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EC number: 207-838-8 | CAS number: 497-19-8
- 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 aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: United States Environmental Protection Age- ncy (1971) Algal Assay Procedure Bottle Test.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: U.S. Environmental Protection Agency(1978) The Selenastrum capricornutum Printz Alagal Assay Procedure Bottle Test, Experimental Design, Application and Data Interpretation
- Principles of method if other than guideline:
- investigated the effect of washing detergent on the growth of algae as a test organism. In particular, we compared the effects of detergents and their components (surfactants and auxiliaries) on algae.
- GLP compliance:
- no
- Analytical monitoring:
- no
- Details on test solutions:
- The test substance was added to the medium to prepare a test solution.
The initial pH of the test solution was adjusted to 7.4 ± 0.1 using 0.1 specified hydrochloric acid or 0,1 specified sodium hydroxide solution. - Test organisms (species):
- other: Selenastrum capricornotum, Mycrocystystis aeruginosa and Nitzschia fonticola
- Details on test organisms:
- - Culturing media and conditions: modified version of Hughes, Gorhamand Zehnderg) No. 11 culture medium.
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 72 h
- Test temperature:
- 24 ± 2 ° C
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 500 ml of triangularflasko, and silicosen 13 (Shinetsu Polymer Co., Ltd., Cap), place in a rotary shake that rotates 90 times per minute under a white fluorescent lamp (Sanline Ace, Nittate Seisakusho) that irradiates from the upper part.
- Initial cells density: The algae in the logarithmic growth phase in the preculture were concentrated by sedimentation (about 7,000 × 9,10 minutes) and diluted in a new culture, and used for the seeding of the test culture. The planting concentration was 0.7 ± 0.2 mg dry weight
- No. of vessels per concentration (replicates): 3
GROWTH MEDIUM
- Standard medium used: no
- Detailed composition if non-standard medium was used:
Compound Concentration (mg/L)
NaNO3 99.2
K2HPO4 7.8
MgSO4*7H2O 15
CaCl2*2H2O 7.2
Na2CO3 4
Na2SiO3*9H2O 11.6
Na2EDTA*2H2O 1
Citric acid 1.2
Fe citrate 1.
Gaffron’s micronutrients stock solution 0.08
EFFECT PARAMETERS MEASURED :
- Determination of cell concentrations: by the intensity of fluorescence emitted by chlorophyll (Model 10000R Firefly Luminometer, Turner Design) every 12 hours
- Chlorophyll measurement:
- Other:
TEST CONCENTRATIONS
- Spacing factor for test concentrations:
- Justification for using less concentrations than requested by guideline:
- Range finding study
- Test concentrations:
- Results used to determine the conditions for the definitive study:
CULTURING APPARATUS
-Details on culturing apparatus used: - Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 800 mg/L
- Nominal / measured:
- nominal
- Basis for effect:
- growth rate
- Conclusions:
- Exposure of three green algaaes for 72h to Na2CO3 resulted in a EC50 >800 mg/L based on the inihibition of the growth rate
- Executive summary:
A study was conducted exposing three different green-algae, Selenastrum capricornotum, Mycrocystystis aeruginosa and Nitzschia fonticola to sodium carbonate, chosen as builder in the formulations of laundry detergents.
Tests were conducted followinf the EPA (1971) Algal Assay Procedure Bottle test. Results showed an EC50 > 800 mg/l after 72 h of exposure.
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 2014
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Investigate the toxic effects of alkaline salt on algal photosynthesis, we used Na2CO3 to stress C. reinhardtii, a model organism of single cell, to determine the algal growth, ROS production, as well as changes of photosynthetic pigments and chlorophyll fluorescence
- GLP compliance:
- no
- Specific details on test material used for the study:
- no data
- Analytical monitoring:
- no
- Details on sampling:
- not applicable
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION: test item was added in the test culture at the desired concentration
- Test organisms (species):
- Chlamydomonas reinhardtii
- Details on test organisms:
- TEST ORGANISM
- Common name: single-cell green alga
- Strain: CC-125 wild type mt+ [137c]
- Source (laboratory, culture collection): Duke University, Durham, NC, USA
- Method of cultivation: grown in 25 mL liquid Tris-acetate- phosphate (TAP) medium (Na+ only 0.26 mM), put on a shaking table with 120 rpm, and kept at a light (16 h)/dark (8 h) regime at 23◦C, with an illumination of 100 μmol m-1 s-1. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 24 h
- Test temperature:
- 23 C
- pH:
- 7.9-10.5 depending on the exposure concentration
- Nominal and measured concentrations:
- 10 mM, 25 mM, 50 mM and 150 mM Na2CO3
- Details on test conditions:
- TEST SYSTEM
- Test vessel: suspended in 25 mL freshly prepared medium with different salt concentration
- Initial cells density: 6 × 106 cells/mL
- Control end cells density: around 10.5 × 106 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 3
GROWTH MEDIUM
- Standard medium used: liquid Tris-acetate- phosphate (TAP) medium (Na+ only 0.26 mM)
OTHER TEST CONDITIONS
- Photoperiod: 14 h light/8 h dark/2 h light
- Light intensity and quality: 100 μmol m-1 s-1
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: blood cell counting plate, with each value being the means of 6 repeats.
- Chlorophyll measurement: fluorescence
- Other: photosynthetic pigment - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 1 060 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Duration:
- 24 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 15 898.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Chlorophyll
- Duration:
- 12 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 5 300 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Phosynthetic activity Fv/Fm
- Details on results:
- Under Na2CO3 stress, the absorbance peaks were not markedly changed at 10 mM, but they were declined at 25 mM. In the treatment with 50 mM Na2CO3, the absorbance peak at 457 nm disappeared after 1 h, while a new peak at 416 nm appeared after 2 h. The shapes of peaks were significantly changed in the treatment with Na2CO3 at 150 mM, and new absorbance peaks at 416 nm, 443 nm and 640 nm were reduced gradually with prolonging the treatment time.
- Executive summary:
A study was conducted exposing the green algae, C. reinhardtii, for 24h to Na2CO3 at the concentration range of 10-150 mM. Results showed that cell density was significantly affected at the lowest concentration tested, determining a LOEC of 10 mM (1060 mg/L). Chlorophyll content was instead significantly decreased only at the highest concentration tested, determining a LOEC of 150 mM (15898.8 mg/l).
Referenceopen allclose all
Description of key information
The study does not need to be conducted as in the aquatic environment; sodium carbonate is dissociated into sodium and carbonate ions. Both ions originally exist in nature, and their concentrations in surface water are dependent on various factors, such as geological parameters, weathering and human activities. Therefore, there is a continuous source of both ions into the environment and have been measured extensively in aquatic ecosystems. Non-performance of an algal toxicity study was also accepted in earlier evaluation (OECD, 2002): since results can be predicted based on the increase of the pH of the test solution, the results will depend on the algal species selected, the composition of the test medium and probably the growth conditions before the start of the test. The results cannot be extrapolated directly to aquatic ecosystems because the growth conditions are in many cases not comparable to the laboratory conditions.
Two reliable studies are available (K2) exposing the green algaes to sodium carbonate.
One study (Zou, 2014) exposed the green algae, Chlamydomonas reinhardtii, for 24h to Na2CO3 at the concentration range of 10-150 mM. Results showed that cell density was significantly affected at the lowest concentration tested, determining a LOEC of 10 mM (1060 mg/L). Chlorophyll content was instead significantly decreased only at the highest concentration tested, determining a LOEC of 150 mM (15898.8 mg/l).
The second available reliable study (Yamane, 1984) was conducted exposing three different green-algae, Selenastrum capricornotum, Mycrocystystis aeruginosa and Nitzschia fonticola to sodium carbonate, chosen as builder in the formulations of laundry detergents. Tests were conducted following the EPA (1971) Algal Assay Procedure Bottle test. Results showed an EC50 > 800 mg/l after 72 h of exposure
Key value for chemical safety assessment
Additional information
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