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EC number: 231-113-5 | CAS number: 7440-03-1
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Repeated dose toxicity: oral
Administrative data
- Endpoint:
- short-term repeated dose toxicity: oral
- Remarks:
- combined repeated dose and reproduction / developmental screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 14 September 2009 to 12 April 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- yes
- Remarks:
- urinalysis was not performed on the samples collected from five randomly selected males. Food was not withheld overnight prior to blood sampling. These deviations are considered to have no impact on the validity of the study.
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Diniobium pentaoxide
- EC Number:
- 215-213-6
- EC Name:
- Diniobium pentaoxide
- Cas Number:
- 1313-96-8
- Molecular formula:
- Nb2O5
- IUPAC Name:
- µ-oxido[tetrakis(oxido)]diniobium
- Reference substance name:
- Diniobium Pentoxide
- IUPAC Name:
- Diniobium Pentoxide
- Test material form:
- solid: particulate/powder
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Test System
Young healthy male and nulliparous, non pregnant female rats [strain: Wistar Crl:WI] (Full-Barrier), were used in this study. The animals were derived from a controlled full barrier maintained breeding system (SPF) (Source: Charles River, Sulzfeld, Germany). According to Art. 9.2, No.7 of the German Act on Animal Welfare the animals were bred for experimental purposes.
At the beginning of the study, the age of the animals was 8-9 weeks.
The range of the body weight was:
Females: 158.3-194.8 g, (mean: 176.82 g, ± 20%= 35.36 g)
Males: 236.1-275.4 g, (mean: 254.82 g, ± 20%= 50.96 g)
Housing and Feeding Conditions
After an adequate acclimatisation period (at least five days) the animals were barrier maintained (full-barrier) in air conditioned rooms under the following conditions:
- Temperature: 22 ± 3 °C
- Relative humidity: 55 ± 10%
- Artificial light, sequence being 12 h light, 12 h dark
- Air change: 10 x / h
- 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, microbiol. controlled periodically)
- housed individually in IVC cages, type III H, polysulphone cages on Altromin saw fibre bedding
Certificates of food, water and bedding are filed at BSL BIOSERVICE.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- Dosage
Based on the available information from other toxicity studies and in consultation with sponsor following doses were selected:
Control: 0 mg/kg bw/d
LD: 250 mg/kg bw/d
MD: 500 mg/kg bw/d
HD: 1000 mg/kg bw/d
The highest dose level was chosen with the aim of inducing toxic effects but not death or severe suffering. Thereafter, a descending sequence of dose levels is selected with a view to demonstrate any dosage related response and no observed adverse effect (NOAEL). The animals in the control group were handled in an identical manner to the test group subjects and received the vehicle in the volume same as treated groups.
Administration of Doses
The animals were dosed with the test item on 7 days per week. The test substance was administered daily during 14 days pre-mating and 14 days mating in both male and in female, during gestation period and up to post natal day 3 in females. Males were dosed for 28-29 days. Femals for maximum 54 days. The test item was administered by gavage using a gavaging canula. The maximum dose volume administered was 10 mL / kg body weight.
For each animal the individual dosing volume was calculated on the basis of the most recently measured body weight. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- All formulation samples were stored frozen (approximately -20°C) till the shipment to analytic laboratory and analysis is performed. The mean nominal concentration of week 1, 3, 5 and 7 was 87.8, 97.6 and 90.3% at the high, mid and low dose group.
The dose formulation analysis was performed at CURRENTA GmbH & Co. OHG Services Analytik Building Q 25, Leverkusen, Germany. - Duration of treatment / exposure:
- Males: 28-29 days.
Females: maximum 54 days - Frequency of treatment:
- 7 days per week
Doses / concentrationsopen allclose all
- Dose / conc.:
- 250 mg/kg bw/day (nominal)
- Dose / conc.:
- 500 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 10
- Control animals:
- yes
- Details on study design:
- - Dose selection rationale: Based on results of other toxicology studies and in consultation with sponsor.
The test item was administered by gavage using a gavaging cannula. The maximum dose volume administered was 10 mL/kg body weight. - Positive control:
- no
Examinations
- Observations and examinations performed and frequency:
- General clinical observations were made twice a day except during weekend and holidays where observations were made only once, approximately at the same time each day and considering the peak period of anticipated effects after dosing. Pertinent behavioural changes, signs of difficult or prolonged parturition and all signs of toxicity, including mortality were recorded.
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, apnoe, asphyxia, vocalisation, diarrhoea, changes in the skin and fur, eyes and mucous membranes (salivation, discharge), and piloerection and pupil size. Changes in gait, posture, response to handling as well as the presence of clonic or tonic movements, stereotypies, difficult or prolonged parturition or bizarre behaviour was recorded.
Sensory reactivity to different modalities, grip strength and motor activity assessments and other behaviour observations were conducted on five randomly selected males and females from each group. Observations were occured during the last week of treatment in males and on day 3 of the lactation in females (only lactating females were evaluated).
The animals were weighed at randomisation, males weekly during the entire study period and at terminal sacrifice. Females were weighed weekly during pre mating period, on gestation day 0, 7/8, 14, 20 and on PND 1 (within 24 hours of parturition) and 4 along with pups.
Food consumption was measured on corresponding day of body weight after beginning of the dose administration. Food consumption was not measured during mating period. - Sacrifice and pathology:
- Males were sacrificed after the completion of mating period (total dosing of 28-29 days) and females were sacrificed on respective post natal day 4 along with pups by using high dose of sodium pentobarbital.
Dead pups and pups sacrificed at day 4 post-partum, or shortly thereafter were carefully examined for gross abnormalities. - Other examinations:
- Litter observations
The duration of gestation was recorded and was calculated from day 0 of 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.
Live pups were counted and sexed and litters weighed within 24 hours of parturition (day 0 post-partum) and on day 4 post-partum. Live Pups were identified by writing actual numbers on the back with the help of permanent marker In addition to the observations on parent animals; any abnormal behaviour of the offspring was recorded.
Haematology
The following haematological examinations were made in five males and five females randomly selected from each group.
Haematocrit, haemoglobin, erythrocyte count, total and differential leucocyte count,
platelet count, blood clotting time.
Blood samples were taken from abdominal aorta as a part of the procedure for killing the animals, and stored under appropriate conditions.
Clinical Biochemistry
Clinical biochemistry determinations to investigate major toxic effects in tissues and, specifically, effects on kidney and liver were performed on blood samples obtained from the randomly selected five males and five females of each group. Investigations of plasma or serum included sodium, potassium, glucose, total cholesterol, urea, creatinine, total protein and albumin, two enzymes indicative of hepatocellular effects (such as alanine aminotransferase, aspartate aminotransferase, alkaline phosphatase).
Urinalysis was not performed on the samples collected from five randomly selected males at the terminal sacrifice.
Gross Pathology
Males were sacrificed after the completion of mating period (total dosing of 28-29 days) and females were sacrificed on respective post natal day 4 along with pups by using high dose of sodium pentobarbital. However, in the animals randomly selected for the blood collection, anaesthesia solution (Ketamin/Xylazin, 2:1) was used. At the time of sacrifice or death during the study, the adult animals were subjected to a full, detailed gross necropsy which includeed careful examination of the external surface of the body, all orifices and the cranial, thoracic and abdominal cavities and their contents. Special attention was paid to the organs of the reproductive system.
The number of implantation sites and corpora lutea was recorded for each lactating female at necropsy.
Dead pups and pups sacrificed at day 4 post-partum, or shortly thereafter were carefully examined for gross abnormalities.
The ovaries, uterus with cervix, vagina, testes, epididymides, accessory sex organs (prostate, seminal vesicle with coagulating glands as a whole), and all organs showing macroscopic lesions of all adult animals were preserved. Tissues were fixed in 10% formalin with the exception of testes and epididymides which were fixed in modified Davidson's solution.
Organ Weight
Reproductive organs from all animals were weighed (testes, epididymides, prostate, seminal vesicle with coagulating glands as whole, ovaries, uterus with cervix as applicable). Apart from the reproductive organs from all animals, from five males and females randomly selected from each group, the wet weight of the liver, kidneys, adrenals, thymus, spleen, brain and heart were taken as soon as possible.
Paired organs were weighed separately and no organ weights were taken for found dead animals.
The following tissues of same selected animals were preserved in 10% formalin as it is the most appropriate medium for both the type of tissue and the intended subsequent histopathological examination.
- all gross lesions
- brain (representative regions including cerebrum, cerebellum and pons)
- spinal cord
- liver
- kidneys
- adrenals
- stomach
- small and large intestines (including Peyer´s patches)
- thymus
- thyroid
- spleen
- trachea and lungs (preserved by inflatation with fixative and then immersion)
- heart
- urinary bladder
- lymphnodes (one lymph node covering the route of administration (mandibular) and another one distant from the route of administration to cover systemic effects (mesenteric))
- peripheral nerve (e.g. N. ischiadicus/ N. tibialis) in close proximity to muscle
- section of bone marrow
Histopathology
Full histopathology was carried out on the preserved organs and tissues of the five randomly selected animals (male and female) in the control and high dose groups. On the HE (Haematoxylin and Eosin) stained slides of all preserved organs and tissues. These examinations were not extended to animals of all other dosage groups as no treatment related changes were observed in the high dose group.
Testes, epididymides, ovaries, uterus with cervix, vagina, accessory sex organs (prostate, seminal vesicle with coagulating gland) and all organs showing gross lesions were examined in all animals.
For testis, a detailed qualitative examination was made; taking into account the tubular stages of the spermatogenic cycle at evaluation of additional hematoxylin-PAS (Periodic Acid Schiff) stained slides.
Histopathological evaluation and processing was performed at GLP-certified test site KALEIDIS –Consultancy in Histopathology, Saint-Louis, France. Blocking, embedding, cutting, staining and professional evaluation was performed according to the corresponding SOPs of the test site, Propath UK Ltd, Willow Court, GB - Hereford. - Statistics:
- Parameters like body weight change and food consumption was calculated for each animal as the difference in weight measured from one week to the next. The relative organ weights were calculated in relation to the body weight (measured at necropsy) and presented as percentage.
For statistical analysis one-way analysis of variance (ANOVA) followed by Dunnett’s multiple comparison test was carried out to reveal any differences between control and test groups. Statistical analysis performed with GraphPad Prism V.x software (p<0.05 was considered as statistical significant).
In the evaluation of laboratory parameters, all values within a range of the mean value ± the two fold standard deviation (x ± 2s) are considered to be "normal" values within a "normal" population.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- > 1 000 mg/kg bw (total dose)
- Based on:
- test mat.
- Remarks:
- nominal
- Sex:
- male/female
- Basis for effect level:
- other: no adverse effects up to the highest dose tested
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Mortality
C (0 mg/kg) |
LD (250 mg/kg) |
MD (500 mg/kg) |
HD (1000 mg/kg) |
|
Total number of animals examined: males |
10 |
10 |
10 |
10 |
Total number of animals examined: females |
10 |
10 |
10 |
10 |
No mortality was observed in any male from various treatment and control group during the entire period of the study. One female animal from low dose was found dead on gestation day 15 due to gavaging error (not attributed to test item). |
Clinical Observations – Male
Clinical Finding |
C (0 mg/kg) |
LD (250 mg/kg) |
MD (500 mg/kg) |
HD (1000 mg/kg) |
Total number of animals examined |
10 |
10 |
10 |
10 |
No clinical signs were observed in any male from various treatment and control group during the entire period of the study. |
Clinical Observations – Female
Clinical Finding |
C (0 mg/kg) |
LD (250 mg/kg) |
MD (500 mg/kg) |
HD (1000 mg/kg) |
Total number of animals examined |
10 |
10 |
10 |
10 |
No clinical signs were observed in any female from various treatment and control group during the entire period of the study. |
Reproductive Indices
Index |
Group |
|
||||
|
C (0 mg/kg) |
LD (250 mg/kg) |
MD (500 mg/kg) |
HD (1000 mg/kg) |
|
|
Copulation Index |
(%) |
100 |
100 |
100 |
100 |
|
Fertility Index |
(%) |
90 |
100 |
80 |
100 |
|
Delivery Index |
(%) |
100 |
100 |
100 |
100 |
|
Viability Index |
Mean |
100.00 |
100.00 |
100.00 |
97.00 |
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
Viability Index (%)= (No. of live offspring at day 4/ No.of live offspring at birth)x 100
No. of live offspring at day 4/ No.of live offspring at birth)x 100
Macroscopic Findings - Male
Findings (External/Internal) |
C (0 g/kg) |
LD (250 mg/kg) |
MD (500 mg/kg) |
HD (1000 mg/kg) |
Total number of animals examined |
10 |
10 |
10 |
10 |
Left seminal vesicle diminished |
1 |
0 |
0 |
0 |
Epididymidis-yellowish, whitish deposition (bilateral) |
1 |
0 |
1 |
0 |
Right epididymis-yellowish, whitish deposition |
0 |
1 |
1 |
0 |
Lung redish discolouration |
0 |
0 |
1 |
0 |
Left Epididymidis-yellowish, whitish deposition |
0 |
0 |
1 |
1 |
Right seminal vesicle with white spots( 1-2mm) |
0 |
0 |
0 |
1 |
Macroscopic Findings- Female
Findings (External/Internal) |
C (0 g/kg) |
LD (250 mg/kg) |
MD (500 mg/kg) |
HD (1000 mg/kg) |
Total number of animals examined |
10 |
10 |
10 |
10 |
Lymph nodes axillary: left slightly enlarged; right red discolouration at the margin |
1 |
0 |
0 |
0 |
Lung-residuals of the test item |
0 |
2 |
1 |
2 |
Lung-bloody infiltrated,foam |
0 |
1 |
0 |
0 |
Kidney- small cyst on right kidney. |
0 |
0 |
1 |
0 |
Thymus- slightly reduced in size |
0 |
0 |
2 |
0 |
Lung-slight bloody, red spots |
0 |
0 |
1 |
0 |
oesophagos-residuals of the test item |
0 |
0 |
1 |
0 |
Axillary lymphnode-left slightly enlarged |
0 |
0 |
0 |
1 |
Lung- bloody, red discoloured |
0 |
0 |
0 |
2 |
Applicant's summary and conclusion
- Conclusions:
- In conclusion, the repeated dose administration of Diniobium Pentoxide (Nb2O5) in deionised water to the male (28-29 days) and female (maximum 54 days) Wistar rats at dosages of 250, 500 and 1000 mg/kg body weight revealed no toxicological findings.
Based on the data generated from this combined repeated dose toxicity and reproduction/ developmental toxicity screening test with Diniobium Pentoxide, the no observed adverse effect level (NOAEL) is believed to be 1000 mg/kg body weight in males and females.
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