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EC number: 460-110-3 | CAS number: 797751-43-0 WASOX-MMAC2
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- one-generation reproductive toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- July 11, 2007 - April 21, 2008
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Test method according to OECD 415. GLP study.
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 009
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 415 [One-Generation Reproduction Toxicity Study (before 9 October 2017)]
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- 4-methylpentan-2-one oxime
- EC Number:
- 203-298-2
- EC Name:
- 4-methylpentan-2-one oxime
- Cas Number:
- 105-44-2
- IUPAC Name:
- 4-methylpentan-2-one oxime
- Details on test material:
- - Name of test material (as cited in study report): Methyl isobutil ketoxime (MIBKO)
- Molecular formula (if other than submission substance): C6H13NO
- Molecular weight (if other than submission substance): 115.1735
- Smiles notation (if other than submission substance): CC(C)CC(\C)=N\O
- InChl (if other than submission substance): 1/C6H13NO/c1-5(2)4-6(3)7-8/h5,8H,4H2,1-3H3/b7-6+
- Structural formula attached as image file (if other than submission substance): see Fig.
- Source: Honeywell International (Claymont, Delaware)
- Purity: 99.9%
- Lot/batch No.: 061001
- Expiration date of the lot/batch: 25 October 2007
- Others: MIBKO was obtained as a pure, clear, colorless solution.
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 (UK) Ltd.
- Age at study initiation: (P) 6 wks, (F1) 3 wks.
- Weight at study initiation: (P) Males: 165 to 245 g; Females: 125 to 197 g
- Fasting period before study: Yes
- Housing: Animals were housed in groups of 4 per sex in solid polycarbonate cages with Lignocel 3/4 wood flakes for breeding. During mating 1, male and 1 female from the same treatment group were housed together. During gestation and lactation, females were housed individually or with their litters.
- Diet (e.g. ad libitum): Ad libitum
- Water (e.g. ad libitum): Ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-23 ºC
- Humidity (%): 40-70 %
- Photoperiod (hrs dark / hrs light): Artificial lighting 12 hrs dark / 12 hrs light
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: The required volume of vehicle was measured and added to the test substance and mixed using a whirlmixer for a minimum of one minute and then stirred magnetically whilst sampling (five minutes). Moisture was avoided at all times during formulation. The test substance was used as supplied. All formulations were prepared freshly each week and stored refrigerated until the day of use.
VEHICLE
- Justification for use and choice of vehicle (if other than water): In a previous study corn oil formulations were shown to be homogenous in the vehicle and stable at ambient temperature for two days and for 15 days following refrigerated storage.
- Concentration in vehicle: 0 (control), 5.0, 15.0, 50.0 mg/mL
- Amount of vehicle (if gavage): 2 mL/kg - Details on mating procedure:
- - M/F ratio per cage: 1
- Length of cohabitation: two weeks
- Proof of pregnancy: Ejected copulation plugs. Vaginal smears were prepared and examined for the presence of spermatozoa and the stage of the oestruous cycle. Evidence of mating was referred to as day 0 of pregnancy
- After 7 days of unsuccessful pairing replacement of first male by another male with proven fertility.
- After successful mating each pregnant female was caged (how): Individually during gestation and with litters during post partum - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples of each formulation prepared for administration for Weeks 1, 5, 11 and 14 of treatment of the F0 animals and Week 1 of treatment of the selected F1 animals were analysed for achieved concentration of the test substance. The analytical procedure was validated with respect to linearity of detector response, precision of injection, specificity of chromatographic analysis, limit of detection, accuracy and precision. The homogeneity and stability was confirmed for MIBKO in corn oil formulations at a nominal concentration of 50 mg/mL. The mean concentrations of MIBKO in test formulations analysed for the study were within +10%/-15% of nominal concentrations, confirming accurate formulation.
- Duration of treatment / exposure:
- Parental rats were dosed 10 weeks prior to mating, for up to 2 weeks during mating, or until signs of mating were noted, and then during both gestation and lactation. Selected F1 animals were treated from weaning (Day 21 of age) to approximately 7 weeks of age.
- Frequency of treatment:
- Daily
- Details on study schedule:
- - Age at mating of the mated animals in the study: 16 weeks (6 weeks at study initiation + 10 weeks dosing period).
- Offspring were weaned on Day 21 of age and separated from the dam. The allocation of offspring to form the F1 generation was made before weaning on Day 21 of age.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 10 mg/kg bw/day (nominal)
- Dose / conc.:
- 30 mg/kg bw/day (nominal)
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- F0 gneration: 28 animals per sex and per dose.
F1 generation: 24 animals per sex and per dose. - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The doses used in this study with reference to preliminary work with this compound performed by Huntingdon (NBJ0037/070047). MIBKO at dose levels of 10, 30 and 100 mg/kg/day had no adverse effects on reproductive performance or F1 pre- and postnatal development, following treatment of F0 males and F0 females for 28 days before pairing, and during gestation and post partum.
Examinations
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS:
- Time schedule: at least twice daily
- Observations: evidence of ill-health or reaction to treatment
CLINICAL OBSERVATIONS: Yes
- Time schedule: Daily during Weeks 1 to 2, twice weekly during Weeks 3 to 5 (middle and end of each week) and once a week from Week 6 onwards for F0 females on Days 0, 6, 13 and 20 after mating and Days 1, 7, 14 and 21 post partum. A more detailed physical examination was performed on each adult F0 animal weekly, F0 females on Days 0, 6, 13 and 20 after mating and Days 1, 7, 14 and 21 post partum.
BODY WEIGHT: Yes
- Time schedule for examinations: weekly until termination. The weight of each F0 female was recorded weekly until mating was detected. After mating
bodyweights were recorded on Days 0, 3, 6, 10, 14, 17 and 20 and on Days 1, 4, 7, 11, 14, 18 and 21 post partum.
FOOD CONSUMPTION:
- Time schedule: For each F0 male the weight of food supplied, that remaining and an estimate of any spilled was recorded weekly until paired for mating. For each F0 female, the weight of food supplied, that remaining and an estimate of any spilled was recorded weekly until paired for mating, Days 0-2, 3-5, 6-9, 10-13, 14-16 and 17-19 after mating and 1-3, 4-6, 7-10, 11-13, 14-17 and 18-20 post partum. - Oestrous cyclicity (parental animals):
- Three weeks prior to mating, vaginal smears were prepared to observe the estrous cycle of the F0 and F1 females. Daily vaginal smears taken from females before necropsy (Days 25 to 28 post partum) were used to determine the stage of the oestrous cycle at termination. For females whose litters had previously died, the smears were taken on the theoretical Days 25-28.
- Sperm parameters (parental animals):
- Sperm analysis was performed in all male parental generations. After termination, the left vas deferens, epididymis and testis was removed and the epididymis and testis were weighed. The following tests were performed: Sperm motilitly, sperm morphology, sperm count and homogenisation-resistan spermatids count.
- Litter observations:
- STANDARDISATION OF LITTERS
- On postnatal day 4, litters were culled to 8 or 10 pups, with equal numbers of males and females were possible, by random selection. Pups that were selected continued in the study until postnatal day 55.
PARAMETERS EXAMINED
The following parameters were examined in [F1] offspring:
- Following delivery the number of pups were determined and the ratio of male to female pups was calculated.
- Litters were examined daily for dead pups.
- Pups were weight on postanal days 1, 4, 7, 11, 14, 18, 21, 25, and 28.
- Total litter size, number of male and female pups, number of stillborn and live births and grossly malformed pups, and pups showing abnormalities were recorded on postanatal day 1.
- The number of live and dead pups, as well as pups showing malformations or abnormalities, was recorded on postnatal days 4, 7, 14 and 21.
- Sexual maturation: Males were examined daily from day 38 until blanopreputial separation occurred and selected females were examined daily from day 28 until the vaginal opening occurred. Body weights were recorded at these events.
GROSS EXAMINATION OF DEAD PUPS:
- Yes, for external and internal abnormalities.
STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: yes
- If yes, maximum of 10 pups/litter (5/sex/litter as nearly as possible); excess pups were killed and discarded.
PARAMETERS EXAMINED
The following parameters were examined in F1 offspring:
- Parturition observation and gestation lengh: umbers of live and dead offspring, duration of gestation.
- Clinical observations: All litters were examined at approximately 24 hours after birth (Day 1 of age) and then daily thereafter. Selected F1 animals were assessed weekly from Day 21 of age for detailed physical examinations.
- Bodyweight: Individual offspring bodyweights were recorded on Days 1, 4 (before culling), 7, 11, 14, 18 and 21 of age. The weight of each selected F1 animal was recorded on Days 21, 25 and 28 of age.
- Litter size: Daily records were maintained of mortality and consequent changes in litter size from Days 1-21 of age.
- Sex ratio: The sex ratio of each litter was recorded on Days 1, 4 (before and after culling) and on Day 21 of age.
- Sexual maturation: For all selected males, sexual maturation was assessed by daily examination from Day 38 of age until balano-preputial separation occurred. For all selected females, sexual maturation was assessed by daily examination from Day 28 of age until vaginal opening occurred.
[number and sex of pups, stillbirths, live births, postnatal mortality, presence of gross anomalies, weight gain, physical or behavioural abnormalities, other:]
GROSS EXAMINATION OF DEAD PUPS:
Yes, for external and internal abnormalities (see below); possible cause of death was determined for pups born or found dead. - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: All surviving animals were killed when majority of litters had been weaned (approx. 16 weeks).
- Maternal animals: Females surviving until the end of the scheduled study period were killed on Day 28 post partum, which failed to produce viable litter on Day 25 and whose litter died before Day 21 post partium on the day the last offspring died.
GROSS NECROPSY
- Gross necropsy consisted of:full macroscopic examination of the tissues, all external features and orífices; the neck and associated tissues and the thoracic, abdominal and pelvic cavities and their viscera, abnormal position, morphology or interaction; external and cut surfaces of the
organs and tissues; abnormalities in the appearance or size of any organ and tissue. For females, the numbers of implantation sites in each uterine horn was counted.
ORGAN WEIGHTS:
- Adrenals, brain, epididymides, kidneys, liver, ovaries, pituitary, prostate, seminal vesicles, spleen, testes, thyroids, uterus with cervix and oviducts.
HISTOPATHOLOGY
- All parental animals from control and 100 mg/kg bw/day.
- Pathology: adrenals, brain, epididymis, kidneys, liver, mammary area-caudal, ovaries, piruitary, prostate, seminal vesicles, spleen, testis, thyroids, uterus with cervix and oviductus, vagina, any abnormal tissue plus the lymph nodes draining the regions adjacent to masses. Reproductive organs were also analysed in animals at 10 and 30 mg/kg bw/day that showed reduced fertility. Spleen (both sexes) and kidneys (males only) were examined for all F0 adults since were considered to exhibit a reaction to treatment at the high dose.
- Histology: Epididymis, kidneys, liver, ovaries, seminal vesicles, uterus, vagina. - Postmortem examinations (offspring):
- SACRIFICE
- The F1 offspring not selected as F1 generation were sacrificed approximately at 21 days of age.
- Selected F1 animals were killed at approximately 7 weeks of age.
- Selected F1 offspring + non selected ones with external abnormalities + premature deaths, were subjected to postmortem examinations (macroscopic and/or microscopic examination) as follows:
GROSS NECROPSY
- Gross necropsy consisted of: full macroscopic examination of the tissues, all external features and orífices; the neck and associated tissues and the thoracic, abdominal and pelvic cavities and their viscera, abnormal position, morphology or interaction; external and cut surfaces of the
organs and tissues; abnormalities in the appearance or size of any organ and tissue. For females, the numbers of implantation sites in each uterine horn was counted.
ORGAN WEIGHTS:
- Unselected F1 offsprings: Brain, spleen and thymus
- Selected F1 offsprings: Spleen
HISTOPATHOLOGY / ORGAN WEIGTHS
- Unselected F1 offsprings: Brain, spleen and thymus.
- Setected F1 offsprings: Spleen. - Statistics:
- Statistical analyses were performed by using one or multiple methods, as appropriate. For categorical data, Fisher’s exact probability test was used. For continuous data, one-way analysis of variance (ANOVA), followed by either Dunnett’s multiple comparison or Barlett’s test, was used. Kruskal-Wallis nonparametric ANOVA, followed by the Mann-Whitney U-test, was used for nonparametric data. In addition, postimplantation loss and sex ratio were analyzed by the mixed linear model Wald chi-square test.
- Reproductive indices:
- Percentage mating, conception rate, fertility index
- Offspring viability indices:
- Litter size, survival indices (post-implantation survival index, live birth index, viability index, lactation index), sex ratio (percentage males).
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Salivation and chin rubbing were the only clinical signs attributed to administration of the test article. These effects were observed in 100 mg/kg bw/day group males and females and diminished following 4 weeks of treatment. No animals were found in moribund conditions. One female at 30 mg/kg/day had a total litter loss with no pups born alive. No remarkable clinical signs were observed. One female was sacrificed for welfare reasons on day 1 of lactation. Clinical signs included piloerection, hunched posture, skin pallor, and hair loss. Neither of these deaths was considered to be treatment related. One female in the 100-mg/kg group was killed on day 1 of lactation due to poor clinical condition.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One male at 30 mg/kg bw/day was found dead on day 32, and another male at 100 mg/kg bw/day was found dead on day 112. One control female was found dead on day 35. The cause of dead was not determined.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Body weight, body-weight change was similar to controls at all time points.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Food consumption was similar to controls at all time points.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- In the spleens, minimal to moderate hemosiderosis was observed in higher incidence and severity in the 100 mg/kg/day males and females. Minimal congestion was seen in the majority of animals of both sexes treated at 100 mg/kg/day. In the kidneys of males, minimal to moderate cortical tubules with hyaline droplets were seen at a significantly higher incidence in animals treated at 30 mg/kg/day or 100 mg/kg/day. All other findings were considered to be incidental and unrelated to the test substance.
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- no effects observed
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- no effects observed
- Description (incidence and severity):
- No effects on estrus cycle were observed.
- Reproductive function: sperm measures:
- no effects observed
- Description (incidence and severity):
- No effects on sperm counts or morphology were observed.
- Reproductive performance:
- no effects observed
- Description (incidence and severity):
- No effects on precoital time, the number of pregnant females, fecundity, or duration of gestation were seen.
One female each from the control, 10 mg/kg/day, and 100 mg/kg/day groups were not pregnant.
Effect levels (P0)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- (parental toxicity)
- Effect level:
- 30 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- histopathology: non-neoplastic
- Dose descriptor:
- NOAEL
- Remarks:
- (reproductive toxicity)
- Effect level:
- > 100 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: based on no effects at the highest dose tested
Target system / organ toxicity (P0)
- Critical effects observed:
- not specified
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- No remarkable clinical signs were observed in litter. A higher incidence of chin rubbing, salivation and post salivation staining was seen in both the males and females at 100 mg/kg/day in F1 generation.
- Dermal irritation (if dermal study):
- not examined
- Mortality / viability:
- no mortality observed
- Description (incidence and severity):
- Litter data, as assessed by the mean number of implantations, total litter size and live litter size on Day 1 and subsequent litter size to Day 21 of age, were similar to the Control and were considered unaffected by treatment. In utero and offspring survival as assessed by post implantation survival index, live birth index, viability index and post partum index was considered unaffected by treatment with MIBKO.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Bodyweight at birth and subsequent weight gain to Day 21 were considered unaffected by treatment.
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Sexual maturation:
- no effects observed
- Description (incidence and severity):
- There was no effect of treatment with MIBKO on the time of completion of vaginal opening or preputial separation at any dose.
- Anogenital distance (AGD):
- not examined
- Nipple retention in male pups:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- Absolute and bodyweight relative spleen weights were statistically significantly high amongst the offspring of females at 100 mg/kg/day. There were no other obvious effects of treatment for animals receiving 10, 30 or 100 mg/kg/day. Nevertheless, there was no effect of treatment apparent upon the weights of the spleens of F1 generation animals.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- No findings were considered related to treatment of the F0 generation.
- Histopathological findings:
- no effects observed
- Other effects:
- no effects observed
Developmental neurotoxicity (F1)
- Behaviour (functional findings):
- not examined
Developmental immunotoxicity (F1)
- Developmental immunotoxicity:
- not examined
Effect levels (F1)
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- (F1 toxicity)
- Generation:
- F1
- Effect level:
- > 100 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Based on no effects at the highest dose tested
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- (developmental and sexual maturation)
- Generation:
- F1
- Effect level:
- > 100 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Based on no effects at the highest dose tested
Target system / organ toxicity (F1)
- Critical effects observed:
- not specified
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- In a one-generation reproduction study performed with methyl isobutyl ketoxime (MIBKO) in Sprague-Dawley rats, the NOAEL for parental toxicity was considered to be 30 mg/kg bw/day (based on histopathological effects on the spleen) and the NOAEL for the F1 generation and reproductive toxicity was considered to be >100 mg/kg bw/day (based on no effects observed on reproduction or developmental parameters).
- Executive summary:
A one-generation reproduction study was performed according to OECD guideline 415 with the analogue substance methyl isobutyl ketoxime (MIBKO) in Sprague-Dawley rats. 28 parental rats per sex and per dose, were given methyl isobutyl ketoxime in water by gavage at doses of 0 (control), 10, 30 and 100 mg/kg bw/day during 10 weeks prior to mating, for up to 2 weeks during mating, or until signs of mating were noted. Males were killed following mating, and females were continuously exposed through gestation and lactation. Parental and litter examinations as well as reproduction observations were performed. All surviving male and female parent rats, were sacrificed for postmortem examinations. All stillborn pups, pups found dead, or pups terminated in a moribund condition and those for which the sexual maturation was observed, were subjected to a throrough necropsy. No adverse effects were observed in any of the reproductive or developmental parameters or in the F1 pups. The toxicity profile includes symptoms of minimal to moderate hemosiderosis and minimal congestion in the spleens at 100 mg/kg bw/day males and females. The NOAEL for parental toxicity in the F0 generation was considered to be 30 mg/kg bw/day based on histological effects on the spleen. The minor changes observed in male kidneys at 30 mg/kg bw/day was not considered to be significant. The NOAEL for the F1 generation and reproductive toxicity was considered to be >100 mg/kg bw/day based on no effects observed at the highest dose.
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