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EC number: 226-195-4 | CAS number: 5324-84-5
- 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
Endpoint summary
Administrative data
Description of key information
Repeat dose toxicity: oral; NOAEL = 5000 ppm (430 mg/kg bw/d); OECD 408; Walker et al. (1967) (Read-across)
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1967
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH - Refer to Section 13.2 for read-across justification document
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Deviations:
- not applicable
- GLP compliance:
- no
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Carworth Farm 'E' strain
- Details on species / strain selection:
- Inhouse laboratory culture.
Pathogen-free. - Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Inhouse culture
- Females (if applicable) nulliparous and non-pregnant: Not reported
- Age at study initiation: 5 weeks
- Weight at study initiation: 150-250 g
- Fasting period before study: No
- Housing: Not reported
- Diet (e.g. ad libitum): Ad lib
- Water (e.g. ad libitum): Ad lib
- Acclimation period: Not reported
DETAILS OF FOOD AND WATER QUALITY: Diet = Diet 86 powder (Withers Ltd., Godalming, Surrey)
ENVIRONMENTAL CONDITIONS
- Temperature (°C): Not reported
- Humidity (%): Not reported
- Air changes (per hr): Not reported
- Photoperiod (hrs dark / hrs light): Not reported
IN-LIFE DATES: From: To: Not reported - Route of administration:
- oral: feed
- Details on route of administration:
- Rats were fed dietary levels of 40, 200, 1000 or 5000 ppm active material (corresponding to 3, 17, 86 and 430 mg/kg bw/day actual ingested) for 13 weeks. Control groups received Diet 86 powder (Withers Ltd., Godalruing, Surrey).
- Vehicle:
- not specified
- Details on oral exposure:
- - PREPARATION OF DOSING SOLUTIONS:
Not reported
- DIET PREPARATION
- Rate of preparation of diet (frequency): Not reported
- Mixing appropriate amounts with (Type of food): Not reported
- Storage temperature of food: Not reported
- VEHICLE
- Justification for use and choice of vehicle (if other than water): Not reported
- Concentration in vehicle: Not reported
- Amount of vehicle (if gavage): N/A
- Lot/batch no. (if required): Not reported
- Purity: Not reported - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- N/A
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- Diet provided ad libitum
- Dose / conc.:
- 40 ppm
- Dose / conc.:
- 200 ppm
- Dose / conc.:
- 1 000 ppm
- Dose / conc.:
- 5 000 ppm
- No. of animals per sex per dose:
- 12 male and 12 female per test treatment group
18 male and 18 female per test Control group - Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: From previous literature (Smyth, Seaton & Fischer, 1941; Fitzhugh & Nelson, 1948; Fitzhugh, Schouboe & Nelson, 1960; Tusing, Paynter, Opdyke & Snyder, 1962).
- Rationale for animal assignment (if not random): Not reported
- Rationale for selecting satellite groups: N/A
- Post-exposure recovery period in satellite groups: N/A
- Section schedule rationale (if not random): N/A - Positive control:
- N/A
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Daily
BODY WEIGHT: Yes
- Time schedule: Weekly
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Mean weekly food intake per treatment group calculated
FOOD EFFICIENCY: No
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes (Haemoglobin, packed cell volume, red blood cell, white blood cell)
- Time schedule for collection of blood: Study terminus
- Anaesthetic used for blood collection: No
- Animals fasted: Not specified
- How many animals: 12 males and 12 females from each test group and 18 males and 18 females from control groups
CLINICAL CHEMISTRY: Yes (urea, protein)
- Time schedule for collection of blood: Study terminus
- Animals fasted: Not specified
- How many animals: 12 males and 12 females from each test group and 18 males and 18 females from control groups.
URINALYSIS: Yes (pH, osmolarity reported and colour, protein, reducing substances and bile salts found to be negative in all test groups)
- Time schedule for collection of urine: Week 12 for 5000 ppm and control groups only
- Metabolism cages used for collection of urine: Yes
- Animals fasted: Not specified
NEUROBEHAVIOURAL EXAMINATION: No
IMMUNOLOGY: No
OTHER: N/A - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, mean organ weights reported (brain (adjusted for initial body weight), heart, liver, spleen, kidneys, testes)
HISTOPATHOLOGY: Yes, sections of organs taken from control and 5000 ppm groups. - Other examinations:
- N/A
- Statistics:
- Statistical analyses of terminal body weights, food intakes and organ weights were made using the initial body weight as a covariate in covariance analysis.
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- A statistically significant increse in Hb, PCV (p ≤ 0.05) and RBC (p ≤ 0.01) was observed in the blood samples collected from female rats treated with 40 ppm. In the absence of a dose response at higher test concentrations, the effects cannot be attributed to a test item related response.
- Clinical biochemistry findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Increase serum urea concentration in females on 5000 ppm and increase in serum total concentration in males on 5000 ppm
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- Significant increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significantly (p ≤ 0.05)
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Spontaneous lesions, mainly hydronephrosis, were present in all groups of animals.
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
- Details on results:
- In conclusion, treatment with the test item at 40, 200, 1000 and 5000 ppm had no definite effect on mortality, clinical condition, body weight gain, feeding, haematology or urinalysis. Increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significantly (p ≤ 0.05). The increase in organ weights at the highest tested concentration (5000 ppm) were unaccompanied by any pathological effects, as a result, 5000 ppm is considered a no-observed effect level (NOAEL) for the test item.
- Dose descriptor:
- NOAEL
- Effect level:
- 5 000 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- organ weights and organ / body weight ratios
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- > 430 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Remarks:
- actual dose received
- Sex:
- male/female
- Basis for effect level:
- organ weights and organ / body weight ratios
- Critical effects observed:
- no
- Conclusions:
- In conclusion, treatment with the test item at 40, 200, 1000 and 5000 ppm had no definite effect on mortality, clinical condition, body weight gain, feeding, haematology or urinalysis. Increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05). The increase in organ weights at the highest tested concentration (5000 ppm) was unaccompanied by any pathological effects, as a result, 5000 ppm is considered a no-observed effect level (NOAEL) for the test item.
This result is appropriate under a read-across approach for applicability to the target substance sodium octane-1-sulphonate monohydrate. - Executive summary:
The purpose of this test was to assess the systemic toxicity potential of sodium lauryl sulphate following repeated exposure to 12 male and 12 female Carwoth Farm ‘E’ strain in rats by dietary administration at dose levels of 40, 200, 1000 and 5000 ppm for up to 13 weeks.
A summary of adult responses to the test item are described below;
Mortality- no treatment related effects were observed.
Clinical signs- no treatment related effects were observed.
Bodyweight- no treatment related effects were observed.
Food consumption and efficiency- no treatment related effects were observed.
Haematology and urinalysis-no treatment related effects were observed
Organ weights- Significant increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05).
Histopathology- The increase in organ weights at the highest tested concentration (5000 ppm) were unaccompanied by any pathological effects.
In conclusion, treatment with the test item at 40, 200, 1000 and 5000 ppm (corresponding to 3, 17, 86 and 430 mg/kg bw/day actual ingested) had no definite effect on mortality, clinical condition, body weight gain, feeding, haematology or urinalysis. Increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05). The increase in organ weights at the highest tested concentration (5000 ppm) was unaccompanied by any pathological effects, as a result, 5000 ppm (430 mg/kg bw/d) is considered a no-observed effect level (NOAEL) for the test item.
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
See document attached in Section 13.2 for analogue read-across justification. - Reason / purpose for cross-reference:
- read-across source
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Dose descriptor:
- NOAEL
- Effect level:
- 5 000 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- organ weights and organ / body weight ratios
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- > 430 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- organ weights and organ / body weight ratios
- Critical effects observed:
- no
- Conclusions:
- In conclusion, treatment with the test item at 40, 200, 1000 and 5000 ppm had no definite effect on mortality, clinical condition, body weight gain, feeding, haematology or urinalysis. Increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05). The increase in organ weights at the highest tested concentration (5000 ppm) was unaccompanied by any pathological effects, as a result, 5000 ppm is considered a no-observed effect level (NOAEL) for the test item.
- Executive summary:
See document attached in Section 13.2 for analogue read-across justification.
The purpose of this test was to assess the systemic toxicity potential of sodium lauryl sulphate following repeated exposure to 12 male and 12 female Carwoth Farm ‘E’ strain in rats by dietary administration at dose levels of 40, 200, 1000 and 5000 ppm for up to 13 weeks.
A summary of adult responses to the test item are described below;
Mortality- no treatment related effects were observed.
Clinical signs- no treatment related effects were observed.
Bodyweight- no treatment related effects were observed.
Food consumption and efficiency- no treatment related effects were observed.
Haematology and urinalysis-no treatment related effects were observed
Organ weights- Significant increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05).
Histopathology- The increase in organ weights at the highest tested concentration (5000 ppm) were unaccompanied by any pathological effects.
In conclusion, treatment with the test item at 40, 200, 1000 and 5000 ppm had no definite effect on mortality, clinical condition, body weight gain, feeding, haematology or urinalysis. Increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05). The increase in organ weights at the highest tested concentration (5000 ppm) were unaccompanied by any pathological effects, as a result, 5000 ppm (430 mg/kg bw/d) is considered a no-observed effect level (NOAEL) for the test item.
Referenceopen allclose all
Table 3 Mean body weights and body weight gains/ losses
Dietary intake (ppm) |
Male |
Female |
||||||
Body weight (g) at week |
Mean weekly food intake (g) |
Body weight (g) at week |
Mean weekly food intake (g) |
|||||
4 |
8 |
13 |
4 |
8 |
13 |
|||
0 |
243 |
319 |
359 |
139 |
172 |
213 |
227 |
107 |
40 |
246 |
323 |
363 |
140 |
175 |
215 |
233 |
108 |
200 |
239 |
315 |
348 |
138 |
170 |
213 |
225 |
104 |
1000 |
234 |
308 |
351 |
133 |
175 |
216 |
228 |
111 |
5000 |
243 |
319 |
365 |
139 |
169 |
213 |
226 |
106 |
Body weights are adjusted for initial body weight
For test groups (n=12) and for control groups (n=18)
Table 4 Mean haematological examination results
Dietary intake (ppm) |
Male |
Female |
||||||
Hb (g/100 mL) |
PCV (%) |
RBC (108/mm8) |
WBC (108/mm8) |
Hb (g/100 mL) |
PCV (%) |
RBC (108/mm8) |
WBC (108/mm8) |
|
0 |
14.4 |
46.2 |
- |
- |
14.1 |
42.8 |
6.52 |
4.8 |
40 |
14.5 |
46.0 |
- |
- |
14.7* |
45.3* |
7.01** |
4.9 |
200 |
14.5 |
47.4 |
- |
- |
14.1 |
45.3 |
6.77 |
4.6 |
1000 |
14.6 |
46.6 |
- |
- |
13.7 |
41.9 |
6.47 |
4.0 |
5000 |
14.5 |
46.1 |
- |
- |
14.6 |
43.7 |
6.74 |
4.5 |
Hb (haemoglobin); PCV (packed cell volume); RBC (red blood cell); WBC (white blood cell)
- RBC and WBC for males was disregarded due to a fault with the measuring device
For test groups (n=12) and for control groups (n=18)
* (p ≤0 0.05); ** (p ≤ 0.01)
Table 5 Mean serum chemistry and urine analysis
Dietary intake (ppm) |
Male |
Female |
||||||
Serum chemistry |
Urine analysis |
Serum chemistry |
Urine analysis |
|||||
Urea (g/100 mL) |
Protein (g/100 mL) |
pH |
Osmolarity (mosmoles) |
Urea (g/100 mL) |
Protein (g/100 mL) |
pH |
Osmolarity (mosmoles) |
|
0 |
52 |
6.4 |
7.1 |
2003 |
56 |
6.3 |
6.3 |
1840 |
40 |
51 |
6.3 |
- |
- |
58 |
6.2 |
- |
- |
200 |
53 |
6.2 |
- |
- |
54 |
6.2 |
- |
- |
1000 |
53 |
6.2 |
- |
- |
60 |
6.0 |
- |
- |
5000 |
54 |
6.3 |
6.7 |
2054 |
53 |
6.5 |
6.2 |
1870 |
Test for blood, bile salts and reducing substances were negative in all groups
- Not examined
For test groups (n=12) and for control groups (n=18)
Table 6 Absolute organ weights (g)
Dietary intake (ppm) |
Male |
Female |
|||||||||||
B.W. |
Brain |
Heart |
Liver |
Spleen |
Kidneys |
Testes |
B.W. |
Brain |
Heart |
Liver |
Spleen |
Kidneys |
|
0 |
359 |
1.96 |
0.98 |
13.71 |
0.66 |
2.40 |
3.51 |
228 |
1.86 |
0.70 |
8.53 |
0.50 |
1.55 |
40 |
363 |
1.96 |
0.98 |
13.02 |
0.67 |
2.43 |
3.45 |
233 |
1.88 |
0.72 |
7.82 |
0.50 |
1.60 |
200 |
348 |
1.95 |
0.96 |
12.85 |
0.66 |
2.31 |
3.47 |
225 |
1.84 |
0.68 |
8.62 |
0.51 |
1.58 |
1000 |
351 |
1.97 |
0.98 |
13.33 |
0.68 |
2.34 |
3.42 |
228 |
1.88 |
0.67 |
8.24 |
0.50 |
1.57 |
5000 |
365 |
1.98 |
0.98 |
13.70 |
0.66 |
2.34 |
3.48 |
226 |
1.83 |
0.70 |
9.30* |
0.51 |
1.59 |
Values are means, except brain, adjusted for initial body weight of groups of 12 test and 18 control animals
B.W. (terminal body weight)
* (p ≤ 0.05)
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 430 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- The endpoint is concluded based on a single read across study with a Klimish rating of 2.
- System:
- other: The NOAEL was derived from the highest tested concentration (5000 ppm), where no adverse effects on the rat were observed.
Repeated dose toxicity: inhalation - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: inhalation
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
In accordance with Annex VIII, Section 8.6.1, Column 2 and supporting ECHA Guidance, concerning repeated dose toxicity testing, the oral route is the default one because it is assumed to maximise systemic availability (internal dose). There was no evidence available to support the use of an alternative route for this study.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: inhalation
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
In accordance with Annex VIII, Section 8.6.1, Column 2 and supporting ECHA Guidance, concerning repeated dose toxicity testing, the oral route is the default one because it is assumed to maximise systemic availability (internal dose). There was no evidence available to support the use of an alternative route for this study.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
In accordance with Annex VIII, Section 8.6.1, Column 2 and supporting ECHA Guidance, concerning repeated dose toxicity testing, the oral route is the default one because it is assumed to maximise systemic availability (internal dose). There was no evidence available to support the use of an alternative route for this study.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
In accordance with Annex VIII, Section 8.6.1, Column 2 and supporting ECHA Guidance, concerning repeated dose toxicity testing, the oral route is the default one because it is assumed to maximise systemic availability (internal dose). There was no evidence available to support the use of an alternative route for this study.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Mode of Action Analysis / Human Relevance Framework
No adverse effects were observed at the highest tested concentration (5000 ppm; 430 mg/kg bw/d).
Additional information
See document attached in Section 13.2 for analogue read-across justification.
OECD 408 - The purpose of this test was to assess the systemic toxicity potential of sodium lauryl sulphate following repeated exposure to 12 male and 12 female Carworth Farm ‘E’ strain in rats by dietary administration at dose levels of 40, 200, 1000 and 5000 ppm for up to 13 weeks.
A summary of adult responses to the test item are described below;
Mortality- no treatment related effects were observed.
Clinical signs- no treatment related effects were observed.
Bodyweight- no treatment related effects were observed.
Food consumption and efficiency- no treatment related effects were observed.
Haematology and urinalysis-no treatment related effects were observed
Organ weights- Significant increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05).
Histopathology- The increase in organ weights at the highest tested concentration (5000 ppm) were unaccompanied by any pathological effects.
In conclusion, treatment with the test item at 40, 200, 1000 and 5000 ppm had no definite effect on mortality, clinical condition, body weight gain, feeding, haematology or urinalysis. Increases in absolute organ weights were confined to the highest test group (5000 ppm) however only the increased liver weights from the females were found to be statistically significant (p ≤ 0.05). The increase in organ weights at the highest tested concentration (5000 ppm) was unaccompanied by any pathological effects, as a result, 5000 ppm (430 mg/kg bw/d) is considered a no-observed effect level (NOAEL) for the test item.
Justification for classification or non-classification
The substance does not meet the criteria for classification in accordance with Regulation (EC) No 1272/2008 (CLP).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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