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EC number: 423-630-1 | CAS number: 62435-71-6
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The work described was performed in compliance with UK GLP standards (Schedule 1, Good Laboratory Practice Regulations 1997 (SI 1997/654)). These Regulations are in accordance with GLP standards published as OECD Principles on Good Laboratory Practice (revised 1997, ENV/MC/CHEM(98)17); and are in accordance with, and implement, the requirements of Directives 87/18/EEC and 88/320/EEC.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- GLP compliance:
- yes (incl. QA statement)
- Details on test solutions:
- For the purpose of the definitive study the test material was prepared by a direct solution in water.
An amount of test material (200 mg) was dissolved in reconstituted water and the volume adjusted to 2 litres to give the 100mg/l test concentration.
The concentration and stability of the test material in the test solutions were verified by chemical analysis at 0 and 48 hours. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- - Common name: Daphnia Magna
- Source: Maintained in a laboratory culture originating from a strain supplied by the Institut National de Recherche Chimique Appliquee (IRCHA), France - Total exposure duration:
- 48 h
- Test temperature:
- Maintained at 21°C throughout the study.
- pH:
- - 7.7 - 7.8
- No treatment related differences for pH were observed throughout the study.
- pH were recorded at the start and termination of the study. - Dissolved oxygen:
- - 8.1 - 8.4
- No treatment related differences for oxygen concentraion were observed throughout the study.
- Dissolved oxygen concentrations were recorded at the start and termination of the study. - Nominal and measured concentrations:
- Water temperature was recorded daily throughout the study.
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- >= 100 mg/L
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Conc. based on:
- test mat. (dissolved fraction)
- Basis for effect:
- mobility
- Conclusions:
- The acute toxicity of the test material to the freshwater invertebrate Daphnia magna has been invesitgated and gave a 48-Hour EC50 of greater than 100 mg/l. Correspondingly the No Observed Effect Concentration was equal to 100 mg/l.
Reference
RESULTS
Range-finding Study
Cumulative immobilisation data from the exposure of Daphnia magna to the test material during the range-finding study are given in Table 1.
Table 1: CUMULATIVE IMMOBILISATION DATA IN THE RANGE-FINDING STUDY
Nominal concentration (mg/l) | Cumulative immobilised Daphnia (initial population: 10 per replicate) | |
24 hours | 48 hours | |
Control | 0 | 0 |
1.0 | 0 | 0 |
10 | 0 | 0 |
100 | 0 | 0 |
No immobilisation was observed at the test concentrations of 1.0, 10 and 100 mg/l.
Based on this information, a single test concentration of four replicates, of 100 mg.l was selected for the definitive study. This experimental design conforms to a "Limit test" to confirm that at the maximum test concentration given in the OECD/EEC guidelines no immobilisation or adverse reactons to exposure were observed.
Definitive Study
>Immobilisation data: Cumulative immobilisation data from the exposure of Daphnia magna to Ethyl tetrahydrofurfuryl ether during the definitive study are given in Table 2.
Table 2: CUMULATIVE IMMOBILSATION DATA IN THE DEFINTIVE STUDY
Nominal concentration (mg/l) | Cumulative immobilised Daphnia (initial population: 10 per replicate) | |||||
24 hours | 48 hours | |||||
No. per replicate | Total | % | No. per replicate | Total | % | |
Control R1 | 0 | 0 | 0 | 0 | 0 | 0 |
Control R2 | 0 | 0 | 0 | 0 | 0 | 0 |
100 R1 | 0 | 0 | 0 | 0 | 0 | 0 |
100 R2 | 0 | 0 | 0 | 0 | 0 | 0 |
100 R3 | 0 | 0 | 0 | 0 | 0 | 0 |
100 R4 | 0 | 0 | 0 | 0 | 0 | 0 |
R1 - R4 = Replicates 1 -4
There was no immobilisation in 40 daphnids exposed to a test concentration of 100mg/l for a period of 48 hours. inspection of the immobilisation data gave the following results:
Time (h) | EC50 (mg/l) | 95% Confidence limits (mg/l) |
24 | >100 | - |
48 | >100 | - |
The No Observed Effect Concentration after 24 and 48 hours exposure was 100 mg/l. The No Observed Effect concentration is based upon a zero immobilisation at this concentration.
It was considered unnecessary and unrealistic to test at concentrations in excess of 100 mg/l.
>Physico-chemical measurements: Temperature was maintained at 21°C throughout the study, and no treatment related differences for oxygen concentration or pH were observed throughout the study. Results are given below.
PHYSICO-CHEMICAL MEASUREMENTS
Nominal concentration (mg/l) | 0 hours | 24 hours | 48 hours | ||||
pH | mg O2/l | T°C | T°C | pH | mg O2/l | T°C | |
Control R1 | 7.8 | 8.4 | 21.0 | 21.0 | 7.7 | 8.2 | 21.0 |
Control R2 | 7.8 | 8.4 | 21.0 | 21.0 | 7.8 | 8.1 | 21.0 |
100 R1 | 7.8 | 8.3 | 21.0 | 21.0 | 7.8 | 8.2 | 21.0 |
100 R2 | 7.8 | 8.4 | 21.0 | 21.0 | 7.8 | 8.2 | 21.0 |
100 R3 | 7.8 | 8.4 | 21.0 | 21.0 | 7.8 | 8.2 | 21.0 |
100 R4 | 7.8 | 8.4 | 21.0 | 21.0 | 7.8 | 8.2 | 21.0 |
R1- R4= Replicates 1 -4
>Verification of test concentrations: Analysis of the test preparations at 0 and 48 hours (refer to attached pdf report no. 905/028) showed the measured test concentrations to be near nominal and so it was considered justifiable to estimate the EC50 values in terms of the nominal test concentrations only.
Description of key information
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
The acute toxicity of the test material to the freshwater invertebrate Daphnia magna has been invesitgated and gave a 48-Hour EC50 of greater than 100 mg/l.
Correspondingly the No Observed Effect Concentration was equal to 100 mg/l.
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