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EC number: 231-840-8 | CAS number: 7758-87-4
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- The study was performed between 19 October 2009 and 03 November 2009.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- refer to analogue justification provided in IUCLID section 13
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
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:
- The Department of Health of the Government of the United Kingdom
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Sodium dihydrogenorthophosphate
- EC Number:
- 231-449-2
- EC Name:
- Sodium dihydrogenorthophosphate
- Cas Number:
- 7558-80-7
- Molecular formula:
- H3O4P.Na
- IUPAC Name:
- sodium dihydrogen phosphate
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: Harlan UK Limited, Bicester, Oxon, UK.
- Females nulliparous and non-pregnant: yes
- 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 (2014 Teklad Global Rodent diet supplied by Harlan Teklad, Blackthorn, Bicester, Oxon, UK)
- Water: ad libitum tap water
- Acclimation period: at least five days
- Indication of any skin lesions:
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 - 25
- Humidity (%): 30 - 70
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
Study design: in vivo (LLNA)
- Vehicle:
- propylene glycol
- Concentration:
- Each group was exposed to concentrations of 10%, 5% or 2.5% w/w (in propylene glycol)
- No. of animals per dose:
- Groups of four mice were treated
- Details on study design:
- RANGE FINDING TESTS:
Using available information regarding the systemic toxicity/irritancy potential of the test material, a preliminary screening test was performed using one mouse. The mouse was treated by daily application of 25 µl of the undiluted test material 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. Any signs of toxicity or excessive local irritation noted during this period were recorded. The bodyweight was recorded on Day 1 (prior to dosing) and on Day 6.
- Lymph node proliferation response:
Clinical observations, bodyweight and mortality data are give in the results section (table 1).
No signs of systemic toxicity were noted.
Based on this information the dose levels selected for the main test were 2.5% , 5% and 10% w/w in propylene glycol.
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 material at concentrations of 10%,5% or 2.5% w/win propylene glycol. The preliminary screening test suggested that the test material would not produce systemic toxicity or excessive local irritation at the highest suitable concentration. The mice were treated by daily application of 25 µl of the appropriate concentration of the test material to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The test material 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 material (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, GE Healthcare UK Ltd) giving a total of 20 µCi to each mouse. - 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 acetone/olive oil 4:1 Stimulation Index (SI) Result
15 10.91 Positive
Alpha-Hexylcinnamaldehyde, Tech 85% was considered to be a sensitiser under the conditions of the test.
EXAMPLE
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Value:
- 1.31
- Test group / Remarks:
- 2.5% test substance
- Parameter:
- SI
- Value:
- 1.01
- Test group / Remarks:
- 5% test substance
- Parameter:
- SI
- Value:
- 1.05
- Test group / Remarks:
- 10% test substance
- Parameter:
- SI
- Value:
- 8
- Test group / Remarks:
- positive control - 90% Phenylacetaldehyde
- Cellular proliferation data / Observations:
- CLINICAL OBSERVATIONS: No signs of systemic toxicity
BODY WEIGHTS: normal
Any other information on results incl. tables
Preliminary Screening Test
Clinical observations, bodyweight and mortality data are given in Table 1.
No signs of systemic toxicity were noted.
Based on this information the dose levels selected for the main test were 10%, 5% and 2.5% 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 2.
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:
Concentration (%w/w) in |
Stimulation Index |
Result |
2.5 |
1.31 |
Negative |
5 |
1.01 |
Negative |
10 |
1.05 |
Negative |
Clinical Observations and Mortality Data
Individual clinical observations and mortality data for test and control animals are given in Table 3.
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 4.
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.
Table1 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 |
|||||
10 |
S-1 |
19 |
19 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0= No signs of systemic toxicity
Table2 Disintegrations per Minute, Disintegrations per Minute/Node and Stimulation Index
Concentration |
dpm |
dpm/Nodea |
Stimulation Indexb |
Result |
Vehicle |
5155.29 |
644.41 |
na |
na |
2.5 |
6770.88 |
846.36 |
1.31 |
Negative |
5 |
5203.17 |
650.40 |
1.01 |
Negative |
10 |
5413.31 |
676.66 |
1.05 |
Negative |
Table3 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 |
|
2.5 |
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 |
|
5 |
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 |
|
10 |
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
Table4 Individual Bodyweights and Bodyweight Changes
Concentration |
Animal Number |
Bodyweight (g) |
Bodyweight Change (g) |
|
Day 1 |
Day 6 |
|||
Vehicle |
1-1 |
19 |
21 |
2 |
1-2 |
18 |
18 |
0 |
|
1-3 |
21 |
20 |
-1 |
|
1-4 |
19 |
19 |
0 |
|
2.5 |
2-1 |
21 |
21 |
0 |
2-2 |
17 |
18 |
1 |
|
2-3 |
19 |
20 |
1 |
|
2-4 |
18 |
18 |
0 |
|
5 |
3-1 |
18 |
20 |
2 |
3-2 |
17 |
19 |
2 |
|
3-3 |
18 |
18 |
0 |
|
3-4 |
20 |
20 |
0 |
|
10 |
4-1 |
18 |
18 |
0 |
4-2 |
19 |
20 |
1 |
|
4-3 |
19 |
19 |
0 |
|
4-4 |
21 |
21 |
0 |
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- 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.
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