Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 285-550-1 | CAS number: 85116-97-8
- 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
- Study period:
- 15 Jun - 21 Jul 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 2004
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- 2008
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- The Department of Health of the Government of the United Kingdom
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: control and 100 mg/L (pooled replicates)
- Sampling method: Duplicate samples were taken at 0 and 48 h.
- Sample storage conditions before analysis: Stored frozen for further analysis. - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: 100 mg of the test item was separately added to 1 L of test water to give a nominal loading rate of 100 mg/L. The test water was stirred by a magnetic stirrer using a vortex speed to form a dimple at the water surface. Stirring was stopped after 23 h and the mixture was allowed to stand for 1 h. Microscopic observations indicate a large proportion of undissolved test material. Thus, the solution was filtered through a glass wool plug (2-4 cm length). A wide bore glass tube, covered at one end with Nescofilm was submerged into the vessel, sealed end down, to a depth of 5 cm from the bottom of the vessel. A length of Tygon tubing was inserted into the glass tube and pushed through the Nescofilm seal. A glass wool plug was inserted into the opposite end of the tubing and the WAF was removed by mid-depth siphoning (the first 75-100 mL were discarded). After filtration no micro-dispersions of the test item were present as indicated by microscopic observation.
- Eluate: no
- Differential loading: no
- Controls: yes, test medium control - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Source: in-house culture
- Age at study initiation: < 24 h
- Method of breeding: Adult daphnia were maintained in 150 mL glass beakers containing Elendt M7 medium in a temperature controlled room at approx. 20 °C. The lightning cycle was 16 h light and 8 h dark with a 20 min transition period. Each culture was fed daily with a mixture of algal suspension (Desmodesmus subspicatus) and Tetramin® flake food suspension. Gravid adults were isolated the day before initiation of the test, such that the young daphnids produced overnight were less than 24 h old.
- Feeding during test: none - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Test temperature:
- 21 - 22 °C
- pH:
- 7.7 - 8.0
- Dissolved oxygen:
- 8.8 - 9.0 mg O2/L
- Nominal and measured concentrations:
- nominal: control and 100 mg/L (loading rate)
measured: < LOQ (control), 0.0642 mg/L (100 mg/L after 0 h), 0.0255 mg/L (100 mg/L after 48 h) - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass jars
- Type (delete if not applicable): covered to reduce evaporation
- Material, size, headspace, fill volume: glass, 250 mL, headspace: 50 mL, fill volume: 200 mL
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water (ISO medium) according to guideline
- Culture medium different from test medium: no
- Intervals of water quality measurement: Temperature was recorded daily. Dissolved oxygen and pH were recorded at the start and termination of the test.
OTHER TEST CONDITIONS
- Photoperiod: 16 h light / 8 h dark
- Light intensity: 573 - 586 lux
EFFECT PARAMETERS MEASURED
- Immobilization and adverse reactions were recorded at 24 and 48 h after start of exposure.
TEST CONCENTRATIONS
- Range finding study
- Test concentrations: Nominal loading rates of 1, 10 and 100 mg/L (same preparation of test solutions as in the definitive test)
- Results used to determine the conditions for the definitive study: No immobilisation was observed at 1, 10 and 100 mg/L loading WAFs. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- other: WAF
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: No sub-lethal effects were observed during exposure.
- Mortality of control: 0%
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: The test solutions appeared to be clear and colorless without undissolved particles after microscopic oberservation. - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- EC50/LC50: EC50 (48 h): 0.75 mg/L (95% CI: 0.69 - 0.82 mg/L)
- Other: NOEC (48 h): 0.56 mg/L - Validity criteria fulfilled:
- yes
- Remarks:
- See Table 1 in "Any other information on results incl. tables".
Reference
The dissolved test item may have been one or several components of the test item. Given that the toxicity cannot be attributed to a single component or a mixture of components, but to the test item as a whole, the results were based on nominal loading rates only.
Table 1: Validity criteria for OECD 202 (2004)
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
In the control, including the control containing the solubilising agent, not more than 10% of the daphnids should have been immobilized. |
None of the control daphnids showed immobilization or other signs of disease or stress. |
yes |
The dissolved oxygen concentration at the end of the test should be ≥ 3 mg/L in control and test vessels. |
The dissolved oxygen concentration at the end of the test was > 3 mg/L in control and test vessels. |
yes |
Description of key information
No effects up to the limit of water solubility (OECD 202)
Key value for chemical safety assessment
Additional information
One experimental study is available investigating the short-term toxicity of Fatty acids, C16-18, esters with diethylene glycol (CAS 85116-97-8) to aquatic invertebrates. Daphnia magna (< 24 h old) was exposed to a nominal loading of 100 mg/L which was prepared as Water Accommodated Fraction to remove any undissolved test material. The actual exposure concentrations were verified by HPLC/MS analysis. 0.0642 mg/L and 0.0255 mg/L were analysed after 0 h and 48 h, respectively.
After exposure of 48 h no immobile daphnids were observed
resulting in an EL50 (48 h) > 100 mg/L (nominal). The dissolved test
item may have been one or several components of the test item. Given
that the toxicity cannot be attributed to a single component or a
mixture of components, but to the test item as a whole, the results were
based on nominal loading rates only.
In conclusion the test substance will not exhibit toxic effects to
aquatic invertebrates up to the limit of water solubility.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.