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EC number: 235-826-2 | CAS number: 12788-93-1
- 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
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:
- weight of evidence
- Study period:
- Mar - Aug 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline conform GLP study.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 999
- Report date:
- 1999
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Dibutyl hydrogen phosphate
- EC Number:
- 203-509-8
- EC Name:
- Dibutyl hydrogen phosphate
- Cas Number:
- 107-66-4
- Molecular formula:
- C8H19O4P
- IUPAC Name:
- Phosphoric acid dibutyl ester
- Test material form:
- other: liquid
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: harlan Winkelmann GmbH, Borchen, Germany
- Age at study initiation: 7 weeks
- Weight at study initiation: males - 33.3 g, females - 27.5 g
- Assigned to test groups randomly: yes
- Housing: in makrolon cages type 3 (5 per cage) on softwood granulate
- Diet (e.g. ad libitum): rat/mice diet ssniff R/M-H (V 1534), ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 3°C
- Humidity (%): 50 +/- 20%
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 18.5. To: 22.6.1999
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: deionized water
- Concentration of test material in vehicle: 1%, 3% or 10%
- Amount of vehicle (if gavage or dermal): 10 mL/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
On days of administration the test substance was emulsified in deionized water at the appropriate concentrations. A magentic stirrer was used to keep the preparations homogeneous until dosing had been completed. - Duration of treatment / exposure:
- twice at an interval of 24 h
- Frequency of treatment:
- twice
- Post exposure period:
- 24 h after dosing
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
100 mg/kg bw
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
300 mg/kg bw
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
1000 mg/kg bw
Basis:
actual ingested
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- 50 mg/kg bw Endoxan containing Cyclophosphamide
Examinations
- Tissues and cell types examined:
- erythrocytes from femor bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
In a preliminary dose range findingstudy, oral administration of 1200 kg/kg bw and higher doses caused strong clinical signs of toxicity and resulted in mortality in male and female mice. Oral administration of 1000 mg/kg bw resulted in mortality in one male mouse.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
The test substance was administered twice at an interval of 24 h orally by gavage to the test animals at doses of 100, 300 and 1000 mg/kg bw. The vehicle and positive control was administered in the same way.
Following dosing, the animals were examined regularly for mortality and clinical signs of toxicity.
DETAILS OF SLIDE PREPARATION:
For each animal, about 3 mL fetal bovine serum was poured into a centrifuge tube. Both femora were removed and the bones freed of muscle tissue. The proximal ends of the femora were opened and the bone marrow flushed into the centrifuge tube. A suspension was formed. The mixture was then centrifuged for 5 min. at approx. 1200 rpm, after which almost all the supernatant was discarded. One drop of the thoroughly mixed sediment was smeared onto a cleaned slide, identified by project code and animal number and air-dried for about 12 h. The cells were stained with Giemsa. - Evaluation criteria:
- 2000 polychromatic erythrocytes were counted for each animal. The number of cells with micronuclei was recorded, not the number of individual micronuclei. In addition, the ratio of polychromatic erythrocytes to 200 total erythrcytes was determined. Main parameter for the statistical analysis, i.e. validity assessment of the study and mutagenicity of the test substance was the proportion of polychromatic erythrocytey with micronuclei out of the 2000 counted erythrocytes. All bone marrow smears for evaluation were coded to ensure that the group from which they were taken remained unknown to the investigator.
Criteria for a positive response:
Both biological and statstical significances were considered together for evaluation puproses.
A substance is considered as positive if there is a significant dose-related increase in the number of micronucleated polychromatic erythrocytes compared with the concurrent negative control group. A test substance producing no significant dose-related increase in the number of micronucleated polychromatic erythrocytes is considered non-mutagenic in this system. - Statistics:
- A one-sided Wilcoxon-Test was evaluated to check the validity of the study. The study was considered as valid in case the proportion of polychromatic reythrocytes with micronclei in the positive control was significantly higher than in the negative control (p = 0.05).
If the validity of the study had been shown the following sequential test procedure for the examination of the mutagenicity was applied: Based on a monotone-dose-relationshi one-sided Wilcoxon tests were performed starting with the highest dose group. These tests were performed with a multiple level of significance of 5%.
Results and discussion
Test resultsopen allclose all
- Sex:
- female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- at 1000 mg/kg bw
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Oral administration of 1000 mg/kg bw resulted in the death of 2 female out of 5 animals treated. These animals wer replaced and survived after treatment. The following clinical sign was observed: motor activity decreased.
The dissection of the 2 female animlas which died within 24 h after the first application revealed the following macroscopic finding: intestinal tract filled with orange colored spume. The dissection of all other animals revealed no test substance related macroscopic findings.
The inicidence of micronucleated polychromatic erythrocytes in the dose groups of Phosphoric acid, butyl ester was within the normal range of the negative control group. No statisitcally significant increase of micronucleated polychromatic erythrocytes was observed. The ratio of polychromatic erythrocytes to total erythrocytes remained essentailly unaffected by the test compound and was not less than 20% of the control values.
Cyclophosphamide induced a marked and statistically significant increae in the number of polychromatic erythrocytes with micronuclei, thus indicating the sensitivty of the test system.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The results lead to the conclusion that Phosphoric acid, butyl ester did not cause a substantial increase of microncleated polychromatic erythrocytes and is not mutagenic in the micronucleus test under the conditions described. - Executive summary:
The test substance was administered twice at an interval of 24 h orally by gavage to the test animals at doses of 100, 300 and 1000 mg/kg bw. The vehicle and positive control was administered in the same way. Following dosing, the animals were examined regularly for mortality and clinical signs of toxicity.
The number of polychromatic erythrocytes was examined.
Oral administration of 1000 mg/kg bw resulted in the death of 2 female out of 5 animals treated. These animals wer replaced and survived after treatment. The following clinical sign was observed: motor activity decreased. The dissection of the 2 female animlas which died within 24 h after the first application revealed the following macroscopic finding: intestinal tract filled with orange colored spume. The dissection of all other animals revealed no test substance related macroscopic findings. The inicidence of micronucleated polychromatic erythrocytes in the dose groups of Phosphoric acid, butyl ester was within the normal range of the negative control group. No statisitcally significant increase of micronucleated polychromatic erythrocytes was observed. The ratio of polychromatic erythrocytes to total erythrocytes remained essentailly unaffected by the test compound and was not less than 20% of the control values. Cyclophosphamide induced a marked and statistically significant increae in the number of polychromatic erythrocytes with micronuclei, thus indicating the sensitivty of the test system.
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