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Diss Factsheets
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EC number: 953-513-5 | CAS number: -
- 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:
- November 2020 to May 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Batch Number CH-DA-01-18
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
In order to determine an appropriate test preparation method, an assessment was made of the material's behaviour in deionised water. A 1000 mg/L stock was prepared in deionised water and the resulting mixture was then stirred for one hour, left to settle for a further hour and its behaviour assessed. As the material was observed to be poorly soluble, it was stirred again for approximately 19 hours, left to settle for a further hour and its behaviour was reassessed.
The material was observed to be poorly soluble so was prepared by Water Accommodated Fractions (WAF). Test material stocks were individually prepared by weighing out an appropriate amount of test material, adding UD EPA culture medium and stirring for approximately 20 hours. The stocks were then left to settle for 1 our and the mid column stock was siphoned off, taking care to avoid siphoning of any undissolved material. Test material stocks were prepared for the range finding test. - Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
-Strain: 278/4
-Source (laboratory, culture collection): SAMS Limited
-Method of cultivation: Pre-cultures in the exponential growth phase were then prepared from stock laboratory cultures by inoculating autoclaved freshwater at 120 oC for 15 minutes with nutrient medium 2 to 4 days before test commencement. The pre-culture flasks were incubated at approximately 21-24 oC under constant illumination and were used as the inoculum source for subsequent toxicity tests. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 21-24 +/- 2 oC
- pH:
- 7.5 +/- 0.1
- Nominal and measured concentrations:
- 1, 3.2, 10, 32, 100, 320 and 1000 mg/L
- Details on test conditions:
- TEST SYSTEM
-Test vessel: 100 mL borosilicate glass conical flasks
-Material, size, headspace, fill volume: 50 mL of test medium
-Initial cells density: 5 x 10^3 cells per millilitre
-No. vessels per concentration (replicates): 3
-No. vessels per control (replicates): 6
GROWTH MEDIUM
-Standard medium used
TEST MEDIUM / WATER PARAMETERS
-Source/preparation of dilution water: Purified water treated by reverse osmosis followed by electro-deionisation
OTHER TESTS CONDITIONS
-Adjusment of pH: pH of the culture medium was adjusted, if required, by adding 1M HCl or NaOH to give a pH of 7.5 +/- 0.1.
-Photoperiod: Continuous
-Light intensity and quality: Light intensity values (4440 to 8880 Ix) were measured daily during the test.
EFFECT PARAMETERS MEASURED
-Determination of cell concentrations: Fluorimeter; haemocytometer, Sedgewick-Rafter chamber
TEST CONCENTRATIONS
-Range finding study
-Test concentration 1, 10, 100 and 1000 mg/L
-Results used to determine the conditions for the definitive study. - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 51.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 70.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 173 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- Exponential growth was observed in the control for the algal test. No abnormalities were reported and no observations were noted that may have caused a difference between the measured and nominal values. The effect concentrations did not exceed the solubility of the substance in the test medium.
- Results with reference substance (positive control):
- The results for the reference substance are valid with an EC50 of 1.7 after 72 hours.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Dihydronepetalactone exhibited a 72h EC(r)50 value of 51.2 mg/L.
- Executive summary:
A short-term toxicity study to determine the aquatic toxicity of dihydronepetalactone to freshwater unicellular algae (Pseudokirchneriella subcapitata) was determined by a GLP compliant study performed in accordance with OECD 201 test guideline.
In order to determine the concentrations to be used in the definitive test a range finding study was performed over 72h to determine the appropriate concentrations at which growth rate effects were observed was conducted. Dihydronepetalactone was characterised as poorly water soluble and was therefore prepared by Water Accommodated Fractions (WAF).
The concentration range used in the definitive study was 1, 3.2, 10, 32, 100, 320 and 1000 mg/L.
The 72h EC50 for dihydronepetalactone was 51.2 mg/L.
Reference
Description of key information
A short-term toxicity study to determine the aquatic toxicity of dihydronepetalactone to freshwater unicellular algae (Pseudokirchneriella subcapitata) was determined by a GLP compliant study performed in accordance with OECD 201 test guideline.
In order to determine the concentrations to be used in the definitive test a range finding study was performed over 72h to determine the appropriate concentrations at which growth rate effects were observed was conducted. Dihydronepetalactone was characterised as poorly water soluble and was therefore prepared by Water Accommodated Fractions (WAF).
The concentration range used in the definitive study was 1, 3.2, 10, 32, 100, 320 and 1000 mg/L.
The 72h EC50 for dihydronepetalactone was 51.2 mg/L.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 51.2 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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