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EC number: 618-347-7 | CAS number: 9003-01-4
- 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

Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study conducted in compliance with GLP regulations.
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 983
- Report date:
- 1983
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 991
- Reference Type:
- secondary source
- Title:
- Chemical Hazards of the Workplace, Second Edition.
- Author:
- Proctor NH et al.
- Year:
- 1 988
- Bibliographic source:
- Science Information Resource Center, J. B. Lippincott Compagny
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Acrylic acid
- EC Number:
- 201-177-9
- EC Name:
- Acrylic acid
- Cas Number:
- 79-10-7
- Molecular formula:
- C3H4O2
- IUPAC Name:
- acrylic acid
- Details on test material:
- - Name of test material (as cited in study report): Acrylic acid, pure
- Analytical purity: 99.74%
- Impurities (identity and concentrations): Diacrylic acid 0.22%, Acetic acid 0.12%, Propionic acid 0.12%, the concentrations of other imputies were < 0.02%
- Test substance No.: 80/386
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Wiga GmbH, D-Sulzfeld
- Age at study initiation: 10 weeks old
- Weight at study initiation: mean weight 215 g
- Housing: Single in Makrolon/wire cages (type MD III supplied by Becker & Co., Castrop-Rauxel)
- Diet (ad libitum): SSNIFF R meal, Ssniff Versuchstierdiaeten GmbH, CH-Soest
- Water (ad libitum): Tap water
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2
- Humidity (%): 55 ± 5
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure (if applicable):
- whole body
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- Exposures were conducted using a continuous infusion pump (type Infu 362). Acrylic acid was metered into the inner coil of a glass evaporator heated by hot water. The acrylic acid vapours were diluted with a flow of fresh conditioned air with a flow meter. This mixture of acrylic acid vapour and air was passed through a glass cooler, thermostated cold water at 8-10°C being passed through its inner coil. The mixture of acrylic acid vapour and air was thus cooled to 23°C and passed to the exposure chambers (made of glass and steel, volume about 500 liters). The following amounts of test substance were used: 1.15 ml/h (study group 1, 40 ppm), 3.4 ml/h (study group 2, 120 ppm), 10.2 ml/h (study group 3, 360 ppm). The temperature in all exposure chambers was continuously monitored using NTC sensors and the measured values were recorded using a 12-channel printer.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The concentration of acrylic acid in the exposure chambers was determined using a continuously operating total hydrocarbons analyzer equipped with a flame ionization detector.
Nominal concentrations (ppm): 40.7, 120.3, 361
Analytical concentrations (ppm): 39.4, 114.0, 356.2 - Details on mating procedure:
- - Impregnation procedure: cohoused
- If cohoused:
- M/F ratio per cage: 1/1
- Length of cohabitation: 15.5 hours
- Verification of same strain and source of both sexes: yes
- Proof of pregnancy: sperm in vaginal smear referred to as day 0 of pregnancy - Duration of treatment / exposure:
- from day 6 to day 15 of gestation
- Frequency of treatment:
- 6 hours/day
- Duration of test:
- until day 20 of gestation
- No. of animals per sex per dose:
- 30
- Control animals:
- yes, sham-exposed
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: not specified
DETAILED CLINICAL OBSERVATIONS: Yes
Prior to the exposure period, animals were observed for clinical signs once daily. Preceding and following each exposure, individual does were observed for clinical signs of toxicity.
BODY WEIGHT: Yes
- Time schedule for examinations: On gestation day 0, 3, 6 9 12, 15, 18 and 20
FOOD CONSUMPTION: Yes
- The feed consumption by each animal was determined on gestation day 0, 3, 6 9 12, 15, 18 and 20
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day 20
- Organs examined: The uteri and ovaries were removed. The uteri were weighed. The number of corpora lutea, implantation sites for each hern of the uterus, dead and live implatations and fetuses were determined.
- 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 - Fetal examinations:
- Living fetuses were weighed, sexed, and examined for externally detectable changes. In addition, attention was paid to the viability of the fetuses, the length of the umbilical cord and the condition of the fetal membranes and amniotic fluid. One-third of the fetuses of each dam were fixed in Bouin's solution and examined for internal soft tissue changes. In order to assess the skeletal system, two-thirds of the living fetuses of each dam were initially fixed in 96% alcohol, then clarified with potassium hydroxide solution and stained with Alizarin red S. The fetuses were stored in 100% glycerol.
- External examinations: Yes: all per dam
- Soft tissue examinations: Yes: one-third per dam
- Skeletal examinations: Yes: two-thirds per dam - Statistics:
- Quantitative continuous random variables, eg. body weight data or food consumption data, were examined with the Williams test. Discrete random variables, eg. number of corpora lutea, number of implantations, or percentage values, such as live fetuses as a percentage of total implantations, fetuses with anomalies (or variations, retardations) as a percentage of total fetuses investigated, were examined with a linear rank test of Krauth. The Fisher test was used for the comparison of frequencies, eg. number of litters with anomalies (or variations, retardations) in relation to the number of litters investigated. All tests were performed with type I error of = 0.05 and = 0.01. The linear rank test and the Fisher test were carried out with a Bonferroni correction, but including additional information. If the Bonferroni corrected test did not show any significance for = 0.05, the comparison was calculated with uncorrected = 0.05. The linear rank test and the Fisher test were calculated by counting all possible permutations.
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Clinical signs:
No animal died in any group. Indications of a toxic effect on the dams emerged at 120 ppm (decreased consumption of feed during the exposure phase and a smaller difference between the body weight and uterus weight after necropsy). A marked toxicity on the pregnant animals was detected at 360 ppm (lower body weight, body weight gain slowed down, decreased consumption of feed, smaller difference between body weight and uterus weight, and clinical signs of an irritant effect caused by acrylic acid vapours).
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- 0.12 mg/L air (nominal)
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- LOAEC
- Effect level:
- 0.36 mg/L air (nominal)
- Basis for effect level:
- other: maternal toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
There were no signs of embryotoxicity, in particular no teratogenic effects.
Effect levels (fetuses)
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- >= 1.08 mg/L air (nominal)
- Basis for effect level:
- other: teratogenicity
- Dose descriptor:
- NOAEC
- Effect level:
- >= 1.08 mg/L air (nominal)
- Basis for effect level:
- other: fetotoxicity
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
EFFECTS OF EXPOSURES ON MATERIAL BODY WEIGHT AND UTERUS WEIGHT (g)
Concentration (ppm) |
0 |
40 |
120 |
360 |
|
Body weight |
Day 0 |
216 (9.4)a |
216 (11.4) |
214 (7.7) |
215 (9.9) |
Day 6 |
243 (10.1) |
243 (16.1) |
242 (9.5) |
242 (12.7) |
|
Day 15 |
288 (9.6) |
284 (19.2) |
280 (14.4) |
261 (16.3)** |
|
Day 20 |
354 (19.9) |
349 (33.3) |
346 (27.0) |
333 (26.1)** |
|
Uterus weight (Day 20) |
64 (18.8) |
66 (25.5) |
68 (23.6) |
65 (21.1) |
|
BWE-uterusb |
290 (12.0) |
283 (17.8) |
278 (16.6)** |
267 (13.4)** |
|
BWE-BWS-uterusc |
74 (11.5) |
67 (11.2)* |
65 (13.1)** |
52 (9.2)** |
aFigures in parentheses indicate standard deviations.
bBWE-uterus = body weight on Day 20 minus uterus weight.
cBWE-BWS-uterus = body weight gain between Day 0 and Day 20 minus uterus weight.
* p<0.05.
**p<0.01.
TERMINAL OBSERVATIONS AND GENERAL FETAL DATA
Concentration (ppm) |
0 |
40 |
120 |
360 |
Number of animals |
30 |
30 |
29 |
29 |
Number of dams |
25 |
27 |
26 |
25 |
Implantations |
12.96 |
12.48 |
12.46 |
12.40 |
Live fetuses |
11.92 |
11.81 |
11.88 |
11.68 |
Dead implantations |
1.04 |
0.67 |
0.58 |
0.72 |
Fetal numbers (male:female) |
145:153 |
140:179 |
149:160 |
133:159 |
Mean weight of live fetuses (g) |
3.51 |
3.64 |
3.73* |
3.77* |
Mean length of live fetuses (cm) |
3.28 |
3.30 |
3.36 |
3.36 |
Mean weight of placenta (g) |
0.50 |
0.55 |
0.52 |
0.48 |
* p<0.05.
FETAL FINDINGS
Concentration (ppm) |
0 |
40 |
120 |
360 |
Anomalies/Litters |
4 (16.0)m |
10 (37.04) |
3 (11.54) |
3 (13.04) |
Anomalies/Fetuses |
6 (1.69)n |
13 (4.76) |
3 (0.81) |
3 (1.06) |
Variations/Litters |
12 (48.00) |
17 (62.96) |
10 (38.46) |
8 (34.78) |
Variations/Fetuses |
20 (8.04) |
36 (11.09) |
17 (5.27) |
10 (4.36) |
Retardations/Litters |
24 (96.00) |
24 (88.89) |
23 (88.46) |
21 (91.30) |
Retardations/fetuses |
114 (35.53) |
95 (32.10) |
104 (30.63) |
89 (32.61) |
mFigures in parentheses show percentage of fetuses examined that were affected per litter.
nFigures in parentheses show percentage of fetuses examined that were affected.
Applicant's summary and conclusion
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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