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EC number: 220-548-6 | CAS number: 2807-30-9
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1987
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted according to guideline and/or standard method but was there were no data on GLPs.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 987
- Report date:
- 1987
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Methods for Acute Toxicity Tests with Fish Macroinvertebrates and Amphibians, Ecological Research Series, EPA-600/3-75-009 , April, 1975.
- Deviations:
- yes
- Remarks:
- Replicate concentrations are not routinely used.
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- not specified
Test material
- Reference substance name:
- 2-(propyloxy)ethanol
- EC Number:
- 220-548-6
- EC Name:
- 2-(propyloxy)ethanol
- Cas Number:
- 2807-30-9
- Molecular formula:
- C5H12O2
- IUPAC Name:
- 2-(propyloxy)ethanol
- Details on test material:
- Test material: Propyl CELLOSOLVE
Source: Union Carbide Corporation
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
No data
Sampling and analysis
- Analytical monitoring:
- not specified
- Details on sampling:
- Dissolved oxygen and pH were determined initially and at 48 hours for all test concentrations and controls.
Mortalities were recorded at 24 and 48 hours.
Test solutions
- Vehicle:
- not specified
- Details on test solutions:
- Kanawha River water obtained from the South Side Boat Ramp (Charleston, at C&P Telephone Company Building) was used in preparation of test solutions. This water is soft and its quality is sufficiently high that it can be used for maintaining long-term Daphnia cultures. The following analyses were obtained on the water:
Total Hardness 60 mg/L as CaCO3
Total Alkalinity 38 mg/L as CaCO3
pH 7.1
Conductivity 250 umhos/cm
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Daphnia magna used in the bioassay came from a culture maintained in the laboratory for several years. This culture was initially stocked from the
EPA laboratory at Duluth. MN. The culture was maintained at 19-23 Deg. C in glass beakers filled with Kanawha River water. Culture transfers and feeding were performed three times a week. The transfer consists of placing 20-30 young Daphnia into each of three 600 ml beakers of river water. The
laboratory-prepared food consisted of pulverized trout food, yeast and alfalfa powder.
The Daphnia neonates ( first instars) used in testing were less than 24 hours old, and were obtained by isolating gravid females for approximately 20 hours.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- None
Test conditions
- Hardness:
- 60 mg/L as CaCO3
- Test temperature:
- No data
- pH:
- 7.1
- Dissolved oxygen:
- No data
- Salinity:
- No data
- Nominal and measured concentrations:
- 5-10 geometrically equidistant concentrations plus control
- Details on test conditions:
- The definitive test was designed to provide a series of from 5-10 geometrically equidistant concentrations plus a control .
The test was conducted in 250 mL beakers containing 200 mL of the test solution and 10 Daphnia. The Daphnia neonates ( first instars) used in testing were less than 24 hours old, and were obtained by isolating gravid females for approximately 20 hours.
Dissolved oxygen and pH were determined initially and at 48 hours for all test concentrations and controls.
Mortalities were recorded at 24 and 48 hours. - Reference substance (positive control):
- no
Results and discussion
Effect concentrations
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 5 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- No additional data
- Results with reference substance (positive control):
- No data
- Reported statistics and error estimates:
- The Trimmed Spearman-Karber computer program was used to calculate the 48-hour LC50 and 95 percent confidence intervals
Any other information on results incl. tables
None
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The 48h LC50 to Daphnia magna is >5000 mg/L.
- Executive summary:
48 hour Static definitive tests were conducted by EPA-ASTM procedures.
The definitive test was designed to provide a series of from 5-10 geometrically equidistant concentrations plus a control. The test was conducted in 250 mL beakers containing 200 mL of the test solution and 10 Daphnia. The Daphnia neonates (first instars) used in testing were less than 24 hours old, and were obtained by isolating gravid females for approximately 20 hours. Daphnia magna used in the bioassay came from a culture maintained in the laboratory for several years. This culture was initially stocked from the EPA laboratory at. MN.
Dissolved oxygen and pH were determined initially and at 48 hours for all test concentrations and controls.
Mortalities were recorded at 24 and 48 hours. The Trimmed Spearman-Karber computer program was used to calculate the 48-hour LC50 and 95 percent confidence intervals.
The 48h LC50 value to Daphnia magna was found to be >5000 mg/L.
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