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EC number: 204-137-9 | CAS number: 116-37-0
- 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
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- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
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- Endpoint summary
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- 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
Endpoint summary
Administrative data
Description of key information
No relevant treatment-related findings were observed for clinical signs, clinical biochemistry, histopathological or reproductive parameters up to the dose-level of 180 mg/kg bw/day in a 90-day repeated toxicity study (OECD 408). Treatment related toxicity including mortality was evident at 250 and 500 mg/kg in a Combined 28 -day and reproduction screening study (OECD 422).
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 26 November 2013 to 26 February 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Version / remarks:
- September 1998
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.26 (Sub-Chronic Oral Toxicity Test: Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Version / remarks:
- May 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.3100 (90-Day Oral Toxicity in Rodents)
- Version / remarks:
- August 1998
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: 4. Japanese Chemical Substances Control Law 1973, Notification of Mar. 31 2012 by MHLW (0331 No.7), METI (No. 5) and MOE (No. 110331009).
- Version / remarks:
- March 2012
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Wistar (Han)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- - Source: Charles River Deutschland, Sulzfeld, Germany.
- Age at study initiation: Young adult animals (approx. 6 weeks old).
- Weight at study initiation: Body weight variation was within +/- 20% of the sex mean (males: 153 grams; females: 130 grams).
- Housing: Group housing of 5 animals per cage in labeled Macrolon cages.
- Diet: Free access to pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany).
- Water: Free access to tap water.
- Acclimation period: At least 5 days.
Environmental controls for the animal room were set to maintain 18 to 24°C, a relative humidity of 40 to 70%, approximately 15 room air changes/hour, and a 12-hour light/12-hour dark cycle. Any variations to these conditions were maintained in the raw data and had no effect on the outcome of the study.
IN-LIFE DATES: From: 26 November 2013 to 26 February 2014 - Route of administration:
- oral: gavage
- Vehicle:
- polyethylene glycol
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Formulations (w/w) were prepared daily within 6 hours prior to dosing, and were homogenized to visually acceptable levels. Adjustment was made for specific gravity of the vehicle. No correction was made for the purity of the test substance.
VEHICLE
- Justification for use and choice of vehicle: The same vehicle was used in the Combined 28-day repeated dose toxicity study with the reproduction/developmental toxicity screening test of LIN10001 4, 4’- Isopropylidenediphenol propoxylated (BPA+2PO) in rats by oral gavage (project 496519).
DOSE VOLUME:
5 ml/kg body weight. Actual dose volumes were calculated according to the latest body weight - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analyses were conducted according to a validated method (project 495511). Samples of formulations were analyzed for homogeneity (highest and lowest concentration) and accuracy of preparation (all concentrations, in Weeks 1, 6 and 13). Stability in vehicle over 6 hours at room temperature under normal laboratory light conditions (lowest concentration) and over 8 days in the refrigerator (highest and lowest concentration) was also determined (in Week 1).
The accuracy of preparation was considered acceptable if the mean measured concentrations were 90-110% of the target concentration for solutions. Homogeneity was demonstrated if the coefficient of variation was = 10%. Formulations were considered stable if the relative difference before and after storage was maximally 10%. - Duration of treatment / exposure:
- 90 days
- Frequency of treatment:
- Once daily, 7 d/w.
- Remarks:
- Doses / Concentrations:
0, 20, 60, 180 mg/kg bw/day
Basis:
actual ingested - No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
In a combined 28-day repeated dose toxicity study with the reproduction/developmental toxicity screening test of LIN10001 4, 4’- Isopropylidenediphenol propoxylated (BPA+2PO) in rats by oral gavage (project 496519), Wistar Han rats were dosed by oral gavage at 125, 250 and 500 mg/kg. Treatment related toxicity was evident at 250 and 500 mg/kg including mortality (3 animals at 250 mg/kg and 10 animals at 500 mg/kg), clinical signs (hunched posture, salivation, piloerection and lethargy, among others), changes in body weights, food consumption, haematology and clinical biochemistry parameters, and organ weight and organ to body weight ratios. Macroscopic and microscopic findings in the heart, stomach, brain, pituitary gland, kidneys, liver thymus, skeletal muscle, prostate gland, seminal vesicles, coagulation gland and ovaries were also noted. Additionally, impaired spermatogenesis was noted for males at 250 and 500 mg/kg. No toxicologically significant changes were noted in functional observations, and no toxicologically relevant effects were seen in any parameter at 125 mg/kg. - Positive control:
- Not required.
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS:
- Time schedule: At least twice daily. The time of death was recorded as precisely as possible.
DETAILED CLINICAL OBSERVATIONS:
- Time schedule: At least once daily from start of treatment onwards, detailed clinical observations were made in all animals immediately after dosing (based on the absence of a peak effect of occurrence of clinical signs in the dose range finding study (project 496584) conducted for the Combined 28-day repeated dose toxicity study with the reproduction/developmental toxicity screening test range finding study (project 496519). Once prior to start of treatment and at weekly intervals, this was also performed outside the home cage in a standard arena. The time of onset, grade and duration of any observed signs were recorded. Signs were graded for severity.
BODY WEIGHT:
- Time schedule for examinations: Weekly.
FOOD CONSUMPTION:
- Time schedule for examinations: Weekly.
WATER CONSUMPTION: no
OPHTHALMOSCOPIC EXAMINATION:
- Time schedule for examinations: at pretest : all animals, at Week 13: Groups 1 and 4.
HAEMATOLOGY:
- Time schedule for collection of blood: immediately prior to scheduled post mortem examination
- Anaesthetic used for blood collection: isoflurane
- Animals fasted: yes
- How many animals: all animals
- Parameters checked: According to test guidelines
CLINICAL CHEMISTRY:
- Time schedule for collection of blood: immediately prior to scheduled post mortem examination
- Anaesthetic used for blood collection: isoflurane
- Animals fasted: yes
- How many animals: all animals
- Parameters checked: According to test guidelines
URINALYSIS: no
NEUROBEHAVIOURAL EXAMINATION:
- Time schedule for examinations: During Week 12-13 of treatment
- Dose groups that were examined: Groups 1 and 4
- Battery of functions tested: hearing ability, pupillary reflex, static righting reflex and grip strength, motor activity test.
OTHER:
Estrous cycle determination: All females had a daily lavage from 05 February 2014 (Day 72) up to and including 25 February 2014 (Day 92) to determine the stage of estrous. - Sacrifice and pathology:
- GROSS PATHOLOGY:
- All animals were fasted overnight with a maximum of 24 hours prior to planned necropsy, but water was provided. Animals surviving to scheduled necropsy and all moribund animals were deeply anaesthetised and subsequently exsanguinated.
- Dose groups that were examined: all groups
- Tissues/organs checked: According to test guidelines
ORGAN WEIGHTS:
Organs checked according to test guidelines
HISTOPATHOLOGY:
According to test guidelines - Statistics:
- The following statistical methods were used to analyze the data:
- If the variables could be assumed to follow a normal distribution, the Dunnett-test (many-to-one t-test) based on a pooled variance estimate was applied for the comparison of the treated groups and the control groups for each sex.
- The Steel-test (many-to-one rank test) was applied if the data could not be assumed to follow a normal distribution.
- The Fisher Exact-test was applied to frequency data.
- The Kruskal-Wallis nonparametric ANOVA test was applied to motor activity data to determine intergroup differences.
All tests were two-sided and in all cases p < 0.05 was accepted as the lowest level of significance. Group means were calculated for continuous data and medians were calculated for discrete data (scores) in the summary tables. Test statistics were calculated on the basis of exact values for means and pooled variances. Individual values, means and standard deviations may have been rounded off before printing. - 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:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Description (incidence and severity):
- Based on subjective appraisal.
- 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):
- no effects observed
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- MORTALITY
One male at 180 mg/kg was found dead approximately 3 hours after dosing on Day 84, and one female at 180 mg/kg was found dead approximately 1 hour after dosing on Day 52. The female showed lethargy on the day of death, and no relevant clinical signs were shown by the male. Body weight gain was normal for these animals prior to death. At necropsy, both animals showed watery-clear fluid in the thoracic cavity. Histopathology revealed no cause of death. No further mortality occurred.
CLINICAL SIGNS
No toxicologically relevant clinical signs were recorded. One surviving female at 180 mg/kg showed hunched posture during the second half of the treatment period. As this clinical sign was not shown by other animals of the same dose group, this was considered to be of no toxicological relevance. Salivation seen after dosing among animals at 20, 60 and 180 mg/kg was considered to be a physiological response rather than a sign of systemic toxicity considering the nature and minor severity of the effect and its time of occurrence (i.e. after dosing). This sign may be related to taste of the test substance. Other incidental findings that were noted included scabs, rales, alopecia, chromodacryorrhoea and thickening of the genital region. These findings occurred within the range of background findings to be expected for rats of this age and strain which are housed and treated under the conditions in this study. At the incidence observed, these were considered signs of no toxicological significance.
BODY WEIGHT AND WEIGHT GAIN
Males at 180 mg/kg showed an apparent slightly lower body weight (gain) over the treatment period, being statistically significant for body weight gain in Week 2 only. Body weight (gain) among other male and female dose groups was similar to control levels.
FOOD CONSUMPTION
Food consumption before or after correction for body weight remained similar to the control level over the study period.
OPHTHALMOSCOPIC EXAMINATION
No toxicologically significant ophthalmology findings were noted. Incidental ophthalmology findings at pretest and/or in Week 13 consisted of (focal) corneal oedema or opacity, haemorrhage from the hyaloid vessel, pinpoint corneal opacities, and haemorrhagic discharge. The nature and incidence of these findings were within the range considered to be normal for rats of this age and strain.
HAEMATOLOGY
The following statistically significant changes in haematology parameters distinguished treated animals from control animals:
- Lower red blood cell counts in males and females at 180 mg/kg, and in females also at 60 mg/kg,
- Lower haemoglobin level in males and females at 180 mg/kg, and in females also at 60 mg/kg,
- Lower haematocrit level in females at 60 and 180 mg/kg,
- Higher mean corpuscular volume (MCV) in males at 180 mg/kg,
- Higher mean corpuscular haemoglobin (MCH) level in males at 180 mg/kg.
Means of the above parameters remained within the range considered normal for rats of this age and strain, except for the higher mean corpuscular volume which only slightly exceeded this normal range.
Any other statistically significant changes in haematology parameters were considered to be of no toxicological significance as they occurred in the absence of a dose-related trend and remained within the range considered normal for rats of this age and strain. The statistically significantly lower Prothrombin time (PT) of males at 60 and 180 mg/kg was considered to be of no toxicological relevance since the opposite effect (i.e. an increase) would be expected in case of target organ toxicity.
CLINICAL CHEMISTRY
The following statistically significant changes in clinical biochemistry parameters distinguished treated animals from control animals:
- Higher alanine aminotransferase activity (ALAT) in males at 180 mg/kg,
- Higher urea level in females at 60 and 180 mg/kg,
- Higher cholesterol level in males and females at 180 mg/kg,
- Lower potassium level in males at 60 and 180 mg/kg,
- Higher calcium level in females at 180 mg/kg,
- Higher inorganic phosphate level in males at 180 mg/kg.
Only cholesterol levels of males clearly exceeded the range considered normal for rats of this age and strain.
Any other statistically significant changes in clinical biochemistry parameters were considered to be of no toxicological significance as they occurred in the absence of a dose-related trend and remained within the range considered normal for rats of this age and strain.
NEUROBEHAVIOUR
Hearing ability, pupillary reflex, static righting reflex and grip strength were normal in all animals. Motor activity was similar between treated and control groups. All groups showed a similar motor activity habituation profile with high activity in the first interval that decreased over the duration of the test period.
ORGAN WEIGHTS
The following (statistically significant) changes in absolute organ weights and relative organ weights (organ to body weight ratio) were considered to be related to treatment:
- Higher liver to body weight ratio in males at 180 mg/kg (relative weight approximately 21% higher than controls; absolute liver weight also slightly higher but not statistically significant),
- Higher kidney to body weight ratio in males at 180 mg/kg (relative weight approximately 13% higher than controls; absolute kidney weight also slightly higher but not statistically significant),
- Higher adrenal to body weight ratio in males at 180 mg/kg (relative weight approximately 25% higher than controls)
- Lower heart to body weight ratio in females at 180 mg/kg (relative weight approximately 10% lower than controls),
- Trend towards higher ovary weight among female dose groups (relative weight at 180 mg/kg approximately 24% higher than controls).
The statistically significantly higher prostate weight at 60 mg/kg was considered to be of no toxicological significance as this change occurred in the absence of a dose-related trend and remained within the range considered normal for rats of this age and strain.
GROSS PATHOLOGY
Necropsy did not reveal any toxicologically relevant alterations. The incidence of necropsy findings among control and treated animals was within the background range of findings that are encountered among rats of this age and strain, did not show a dose-related incidence trend and/or had no treatment-related histopathological correlates. These necropsy findings were therefore considered to be of no toxicological relevance.
HISTOPATHOLOGY
The following histopathological changes were considered to be related to treatment:
- Interstitial cell hypertrophy in the interstitial gland of the ovaries in 6/10 females at 60 mg/kg (6, minimal) and in 7/10 females at 180 mg/kg (5 minimal, 2 slight).
- Centrilobular hepatocellular hypertrophy of the liver in 7/10 males (including the unscheduled death at Day 84) at 180 mg/kg (4 minimal, 3 slight).
Spermatogenic staging profiles were normal for all animals assessed. All other microscopic findings were within the range of background pathology encountered in Wistar rats of this age and strain and occurred at similar incidences and severity in both control and treated rats.
OTHER FINDINGS
Estrous cycle determination: Estrous cycle length was normal for all examined females at 20, 60 and 180 mg/kg. One control female showed an extended estrus cycle length, the incidence of which is within the range considered normal for rats of this age and strain. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 180 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
- Critical effects observed:
- not specified
- Conclusions:
- In this oecd408 study with rats, the NOAEL was determined to be at least 180 mg/kg bw/day.
- Executive summary:
An OECD 408 study (Sub-chronic toxicity study (90-day), oral route (gavage) in rats) was performed with the 4,4’-Isopropylidenediphenol, propoxylated (BPA+2PO) at the dose-levels of 0, 20, 60 and 180 mg/kg bw/day with approval of ECHA for the 2010 Reach registration dossier. The test substance, formulated in polyethylene glycol 400, was administered daily for at least 90 days by oral gavage to SPF-bred Wistar rats. One control group and three treated groups were tested, each consisting of 10 males and 10 females. Chemical analyses of formulations preparations were conducted during the study to assess accuracy,
homogeneity and stability over 6 hours. The following parameters were evaluated: clinical signs daily; functional observation tests in Week 12; body weight and food consumption weekly; ophthalmoscopy at pretest and in Week 13; estrous cycle determination; clinical pathology and macroscopy at termination; organ weights and histopathology on a selection of tissues including spermatogenic staging profiles assessment.
Formulation analyses confirmed that formulations of test substance in polyethylene glycol 400 were prepared accurately and homogenously, and were stable over at least 6 hours.
Two animals given180 mg/kg (one male and one female) were found dead between after dosing on Day 84 and 52, respectively. Histopathology revealed no cause of death but the presence of watery-clear fluid in the thoracic cavity in both of these animals suggest that these deaths were due to a gavage incident.
A number of changes in red blood cell parameters were noted in both sexes at 60 and 180 mg/kg, including lower red blood cell counts, lower haemoglobin and haematocrit level, and higher mean corpuscular volume and mean corpuscular haemoglobin. Means remained essentially within the range considered normal for rats of this age and strain, and no morphological correlates indicative of increased breakdown or production of red blood cells were noted. Therefore, these haematological changes were considered not indicative of an adverse effect on red blood cell turn over. The higher liver to body weight ratio in males at 180 mg/kg corresponded with the centrilobular hepatocellular hypertrophy of the liver observed in most at 180 mg/kg (up to slight degree). Given the low severity of liver hypertrophy, absence of morphological liver findings, and only slight potentially supportive clinical biochemistry changes (higher cholesterol and higher alanine aminotransferase activity in males), these findings were considered adaptive and not adverse in nature. The higher cholesterol levels of females at 180 mg/kg occurred without any apparent morphological correlates.
Other clinical biochemistry changes at 180 mg/kg included lower potassium level (males), higher urea and calcium level (females), and higher inorganic phosphate level (males). At 60 mg/kg, clinical biochemistry changes were confined to lower potassium level (males) and higher urea level (females). As these changes were slight in nature and also occurred in the absence of any supportive morphological changes, these were considered not to be adverse in nature.
Reproductive parameters assessed in this study revealed no adverse changes. The trend towards higher ovary weight among female dose groups was considered to be related to the interstitial cell hypertrophy in the interstitial gland of the ovaries in most females at 60 and 180 mg/kg (up to slight degree). Ovaries are steroid synthezing organs and play a major role in the endocrine system and reproductive system. The main precursor for the production of all steroid hormone synthesis is cholesterol (or cholesterylesters), that can be stored intracellular as lipid droplets in the ovary. The histologic morphology of the recorded interstitial cell hypertrophy, with fine vacuolar appearance is suggestive for an exaggerated lipid storage which can lead to increased organ weight. Since estrous cycle length was normal for all examined females at 20, 60 and 180 mg/kg and the interstitial gland hypertrophy was of a low severity, this finding was considered to be non-adverse.
Spermatogenic staging profiles were normal for all animals assessed.
No histopathological correlates were found for the higher adrenal and kidney to body weight ratio in males and lower heart weight in females at 180 mg/kg. Therefore, these changes were considered not to be of toxicological relevance.
No relevant clinical signs were noted during treatment. Functional observation tests revealed no abnormalities, and ophthalmoscopy showed no treatment-related changes. The slightly lower body weight gain of males at 180 mg/kg was only minor in nature and well within the range considered normal for rats of this age and strain, and was therefore considered to be of no toxicological relevance.
No changes in food intake occurred.
From the results presented above, a No Observed Adverse Effect Level (NOAEL) for 4,4’-Isopropylidenediphenol, propoxylated (BPA+2PO) of at least 180 mg/kg was established.
Reference
Accuracy of preparation: The concentrations analysed in formulations of Group 2, Group 3 and Group 4 were in agreement with target concentrations (i.e. mean accuracies between 90% and 110%). No test substance was detected in Group 1 formulations.
Homogeneity: Formulations of Group 2 and Group 4 were homogeneous (i.e. coefficient of variation = 10%).
Stability: The Group 2 formulation was stable when stored at room temperature under normal laboratory light conditions for at least 6 hours. Formulations of Group 2 and Group 4 were stable when stored in a refrigerator for at least 8 days.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 180 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- GLP study which meets the Annex IX chapter 8.6.2 requirements.
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Quality of whole database:
- REACH Guidance Document R.7.a, Chapter. 7.4 Acute toxicity, indicates that in principle no inhalation studies are needed when vapour pressure < 0.1 Pa at 20°C or particle size > 100 µm. The substance is a viscous liquid with a very negligible vapour pressure at 20°C. The use of the substance is limited to industrial and professional users and does not involve the forming of aerosols, particles or droplets of an inhalable size. Exposure to humans via the inhalation route is considered unlikely to occur. There is no justification to perform further animal studies.
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Quality of whole database:
- REACH Guidance Document R.7.a, Chapter. 7.4 Acute toxicity, indicates that in principle no inhalation studies are needed when vapour pressure < 0.1 Pa at 20°C or particle size > 100 µm. The substance is a viscous liquid with a very negligible vapour pressure at 20°C. The use of the substance is limited to industrial and professional users and does not involve the forming of aerosols, particles or droplets of an inhalable size. Exposure to humans via the inhalation route is considered unlikely to occur. There is no justification to perform further animal studies.
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Combined 28 -day and reproduction screening study
1,1'-isopropylidenebis(p-phenyleneoxy)dipropan-2 –ol was administered by daily oral gavage to male and female Wistar Han rats at dose levels of 125, 250 and 500 mg/kg/day. Males were exposed for 2 weeks prior to mating, during mating, and up to termination (for 29 days). The females were exposed for 2 weeks prior to mating, during mating, during post-coitum, and at least 4 days of lactation (for 43-54 days). Formulation analysis showed that the formulations were prepared accurately, were homogenous, and were stable for at least 6 hours at room temperature.
Parental results: Treatment related toxicity was evident at 250 and 500 mg/kg including mortality (3 animals at 250 mg/kg and 10 animals at 500 mg/kg), clinical signs (hunched posture, salivation, piloerection and lethargy, among others), changes in body weights, food consumption, haematology and clinical biochemistry parameters, and organ weight and organ to body weight ratios. Macroscopic and microscopic findings in the heart, stomach, brain, pituitary gland, kidneys, liver thymus, skeletal muscle, prostate gland, seminal vesicles, coagulation gland and ovaries were also noted. Additionally, impaired spermatogenesis were noted for males at 250 and 500 mg/kg/d.
No toxicologically significant changes were noted in functional observations, and no toxicologically relevant effects were seen in any parameter at 125 mg/kg bw/day. Therefore, the parental NOAEL was set at 125 mg/kg bw/day.
90 -day repeated toxicity study
An OECD 408 study (Sub-chronic toxicity study (90-day), oral route (gavage) in rats) was performed with the 1,1'-isopropylidenebis(p-phenyleneoxy)dipropan-2 –ol at the dose-levels of 0, 20, 60 and 180 mg/kg bw/day with approval of ECHA for the 2010 Reach registration dossier. The test substance, formulated in polyethylene glycol 400, was administered daily for at least 90 days by oral gavage to SPF-bred Wistar rats. One control group and three treated groups were tested, each consisting of 10 males and 10 females.
Chemical analyses of formulations preparations were conducted during the study to assess accuracy, homogeneity and stability over 6 hours.
The following parameters were evaluated: clinical signs daily; functional observation tests in Week 12; body weight and food consumption weekly; ophthalmoscopy at pretest and in Week 13; estrous cycle determination; clinical pathology and macroscopy at termination; organ weights and histopathology on a selection of tissues including spermatogenic staging profiles assessment.
Formulation analyses confirmed that formulations of test substance in polyethylene glycol 400 were prepared accurately and homogenously, and were stable over at least 6 hours.
Two animals given180 mg/kg (one male and one female) were found dead between approximately 1 and 3 hours after dosing on Day 84 and 52, respectively. Histopathology revealed no cause of death. Signs of imminent death were absent by these or other animals of the same dose group or lower dose groups, no further mortality occurred in this study and animals were found dead within a short time period after dosing. In the previous study (i.e. combined 28-day repeated dose toxicity study with the reproduction/developmental toxicity screening test) 3 animals at 250 mg/kg and 10 animals at 500 mg/kg were found dead/sacrificed. The microscopic lesions that were thought to contribute to their moribundity in that study were absent in this study. Overall, this suggests that these deaths were unrelated to a toxicological effect of the test substance. The presence of watery-clear fluid in the thoracic cavity in both of these animals may suggest that these deaths were due to a gavage incident (the formulation was a clear solution).
A number of changes in red blood cell parameters were noted in both sexes at 60 and 180 mg/kg, including lower red blood cell counts, lower haemoglobin and haematocrit level, and higher mean corpuscular volume and mean corpuscular haemoglobin. Means remained essentially within the range considered normal for rats of this age and strain, and no morphological correlates indicative of increased breakdown or production of red blood cells were noted. Therefore, these haematological changes were considered not indicative of an adverse effect on red blood cell turn over. The higher liver to body weight ratio in males at 180 mg/kg corresponded with the centrilobular hepatocellular hypertrophy of the liver observed in most at 180 mg/kg (up to slight degree). Given the low severity of liver hypertrophy, absence of morphological liver findings, and only slight potentially supportive clinical biochemistry changes (higher cholesterol and higher alanine aminotransferase activity in males), these findings were considered adaptive and not adverse in nature. The higher cholesterol levels of females at 180 mg/kg occurred without any apparent morphological correlates.
Other clinical biochemistry changes at 180 mg/kg included lower potassium level (males), higher urea and calcium level (females), and higher inorganic phosphate level (males). At 60 mg/kg, clinical biochemistry changes were confined to lower potassium level (males) and higher urea level (females).
As these changes were slight in nature and also occurred in the absence of any supportive morphological changes, these were considered not to be adverse in nature.
Reproductive parameters assessed in this study revealed no adverse changes. The trend towards higher ovary weight among female dose groups was considered to be related to the interstitial cell hypertrophy in the interstitial gland of the ovaries in most females at 60 and 180 mg/kg (up to slight degree). Ovaries are steroid synthezing organs and play a major role in the endocrine system and reproductive system. The main precursor for the production of all steroid hormone synthesis is cholesterol (or cholesterylesters), that can be stored intracellular as lipid droplets in the ovary. The
histologic morphology of the recorded interstitial cell hypertrophy, with fine vacuolar appearance is suggestive for an exaggerated lipid storage which can lead to increased organ weight. Since estrous cycle length was normal for all examined females at 20, 60 and 180 mg/kg and the interstitial gland hypertrophy was of a low severity, this finding was considered to be non-adverse.
Spermatogenic staging profiles were normal for all animals assessed.
No histopathological correlates were found for the higher adrenal and kidney to body weight ratio in males and lower heart weight in females at 180 mg/kg. Therefore, these changes were considered not to be of toxicological relevance.
No relevant clinical signs were noted during treatment. Functional observation tests revealed no abnormalities, and ophthalmoscopy showed no treatment-related changes. The slightly lower body weight gain of males at 180 mg/kg was only minor in nature and well within the range considered normal for rats of this age and strain, and was therefore considered to be of no toxicological relevance.
No changes in food intake occurred.
From the results presented above, a No Observed Adverse Effect Level (NOAEL) for 1,1'-isopropylidenebis(p-phenyleneoxy)dipropan-2 –ol of at least 180 mg/kg was established.
Justification for classification or non-classification
Based on the results available, 1,1'-isopropylidenebis(p-phenyleneoxy)dipropan-2 –ol does not have to be classified currently and has no obligatory labelling requirement for repeated dose toxicity according to the:
- Globally Harmonized System of Classification and Labelling of Chemicals (GHS) of the United Nations (2007),
- Regulation (EC) No 1272/2008 on classification, labelling and packaging of substances and mixtures.
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