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EC number: 255-424-0 | CAS number: 41519-23-7
- 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
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- March 06, 2017 to July 07, 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- (Z)-hex-3-enyl isobutyrate
- EC Number:
- 255-424-0
- EC Name:
- (Z)-hex-3-enyl isobutyrate
- Cas Number:
- 41519-23-7
- Molecular formula:
- C10H18O2
- IUPAC Name:
- (Z)-hex-3-enyl isobutyrate
Constituent 1
- Specific details on test material used for the study:
- TEST MATERIAL
Name ( stated on the report) : Hexenyl-3-cis Isobutyrate
Appearance: Colourless to pale yellow liquid
Batch: VE00450298
Expiry date: July 15, 2017
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- For the determination of the actual test item concentrations, duplicate samples were taken from each treatment at the start of the test.
After 24, 48 hours and at the end of the test (after 72 hours), stability samples (containing algae) were taken in duplicate from all test concentrations and from the control.
The stability samples (duplicate 10 mL samples) at 24 and 48 hours could not be taken from the test vessels itself, as the principle of a closed system is, that the test vessels have to remain completely filled with test medium during the entire test period. Therefore, for these samplings at 24 and 48 hours, two set of additional flasks containing the corresponding test medium (with algae) was incubated under conditions identical to the test.
For sampling at the end of the test, the test medium of the treatment replicates was pooled. Additional test vessels with test medium at a concentration of 3.2 mg/L were incubated under the following conditions:
- Test medium without algae under light conditions in order to document possible adsorption of the test item onto algae.
- Test medium without algae
Immediately after sampling, acetonitrile (3 mL acetonitrile per 10 mL sample volume) was added to each sample in order to stabilize the latter during the storage period. Thereafter, all samples were stored deep-frozen (at -20 ± 5 °C). Based on pre-experiments for investigation of the storage stability, the test item was found to be stable in the test water under these storage conditions.
Test organisms
- Test organisms (species):
- Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- The test organism used for the study was Pseudokirchneriella subcapitata (formerly Selenastrum capricornutum, occasionally also listed as Raphidocelis subcapitata), Strain No. 61.81 SAG, supplied by the Collection of Algal Cultures (SAG, Institute for Plant Physiology, University of Göttingen, 37073 Göttingen / Germany). The algae were cultivated at IES Ltd Laboratories under standardized conditions according to the test guidelines.
An inoculum culture was set up three days before the start of the exposure. The algae were cultivated under the test conditions and were kept in the exponential growth phase until inoculation of the test solutions.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
Test conditions
- Hardness:
- 15 mg/L as CaCO3
- Test temperature:
- 22°C
- pH:
- 7.5 - 7.8
- Nominal and measured concentrations:
- Nominal concentrations: 0.32, 1.0, 3.2, 10, 32 and 100 mg/L
Mean Measured concentrations: 0.13, 0.39, 0.99, 2.5, 13 and 77 mg/L - Details on test conditions:
- The test flasks were incubated in a temperature controlled orbital shaker (Multitron-Pro, Infors HT, Bottmingen/Switzerland) at a temperature of 22 °C.
The test flasks were positioned randomly and repositioned daily. They were continuously illuminated by LED light installed above the test flasks.
The light intensity at the level of the test solutions was approximately 66 μE s-1 m-2 (range: 65 to 68 μE s-1 m-2, measured at nine places in the experimental area). The light intensity over the HEXENYL-3-CIS ISOBUTYRATE IES Study 20160308 Report Page 13 of 55 incubation area was within a ±15%-deviation from the average light intensity as recommended by the guideline. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 5.3 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 2.6 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- The measured concentrations of HEXENYL-3-CIS ISOBUTYRATE in the test media of all test concentrations were between 80 and 99% of the nominal values at the start of the test (see analytical results and Table 7 in Appendix 1). Thus, the correct dosage of the test item could be verified.
At the end of the test period, the test item concentrations in the test media were betweenThe analytical results of the additional test vessels (without algae, in the dark and under light conditions) could not clarify potential adsorption and photolytic processes (as observed in the range finding test at 10 mg/L) due to the high decrease of test item concentration at the lower concentration level of 3.2 mg/L (see Table 7, Appendix 1). The biological results are based to the mean measured concentrations. These were calculated as the geometric mean of the concentrations measured at all sampling dates (0, 24, 48 and 72 hours). A clear concentration-response relationship was observed for both biological endpoints growth rate and yield during the exposure period.
The test item had a statistically significant inhibitory effect on the growth rate μ and yield Y of the algae after the test period of 72 hours at the mean measured concentration of 2.5 mg/L and at all higher test concentrations.
Therefore, the NOEC for growth rate and yield was determined to be at the mean measured concentration of 0.99 mg/L.
The microscopic examination of the algal cells at the end of the test showed no difference between the algae growing at the nominal test concentration of 10 mg/L (mean measured 2.5 mg/L) and the algal cells in the control. The shape and size of the algal cells were obviously not affected by the test item up to at least this concentration. No remarkable observations were made concerning the appearance of the test media. All test media were clear solutions throughout the test period. - Results with reference substance (positive control):
- The 72-hour EC50 for growth rate in the reference test IES Study Number 20160277 was 0.9 mg/L (October 2016) and showed that the sensitivity of the test system was within the range recommended by the guideline (72-hour EC50 for the growth rate 0.9-1.5 mg/L).
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- The validity criteria for increase of biomass, mean coefficient of variation of the daily growth rates and coefficient of variation of the average specific growth rates were fulfilled for the control
- Conclusions:
- The impact of the test item HEXENYL-3-CIS ISOBUTYRATE on the growth of the freshwater green algal species Pseudokirchneriella subcapitata is summarized in the table below. The results are based on the mean measured concentrations of the test item:
ErC50(72h) = 5.3 mg/L
ErC10 (72h) = 2.6 mg/L - Executive summary:
The impact of the test item HEXENYL-3-CIS ISOBUTYRATE on the growth of the freshwater green algal species Pseudokirchneriella subcapitata was investigated in a 72-hour static test according to the OECD Guideline 201 (2006, corrected 2011) and the Commission Regulation (EU) No 2016/266, C.3.
As the test item is a volatile substance, the test was performed using glass stoppered Erlenmeyer flasks completely filled (without headspace) with test medium that were tightly sealed with glass stoppers to avoid losses of test item by evaporation (closed system). The nominal test item concentrations tested were 0.32, 1.0, 3.2, 10, 32 and 100 mg/L.
Additionally, a control (test water without test item) was tested in parallel. The test media was prepared by completely dissolving the test item in test water using intense stirring for 24 hours in a closed vessel. The mixing vessel was nearly completely filled (including a small headspace) and tightly sealed with glass stoppers.
The measured concentrations of HEXENYL-3-CIS ISOBUTYRATE in the test media of all test concentrations were between 80 and 99% of the nominal values at the start of the test. Thus, the correct dosage of the test item could be verified.
At the end of the test period, the test item concentrations in the test media were between <LOQ (analytical limit of quantification, LOQ = 0.205 mg/L) and 66% of the nominal values.
The biological results are based on the mean measured concentrations. These were calculated as the geometric mean of the concentrations measured at all sampling dates (0, 24, 48 and 72 hours).
A clear concentration-response relationship was observed for both biological endpoints growth rate and yield after the exposure period of 72 hours. A statistically significant inhibitory effect on the growth rate and yield of the algae was observed at the end of the test at the mean measured concentration of 2.5 mg/L.
ErC50(72h) = 5.3 mg/L
ErC10 (72h) = 2.6 mg/L
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