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EC number: 225-218-5 | CAS number: 4724-48-5
- 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 cell study: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- No data
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
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:
- 1 997
- Report date:
- 1997
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 486 (Unscheduled DNA Synthesis (UDS) Test with Mammalian Liver Cells in vivo)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.39 (Unscheduled DNA Synthesis (UDS) Test with Mammalian Liver Cells In Vivo)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable.
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- unscheduled DNA synthesis
Test material
- Reference substance name:
- Octylphosphonic acid
- EC Number:
- 225-218-5
- EC Name:
- Octylphosphonic acid
- Cas Number:
- 4724-48-5
- Molecular formula:
- C8H19O3P
- IUPAC Name:
- octylphosphonic acid
- Test material form:
- other: liquid
- Details on test material:
- Name in study report: Octylphosphonic Acid
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Strain: Alpk:APfSD
- Source: Rodent Breeding Unit (RBU), Zeneca, Alderley Park, Macclesfield, Cheshire
- Age at study initiation: 6-8 weeks
- Weight at study initiation: 215-277 g
- Fasting period before study: 6 hours or overnight
- Housing: individually
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 +/- 3
- Humidity (%): 30-70
- Air changes (per hr): not available
- Photoperiod (hrs dark / hrs light): 12:12
IN-LIFE DATES: from 4 October 2004 to 14 December 2004
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil
- Justification for choice of solvent/vehicle: acceptable solubility and non-toxicity to the animals
- Concentration of test material in vehicle: 10 ml/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: an individual stock emulsion of the test substance was prepared in corn oil for each group of animals.
DIET PREPARATION
- Rate of preparation of diet (frequency): not applicable
- Mixing appropriate amounts with (Type of food): not applicable
- Storage temperature of food: not applicable - Duration of treatment / exposure:
- 2 and 16 hours
- Frequency of treatment:
- once
- Post exposure period:
- not applicable
Doses / concentrations
- Remarks:
- Doses / Concentrations:
2000, 3200 mg/kg
Basis:
actual ingested
- No. of animals per sex per dose:
- 4 (males only)
- Control animals:
- yes
- Positive control(s):
- 2 hours preparation interval: DMH (N,N'-dimethylhydazinedihydrochloride)
- Justification for choice of positive control(s): validated for this assay
- Route of administration: oral gavage
- Doses / concentrations: 40 mg/kg bw / 10 ml/kg bw
16 hours preparation interval: 2-acetylaminofluorene
2 hours preparation interval: DMH (N,N'-dimethylhydazinedihydrochloride)
- Justification for choice of positive control(s): validatd for this assay
- Route of administration: oral gavage
- Doses / concentrations: 100 mg/kg bw / 10 ml/kg bw
Examinations
- Tissues and cell types examined:
- primary hepatocytes
- Evaluation criteria:
- a) Mean net nuclear grain counts for all test substance treated animals of less than zero - NEGATIVE.
b) In this laboratory no vehicle control animal has given a mean net nuclear grain count of greater than zero (Kennelly et al, 1995) and therefore such a value would be considered to represent a biologically significant departure from the norm. An occurrence of a mean net nuclear grain count of zero or above in a test substance treated animal is, therefore, considered to be indicative of a UDS response in that animal. Reproducibility of such a response in animals treated concurrently and in an independent experiment is necessary before concluding that the test substance is positive.
c) Where an individual animal has given rise to a mean net nuclear grain count of at least zero, but this is not fully reproducible, this may require further investigation. - Statistics:
- not required.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 2000-5000 mg/kg
- Solubility: soluble in corn oil vehicle
- Clinical signs of toxicity in test animals: 4/5 mortalities at 5000 mg/kg. No mortality or clinical signs at 3200 mg/kg
Any other information on results incl. tables
Summary of Data
Treatment |
Dose (mg/kg) |
Number of animals |
Mean N |
SD |
Mean C |
SD |
Mean |
SD |
Mean % cells in repair |
2 hours |
|
|
|
|
|
|
|
|
|
Corn oil |
10 ml/kg |
2 |
5.6 |
3.1 |
8.6 |
4.2 |
-3.0 |
1.1 |
1 |
OPA |
2000 |
5 |
4.3 |
1.4 |
7.2 |
2.6 |
-2.9 |
1.2 |
0 |
|
3200 |
5 |
5.3 |
1.8 |
9.1 |
2.3 |
-3.7 |
0.6 |
1 |
DMH.2HCl |
30 |
2 |
20.5 |
10.6 |
6.8 |
3.3 |
13.7 |
7.3 |
82 |
16 hours |
|
|
|
|
|
|
|
|
|
Corn oil |
10 ml/kg |
2 |
4.0 |
0.5 |
7.9 |
0.6 |
-3.9 |
1.1 |
0 |
OPA |
2000 |
5 |
3.9 |
0.6 |
7.1 |
1.7 |
-3.1 |
1.3 |
0 |
|
3200 |
5 |
4.0 |
0.6 |
7.0 |
1.3 |
-3.0 |
0.7 |
0 |
DMH.2HCl |
30 |
2 |
20.1 |
0.3 |
6.6 |
0.8 |
13.5 |
1.2 |
82 |
N: mean nuclear grain count
C: mean cytoplasmic grain count
(N-C): mean net nuclear grain count
SD: standard deviation
Individual Animal Data
Experiment 1 (16 hours)
Treatment |
Dose (mg/kg) |
Animal number |
Mean N |
Mean C |
Mean |
SE |
% cells in repair |
Corn oil |
10 ml/kg |
1 |
4.4 |
7.56.4 |
-3.1 |
0.3 |
0 |
OPA |
2000 |
3 |
3.6 |
6.4 |
-2.8 |
0.3 |
0 |
|
2000 |
4 |
4.4 |
6.4 |
-2.0 |
0.4 |
1 |
|
2000 |
5 |
3.2 |
5.1 |
-1.9 |
0.3 |
0 |
|
3200 |
6 |
3.2 |
5.3 |
-2.0 |
0.3 |
0 |
|
3200 |
7 |
4.0 |
6.9 |
-2.9 |
0.4 |
0 |
DMH.2HCl |
30 |
8 |
19.9 |
7.3 |
12.6 |
1.2 |
80 |
Experiment 2 ( hours)
Treatment |
Dose (mg/kg) |
Animal number |
Mean N |
Mean C |
Mean |
SE |
% cells in repair |
Corn oil |
10 ml/kg |
10 |
3.4 |
5.7 |
-2.3 |
0.3 |
1 |
OPA |
2000 |
12 |
3.0 |
4.4 |
-1.4 |
0.2 |
0 |
|
2000 |
13 |
2.8 |
4.9 |
-2.0 |
0.3 |
0 |
|
2000 |
14 |
4.3 |
7.3 |
-3.0 |
0.4 |
0 |
|
3200 |
15 |
4.0 |
7.0 |
-3.0 |
0.4 |
1 |
|
3200 |
16 |
3.5 |
6.9 |
-3.4 |
0.3 |
0 |
DMH.2HCl |
30 |
18 |
13.0 |
4.5 |
8.6 |
0.9 |
70 |
Experiment 3 (16 hours)
Treatment |
Dose (mg/kg) |
Animal number |
Mean N |
Mean C |
Mean |
SE |
% cells in repair |
Corn oil |
10 ml/kg |
19 |
3.7 |
8.3 |
-4.6 |
0.4 |
0 |
OPA |
2000 |
21 |
4.1 |
7.9 |
-3.8 |
0.5 |
0 |
|
2000 |
22 |
4.6 |
9.5 |
-4.9 |
0.5 |
0 |
|
3200 |
23 |
5.0 |
8.6 |
-3.7 |
0.4 |
1 |
|
3200 |
24 |
3.7 |
6.5 |
-2.8 |
0.3 |
0 |
|
3200 |
25 |
4.0 |
7.7 |
-3.7 |
0.4 |
0 |
DMH.2HCl |
30 |
26 |
20.4 |
6.1 |
14.3 |
1.2 |
83 |
Experiment 4 ( hours)
Treatment |
Dose (mg/kg) |
Animal number |
Mean N |
Mean C |
Mean |
SE |
% cells in repair |
Corn oil |
10 ml/kg |
29 |
7.8 |
11.6 |
-3.8 |
0.5 |
0 |
OPA |
2000 |
30 |
5.7 |
10.3 |
-4.6 |
0.4 |
0 |
|
2000 |
31 |
5.7 |
9.3 |
-3.5 |
0.4 |
0 |
|
3200 |
32 |
7.9 |
12.4 |
-4.5 |
0.5 |
0 |
|
3200 |
33 |
5.2 |
9.1 |
-3.8 |
0.4 |
0 |
|
3200 |
34 |
6.1 |
10.1 |
-4.0 |
0.5 |
1 |
DMH.2HCl |
30 |
36 |
28.1 |
9.2 |
18.9 |
1.3 |
93 |
N: nuclear grain count
C: cytoplasmic grain count
(N-C): net nuclear grain count
SE: standard error
Applicant's summary and conclusion
- Conclusions:
- negative
Under the conditions of test, OPA did not induce DNA repair (as measured by unscheduled DNA synthesis) in the rat liver in vivo. - Executive summary:
Octylphosphonic acid was evaluated, using an autoradiographic technique, for its ability to induce unscheduled DNA synthesis (UDS) in the liver of AlplcAPfSD rats. A single oral dose was given to groups of male rats at dose levels of 2000 and 3200 mg/kg. The latter dose level used represents the maximum tolerated dose (MTD) for male rats based on patterns of clinical signs and lethalities over a four day observation period. Two sampling times, 2 hours and 16 hours post-dose were used and 2 independent experiments were carried out at each time point.
The values recorded for the mean net nuclear grain counts and the percentage of cells in repair clearly show that OPA did not induce DNA repair, as measured by UDS, at either dose level or sampling time investigated. The test system positive control, 1,2-dimethylhydrazine dihydrochloride, induced marked increases in UDS, compared to the vehicle control values, thus demonstrating the sensitivity of the test system to a known genotoxin.
Under the conditions of test, OPA did not induce DNA repair (as measured by unscheduled DNA synthesis) in the rat liver in vivo.
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