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EC number: 701-186-2 | CAS number: -
- 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
Read-across from analogue:
Oral acute toxicity: LD50 > 2000 mg/kg bw , key study with 6 female rats according to OECD Test Guideline 423.
Dermal acute toxicity: LD50 > 2000 mg/kg bw, extrapolation from oral data.
Inhalation acute toxicity: LC50 > 50 mg/l, extrapolation from oral data.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
1. HYPOTHESIS FOR THE ANALOGUE APPROACH: The analogue approach covers the substance Ultramarine Blue (EC nº 701-340-9) and the substance Ultramarine Violet (EC nº 701-186-2).The analogue Ultramarine Blue shares the same structure (Sodalite-type structure (SOD-Zeolite)) with the substance Ultramarine Violet. Therefore, they are expected to be toxicologically equivalent.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES) Ultramarine blue, C.I. Pigment blue 29, EC number: 701-340-9;
Ultramarine Violet, C.I. Pigment Violet 15, EC number: 701-186-2.
No relevant impurities.
3. ANALOGUE APPROACH JUSTIFICATION: The analogue approach covers the substance Ultramarine Blue (EC nº 701-340-9) and the substance Ultramarine Violet (EC nº 701-186-2).The analogue Ultramarine Blue shares the same structure (Sodalite-type structure (SOD-Zeolite)) with the substance Ultramarine Violet. Therefore, they are expected to be toxicologically equivalent.
4. DATA MATRIX (Please, see attached document "Reporting Format for the analogue approach") - Reason / purpose for cross-reference:
- read-across source
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Interpretation of results:
- other: Not classified.
- Remarks:
- Criteria used for interpretation of results: EU. According to GHS criteria the test item could be classified in the Category 5 or as " GHS criteria not met", further information is needed regarding acute oral toxicity taking 5000mg/kg bw
- Conclusions:
- Based on the experimental results obtained with the analogue, the read-across approach is applied and the LD50 for substance Ultramarine Violet is considered to be greater than 2000 mg/kg bw.
- Executive summary:
Based on the experimental results obtained with the analogue, the read-across approach is applied and the LD50 for substance Ultramarine Violet is considered to be greater than 2000 mg/kg bw.
Reference
The analogue approach covers the substance Ultramarine Blue (EC nº 701-340-9) and the substance Ultramarine Violet (EC nº 701-186-2).
The analogue Ultramarine Blue shares the same structure (Sodalite-type structure (SOD-Zeolite)) with the substance Ultramarine Violet. Therefore, they are expected to be toxicologically equivalent.
Based on the experimental results obtained with the analogue, the read-across approach is applied and the LD50 for substance Ultramarine Violet is considered to be greater than 2000 mg/kg bw.
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- other: extrapolation from results obtained by the oral route
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Extrapolation based on available guidelines on route-to-route extrapolation of toxicity data when assessing health risks of chemicals.
- Principles of method if other than guideline:
- Extrapolation based on available guidelines on route-to-route extrapolation of toxicity data when assessing health risks of chemicals.
- Key result
- Dose descriptor:
- LC50
- Effect level:
- > 50 mg/L air
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- Based on the assumptions for the extrapolation from the acute oral toxicity data, the 4 -h LC50 would be greater than 10-50 mg/l.
- Executive summary:
From the available data on two acute oral toxicity studies, it is concluded that the oral LD50 for the substance is greater than 2000 mg/kg bw (study 1: no mortality was observed) and greater from 10000 mg/kg bw (study 2: mortality was observed). As recommended in the corresponding guidelines, where data from the oral route is being used as the starting point, if no data are available on oral bioavailability, it is appropriate to assume that 100% of an orally administered dose is systemically available. Since no data is available on inhalation absorption, the most precautionary default would be to assume 100% absorption by this route.
Based on this acute oral toxicity data, an oral NOAEL may be identified as greater than 10000 mg/kg bw. This NOAEL can be modified into an inhalation NOAEL using a route-to-route extrapolation based on the assumptions stated above. Taking into account an exposure of 4 hours for the acute inhalation toxicity study, the value of the oral LD50 is divided by the default physiological parameter under the allometric scaling principle which is approximately 0.2 m3/kg bw for rats. This extrapolation leads to a value of 10 mg/l (study 1) and 50 mg/l (study 2). Therefore, the 4 -h LC50 would be greater than 10 -50 mg/l.
Reference
Based on available guidelines on route-to-route extrapolation of toxicity data when assessing health risks of chemicals, an extrapolation based on the acute oral toxicity data is calculated for the inhalation route.
From the available data on two acute oral toxicity studies, it is concluded that the oral LD50 for the substance is greater than 2000 mg/kg bw (study 1: no mortality was observed) and greater from 10000 mg/kg bw (study 2: mortality was observed). As recommended in the corresponding guidelines, where data from the oral route is being used as the starting point, if no data are available on oral bioavailability, it is appropriate to assume that 100% of an orally administered dose is systemically available. Since no data is available on inhalation absorption, the most precautionary default would be to assume 100% absorption by this route.
Based on this acute oral toxicity data, an oral NOAEL may be identified as greater than 10000 mg/kg bw. This NOAEL can be modified into an inhalation NOAEL using a route-to-route extrapolation based on the assumptions stated above. Taking into account an exposure of 4 hours for the acute inhalation toxicity study, the value of the oral LD50 is divided by the default physiological parameter under the allometric scaling principle which is approximately 0.2 m3/kg bw for rats. This extrapolation leads to a value of 10 mg/l (study 1) and 50 mg/l (study 2). Therefore, the 4 -h LC50 would be greater than 10 -50 mg/l.
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- other: extrapolation from results obtained by the oral route
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Extrapolation based on available guidelines on route-to-route extrapolation of toxicity data when assessing health risks of chemicals.
- Principles of method if other than guideline:
- Extrapolation based on available guidelines on route-to-route extrapolation of toxicity data when assessing health risks of chemicals.
- Dose descriptor:
- LD50
- Effect level:
- > 1 000 mg/kg bw
- Key result
- Dose descriptor:
- LD50
- Effect level:
- > 5 000 mg/kg bw
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- Based on the assumptions for the extrapolation from the acute oral toxicity data, the dermal LD50 would be greater than 1000 mg/kg bw (study 1) and greater than 5000 mg/kg bw (study 2).
- Executive summary:
From the available data on two acute oral toxicity studies, it is concluded that the oral LD50 for the substance is greater than 2000 mg/kg bw (study 1: no mortality was observed) and greater from 10000 mg/kg bw (study 2: mortality was observed). As recommended in the corresponding guidelines, where data from the oral route is being used as the starting point, if no data are available on oral bioavailability, it is appropriate to assume that 50% of an orally administered dose is systemically available. Since no data is available on skin absorption, the most precautionary default would be to assume 100% absorption by this route although in reality very few substances will cross the skin to this extent. Therefore, based on these assumptions, the dermal LD50 would be greater than 1000 mg/kg bw (study 1) and greater than 5000 mg/kg bw (study 2).
Reference
Based on available guidelines on route-to-route extrapolation of toxicity data when assessing health risks of chemicals, an extrapolation based on the acute oral toxicity data is calculated for the dermal route.
From the available data on two acute oral toxicity studies, it is concluded that the oral LD50 for the substance is greater than 2000 mg/kg bw (study 1: no mortality was observed) and greater from 10000 mg/kg bw (study 2: mortality was observed). As recommended in the corresponding guidelines, where data from the oral route is being used as the starting point, if no data are available on oral bioavailability, it is appropriate to assume that 50% of an orally administered dose is systemically available. Since no data is available on skin absorption, the most precautionary default would be to assume 100% absorption by this route although in reality very few substances will cross the skin to this extent. Therefore, based on these assumptions, the dermal LD50 would be greater than 1000 mg/kg bw (study 1) and greater than 5000 mg/kg bw (study 2).
Additional information
Read-across from analogue:
Oral acute toxicity:
Key study: Study with 6 female rats (2 groups with 3 female rats per group) in a single dose oral toxicity test at 2000 mg/kg bw.
OECD Test Guideline 423.
The result was as follows: LD50 >2000 mg/kg bw.
Dermal acute toxicity:
Key study: Extrapolation from oral data.
From the available data on two acute oral toxicity studies, it is concluded that the oral LD50 for the substance is greater than 2000 mg/kg bw (study 1: no mortality was observed) and greater from 10000 mg/kg bw (study 2: mortality was observed). As recommended in the corresponding guidelines, where data from the oral route is being used as the starting point, if no data are available on oral bioavailability, it is appropriate to assume that 50% of an orally administered dose is systemically available. Since no data is available on skin absorption, the most precautionary default would be to assume 100% absorption by this route although in reality very few substances will cross the skin to this extent. Therefore, based on these assumptions, the dermal LD50 would be greater than 1000 mg/kg bw (study 1) and greater than 5000 mg/kg bw (study 2).
Inhalation acute toxicity:
Key study: Extrapolation from oral data.
From the available data on two acute oral toxicity studies, it is concluded that the oral LD50 for the substance is greater than 2000 mg/kg bw (study 1: no mortality was observed) and greater from 10000 mg/kg bw (study 2: mortality was observed). As recommended in the corresponding guidelines, where data from the oral route is being used as the starting point, if no data are available on oral bioavailability, it is appropriate to assume that 100% of an orally administered dose is systemically available. Since no data is available on inhalation absorption, the most precautionary default would be to assume 100% absorption by this route.
Based on this acute oral toxicity data, an oral NOAEL may be identified as greater than 10000 mg/kg bw. This NOAEL can be modified into an inhalation NOAEL using a route-to-route extrapolation based on the assumptions stated above. Taking into account an exposure of 4 hours for the acute inhalation toxicity study, the value of the oral LD50 is divided by the default physiological parameter under the allometric scaling principle which is approximately 0.2 m3/kg bw for rats. This extrapolation leads to a value of 10 mg/l (study 1) and 50 mg/l (study 2). Therefore, the 4 -h LC50 would be greater than 10 -50 mg/l.
Justification for classification or non-classification
Oral acute toxicity LD50> 2000 mg/kg: not classified.
Dermal acute toxicity LD50> 2000 mg/kg: not classified.
Inhalation acute toxicity LC50 > 10 -50 mg/l: not classified (inhalation of dusts)
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