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EC number: 237-623-4 | CAS number: 13870-28-5
- 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

Toxicity to reproduction
Administrative data
- Endpoint:
- multi-generation reproductive toxicity
- Remarks:
- based on test type (migrated information)
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-guideline study with survival of offspring and gross morphological changes as the only parameters examined. For justification of read across see endpoint summary.
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Effects of soluble silica on growth, nutrient balance and reproductive performance of albino rats.
- Author:
- Smith, G. S. et al.
- Year:
- 1 973
- Bibliographic source:
- J. Animal Sc. 36, 271-278
- Reference Type:
- secondary source
- Title:
- Unnamed
- Year:
- 2 004
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Non-guideline study with survival of offspring and gross morphological changes as the only parameters examined.
- GLP compliance:
- no
- Limit test:
- no
Test material
- Reference substance name:
- Silicic acid, sodium salt
- EC Number:
- 215-687-4
- EC Name:
- Silicic acid, sodium salt
- Cas Number:
- 1344-09-8
- IUPAC Name:
- sodium hydroxy(oxo)silanolate
- Details on test material:
- SOURCE: Diamond Alkali Company, Cleveland, Ohio, USA
PURITY: Not reported
IMPURITY/ADDITIVE/ETC.: Not reported
ANY OTHER INFORMATION: Molar ratio 3.2
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- All animals were maintained on a normal diet (which contained 0.1 to 1.0% of SiO2 (based on dry weight). Housing conditions of the animals were not optimal, so that even in the control group survival of offspring until weaning was poor (35%).
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Duration of treatment / exposure:
- Exposure period: 12 weeks, between weaning and sexual maturity, each generation F0, F1, F2, F3 & F4
Premating exposure period (males): 12 weeks
Premating exposure period (females): 12 weeks
Duration of test: 2.5 years - Frequency of treatment:
- continuous
Doses / concentrations
- Remarks:
- Doses / Concentrations:
79 and 159 mg sodium silicate/kg body weight/d
Basis:
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Rats were treated with 0, 600 and 1200 mg SiO2/l drinking water from weaning age (3 weeks) to maturity (4 months). Six males and six females were then mated in each treatment group. Offspring from the control group were distributed among all water treatments upon weaning (3 weeks of age) -nine additional males and nine additional females were thereby added to each treatment group- and upon attainment of maturity these rats were also mated within their treatment groups. This process whereby offspring from control groups were distributed among treatments was repeated three times during a period of 2.5 years, and the mating procedure was repeated at four separate phases during the overall study, thereby providing data from 77 matings involving 59 females for each of the three treatments in the overall study.
Examinations
- Parental animals: Observations and examinations:
- PARAMETERS ASSESSED DURING STUDY P AND F1:
- Clinical observations: Not executed
- Body weight: Not reported
- Mortality: Examined, but frequency of observations not specified. - Oestrous cyclicity (parental animals):
- - Estrous cycle: Not examined
- Sperm parameters (parental animals):
- - Sperm examination: Not executed
- Litter observations:
- OFFSPRING: Gross morphological anomalies, stillbirths
- Statistics:
- Chi-square Test
Results and discussion
Results: P0 (first parental generation)
Details on results (P0)
-Parental data and F1: No effects on mortality, the only parameter studied, were observed in the parental generation at any dose level. Reduced pup survival was observed in the treatment groups.
- Mortality: No effects on length of life of the rats receiving sodium silicate in drinking water after weaning. Offspring from the treatment groups was frequently stillborn or small and weak, with survival limited to only a few days. Cannibalism was prevalentamong females receiving sodium silicate, especially among those receiving 1200 ppm.
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Effect level:
- > 159 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- mortality
- Remarks on result:
- other: no mortality observed a the high dose
Results: F1 generation
Details on results (F1)
- Litter size and weights: On average 9.6, 6.8 and 8.4 animals/litter (at 0, 600 and 1200 mg SiO2/l). No data on body weights
- Viability index: see table below
- Post natal survival until weaning: 35%, 24% and 11% (at 0, 600 and 1200 mg SiO2/l)
- Effects on offspring: Necrosis of the tail and of the feet as well in both treated groups. Litters were frequently stillborn or small and weak.
Effect levels (F1)
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Sex:
- male/female
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
ACTUAL DOSE RECEIVED BY DOSE LEVEL BY SEX:
600 and 1200 mg SiO2/l in drinking water, corresponding to 790 ppm and 1580 ppm sodium silicate, respectively. This converts to 79 and 159 mg/kg bw/d on the assumption of a mean body weight of 200 g and a mean daily water consumption of 20 ml/d.
The results from the 4 consecutive breedings are reported in the publication as summed data only:
0 600 1200 ppm SiO2
-----------------------------------------------------------------
Number of matings 77 77 77
Number of litters 54 51 49
Total offspring born 517 346* 414*
Total offspring weaned 182 83* 44*
% of offspring weaned 35% 24% 11%
Difference, % of controls
born - 67% 80%
weaned - 46% 24%
-----------------------------------------------------------------
* Values differ from controls, P<0.001
Applicant's summary and conclusion
- Conclusions:
- In a 4-generation study, Smith et al. (1973) assessed the effect of sodium silicate administered via drinking water to rats. Due to the limitations of the study only a NOAEL for parentaral toxicity (> 159 mg/kg bw/day) can be derived. For the F1 generation no NOAEL was identified.
- Executive summary:
In a 4-generation study, Smith et al. (1973) assessed the effect of sodium silicate administered via drinking water to rats. The exposure concentration was 600 and 1200 mg SiO2/L, corresponding to 79 and 159 mg sodium silicate/kg bw/d from weaning until mating. Control groups received no sodium silicate in their drinking water. For 4 consecutive generations, the rats were mated and the total number of offspring analysed. No dose-related effect on litter number up to and including 159 mg/kg bw/d was observed. Survival of offspring until weaning was poor, even in the controls (35, 24, and 11 % at 0, 79, 159 mg/kg bw/d, respectively). The total number of offspring born was reduced to 67 % of the controls at 79 mg/kg bw/d and to 80 % at 159 mg/kg bw/d. Litters born to females receiving silicate were frequently stillborn or small and weak, with survival limited to only a few days. In addition, cannibalism was prevalent and necrosis of the tail and occasionally the feet was observed in offspring of silicate-treated animals. Due to the limitations of the study (also severe effects in control animals e.g. inter-current deaths, no dose-response relationship for total offspring born) makes it however difficult to draw any firm conclusions from this study. Thus a NOAEL can only be derived for parentaral toxicity (> 159 mg/kg bw/day). For the F1 generation no NOAEL was identified.
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