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Diss Factsheets
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EC number: 279-131-2 | CAS number: 79295-99-1
- 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
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Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed (positive)
Genetic toxicity in vivo
Description of key information
CA: Not mutagenic
UDS: Not mutagenic
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
No studies on "genetic toxicity" are available for the substance in itself. Nevertheless a study has been conducted with a analogue molecules (Similar Substance 01 and 05). Further information are reported in the Read Across justification attached to section 13.
In vitro Genetic Toxicity
An Ames test is on going and is expected to be negative.
In vivo Genetic Toxicity
In the first in vivo study the substance (Similar Substance 05) was tested for the ability to induce unscheduled DNA synthesis (UDS) in an in vivo rat hepatocyte assay. Male Fischer 344 rats were treated with a single oral doseby gavage at 1250, or 2000 mg/kg body weight. The highest test dose, 2000 mg/kg was the limit test dose for a non-toxic test agent in this assay. Animals were killed and hepatocytes prepared four hours and twelve hours following administration of the chemical. Two independent experiments were carried out for each time point.
Hepatocytes from treated rats were exposed to [³H]-thymidine and the amount of radioactivity incorporated into the nucleus [N] and an equal area of cytoplasm [C] determined by autoradiography. The cytoplasmic grain count was subtracted from that of the nucleus. The value obtained, the mean net nuclear grain count [N-C], is an index of UDS activity. In the respective testing laboratory, no negative control animal has shown a mean net nuclear grain count greater than zero. An [N-C] of more than zero in a treated animal is therefore considered indicative of a UDS response.
Each experiment was validated by concurrent control treatments of rats with corn oil, the solvent for the test substance and with the carcinogens 2-acetylaminofluorene [2AAF] at twelve hours and N-nitrosodimethylamine [NDMA] or 6-p-dimethylaminophenylazobenzthiazole [6BT] at four hours. Solvent treated rats gave rise to mean net grain counts of less than zero, whilst hepatocytes from 2AAF, 6BT or NDMA treated animals had mean net nuclear grain counts of greater than +5. These data showed that background levels of UDS were normal and that the tester animals were responsive to known carcinogens requiring metabolic activation for genotoxic activity.
Hepatocytes from treated animals were assessed for UDS at two dose levels of 1250 and 2000 mg/kg body weight. Treatments with the test substance in no case resulted in a mean net grain count greater than zero, at either time point.
It is concluded that, when tested up
to a limit dose of 2000 mg/kg body weight, the test sample did not
induce DNA repair (as measured by unscheduled DNA Synthesis) in
hepatocytes from rats treated in vivo.In a second in vivo study,
carried out on Similar Substance 01, the test item was tested for its
genetic toxicity effects according to OECD Guideline 474, in male and
female Sprague Dawley Rats. The test substance was suspended in Tylose
H4000 G4 PHA 0.5% and was given twice at an interval of 24 hours as an
oral dose of 2000 mg per kg body weight. At study start the animals were
6 weeks of age and had mean body weights of 181.2 g (M) and 142.5 g (F).
According to the test procedure the animals were killed 24 hours after
the last administration
Cyclophosphamide
was used as positive control substance and was administered once orally
at a dose of 40 mg per kg body weight.
The
number of polychromatic erythrocytes containing micronuclei was not
increased compared with the control. The ratio of polychromatic
erythrocytes to total erythrocytes in both male and female animals
remained unaffected by the treatment with the test substance and
differed less than 20 % from the control value.
Cyclophosphamide
induced a marked statistically significant increase in the number of
polychromatic cells with micronuclei, indicating the sensitivity of the
test system. The ratio of polychromatic erythrocytes to total
erythrocytes was not changed to a significant extent.
Under
the conditions of the present study the results indicate that the test
substance is not clastogenic in the micronucleus test in vivo.
Justification for classification or non-classification
GERM CELL MUTAGENICITY
This hazard class is primarily concerned with substances that may cause mutations in the germ cells of humans that can be transmitted to the progeny. However, the results from mutagenicity or genotoxicity tests in vitro and in mammalian somatic and germ cells in vivo are also considered in classifying substances and mixtures within this hazard class.
Category 1: Substances known to induce heritable mutations or to be regarded as if they induce heritable mutations in the germ cells of humans. Substances known to induce heritable mutations in the germ cells of humans.
Categoty 2: Substances which cause concern for humans owing to the possibility that they may induce heritable mutations in the germ cells of humans.
The classification in Category 2 is based on:
— positive evidence obtained from experiments in mammals and/or in some cases from in vitro experiments, obtained from:
— somatic cell mutagenicity tests in vivo, in mammals; or
— other in vivo somatic cell genotoxicity tests which are supported by positive results from in vitro mutagenicity assays.
Note: Substances which are positive in in vitro mammalian mutagenicity assays, and which also show chemical structure activity relationship to known germ cell mutagens, shall be considered for classification as Category 2 mutagens.
Classification for heritable effects in human germ cells is made on the basis of well conducted, sufficiently validated tests as:
- In vivo somatic cell mutagenicicty tests such as these indicated in paragraph 3.5.2.3.5:
— mammalian bone marrow chromosome aberration test;
— mouse spot test;
— mammalian erythrocyte micronucleus test.
- In vitro mutagenicity tests such as these indicated in 3.5.2.3.8:
— in vitro mammalian chromosome aberration test;
— in vitro mammalian cell gene mutation test;
— bacterial reverse mutation tests.
The test substance is Not Classified for Mutagenic Toxicity.
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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