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EC number: 942-293-6 | CAS number: -
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- March 2012-december 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 421 (Reproduction / Developmental Toxicity Screening Test)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- N,N-Bis(2-hydroxyethyl)-C12-18(even numbered, C18 unsaturated) alkyl-1-amine oxides
- EC Number:
- 942-293-6
- Molecular formula:
- not applicable
- IUPAC Name:
- N,N-Bis(2-hydroxyethyl)-C12-18(even numbered, C18 unsaturated) alkyl-1-amine oxides
- Test material form:
- liquid: viscous
Constituent 1
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on mating procedure:
- The mating began 2 weeks after the initiation of treatment with one female and one male of the same dose group (1:1 mating) in a single cage. Females remained with the same male until copulation occured or up to two weeks.
A vaginal smear was prepared daily during the mating period and stained with 1% aqueous methylene blue solution. The smears were examined with a light mictroscope, the presence of vaginal plug or sperm in the vaginal smear was considered as evidence of copulation. Sperm positive females were caged individually. Mating pairs were clearly identified in the data, mating of siblings was avoided. - Analytical verification of doses or concentrations:
- yes
- Duration of treatment / exposure:
- 28 days for males and up to 54 days for females (14 days pre-mating + up to 14 days for mating + gestation + 4 days of lacation)
- Frequency of treatment:
- once per day
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 12.5, 50, 200
Basis:
nominal in water
- No. of animals per sex per dose:
- 12
- Control animals:
- yes, concurrent vehicle
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- effects observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- limited to organs with macroscopic changes
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- effects observed, treatment-related
Details on results (P0)
At 200 mg/kg bw: one male animal was found dead after 22 treatments. Decreased activity, red liquid on the nose, piloerection and hunched back position were noted prior to the death. Upon histopathological investigation, malignant lymphoma that affected the spleen, thymus, liver, lungs and adrenal glands was considered to be cause of death.
Clinical signs
At 200 mg/kg bw, one surviving male displayed noisy respiration, piloerection and lack of grooming, and four females exhibited noisy respiration.
BODY WEIGHT AND WEIGHT GAIN
At 200 mg/kg bw, reduced body weight or body weight gain was noted for males and females.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
At 200 mg/kg bw, reduced food consumption was noted for males and females
HAEMATOLOGY
No toxicologically significant effect was found.
CLINICAL CHEMISTRY
No toxicologically significant effect was found.
ORGAN WEIGHTS
No toxicologically significant effect was found.
GROSS PATHOLOGY
At 200 mg/kg bw, thickened/rough surface non glandular mucosa was noted.
HISTOPATHOLOGY: NON-NEOPLASTIC
At 200 mg/kg bw, minimal to mild diffuse parakeratotic hyperkeratosis of the non-glandular stomach was found.
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: At 200 mg/kg bw, clinical signs and decreased body weight gain was observed.
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- no effects observed
- Mortality / viability:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Histopathological findings:
- not examined
Details on results (F1)
At 200 mg/kg bw, reduced number of living pubs at the first observation after birth and increased postnatal mortality was found.
At 50 and 12.5, the number of living pubs were reduced when compared to the corresponding control, but the obtained values were within the historical control range and were considered as incidental.
CLINICAL SIGNS (OFFSPRING)
No finding
BODY WEIGHT (OFFSPRING)
The body weight at 200 mg/kg bw was reduced when compared to the corresponding control.
Effect levels (F1)
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- 50 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: At 200 mg/kg bw, reduced litter size at birth and increased postnatal mortality occured.
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
Tab 1a: Body weight development for males [g] |
||||||
Dose group |
Day numbers relative to start date |
|||||
|
Pre-mating |
Mating |
||||
|
0 |
7 |
14 |
21 |
28 |
|
Control |
Mean |
421.25 |
442.67 |
436.75 |
475.33 |
495.67 |
S.D. |
16.45 |
18.24 |
22.04 |
25.46 |
28.57 |
|
N |
12 |
12 |
12 |
12 |
12 |
|
12.5 mg/kg bw/day |
Mean |
421.25 |
443.42 |
439.08 |
475.33 |
496.58 |
S.D. |
15.49 |
14.28 |
14.32 |
18.89 |
20.99 |
|
N |
12 |
12 |
12 |
12 |
12 |
|
50 mg/kg bw |
Mean |
420.75 |
441.75 |
437.67 |
473.25 |
498.17 |
S.D. |
13.98 |
17.80 |
17.60 |
17.48 |
19.93 |
|
N |
12 |
12 |
12 |
12 |
12 |
|
200 mg/kg bw/day |
Mean |
420.92 |
432.83 |
422.17* |
450.10** |
475.91* |
S.D. |
14.30 |
13.87 |
11.75 |
24.28 |
23.07 |
|
N |
12 |
12 |
12 |
11 |
11 |
Tab 1b: Body weight development for females [g] |
||||||||||
Dose group |
|
Pre-mating |
Gestation |
Lactation |
||||||
|
0 |
7 |
14 |
0 |
7 |
14 |
20 |
0 |
4 |
|
Control |
Mean |
239.67 |
251.00 |
248.89 |
262.00 |
297.67 |
335.78 |
424.00 |
330.67 |
347.56 |
S.D. |
11.65 |
12.66 |
14.73 |
14.76 |
17.33 |
19.47 |
26.40 |
23.69 |
30.53 |
|
N |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
|
12.5 mg/kg bw/day |
Mean |
239.75 |
246.58 |
244.17 |
259.75 |
287.33 |
322.75 |
397.25 |
313.42 |
329.33 |
S.D. |
10.64 |
12.24 |
14.44 |
14.64 |
15.71 |
20.04 |
25.07 |
24.48 |
25.66 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
|
50 mg/kg bw |
Mean |
240.73 |
249.64 |
245.18 |
260.00 |
294.91 |
329.18 |
401.36 |
327.55 |
335.82 |
S.D. |
10.26 |
10.60 |
13.63 |
16.53 |
17.11 |
23.50 |
36.75 |
25.73 |
30.87 |
|
N |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
|
200 mg/kg bw/day |
Mean |
240.00 |
247.82 |
241.36 |
254.27 |
280.09 |
315.18 |
390.09* |
296.91* |
291.45** |
S.D. |
10.35 |
13.36 |
12.45 |
10.16 |
20.30 |
21.82 |
24.26 |
29.00 |
21.64 |
|
N |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
Tab 2a: Hematology for males |
|||||||||||||||
Dose group |
|
Hb |
RBC |
Hct |
MCH |
MCV |
MCHC |
WBC |
Neut |
Lymph |
PTT |
PLT |
MPV |
APTT |
Retic |
|
g/dl |
10^12/l |
% |
pg |
g/dl |
g/dl |
10^9/l |
% |
% |
sec |
10^9/l |
fl |
sec |
% |
|
Control |
Mean |
17.63 |
9.14 |
48.61 |
19.33 |
53.18 |
36.30 |
9.12 |
21.55 |
71.46 |
24.67 |
868.08 |
7.88 |
16.01 |
1.99 |
S.D. |
1.08 |
0.51 |
2.80 |
0.89 |
1.13 |
1.36 |
2.64 |
8.88 |
9.77 |
1.31 |
243.48 |
1.06 |
1.71 |
0.17 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
|
12.5 mg/kg bw/day |
Mean |
17.24 |
9.20 |
48.78 |
18.78 |
53.05 |
35.38* |
9.75 |
17.23 |
76.58 |
24.83 |
948.92 |
9.28 |
17.18 |
2.19 |
S.D. |
1.00 |
0.48 |
3.13 |
0.74 |
1.66 |
0.95 |
1.82 |
6.47 |
7.39 |
1.34 |
377.90 |
4.37 |
1.65 |
0.34 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
|
50 mg/kg bw/day |
Mean |
17.18 |
9.28 |
49.09 |
18.53* |
52.93 |
35.00** |
11.25 |
14.52* |
80.48** |
24.66 |
1111.33 |
9.24* |
17.99 |
2.06 |
S.D. |
0.78 |
0.35 |
2.06 |
0.64 |
1.24 |
0.93 |
2.70 |
6.49 |
6.69 |
2.38 |
341.82 |
2.07 |
2.70 |
0.36 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
|
200 mg/kg bw/day |
Mean |
16.26** |
9.20 |
47.38 |
17.69** |
51.49* |
34.34** |
10.97 |
15.72 |
78.71* |
24.19 |
1076.10 |
8.37 |
18.48 |
1.73 |
S.D. |
0.42 |
0.32 |
1.67 |
0.48 |
1.41 |
0.61 |
1.88 |
4.51 |
5.17 |
3.25 |
268.10 |
0.48 |
4.98 |
0.36 |
|
N |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
10 |
Tab 2b: Hematology for females |
|||||||||||||||
Dose group |
|
Hb |
RBC |
Hct |
MCH |
MCV |
MCHC |
WBC |
Neut |
Lymph |
PTT |
PLT |
MPV |
APTT |
Retic |
|
g/dl |
10^12/l |
% |
pg |
g/dl |
g/dl |
10^9/l |
% |
% |
sec |
10^9/l |
fl |
sec |
% |
|
Control |
Mean |
16.34 |
8.67 |
47.12 |
18.84 |
54.33 |
34.68 |
4.61 |
21.10 |
74.02 |
23.51 |
951.78 |
8.13 |
18.28 |
2.49 |
S.D. |
0.83 |
0.36 |
1.86 |
0.84 |
1.73 |
0.61 |
1.04 |
5.77 |
6.01 |
1.25 |
269.92 |
0.61 |
1.62 |
0.59 |
|
N |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
9 |
|
12.5 mg/kg bw/day |
Mean |
16.22 |
8.71 |
47.03 |
18.61 |
53.98 |
34.45 |
5.63 |
14.68 |
80.72* |
23.05 |
1097.83 |
8.27 |
18.39 |
2.37 |
S.D. |
0.72 |
0.31 |
2.01 |
0.48 |
1.36 |
0.62 |
2.27 |
4.16 |
4.24 |
2.54 |
139.50 |
0.35 |
2.25 |
0.51 |
|
N |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
12 |
|
50 mg/kg bw/day |
Mean |
16.17 |
8.52 |
46.78 |
19.00 |
54.92 |
34.59 |
6.40* |
21.63 |
73.22 |
23.97 |
1068.82 |
8.62* |
18.36 |
2.54 |
S.D. |
0.65 |
0.36 |
1.83 |
0.73 |
1.50 |
0.49 |
1.69 |
21.87 |
24.43 |
1.04 |
245.42 |
0.54 |
1.00 |
0.51 |
|
N |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
|
200 mg/kg bw/day |
Mean |
15.67 |
8.39 |
45.74 |
18.71 |
54.57 |
34.29 |
8.46** |
15.04 |
80.49* |
24.78 |
1010.18 |
8.77* |
18.67 |
2.26 |
S.D. |
0.44 |
0.42 |
1.53 |
0.58 |
1.59 |
0.65 |
3.28 |
6.88 |
7.31 |
1.71 |
187.18 |
0.51 |
1.73 |
0.39 |
|
N |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
11 |
Tab 3: Summary report of effects on reproduction/development |
||||
|
Dose group |
|||
|
Control |
12.5 mg/kg bw/day |
50 mg/kg bw/day |
200 mg/kg bw/day |
No. of females paired |
12 |
12 |
12 |
12 |
No. of females mated |
9 |
12 |
11 |
11 |
No. of females pregnant |
9 |
12 |
11 |
11 |
No. of dams with living pubs |
9 |
12 |
11 |
11 |
Body weight on GD20 [g] |
424 |
397 |
401 |
390* |
Body weight on PN4 [g] |
348 |
329 |
336 |
291** |
Corpora lutea |
17.3 |
15.2 |
12.6* |
15.7 |
Implantation sites |
15.2 |
13.7 |
11.3* |
13.4 |
No. of pubs alive at birth |
14.7 |
12.4** |
11.2* |
9.3** |
No. of pubs alive at PN4 |
14.6 |
12.1** |
11.0* |
1.2** |
* p < 0.05; ** p <0.01; ***p < 0.001
Applicant's summary and conclusion
- Conclusions:
- The registration substance was investigated for its reproduction toxicity according to the OECD Guideline 421. The NOAEL of 50 mg/kg bw was derived for systemic toxicity and for reproductive toxicity.
- Executive summary:
The registration substance was investigated for its reproduction toxicity according to the OECD Guideline 421. Rats were treated with the registration substance at doses of 12.5, 50 and 200 mg/kg bw.
The generation toxicity on parental animals at 200 mg/kg bw comprised noisy respiration, piloerection, lack of grooming. At this dose, the males exhibited remarkable decreased body weight gain in the pre-mating phasee and females significant body weight decrease in the lactation phase. Further observation included macroscopic and microscopic changes in the stomach at 200 mg/kg bw.
At 200 mg/kg bw, significantly reduced living pub numbers at first observation after birth and increased postnatal mortality was found.
The NOAEL of 50 mg/kg bw was derived for systemic toxicity and for reproductive toxicity.
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