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EC number: 246-805-2 | CAS number: 25306-75-6
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11.06.2021 - 28.09.2021
72 hours - Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- Guideline study
It is accepted that the parent substance will have hydrolysed in the course of the testing, but OECD Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures (Guideline 23) was followed.
The method allows for pre-mixing hydrolytically unstable substances in water to mimic the release to the environment via waste-water systems.
Analysis for parent material not possible. - Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Sodium isobutyl xanthate (Sodium O-isobutyl dithiocarbonate);
batch no.: MK/01/04/2021,
the content of sodium O-isobutyldithiocarbonate: 94.0 ±1%;
manufacturing date: April 15,2021, expiry date: April 15, 2022. - Analytical monitoring:
- yes
- Details on sampling:
- At start and end of exposure period
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- The unicellular freshwater green algae, Raphidocelis
subcapitata (formerly Pseudokirchneriella subcapitata
(Korshikov) Hindák, Selenastrum capricornutum Prinz) SAG
61.81 cultivated at the Łukasiewicz Research Network –
Institute of Industrial Organic Chemistry Branch Pszczyna,
Ecotoxicology Research Group, Laboratory of Aquatic
Organisms Toxicology.
The algae were obtained from the Culture Collection of Algae at Göttingen University, Germany - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 22.0 – 23.1°C
- pH:
- 7.53 – 8.73
- Nominal and measured concentrations:
- 10, 3.13, 0.98, 0.31, 0.095 mg/L plus the control.
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.31 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- yield
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1.279 mg/L
- 95% CI:
- > 0.798 - < 2.002
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- yield
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.31 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.1 mg/L
- 95% CI:
- > 1.566 - < 2.971
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Validity criteria fulfilled:
- yes
- Executive summary:
The growth of the green algae Raphidocelis subcapitata SAG 61.81 (formerly Pseudokirchneriella subcapitata) exposed to the test item, Sodium isobutyl xanthate (Sodium O-isobutyl dithiocarbonate), was investigated during a 72-hour test.
The test was performed in glass flasks with a capacity of 250 mL containing 100 mL of either the test item concentration, or the control, per replicate. The initial density of the algae was 1 x 104 cells/mL.
The definitive test was performed with the following test item concentrations:
10, 3.13, 0.98, 0.31, 0.095 mg/L plus the control.
The number of algal cells was determined with an indirect method, which involves a spectrophotometric measurement of the absorbance of algal suspension at 670 nm and converting its value into the number of cells using a standard curve. The absorbance for each replicate of each test item concentration and the control were measured after 24, 48, and 72 h of exposure.
Calculated inhibition of growth rate for the test item concentrations ranging from 0.095 to 10 mg/L after 72 h of exposure was in the range of -0.5 – 86.1% when compared to the control. Inhibition of yield for the test item concentrations ranging from 0.095 to 10 mg/L after 72 h of exposure was in the range of -2.0 – 99.1% when compared to the control.
In all test item concentrations, no differences in shape, size and colour of algal cells were reported as compared to the algal cells in the control.
Morphology observations of the algae cells were performed at exposure termination. In the test item concentrations of 0.095, 0.031 and 0.98 mg/L, no differences in shape, size and colour of algal cells were reported as compared to the algae cells in the control. In the test item concentrations of 3.13 and 10 mg/L smaller algae cells were observed as compared to the algae cells in the control.
As hydrolysis would have occured and because a flow-through test is not possible to perform, it is accepted that the test material will quickly dissapear. Analysis by total organic carbon analyses was performed in fresh samples of all test item concentrations and the control at exposure initiation and in old samples of all test item concentrations and the control at exposure termination (72-h old). This analytical approach did not account for any degradation or metabolisation effects which may have occurred
during exposure. The results were corrected by the value determined for the control sample
in a series and presented as the concentrations of total organic carbon (TOC).
In samples collected at exposure initiation, the analysed total organic carbon concentrations were in the range of below the LoQ value (< 1.0 mg C/L) – 11.8 mg C/L.
In 48-h old samples collected at exposure termination, the analysed total organic carbon concentrations were in the range of below the LoQ value (< 1.0 mg C/L) – 11.8 mg C/L.The endpoint values were determined based on the nominal test item concentrations.
The endpoint values based on nominal test item concentration is given below:
The ErC50/72 h value is 2.145 mg/L (95% confidence interval: 1.566 – 2.971).
The LOEC/72 h value for growth rate is 0.98 mg/L.
The NOEC/72 h value for growth rate is 0.31 mg/L.The EyC50/72 h value is 1.279 mg/L (95% confidence interval: 0.798 – 2.002).
The LOEC/72 h value for yield is 0.98 mg/L.
The NOEC/72 h value for yield is 0.31 mg/L.
Reference
Description of key information
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 2.1 mg/L
Additional information
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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