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EC number: 213-384-1 | CAS number: 941-98-0
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- secondary literature
- Justification for type of information:
- Data from secondary source
Data source
Reference
- Reference Type:
- secondary source
- Title:
- one generation reproduction toxicity study in Wistar rats
- Author:
- European Food Safety Agency (EFSA)
- Year:
- 2 010
- Bibliographic source:
- Additional Report to the DAR for test material ,2010
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Principles of method if other than guideline:
- Developmental Toxicity study was performed on rabbits.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- 2-naphthyloxyacetic acid
- EC Number:
- 204-380-0
- EC Name:
- 2-naphthyloxyacetic acid
- Cas Number:
- 120-23-0
- Molecular formula:
- C12H10O3
- IUPAC Name:
- 2-naphthyloxyacetic acid
- Details on test material:
- - Name of test material (as cited in study report):2-naphthyloxyacetic acid
- Molecular formula (if other than submission substance):C12H10O3
- Molecular weight (if other than submission substance):202.208 g/mol
- Substance type:Organic
Constituent 1
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Details on test animals or test system and environmental conditions:
- No data available
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: 0.5% Carboxymethyl cellulose
- Details on exposure:
- Details on exposure
PREPARATION OF DOSING SOLUTIONS:
Test material dissolved in 0.5% Carboxymethyl cellulose
DIET PREPARATION
- Rate of preparation of diet (frequency):
- Mixing appropriate amounts with (Type of food):
- Storage temperature of food:
VEHICLE
- Justification for use and choice of vehicle (if other than water): Test material dissolved in 0.5% Carboxymethyl cellulose
- Concentration in vehicle: 0, 3, 10,50mg/kg/day
- Amount of vehicle (if gavage):
- Lot/batch no. (if required):
- Purity: - Analytical verification of doses or concentrations:
- not specified
- Details on mating procedure:
- No data available
- Duration of treatment / exposure:
- 23(gestation day 6 to 28)
- Frequency of treatment:
- daily
- Duration of test:
- 30 days
Doses / concentrations
- Remarks:
- 0, 3, 10,50mg/kg/day.
- No. of animals per sex per dose:
- Total:100
0mg/kg/day: 25 female
3mg/kg/day:25 female
10mg/kg/day:25 female
50mg/kg/day:25 female - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: base on the preliminary range-finding study (0, 10, 60 and 300 mg/kg/day).
- Rationale for animal assignment (if not random):
- Other:
Examinations
- Maternal examinations:
- Parental animals observation and examinations
CAGE SIDE OBSERVATIONS: yes
DETAILED CLINICAL OBSERVATIONS: Yes
Time schedule: twice daily
BODY WEIGHT: Yes
Time schedule for examinations: Individual body weights were recorded on gestation days 0, 3, 5, 8, 11, 14, 17, 20, 23, 26, 29 and 30.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes Food consumption per cage of animals were measured over the following periods during gestation: days 0-3, 3- 5, 5-8, 8-11, 11-14, 14-17, 17-20, 20-26, 26-29 and 29-30.
Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / No data: No data available
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No data
Time schedule for examinations:
OTHER: - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
- Other: - Fetal examinations:
- - External examinations: Yes: all per litter
- Soft tissue examinations: Yes
- Skeletal examinations: Yes:
- Head examinations: Yes - Statistics:
- The test parameters body weight, percent body weight change, feed consumption, prenatal data and foetal data will be analysed using statistical techniques like Bartlett’s test, ANOVA and Dunett’s and Student’s t tests. Foetal examination will be analysed using Chi-square test.
- Indices:
- No data available
- Historical control data:
- No data available
Results and discussion
Results: maternal animals
General toxicity (maternal animals)
- Clinical signs:
- not specified
- Dermal irritation (if dermal study):
- not specified
- Mortality:
- no mortality observed
- Description (incidence):
- There were no maternal death
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There was a significant reduction in the body weight gain during the treatment period in the high dose group (50 mg/kg).The reduction in body weight during the treatment period was considered treatment related.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- The food consumption was comparable to the vehicle control group.
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Neuropathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- not specified
Maternal developmental toxicity
- Number of abortions:
- effects observed, treatment-related
- Description (incidence and severity):
- One rabbit aborted in the 50mg/kg dose group
- Pre- and post-implantation loss:
- no effects observed
- Description (incidence and severity):
- The maternal data parameters comprising of pre and post-implantation loss in all the treatment groups were comparable to the vehicle control group
- Total litter losses by resorption:
- no effects observed
- Description (incidence and severity):
- The maternal data parameters comprising of early and late resorptions in all the treatment groups were comparable to the vehicle control group
- Early or late resorptions:
- no effects observed
- Description (incidence and severity):
- The maternal data parameters comprising of early and late resorptions in all the treatment groups were comparable to the vehicle control group
- Dead fetuses:
- not specified
- Changes in pregnancy duration:
- not specified
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Effects on pregnancy duration" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsMaternalAnimals.MaternalDevelopmentalToxicity.EffectsOnPregnancyDuration): not specified - Changes in number of pregnant:
- effects observed, treatment-related
- Description (incidence and severity):
- There were 2 non pregnant rabbits in control, 4 in low dose group, 3 in mid dose group and 4 in the high dose group. There was one complete resorption in mid dose group.
- Other effects:
- not specified
Effect levels (maternal animals)
- Dose descriptor:
- NOAEL
- Effect level:
- 10 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- changes in number of pregnant
- early or late resorptions
- food consumption and compound intake
- mortality
- number of abortions
- pre and post implantation loss
- total litter losses by resorption
- Remarks on result:
- other: No toxic effects observed
Maternal abnormalities
- Abnormalities:
- not specified
- Localisation:
- not specified
Results (fetuses)
- Fetal body weight changes:
- no effects observed
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Fetal/pup body weight changes" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsFetuses.FetalPupBodyWeightChanges): not specified - Reduction in number of live offspring:
- not specified
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- not specified
- Changes in postnatal survival:
- not specified
- External malformations:
- not specified
- Skeletal malformations:
- not specified
- Visceral malformations:
- not specified
- Other effects:
- not specified
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- not specified
- Basis for effect level:
- changes in sex ratio
- fetal/pup body weight changes
- Remarks on result:
- other: No developmental toxic effects observed
Fetal abnormalities
- Abnormalities:
- not specified
- Localisation:
- other: not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
- Treatment related:
- not specified
- Relation to maternal toxicity:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
Any other information on results incl. tables
Main parameters of pregnant rabbits treated with test material during organogenesis period
Group |
1 |
2 |
3 |
4 |
||
dose (mg/kg/d) |
0 |
3 |
10 |
50 |
||
Maternal observations |
||||||
Mortality
|
0/25 |
0/25
|
0/25 |
0/25 |
||
|
Day 0-6 |
6.80 |
8.06
|
8.85 |
6.44 |
|
Body weight gain (%) |
|
|
|
|||
Day 6-30 |
15.67 |
10.62 |
18.99 |
9.28* |
||
Day 0-30 |
20.55 |
17.54 |
25.32 |
14.74 |
||
No. of rabbits aborted |
0 |
0 |
0 |
1 |
||
No. of non pregnant rabbits |
2 |
4 |
3 |
4 |
||
No of pregnant rabbits |
23 |
21 |
22 |
20 |
||
Dams with complete resorptions |
0 |
1 |
0 |
0 |
||
Number of litter examined |
23 |
20 |
22 |
20 |
||
* : Significantly different from vehicle control at p≤0.05
Main parameters of pregnant rabbits treated with test material during organogenesis period
Group |
1 |
2 |
3 |
4 |
|
dose (mg/kg/d) |
0 |
3 |
10 |
50 |
|
Litter observations |
|
||||
Number of Corpora lutea |
8.43 |
8.24 |
8.77 |
6.70* |
|
Pre-implantation loss (%) |
9.00 |
11.33 |
6.37 |
19.43* |
|
Post-implantation loss (%) |
3.60 |
7.82 |
5.65 |
5.26 |
|
Early resorptions |
0.35 |
0.24 |
0.36 |
0.25 |
|
Late resorptions |
0.00 |
0.14 |
0.09 |
0.05 |
|
Mean litter size |
7.70 |
7.52 |
8.27 |
5.50** |
|
Fetus weight (g) |
Male |
44.03 |
43.15 |
41.83 |
43.27 |
Female |
42.28 |
40.82 |
42.10 |
42.85 |
|
Sex ratio- Male: Female |
1:1.85 |
1:1.30 |
1:1.15 |
1:1.00 |
* : Significantly different from vehicle control at p≤0.05
**: Significantly different from vehicle control at p≤0.01
Applicant's summary and conclusion
- Conclusions:
- No Observed Adverse Effect Level (NOAEL) for developmental toxicity was considered to be 50 mg/kg/day, When female rabbits were treated with test material orally.
- Executive summary:
The developmental toxicity study of test material was performed according toOECD guideline 414 on rabbits.Young adult nulliparous New-Zealand white strain female and male rabbits (Oryctolagus cuniculus) were used in study. The test material dissolved in 0.5% Carboxymethyl cellulose in dose concentration 0, 3, 10 and 50 mg/kg/day and adminstered by daily gavage through gestation day 6 to 28to mated females (25/dose group).The preliminary range-finding study (0, 10, 60 and 300 mg/kg/day) was performed,Based on preliminary range-finding study findings, 0, 3, 10 and 50 mg/kg/day were selected for the main study. Animals were observed twice daily for moribundity and mortality. Individual clinical signs were recorded at least once a day during the treatment period and once daily during the pre- and post-treatment periods. Individual body weights were recorded on gestation days 0, 3, 5, 8, 11, 14, 17, 20, 23, 26, 29 and 30. Food consumption per cage of animals were measured over the following periods during gestation: days 0-3, 3- 5, 5-8, 8-11, 11-14, 14-17, 17-20, 20-26, 26-29 and 29-30. On Day 29 of gestation, all the rabbits were sacrificed using intravenous injection of sodium thiopentone. Any gross pathological changes in all the visceral organs of dams were recorded. Organs with macroscopic findings and kidneys were preserved for possible histological evaluation. The ovaries, uteri and uterine contents were removed and examined to determine: the number of corpora lutea, the number of implantations, early and late resorptions, the weight of intact gravid uterus, the number and distribution of live foetuses, the number and distribution of intra-uterine dead foetuses, the individual foetal weight and sex, foetal abnormalities.
There were no maternal death or necropsy findings at any dose levels. There was a significant reduction in the body weight gain during the treatment period in the high dose group (50 mg/kg). The food consumption was comparable to the vehicle control grou. The reduction in body weight during the treatment period was considered treatment related. One rabbit aborted in the high dose group, there were 2 non pregnant rabbits in control, 4 in low dose group, 3 in mid dose group and 4 in the high dose group. There was one complete resorption in mid dose group. At the end, at least 20 litters were observed in each of the dose groups. The maternal data parameters comprising of implantations, early and late resorptions, pre and post-implantation loss in all the treatment groups were comparable to the vehicle control group. The mean number of corpora lutea, implantation and live foetus were significantly lower in high dose group (50 mg/kg body weight/day) when compared with the control group. Observed decrease in corpora lutea at 50 mg/kg body weight/day is considered as biological variation because the treatment was initiated after the implantation (gestation day 6). Therefore, the decrease observed in the absolute uterine weight, implantation and live foetus reported at this dose level are also considering as biological variation as these observations are directly correlated with the decrease in the number of the corpora lutea. Hence No Observed Adverse Effect Level (NOAEL) for developmental toxicity was considered to be 50 mg/kg/day,When female rabbits were treated with test material orally.
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