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EC number: 269-075-7 | CAS number: 68187-15-5 An inorganic pigment that is the reaction product of high temperature calcination in which praseodymium (III) oxide, praseodymium (IV) oxide, silicon oxide, and zirconium (IV) oxide in varying amounts are homogeneously and ionically interdiffused to form a crystalline matrix of zircon. Its composition may include any one or a combination of the modifiers alkali or alkaline earth halides.
- 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

Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
The in-vitro and in-vivo experiments described above are in very good agreement with regards to the negligible level of bioavailability of the elements Zr and Pr contained in the pigment.
(1) In in-vitro dissolution experiments in five different artificial physiological media, the highest dissolved Zr, Si and Pr concentrations were below 2.4 µg/L (24h, ALF), 62.7 µg/L (24h, ALF) and 574 µg/L (24h, GST), respectively, even at the highest loading of 0.1 g/L, referring to a solubility of 0.0024 %, 0.063 % and 0.574 %, respectively. Thus, the pigment is considered biologically inert. The dissolved Zr, Pr and Si concentrations from this pigment in GST, after 2h hours (2-hour gastric passage) were below LoD, 350 μg/L and 30 μg/L, respectively, even at the highest loading of 0.1g/L, corresponding to a solubility of less than 0.4 %.
(2) In a 28-day oral toxicity study with 1,000 mg/kg pigment no increase in Zr and Pr plasma and urine concentrations were observed when sampled at the end of the 28-day exposure period. From a final dose of 1,000 mg/kg of the pigment that the animals received on the last day of the study, only cumulated relative amounts of << 0.001 % (m/f) were found in the terminal 24-h urine collection period.
(3) In a mass balance study with a single oral dose of 1,000 mg/kg of the pigment, 102% Pr of the dose and 74.3% Zr were excreted via faeces within 3 days, with only <0.00001% Pr and < 0.002% Zr of the dose being excreted via urine at the same time.
(4) In a bioavailability study, the absolute (0.000055% (Pr)) and relative (0.000011% (Pr)) bioavailability of orally administered pigment was calculated in relation to a soluble Pr3+compound (PrCl3), injected i.v..
Comparing the findings ofin-vitrodissolution testing (1) within-vivoresults (2-4), thein-vivodata consistently demonstrates slightly lower bioavailability. This is in agreement with the general understanding thatin-vitroexperiments in simulated gastric juice provide a conservative estimate of actual (in-vivo) bioavailability.
In conclusion, the oral relative bioavailability of the pigment "Zirconium praseodymium yellow zircon" can be assumed to be negligible, as demonstrated in three independent in-vivo studies in rats yielding very comparably results supported by anin-vitrodissolution experiment in five different artificial physiological media.
A rounded value of <<0.01% for oral absorption can be taken forward from (i) terminal urine/plasma sampling in a study involving 28 repeated oral doses of 1,000 mg pigment/kg bw/d (<<0.001% for Pr) and (ii) a mass balance study involving a single dose of 1,000 mg pigment/kg bw (0.00003% for Pr and <<0.00001% for Zr).
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
The in-vitro and in-vivo experiments described above are in very good agreement with regards to the negligible level of bioavailability of the elements Zr and Pr contained in the pigment.
(1) In in-vitro dissolution experiments in five different artificial physiological media, the highest dissolved Zr, Si and Pr concentrations were below 2.4 µg/L (24h, ALF), 62.7 µg/L (24h, ALF) and 574 µg/L (24h, GST), respectively, even at the highest loading of 0.1 g/L, referring to a solubility of 0.0024 %, 0.063 % and 0.574 %, respectively. Thus, the pigment is considered biologically inert. The dissolved Zr, Pr and Si concentrations from this pigment in GST, after 2h hours (2-hour gastric passage) were below LoD, 350 μg/L and 30 μg/L, respectively, even at the highest loading of 0.1g/L, corresponding to a solubility of less than 0.4 %.
(2) In a 28-day oral toxicity study with 1,000 mg/kg pigment no increase in Zr and Pr plasma and urine concentrations were observed when sampled at the end of the 28-day exposure period. From a final dose of 1,000 mg/kg of the pigment that the animals received on the last day of the study, only cumulated relative amounts of << 0.001 % (m/f) were found in the terminal 24-h urine collection period.
(3) In a mass balance study with a single oral dose of 1,000 mg/kg of the pigment, 102% Pr of the dose and 74.3% Zr were excreted via faeces within 3 days, with only <0.00001% Pr and < 0.002% Zr of the dose being excreted via urine at the same time.
(4) In a bioavailability study, the absolute (0.000055% (Pr)) and relative (0.000011% (Pr)) bioavailability of orally administered pigment was calculated in relation to a soluble Pr3+compound (PrCl3), injected i.v..
Comparing the findings of in-vitro dissolution testing (1) with in-vivo results (2-4), the in-vivo data consistently demonstrates slightly lower bioavailability. This is in agreement with the general understanding that in-vitro experiments in simulated gastric juice provide a conservative estimate of actual (in-vivo) bioavailability.
In conclusion, the oral relative bioavailability of the pigment "Zirconium praseodymium yellow zircon" can be assumed to be negligible, as demonstrated in three independent in-vivo studies in rats yielding very comparably results supported by an in-vitro dissolution experiment in five different artificial physiological media.
A rounded value of <<0.01% for oral absorption can be taken forward from (i) terminal urine/plasma sampling in a study involving 28 repeated oral doses of 1,000 mg pigment/kg bw/d (<<0.001% for Pr) and (ii) a mass balance study involving a single dose of 1,000 mg pigment/kg bw (0.00003% for Pr and <<0.00001% for Zr).
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