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Reaction product of acid red 143 (free acid) or the respective sodium salt (e.g Lansyn red F-5B) (UVCB) with Tetrabutylammonium bromide (CAS nr.: 1643-19-2) resulting in a mixture of AR143-(TBN)2 (Main component), AR143-(TBN), AR143-(TBN)3, AR143-(TBN) without alkyl tail, AR143-(TBN)2 without alkyl tail.Chemical name main component AR143-(TBN)2:di-(tetra-n-butylammonium) salt of 1-benzoyl-4-[4'-(1'',1''-dimethylpropyl)-phenoxy]-6-phenylamino-2,7-dioxo-2,7-dihydro-3H-naphtho(1,2,3-de)quinolin, disulfonic acid
EC number: 944-248-6 | 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 17/10/2006 - 11/12/2006
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- European Economic Community (EEC). Directive 2000/32/EC, Part B: Methods for the Determination of Toxicity; B.12: "Mutagenicity: In Vivo Mammalian Erythrocyte Micronucleus Test" (Published June 8, 2000)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- Organisation for Economic Co-operation and Development (OECD), OECD Guidelines for the Testing of Chemicals, Guideline No. 474: Mammalian Erythrocyte Micronucleus Test (adopted July 21, 1997)
- GLP compliance:
- yes
Test material
- Reference substance name:
- -
- EC Number:
- 473-100-9
- EC Name:
- -
- Test material form:
- solid: particulate/powder
- Details on test material:
- - Description: dark purple powder
- Solubility in the water: <= 0.412 g/L
- Melting point: > 250 °C
- Boiling point: > 250 °C
- Explosion: not explosion
- Log Pow: >= 3.3
- Test substance storage: at room temperature in the dark, 20°C, dry store
- Stability under storage conditions: stable
1
- Specific details on test material used for the study:
- SXjul2006 was suspended in corn oil (Roth, Karlsruhe, Germany). SXjul2006 concentrations were blended and treated with ultra-sonic waves to obtain a homogeneous suspension. SXjul2006 concentrations were dosed within 3 hours after preparation.
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Details on species / strain selection:
- These mice are recommended by internation guidelines (e.g. OECD, EEC). Females were nulliparous and non-pregnant. The animals were provided by Charles River, Sulzfeld, Germany.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- In the micronucleus main test 5 male and 5 female mice were treated per sampling time in each treatment group. Young adult animals were selected (6-8 weeks old).
The body weight of the mice at the start of the treatment were within 20% of the sex mean. The mice were identified by a unique number on the tail written with a marker pen. The animals were allocated to treatment groups as they came to hand from the delivery boxes.
On arrival and at the start of the treatment, all animals were clinically examined to ensure selected animals were in a good state of health.
Administration / exposure
- Route of administration:
- other: intraperitoneal injection
- Vehicle:
- Corn oil
- Details on exposure:
- Five male and five female animals were used in each of the six treatment groups, including negative and positive controls. All groups received a single intraperitoneal injection. The negative and positive control groups were treated with vehicle and 50 mg/kg body weight of cyclophosphamide (CP), respectively. Animals were dosed with SXjul2006 at 15 (two groups), 7.5 (one group) and 3.8 (one group) mg/kg body weight.
- Duration of treatment / exposure:
- Bone marrow of the groups treated with SXjul2006 was samples 24 or 48 (highest dose only) hours after dosing. Bone marrow of the negative and positive control groups was harvested 24 and 48 hours after dosing, respectively
- Frequency of treatment:
- All groups received a single intraperitoneal injection.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 15 other: mg/kg body weight
- Remarks:
- two groups
- Dose / conc.:
- 7.5 other: mg/kg body weight
- Remarks:
- one group
- Dose / conc.:
- 3.8 other: mg/kg body weight
- Remarks:
- one group
- No. of animals per sex per dose:
- five male and five female
- Positive control(s):
- The positive control used in the micronucleus test was cyclophosphamide (CP; CAS no. 50-18-0; Endoxan, Asta-Werke, Germany) dissolved in physiological saline (Ziekenhuis Apotheek Noordoost-Brabant, Den Bosch, The Netherlands) dosed as a single intraperitoneal injection of 50 mg/kg body weight.
Results and discussion
Applicant's summary and conclusion
- Conclusions:
- It is concluded that this test is valid and that SXjul2006 is not clastogenic in the micronucleus test under the experimental conditions described in this report.
- Executive summary:
SXjul2006 induced a statistically significant increase in the mean number of micronucleated polychromatic erythrocytes compared to the corresponding solvent control group in female animal dosed with 7.5 mg/kg b.w. Since the mean number of micronucleated polychromatic erythrocytes per 2000 polychromatic erythrocytes (1.2 +- 1.1) of this group as well as the individual number of micronucleated polychromatic erythrocytes per 2000 polychromatic erythrocytes per animal were well within the historical data range (0 -4), the increase was considered not to be biologically relevant.
No increase in the frequency of micronucleated polychromatic erythrocytes, compared to the vehicle treated animals, was observed in the polychromatic erythrocytes of the bone marrow of all other dose groups treated with SXjul2006.
The incidence of micronucleated polychromatic erythrocytes in the bone marrow of all negative control animals was within the historical solvent control data range. Cyclophosphamide, the positive control substance, induced a statistically significant increase in the number of micronucleated polychromatic erythrocytes in both sexes. Hence, both criteria for an acceptable assay were met.
The groups that were treated with 7.5 and 3.8 mg SXjul2006/kg b.w. showed no decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the vehicle controls, which reflects a lack of toxic effects of this compound on the erythropoiesis. In the group treated with 15 mg SXjul2006/kg b.w., sampled after 48 hours, a decrease in the ratio of polychromatic to normochromatic erythrocytes was observed compared to the vehicle controls. This provides evidence that SXjul2006 reaches the bone marrow and has a toxic effect on the erythropoiesis following a 48 h exposure. The animals treated with 15 mg SXjul2006/kg b.w. sampled after 24 hours did not show a decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the vehicle controls.
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