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EC number: 215-239-8 | CAS number: 1314-62-1
- 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
Endpoint summary
Administrative data
Description of key information
Acute oral toxicity: LD50 = 467 mg/kg bw (OECD 401; GLP; female rats)
Acute inhalation toxicity: LC50 > 4.3 mg/L air (analytical) (OECD 436; GLP)
Acute dermal toxicity: LD50 > 2500 mg/kg bw (OECD 402; GLP)
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1991-08-19 to 1991-09-30
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Minor deviations: - According to the guideline, the relative humidity should be between 30 - 70 %. In this study the relative humidity was slightly higher (60 +/- 20 %). - According to the guideline, a stomach tube or a suitable intubation cannula should be used when the test substance is administered by gavage. The study report does not stated what was used in order to administered the test substance by gavage. -According to the guideline, after the substance has been administered, food may be withheld for a further 3 -4 hours. In the study report it was not stated if food was withheld after the administration of the test substance. - According to the guideline, the individual weights should be determined before the application of the test substance , which was done in this study. The individual weights were not provided in the report but only the average weight of the males and females per dose.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Version / remarks:
- 1987-02-24
- Deviations:
- yes
- Remarks:
- see rational for reliability
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- signed 2009-11-12
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Lippische Versuchstierzucht HAGEMANN GmbH D-4923 Extertal 1
- Age at study initiation: approx. 40 - 60 days
- Weight at study initiation: 150 g - 200 g
- Fasting period before study: approx. 16 hours
- Housing: Animals were kept in groups of two or three in MAKROLON cages (type III). Gradulated textured wood was used as bedding material (Granulat Typ A2, supplier: Messrs. BRANDENBURG, Inh. H.Brandenburg, D-2849 Goldenstedt).
- Diet: Standardized diet for rats ALTROMIN 1324 (supplied by: ALTROMIN GmbH, D-4937 Lage/Lippe)
- Water (ad libitum): tap water
- Quarantine period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22 °C +/- 3 °C (maximum range)
- Relative humidity: 60 % +/- 20 % (maximum range)
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- other: hydroxypropyl-methylcellulose gel
- Details on oral exposure:
- VEHICLE
V2O5 analytical grade pulverised was suspended in 0.8 % aqueous hydroxypropyl-methylcellulose gel (Methocel E 4 M).
Batch no. (Vehicle): MM 84097413
MAXIMUM DOSE VOLUME APPLIED: The volume of application was 20 ml/kg b.w. for all groups. (The dose interval factor was 1.47) - Doses:
- 215 mg/kg, 316 mg/kg, 464 mg/kg, 681 mg/kg and 1000 mg V2O5 analytical grade pulverised/kg b.w.
- No. of animals per sex per dose:
- 5 males / 5 females
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Observations were performed immediately, 5, 15, 30 and 60 min, as well as 3 h, 6 h and 24 h after administration. During the follow-up period, changes of skin and fur, eyes and mucous membranes, respiratory and circulatory, autonomic and central nervous system and somatomotor activity as well as behaviour pattern were observed at least once a day until all symptoms subsided, and thereafter each working day. Observations on mortality were made at least once daily with appropriate actions taken to minimize loss of animals during the study.Individual body weights were recorded before administration of the substance, thereafter in weekly intervals up to the end of the study, and at death.
- Necropsy of survivors performed: yes, at the end of the experiment all surviving animals were sacrificed, dissected and inspected macroscopically. All gross pathological changes were recorded. From animals which survived 24 hours or longer a microscopic examination of all organs which show evident lesions is performed. Autopsy and macroscopic inspection of rats which died prematurely were carried out as soon as possible after exitus.
- Other examinations performed: Attention was also paid to possible tremor, convulsions, salivation, diarrhoea, lethargy, sleep and coma. Changes in weight were calculated and recorded when survival exceeds one day. - Statistics:
- The LD50 was calculated according to FINNEY (probit analysis).
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 474.2 mg/kg bw
- 95% CL:
- > 379.01 - < 593.35
- Remarks on result:
- other: Slope: 7.82
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- 466.93 mg/kg bw
- Remarks on result:
- other: Slope: 29.94; The LD50 was calculated by regressions analysis; no estimation of the confidence limits possible, due to the low number of animals employed and the steepness of the mortality curve.
- Mortality:
- Under the present test concitions first intolerance reactions (death) occured at 316 mg V2O5 analytical grade pulverised/kg b.w. p.o. The lowest lethal dose for males and females was 316 mg/kg b.w. p.o. Animals died between 48 hours and 7 days unobserved.
Dose level and number of dead animals:
316 mg/kg b.w. : 1/5 males; 1/5 females
464 mg/kg b.w. : 1/5 males; 2/5 females
681 mg/kg b.w.: 5/5 males; 5/5 females
1000 mg/kg b.w.: 5/5 males; 5/5 females - Clinical signs:
- other: Reduced motility, ataxia and dyspnoea were observed from a dose-level of 464 mg/kg b.w. onwards. Animals showed symptoms between 24 h and days 2. The symptoms varied between slight and moderate. Dose level: 464 mg/kg b.w. : reduced motility (4/5 males; 3/
- Gross pathology:
- Autopsy of deceased animals: There were no pathological findings in males or females.
Autopsy of surviving animals: There were no pathological findings in males or females. - Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- LD50 (female rats) = 466.93 mg/kg bw
According to the Regulation (EC) No 1272/2008 and subsequent adaptations, the substance is classifed as acutely toxic via the oral route (Category 4).
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 467 mg/kg bw
- Quality of whole database:
- GLP guideline studies with divanadium pentaoxide in three different grades (i.e. analytical-pulverized, technical-fused, technical-pulverised) exist.
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1991-10-02 to 1991-11-13
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Minor deviations: - According to the guideline, the weight variation in animals or between groups used in a test should not exceed +/- 20 % of the mean weight. The males of the group with the 2.42 mg/l air concentration were slightly outside this weight range. - According to the guideline, the relative humidity should be between 30 - 70 % in the animal room. In this study the relative humidity was slightly higher (60 +/- 20 %). -According to the guideline, animals should be tested with inhalation equipment designed to sustain a dynamic air flow of 12 to 15 air changes per hour. In this study in the high concentration group the air flow was 29.4 changes per hour. - According to the guideline, the duration of exposure should be at least 4 hours after equilibration of the chamber concentration. It was not stated if the 4 hours started after equilibration of the chamber concentration. - According to the guideline, weight changes should be calculated and recorded when survival exceeds one days. This is missing in this study. -The GSD for the MMAD is missing. - The 95 % confidence level for the females is missing.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Version / remarks:
- 1981-05-12
- Deviations:
- yes
- Remarks:
- see "rational for reliability"
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The study report stated that the study was performed according to "Good Laboratory Practice" Regulations of the EEC enacted in Germany in the "Chemikaliengesetz" dated March 14th, 1990, BGBL I, pp. 521, 1990.
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Lippische Versuchstierzucht HAGEMANN GmbH, D-4923 Extertal 1
- Age at study initiation: 52-69 days
- Weight at study initiation: 188 - 270 g (males; 164 - 206 g (females)
- Fasting period before study: approx. 16 hours
- Housing: Animales were kept in groups of two or three in Makrolon cages (type III). Granulated textured wood (type 2, supplied by Johannes Brandenburg, D-4937 Goldenstedt) was used as bedding material.
- Diet (ad libitum): Standardized diet for rats ALTROMIN 1324 (supplied by: ALTROMIN GmbH, D- 4937 Lage/Lippe)
- Water (ad libitum): tap water
- Quarantine period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22 °C +/- 3 °C (maximum range)
- Relative humidity: 60 % +/- 20 % (maximum range)
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- inhalation: dust
- Type of inhalation exposure:
- nose only
- Vehicle:
- other: air
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus & Exposure chamber volume: : The study was carried out using a dynamic inhalation apparatus with a nose only exposure of the animals according to KIMMERLE & TREPPER (Rhema-Labortechnik, D-6238 Hofheim/Taunus). The apparatus consists of a cylindrical exposure chamber (volume 40 l) which holds a maximum of 20 animals in pyrex tubes at the edge of the chamber in a radial position.
- Source and rate of air: At the bottom of the exposure chamber the air was sucked off at the similar rate as created by the dust generator in order to produce a homogenous distribution in the exposure chamber. Air-flow meters (Rotameter, ROTA Apparate- und Maschinenbau, D-7867 Wehr 2/Baden) were used to control the constant supply of compressed air and vacuum. Flow rates were checked at least once/hour and corrected if necessary. Air flow was 480 l/h for the low and medium concentration, and 1175 l/h for the high concentration. The air change was 12.0 changes per hour for the low and medium concentration, and 29.4 changes per hour for the high concentration.
- System of generating particulates/aerosols: The dust was generated with a dust generator and dosing apparatus (BURGHART, D-2000 Wedel/Holstein). The generator was fed with compressed air from a compressor.
- Method of particle size determination: An analysis of the particle size distribution was carried out twice during the exposure period using a cascade impactor according to MAY (1975).
The impactor is a device that classifies particles present in a sampleof air or gas into known size ranges. It does this by drawing the air sample through a cascade of progressively finer nozzles. The air jets from these impact on plane sampling surfaces (slides) covered with adhesive tape. Each stage represents an aerodynamic size range. The dust from the exposure chamber was sucked through the cascade impactor for 1.5 to 5 minutes at a constant flow rate of 5 l/min. The slides were removed from the impactor and were weighed on an analytical balance (SARTORIUS, type 1601004, precision 10µg).
Respirable amount (particle size <= 4 µm)
Dose level 0.90 mg/l air:0.61 mg/l air
Dose level 2.42 mg/l air:2.01 mg/l air
Dose level 4.72 mg/l air: 3.52 mg/l air
The sample supplied had a particle size distribution of 55.9 % in the particle size range of 2.4 to 5.0 µm.
- Temperature, humidity: The temperature (GTH 1200 Digital Thermometer, Fa. Greisinger Electronic GmbH) and humidity (Sekunden-Hygrometer Typ 6100, Testoterm) was continuously monitored close to the nose of the animals in the inhalation chamber. The temperature was 19 °C - 21 °C and the relative humidity was 60 % - +/- 20 %.
TEST ATMOSPHERE (Test substance concentration)
- Brief description of analytical method used: The dust concentration in the inhalation chamber was measured with an air sample filter (Minisart SM 17598) and pump (water jet air pump controlled by a rotameter). Dust samples were taken during the first half and during the second half of the exposure. The Minisart SM 17598 filters were placed close to the animals' nose and sucked through with a constant flow of air of 300 l/h for 1 to 3 minutes. The filters were weighed before and after sampling (accuracy 0.01 mg).
TEST ATMOSPHERE
- Particle size distribution: The sample supplied had a particle size distribution of 55.9 % in the particle size range of 2.4 to 5.0 µm measured with a Malvern particle sizer.
Particle size (µm) and mean (concentration 0.90 mg/l air):
<0.5 µm: 1.33 %
0.5 µm: 12.80 %
1 µm: 22.25 %
2 µm: 52.36 %
4 µm: 68.25 %
8 µm: 75.84 %
16 µm: 90.17 %
>= 32 µm: 99.90 &
Particle size (µm) and mean (concentration 2.42 mg/l air):
<0.5 µm: 0.0 %
0.5 µm: 5.18 %
1 µm: 17.19 %
2 µm: 52.89 %
4 µm: 83.10 %
8 µm: 87.50 %
16 µm: 93.73 %
>= 32 µm: 100.01 %
Particle size (µm) and mean (concentration 4.72 mg/l air):
<0.5 µm: 1.87 %
0.5 µm: 8.85 %
1 µm: 31.02 %
2 µm: 69.52 %
4 µm: 74.59 %
8 µm: 78.18 %
16 µm: 91.77 %
>= 32 µm: 100.0 %
- MMAD:
Dose level 0.90 mg/l air: 2.44 µm
Dose level 2.42 mg/l air: 2.32 µm
Dose level 4.72 mg/l air: 2.01µm - Analytical verification of test atmosphere concentrations:
- yes
- Remarks:
- see "details on inhalation exposure" above.
- Duration of exposure:
- 4 h
- Remarks on duration:
- Exposition started by locating the rats into the exposure chamber.
- Concentrations:
- mean actual concentration 0.90 +/- 0.39 (nominal concentration: 1.9 mg/l air), 2.42 +/- 0.38 (nominal concentration: 7.4 mg/l air), 4.72 +/- 1.45 (nominal concentration: 8.6 mg/l air) mg V2O5 analytical grade pulverised/l air. 4.72 mg/l air was the highest concentration that could be generated in the inhalation chamber.
- No. of animals per sex per dose:
- 5 males /5 females
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: During and following espoxure, observations were made. A careful clinical examination was made at least once each day until all symptoms subsided, thereafter each working day. Observations on mortality were made at least once daily with appropriate actions taken to minimize loss of animals to the study. Individual body weights of the animals were determined before the exposure, after 1 week and at study termination.
- Necropsy of survivors performed: Yes, Necropsy of all animals was carried out and all gross pathological changes were recorded. From animals which survived 24 hours or longer a microscopic examination of all organs which showed evident lesions was performed after preparation of paraffin sections and HE-staining..
- Other examinations performed: clinical signs, body weight,organ weights, histopathology, other: Cageside observations included, but were not limited to, changes in the skin and fur, eyes, mucous membranes, respiratory, circulatory, autonomic and central nervous system, and somatomotor activity and behaviour pattern. Particluar attention was directed to observation of tremors, convulsions, salivation, diarrhoea. lethargy, sleep and coma. - Statistics:
- The mass median aerodynamic diameter (MMAD) was estimated by means of nonlinear regression analysis (LICHFIELD & WILCOXON). The 32 mm particle size range was not included in the determination of the MMAD in order not to give undue weight to this value.
The LC50 (24 hours/14days) was calculated by regression analysis (if possible according to FINNEY). - Sex:
- male
- Dose descriptor:
- LC50
- Effect level:
- 11.09 mg/L air
- 95% CL:
- > 0.68 - < 180.68
- Exp. duration:
- 4 h
- Remarks on result:
- other: Slope: 1.783; LC50 was calcualted according to Finney (probit analysis)
- Sex:
- male
- Dose descriptor:
- LC0
- Effect level:
- 2.42 mg/L air
- Exp. duration:
- 4 h
- Key result
- Sex:
- female
- Dose descriptor:
- LC50
- Effect level:
- 4.29 mg/L air
- Exp. duration:
- 4 h
- Remarks on result:
- other: Slope: 20.14; LC50 was calculated by regressiong analysis.
- Sex:
- female
- Dose descriptor:
- LC0
- Effect level:
- 4.72 mg/L air
- Exp. duration:
- 4 h
- Mortality:
- Death at 2.42 mg/l in males and 4.72 mg/l in females.
At the dose-level of 2.42 mg/l prematurely deceased animal (1/5 males) died 4 days after start of exposure.
At the dose level of 4.72 mg/l prematurely deceased animals (1/5 males; 4/5 females) died 2 days after start of exposure. - Clinical signs:
- other: Dose level and toxic signs: 0.90 mg/l: no signs of systemic intolerance (males and females) 2.42 mg/l: Except for mortality no signs of systemic intolerance (males and females) 4.72 mg/l: except for mortalitiy no signs of systemic intolerance (males and
- Body weight:
- There was no inhibition of body weight gain in males or females.
- Gross pathology:
- Autopsy of deceased animals:
lungs haemorrhagic: 4.72 mg/l (1/1 males; 3/4 females). All further deceased animals showed no pathological findings.
Autopsy of surviving animals:
lungs haemorrhagic: 2.42 mg/l air (2/4 males; 1/5 females)
Lungs haemorrhagic and light dark coloured: 4.72 mg/l air (1/4 males)
All further scarificed animals showed no pathological findings.
The histopathological changes found in the lungs were:
2.42 mg/l air: vascular congestion (2/2 males); oedema (1/2 males) and (inital) haemorrhagic bronchopneumonia (2/2 males)
4.72 mg/l air: vascular congestion (2/2 males; 3/3 females); oedema (1/2 males; 2/3 females) and (inital) haemorrhagic bronchopneumonia (2/2 males; 3/3 females)
These changes can be regarded as unspecific effects which can normally occur after the administration of a dust. - Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- LC50 (female rats) = 4.29 mg/L air
According to the Regulation (EC) No 1272/2008 and subsequent adaptations, the substance is classifed as acutely toxic via the inhalation route (Category 4).
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 4 290 mg/m³ air
- Quality of whole database:
- GLP guideline studies with divanadium pentaoxide in three different grades (i.e. analytical-pulverized, technical-fused, technical-pulverised) exist.
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1991-08-20 to 1991-09-17
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Minor deviations: - According to the guideline, a limit test of at least 2000 mg/kg bw can be carried out. In this study one additional concentration above the limit dose was also tested. - According to the guideline, the individual weights should be determined before the application of the test substance , which was done in this study. The individual weights were not provided in the report but only the average weight of the males and females per dose. - The guideline suggested that the rats should be in the weight range of 200 to 300 g at the beginning of the study but in this study the rats were in the weight range of 166 -181 g. - According to the guideline, the rats should be housed indivdually. In this study they were housed in groups of two or three rats. - According to the guideline the relative humidity should be between 30 - 70 %. In this study the relative humidity was slightly higher (60 +/- 20 %). - According to the guideline, the test substance should be applied to the skin. In this study the test substance was applied first to the patch and the patch was placed onto the skin.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Version / remarks:
- 1987-02-24
- Deviations:
- yes
- Remarks:
- see rational for reliability
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The study states that the study was performed according to eg. "Good Laboratory Practice" Regulations of the EEC enacted in Germany in the "Chemikaliengesetz" dated March 14 th, 1990, BGBL.I, pp. 521, 1990.
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Lippische Versuchstierzucht HAGEMANN GmbH, D- 4923 Extertal 1
- Age at study initiation: approx. 40 - 60 days
- Weight at study initiation: 166 - 181 g
- Fasting period before study: approx. 16 hours
- Housing: Animals were kept in groups of two or three in MAKROLON cages (type III). Gradulated textured wood was used as bedding material (Granulat Typ A2, supplier: Messrs. BRANDENBURG, Inh. H.Brandenburg, D-2849 Goldenstedt)
- Diet: Standardized diet for rats ALTROMIN 1324 (supplied by: ALTROMIN GmbH, D-4937 LAge/Lippe)
- Water (ad libitum): tap water
- Quarantine period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22 °C +/- 3 °C (maximum range)
- Relative humidity: 60 % +/- 20 % (maximum range)
- Photoperiod (hrs dark / hrs light): 12/12 - Type of coverage:
- occlusive
- Vehicle:
- other: hydroxypropyl-methylcellulose
- Details on dermal exposure:
- TEST SITE
The test substance was applied on the shaved intact dorsal skin of rats (5 X 6 cm, 1/10 of body surface). The hair on the site of application was clipped with hair-clippers without causing injury approximately 24 hours before application. The site was situated on the animal's back between the fore and hind extremeties and had an area of approx. 5 X 6 cm.
The test substance was applied to 8 layers of gauze and to the application site. The patch was covered with a plastic sheet and secured with adhesive plaster.
REMOVAL OF TEST SUBSTANCE
- Time after start of exposure: At the end of the exposure period, residual substance was removed with tepid tap water.
TEST MATERIAL
- Amount(s) applied (volume or weight with unit): The volume of application was 20 ml/kg b.w.. The dose interval factor was 1.25.
VEHICLE
0.8 % aqueous hydroxypropyl-methylcellulose gel (Methocel E 4 M) served as vehicle for V2O5 analytical grade pulverised.
Batch No.(Vehicle): MM 84097413 - Duration of exposure:
- 24 hours
- Doses:
- 2000, 2500 mg V2O5 analytical grade pulverised/kg b.w.
- No. of animals per sex per dose:
- 5 males /5 females
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Observations were performed immediatly, 5, 15, 30 and 60 min, as well as 3 h, 6 h and 24 h after administration. During the follow-up period changes in skin and fur, eyes and mucous membranes, and the respiratory, circulatory, autonomic and central nervous system and somatomotor activity and behaviour pattern were observed at least once a day until all symptoms have subsided, thereafter each working day. Attention was also paid to possible tremors, convulsions, salivation, diarrhoea, lethargy, sleep and coma. Observations on mortality were made at least once daily with appropriate actions taken to minimise loss of animals during the study.
Individual body weights were recorded before administration of the substance, thereafter in weekly intervals up to the end of the study, and at death.
- Necropsy of survivors performed: yes, at the end of the experiments all surviving animals were sacrificed, dissected and inspected macroscopically. All gross pathological changes were recorded. From animals which survive 24 hours or longer a microscoic examination of all organs which show evident lesions was performed. Autopsy and macroscopic inspection of the animals which died prematurely were carried out as soon as possible after exitus.
- Other examinations performed: Changes in weight were calculated and recorded when survival exceeds one day. The skin was observed for the development of erythema and oedema and was rated as follows:
Erythema
0 = no erythema
1 = very slight erythema (barely perceptible)
2 = well-defined erythema
3 = moderate to severe erythema
4 = severe erythemy (beet redness) to slight eschar formation (injuries in depth)
Oedema
0 = no oedema
1 = very slight oedema (barely perceptible)
2 = slight oedema (edges of area well defined by definite raising)
3 = moderate oedema (raised approx. 1 mm)
4 = severe oedema (raised more than 1 mm and extending beyond the area of exposure) - Statistics:
- The LD50 could not be calculated because none of the animals died prematurely.
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- > 2 500 mg/kg bw
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 2 500 mg/kg bw
- Mortality:
- None of the animals died prematurely.
- Clinical signs:
- other: Under the present test conditions no local or systemic intolerance reactions were observed up to the highest testd dose-level of 2500 mg V2O5 analytical grade pulverised /kg b.w. by dermal administration to rats.
- Gross pathology:
- No pathological findings
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- LD50 (rats) > 2500 mg/kg bw
According to the EC-Regulation 1272/2008 and subsequent regulations, the test item is not classified as acute toxic via the dermal route.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- discriminating dose
- Value:
- 2 500 mg/kg bw
- Quality of whole database:
- GLP guideline studies with divanadium pentaoxide in three different grades (i.e. analytical-pulverized, technical-fused, technical-pulverised) exist.
Additional information
Acute toxicity, oral
Divanadium pentaoxide in three different grades (i.e. analytical-pulverized, technical-fused, technical- pulverised) is harmful if swallowed (LD50≥ 221 < 2000 mg/kg b. w. p. o.) based on results of acute oral toxicity studies in the rat.
Acute toxicity, inhalative
Divanadium pentaoxide in three different grades (i.e. analytical-pulverized, technical-fused, technical- pulverised) is harmful if inhaled (LC50(4h) ≥ 2.21 < 5 mg/L) based on results of acute inhalation toxicity studies in the rat.
Acute toxicity, dermal
No acute toxicity was observed in rats after dermal administration of up to 2500 mg V2O5/kg b.w. in three different grades (i.e. analytical-pulverised, technical-fused, technical-pulverised).
The following information of V2O5 powder (analytical grade) is taken into account for the hazard / risk assessment:
Acute toxicity - oral: (LD50: 467 mg/kg b.w. p.o.)
Acute toxicity - inhalation: harmful (LD50: 4.3 mg/L)
Acute toxicity - dermal: non-toxic (LD50: > 2500mg/kg b.w. p.o.)
Justification for classification or non-classification
Oral toxicity
According to EC Regulation 1272-2008, divanadium pentaoxide need to
be classified for acute oral toxicity study as follows:
analytical grade - pulverised: Category 4 (LD50≥ 467mg/kg b.w. p.o.), H302: Harmful if swallowed
technical grade - fused: Category 4 (LD50≥ 658mg/kg b.w. p.o.), H302: Harmful if swallowed
technical grade - pulverized: Category 3 (LD50≥221 mg/kg b.w. p.o.), H301: Toxic if swallowed
Inhalation toxicity
According to EC Regulation 1272/2008, divanadium pentaoxide in three different grades (i.e. analytical-pulverized) need to be classified as Category 4, H 332: Harmful if inhaled.
Acute toxicity, dermal
No acute toxicity was observed after dermal administration of up to 2500 mg V2O5 /kg b.w. in rats in three different grades (i.e. analytical-pulverised). According to EC Regulation 1272 /2008, V2O5 can be classified as relatively non-toxic based on results in acute dermal toxicity studies in the rat.
Respiratory irritation:
Based on human data, exposure to divanadium pentaoxide may result in respiratory irritation (see Section 7.3). Thus, criteria for classification in STOT-SE Category 3 - respiratory tract irritation are met. According to the EC Regulation 1272/2008, divanadium pentaxoide is classified STOT SE Category 3: H335: May cause respiratory irritation.
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