slight decrease at the commencement of the test. Male rats in this group showed a slightly decreased weight gain compared to control. There was no apparent effect on gonadal function, oestrus cycle, mating behaviour, conception rates, gestation period, parturition and lactation during the two breedings. The average litter size, neonatal viability and growth of the new-born pups appeared normal. Autopsy of F1b pups failed to reveal any gross pathology. The average litter weights of the F1a test pups were similar to controls. Pups from the F1b control changed to the 0.5% TBHQ showed a somewhat lower body weight than those left on control diet, for the period of study (up to two weeks past weaning). This may be related to rejection of the diet (Krasavage & Terhaar, 1970). Special studies on teratogenicity Groups each of 20 pregnant female S-D rats were fed test diets containing 0, 0.125, 0.25 and 5% TBHQ, and 0.03 and 0.12 Apholate (as positive control), at days 6-16 of gestation. On day 20 all females were sacrificed, and total implantation sites evaluated for resorptions, live foetuses and dead foetuses. The foetuses were weighed and examined for gross anomalies and either soft or skeletal tissue anomalies. All females on the TBHQ test diets showed weight gains similar to control. The mean body weight of both male and female foetuses of all treated groups were comparable to control, with the exception of the high Apholate group. Two foetuses in the high dose TBHQ showed soft tissue anomalies. The percentage skeletal tissue anomalies in the TBHQ test groups was not greater than controls (Krasavage, 1973). Other special studies (a) Response to liver processing enzyme and liver G-6-P activity to TBHQ Rat Adult male rats S-D strain were maintained on standard diets containing the following additions: (1) none; (2) 5% heated cottonseed oil; (3) DL-Ethionine, 2.5% level for 10 days; (4) 100 mg/kg/day phenobarbital for five days (intraperitoneal injection), (5) 1% corn oil + 0.05% BHA; (6) 4% corn oil + 0.2% BHA; (7) 1% corn oil + 0.05% TBHQ; (8) 4% corn oil + 0.2% TBHQ; and (9) 5% heated cottonseed oil + 0.025% TBHQ. A liver microsomal fraction was prepared from each group of animals and glucose-6-phosphatase (G-6-P), p-nitroanisole demethylase (pNaD) and aniline hydroxylase (AHase) activities determined. The expected elevation of pNaD (5X) and AHase (3X) occurred with phenobarbital and DL-ethionine had no significant effect on these enzymes. Phenobarbital produced a depression of G-6-P activity (25%), TBHQ at 0.05% level produced a 25% depression in G-6-Pase which was absent at the 0.2% level. TBHQ had no effect on pNaD at the 0.05% level, but produced at the 0.2% level a 60% elevation of pNaD. There was no clear effect on AHase. In contrast, BHA produced a 30% decrease in G-6-P at both levels, a 50% increase in pNaD at 0.05% and 700% increase of pNaD at the 0.2% level. There was no effect on AHase. Inclusion of heated oil in the diet had no marked effect on previous changes. In another experiment in which enzyme activities were measured of microsomal preparation from livers of rats fed for 180 days diets containing 0.5% TBHQ dissolved in either heated or unheated cottonseed oil, no significant differences were observed that could be attributed to heat treatment of oil before addition to the diet (Tischer & Walton, 1968). Dog pNaD, AHase, and G-6-Pase activities of microsomal fractions from dogs which had been maintained on diets containing 0, 0.05, 0.16, and 0.5% levels of TBHQ for two years were within range of control values (Tischer & Walton, 1968). Electron microscopy studies of liver and kidney tissue from both dog and rat showed that long-term administration of TBHQ did not significantly alter the subcellular constituents, or cause a proliferation of the endoplasmic reticulus of liver cells (Wolf & Fassett, 1968a and b). (b) TBHQ in heated or unheated oil six month dietary study in rats Eight groups, each of 30 rats (S-D) (equally divided by sex), were fed four levels of TBHQ in unheated oil and at the same level in heated oil (one hour to raise temperature to 375°F followed by four hours at 375°F). The levels of TBHQ in the oils were 0, 0.02, 0.1 and 0.5%. Oils were incorporated at a 5% level into a standard diet of ground Purina Chow. Animals were housed five/cage and water was available at all times. Body weight and gross feed consumption was recorded weekly for the first two months and thereafter fornightly. General appearance and behaviour was observed during the test period. Haemograms and urinalysis were done on the 0.5% unheated and heated and control at one, five, and six months. Haemograms consisted of haemoglobin, haematocrit, WBC and differentials and protein determination. Urinalysis consisted of pH, SpGr, occult blood, albumin, reducing sugar and microscopic examinations of the sediment. SGOT and SAP were done on the high and control groups at three and six months. At autopsy, liver, kidney, heart, spleen, lung, brain and testes weights were determined. The following tissues were examined microscopically: lung, heart, tongue, oesophagus, stomach, small and large intestines, liver, kidney, urinary bladder, pituitary gland, adrenal, pancreas, thyroid, gonads, spleen, bone marrow, cerebrum, cerebellum and eye. Three deaths occurred during the test period, but these were not compound related. Male rats on the 0.5% TBHQ/unheated fat showed a slight depression in weight gain and those in the 0.02% TBHQ/unheated fat a significant increase in weight gain over control. These effects were not observed in female rats on diets containing heated fats. Female rats in all groups showed similar weight gains to controls. Food intake of test groups was comparable or better than controls. Haematologic tests gave similar values for test and control groups with the exception of the 0.5% TBHQ/unheated fat male group at three months, where the WBC was slightly elevated. This effect was not noted at six months. Urinalysis, SGOT and SAP values of test and control groups were comparable and within normal limits. Organ/body weight ratios indicated a slight increase in ratios for testes and livers of the male rats from 0.5% TBHQ/heated oil group and liver weight ratio of the female rats of the 0.5% and 0.2% heated oil group. These minor differences appeared to be related to heated versus unheated fat rather than a compound effect. Histological studies did not reveal any compound related effects (Terhaar & Krasavage, 1968b). Acute toxicity LD50 References Animal Route (mg/kg body weight) 955 (10% in corn oil) Rat (fed) Oral 890 ( 5% in corn oil) Terhaar et al., 1968a 756 (10% in corn oil) Rat (fasted) Oral 802 ( 5% in corn oil) Terhaar et al., 1968a Mice (fasted) Oral 1 260 Terhaar et al., 1968a Guinea-pig Oral 790 Terhaar et al., 1968a Dog Oral <400 (consistently Terhaar et al., 1968a regurgitated) Short-term studies Rat Rats were injected (intraperitoneally) with 200 mg/kg TBHQ daily for one month without mortality but some loss of weight. At 100 mg/kg (intraperitoneally) daily for one month, there was no loss of weight. No histopathologic changes occurred in either case. Rats were maintained for 22 days on a diet containing 1% TBHQ. Initial rejection of food was followed by near normal food intake and growth curve paralleling control group. There were no mortalities, nor was there any gross or microscopic pathology (Fassett et al., 1968). Long-term studies Rat Groups of each of 100 albino rats (A & C Farms, Altamont, N.Y.) equally divided by sex were maintained on diets containing 0, 0.016, 0.05, 0.16 and 0.5% TBHQ for 20 months. Animals were observed for changes in appearance and behaviour. Body weight was reported at approximately 14-day intervals and group food intake at approximately 23-day intervals. Haematology was carried out at three, six, 12 and 20 months on 10 rats (five of each sex) from each of the 0, 0.16 and 0.5% level groups. Haematological tests consisted of haemoglobin, PCV, WBC and differentials. Clinical chemical tests and urinalysis were carried out on the same groups of animals at six, 12 and 20 months. The clinical chemical tests consisted of SGPT at six months, and SGPT, SGOT and SAP at 12 and 20 months. Urinalysis consisted of SpGr, albumin, sugar and appearance. At six and 12 months, approximately 20 rats (10 of each sex) of each group were sacrificed and at 20 months all surviving animals were sacrificed and autopsied. Organ weights were determined for liver, adrenal, kidney, spleen, heart, brain, lung and testes. Haematological studies were made on trachea, lung, heart, oesophagus, stomach, small intestine, large intestine, liver, kidney, urinary bladder, adrenal, pancreas, thyroid, ovary or testes, uterus, spleen, femoral bone marrow, cerebrum, cerebellum and eye. There were no adverse changes in appearance and behaviour of the rats during the test period. Mortalities occurred with equal frequency in all groups and were particularly heavy during the 12 to 20-month period. Deaths did not appear to be compound related. Growth rate, food intake and feed efficiency were comparable for all groups during the experimental period. Haematologic, biochemical tests and urinalysis of test and control groups were similar and within normal limits. Although there were some decreases in the absolute organ weight of spleen and brain of males of the 0.16 and 0.05 group at 20 months, these were not significantly different from control when expressed as organ/body weight ratio. No gross or microscopic lesions that could be attributed to the test compound were detected (Terhaar et al., 1968b). Dog Four groups each of eight pure bred beagle dogs (four male, four female), approximately six to eight months of age were used. The dogs were maintained on a commercial diet to which 6% cottonseed oil was added. TBHQ was added to the test diets at levels equivalent to 500, 1500 and 5000 ppm. Diets were available ad lib for one hour, six days/week. Water was available ad lib at all times. The dogs were housed individually. Daily inspection was made for appearance, behaviour, survival and physical signs. Body weight was determined weekly for first 12 weeks, and thereafter biweekly. Food intake was determined weekly during the first 12 weeks, and thereafter periodically. Complete physical examinations were conducted at various times during the test period. Haematological and biochemical studies and urine analyses were made twice before commencement of the feeding study, and at weeks 12, 26, 52, 78 and 104. Haematologic studies consisted of haemoglobin conc., haematology, RBC, WBC and differentials. Biochemical studies consisted of serum BUN, glucose, LDM, SAP and SGPT and bilirubin at week 104 only. Urinalysis consisted of pH, albumin, glucose, ketone bodies and occult blood. Because some minor abnormalities were noted in the haematology, the test period was increased to 117 weeks to permit additional observations. At week 108, peripheral blood samples were taken. At week 108, TBHQ was withdrawn from the diet of two dogs of the high level group. The animals were maintained in metabolism cages and 24-hour urine samples were collected daily. Blood samples were collected on days one, two, three, four, seven, 10 and 13 of this period. An interim sacrifice of one male and one female of each test group was made at one year. The remaining animals were sacrificed at week 117. At autopsy, animals were examined for gross pathological changes. The liver, kidneys, spleen, heart, brain, lungs, gonads, adrenals, thyroid and pituitary of all dogs were weighed. Tissues from the following organs of all dogs of control and high level groups were examined microscopically: liver, spleen, gallbladder, stomach, small and large intestines, pancreas, kidneys, urinary bladder, adrenals, gonads and adnexa, pituitary, thymus, thyroid, salivary glands, lymph nodes, heart, lungs, marrow, aorta, skin, muscle, spinal cord and brain. The liver, stomach, small and large intestines and kidneys of all dogs on low-and mid-level test diets were also examined microscopically. In addition, specimens of liver and kidney tissues were prepared for electron microscopy. No deaths occurred during the test period. Behaviour and appearance was normal at all times and physical examinations did not reveal any treatment related problems. Growth and food consumption was similar for control and test groups except at the beginning of the test when dogs were adjusting to the test diet. Biochemical studies and urinalysis showed variations within animals and groups, but none of these differences appeared to be compound related effects. Haematologic studies showed variable effects in the high level group. RBC were slightly lower in both male and female dogs than their respective controls. These shifts were also reflected in the haemoglobin conc. and haematocrits of some animals. At week 99, and a subsequent test period there was a slight deviation of reticulocytes in the high level groups. Peripheral blood smears also showed more normoblasts as well as occasional increase in erythrocyte basophilia. These effects were not observed in the lower level groups. Organ weight and gross pathology and histopathology failed to reveal any compound related changes. Electron microscopy of liver and kidney showed normal cellular constituents in test animals. There was no increase in the endoplasmic reticulum in liver cells of treated animals (Anonymous, 1968b). OBSERVATIONS IN MAN See "Biochemical aspects". Comments: Metabolic studies in rats indicate >90% of an ingested dose of TBHQ is absorbed. Excretion is rapid, primarily as the o-sulfate. At higher levels of intake there is an increasing urinary excretion of the o-glucuronide. About 10% of the urinary excretion is unchanged TBHQ. Even after chronic administration of 0.5% TBHQ in the diet, less than 1 ppm is stored in any tissue and the oxidative stability of the fat of chronically fed animals does not differ from that of controls. TBHQ is shown to pass across the placenta with about 0.2% of the chronically administered dose remaining in the foetus. In dog the metabolic, excretory and storage patterns were qualitatively similar to rats, except that a greater percentage of the o-glucuronide was excreted in the case of males, and a greater amount was stored in fat. Storage in fat was two times greater for females than males. In humans dosed with TBHQ absorption by capsule resulted in 22-40% absorption, whereas absorption approached 100% when incorporated into food. No free TBHQ was excreted in the urine. Urinary excretion was as the o-sulfate or o-glucuronide in a ratio of 3:1. Excretion was almost complete in 24 hours and studies of haematology, urine analysis, blood chemistry and clinical signs showed no effects due to administration of TBHQ. In a 20-month study in rats fed TBHQ in their diet there were no adverse effects noted. In a 117-week study dogs were given TBHQ in their diets. Parameters studied were similar to those for rats and in addition, electron microscopy of liver and kidney were performed. Aside from a slight decrease in RBC, haemoglobin and haematocrits, more normoblasts and occasional increases in erythrocyte basophilia, seen at the highest dose, there were no TBHQ-related effects observed. A three-generation reproduction study including an "a" and "b" littering, done in rats, showed scattered incidents of increased deaths from birth to weaning and deaths from weaning to five weeks were more frequent in the TBHQ-fed group. No other abnormalities were noted in the fed animals as compared to the controls. In a cross-over study with rats fed TBHQ, pups from untreated parents nursed with TBHQ-treated parents gained less weight than the corresponding cross-over, suggesting that diet rejection is the major factor rather than an organic deficiency in pups from TBHQ-fed parents. A teratology study in rats showed no abnormal effects. In a study designed to demonstrate the safety of reacted TBHQ, rats were fed TBHQ in oils that had been heated for four hours at 375°F for six months. Groups of rats were fed the same diets using unheated oils. Except for a slight depression in weight gain in the high level rats fed the 0.5% TBHQ, there were no deleterious compound related effects noted. Enzyme induction experiments were done with rat and dog. Glucose-6-phosphatase, paranitroanisole demethylase (pNaD) and aniline hydroxylase (AHase) activities in liver microsomes were studied. In dog no induction effects were noted. In rat and dog heated oil had no effect on enzyme activities. In rat induction of pNaD and AHase were noted. There was a non-dose related elevation in G-6-P that is probably artifact. Chronic administration did not alter the picture in the rat. Since there was no change in enzyme induction seen in chronically exposed as opposed to acutely exposed rats, it is reasonable to conclude the enzyme induction activity noted for TBHQ is freely reversible. In the seventeenth report of the Joint FAO/WHO Expert Committee, reference was made to recent evidence indicating possible effects on reproduction in the rat when butylated hydroxyanisole, alone or with propylgallate, was mixed with lard in the diet. The Committee, noting that TBHQ was chemically similar to both BHA and BHT, concluded that the same type of data should be forthcoming for this compound. EVALUATION Level causing no toxicological effect in the dog 3000 ppm in the diet equivalent to 75 mg/kg body weight. Estimate of acceptable daily intake for man 0-0.75 mg/kg body weight.* FURTHER WORK OR INFORMATION Required by 1978. Appropriate studies on reproduction using tertiary butyl hydroquinone in mixtures with propylgallates. * Temporary. REFERENCES Anonymous (1968a) Determination of the stability and tertiary butyl hydroquinone content of rat and dog fat extracts. Unpublished technical report No. 495-F submitted to the World Health Organization by Eastman Chemical Products, Inc. Anonymous (1968b) Two-year chronic feeding studies with tertiary butyl hydroquinone (TBHQ) in dogs. Unpublished report from the Food and Drug Research Labs, Inc. submitted to the World Health Organization by Eastman Chemical Products, Inc. Astill, B. D., Blakeley, R. V. & Cantor, E. E. (1967a) The metabolic fate of TBHQ in rats and dogs and of TBHQ-14C in rats. Unpublished report of the Biochemical Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Astill, B. D. Cantor, E. E. & McEwan, D. B. (1967b) Long-term feedings of TBHQ to rats and dogs: urinary conjugate excretions, serum TBHQ levels and autopsied fat analyses. Unpublished report from the Biochemistry Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Astill, B. D., Cantor, E. E., Ely, T. S., Jones, W. H. & Uskavitch, R. J. (1967c) The oral ingestion of t-butylhydro-quinone (TBHQ) by humans; clinical observations and metabolic fate. Unpublished report from the Laboratory of Industrial Medicine, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Astill, B. D. & Walton, D. A. (1968) Distribution of radioactivity in pregnant rats receiving 14C-labeled TBHQ. Unpublished report from the Biochemistry Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Astill, B. D., Blakeley, R. V., Cantor, E. E., Tischer, K. S., Walton, D. A., McEwan, D. B., Jones, W. H. & Ely, T. S. (1968) Biochemical studies on Tert-Butylhydroquinone (TBHQ). A Summary. Unpublished report from the Laboratory of Industrial Medicine, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Astill, B. D. & Jones, B. E. (1969) Long-term feedings of TBHQ to rats and dogs: levels of TBHQ in tissues and organs of autopsied animals. Unpublished report from the Biochemistry Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Fassett, D. W., Terhaar, C. J. & Astill, B. D. (1968) Summary of the safety evaluation of monotertiary butyl hydroquinone. Unpublished report from the Laboratory of Industrial Medicine, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Krasavage, W. J. & Terhaar, C. J. (1970) The reproductive performance of rats fed monotertiary butyl hydroquinone: a single generation study. Unpublished report from the Toxicology Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Krasavage, W. J. (1973) A study of the teratogenic potential of monotertiary butyl hydroquinone in rats. Unpublished report from the Health and Safety Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Terhaar, C. J. & Krasavage, W. J. (1968a) The reproductive performance of rats fed monotertiary butyl hydroquinone. Unpublished report from the Toxicology Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Terhaar, C. J. & Krasavage, W. J. (1968b) Monotertiary butyl hydroquinone (TBHQ) in heated and unheated cottonseed oil. A six-month dietary feeding study in rats. Unpublished report from the Toxicology Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Terhaar, C. J., Vis, E. A. & Kesel, H. J. (1968a) Acute oral toxicity of monotertiary butyl hydroquinone (TBHQ). Unpublished report from the Laboratory of Industrial Medicine, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Terhaar, C. J., Krasavage, W. J., Wolf, G. L. & Leonard, W. J. (1968b) Study of the tolerance of rats to monotertiary butyl hydroquinone in the diet. Final report at 20 months. Unpublished report from the Toxicology Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Tischer, K. S. & Walton, D. A. (1968) Dietary feeding of TBHQ and related compounds to rats and dogs: the response of liver processing enzymes and liver glucose-6-phosphatase activity. Unpublished report from the Biochemistry Laboratory, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Wolf, G. L. & Fassett, D. W. (1968a) Electron microscope study of livers of rats fed monotertiary butyl hydroquinone. Unpublished report from the Laboratory of Industrial Medicine, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc. Wolf, G. L. & Fassett, D. W. (1968b) Electron microscope study of livers of dogs fed monotertiary butyl hydroquinone for two years. Unpublished report from the Laboratory of Industrial Medicine, Eastman Kodak, submitted to the World Health Organization by Eastman Chemical Products, Inc.
See Also: Toxicological Abbreviations