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EC number: 208-655-6 | CAS number: 537-01-9
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Short-term toxicity to fish:
One study of reliability 1 according to Klimisch was available and was selected as a key study .
The acute toxicity of the test item, dicerium tricarbonate, to rainbow trout (Oncorhynchus mykiss) was determined in a 96-hour semi-static test with a daily test medium renewal according to the EU Commission Directive 92/69/EEC, Part C.1 (1992), and the OECD Guideline for Testing of Chemicals No. 203 (1992).Fish were exposed to control and test chemical at a loading rate of 100 mg/L for 96h. Mortality and visible abnormalities were observed daily. No mortality or other visible abnormalities were observed during the test.The 96-hour NOELR and the 96-hour LL50 of dicerium tricarbonate to rainbow trout were thus determined to be > 100 mg/. In conclusion, the test item dicerium tricarbonate had no acute toxic effects on rainbow trout up to the solubility limit in the test water, at the loading rate of 100 mg/L.
Short-term toxicity to aquatic invertebrates:
One study of reliability 1 according to Klimisch was available and was selected as a key study .
The 48hr-acute toxicity of cerium carbonate
to Daphnia magna was studied under static conditions according to the EU
Commission Directive 92/69/EEC, Part C.2 (1992) and the OECD Guideline
for Testing of Chemicals, N°202 (2004). Daphnids were exposed to control
and test chemical at nominal concentration of 100 mg of dry substance /L
(loading rate) for 48 hr. Mortality/immobilization were observed daily.
In the control and at the loading rate of 100 mg/L, no immobilized test
organisms were observed during the test period of 48 h. Thus, the 48
hour LL50 was > 100 mg/L and the 48h NOEC were >= 100 mg/L.
Long-term toxicity to aquatic invertebrates:
One study of reliability 1 according to Klimisch was available and was selected as a key study.
The effect of the test item, dicerium
tricarbonate, on the survival and reproduction of Daphnia magna was
investigated in a semi-static test over 21 days following the OECD
Guidelines for Testing of Chemicals, No. 211 (1998) and the EU
Commission Directive 92/69/EEC, C.20 (2001). Daphnids were exposed to
control, and test chemical at nominal concentration of 130 mg of dry
substance /L (loading rate) and the dilutions 1:3.2, 1:10, 1:32 and
1:100 of the saturated solution. The mortality and reproduction of the
daphnids were compared with the corresponding parameters in the control
and symptoms of toxicity were recorded. The test item, dicerium
tricarbonate, had no toxic effect on survival and reproduction of
Daphnia magna after the exposure period of 21 days up to the loading
rate of 130 mg/L. Thus, the NOELR of the test item was determined to be
at least the loading rate of 130 mg/L (100 mg/L, when corrected for the
water content of the test item). The LOELR was above the loading rate of
130 mg/L.
Toxicity to aquatic algae:
One study of reliability 1 according to Klimisch was available and was selected as a key study.
The influence of dicerium tricarbonate on the
growth of the green algal species Scenedesmus subspicatus was
investigated in a 72 -hour static test according to guidelines EU C.3
(1992) and OCDE 201 (2006). The GLP were stated. Algal suspensions were
exposed to the test item with a loading rate of 100 mg/L (corrected for
water content) and to dilutions 1:2, 1:4, 1:8, 1:16, 1:32. Additionally,
a control was tested in parallel.
The algal cell densities were counted daily, and inhibition of algal
growth was assessed.
The inhibition of algal growth observed only at the two highest
concentrations, i.e. 50 and 100 mg/L, was presumably caused by a
secondary effect, the complexation of the essential algal nutrient
phosphate by the test item. A statistically significant decrease of the
phosphate concentration was determined at the loading rates of 50 and
100 mg/L. Thus the growth inhibition determined at these loading rates
has probably been caused by depletion of phosphate in the test medium.
Toxicity to microorganisms:
One study of reliability 1 according to Klimisch was available and was selected as a key study.
The inhibitory effect of the test item dicerium tricarbonate on the respiration rate of aerobic wastewater microorganisms of activated sludge was investigated in a 3-hour respiration inhibition test according to the EU Commission Directive 88/302/EEC, Part C.11, and the OECD Guideline for Testing of Chemicals, No. 209.
In accordance with the EU Commission Directive 92/69/EEC (C.1, C.2, and C.3) and the OECD Series on Testing and Assessment No. 23 (Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures, 2000), a limit test was performed with one concentration of dicerium tricarbonate of nominal 1000 mg/L, to demonstrate that the test item has no toxic effect on activated sludge microorganisms up to and including this concentration.
In addition, two controls and three different concentrations of the reference item 3,5 dichlorophenol (5, 16, and 50 mg/L) were tested in parallel. The results of these reference treatments (EC50 = 12 mg/L within the guideline-recommended range of 5 - 30 mg/L) confirmed suitability of the activated sludge and the method used.
The test item, dicerium tricarbonate, had no significant inhibitory effect on the respiration rate of activated sludge after the incubation period of three hours at the limit test concentration of 1000 mg/L. Thus, the 3-hour NOEC of dicerium tricarbonate to activated sludge microorganisms was at the limit of water solubility of dicerium tricarbonate under the test conditions, or at 1000 mg/L. The 3-hour EC20, EC50 and EC80 were clearly higher than the limit of water solubility of dicerium tricarbonate under the test conditions, or higher than 1000 mg/L.
In summary, dicerium tricarbonate did not induce anyadverse effects up to its solubility limit into water.
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