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EC number: 500-057-6 | CAS number: 27104-30-9
- 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
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Between 20/03/1995 and 21/04/1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD 474 and GLP study. The clinical signs observed in main study were not detailed.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1996
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- clinical signs observed are not detailed
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- clinical signs observed are not detailed
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 1994-03-16
- Type of assay:
- micronucleus assay
Test material
- Test material form:
- other: liquid stored at room temperature
- Details on test material:
- - Substance type: liquid (pale straw-coloured)
- Analytical purity: no data
- Storage condition of test material: room temperature
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 (UK) Ltd, Manston, Kent
- Age at study initiation: 5-7 weeks
- Weight at study initiation: males: 21-28 g, females 20-24 g
- Assigned to test groups randomly: yes
- Fasting period before study: no data
- Housing: groups of up to 5 by sex.
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 21-22 C°
- humidity 47-50%
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: Sterile distilled water
- Concentration of test material in vehicle: 21.25, 42.5 and 85 mg/mL for dose levels 212.5, 425 and 850 mg test material/kg respectively
- Amount of vehicle: 10 mL/kg
- Lot/batch no.: 401034 - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: freshly prepared as required as a solution in distilled water
- Duration of treatment / exposure:
- Not applicable (following single gavage, 24 or 48-hour observation period before sacrifice)
- Frequency of treatment:
- once
- Post exposure period:
- none
Doses / concentrations
- Remarks:
- Doses / Concentrations:
212.5, 425 and 850 mg test material/kg bw , equivalent to 140.2, 280.5 and 561 mg Active Ingredient (AI)/kg bw respectively.
Basis:
nominal conc.
Animals were dosed at 212.5, 425 and 850 mg test material/ kg following range-finding toxicity study which showed 0/4 deaths at 750 and 850 mg test material/ kg bw, 1/4 deaths at 900 mg test material/kg bw and 2/4 at 1000 mg test material/kg bw.
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - Name: cyclophosphamide monohydrate
- Justification for choice of positive control(s): no data
- Route of administration: gavage
- Volume administered: 10 mL/kg b.w
Examinations
- Tissues and cell types examined:
- Both femurs were dissected out from each animal to remove the proximal epiphysis from each bone. The bone marrow of both femurs from each animal was pooled in order to obtain cell suspension (see Table 7.6.2/2).
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: preliminary toxicity test was performed to determine a suitable dose level for use in the micronucleus test; the maximum tolerated dose, i.e. the highest dosage which would be expected to elicit signs of toxicity without producing extreme clinical signs or having a significant effect on survival.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): no data
DETAILS OF SLIDE PREPARATION: dissected femurs were aspirated with foetal calf serum. Bone marrow smears were prepared following centrifugation and re-suspension. Smears were air dried, fixed in absolute methanol and stained in May-Grünwald/Giemsa.
METHOD OF ANALYSIS: The stained smears were examined by light microscopy to determine the incidence of micronucleated cells per 2000 polychromatic erythrocytes/animal.
OTHER: no data - Evaluation criteria:
- - A statistically significant dose-related increase in the frequency of micronucleated polychromatic erythrocytes for 24 or 48h kill times relative to control is indicative of a positive mutagenic response.
- A positive response for bone marrow toxicity is indicated when the polychromatic to normochromatic ratio is significantly different from the vehicle control group. - Statistics:
- All data were analysed using Student’s t-test (two tailed), and any significant results were confirmed using the one way analysis of variance. The analyses used are considered to be appropriate.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- Recorded on in preliminary study: at 900 and 1000 mg test material /kg and above : Premature deaths were seen, and the following clinical signs were observed: hunched posture, lethargy, decreased respiration rate, laboured respiration, ptosis and ataxia.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 750-1000 mg test material/kg bw
- Clinical signs of toxicity in test animals: loss of righting reflex, decreased respiratory rate, laboured respiration, ataxia, lethargy, ptosis, hunched posture, splayed gait, red-stained urine and pallor of the extremities observed at and above 900 mg test material/kg bw.
- Other: premature mortalities at 900 mg test material/kg bw and above
Conclusion: 212.5-850 mg Test material/kg bw selected for defenitive study.
RESULTS OF DEFINITIVE STUDY
- Mortality: 1 female died at 212.5 mg/kg-1 (Sample time: 24 hours) and 2 females died at 850 mg/kg-1 (sample time: 48 hours).
- Induction of micronuclei (for Micronucleus assay): there was no evidence of induction of micronuclei by the test substance See table 7.6.2/3
- Ratio of PCE/NCE (for Micronucleus assay): there was no statistically significant change in the PCE/NCE ratio in any of the test material groups when compared to their concurrent vehicle control groups, however a dose-related reduction in the PCE/NCE ratio in the 24-hour dose groups was observed , this together with the presence of clinical signs and premature deaths would indicate systemic absorption had occurred.
- Appropriateness of dose levels and route: appropriate
- Statistical evaluation: see description above
Any other information on results incl. tables
Table 7.6.2/3: Results of in vivo micronucleus test with THPC-urea
|
Control |
Low dose |
Mid dose |
High dose |
|
Number of cells evaluated |
1378 |
1282 |
1413 |
1424 |
|
Sampling time (h) |
24 h
|
||||
Number of erythro-cytes |
normochromatic |
378+/-70 |
282+/-66 |
413+/-68 |
424+/-63 |
polychromatic |
1000+/-0 |
1000 +/- 0 |
1000 +/-0 |
1000+/-0 |
|
polychromatic with micronuclei |
0.9+/-1.1 |
0.7 +/-0.7 |
1.1+/-1.21 |
1.2+/-0.9 |
|
Ratio of erythrocytes |
polychromatic / normochromatic |
1.73+/-0.53 |
2.71+/-0.86 |
1.50 +/-0.51 |
1.41+/-0.38 |
polychromatic with micronuclei / normochromatic |
0.02 +/-0.02 |
0.03 +/-0.01 |
0.03 +/-0.02 |
0.03 +/-0.01 |
|
Control |
Low dose |
Mid dose |
High dose |
|
Number of cells evaluated |
1372 |
- |
- |
1465 |
|
Sampling time (h) |
48h
|
||||
Number of erythro-cytes |
normochromatic |
372+/-0.1 |
- |
- |
465+/-128 |
polychromatic |
1000+/-1.1 |
- |
- |
1000+/-0 |
|
polychromatic with micronuclei |
1.1+/-1.2 |
- |
- |
0.9+/-1.1 |
|
Ratio of erythrocytes |
polychromatic / normochromatic |
1.78+/-0.57 |
- |
- |
1.31+/-0.66 |
polychromatic with micronuclei / normochromatic |
0.03 +/-12 |
|
|
0.02 +/-0.09 |
- Number of PCE with Micronuclei per 1000 PCE (positive control 24 -hour sampling time): 31.4*** +/- 12.2
- PCE/NCE Ratio (positive control 24 -hour sampling time): 1.79 +/- 0.78
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the test conditions, Tetrakis (hydroxy methyl) phosphonium chloride, oligomeric reaction products with urea (THPC-urea) was considered to be non-genotoxic - Executive summary:
Bone marrow micronucleus assay was conducted in CD-1 mouse according to OECD guidelines 474 (SPL, 1996) and in compliance with GLP. Animals (5/sex/dose) were treated by gavage with test substance identified as Tetrakis (hydroxy methyl) phosphonium chloride, oligomeric reaction products with urea (THPC-urea) at doses of 140, 280 and 561 mg AI/kg b.w. Bone marrow cells were harvested at 24 hours post-treatment for all doses tested groups and at 48 hours for the highest dose group. The water was used as concurrent vehicle negative control. A group of 5 males and 5 females were treated by gavage with cyclophosphamide as concurrent positive control.
There was no statistically significant change in the PCE/NCE ratio in any of the test material dose groups when compared to their concurrent vehicle control groups, however, a dose-related reduction was observed in the 24 -hour groups, this together with the presence of clinical signs and premature deaths would indicate systemic absorption had occured. Test substance was tested at adequate doses based on a preliminary assay at 495, 591, 594 and 660 mg AI/kg. The positive control induced the appropriate response. There was not a significant increase in the frequency of micronucleated polychromatic erythrocytes in bone marrow after any treatment time.
This study is classified as acceptable and satisfies the requirement for Test Guideline OECD 474 for in vivo cytogenetic mutagenicity data.
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