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EC number: 262-967-7 | CAS number: 61788-32-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-compliant EPA guideline study, available as unpublishedd report, no restrictions, adequate for assessment.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 984
- Report date:
- 1984
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.8700 (Subchronic Oral Toxicity Test)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Terphenyl, hydrogenated
- EC Number:
- 262-967-7
- EC Name:
- Terphenyl, hydrogenated
- Cas Number:
- 61788-32-7
- Molecular formula:
- C18Hn (n >18-36)
- IUPAC Name:
- Terphenyl, hydrogenated
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Inc., Kingston, New York 12484
- Age at study initiation: 43 days old
- Weight at study initiation: 197 grams for males (173-213) and 157 grams for females (131-175)
- Housing: doubly housed
- Diet (e.g. ad libitum): ad libitum; standard laboratory diet (Purina certified rodent chow #5002)
- Water (e.g. ad libitum): ad libitum; (Elizabethtown water company)
- Acclimation period: 14 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 61-75°F
- Humidity (%): 15-65%
- Photoperiod (hrs dark / hrs light): 12 hour light/dark cycle (7 am to 7 pm)
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- DIET PREPARATION
- Rate of preparation of diet (frequency): weekly
- Mixing appropriate amounts with (Type of food): standard laboratory diet (Purina certified rodent chow #5002) - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Four ouce samples were taken for the control group and each dose level weekly and were stored frozen at Bio/dynamics, Inc. Duplicate samples were taken for weeks 1, 2, 3, 4, 6, 8, 10 and 12 and analyses for concentration were performed by the Department of Metabolism and Analytical Chemistry of Bio/dynamics, Inc.
- Duration of treatment / exposure:
- 14 weeks
- Frequency of treatment:
- 7 days/week
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 ppm
- Remarks:
- nominal in diet, corresponding to 0 mg/kg bw/d
- Dose / conc.:
- 50 ppm
- Remarks:
- nominal in diet, corresponding to 3 mg/kg bw/d (nominal) and 3.6 mg/kg/d (Males; actual ingested) and 4.2 mg/kg/d (Females; actual ingested)
- Dose / conc.:
- 200 ppm
- Remarks:
- nominal in diet, corresponding to 12 mg/kg bw/d (nominal) and 14.8 mg/kg/d (Males; actual ingested) and 17.0 mg/kg/d (Females; actual ingested)
- Dose / conc.:
- 2 000 ppm
- Remarks:
- nominal in diet, corresponding to 120 mg/kg bw/d (nominal) and 143.7 mg/kg/d (Males; actual ingested) and 169.2 mg/kg/d (Females; actual ingested)
- No. of animals per sex per dose:
- 12 animals per sex per dose
- Control animals:
- yes
Examinations
- Observations and examinations performed and frequency:
- OBSERVATIONS FOR MORTALITY AND GROSS SIGNS OF TOXICOLOGIC OR PHARMACOLOGIC EFFECTS: Yes
- Time schedule: Twice daily, once in the morning and once in the afternoon
DETAILED PHYSICAL EXAMINATION FOR SIGNS OF LOCAL OR SYSTEMIC TOXICITY? PHARMACOLOGIC EFFECTS AND PALPATION FOR TOSSUE MASSES: Yes
- Time schedule: Twice pretest and weekly thereafter
BODY WEIGHT: Yes
- Time schedule for examinations: twice pretest, weekly during treatment and terminally (after fasting)
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption determined : Yes; weekly, beginning one week prior to treatment
- Compound intake calculated : Yes; calculated from food consumption data and based on nominal concentrations
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: once pretest and at study termination
- Dose groups that were examined: all animals
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at approximately 1 month and at study termination
- Anaesthetic used for blood collection: Yes (light ether anesthesia)
- Animals fasted: Yes
- How many animals: 10 animals per sex per group
- Parameters checked in Table 1 were examined.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: at approximately 1 month and at study termination
- Animals fasted: Yes
- How many animals: 10 animals per sex per group
- Parameters checked in Table 2 were examined. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (see Table 3)
HISTOPATHOLOGY: Yes (see Table 4)
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- CLINICAL SIGNS AND MORTALITY:
Physical observations noted in control and treated animals included alopecia, chromodacryorrhea and excessive lacrimation. These observations occured sporadically in control and treated animals. These incidences did not exhibit a dose-response and were not considered related to the administration of the test material. These findings are not uncommon in laboratory rats and may suggest the presence of a sialodacryoadenitis infection in these animals.
All control and treated animals survived the duration of the study.
BODY WEIGHT AND WEIGHT GAIN
The mean body weights of the treated males from all groups were unremarkable throughout the study when compared to the controls.
The mean body weights of the high-dose females (Group IV - 2000 ppm) were slightly (3-7%) lower than control throughout the treatment period. While the differences from control were small, they were consistent over time and were therefore attributed to the administration of the test material.
The mean body weights of the low- and mid-dose females were comparable to the controls throughout the study.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
The mean food consumption values of the high-dose males and females were slightly lower than control during the first week of the study. In addition, feed spillage was noted more frequently in the mid- and high-dose males than in the control males. These findings (decreased food consumption and spillage) may suggest a palatability problem with this material.
Food consumption data was unremarkable for the males and females for the remainder of the treatment-period.
OPHTHALMOSCOPIC EXAMINATION:
There were no ophthalmoscopic findings noted in the treated animals at study termination which were considered related to the administration of the test material.
HAEMATOLOGY:
The high-dose males, at the 1 month bleeding interval, exhibited slight decreases in mean hemoglobin concentration, hematocrit and erythrocyte counts and a slight increase in mean platelet count, these findings were statistically significant. At termination the high-dose males continued to exhibit slight (not statistically significant) decreases in mean hemoglobin concentration, hematocrit and erythrocyte count and a statistically significant increase in mean platelet count. While differences from control were slight the consistency of these findings at month 1 and study termination suggests a relationship to the administration of the test material.
Hematology data was unremarkable in the low- and mid-dose males and in all treated females at 1 month and at study termination.
CLINICAL CHEMISTRY:
The high-dose males exhibited slight, statistically significant elevations in mean cholesterol levels at month 1 and termination. In addition, the mean albumin level of the high-dose males was significantly elevated at study termination. The high-dose females exhibited a slight (statistically significant) reduction in mean glucose levels at month 1 and at study termination (not statistically significant).
The mid- and high-dose females exhibited slight (statistically significant) increases in mean calcium levels at 1 month. Slight (not statistically significant) increases were also noted in the mean calcium level of the mid- and high-dose females at study termination.
ORGAN WEIGHTS:
The high-dose males and females exhibited statistically significant increases in kidney to body weight ratios and slight (not statistically significant) increases in mean kidney weights and kidney to brain weight ratios. These increases were possibly related to slight decreases in mean terminal body weights in the high-dose males (2.5%) and females (6.4%). The high-dose males and females also exhibit significant increases in mean liver weights (47% and 21%), liver to body weight ratios (51% and 29%), and liver to brain weight ratios (49 and 22%). The high-dose females exhibited slight increases in mean adrenal weights, adrenal to body weight ratios and adrenal to brain weight ratios. Similar adrenal weight findings were not noted in the treated males.
GROSS PATHOLOGY:
There was no indication that the gross tissue changes noted during necropsy were treatment associated. Often the gross observations were related to normal color or architectural tissue pattern variations which had no microscopic correlation. Other tissue lesions were sporadic in occurrence or were of the type commonly encountered in laboratory rats of this age group. The were judged to have had no treatment relationship.
HISTOPATHOLOGY: NON-NEOPLASTIC
Microscopic assessment of the tissues revealed no histomorphological evidence of a direct treatment associated toxicopathological effect. There was noted, however, an increased incidence of a spontaneously occuring renal lesions when kidneys from high-dose male rats were compared to those of the male controls.
The minimal lesion was one which has been noted frequently in control male animals and was characterized by single or multiple small foci of proximal tubule epithelial cell hypertrophy and basophillia. These foci were interpreted as representing young regenerative cells. The exact cause of the lesion is obscure. In this study the regenerative foci were noted in 10 of 12 high-dose males and 4 of 12 control males. Similar foci were noted in 5 of 12 mid- and 5 of 12 low-dose rats. The renal lesion was not present in females except for 2 of 12 mid-dose animals.
Although the incidence was increased in high-dose males, the severity of the lesion was comparable to that noted in control males.
An increased of this spontaneous renal lesion in male rats treated with various other non-related compounds has been observed on previous occasions. The pathogenesis and biological significance of the lesion remains unclear.
Various other tissue alterations were noted in rats of both the control and treated groups. They occurred sporadically or with approximately equal frequency and degree in control rats as in treated animals and were judged to have no treatment relationship.
Under the conditions of this test, the following conclusions were made based on the gross and microscopic evaluation:
1. Terphenyl, hydrogenated when fed in the diet caused no specific toxicoppathological alteration in the tissues of male or female rats.
2. Terphenyl, hydrogenated high-dose treated male rats had an increased incidence but no increased severity of a spontaneously occuring regenerative renal lesion which was also present in the control males. The change was not present in high-dose females. The toxicopathological significance of the increased incidence in high-dose males when compared to control males was unclear.
A gross and microscopic correlation of lesions noted at necropsy revealed no evidence of a treatment associated response. No gross or microscopic pathology was noted which would correlate with the increased kidney and liver weights seen in the high-dose and/or females.
Microscopic evaluation of the tissues revealed no histomorphological evidence of a direct toxicopathological effect. Tissues from control rats were comparable to those from the treated animals.
There was, however, an increased incidence of a spontaneously occurring renal tubular lesion in high-dose males when compared to control males. the lesion incidence in low- and mid-dose males was similar to that observed in controls. Females were essentially free of the lesion. The ethiology and toxicopathological significance of the increased incidence rate in high-dose males was unclear.
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 12 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- clinical biochemistry
- clinical signs
- food consumption and compound intake
- gross pathology
- haematology
- mortality
- ophthalmological examination
- organ weights and organ / body weight ratios
- Dose descriptor:
- NOAEL
- Effect level:
- 14.8 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- body weight and weight gain
- clinical biochemistry
- clinical signs
- food consumption and compound intake
- gross pathology
- haematology
- mortality
- ophthalmological examination
- organ weights and organ / body weight ratios
- Remarks on result:
- other: analytically verified
- Dose descriptor:
- NOAEL
- Effect level:
- 17 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- body weight and weight gain
- clinical biochemistry
- clinical signs
- food consumption and compound intake
- gross pathology
- haematology
- mortality
- ophthalmological examination
- organ weights and organ / body weight ratios
- Remarks on result:
- other: analytically verified
- Dose descriptor:
- LOAEL
- Effect level:
- 120 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- clinical biochemistry
- clinical signs
- food consumption and compound intake
- gross pathology
- haematology
- mortality
- ophthalmological examination
- organ weights and organ / body weight ratios
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- NOAEL = 200 ppm (nominal 12 mg/kg body weight/day, after analytical verification corresponding to 14.8 mg/kg bw/day in males and 17.9 mg/kg bw/day in females)
- Executive summary:
Terphenyl, hydrogenated heat transfer fluid was administered orally, via dietary mixture to 72 Sprague-Dawley CD rats (12/sex/group) at dose levels of 50, 200 and 2000 ppm in the diet for a period of approximately 14 weeks, corresponding with nominal doses of 3, 12 and 120 mg/kg body weight/day. Control animals (12/sex/group) received a standard laboratory diet. Physical observations, ophtalmoscopic examinations, body weight and food consumption measurements were performed on all animals at selected intervals during the treatment period. Hematology and clinical chemistry evaluations were performed on 10 animals/sex/group at approximately 1 month and at study termination. After approximately 14 weeks of treatment, all survivors were sacrificed, selected organs were weighed and organ/body and organ/brain weight ratios calculated. Complete gross postmortem examinations were conducted on all animals. Histopathological evaluations were conducted on specified tissues for all animals in Group I (0 ppm) and IV ( 2000 ppm). Lungs, liver and kidneys were evaluated from all animals in Groups II (50 ppm) and III (200 ppm). All rats survived the 3-month test. The mean body weights of the high-dose females (Group IV – 2000 ppm) were slightly (3-7%) lower than control throughout the treatment-period. The mean food consumption values of high-dose males and females were slightly lower than control during the first week of the study and were unremarkable for the remainder of the treatment-period. The high-dose males, at the 1 month and terminal bleeding intervals exhibited slight decrease in mean hemoglobin concentration, hematocrit and erythrocyte counts and a slight increase in mean platelet count. While differences from control were slight the consistency of these findings at Month 1 and study termination suggests a relationship to administration of the test material. The high-dose males exhibited slight, statistically significant elevations in mean cholesterol levels at month 1 and termination. In addition, the mean albumin level of the high-dose males was significantly elevated at study termination. The high-dose females exhibited a slight (statistically significant) reduction in mean glucose levels at month 1 and at study termination (not statistically significant). The mid- and high-dose females exhibited slight (statistically significant) increases in mean calcium levels at 1 month. Slight (not statistically significant) increases were also noted in the mean calcium level of the mid- and high-dose females at study termination. A gross and microscopic correlation of lesions noted at necropsy revealed no evidence of a treatment associated response. Microscopic evaluation of the tissues revealed no histomorphical evidence of a direct toxicopathological effect. Tissues from control rats were comparable to those from the treated animals. There was, however, an increased incidence of a spontaneously occurring renal tubular lesions in high dose males when compared to control males. The lesion incidence in low and mild dose males was similar to that observed in controls. Females were essentially free of the lesion. The etiology and toxicopathological significance of the increased incidence rate in high dose males was unclear. Various other tissue alterations were encountered; however, they occurred sporadically or with approximately equal frequency and degree in control rats as in treated animals. They were judged to have had no treatment relationship. NOAEL was therefore set at 200 ppm in the diet, corresponding to nominal 12 mg/kg body weight/day which was shown to be after analytical verification 14.8 mg/kg bw7day in males and 17.0 mg/kg bw/day in females.
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