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EC number: 237-714-9 | CAS number: 13939-25-8
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- The study was performed between 03 April 2012 and 17 April 2012.
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results. The reliability has been amended in accordance with 'practical guide 6: How to report read-across and categories' which states that the maximum reliability for a read-across study is 2. The study is considered to be adequate and reliable for the purpose of registration under REACH (Regulation (EC) No. 1907/2006) and for classification and labelling in accordance with Regulation (EC) No. 1272/2008 (EU CLP). Read-across is justified on the basis that the sensitisation potential of aluminium dihydrogen triphosphate will be determined by the Al cation. Triphosphate itself is not considered to be a sensitiser, in addition, the ultimate breakdown product of triphosphate (orthophosphate) is a natural component of blood and cellular fluids. As aluminium dihydrogen triphosphate has a lower water solubility than aluminium orthophosphate it is considered to be less bioavailable and therefore aluminium orthophosphate is considered to be a worst case for sensitisation potential of the Al cation. The study reports that aluminium orthophosphate is a non-sensitiser under the conditions of the study.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of inspection: 19-21 July 2011. Date of signature: 31 August 2011
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Aluminium orthophosphate
- EC Number:
- 232-056-9
- EC Name:
- Aluminium orthophosphate
- Cas Number:
- 7784-30-7
- IUPAC Name:
- [phosphato(3-)-kappa~3~O,O',O'']aluminum
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
- Details on test material:
- Sponsor's identification: Aluminium orthophosphate
Description: off white powder
Batch number: MV 3371
Purity: not supplied
Date received: 14 March 2012
Expiry date: not supplied
Storage conditions: room temperature in the dark
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- other: CBA/Ca (CBA/CaOlaHsd)
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Female CBA/Ca (CBA/CaOlaHsd) strain mice were supplied by Harlan Laboratories UK Ltd., Oxon, UK.
- Age at study initiation: At the start of the study the animals were eight to twelve weeks old.
- Weight at study initiation: At the start of the study the animals were in the weight range of 15 to 23g.
- Housing: The animals were individually housed in suspended solid-floor polypropylene cages furnished with softwood woodflakes.
- Diet: ad libitum (2014C Teklad Global Rodent diet supplied by Harlan Laboratories UK Ltd., Oxon, UK)
- Water: ad libitum.
- Acclimation period: At least five days.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): The temperature was controlled to remain within the target ranges of 19 to 25°C.
- Humidity (%): The humidity was controlled to remain within the target ranges of 30 to 70%.
- Air changes (per hr): The rate of air exchange was approximately fifteen changes per hour.
- Photoperiod (hrs dark / hrs light): The lighting was controlled by a time switch to give twelve hours continuous light (06:00 to 18:00) and twelve hours darkness.
IN-LIFE DATES: From: Day 1 To: Day 6
Study design: in vivo (LLNA)
- Vehicle:
- propylene glycol
- Remarks:
- Please see below for Vehicle Determination Record
- Concentration:
- Each group was exposed to concentrations of 25 &, 10 or 5% w/w (in propylene glycol)
- No. of animals per dose:
- Groups of four mice were treated
- Details on study design:
- Preliminary Screening Test
Using available information regarding the systemic toxicity/irritancy potential of the test item, a preliminary screening test was performed using one mouse. The mouse was treated by daily application of 25 μl of the test item at a concentration of 25% w/w in propylene glycol, to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The mouse was observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Local skin irritation was scored daily according to the scale included as Appendix 4. Any clinical signs of toxicity, if present, were also recorded. The
bodyweight was recorded on Day 1 (prior to dosing) and on Day 6.
The thickness of each ear was measured using an Oditest micrometer (Dyer, PA), pre-dose on Day 1, post dose on Day 3 and on Day 6. Any changes in the ear thickness were noted. Mean ear thickness changes were calculated between time periods Days 1 and 3 and Days 1 and 6. A mean ear thickness increase of equal to or greater than 25% was considered to indicate excessive irritation and limited biological relevance to the endpoint of sensitisation.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
-animals were selected at random and given a number unique within the study by indelible ink marking on the tail and a number written on a cage card
- Name of test method:
Local Lymph Node Assay in the Mouse. The assay has undergone extensive inter-laboratory validation and has been shown to reliably detect test materials that are moderate to strong sensitisers.
- Criteria used to consider a positive response:
The proliferation response of lymph node cells was expressed as the number of radioactive disintegrations per minute per lymph node(dpm/node) and as the ratio of 3HTdR incorporation in lymph node cells of test nodes relative to that recorded for the control nodes (stimulation Index).
The test material will be regarded as a sensitiser if at least one concentration of the test material results in a threefold or greater increase in 3HTdR incorporation compared to control values. Any test material failing to produce a threefold or greater increase in 3HTdR incorporation will be classified as a "non-sensitier".
TREATMENT PREPARATION AND ADMINISTRATION:
For the purpose of the study, the test material was used undiluted and also freshly prepared in propylene glycol. This vehicle was chosen as it produced the most suitable formulation at the required concentration. The concentrations used are given above.
Determination, by analysis, of the concentration, homogeneity and stability of the test material preparations was not appropriate because it was not specified in the Study Plan and is not a requirement of the Test Guidelines.
Test Material Administration
Groups of four mice were treated with the test item at concentrations of 25%, 10% or 5% w/w in propylene glycol. The preliminary screening test suggested that the test item would not produce systemic toxicity or excessive local skin irritation at the highest suitable concentration. The mice were treated by daily application of 25 μl of the appropriate concentration of the test item to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The test item formulation was administered using an automatic micropipette and spread over the dorsal surface of the ear using the tip of the
pipette.
A further group of four mice received the vehicle alone in the same manner.
3H-Methyl Thymidine Administration:
Five days following the first topical application of the test item or vehicle (Day 6) all mice were injected via the tail vein with 250 μl of phosphate buffered saline (PBS) containing 3H-methyl thymidine (3HTdR: 80 μCi/ml, specific activity 2.0 Ci/mmol, ARC UK Ltd) giving a total of 20 μCi to each mouse.
OBSERVATIONS
Clinical Observations: All animals were observed twice daily on Days 1, 2 and 3 and on a daily basis on Days 4, 5 and 6. Any signs of toxicity or signs of ill health during the Test were recorded.
Bodyweights: The bodyweight of each mouse was recorded on Day 1 (prior to dosing) and Day 6 (prior to termination).
TERMINAL PROCEDURES
Termination: Five hours following the administration of 3HTdR all mice were killed by carbon dioxide asphyxiation. The draining auricular lymph nodes from the four mice were excised and pooled for each experimental group. For each group 1 ml of PBS was added to the pooled lymph nodes.
Preparation of Single Cell Suspension: A single cell suspension of pooled lymph node cells was prepared by gentle mechanical disaggregation through a 200-mesh stainless steel gauze. The lymph node cells were rinsed through the gauze with 4 ml of PBS into a petri dish labelled with the project number and dose concentration. The lymph node cell suspension was transferred to a centrifuge tube. The petri dish was washed with an additional 5 ml of PBS to remove all remaining lymph node cells and these were added to the centrifuge tube. The pooled lymph node cells were pelleted at 1400 rpm (approximately 190 g) for ten minutes. The pellet was resuspended in 10 ml of PBS and re-pelleted. To precipitate out the radioactive material, the pellet was resuspended in 3 ml of 5% Trichloroacetic acid (TCA).
Determination of 3HTdR Incorporation: After approximately eighteen hours incubation at approximately 4°C, the precipitates were recover ed by centrifugation at 2100 rpm (approximately 450 g) for ten minutes, resuspended in 1 ml of TCA and transferred to 10 ml of scintillation fluid (Optiphase 'Trisafe'). 3HTdR incorporation was measured by b-scintillation counting. The "Poly QTM" vials containing the samples and scintillation fluid were placed in the sample changer of the scintillator and left for approximately twenty minutes. The purpose of this period of time in darkness was to reduce the risk of luminescence, which has been shown to affect the reliability of the results. After approximately twenty minutes, the vials were shaken vigorously. The number of radioactive disintegrations per minute was then measured using the Beckman LS6500 scintillation system (Beckman Instruments Inc, Fullerton, CA, USA). - Positive control substance(s):
- other: Phenylacetaldehyde (90%)
Results and discussion
- Positive control results:
- One group of five animals was treated with 50 µl (25 µl per ear) of Phenylacetaldehyde (90%) as a solution in propylene glycol at a concentration of 2.5% v/v. A further group of five animals was treated with propylene glycol alone.
The Stimulation Index expressed as the mean radioactive incorporation for the treatment group divided by the mean radioactive incorporation of the vehicle control group are as follows:
Concentration (% v/v) in Stimulation Index Result
propylene glycol
2.5 3.49 Positive
Phenylacetaldehyde (90%) was considered to be a sensitiser under the conditions of the test.
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Remarks on result:
- other: A stimulation index of less than 3 was recorded for the test material at concentrations of 10%, 5% and 2.5% w/w in propylene glycol
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: The radioactive disintegrations per minute (dpm) per lymph node and the stimulation index (SI) are given in Table 2.
Any other information on results incl. tables
Preliminary Screening Test
Clinical observations, bodyweight and mortality data are given in Table 2 and local skin irritation is given in Table 3. The ear thickness measurements and mean ear thickness changes are given in Table 4.
No signs of systemic toxicity, visual local skin irritation or irritation indicated by an equal to or greater than 25% increase in mean ear thickness were noted.
Based on this information the dose levels selected for the main test were 25%, 10% and 5% w/w in propylene glycol.
Main Test
Estimation of the Proliferative Response of Lymph Node Cells
The radioactive disintegrations per minute per lymph node and the stimulation index are given in Table 1.
The Stimulation Index expressed as the mean radioactive incorporation for each treatment group divided by the mean radioactive incorporation of the vehicle control group are as follows:
Table 1.
Concentration (%w/w) in |
Stimulation Index |
Result |
5 |
1.06 |
Negative |
10 |
1.01 |
Negative |
25 |
0.89 |
Negative |
Clinical Observations and Mortality Data
Individual clinical observations and mortality data for test and control animals are given in Table 5.
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test.
Bodyweight
Individual bodyweights and bodyweight changes for test and control animals are given in Table 6.
Bodyweight changes of the test animals between Day 1 and Day 6 were comparable to those observed in the corresponding control group animals over the same period.
Table 2 Clinical Observations, Bodyweight and Mortality Data – Preliminary Screening Test
Concentration (%w/w) in |
Animal Number |
Bodyweight (g) |
Day |
|||||||||
1 |
2 |
3 |
4 |
5 |
6 |
|||||||
Day 1 |
Day 6 |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
|||||
25 |
S-1 |
20 |
19 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0= No signs of systemic toxicity
Table 3. Local skin irritation - preliminary screening test
Concentration (%w/w) in propylene glycol |
Animal number |
Local skin irritation |
|||||||||||
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
||||||||
Left |
Right |
Left |
Right |
Left |
Right |
Left |
Right |
Left |
Right |
Left |
Right |
||
25 |
S-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Table 4. Measurement of Ear Thickness and Mean Ear Thickness Changes – Preliminary Screening Test
Concentration (% w/w) in propylene glycol |
Animal number |
Ear thickness measurement (mm) |
|||||
Day 1 |
Day 3 |
Day 6 |
|||||
Pre-dose |
Post-dose |
||||||
Left |
Right |
Left |
Right |
Left |
Right |
||
25 |
S-1 |
0.230 |
0.230 |
0.240 |
0.235 |
0.230 |
0.235 |
Overall mean (mm) |
0.230 |
0.238 |
0.233 |
||||
Overall mean ear thickness change (%) |
n/a |
3.261 |
1.087 |
Table 5. Disintegrations per Minute, Disintegrations per Minute/Node and Stimulation Index
Concentration |
dpm |
dpm/Nodea |
Stimulation Indexb |
Result |
Vehicle |
6112.62 |
764.08 |
na |
na |
5 |
6450.73 |
806.34 |
1.06 |
Negative |
10 |
6192.92 |
774.12 |
1.01 |
Negative |
25 |
5463.95 |
682.99 |
0.89 |
Negative |
dpm = Disintegrations per minute
a = Disintegrations per minute/node obtained by dividing the disintegrations per minute value by 8
(total number of lymph nodes)
b = Stimulation Index of 3.0 or greater indicates a positive result
na = Not applicable
Table 6. Individual Clinical Observations and Mortality Data
Concentration |
Animal Number |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
|||
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
|||||
Vehicle |
1-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
1-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
5 |
2-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
2-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
10 |
3-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
3-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
25 |
4-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
4-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0= No signs of systemic toxicity
Table 7. Individual Bodyweights and Bodyweight Changes
Concentration |
Animal Number |
Bodyweight (g) |
Bodyweight Change (g) |
|
Day 1 |
Day 6 |
|||
Vehicle |
1-1 |
20 |
19 |
-1 |
1-2 |
18 |
17 |
-1 |
|
1-3 |
23 |
22 |
-1 |
|
1-4 |
18 |
18 |
0 |
|
5 |
2-1 |
21 |
20 |
-1 |
2-2 |
21 |
22 |
1 |
|
2-3 |
20 |
20 |
0 |
|
2-4 |
20 |
21 |
1 |
|
10 |
3-1 |
20 |
21 |
1 |
3-2 |
19 |
20 |
1 |
|
3-3 |
19 |
19 |
0 |
|
3-4 |
21 |
21 |
0 |
|
25 |
4-1 |
20 |
20 |
0 |
4-2 |
20 |
21 |
1 |
|
4-3 |
18 |
19 |
1 |
|
4-4 |
20 |
20 |
0 |
Please see attachment "Appendix 1 Current Positive Control Study for the Local Lymph Node Assay”
Please see attachment "Appendix 2 Summary of Positive Control Data for the Local Lymph Node Assay”
Applicant's summary and conclusion
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The test material was considered to be a non-sensitiser under the conditions of the test. The study is considered to be reliable and acceptable for use as a key study.
Read-across is justified on the basis that the sensitisation potential of aluminium dihydrogen triphosphate will be determined by the Al cation. Triphosphate itself is not considered to be a sensitiser, in addition, the ultimate breakdown product of triphosphate (orthophosphate) is a natural component of blood and cellular fluids. As aluminium dihydrogen triphosphate has a lower water solubility than aluminium orthophosphate it is considered to be less bioavailable and therefore aluminium orthophosphate is considered to be a worst case for sensitisation potential of the Al cation. The study reports that aluminium orthophosphate is a non-sensitiser under the conditions of the study.
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