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EC number: 406-260-5 | CAS number: 58834-75-6 BTN; VPO CATALYST
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study conducted using methods similar to accepted test guidelines and published in a peer reviewed journal
Data source
Reference
- Reference Type:
- publication
- Title:
- Developmental toxicity of vanadium in mice after oral administration
- Author:
- Paternain JL, Domingo JL, Gomez M, Ortega A and Corbella J
- Year:
- 1 990
- Bibliographic source:
- Journal of Applied Toxicology 10(3): 181-186, 1990
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- Mouse rather than rat used
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- vanadyl sulphate pentahydrate
- IUPAC Name:
- vanadyl sulphate pentahydrate
- Reference substance name:
- 14708-82-8
- Cas Number:
- 14708-82-8
- IUPAC Name:
- 14708-82-8
- Details on test material:
- - Name of test material (as cited in study report): Vanadyl sulphate pentahydrate
- Molecular formula (if other than submission substance): VOSO4.5H2O
- Molecular weight (if other than submission substance): 253.077
- Smiles notation (if other than submission substance): [V+2]=O.O.O.O.O.O.S(=O)(=O)([O-])[O-]
- InChl (if other than submission substance): 1/H2O4S.5H2O.O.V/c1-5(2,3)4;;;;;;;/h(H2,1,2,3,4);5*1H2;;/q;;;;;;;+2/p- 2/rH2O4S.OV.5H2O/c1-5(2,3)4;1-2;;;;;/h(H2,1,2,3,4);;5*1H2/q;+2;;;;;/p-2
- Structural formula attached as image file (if other than submission substance): see Fig. 3
Constituent 1
Constituent 2
Test animals
- Species:
- mouse
- Strain:
- Swiss
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Panlab, Barcelona, Spain
- Age at study initiation: No data
- Weight at study initiation: 25 - 30 g
- Fasting period before study: No
- Housing: Mating phase - 1 male/2 females per cage, otherwise not detailed
- Diet (e.g. ad libitum): Panlab commercial rodent diet, ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 10 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 - 23 deg C
- Humidity (%): 40 - 50 % RH
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Analytical verification of doses or concentrations:
- not specified
- Details on mating procedure:
- - Impregnation procedure: cohoused
- M/F ratio per cage: 1 male / 2 females
- Length of cohabitation: No data
- Proof of pregnancy: sperm in vaginal smear referred to as day 0 of pregnancy
- Any other deviations from standard protocol: None reported - Duration of treatment / exposure:
- Days 6-15 of gestation
- Frequency of treatment:
- Daily
- Duration of test:
- 18 days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
37.5, 75 or 150 mg/kg/day
Basis:
nominal conc.
- No. of animals per sex per dose:
- 22 mated, sperm positive, females / dose group
- Control animals:
- yes, concurrent vehicle
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
- Cage side observations included mortaility / morbidity.
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: Daily throughout gestation (during pre-treatment, treatment and post-treatment periods)
FOOD CONSUMPTION AND COMPOUND INTAKE: Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/animal/3 or 6 day period
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 18
- Organs examined: Liver, kidney, gravid uterus and placentae weighed - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes: 1/3 per litter
- Skeletal examinations: Yes: 2/3 per litter
- Head examinations: No data - Statistics:
- Continuous data (maternal body weight, body weight gain, food consumption, etc.) were analysed using a one-way analysis of variance with significant F values analysed further using Student's f-test or the Mann-Whitney U test. Statistical comparison of the vanadium analyses were by Student's t-test (one tailed) with a Bonferroni correction for multiple comparisons between treatment groups. A probability of P < 0.05 was used as the criterion of statistical significance. Incidence data were compared using X2 contingency tables with each test group compared to the control group when X2 was significant.
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Mean maternal body weight gain during the pretreatment interval (Days 0-6 of gestation) was comparable between treated and control groups. There were significant decreases in body weight gain during the exposure period (Days 6-15 of gestation) in treated animals. This was dose-related and observed at all dose levels. Body weight gain during the post-exposure period (Days 15-18 of gestation) indicated that treated animals gained less weight than controls although these differences were not statistically significant.
There was no significant differences between groups in food consumption although an apparent decrease in the mean food consumption was observed for the 75 and 150 mg/kg/day treatment groups from Day 0 to Day 18 of gestation.
A treatment-related affect on maternal organ weights, including absolute and corrected body weight, absolute liver weight, absolute kidney weight and placenta weight was apparent on termination. Gravid uterine weights were significantly lower at all dose levels compared with controls. Absolute maternal liver weight (but not relative liver weight) was significantly decreased at the two higher dose levels, 75 and 150 mg/kg/day, and absolute kidney weight was significantly decreased at 150 mg/kg/day.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 37.5 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: maternal toxicity
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
- Dose descriptor:
- NOAEL
- Effect level:
- 37.5 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: developmental toxicity
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
Treatment had no effect on the number of total implantations, live and dead foetuses, late resorptions per litter, or on the percentage of post-implantation losses or the sex ratio. The incidence of early resorptions per litter exhibited a dose-related increase in all treatment groups.
Mean foetal body weights and the mean foetal body lengths were significantly lower in the treated groups compared to controls and there was a significant incidence of stunted fetuses in the 75 and 150 mg/kg/day groups relative to controls.
Selected foetal tissues were analysed for vanadium. Vanadium could not be detected in the tissues of control animals. It was present at detectable levels in both maternal and foetal tissues of treated animals.
Cleft palate and micrognathia were the most significant external malformations observed in the 150 mg/kg/day group. The total number of external defects was statistically significant for all treated groups relative to controls. The only incidental abnormality observed after visceral examination was hydrocephaly in fetuses from dams receiving 75 or 150 mg/kg/day.
Increased incidence of skeletal variations was seen in all treated groups. Decreased ossification of the supraoccipital bone and decreased ossification of the carpus and tarsus were the most common findings. The increase in the total number of skeletal defects was significantly different from the controls in all the treated groups, this increase being dose-dependent.
Effect levels (fetuses)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 37.5 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: embryotoxicity
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
- Dose descriptor:
- NOAEL
- Effect level:
- 37.5 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: fetotoxicity
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
Maternal toxicity
Observation |
Dose level(mg/kg/day) |
||||
0 |
37.5 |
75 |
150 |
||
Number of dams |
20 |
16 |
20 |
20 |
|
Weight gain (g) |
Day 6-15 (treatment period) |
18.41 |
10.01* |
8.58** |
7.63** |
Day 0-18 (total study period) |
29.75 |
24.30* |
20.07* |
18.48** |
|
Food consumption (g/dam) |
Day 6-15 (treatment period) |
46.00 |
37.87 |
38.90 |
40.50 |
Day 0-18 (total study period) |
89.92 |
89.31 |
84.20 |
85.30 |
|
Terminal weight (g) |
54.62 |
44.31* |
45.49** |
43.47** |
|
Organ weights (g) |
Liver |
2.53 |
2.11 |
2.02 * |
1.98 * |
|
Kidney |
0.41 |
0.40 |
0.35 * |
0.34 * |
|
Gravid uterus |
20.61 |
14.24* |
16.50* |
15.03* |
|
Placenta |
0.15 |
0.15 |
0.15 |
0.14** |
Significantly different to controls; * p<0.05); **p<0.01
Litter parameters
|
Dose level(mg/kg/day) |
|||
0 |
37.5 |
75 |
150 |
|
No. litters |
20 |
16 |
20 |
20 |
No. implantations/litter |
12.6 |
11.2 |
12.3 |
12.8 |
No. early resorptions/litter |
0.30 |
1.7* |
0.70* |
1.2* |
No. late resorptions/litter |
0.00 |
0.00 |
0.10 |
0.22 |
No. dead foetuses/litter |
0.10 |
0.00 |
0.50 |
0.20 |
No. live foetuses/litter |
12.2 |
9.5 |
11.0 |
11.2 |
Post-implantation loss (%) |
3.1 |
15.1 |
10.5 |
12.5 |
Sex ratio (M/F) |
1.03 |
0.85 |
0.83 |
0.89 |
Foetal body weight (g) |
1.35 |
1.18 ** |
1.18 ** |
1.07 ** |
Foetal body length (mm) |
28.7 |
27.7 * |
24.4 ** |
23.4 ** |
Significantly different to controls; * p<0.05); **p<0.001
Foetal abnormalities
|
Dose level(mg/kg/day) |
|||
0 |
37.5 |
75 |
150 |
|
External abnormalities |
|
|
|
|
No. examined/No. litters |
240/20 |
152/16 |
220/20 |
188/20 |
No. stunted foetuses/affected litters |
2/2 |
15/2 |
11/7* |
31/12*** |
Haematoma - face |
0 |
4 (3)** |
2 (1) |
5 (4)** |
- neck |
2/2 |
9/4 ** |
3/2 |
12/8 ** |
- thorax |
0 |
0 |
2/2 |
6/4 ** |
- limbs |
0 |
0 |
4/2 |
0 |
- dorsal |
0 |
8/2 * |
5/2 * |
4/2 * |
Anophthalmia / microphthalmia |
0 |
10/3 |
0 |
0 |
Exencephaly |
2/1 |
0 |
0 |
4/3 |
Exophthalmia |
0 |
0 |
4/3 |
0 |
Cleft palate |
0 |
0 |
4/3 |
58/12 *** |
Micrognathia |
0 |
2 (1) |
3 (1) |
12/3 *** |
Club foot |
0 |
0 |
0 |
4/2 |
Curled tail |
0 |
0 |
2/1 |
2/2 |
Total external defects |
4/2 |
22/8 *** |
25/11 *** |
76/17 *** |
Visceral abnormalities |
|
|
|
|
Hydrocephaly |
0 |
0 |
2/2 |
4/3 |
Skeletal abnormalities |
|
|
|
|
No. examined/No. litters |
120/20 |
70/16 |
117/20 |
86/20 |
Reduced ossification - Supraoccipital |
6/3 |
4/3 |
28/7* |
38/13 *** |
- Carpus |
0 |
10/2 *** |
7/3 *** |
16/6 *** |
- Tarsus |
0 |
10/2 *** |
12 (2)*** |
27/8 *** |
- Sternebrae |
4/2 |
8/2 * |
8/3 |
10/3 * |
Bipartite sternebrae |
7/3 |
3/2 |
18/9 ** |
23/12 *** |
Asymmetric ribs |
9/4 |
13/9 * |
44/15 *** |
69/20 *** |
Total skeletal defects |
9/4 |
13/9 * |
44/15 *** |
69/20 *** |
Significantly different to controls; *p<0.05); **p<0.01; ***p<0.001
Tissue vanadium concentration(µg/g wet weight)
Organ |
Dose level(mg/kg/day) |
|||
0 |
37.5 |
75 |
150 |
|
Dam liver |
<loq |
0.484 |
0.850 |
1.589 |
Dam kidney |
<loq |
0.493 |
0.769 |
1.912 |
Dam spleen |
<loq |
0.707 |
1.340 |
2.369 |
Placenta |
<loq |
0.226 |
0.375 |
0.640 |
Foetus |
<loq |
1.588 |
2.896 |
4.492 |
Loq: Limit of quantitation
Applicant's summary and conclusion
- Conclusions:
- Maternal toxicity was apparent as decreased weight gain and reduced body weight in pregnant mice treated with vanadyl sulphate pentahydrate at doses of 37.5, 75 or 150 mg/kg/day. Effects on foetal weights and lengths, in addition to an increased incidence of poorly ossified skeletal elements at all dose levels was seen as embryofoetotoxicity. Treatment resulted in increased incidence of external malformations and gross, visceral and skeletal variations with cleft palate and micrognathia being the major gross malformations seen at the highest dose level (150 mg/kg/day).
The No Observed Effect Level (NOEL) for maternal toxicity, embryotoxicity, foetotoxicity and teratogenicity was less than 37.5 mg/kg/day. - Executive summary:
A prenatal developmental toxicity study has been undertaken on vanadyl sulphate pentahydrate using methods similar to those described in OECD TG No. 414.
Maternal toxicity was apparent as decreased weight gain and reduced body weight in pregnant mice treated with vanadyl sulphate pentahydrate at doses of 37.5, 75 or 150 mg/kg/day. Effects on foetal weights and lengths, in addition to an increased incidence of poorly ossified skeletal elements at all dose levels was seen as embryofoetotoxicity. Treatment resulted in increased incidence of external malformations and gross, visceral and skeletal variations with cleft palate and micrognathia being the major gross malformations seen at the highest dose level (150 mg/kg/day).
The No Observed Effect Level (NOEL) for maternal toxicity, embryotoxicity, foetotoxicity and teratogenicity was less than 37.5 mg/kg/day.
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