Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 231-174-8 | CAS number: 7440-65-5
- 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
No repeated dose toxicity study is available with the test substance
yttrium metal. Therefore, read across is performed using a study from
the related substance yttrium oxide. The read across justification is
attached to IUCLID Section 13.
Repeated dose toxicity - oral:
A combined repeated dose toxicity study with
reproduction/developmental toxicity screening has been performed with
the related substance according to OECD 422 test guideline using the
oral exposure route on Wistar rats. Under the conditions of this study,
no adverse systemic effects were observed and the No Observed Effect
Level (NOEL) in males and females was considered to be 1000 mg/kg/day
for yttrium oxide. The substance is considered not to be classified as
STOT RE according to the CLP Regulation. The same is assumed for yttrium
metal.
Repeated dose toxicity - dermal:
A key study is available for the oral route of exposure. According
to the REACH Regulation, only one route of exposure should be tested for
repeated dose toxicity (column 2, annex VIII, section 8.6.1).
Repeated dose toxicity - inhalation:
A key study is available for the oral route of exposure. According
to the REACH Regulation, only one route of exposure should be tested for
repeated dose toxicity (column 2, annex VIII, section 8.6.1).
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
- Remarks:
- combined repeated dose and reproduction / developmental screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to 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)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Details on animals:
Species/strain: Wistar rats, Crl: WI(Han) (Full Barrier)
Source: Charles River, 97633 Sulzfeld, Germany
Sex: male and female; the female animals were non-pregnant and nulliparous.
Age at the start of
the treatment period: males: 10-11 weeks old. females: 10-11 weeks old.
Body weight at the allocation of the animals to the experimental groups: males: 250 - 298 g (mean: 272.80 g, ± 20% = 218.24 – 327.36 g) - females: 162 - 199 g (mean: 183.13 g, ± 20% = 146.50 – 219.75 g)
The animals were derived from a controlled full-barrier maintained breeding system (SPF).
Housing and Feeding Conditions
- Full barrier in an air-conditioned room
- Temperature: 22 3°C
- Relative humidity: 55 10%
- Artificial light, sequence being 12 hours light, 12 hours dark
- Air change: 10 x / hour
- Free access to Altromin 1324 maintenance diet for rats and mice
- Free access to tap water, sulphur acidified to a pH of approximately 2.8 (drinking water, municipal residue control, microbiological controls at regular intervals)
- The animals were kept individually in IVC cages (except during the mating period when one female will be paired with one male), type III H, polysulphone cages on Altromin saw fibre bedding
- Adequate acclimatisation period (at least 5 days) under laboratory conditions - Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Remarks:
- 0.5 %
- Details on oral exposure:
- Preparation of the Animals
Prior to the start of the treatment period a detailed clinical observation outside the home cage was made. Before the first administration all animals used for the study were weighed and assigned to the experimental groups with achieving a most homogenous variation in body weight throughout the groups of males and females.
Experimental Groups and Doses
According to the results of the dose range finding study the following doses: 100 ; 300 and 1000 mg/kg bw were selected for the 3 dose groups (LD = low dose, MD = medium dose, HD = high dose) and 1 control group (C).
The test item and vehicle were administered at a single dose to the animals by oral gavage. The application volume for all groups was 5 mL/kg body weight. For each animal the individual dosing volume was calculated on the basis of the body weight. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Dose Formulation Analysis
Each dosing concentration was analyzed for nominal concentration by ICP - optical emission spectroscopy using a validated analytical procedure. Stability and homogeneity of the test item in the vehicle was analyzed for the LD, MD and HD dosing formulation.
Samples for the nominal concentration verification was taken in study week 1 (first week of pre mating period), 3 (first week of mating), 5 (gestation) and 7 (gestation/lactation) of control and all treatment groups.
Samples for homogeneity were taken from the top, middle and bottom of HD, MD, and LD preparation in study week 1 and 5. - Duration of treatment / exposure:
- The animals were treated with the test item formulation or vehicle on 7 days per week for a period of 54 days, i.e. during 14 days of pre-mating and maximum 14 days of mating in both males and females, during the gestation period and up to post-natal day 3 in females.
Males were dosed after the mating period until the minimum total dosing period of 28 days was completed. - Frequency of treatment:
- Once daily
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- Remarks:
- actual ingested
- Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Remarks:
- actual ingested
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Remarks:
- actual ingested
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Remarks:
- actual ingested
- No. of animals per sex per dose:
- 10 animals per sex per dose.
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- According to the results of the dose range finding study and in consultation with the sponsor three selected doses were tested for the 3 dose groups (LD = low dose, MD = medium dose, HD = high dose) and 1 control group (C).
- Observations and examinations performed and frequency:
- Body Weight and Food Consumption
The body weight of all animals were recorded once before the assignment to the experimental groups. on the first day of administration and weekly during the treatment period as well as at the end of the study. During pregnancy, females were weighed on gestation days (GD) 0, 7, 14 and 20 and within 24 hours of parturition (day 0 post-partum) as well as day 4 post-partum along with pups.
Food consumption was measured weekly on the corresponding days of the body weight measurements after the beginning of the dose administration. Food consumption was not measured during the mating period in males and females and the post-mating period in males. The food consumption in males were measured only for two week during premating period and not during the postmating period as the number of days during the postmating period are not uniform in all males due to difference in mating.
Mating
Mating was performed in a ratio of 1:1 (male to female). The vaginal smears of the females were checked every morning after the start of the mating period to confirm the copulation. The day of the vaginal plug and/or sperm was considered as day 0 of gestation.
The cages were arranged in such a way that possible effects due to cage placement were minimised.
Copulation index, fertility index and delivery index was calculated for each group. The calculations were made using the formula as below,
Copulation Index (%) = (No. of rats copulated / No.of pairs) X 100
Fertility Index (%) = (No. of females pregant / No.of females copulated) X 100
Delivery Index (%) = (No. of dams with live newborns / No.of pregnant dams) X 100
Clinical Observations
General clinical observations were made once a day. Once before the first exposure, and once a week thereafter, detailed clinical observations were made in all animals outside the home cage in a standard arena. Clinical observations included spontaneous activity, lethargy, recumbent position, convulsions, tremors, apnoea, asphyxia, vocalization, diarrhea, changes in the skin and fur, eyes and mucous membranes (salivation, discharge), piloerection and pupil size, Changes in gait, posture, response to handling as well as the presence of clonic or tonic movements, stereotypes, difficult or prolonged parturition or bizarre behaviour were recorded.
Functional Observations
Multiple detailed behavioural observations were made in the week before the first treatment and during the last week of the treatment in 5 selected males and on lactation days in 5 selected females (only lactating females were evaluated) of control and treated groups outside the home cage using a functional observational battery of tests [11]:
Sensory reactivity to different modalities, grip strength and motor activity assessments and other behavioural observations as well as rearing supported and not supported, urination, defecation, startle/ auditory response, equilibrium reflex, positional passivity, visual placing, fore and hind limb grip strength, tail pinch response, toe pinch reflex, extensor thrust/limb tone, hind limb reflex, righting reflex on the ground, air righting reflex, pupil response, body temperature and ophthalmoscopy (anterior chamber of the eye and fundus of eye).
Litter Observations
The duration of the gestation was recorded and was calculated from day 0 of the pregnancy. Each litter was examined as soon as possible after delivery of the dam to establish the number and sex of pups, stillbirths, live births, runts and the presence of gross abnormalities.
The pre- and post- implantation losses were calculated using number of corpora lutea, number of implantation sites and number of live pups born on PND 0 for each dam. The formula used for the calculation are as follows,
Pre Implantation Loss (%) = (No. of corpora Lutea - No. of implantation site / No. of corpora Lutea) x 100
Post Implantation Loss (%) = (No. of implantation site – No. of live pups / No. of implantation site) x 100
Live pups were counted and sexed and weighed within 24 hours of parturition (day 0 post-partum) and on day 4 post-partum. Live pups were identified by tattooing. In addition to the observations of parent animals, any abnormal behaviour of the offspring was recorded.
Haematology
Haematological parameters from five selected males and females of each group were examined at the end of the treatment.
Blood from the abdominal aorta of the animals was collected in EDTA-coated tubes.
The following haematological parameters were examined:
Ihaematocrit value
haemoglobin content
red blood cell count
mean corpuscular volume (
mean corpuscular haemoglobin
mean corpuscular haemoglobin concentration
reticulocytes
platelet count
white blood cells
neutrophils
lymphocytes
monocytes
eosinophils
basophils
Blood Coagulation
Coagulation parameters from five selected males and females of each group were examined at the end of the treatment.
Blood from the abdominal aorta of the animals was collected in citrate- coated tubes.
The following coagulation parameters were examined:
prothrombin time
activated partial thromboplastin time
Clinical Biochemistry
Parameters of clinical biochemistry from five selected males and females of each group were examined at the end of the treatment.
Blood from the abdominal aorta of the animals was collected in serum separator tubes.
The following parameters of clinical biochemistry were examined:
alanine aminotransferase
aspartate-aminotransferase
alkaline phosphatase
creatinine
total protein
albumin
urea
total bile acids
total cholesterol
glucose
sodium
potassium
Calcium
Phosphorus
Urinalysis
A urinalysis was performed with samples collected from 5 selected males of each group at necropsy. Additionally, urine colour/ appearance were recorded.
The following parameters were measured using qualitative indicators (Heiland Urine Stripes URI 10SL).
specific gravity
nitrite
ph-value
protein
glucose
ketone bodies
urobilinogen
bilirubin
blood
leukocytes
Sperm analysis
At necropsy (one day after the last administration) one epididymis and one testis from males of each group were separated and used for evaluation of sperm parameters. Epididymal sperm motility was evaluated in all male animals using Hamilton Thorn Sperm Analyser. The testicular sperm count could not be measured at the end of the study as the testes stored at -80oC were inadvertently taken out of the freezer before the scheduled measurement. - Sacrifice and pathology:
- Gross necropsy
All male animals were sacrificed after the completion of the mating period (minimum dosing period: 28 days) on study day 29 or 30, while female animals were sacrificed on post-natal day 4 (maximum dosing period: 54 days) using an anaesthesia was used.
Females showing no sign of pregnancy was sacrificed on day 26 after the last day of the mating period.
All animals were subjected to a detailed gross necropsy which includes careful examination of the external surface of the body, all orifices and the cranial, thoracic and abdominal cavities and their contents.
Organ Weights
The wet weight of the organsof 5 males and 5 females selected from each group was recorded as soon as possible. Paired organs were weighed separately. In addition reproductive organs of all animals were weighed. The enclosed organs were weighed at necropsy:
liver
uterus with cervix
kidneys
thymus
adrenals
thyroid/parathyroid glands
testes
spleen
epididymides
brain
prostate. seminal vesicles and coagulating glands
pituitary gland
ovaries
The following tissues of the same selected animals from each group were preserved in 10% neutral buffered formalin except eyes, testes and epididymides that were fixed in Modified Davidson’s Fixative for approximately 24 hours before they were transferred to 10% neutral buffered formalin:
brain (cerebrum, cerebellum and pons)
ovaries (females)
spinal cord
uterus with cervix (females)
liver
vagina (females)
kidneys
testes (males)
adrenal glands
epididymides (males)
stomach
prostate and seminal vesicles with coagulating glands as a whole (males)
small and large intestines (including Peyer´s patches)
urinary bladder
thymus
lymphnodes (mesentric and axillary)
Thyroid
peripheral nerve (e.g. sciatic nerve) with skeletal muscle
spleen
bone with bone marrow (sternum)
lung and trachea
pituitary gland
mammary glands
oesophagus
heart
gross lesions
Histopathology
All organs and tissues listed in Table 7 were evaluated from five selected males and females of the control and high dose group:
Reproductive organsand macroscopic changes were evaluated in all study animals. For the testes, a detailed qualitative examination was made. - Statistics:
- Evaluation of Results and Statistical Analysis
The findings of this study were evaluated in terms of the observed effects, the necropsy and the microscopic findings.
Parameters like body weight gain and food consumption were calculated for each animal as the difference in weight measured from one week to the next. Mean body weights are also presented as figures. The relative organ weights were calculated in relation to the body weight (measured at necropsy) and are presented as percentage.
A statistical assessment of the results of the body weight. food consumption, parameters of haematology, blood coagulation and clinical biochemistry and absolute and relative organ weights were performed for each gender by comparing values of dosed with control animals of the main groups using a one-way ANOVA and a post-hoc Dunnett Test. These statistics were performed with GraphPad Prism 5.01 software (p<0.05 was considered as statistically significant). - Clinical signs:
- no effects observed
- Description (incidence and severity):
- There were no clinical signs recorded in male and female animals of treated groups that could be directly related to treatment. However, there were few clinical signs namely moving the bedding, nasal discharge (dark or reddish), salivation and piloerection seen occasionally and transciently during the study period in MD or HD group animals. These findings were considered to be due to local effect but not the systemic effect of the test item. These findings were considered not likely to be adverse. In addition. there was alopecia (on hindlimb, forelimb, thorax and abdominal region) of few isolated animals of MD or HD groups, which was assumed to be incidental in origin.
During the weekly detailed clinical observation, no significant changes or differences between the groups were found.
There were no ophthalmoscopic findings in any of the animals of this study. - Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- In both males and females, no treatment related changes were noted for body weight and body weight change during the study period. Statistically there were significant increase in body weight change in female HD group during 2nd week of premating period when compared to control. In addition, there was lower mean body weight gain noted between days 1-7 of premating when compared to control without attaining the statistical significance. But, this increase or decrease in weight gain did not correlate with food intake during the same period. Hence, the changes were not considered likely to be adverse. There was decrease in body weight gain noted in female MD and HD groups during lactation period when compared to control. This decrease had no statistical significance and was not likely to be adverse.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- In both males and females, no treatment related changes were noted for treated group when compared to corresponding control. The statistical evaluation of the data revealed no significant changes in food intake in treated group animals when compared to control.
- Food efficiency:
- not examined
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- Haematology and Coagulation (tables 3 and 4)
No treatment related changes were noted for haematology and blood coagulation parameters measured at the end of treatment period in male and female animals. There were no statistically significant changes noted for haematological and coagulation parameters between the treated and control groups. - Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- Clinical Biochemistry (Tables 1 and 2):
There were no treatment related changes considered for measured clinical biochemistry parameters of male and female treated groups when compared to corresponding control. However, there was statistically significant increase noted for mean potassium value in male MD group. In the absence of dose response pattern no relevance to treatment was considered. - Urinalysis findings:
- no effects observed
- Description (incidence and severity):
- The urinalysis performed in male animals revealed no considerable changes in treated groups when compared to the control.
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- There were no changes considered to be related to treatment noted for organ weight in both males and females when compared to corresponding control. However, there was statistically significant increase in relative weight of left kidney weight in male treated (LD, MD and HD) groups, but not total kidney weight. This change in left kidney weight, in the absence of histological changes was not considered to have toxicological relevance.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- At terminal sacrifice, macroscopic organ findings noted were few, and none of them was considered to be test item related.
Yellow spot(s) at the epididymis were observed without dose relationship in 2/10 control males, 1/10 male of LD group, 3/10 males of MD group and 2/10 males of HD group. They were not considered treatment related as histologically they were confirmed to represent spermatic granuloma, a finding known to occur spontaneously in untreated rats of this strain and age. - Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- Reproductive organs
No test item-related effects were noted on male and female reproductive organs in any of the treatment groups.
Histopathological findings noted in male reproductive organs were few and considered to be spontaneous in nature and unrelated to the test item, comprising multifocal atrophic tubules in the testis of each one male treated at 300 and 1000 mg/kg/day and subsequent epididymal changes in the same animals.
Reproductive organs of most study females showed histomorphological evidence of precedent pregnancy in the uterus. The number of large corpora lutea in the ovary was not essentially different between the groups.
Non pregnant animalsshowed physiological sexual cycling, and their unsuccessful mating was considered unrelated to the treatment.
Other organs
No test item-related histopathological findings were noted in the other organs evaluated in randomized males and females of the control and high dose group.
Histopathological changes seen at terminal sacrifice were considered to be incidental in origin and/or within the range of expected changes for rats of this age and strain kept under laboratory conditions. - Other effects:
- no effects observed
- Description (incidence and severity):
- Functional Observation:
No relevant effects of treatment were observed in any of the parameters of the functional observation battery before and at the end of the treatment period. There were no biologically relevant differences in body temperature between the groups.
Litter Data
No treatment-related changes were noted for number of still births, number of runts, total number of pups born on PND 0 and number of male and female pups, sex ratio, live pups on PND 0 and PND 4. The statistical evaluation of data revealed no significant differences between the values of treated and control groups.
Litter Weight Data
No treatment related changes were noted for the mean litter weight, total litter weight, male and female litter weight on PND 0 and 4 in treated groups when compared to corresponding control. The statistical evaluation of data revealed no significant differences between the values of the treated and control groups. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- In conclusion, the repeated dose administration of the Yttrium Oxide to the male (minimum 28 days) and female (maximum 54 days) Wistar rats at dosages of 100, 300 and 1000 mg/kg body weight revealed neither mortalities nor findings of toxicological relevance in male and female animals. There were also no toxicologically relevant findings noted for reproductive and developmental parameters.
Based on the data generated from this “Combined Repeated Dose Oral Toxicity Study with the Reproduction/ Developmental Toxicity Screening Test with Yttrium Oxide, the no observed adverse effect level (NOAEL) for systemic and reproductive and developmental toxicity is considered to be 1000 mg/kg body weight.
No classification for repeat-dose toxicity is warranted based on the absence of toxicologically relevant effects in this study, according to the criteria of Annex VI Directive 67/748/EEC or the 1272/2008 regulation -CLP). - Executive summary:
There was no mortality noted in treated (at 100, 300 and 1000 mg/kg bw/day) and control groups during the study period (at least 28 days for males and 54 days for females).
During the weekly detailed clinical observation, no significant changes or differences between the groups were found.
There were no ophthalmoscopic findings in any of the animals of this study.
Weight increase or decrease had no statistical significance and was not likely to be adverse.
The statistical evaluation of food consumption revealed no significant changes in food intake in treated group animals when compared to control.
There were no statistically significant changes noted nor for haematological and coagulation parameters nor for clinical biochemistry parameters of male and female treated groups when compared to corresponding control.
The urinalysis performed in male animals revealed no considerable changes in treated groups when compared to the control.
There were no changes considered to be related to treatment noted for organ weight in both males and females when compared to corresponding control. However, there was statistically significant increase in relative weight of left kidney weight in male treated (LD, MD and HD) groups, but not total kidney weight. This change in left kidney weight, in the absence of histological changes was not considered to have toxicological relevance.
At terminal sacrifice, macroscopic organ findings noted were few, and none of them was considered to be test item related.
No test item-related histopathological findings were noted in the other organs evaluated in randomized males and females of the control and high dose group.
Reference
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:
- Test was performed according to an international guideline and according to GLP.
Repeated dose toxicity: inhalation - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: inhalation
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: inhalation
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Repeated dose toxicity - oral:
No repeated dose toxicity study with the test substance yttrium metal is available. Data generated with the related substance yttrium oxide is used for endpoint coverage. The justification of this read-across approach is included in section 13.
A combined repeated dose toxicity study with reproduction/ developmental toxicity screening has been conducted according to OECD 422 test guideline using the oral exposure route on Wistar rats (K1; Shivakumar, 2013). Yttrium oxide was administered daily by oral gavage to male and female Wistar rats, 7 days per week at dose-levels of 100, 300 or 1000 mg/kg/day during at least 28 days for males and 54 days for females. No mortality was observed. During the weekly detailed clinical observation, no significant changes or differences between the groups were found. There were no ophthalmoscopic findings in any of the animals of this study. Weight increase or decrease had no statistical significance and was not likely to be adverse. The statistical evaluation of food consumption revealed no significant changes in food intake in treated group animals when compared to control.
There were no statistically significant changes noted nor for haematological and coagulation parameters nor for clinical biochemistry parameters of male and female treated groups when compared to corresponding control. The urinalysis performed in male animals revealed no considerable changes in treated groups when compared to the control.
There were no changes considered to be related to treatment noted for organ weight in both males and females when compared to corresponding control. However, there was statistically significant increase in relative weight of left kidney weight in male treated groups (all dose levels), but not total kidney weight. This change in left kidney weight, in the absence of histological changes was not considered to have toxicological relevance. At terminal sacrifice, macroscopic organ findings noted were few, and none of them was considered to be test item related. No test item-related histopathological findings were noted in the other organs evaluated in randomized males and females of the control and high dose group.
Based on the experimental conditions of this study, the No Observed Adverse Effect Level (NOAEL) for parental toxicity was considered to be 1000 mg/kg/day in female and male rats.
Repeated dose toxicity - dermal:
A key study is available for the oral route of exposure. According to the REACH Regulation, only one route of exposure should be tested for repeated dose toxicity (column 2, annex VIII, section 8.6.1).
Repeated dose toxicity - inhalation:
A key study is available for the oral route of exposure. According to the REACH Regulation, only one route of exposure should be tested for repeated dose toxicity (column 2, annex VIII, section 8.6.1).
Justification for classification or non-classification
No repeated dose toxicity study is available with yttrium metal. Data from the related substance yttrium oxide is used for endpoint coverage in a read-across approach. Based on study results and according to the criteria of the CLP Regulation, yttrium oxide is considered not classified as STOT RE. The same is assumed for yttrium metal. The read across justification is included in section 13.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.