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EC number: 231-900-3 | CAS number: 7778-18-9
- 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:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study is well documented and comparabale to a guideline but not performed to GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 974
- Report date:
- 1974
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- no
- Remarks:
- Predates GLP
- Limit test:
- no
Test material
- Reference substance name:
- Calcium sulfate
- EC Number:
- 231-900-3
- EC Name:
- Calcium sulfate
- Cas Number:
- 7778-18-9
- Molecular formula:
- CaSO4
- IUPAC Name:
- calcium sulfate
- Details on test material:
- - Name of test material (as cited in study report): Calcium sulfate
- Physical state: Solid (white powder)
Constituent 1
Test animals
- Species:
- other: mice, rats and rabbits
- Strain:
- other: Albino CD-1 outbred mice; Wistar derived albino rats; Dutch-belted rabbits
- Details on test animals or test system and environmental conditions:
- Mice:
Adult virgin mice were gang-housed in disposable plastic cages in temperature and humidty controlled quarters with free access to food and fresh tap water.
Rats:
Adult virgin rats were individually housed in mesh bottom cages in temperature and humidity-controlled quarters with free access to food and fresh tap water.
Rabbits:
Adult virgin rabbits were individually housed in mesh bottom cages in temperature and humidity-controlled quarters with free access to food and fresh tap water.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Details on exposure:
- Mice: beginning on Day 6 and continuing daily through Day 15 of gestation the females were dosed with the indicated doses.
Rats: beginning on Day 6 and continuing daily through Day 15 of gestation the females were dosed with the indicated doses.
Rabbits: beginning on Day 6 and continuing daily through Day 18 the females were dosed. - Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- None specified
- Details on mating procedure:
- Mice: mated with young adult males, and observation of the vaginal sperm plug was considered Day 0 of gestation.
Rats: mated with young adult males, and observation of the vaginal sperm plug was considered Day 0 of gestation.
Rabbits: On Day 0, each doe was given an injection of 0.4 mL of human chorionic gonadotrophin (400 IU) via the marginal ear vein. Three hours later, each doe was inseminated artificially with 0.3 mL of diluted semen from a proven donor buck using approximately 20E+06 motile sperm according to the procedure described by Vogin et al. - Duration of treatment / exposure:
- Mice: 10 days
Rats: 10 days
Rabbits: 13 days - Frequency of treatment:
- Daily
- Duration of test:
- Mice: 17 days
Rats: 20 days
Rabbits: 29 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 16 mg/kg bw/day
- Remarks:
- Species: mice, rats, rabbits
- Dose / conc.:
- 74.3 mg/kg bw/day
- Remarks:
- Species: mice, rats, rabbits
- Dose / conc.:
- 345 mg/kg bw/day
- Remarks:
- Species: mice, rats, rabbits
- Dose / conc.:
- 1 600 mg/kg bw/day
- Remarks:
- Species: mice, rats, rabbits
- No. of animals per sex per dose:
- Mice: Mated animals 24-30
Rats: Mated animals 25
Rabbits: Mated animals 20-22
Refer to tables 3 (mice) table 4 (rats) and table 5 (rabbits) - Control animals:
- yes, sham-exposed
- other: Asprin was used as the positive control in mice at a dose of 150 mg/kg and in rats at a dose of 250 mg/kg ... (see attached file)
- Details on study design:
- None specified
Examinations
- Maternal examinations:
- Mice:
Body weights were recorded on Days 0, 6, 11, 15 and 17 of gestation.
All animals were observed daily for appearance and behaviour with particular attention to food consumption and weight in order to rule out any abnormalities which may have occurred as a result of anorexic effects in the pregnant female animal. The urogenital tract of each dam was examined in detail for anatomical abnormality.
Rats:
Body weights were recorded on Days 0, 6, 11, 15 and 20 of gestation.
All animals were observed daily for appearance and behaviour with particular attention to food consumption and weight in order to rule out any abnormalities which may have occurred as a result of anorexic effects in the pregnant female animal. The urogenital tract of each dam was examined in detail for anatomical abnormality.
Rabbits:
Body weights were recorded on Days 0, 6, 12, 18 and 29 of gestation.
All animals were observed daily for appearance and behaviour with particular attention to food consumption and weight in order to rule out any abnormalities which may have occurred as a result of anorexic effects in the pregnant female animal. The urogenital tract of each dam was examined in detail for anatomical abnormality. - Ovaries and uterine content:
- Mice:
Number of implanation sites, resorption sites and live and dead foetuses were recorded.
Rats:
Number of implanation sites, resorption sites and live and dead foetuses were recorded.
Rabbits:
The number of corpora lutea, implanation sites, resorption sites and live and dead foetuses were recorded. - Fetal examinations:
- Mice:
Body weights of live pups were recorded. All foetuses were examined for the presence of external congenital abnormalities. One third of the foetuses for each litter underwent detailed visceral examinations employing the Wilson technique. The remaining two-thirds were cleared in potassium hydroxide (KOH), stained with alizarin red S dye and examined for skeletal defects.
Rats:
Body weights of live pups were recorded. All foetuses were examined for the presence of external congenital abnormalities. One third of the foetuses for each litter underwent detailed visceral examinations employing the Wilson technique. The remaining two-thirds were cleared in potassium hydroxide (KOH), stained with alizarin red S dye and examined for skeletal defects.
Rabbits:
Body weights of live pups were recorded. All foetuses were examined for the presence of external congenital abnormalities. The live foetuses of each litter were then placed in an incubator for 24 h for the evaluation of neonatal survival. All surviving pups were sacrificed and all pups were examined for visceral abnormalities by dissection. All foetuses were then cleared in potassium hydroxide (KOH), stained with alizarin red S dye and examined for skeletal defects. - Statistics:
- None specified
- Indices:
- None specified
- Historical control data:
- None specified
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
Not applicable
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- Mice
- Effect level:
- 1 600 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: no clearly discernable effects on nidation or on maternal or foetal survival.
- Dose descriptor:
- NOAEL
- Remarks:
- Rats
- Effect level:
- 1 600 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: no clearly discernable effects on nidation or on maternal or foetal survival.
- Dose descriptor:
- NOAEL
- Remarks:
- Rabbits
- Effect level:
- 1 600 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: no clearly discernable effects on nidation or on maternal or foetal survival.
Maternal abnormalities
- Abnormalities:
- no effects observed
Results (fetuses)
- Reduction in number of live offspring:
- no effects observed
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- no effects observed
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
Not applicable
Effect levels (fetuses)
- Dose descriptor:
- NOAEL
- Effect level:
- 1 600 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- not specified
- Basis for effect level:
- other: no clearly discernable effects on nidation or on maternal or foetal survival. The number of abnormalities seen in either soft or skeletal tissues of the test groups did not differ from the number occurring spontaneously in the sham-treated controls.
Fetal abnormalities
- Abnormalities:
- no effects observed
Overall developmental toxicity
- Developmental effects observed:
- no
Any other information on results incl. tables
Table 6: Fate summary for mice:
Group |
Material |
Dose** |
Total |
Surviving at term |
||
Mated |
Pregnant |
Total |
Pregnant1 |
|||
341 |
Sham |
0.0 |
25 |
22 |
25 |
22 |
342 |
Aspirin |
150.0 |
25 |
19 |
25 |
19 |
343 |
FDA71 - 86 |
16.0 |
28 |
22 |
28 |
22 |
344 |
FDA71 – 86 |
74.3 |
24 |
22 |
24 |
22 |
345 |
FDA71 – 86 |
345.0 |
25 |
24 |
25 |
24 |
346 |
FDA71 - 86 |
1600.0 |
30 |
23 |
29 |
22 |
* positive control: 150 mg/kg
** administered as a water solution (10 mL per kg of body weight)
1) includes all dams examined at term
Table 7: Reproduction data for mice:
Group |
341 |
342 |
343 |
344 |
345 |
346 |
Dose (mg/kg) |
Sham |
Aspirin** |
16.0 |
74.3 |
345.0 |
1600.0 |
Pregnancies |
||||||
Total No. |
22 |
19 |
22 |
22 |
24 |
23 |
Died or aborted (before Day 17) |
0 |
0 |
0 |
0 |
0 |
1 |
To term (on Day 17) |
22 |
19 |
22 |
22 |
24 |
22 |
Live litters |
||||||
Total No.* |
21 |
19 |
22 |
21 |
24 |
21 |
Implant sites |
||||||
Total No. |
251 |
240 |
263 |
283 |
265 |
267 |
Average/dam* |
11.4 |
12.6 |
12.0 |
12.9 |
11.0 |
12.1 |
Resorptions |
||||||
Total No. * |
19 |
8 |
5 |
12 |
21 |
14 |
Dams with 1 or more sites resorbed |
6 |
5 |
4 |
2 |
9 |
7 |
Dams with all sites resorbed |
1 |
- |
- |
1 |
- |
1 |
Percent partial resorptions |
27.3 |
26.3 |
18.2 |
9.09 |
37.5 |
31.8 |
Percent complete resorptions |
4.55 |
- |
- |
4.55 |
- |
4.55 |
Live foetuses |
||||||
Total No. |
229 |
224 |
255 |
268 |
243 |
250 |
Average/dam* |
10.4 |
11.8 |
11.6 |
12.2 |
10.1 |
11.4 |
Sex ratio (M/F) |
1.16 |
1.07 |
0.90 |
1.00 |
0.94 |
1.02 |
Dead foetuses |
||||||
Total* |
3 |
8 |
3 |
3 |
1 |
3 |
Dams with 1 or more dead |
2 |
6 |
2 |
3 |
1 |
3 |
Dams with all dead |
- |
- |
- |
- |
- |
- |
Percent partial dead |
9.09 |
31.6 |
9.09 |
13.6 |
4.17 |
13.6 |
Percent all dead |
- |
- |
- |
- |
- |
- |
Average Foetus weight, g. |
0.89 |
0.87 |
0.86 |
0.87 |
0.91 |
0.88 |
* includes only those dams examined at term
** positive control, 150.0 mg/kg
Table 8: Fate summary for rats:
Group |
Material |
Dose** |
Total |
Surviving at term |
||
Mated |
Pregnant |
Total |
Pregnant1 |
|||
341 |
Sham |
0.0 |
25 |
25 |
25 |
25 |
342 |
Aspirin |
250.0 |
25 |
23 |
25 |
23 |
343 |
FDA71 - 86 |
16.0 |
25 |
21 |
25 |
21 |
344 |
FDA71 – 86 |
74.3 |
25 |
23 |
25 |
23 |
345 |
FDA71 – 86 |
345.0 |
25 |
23 |
25 |
23 |
346 |
FDA71 - 86 |
1600.0 |
25 |
21 |
25 |
21 |
* positive control 250 mg/kg
** administered as a water solution
1) includes all dams examined at term
Table 9: Reproduction data for rats.
Group |
341 |
342 |
343 |
344 |
345 |
346 |
Dose |
Sham |
Aspirin** |
16.0 |
74.3 |
345.0 |
1600.0 |
Pregnancies |
||||||
Total No. |
25 |
23 |
21 |
23 |
23 |
21 |
Died or aborted (before Day 20) |
0 |
0 |
0 |
0 |
0 |
0 |
To term (on Day 20) |
25 |
23 |
21 |
23 |
23 |
21 |
Live litters |
||||||
Total No.* |
25 |
18 |
21 |
23 |
23 |
21 |
Implant sites |
||||||
Total No. |
279 |
231 |
229 |
270 |
253 |
233 |
Average/dam* |
11.2 |
10.0 |
10.9 |
11.7 |
11.0 |
11.1 |
Resorptions |
||||||
Total No. * |
4 |
62 |
4 |
7 |
7 |
4 |
Dams with 1 or more sites resorbed |
3 |
11 |
3 |
3 |
2 |
3 |
Dams with all sites resorbed |
- |
4 |
- |
- |
- |
- |
Percent partial resorptions |
12.0 |
47.8 |
14.3 |
13.0 |
8.70 |
14.3 |
Percent complete resorptions |
- |
17.4 |
- |
- |
- |
- |
Live foetuses |
||||||
Total No. |
275 |
168 |
224 |
263 |
246 |
229 |
Average/dam* |
11.0 |
7.30 |
10.7 |
11.4 |
10.7 |
10.9 |
Sex ratio (M/F) |
1.07 |
1.06 |
0.87 |
1.07 |
1.18 |
0.75 |
Dead foetuses |
||||||
Total* |
- |
1 |
1 |
- |
- |
- |
Dams with 1 or more dead |
- |
1 |
1 |
- |
- |
- |
Dams with all dead |
- |
1 |
- |
- |
- |
- |
Percent partial dead |
- |
4.35 |
4.76 |
- |
- |
- |
Percent all dead |
- |
4.35 |
- |
- |
- |
- |
Average Foetus weight, g. |
3.68 |
2.39 |
3.92 |
3.94 |
3.77 |
4.04 |
* includes only those dams examined at term
** positive control: 250 mg/kg
Table 10: Fate summary for rats
Group |
Material |
Dose** mg/kg |
Total |
Surviving at term |
||
Mated |
Pregnant |
Total |
Pregnant1 |
|||
341 |
Sham |
0.0 |
18 |
13 |
18 |
13 |
342 |
6-AN* |
2.5 |
20 |
10 |
19 |
10 |
343 |
FDA71 - 86 |
16.0 |
22 |
14 |
19 |
11 |
344 |
FDA71 - 86 |
74.3 |
22 |
13 |
21 |
13 |
345 |
FDA71 - 86 |
345.0 |
20 |
13 |
19 |
12 |
346 |
FDA71 - 86 |
1600.0 |
20 |
14 |
15 |
11 |
* positive contorl: 2.5 mg/kg of 6 aminonicotinamide dosed on Day 9
** administered as a water solution.
1) includes all dams examined at term.
Table 11: Reproduction data for rabbits
Group |
341 |
342 |
343 |
344 |
345 |
346 |
Dose |
Sham |
6-AN** |
16.0 |
74.3 |
345.0 |
1600.0 |
Pregnancies |
||||||
Total No. |
13 |
10 |
14 |
13 |
13 |
14 |
Died or aborted (before Day 29) |
0 |
1 |
3 |
0 |
1 |
3 |
To term (on Day 29) |
13 |
10 |
11 |
13 |
12 |
11 |
Corpora lutea |
||||||
Total No. |
174 |
122 |
195 |
173 |
134 |
139 |
Average/dam mated |
9.67 |
6.42 |
9.29 |
8.65 |
7.05 |
7.72 |
Live litters |
||||||
Total No. |
12 |
10 |
11 |
13 |
10 |
10 |
Implant sites |
||||||
Total No. |
69 |
56 |
60 |
70 |
68 |
62 |
Average/dam |
5.31 |
5.60 |
5.45 |
5.38 |
5.67 |
5.64 |
Resorptions |
||||||
Total No.* |
4 |
2 |
4 |
7 |
9 |
4 |
Dams with 1 or more sites resorbed |
3 |
1 |
3 |
3 |
6 |
1 |
Dams with all sites resorbed |
1 |
- |
- |
- |
2 |
1 |
Percent partial resorptions |
23.1 |
10.0 |
27.3 |
23.1 |
50.0 |
9.09 |
Percent complete resorptions |
7.69 |
- |
- |
- |
16.7 |
9.09 |
Live foetuses |
||||||
Total No.* |
65 |
54 |
56 |
63 |
59 |
58 |
Average/dam |
5.00 |
5.40 |
5.09 |
4.85 |
4.92 |
5.27 |
Sex ratio (M/F) |
0.86 |
0.74 |
1.33 |
1.30 |
1.36 |
1.42 |
Dead foetuses |
||||||
Total No.* |
- |
- |
- |
- |
- |
- |
Dams with 1 or more dead |
- |
- |
- |
- |
- |
- |
Dams with all dead |
- |
- |
- |
- |
- |
- |
Percent partial dead |
- |
- |
- |
- |
- |
- |
Percent all dead |
- |
- |
- |
- |
- |
- |
Average foetus weight |
38.2 |
33.8 |
37.8 |
38.2 |
39.9 |
42.4 |
* included only those dams examined at term
** positive control: 2.5 mg/kg of 6-aminonicotinamide dosed on Day 9
Applicant's summary and conclusion
- Conclusions:
- Mice:
Administration of up to 1600 mg/kg (body weight) of the test material to pregnant mice for 10 consecutive days had no clearly discernable effects on nidation or on maternal or foetal survival.
Rats:
The administration of up to 1600 mg/kg (body weight) of the test material to pregnant rats for 10 consecutive days had no clearly discernable effects on nidation or on maternal or foetal survival.
Rabbits:
up to 1600 mg/kg (body weight) of the test material to pregnant rabbits for 13 consecutive days had no clearly discernable effects on nidation or on maternal or foetal survival.
All species: The number of abnormalities seen in either soft or skeletal tissues of the test groups did not differ from the number occurring spontaneously in the sham-treated controls.
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