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EC number: 436-230-7 | CAS number: 359406-89-6
- 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
Some information in this page has been claimed confidential.
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Read-across from supporting substance. Guideline study to GLP.
Cross-reference
- Reason / purpose for cross-reference:
- read-across: supporting information
Reference
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Sex:
- female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- Doses producing toxicity Females - 320 mg/kg
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- at 200 mg/kg splayed gait and signs of urinary incontinence were observed
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 996
- Report date:
- 1996
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Details on test material:
- - Name of test material (as cited in study report): ITC 826 Concentrate
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Margate, UK
- Age at study initiation: Phase I: 4-13 weeks; Phase II: 9-10 weeks
- Weight at study initiation: not available
- Fasting period before study: not available
- Housing: 5 per cage
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 6 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-23
- Humidity (%): 40-70
- Air changes (per hr): at least 15
- Photoperiod (hrs dark / hrs light): 12:12
Administration / exposure
- Route of administration:
- oral: unspecified
- Vehicle:
- Sterilised deionised water.
- Duration of treatment / exposure:
- Single exposure
- Frequency of treatment:
- Once
- Post exposure period:
- 24 and 48 hours
- No. of animals per sex per dose:
- Male: 200 mg/kg; No. of animals: 5; Sacrifice time: 24 hours
Male: 200 mg/kg; No. of animals: 5; Sacrifice time: 48 hours
Female: 320 mg/kg; No. of animals: 5; Sacrifice times: 24 hours
Female: 320 mg/kg; No. of animals: 5; Sacrifice times: 48 hours - Positive control(s):
- Cyclophosphamide
- Justification for choice of positive control(s): Standard positive control substance
- Route of administration: oral
- Doses / concentrations: 65 mg/kg
Examinations
- Tissues and cell types examined:
- Bone marrow erythrocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: MTD in preliminary (Phase I) test
TREATMENT AND SAMPLING TIMES : examination of bone marrow from femur at 24 and 48 hours post dosing
DETAILS OF SLIDE PREPARATION: four smears of marrow per slide. Slides were allowed to air dry and stained with polychrome methylene blue and eosin using an automatic staining machine
METHOD OF ANALYSIS:
Slides were coded and scored blind. for each animal, 2 x 1000 polychromatic erythrocytes were examined for the presence of micronuclei. Extended analysis of a further 2000 polychromatic erythrocytes was conducted for female vehicle control and female treated mice at the 24 hour sampling time.
OTHER:
Slides were examined for evidence of cytotoxicity (alterations in ratio of polychromatic to normochromatic erythrocytes in a sample of 1000 erythrocytes). - Evaluation criteria:
- As described by Schmid (1976).
- Statistics:
- Analysis of variance at 24 and 48 hours, separately for males and females.
Results and discussion
Test resultsopen allclose all
- Key result
- Sex:
- female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- Doses producing toxicity: Females - 320mg/kg. In females at 320 mg/kg hunched posture was observed.
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- at 200 mg/kg splayed gait and signs of urinary incontinence were observed
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Observations:
No biologically significant increases in micronucleus
formation were seen in any animals at any timepoint.
Any other information on results incl. tables
Phase I: Determination of MTD
Group |
Test substance |
Dose (mg/kg) |
Sex |
No. deaths/No. dosed |
1 |
ITC 826 Concentrate |
500 |
Male |
0/2 |
2 |
ITC 826 Concentrate |
800 |
Male |
2/2 |
3 |
ITC 826 Concentrate |
500 |
Male Female |
1/2 2/5 |
4 |
ITC 826 Concentrate |
320 |
Male Female |
3/5 0/5 |
5 |
ITC 826 Concentrate |
200 |
Male |
0/5 |
Phase II: Incidence of micronucleated PEs:
Males:
Group |
Treatment |
Dose |
Mean incidence of MPE/1000 PE +/- SD |
|
24 hours |
48 hours |
|||
11 |
Vehicle control |
20 ml/kg |
1.0 +/- 0.9 |
1.5 +/- 0.9 |
12 |
Cyclophosphamide |
65 mg/kg |
16.3 +/- 5.7 ** |
|
13 |
ITC 826 Concentrate |
200 mg/kg |
0.8 +/- 0.5 |
0.8 +/- 0.3 |
PE: polychromatic erythrocytes
MPE:micronucleated polychromatic erythrocytes
SD: standard deviation
** statistically significant increase p<0.01
Females (original count):
Group |
Treatment |
Dose |
Mean incidence of MPE/1000 PE +/- SD |
|
24 hours |
48 hours |
|||
11 |
Vehicle control |
20 ml/kg |
0.2 +/- 0.5 |
1.1 +/- 0.7 |
12 |
Cyclophosphamide |
65 mg/kg |
15.9 +/- 8.0 ** |
|
14 |
ITC 826 Concentrate |
320 mg/kg |
1.6 +/- 0.7* |
0.9 +/- 0.2 |
PE: polychromatic erythrocytes
MPE:micronucleated polychromatic erythrocytes
SD: standard deviation
** statistically significant increase p<0.01
* statistically significant increase p<0.05
A statistically significant increase in micronuclei in
high dose females at 24 hours was considered to be due to
low control values and was therefore considered not to be of
toxicological significance. An extended count of a further
2000 polychromatic erythrocytes conducted at the 24 hour
timepoint in females did not show any
increase in the incidence of micronucleated polychromatic erythrocytes.
Females (additional count)
Group |
Treatment |
Dose |
Mean incidence of MPE/1000 PE +/- SD |
|
24 hours |
48 hours |
|||
11 |
Vehicle control |
20 ml/kg |
0.8 +/- 0.8 |
|
14 |
ITC 826 Concentrate |
320 mg/kg |
0.7 +/- 0.5 |
|
Combined original and additional counts
Group |
Treatment |
Dose |
Mean incidence of MPE/1000 PE +/- SD |
|
24 hours |
48 hours |
|||
11 |
Vehicle control |
20 ml/kg |
0.5 +/- 0.5 |
|
14 |
ITC 826 Concentrate |
320 mg/kg |
1.2 +/- 0.3* |
|
All means based on 20 observations (4 counts of 1000 PE per animal)
There was no change in polychromatic/normochromatic ratio.
Percentage of polychromatic erythrocytes:
Males:
Group |
Treatment |
Dose |
Mean percentage of PE +/- SD |
|
24 hours |
48 hours |
|||
11 |
Vehicle control |
20 ml/kg |
44.1 +/- 3.6 |
45.6 +/- 4.2 |
12 |
Cyclophosphamide |
65 mg/kg |
41.1 +/- 3.2 |
|
13 |
ITC 826 Concentrate |
320 mg/kg |
44.8 +/- 3.5 |
45.3 +/- 2.3 |
PE: polychromatic erythrocytes
SD: standard deviation
Females:
Group |
Treatment |
Dose |
Mean percentage of PE +/- SD |
|
24 hours |
48 hours |
|||
11 |
Vehicle control |
20 ml/kg |
35.9 +/- 9.1 |
36.0 +/- 4.7 |
12 |
Cyclophosphamide |
65 mg/kg |
31.5 +/- 13.2 |
|
14 |
ITC 826 Concentrate |
320 mg/kg |
37.3 +/- 5.1 |
37.9 +/- 5.5 |
PE: polychromatic erythrocytes
SD: standard deviation
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the conditions of the test, ITC 826 Concentrate is not clastogenic in the mouse bone marrow micronucleus test. - Executive summary:
ITC 826 Concentrate was evaluated for its ability to induce micronucleated polychromatic erythrocytes in the bone marrow of CD-1 mice. A single oral dose was given to groups of 5 male mice at a dose level of 200 mg/kg and to groups of 5 female mice at a dose level of 320 mg/kg. In each case the dose level used represented the maximum tolerated dose (MTD) based on patterns of clinical signs and lethalities over a four day observation period . Bone marrow samples were taken 24 and 48 hours after dosing.
No statistically or biologically significant increases in the incidence of micronucleated polychromatic erythrocytes, over the control values, were seen in males at the 24 hour sampling time or in either males or females at the 48 hour sampling time. Although a small but statistically significant increase in the incidence of micronucleated polychromatic erythrocytes, compared to the vehicle control, was observed at the 24 hour sampling time in females dosed with ITC Concentrate at 320 mg/kg, this was not reproduced in an extended analysis of a further 2000 polychromatic erythrocytes and is therefore considered of no biological significance.
Comparison of the percentage of polychromatic erythrocytes showed no statistically or biologically significant differences in either sex at either of the sampling times between the vehicle control animals and those treated with ITC 826 Concentrate.
The test system positive control, cyclophosphamide, induced statistically significant and biologically meaningful increase in the incidence of micronucleated polychromatic erythrocytes, compared to the vehicle control values, thus demonstrating the sensitivity of the test system to a known clastogen.
Under the conditions of the test, ITC 826 Concentrate is not clastogenic in the mouse bone marrow micronucleus test.
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