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EC number: 272-599-9 | CAS number: 68892-13-7
- 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
Endpoint summary
Administrative data
Description of key information
In a GLP-compliant OECD Test guideline 422 study performed in rats, the registered substance 1 -phenyldecane-1,3 -dione administered by oral gavage at dose levels of 100, 300 and 1000 mg/kg/day induced no adverse effects up to the highest dose level. The No Observed Adverse Effect Level (NOAEL) was therefore 1000 mg/kg bw/day.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 08 December 2015 to 21 July 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- March 1996
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Batch No.of test material: MR92143651
- Expiration date of the lot/batch: 01 January 2017
- Purity: 86.4% (No correction was made for purity of the test substance)
- Purity test date: 18 June 2015
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: At room temperature
- Stability under test conditions: Yes, maximum temperature: 50°C, maximum duration: unknown (until liquefaction).
- Solubility and stability of the test substance in the solvent/vehicle: Stability of the test item in the vehicle for the range of concentration 0.5 to 100 mg/mL: 8 Days when stored at room temperature (+ 15 to + 25°C) or refrigerated (+ 2 to + 8°C) (validation study no. AB21059; data not shown).
- Reactivity of the test substance with the solvent/vehicle of the cell culture medium: Not assessed.
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: The preparation was warmed in a water bath at 40°C ± 5°C (except for the fourth preparation of group 3 and 4, warmed in a water bath at 47.3 °C and 46.9 °C, respectively. However the temperatures of preparations were measured and were below 45°C) under magnetic stirring for at least 10 minutes until a solution is obtained. The test item was prepared as a solution in the vehicle at concentrations of 10, 30 and 100 mg/mL.
- Preliminary purification step (if any): N/A
- Final dilution of a dissolved solid, stock liquid or gel: N/A
- Final preparation of a solid: N/A
FORM AS APPLIED IN THE TEST (if different from that of starting material): N/A - Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, Domaine des Oncins, 69210 Saint-Germain-Nuelles, France.
- Females (if applicable) nulliparous and non-pregnant: N/A
- Age at study initiation: Virgin males: approximately 10 Weeks ; Virgin females: approximately 8 Weeks.
- Weight at study initiation: males: 298 to 339 g; females: 164 to 214 g.
- Fasting period before study: All animals were fasted for approximately 16 hours before sampling for clinical laboratory determinations.
- Housing: Male rats (throughout the study except during mating) and female rats (during the pre-mating period) were housed in groups of 5 of the same sex and dose group in plastic cage meeting European directive 2010/63/EU requirements. During cohabitation with males and during gestation and lactation (together with their litter), females were housed individually in plastic cage meeting European directive 2010/63/EU requirements.
- Diet (e.g. ad libitum): Rat pelleted commercial complete rodent diet ad libitum (Diet reference Safe, A04C-10).
- Water (e.g. ad libitum): Softened and filtered (0.2 μm) mains drinking water was available ad libitum.
- Acclimation period: 7 Days between animal arrival and the start of treatment
DETAILS OF FOOD AND WATER QUALITY:
Rat pelleted commercial complete rodent diet sterilised by irradiation and analysed for a predefined list of chemical and bacteriological contaminants. Each batch of diet is supplied with a certificate of analysis which is verified and authorized for release by a veterinarian.
Water is analysed twice a year for chemical and bacterial contaminants by Laboratoire Santé Environnement Hygiène de Lyon, France.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 + 3°C (target range).
- Humidity (%): > 35% (target).
- Air changes (per hr): At least 10 air changes per hour.
- Photoperiod (hrs dark / hrs light): 12 hours light (artificial)/12 hours dark (except when required for technical acts).
IN-LIFE DATES: From: 08 December 2015 To: 26 January 2016 - Route of administration:
- oral: gavage
- Details on route of administration:
- Gavage using a plastic cannula.
- Vehicle:
- corn oil
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Preparation:
The test item was prepared as a solution in the vehicle..
Method:
The test item was weighed and then the vehicle was added. The preparation was warmed in a water bath at 40°C ± 5°C under magnetic stirring for at least 10 minutes until a solution is obtained.
VEHICLE
- Justification for use and choice of vehicle (if other than water): Corn oil was chosen because it allowed to prepare appropriate concentrations of the test item.
- Concentration in vehicle: 10, 30 and 100 mg/mL
- Amount of vehicle (if gavage): 10 mL/kg/Day
- Lot/batch no. (if required): 14090129/B
- Purity: 100% - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analysis of preparations::
Four samples of 1 g were taken from each formulation, including the vehicle, used on the first Day of treatment and on a suitable Day during each of the third and penultimate Weeks of treatment. The samples were stored at room temperature (+ 15 to + 25°C).
One set of samples was analysed at the Test Facility, within the defined stability period (see above), using a validated method. The transfer and validation of the analytical method was the subject of a separate study (study number AB21059). - Duration of treatment / exposure:
- Males: 14 Days before mating, throughout the mating period and up to the Day before necropsy.
Females: 14 Days before mating, throughout the mating period, during gestation (the first Day of gestation is designated as G0) and up to to 4 Days after parturition (the first Day of birth is designated as L0). Mated females that failed to produce a viable litter: until Day 25 or 26 post-coitum. Unmated female: for 20 Days after the last Day of the mating period. - Frequency of treatment:
- Once daily.
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 10 rats/sex/dose
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: In the absence of severe clinical signs during the DRF phase, the same dose levels were selected for the main study phase/
- Rationale for animal assignment (if not random): Performed during the acclimatisation period, using a computer-generated randomisation. The mean body weight of each group at allocation was not statistically significantly different from each other (analysis of variance), each sex being considered separately.
- Rationale for selecting satellite groups: N/A
- Post-exposure recovery period in satellite groups: N/A
- Section schedule rationale (if not random): N/A - Positive control:
- No
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes / No / Not specified
- Time schedule: All adults were observed twice daily at the beginning and at the end of each working Day (including Weekends and public holiDays) to detect any which were moribund. Animals judged to be in a moribund condition were necropsied. A full clinical examination was performed on each weighing Day.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: All animals were observed daily for clinical signs During the treatment period, the animals were observed before and at least once after treatment to detect any abnormalities in appearance, behaviour or other signs of reaction to treatment.
BODY WEIGHT: Yes
- Time schedule for examinations: Individual body weights for males were recorded Weekly. Individual body weights for females were recorded:
− Weekly during pre-mating and mating periods (only pre-mating data was reported)
− on Days 0, 7, 14 and 20 of gestation
− on Days 1 and 4 of lactation.
FOOD CONSUMPTION: Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
FOOD EFFICIENCY: N/A
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
- Time schedule for examinations:
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY AND CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: At the end of the pre-mating period (Day 14).
- Anaesthetic used for blood collection: Blood was withdrawn from the retro-orbital sinus under isoflurane anaesthesia (AErrane®, Baxter SA)
- Animals fasted: Yes ( for at least 16 hours)
- How many animals: Five randomly selected animals/sex/group.
- Parameters checked in table no. 7.5.1.1 were examined.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: Yes.
- Time schedule for examinations: Males: at the end of the treatment period, the Day before necropsy (Day 31). Females: during lactation, shortly before necropsy (Day 4 of lactation).
- Dose groups that were examined:
- Battery of functions tested: The following tests were performed: auditory reflex, pupillary reflex, righting reflex, fore- and hind-limb grip strength and locomotor activity in an open field test.
Activity was monitored by a video image analysis system (Videotrack supplied by Viewpoint, Lyon, France). The arena was divided into nine equal invisible regions; the time spent by the animal in each type of region (i.e. corner, centre or lateral) was recorded. Motor activity was divided into three categories: ambulatory activity (in which the centre of the image moved at more than 7 cm/sec), small movements (including grooming etc.) and inactivity. The proportion of time spent engaged in each type of activity and the total distance travelled by the rat was calculated.
IMMUNOLOGY: No
OTHER: No - Sacrifice and pathology:
- Terminal Examinations
Moribund adults and females showing signs of parturition difficulties or total litter death were killed by carbon dioxide inhalation and exsanguination then necropsied.
Surviving adult animals were killed by carbon dioxide inhalation followed by exsanguination then necropsied according to the following schedule:
− males: after completion of the mating period (31 Days of oral administration)
− females: on Day 4 of lactation (mated females that failed to produce a viable litter by Day 26 or 27 post-coitum were killed and necropsied)
− apparently unmated female: 21 Days after the last Day of the mating period (Day 50).
GROSS PATHOLOGY: Yes (see list of organs examined in table 7.8.1.2)
HISTOPATHOLOGY: Yes (see list of organs/tissues examined table 7.8.1.2) - Other examinations:
- Mating; pregnancy and parturition, and Litter data. Data described in section 7.8.1 (Toxicity to reproduction)
- Statistics:
- The following parameters were analysed statistically on each occasion for males and females separately, by the Provantis data acquisition system:
− body weights and body weight gains, food consumption, gripping test, open field test, haematology, coagulation and serum clinical chemistry parameters, pre-coital interval,terminal body weights, absolute and relative organ weights.
The best transformation for the data (none, log or rank) was determined depending upon the kurtosis of the data, the probability of the Bartlett's test for homogeneity of the variances and the similarity of the group sizes. Non- or log-transformed data were analysed by parametric methods. Rank transformed data were analysed using non-parametric methods. The homogeneity of means was assessed by analysis of variance (ANOVA).
Data were then analysed to test for a dose-related trend to detect the lowest dose at which there was a significant effect, based on the Williams test for parametric data or Shirley's test for non-parametric data.
If no trend was found and the means were not homogeneous, the data were analysed by a stepwise parametric or non-parametric Dunnett's test to look for significant differences from the control group.
Open field test and pre-coital interval data were analysed using a SAS software package. Levene’s test will be used to test the equality of variance across groups and Shapiro-Wilk's test will be used to assess the normality of the data distribution in each group. Data with homogeneous variances and normal distribution in all groups will be analysed using ANOVA followed by Dunnett’s test. Data showing non homogeneous variances or a non-normal distribution in at least one group will be analysed using Kruskal-Wallis test followed by Wilcoxon's rank sum test. - Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Two females given 1000 mg/kg/Day had decreased activity and/or piloerection noted after the first administration only. There were no test item-related clinical signs for females given 100 and 300 mg/kg/Day and for males at all dose levels.
Vehicle-related clinical signs included hypersalivation, abnormal foraging and pedalling and were observed in all groups. - Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One female in each of the control (no. 115) and 1000 mg/kg/Day (no. 172) groups were sacrificed in moribund condition on G 24 and 23, respectively. Female no. 115 was sacrificed moribund after giving birth to 10 stillborn pups and female no. 172 was unable to deliver. Before sacrifice, both females presented decreased activity, pallor, marked piloerection, subdued and/or rapid breathing. At necropsy, the cause of the poor health of both females could not be determined.
In addition, one female in each of the 100 and 1000 mg/kg/Day groups (nos. 137 and 176, respectively) were euthanized following total litter death on L 1 or L4, respectively. - Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Males:
There was a lower mean body weight gain from Day 1 to Day 15 for males given 1000 mg/kg/Day (- 66%) when compared with the control. Thereafter, body weight gain improved but the overall mean body weight gain (Day 1 to Day 29) remained lower (- 40%), with an absolute mean body weight at the end of the treatment period statistically significantly lower compared with the control group (- 7%).
A lower mean body weight gain from Day 8 to Day 15 was also observed for males given 300 mg/kg/Day compared with the control but at a lesser intensity (- 27%). However, terminal mean body weight remained comparable with the control group.
There was no obvious effect of treatment on mean body weight gain or absolute body weight for males at 100 mg/kg/Day.
Females:
There was a lower mean body weight gain from Day 7 to 20 of gestation for females given 1000 mg/kg/Day (-20 %) when compared with the control.
There was no obvious test item-related effect on mean body weight or body weight gain during the pre-mating or lactation periods at any dose level, or during the gestation period at 100 and 300 mg/kg/Day. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Males:
There was a slightly lower mean food consumption between Day 1 to Day 8 for males given 1000 mg/kg/Day (- 11%) when compared with the control.
There was no obvious effect on mean food consumption for males treated at lower doses.
Females:
There was a dose-related lower mean food consumption between Day 1 to Day 4 of lactation for females given 300 and 1000 mg/kg/Day (- 17% and - 21%, respectively) when compared with the control.
There was no obvious effect on mean food consumption for females during the pre-mating or gestation period at any dose level and during the lactation period at 100 mg/kg/Day.
In addition, when compared with the historical control data (see Addendum 6), there was a lower mean food consumption for both sexes during the pre-mating, gestation and/or lactation periods in all groups receiving the vehicle with or without the test item. This finding was therefore considered to be associated with the vehicle (i.e. corn oil). - Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- On Day 14, there was no obvious effect of treatment on haematology or coagulation parameters for males or females at any dose level.
- Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- On Day 14, there was no obvious effect of treatment on serum clinical chemistry parameters for males or females at any dose level.
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Description (incidence and severity):
- There was no obvious effect of treatment on the auditory, pupillary and, righting reflexes, or on the gripping and open field tests for the males or females at any dose level.
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- The liver weight was increased for both sexes at 1000 mg/kg/Day and for males given 300 mg/kg/Day. The liver weight increase for females at 300 mg/kg/Day was only marginal.
There was increased weight of thyroids which was observed at all dose levels, except for females given 300 mg/kg/Day. - Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- The liver was enlarged at necropsy for males given 1000 mg/kg/Day.
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- The increase in liver weight correlated with minimal test item-related centrilobular hepatocellular hypertrophy, which was noted for both sexes at 300 and 1000 mg/kg/Day.
In the thyroid glands, there was a minimal diffuse follicular cell hypertrophy at all dose levels for both sexes. - Histopathological findings: neoplastic:
- not examined
- Details on results:
- The changes in the liver at 300 and 1000 mg/kg/Day and in the thyroid glands at all dose levels.are considered adaptive non-adverse reactions likely the consequence of hepatic enzyme induction.
In view of the changes in the thyroid glands, no NOEL could be established in this study. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No adverse effects observed up to the highest dose tested
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- Oral (gavage) administration of 1-Phenyldecane-1,3-dione at doses of 100, 300 and 1000 mg/kg/Day was associated with a transient reduction in body weight gain and/or food consumption for males and females at 300 and 1000 mg/kg/Day. In addition, adaptative non-adverse test item-related changes in the liver at 300 and 1000 mg/kg/Day and in the thyroid glands at all dose levels were observed. The No Observed Adverse Effect Level (NOAEL) for parental toxicity is therefore 1000 mg/kg/Day.
- Executive summary:
The objectives of this study were to evaluate the potential toxic effects of the test item, 1-Phenyldecane-1, 3-dione, when exposed for a minimum of 28 Days and the potential to affect male and female reproductive performance such as gonadal function, mating behaviour, conception, parturition and early postnatal development. Parental, reproduction (up to and including implantation) and developmental (from implantation onwards) No-Observed-Adverse-Effect-Levels (NOAELs) were evaluated. This GLP study was carried out according to OECD test guideline No. 422 (March 1996).
Three groups of 10 male and 10 female Wistar Han rats were given the test item, 1-Phenyldecane-1,3-dione, by daily oral (gavage) administration at dose levels of 100, 300 and 1000 mg/kg/Day from 14 Days before mating (Day 1) until Day 31 for males or until Day 4 of lactation for females. A control group of 10 male and 10 female Wistar Han rats was given 10 mL/kg/Day of the vehicle (corn oil).
Clinical condition, body weight and food consumption of the animals were monitored throughout the study. Clinical laboratory determinations were performed at the end of the pre-mating period (Day 14). After two Weeks of treatment, one male and one female of the same group were paired for a maximum of 14 Days. The females were allowed to give birth and litter parameters, including the number of pups born, pup survival, sex and pup weights were recorded up to postnatal Day 4. Functional tests were performed at the end of the treatment period for 5 selected males in each group and on Day 4 of lactation for 5 selected females in each group.
The males were necropsied after the pairing period. The dams and pups were necropsied on Day 4 of lactation. All animals were submitted to a macroscopic examination and selected organs were weighed. Selected organ/tissue samples were fixed and preserved at necropsy for half of the animals/group and reproductive organs samples were fixed and preserved at necropsy from all animals. Histopathological examinations were performed on selected organs/tissues from animal killed moribund, from half of the group 1 and 4 animals killed at the end of the treatment period, from all males suspected to be infertile or that failed to sire, and from all females that failed to deliver healthy pups.
There was no obvious test item-related mortality in any group. However, one female in each of the control and 1000 mg/kg/Day groups were sacrificed in a moribund condition following dystocia.
Two females given 1000 mg/kg/Day had decreased activity and/or piloerection noted after the first administration only. There were no test item-related clinical signs for females given 100 and 300 mg/kg/Day and for males at all dose levels.
There was a reduced body weight gain for males given 300 (from Day 8 to Day 15) and 1000 mg/kg/Day (from Day 1 to Day 15), and for females given 1000 mg/kg/Day (from Days 7 to 20 of gestation).
There was a reduce food consumption for males given 1000 mg/kg/Day (from Day 1 to Day 8) and for females given 300 and 1000 mg/kg/Day (from Day 1 to Day 4 of lactation).
On Day 14, there was no obvious effect of treatment on haematology, coagulation and serum clinical chemistry parameters from males or females at any dose level.
There was no obvious effect of treatment on functional tests (i.e. auditory reflex, pupillary test, righting reflex, gripping test or open field test) for either sex at any dose level.
Adaptative non-adverse test item-related changes were observed in the liver (i.e. centrilobular hepatocellular hypertrophy) for both sexes at 1000 mg/kg/Day and for males given 300 mg/kg/Day and the thyroid glands (i.e. diffuse follicular cell hypertrophy) at all dose levels for both sexes. There were no test item-related pathological changes in the male or female genital system.
It should be noted that there was some vehicle-related effects including clinical signs (i.e. hypersalivation, abnormal foraging, pedalling and straub tail), reduce food consumption (consistent with the oily nature of the vehicle), a suspected prolongation of gestation and higher pre-birth loss.
In conclusion, oral (gavage) administration of 1-Phenyldecane-1,3-dione at doses of 100, 300 and 1000 mg/kg/Day was associated with a transient reduction in body weight gain and/or food consumption for males and females at 300 and 1000 mg/kg/Day. In addition, adaptative non-adverse test item-related changes in the liver at 300 and 1000 mg/kg/Day and in the thyroid glands at all dose levels were observed. The No Observed Adverse Effect Level (NOAEL) for parental toxicity is therefore 1000 mg/kg/Day.
Reference
Formulation Analysis:
No test item was detected in the vehicle sample.
Achieved concentration of formulation of 1-Phenyl decane-1.3-dione at 10, 30 and 100 mg/mL in corn oil as vehicle used for the first Day of treatment and on the third and penultimate Week of treatment, were in agreement with acceptance criteria with a deviation from nominal concentration ranging from - 9.9% to - 1.7%.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Fully reliable study (OECD 422 and GLPs compliant)
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
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
In a GLP-compliant repeated dose toxicity study performed according to OECD Test guideline 422, 1-Phenyldecane-1, 3-dione was administered by oral gavage to three groups of 10 male and 10 female Wistar Han rats at dose levels of 100, 300 and 1000 mg/kg/Day from 14 Days before mating (Day 1) until Day 31 for males or until Day 4 of lactation for females. A control group of 10 male and 10 female Wistar Han rats was given 10 mL/kg/Day of the vehicle (corn oil).
There was no obvious test item-related mortality in any group. However, one female in each of the control and 1000 mg/kg/Day groups were sacrificed in a moribund condition following dystocia.
Two females given 1000 mg/kg/Day had decreased activity and/or piloerection noted after the first administration only. There were no test item-related clinical signs for females given 100 and 300 mg/kg/Day and for males at all dose levels.
There was a reduced body weight gain for males given 300 and 1000 mg/kg/Day and for females given 1000 mg/kg/Day.
There was a reduce food consumption for males given 1000 mg/kg/Day and for females given 300 and 1000 mg/kg/Day.
On Day 14, there was no obvious effect of treatment on haematology, coagulation and serum clinical chemistry parameters from males or females at any dose level.
There was no obvious effect of treatment on functional tests (i.e. auditory reflex, pupillary test, righting reflex, gripping test or open field test) for either sex at any dose level.
Adaptative non-adverse test item-related changes were observed in the liver (i.e. centrilobular hepatocellular hypertrophy) for both sexes at 1000 mg/kg/Day and for males given 300 mg/kg/Day and the thyroid glands (i.e. diffuse follicular cell hypertrophy) at all dose levels for both sexes. There were no test item-related pathological changes in the male or female genital system.
Based on these results, the No Observed Adverse Effect Level (NOAEL) for parental toxicity is therefore 1000 mg/kg/Day.
Justification for classification or non-classification
The registered substance 1-phenyldecane-1,3-dione is not classified for repeated dose toxicity according to CLP and GHS-UN regulations because no adverse effects have been reported in an OECD Test guideline 422 rat study up to the highest recommended dose level of 1000 mg/kg bw/day.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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