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EC number: 412-550-2 | CAS number: 85776-14-3 GRAPHTOL ORANGE 3RT; PERMANENT ORANGE 2 RLD; PERMANENT ORANGE 3 RTN
- 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
Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- - Rationale for reliability of the study report related to the source substance: Guideline study (OECD 476), GLP compliant (original reliability: 1) - Read across hypothesis: The similar chemical structure and the uniformity of physicochemical, environmental fate and toxicological properties justifies the application of read across to predict the outcome of a Developmental/Reproduction Screening Test and an In Vitro Mammalian Cell Gene Mutation Test (HPRT) of the target pigment based on available date coming from several source pigments.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- mammalian cell gene mutation assay
Test material
Constituent 1
Method
- Target gene:
- hypoxanthine-guanine phosphoribosyl transferase (HPRT)
Species / strain
- Species / strain / cell type:
- Chinese hamster lung fibroblasts (V79)
- Details on mammalian cell type (if applicable):
- - Type and identity of media: minimum essential medium containing 10% fetal calf serum
- Properly maintained: yes
- Periodically checked for Mycoplasma contamination: yes
- Periodically checked for karyotype stability: yes
- Periodically "cleansed" against high spontaneous background: yes
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9-mix (phenobarbital/beta-naphthoflavone-induced rat liver protein with cofactors)
- Test concentrations with justification for top dose:
- 3.1, 6.3, 12.5, 25.0, 50.0 and 400 μg/ml with and without metabolic activation
- Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: DMSO
Controls
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- ethylmethanesulphonate
- Remarks:
- Migrated to IUCLID6: w/o metabolic activation; 7,12-Dimethylbenz(a)anthracene with metabolic activation
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in medium (4h-incubation without serum, 24 h incubations with serum)
DURATION
- Preincubation period: none
- Exposure duration: 4 and 24 h
- Expression time (cells in growth medium): 7 days
- Selection time (if incubation with a selection agent): 8 days
- Fixation time (start of exposure up to fixation or harvest of cells):
SELECTION AGENT (mutation assays): 6-thioguanine
STAIN (for cytogenetic assays): 10% methylene blue in 0.01% KOH solution
NUMBER OF REPLICATIONS: 5/experiment, 2 experiments
NUMBER OF CELLS EVALUATED: colonies >50 cells
DETERMINATION OF CYTOTOXICITY
- Method: cloning efficiency - Evaluation criteria:
- test item classified as positive for mutagenicity if induces either concentration-related increase of mutant frequency or reproducible and positive response at one of the test points (at least three times above the spontaneous mutation frequency)
- Statistics:
- linear regerssion on dose-dependeny of mutant frequencies using SYSTAT statistics software
Results and discussion
Test results
- Species / strain:
- Chinese hamster lung fibroblasts (V79)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Remarks:
- precipitation was observed at 12.5 µg/ml and higher (Exp. I without S9-mix), at 25.0 µg/ml and higher (Exp. I with S9-mix and Exp. II)
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH: negligible decrease (0.1 pH-units) at highest dose
- Effects of osmolality: negligible increase (+3 mOsm) at highest dose - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Results of V79/HPRT assay with test item
Concentration [microgram/mL] |
mutant colonies per 10^-6 cells** |
mutant colonies per 10^6 cells** |
Cytotoxicity |
Remarks |
|
— MA |
+ MA |
|
|
0* |
7.6, 6.2 |
5.2, 21.2 |
no |
Exp. I |
3.1 |
13.6, 8.5 |
11.7, 13.4 |
no |
|
6.3 |
7.8, 14.7 |
8.6, 26.8 |
no |
|
12.5 |
12.3, 8.6 |
13.4, 19.5 |
no |
|
25.0 |
12.3, 10.9 |
7.4, 22.3 |
no |
|
400 |
15.9, 10.6 |
13.1, 12.5 |
no |
|
Positive control*** |
151.7, 87.5 |
1239.9, 1528.8 |
-MA: no; +MA: yes |
|
0* |
13.9, 11.3 |
- |
no |
Exp. II |
3.1 |
11.4, 6.1 |
- |
no |
|
6.3 |
12.2, 7.7 |
- |
no |
|
12.5 |
17.1, 12.9 |
- |
no |
|
25.0 |
11.0, 9.6 |
- |
no |
|
400 |
5.5, 7.7 |
- |
no |
|
Positive control*** |
186.6,. 136.9 |
- |
yes |
|
*solvent control with DMSO
** mean of 5 plates each in culture I and culture II
***without MA: EMS, with MA: DMBA
Read across justification
The purpose of this assessment is to provide justification for read across in order to predict the potential genetic and reproductive toxicity of the target substance Pigment Orange 74 based on available date coming from a set of source substances (Pigment Red 22, 112, 146, 147, 179).
The pigments used for read across are structurally similar and differ only by different substituents in the common core molecule. Target and source substances are solids which decompose or melt at high temperatures (>= 237°C). Solubility in water or n-octanol is very low or low (< 12 μg/L and < 3.4 mg/L, respectively). For the target substance solubility in water was determined to be below the limit of detection (<0.1 mg/L) and in n-octanol 0.16 mg/L. These values suggest poor absorption and low bioavailability for all pigments involved in this evaluation. The log n-octanol-water partition coefficients are in the range of 1.28 to 2.5 for all of the source pigments which fit together with log n-octanol-water partition coefficient of Pigment Orange 74 (>0.2). These values are far below the limit of concern considered to be critical for bio-accumulative properties. All pigments showed very limited biodegradability, which is assumed to be due to their unavailability for microorganisms. Lacking bioavailability is probably also the reason for the absence of any relevant mammalian toxicity: None of the source pigments showed any toxic effects after single oral or dermal or after repeated oral exposure including effects on reproductive performance (examined for Pigment Red 22 and 170). This pertains also for the target substance with the exception of one death in association with lung coloration observed after single oral application (2000 mg/kg bw) which might be attributed to incorrect dosing or inhaling of foamed vomit. A spontaneous not treatment related death cannot be ruled out as well. This seems not unlikely in view of the fact that no such effects were observed in an oral repeated dose study. Target and source pigments have no skin sensitising effects. All pigments are not mutagenic in the Bacterial Reverse Mutation Assay or the Mammalian Chromosomal Aberration Test. Negative results were also obtained for the source substances in the In vitro Mammalian Cell Gene Mutation Test (HPRT).
Due to the very low solubility of the pigments it can reasonably be assumed that the members of this read across approach are (nearly) not present in a dissolved form on the skin or mucous membranes after dermal, oral or inhalative exposure, i.e. they could not be absorbed via skin and mucous membranes. This conclusion is supported by the observation that the pigments evaluated do not exert any relevant toxicity.
This assessment is based on experimental data on the source pigments as compared to available data of the target pigment covering the following endpoints: Acute oral or dermal toxicity, skin and eye irritation, skin sensitisation, genotoxicity in vitro, subacute oral toxicity, toxicity to reproduction, and inherent biodegradability (for details see data matrix).
In conclusion, the uniformity of physicochemical, environmental fate and toxicological properties justifies the application of read across to predict the outcome of a Developmental/Reproduction Screening Test and an In Vitro Mammalian Cell Gene Mutation Test (HPRT) of the target pigment based on available date coming from several source pigments. The minor differences in the structure do not significantly alter the basic physicochemical properties or the basic biological effects.
Data Matrix
CHEMICAL NAME |
Pigment Orange 74 |
Pigment Red 22 |
Pigment Red 112 |
Pigment Red 146 |
Pigment Red 147 |
Pigment Red 170 |
Role |
Target Substance |
Source Substance |
Source Substance |
Source Substance |
Source Substance |
Source Substance |
CAS No. |
85776-14-3 |
6448-95-9 |
6535-46-2 |
5280-68-2 |
68227-78-1 |
2786-76-7 |
PHYSICAL AND CHEMICAL PROPERTIES |
||||||
State of the substance at 20° C and 101,3 kPa |
orange solid |
red solid |
red solid |
red solid |
red solid |
red solid |
Melting/freezing point |
>= 278.2°C, |
decomp. starting at 237°C, 534 J/g |
decomp. starting at 270°C, 300 J/g |
decomp. starting at 283°C, 418 J/g |
decomp. starting at 278°C, 92 J/g |
decomp. starting at 313°C, 80 J/g |
Water solubility |
< 0.1 mg/L (below the detection limit) |
11.8 μg/L |
9.80 μg/L |
8.7 μg/L |
10 μg/L |
11.9 μg/L |
n-Octanol solubility |
0.16 mg/L
0.192 |
1.80 mg/L |
3.31 mg/L |
0.100 mg/L |
0.74 mg/l |
0.225 mg/L |
log Partition coefficientn-octanol/water |
> 0.2 (exact value could not be determined because water solubility was below the detection limit) |
2.18 |
2.5 |
1.87 |
1.87 |
1.28 |
Stability in organic solvents and identity of relevant degradation products |
>72 h in DMSO and 1,2-propylene glycol |
>72h in DMSO and 1,2-propylene glycol |
>72h in DMSO and sesame oil |
>72h in DMSO and 1,2-propylene glycol |
>72h in DMSO and 1,2-propylene glycol |
>72h in DMSO and 1,2-propylene glycol |
TOXICOLOGICAL INFORMATION |
||||||
Skin irritation |
not irritating |
not irritating |
not irritating |
not irritating |
not irritating |
not irritating |
Eye irritation |
not irritating |
not irritating (read across) b |
not irritating |
not irritating |
not irritating |
not irritating |
Skin sensitization |
not skin sensitising |
not skin sensitising (read across) |
not skin sensitising |
not skin sensitising |
not skin sensitising |
not skin sensitising |
In vitrogene mutation study in bacteria |
not mutagenic |
not mutagenic |
not mutagenic |
not mutagenic |
not mutagenic |
not mutagenic |
In vitrocytogenicity study in mammalian cells |
not mutagenic (CA in V79 cells) |
not mutagenic (CA in V79 cells) |
not mutagenic (MN in V79 cells) |
not mutagenic (CA in V79 cells) |
not mutagenic (CA in V79 cells) |
not mutagenic (CA in V79 cells) |
In vitrogene mutation study in mammalian cells |
RA-conclusion: not mutagenic (HPRT in V79 cells) |
not mutagenic (read across) |
Applied Source Substance: not mutagenic (HPRT in V79 cells) |
Applied Source Substance: not mutagenic (HPRT in V79 cells) |
Applied Source Substance: not mutagenic (HPRT in V79 cells) |
Applied Source Substance: not mutagenic (HPRT in V79 cells) |
Otherin vivomutagenicity tests |
No data requirement |
not mutagenic (read across) |
not mutagenic (read across) |
not mutagenic (read across) |
not mutagenic (UDS in vivo) |
not mutagenic (read across) |
Acute toxicity, oral route, (LD50 mg/kg b.w., rats) |
> 2000 |
> 2000 |
> 5000 |
> 10000 |
> 2000 |
> 15000 |
Acute tocity, inhalation (LC50 mg/L, rats ) |
Waiving (according to REACH Annex VIII, no.8.5, column 2; data for 2 application routes of acute toxicity available) |
Waiving (according to REACH Annex VIII, no.8.5, column 2; data for 2 application routes of acute toxicity available) |
Waiving (according to REACH Annex VIII, no.8.5, column 2; data for 2 application routes of acute toxicity available) |
Waiving (according to REACH Annex VIII, no.8.5, column 2; data for 2 application routes of acute toxicity available) |
Waiving (according to REACH Annex VIII, no.8.5, column 2; data for 2 application routes of acute toxicity available) |
Waiving (according to REACH Annex VIII, no.8.5, column 2; data for 2 application routes of acute toxicity available) (>1580 mg/m3/4h; RL3) |
Acute toxicity dermal route (LD50 mg/kg b.w., rat) |
> 2000 |
> 2000 |
> 5000 |
> 2000 |
> 2000 |
> 2000 |
Short-term repeated dose toxicity study in rats (oral) |
NOAEL 1000 mg/kg bw (highest dose tested; OECD 407) |
NOAEL 1000 mg/kg bw (highest dose tested; OECD 422) |
NOAEL 1000 mg/kg bw (highest dose tested; OECD 407) |
NOAEL 1000 mg/kg bw (highest dose tested; OECD 407) |
NOAEL 1000 mg/kg/day (read across) |
NOAEL ca. 1200 mg/kg bw (highest dose tested; OECD 407) |
Sub-chronic toxicity study in rats (oral) |
waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and short-term repeated dose studiesàpredicted not to be toxic after long-term repeated exposure) |
waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and short-term repeated dose studiesàpredicted not to be toxic after long-term repeated exposure) |
waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and short-term repeated dose studiesàpredicted not to be toxic after long-term repeated exposure) |
waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and short-term repeated dose studiesàpredicted not to be toxic after long-term repeated exposure) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and short -term repeated dose studiesàpredicted not to be toxic after long-term repeated exposure) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and short-term repeated dose studiesàpredicted not to be toxic after long-term repeated exposure) |
Carcinogenicity |
No data requirement |
No data requirement |
No data requirement |
No data requirement |
No data requirement |
No data requirement |
Screening for reproduction/developmental toxicity, rats |
RA-conclusion: NOAEL 1000 mg/kg bw |
Applied Source Substance: NOAEL 1000 mg/kg bw (highest dose tested; OECD 422) |
NOAEL 1000 mg/kg/day |
NOAEL 1000mg/kg/day |
NOAEL 1000 mg/kg/day |
Applied Source Substance: NOAEL 1000 mg/kg bw (highest dose tested; OECD 421) |
Reproductive Toxicity – Fertility |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be toxic to reproduction) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be toxic to reproduction) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be toxic to reproduction) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be toxic to reproduction) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be toxic to reproduction) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be toxic to reproduction) |
Reproductive Toxicity – Developmental Toxicity |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be developmental toxic) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be developmental toxic) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be developmental toxic) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be developmental toxic) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be developmental toxic) |
Waiving (Annex XI: scientifically unjustified, because substances are not bioavailable and show no toxic effects in acute and repeated dose and reproduction / developmental screening studiesàpredicted not to be developmental toxic) |
Toxicokinetic behaviour |
Available data point to inert behavior and non-bioavailability |
Available data point to inert behavior and non-bioavailability |
Available data point to inert behavior and non-bioavailability |
Available data point to inert behavior and non-bioavailability |
Available data point to inert behavior and non-bioavailability |
Available data point to inert behavior and non-bioavailability |
ENVIRONMENTAL FATE |
||||||
Inherent biodegradability |
Not readily biodegradable |
Not inherently biodegradable (read across) |
Not inherently biodegradable (read across) |
Not inherently biodegradable (read across) |
Not inherently biodegradable (read across) |
Not inherently biodegradable (read across) |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative with and without metabolic activation
The test item was not genotoxic in the mammalian cell gene (HPRT) mutation test in V79 Chinese Hamster cells when tested with and without rat liver S9 metabolic activation at concentrations up to 400 µg/mL. - Executive summary:
The study was performed to investigate the potential of the test item to induce gene mutations at the HPRT locus in V79 cells of the Chinese hamster.
The assay was performed in two independent experiments using duplicate cultures. The cells were exposed to the test item for 4 hours in the first experiment with and without metabolic activation. The second experiment was solely performed in the absence of metabolic activation with a treatment period of 24 h.
The highest applied concentration (400 µg/mL) was limited by the solubility properties of the test item in DMSO and aqueous media.
No substantial and reproducible dose dependent increase of the mutation frequency was observed in both main experiments.
Appropriate reference mutagens were used as positive controls and showed a distinct increase in induced mutant colonies confirming the sensitivity of the test system and the activity of the S9 mix.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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