4-tert-butylpyrocatechol

Repeated dose toxicity: oral

Administrative data

Endpoint:

sub-chronic toxicity: oral

Type of information:

experimental study

Adequacy of study:

key study

Study period:

August - November 1996

Reliability:

1 (reliable without restriction)

Rationale for reliability incl. deficiencies:

comparable to guideline study

Data source

Reference

Reference Type:

study report

Title:

Unnamed

Year:

2002

Materials and methods

Test guideline

Test guideline 1

Qualifier:

equivalent or similar to guideline

Guideline:

EU Method B.26 (Sub-Chronic Oral Toxicity Test: Repeated Dose 90-Day Oral Toxicity Study in Rodents)

Test guideline 2

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)

GLP compliance:

yes

Test material

Test material information

Constituent 1

Reference substance name:

4-tert-butylpyrocatechol

EC Number:

202-653-9

EC Name:

4-tert-butylpyrocatechol

Cas Number:

98-29-3

Molecular formula:

C10H14O2

IUPAC Name:

4-tert-butylbenzene-1,2-diol

Details on test material:

p-tert-butylcatechol (TBC) from Aldrich Chemical Company (Lot No. 19115EN).
The purity was determined to be greater than 99% by HPLC.
Two impurities were detected, at approximately 0.26 and 0.20% concentration (no data about their nature).

Test animals

Species:

rat

Strain:

Fischer 344

Sex:

male/female

Details on test animals or test system and environmental conditions:

TEST ANIMALS
- Source: Taconic Laboratory Animals and Services (Germantown, NY)
- Age at study initiation: 6 weeks old
- Weight at study initiation: 78 g (males) and 75 g (females)
- Fasting period before study: no
- Housing: 5 animals per cage (polycarbonate, changed twice per week)
- Diet: NTP-2000 mash feed, available ad libidum
- Water: tap water via automatic watering system, available ad libidum
- Acclimation period: 11 (males) or 12 (females) days

ENVIRONMENTAL CONDITIONS
- Temperature: ca. 22°C
- Humidity: 50% +/- 15%
- Air changes: 10/hour
- Photoperiod: 12 hours light/day

IN LIFE DATES:
26 (males) or 27 (females) August 1996 to 25 (males) or 26 (females) November 1996.

Administration / exposure

Route of administration:

oral: feed

Details on oral exposure:

DETAILS ON DIET PREPARATION
- Rate of preparation of diet: every 4 weeks
- Type of food: irradiated feed
- Storage of food : in plastic bags inside buckets at 5°C for up to 42 days

Analytical verification of doses or concentrations:

yes

Details on analytical verification of doses or concentrations:

- Analytical verification of homogeneity of doses/concentrations: Yes (performed in the 781 and 12500 ppm dose formulations)
- Analytical verification of stability of doses/concentrations: Yes (stability of the 781 ppm dose formulation was confirmed for 42 days for samples stored in plastic bags at temperatures up to 5°C. Samples subjected to animal room conditions showed declines of up to 37% in TBC concentrations with time.)
- dose formulations were analyzed at the beginning, midpoint, and end of the study; all dose formulations analyzed were within 10% of the target concentrations. Animal room samples of these dose formulations were also analyzed; the concentrations of 9 of 15 animal room samples were less than 90% of the target concentrations (these low concentrations are attributed to chemical degradation, oxidation, evaporation or binding with feed)

Duration of treatment / exposure:

14 weeks

Frequency of treatment:

7 days per week

Doses / concentrations

Doses / concentrations 1

Remarks:

Doses / Concentrations:
0, 781, 1562, 3125, 6250 and 12500 ppm
Basis:
nominal in diet

Doses / concentrations 2

Remarks:

Doses / Concentrations:
0, 70, 135, 270, 525 and 1030 mg/kg bw
Basis:
other: males

Doses / concentrations 3

Remarks:

Doses / Concentrations:
0, 70, 145, 265, 555 and 1010 mg/kg bw
Basis:
other: females

No. of animals per sex per dose:

10

Control animals:

yes, plain diet

Details on study design:

Dose selection rationale: based on the results in the 15-day study in rats: based on the body weight effects in the 25000 ppm groups and mortality in the 50000 ppm groups, the highest exposure concentration selected for the 14-week study was 12500 ppm.

Post-exposure period: none

Examinations

Observations and examinations performed and frequency:

CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily

DETAILED CLINICAL OBSERVATIONS: No
- Time schedule: weekly

BODY WEIGHT: Yes
- Time schedule: initially, weekly and at the end of the study

FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No

FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No

WATER CONSUMPTION AND COMPOUND INTAKE: No
OPHTHALMOSCOPIC EXAMINATION: No

HAEMATOLOGY: Yes
- Time schedule for collection of blood: on days 4 and 22 and at the end of the study
- Anaesthetic used for blood collection: Yes (mixture of carbon dioxide and oxygen)
- Animals fasted: No data
- How many animals: all animals
- Parameters examined: haematocrit; haemoglobin concentration; erythrocyte, reticulocyte and platelet counts; erythrocyte and platelet morphology; mean cell volume; mean cell haemoglobin; mean cell haemoglobin concentration; leukocyte count and differentials

CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: on days 4 and 22 and at the end of the study
- Anaesthetic used for blood collection: Yes (mixture of carbon dioxide and oxygen)
- Animals fasted: No data
- How many animals: all animals
- Parameters examined: urea nitrogen, creatinine, total protein, albumin, alanine aminotransferase, alkaline phosphatase, creatine kinase, sorbitol dehydrogenase and bile salts

URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No

Sacrifice and pathology:

- Organ weights examined at necropsy (in all animals): heart, right kidney, liver, lungs, right testis, thymus.
- GROSS PATHOLOGY: yes
- HISTOPATHOLOGY (in all animals of the 0 and 12500 ppm groups): adrenal gland, bone with marrow, brain, clitoral gland, esophagus, heart with aorta, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, liver, lung, lymph nodes (mandibular and mesentric), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, spleen, stomach (forestomach, glandular), testis with epididymis and seminal vesicle, thymus, thyroid gland, trachea, urinary bladder, uterus.

Statistics:

- The Fisher exact test was used to determine significance of the incidences of microscopic lesions;
- The parametric multiple comparison procedures of Dunnett and Williams were used to determine significance of organ and body weight data;
- Haematology, clinical chemistry, spermatid and epididymal spermatozoal data were analysed using the nonparametric multiple comparison methods of Shirley and Dunn;
- Jonckheere's test was used to assess the significance of the dose-related trends;
- Extreme values were identified by the outlier test of Dixon and Massey;
- Average severity values were analysed for significance with the Mann-Whitney U test.

Results and discussion

Results of examinations

Clinical signs:

no effects observed

Description (incidence and severity):

There were no clinical findings of toxicity.

Mortality:

no mortality observed

Description (incidence):

All rats survived to the end of the study.

Body weight and weight changes:

effects observed, treatment-related

Description (incidence and severity):

Final mean body weights and body weight gains of male rats exposed to 1562 ppm or greater and females exposed to 3125 ppm or greater were significantly less than those of the controls.

Food consumption and compound intake (if feeding study):

effects observed, treatment-related

Description (incidence and severity):

Feed consumption by 6250 and 12500 ppm rats at week 1 and by 12500 ppm rats at week 14 was less than that by the controls.

Food efficiency:

not examined

Water consumption and compound intake (if drinking water study):

not examined

Ophthalmological findings:

not examined

Haematological findings:

effects observed, treatment-related

Description (incidence and severity):

After 4 days of exposure, hematocrit values, hemoglobin concentrations, and erythrocyte counts in 6250 and 12500 ppm males and females were increased,
consistent with a minimal to mild erythrocytosis. This increase was accompanied by unchanged to slightly decreased reticulocyte counts, suggesting that the
erythrocytosis was related to an altered hydration status. The erythrocytosis was transient and occurred only in the 12500 ppm groups on day 22. By the end of the study, no groups were affected. The erythrocytosis was accompanied by minimal decreases in mean cell volumes and mean cell hemoglobin values,
suggesting that circulating red cells were slightly smaller than expected. This effect was also transient and, at week 14, had reversed, with minimally increased erythrocyte sizes in males in the 6250 and 12500 ppm groups.
Platelet counts in 12500 ppm rats also demonstrated a transient, minimal increase on day 4 that had abated by day 22.

Clinical biochemistry findings:

effects observed, treatment-related

Description (incidence and severity):

On days 4 and 22, there was evidence of a transient hepatic effect, as indicated by increased serum alanine aminotransferase activities and bile salt
concentrations in exposed males and females. These increases had abated by the end of the study. On day 4, alanine aminotransferase activities were minimallyincreased in 6250 and 12500 ppm males and all exposed groups of females. On day 22, alanine aminotransferase activities were minimally increased in 3125
ppm males and in males and females exposed to 6250 ppm or greater. The increases in activity were not exposure concentration related at either time point.
There were no significant increases in the activity of sorbitol dehydrogenase.
On day 4, bile salt concentrations were increased in males exposed to 1562 ppm or greater and 12500 ppm females. On day 22, only 12500 ppm females were affected. Alkaline phosphatase activities, another marker of cholestasis, were decreased (day 4) or unaffected.
Sporadic differences occurred in other clinical chemistry parameters at varying time points. These differences, which generally did not demonstrate a treatment relationship and/or were inconsistent between males and females, were not considered to be toxicologically relevant.

Urinalysis findings:

not examined

Behaviour (functional findings):

not examined

Organ weight findings including organ / body weight ratios:

effects observed, treatment-related

Description (incidence and severity):

Organ weight differences in exposed rats reflected decreases in body weights.

Gross pathological findings:

no effects observed

Description (incidence and severity):

There were no exposure-related gross lesions.

Histopathological findings: non-neoplastic:

effects observed, treatment-related

Description (incidence and severity):

The incidences of hyperkeratosis of the forestomach epithelium were significantly increased in males and females in all exposed groups. Forestomach epithelial hyperplasia also occurred in males exposed to 1562 ppm or greater and females exposed to 3125 ppm or greater, and the incidences
in these groups were significantly increased except for the 1562 ppm group. The severity of the forestomach lesions generally increased with increasing exposure concentration. The absence of associated ulceration and inflammation would suggest a primary proliferative effect as opposed to an irritant effect. The hyperplasia in rats exposed to p-tert-butylcatechol had no atypical histologic features that were suggestive of a preneoplastic lesion.
All 6250 and 12500 ppm males had minimal cytoplasmic alteration in the liver.

Histopathological findings: neoplastic:

not examined

Details on results:

CLINICAL SIGNS
There were no clinical findings of toxicity.

MORTALITY
All rats survived at the end of the study.

BODY WEIGHT AND WEIGHT GAIN
Final mean body weights and body weight gains of males exposed to 1562 ppm or greater and females exposed to 3125 ppm or greater were significantly
lower than those of the controls (-4.5%, -7%, -12% and -23% for males, respectively and -4.5%, -8.5% and -9% for females, respectively).

FOOD CONSUMPTION AND COMPOUND INTAKE
Feed consumption by males and females in the 6250 and 12500 ppm groups at week 1 and the 12500 ppm groups at week 14 was lower than that by the
controls.

HAEMATOLOGY
An erythrocytosis, indicated by increased hametocrit values, hemoglobin concentrations, and erythrocyte counts, was observed in 6250 and 12500 ppm rats on day 4 and in 12500 ppm rats on day 22.

CLINICAL CHEMISTRY
On days 4 and 22, a transient hepatic effect was demontrated by increases in serum alanine aminotransferase activities and bile salt concentrations in
exposed rats. Increases in bile salt concentrations are, in general, used as a marker of hepatic cholestasis. There was evidence early in the current study of decreased feed consumption by rats in the higher exposure groups; thus, the increase in alanine aminotransferase activities and bile salt concentrations could suggest a transient, minimal liver effect that was not expressed in the other markers of liver injury or cholestasis.

ORGAN WEIGHTS
Organ weight differences in exposed reflected decreases in body weights.
Differences in reproductive organ weights were observed, as detailed below.

GROSS PATHOLOGY
There were no exposure-related gross lesions.

REPRODUCTIVE ORGANS
See details in section 7.8.1.

HISTOPATHOLOGY: NON-NEOPLASTIC
The incidence of hyperkeratosis of the forestomach epithelium were significantly increased in males and females in all exposed groups. The incidence of hyperplasia of the forestomach epithelium was significantly increased in males and females exposed to 3125 ppm or greater. The severities of the forestomach lesions were minimal to moderate in males and minimal to mild in females. All males exposed to 3250 or 12500 ppm had minimal cytoplasmic alteration of the liver.

Effect levels

1

Dose descriptor:

NOAEL

Effect level:

< 781 ppm

Based on:

test mat.

Sex:

male/female

Basis for effect level:

histopathology: non-neoplastic

Remarks on result:

other:

Remarks:

Local effects: Hyperkeratosis and hyperplasia were observed in the forestomach.

2

Dose descriptor:

NOAEL

Effect level:

< 781 ppm

Based on:

test mat.

Sex:

female

Basis for effect level:

clinical biochemistry

Remarks on result:

other:

Remarks:

Systemic effects: The increases in alanine aminotransferase activities and bile salt concentrations could suggest a transient, minimal liver effect. Alanine aminotransferase activities were minimally increased in all exposed groups of females. In a worst case approach this effect is considered as adverse even if it was transient and minimal.

Target system / organ toxicity

Critical effects observed:

not specified

Any other information on results incl. tables

Mean body weight:

Concentration (ppm)	Initial	Final	Change relative to controls (%)
Male
0	79	311
781	79	319	+2
1562	76	297*	-5
3125	78	290**	-7
6250	80	273**	-12
12500	76	240**	-23
Female
0	75	178
781	76	183	+3
1562	74	184	+3
3125	76	170*	-4
6250	75	163**	-9
12500	72	162**	-9

* Significantly different (P ≤ 0.05) from the control group    ** P ≤0.01

Incidences of selected nonneoplastic lesions:

	0 ppm	781ppm	1562 ppm	3125 ppm	6250 ppm	12500ppm
Male
Forestomach^a	10	10	10	10	10	10
Epithelium, hyperplasia^b	0	4* (1.0)c	8** (2.0)	9** (1.8)	10** (2.2)	10** (3.1)
Epithelium, hyperkeratosis	0	0	2 (1.0)	8** (1.8)	8** (2.0)	10** (2.6)
Liver	10	10	10	10	10	10
Cytoplasmic alteration	0	0	0	0	10** (1.0)	10** (1.0)
Female
Forestomach	10	10	10	10	10	10
Epithelium, hyperplasia	0	6** (1.0)	7** (1.4)	9** (1.6)	10** (2.0)	10** (2.2)
Epithelium, hyperkeratosis	0	0	0	5* (1.6)	8** (1.8)	10** (2.2)

* Significantly different (P ≤ 0.05) from the control group    ** P ≤0.01

^anumber of animals with forestomach examined microscopically

^bnumber of animals with lesion

^caverage severity grade of lesions in affected animals; 1=minimal, 2=mild, 3=moderate, 4=marked

Applicant's summary and conclusion

Conclusions:

Following 14 weeks of dietary administration to rats, 4-tert-butylpyrocatechol induced hyperkeratosis and hyperplasia in the forestomach (local effect). Transient and minimal effects on liver were also observed (systemic effect).
These effects were observed at all exposure concentrations (only in females for the increase in alanine aminotransferase activities), and the No-Observed-Adverse-Effect-Level (NOAEL) was not determined for these effects.

Executive summary:

In a 14 week dietary toxicity study (NTP study, 2002), 4 -tert-butylpyrocatechol was administered to 6 -week male and female Fischer 344 rats, 10/dose, in diet, at the dose levels of 0, 781, 1562, 3125, 6250 and 12500 ppm, resulting in doses of 0, 70, 135, 270, 525 and 1030 mg/kg bw to males and 0, 70, 145, 265, 555 and 1010 mg/kg bw to females.

There were no clinical findings of toxicity and no mortality. Mean body weights of males exposed to 1562 ppm or greater and females exposed to 3125 ppm or greater were significantly lower than those of the controls (from -4.5% to -23%). Feed consumption by males and females in the 6250 ppm (week 1) and 12500 ppm (weeks 1 and 14) was less than that by the controls.

An erythrocytosis, indicated by increased hematocrit values, hemoglobin concentrations, and erythrocyte counts, was observed in 6250 and 12500 ppm groups on day 4 and in 12500 ppm groups on day 22. At these time points, a transient hepatic effect was demonstrated by increases in alanine aminotransferase activities and bile salt concentrations in exposed rats (increase in alanine aminotransferase activities was observed in all treated females).

Organ weight differences in exposed animals reflected decreases in body weights.

There were no exposure-related gross lesions. The incidence of hyperkeratosis of the forestomach epithelium were significantly increased in males and females in all exposed groups. The incidences of hyperplasia of the forestomach epithelium were significantly increased in males and females exposed to 3125 ppm or greater.

The NOAEL was < 781 ppm (equivalent to 70 mg/kg bw/day) for local and systemic effects.

This subchronic toxicity study in rats is acceptable and was conducted comparably to the guideline requirements for a subchronic oral study (OECD 408) in rats.