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EC number: 222-619-7 | CAS number: 3558-60-9
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- for read across
- Justification for type of information:
- Data for the target chemical is summarized based on the structurally similar read across chemicals
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Qualifier:
- according to guideline
- Guideline:
- other: Scenedesmus cell proliferation inhibition test, DIN 38412 part 9, Determination of the inhibitory effect of water constituents green algae
- Qualifier:
- according to guideline
- Guideline:
- other:
- Version / remarks:
- The objctive of the study was to determine effective concentration of test chemical on aquatic algae.
- Principles of method if other than guideline:
- WoE report is based on two toxicity studies on aquatic algae of the test chemical :
WoE-1 & WoE- 2 - GLP compliance:
- not specified
- Analytical monitoring:
- no
- Test organisms (species):
- other: 2: Scenedesmus subspicatus
- Details on test organisms:
- 2:
- Common name: green algae
- Source (laboratory, culture collection): BASF AG Ludwigshafen - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 72 h
- Reference substance (positive control):
- not specified
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 300 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 2
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 490 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 2
- Duration:
- 72 h
- Dose descriptor:
- EC90
- Effect conc.:
- 790 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 2
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 162 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 3
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Study was conducted to determine effect of test chemical on Scenedesmus subspicatus. For the test chemical, based on effect on growth rate of the test organism green algae, the 72 hr EC10, EC50 and EC90 was determined to be 300,490 and 790 mgIL respectively and 96 h EC50 was 162 mg/l.
- Executive summary:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the toxicity of aquatic algae of the test chemical .The studies are as mentioned below:
In first study,toxicity to green algae was carried out according to Scenedesmus cell proliferation inhibition test, DIN 38412 part 9, Determination of the inhibitory effect of water constituents green algae
out for assessing the effect of the test chemical. The study was conducted for 72 hrs on test organism Scenedesmus subspicatus. Thus, based on effect on growth rate of the test organism green algae, the 72 hr EC10, EC50 and EC90 was determined to be 300,490 and 790 mgIL respectively and therefore chemical can be considered as non-toxic to aquatic algae and can be considered to be ‘’not classified’’ as per CLP classification criteria.
In last study, toxicity to green algae was carried out for assessing the effect of the test chemical. The study was conducted for 96hrs. On the basis of growth rate, the median effect concentration (EC50) was determined to be 162 mg/l. Thus, based on the growth rate effect with EC50 value , chemical can be considered as non-toxic to aquatic algae and can be considered to be ‘’not classified’’ as per CLP classification criteria.
Based on the EC50 values , it can be concluded that the chemical was not toxic and can be consider to be not classified as per the CLP classification criteria.
Reference
Description of key information
Study was conducted to determine effect of test chemical on Scenedesmus subspicatus. For the test chemical, based on effect on growth rate of the test organism green algae, the 72 hr EC10, EC50 and EC90 was determined to be 300,490 and 790 mgIL respectively and 96 h EC50 was 162 mg/l.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 490 mg/L
Additional information
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the toxicity of aquatic algae of the test chemical .The studies are as mentioned below:
In first study,toxicity to green algae was carried out according to Scenedesmus cell proliferation inhibition test, DIN 38412 part 9, Determination of the inhibitory effect of water constituents green algae
out for assessing the effect of the test chemical. The study was conducted for 72 hrs on test organism Scenedesmus subspicatus. Thus, based on effect on growth rate of the test organism green algae, the 72 hr EC10, EC50 and EC90 was determined to be 300,490 and 790 mgIL respectively and therefore chemical can be considered as non-toxic to aquatic algae and can be considered to be ‘’not classified’’ as per CLP classification criteria.
In last study, toxicity to green algae was carried out for assessing the effect of the test chemical. The study was conducted for 96hrs. On the basis of growth rate, the median effect concentration (EC50) was determined to be 162 mg/l. Thus, based on the growth rate effect with EC50 value , chemical can be considered as non-toxic to aquatic algae and can be considered to be ‘’not classified’’ as per CLP classification criteria.
Based on the EC50 values , it can be concluded that the chemical was not toxic and can be consider to be not classified as per the CLP classification criteria.
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