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EC number: 201-122-9 | CAS number: 78-51-3
- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study but no data on test substance purity
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 990
- Report date:
- 1990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- no data on substance purity
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Tris(2-butoxyethyl) phosphate
- EC Number:
- 201-122-9
- EC Name:
- Tris(2-butoxyethyl) phosphate
- Cas Number:
- 78-51-3
- Molecular formula:
- C18H39O7P
- IUPAC Name:
- tris(2-butoxyethyl) phosphate
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Hoechst AG: Kastengrund, SPF breeding colony
- Age at study initiation: no data
- Weight at study initiation: males 32-42 g; females 24-36 g
- Assigned to test groups randomly: yes
- Fasting period before study: no data
- Housing: no data
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 2 deg C
- Humidity (%): 55 +/- 10%
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Sesame oil
- Duration of treatment / exposure:
- Single gavage dose
- Frequency of treatment:
- once
- Post exposure period:
- 24, 48 or 72 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1800 mg/kg
Basis:
actual ingested
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide (Endoxan(R)), 50 mg/kg
Examinations
- Tissues and cell types examined:
- Bone marrow
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 2000-5000 mg/kg
- Solubility: soluble in sesame oil
- Clinical signs of toxicity in test animals: ataxic gait, abnormal/reduced movement, tonic/clonic convulsions, coma, death
- Evidence of cytotoxicity in tissue analyzed: not reported
- Rationale for exposure: standard test route
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): no increase
- Ratio of PCE/NCE (for Micronucleus assay): not affected
- Appropriateness of dose levels and route: maximum tolerated dose
- Statistical evaluation: by "Diamant" computer program v2
Any other information on results incl. tables
In the preliminary toxicity study, mortalities were:
5000 mg/kg: male 1/3; female 3/3. 3000 mg/kg: male 0/3; female 1/3. 2000 mg/kg: male 0/3; female 0/6
Significant clinical signs were reported at all dose levels. Clinical signs at 2000 mg/kg included ataxic/uncoordinated gait, forward movement in crawling posture, tonic/clonic convulsions, trembling, piloerection. The dose level determined for the main study was 1800 mg/kg.
In the main study at 1800 mg/kg, 2/30 females died. They were replaced and replacements survived after treatment.
Signs of toxicity noted were ataxic gait, reduced spontaneous activity, abdominal position, forward movement in crawling posture, piloerection, narrowed palpebral fissures, saltatory and rolling convulsions, tonic convulsions, impaired general condition.All clinical signs had resolved after 48 hours. There were no abnormal macroscopic findings on necropsy.
There was no statistically significant increase in micronucleated polychromatic erythrocytes. The number of normochromatic erythrocytes with micronuclei did not differ from the values in negative control animals at any of the three killing times investigated. The ratio of polychromatic to normochromatic erythrocytes was essentially unaffected by treatment.
Cyclophosphamide (Endoxan(R) at 50 mg/kg induced a marked and statistically sigificant increase in the number of polychromatic erythrocytes with micronuclei in both males and females..
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: negative
TBEP was not mutagenic in this test system. - Executive summary:
TBEP was tested in the micronucleus test. Following a preliminary toxicity study at dose levels of 2000 -5000 mg/kg bw, the test compound was administered once by gavage to male and female NMRI mice, at doses of 0 and 1800 mg/kg in sesame oil. The animals were observed and killed 24, 48 or 72 hours after test compound administration. endoxan(R) (cyclophosphamide) was used as a positive control at 50 mg/kg.
2/30 females died. They were replaced and replacements survived after treatment.
Signs of toxicity noted were ataxic gait, reduced spontaneous activity, abdominal position, forward movement in crawling posture, piloerection, narrowed palpebral fissures, saltatory and rolling convulsions, tonic convulsions, impaired general condition.All clinical signs had resolved after 48 hours. There were no abnormal macroscopic findings on necropsy.
There was no statistically significant increase in micronucleated polychromatic erythrocytes. The number of normochromatic erythrocytes with micronuclei did not differ from the values in negative control animals at any of the three killing times investigated. The ratio of polychromatic to normochromatic erythrocytes was essentially unaffected by treatment.
Cyclophosphamide (Endoxan(R) induced a marked and statistically sigificant increase in the number of polychromatic erythrocytes with micronuclei in both males and females.
TBEP was therefore considered not to be mutagenic in this test system.
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