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: 236-195-6 | CAS number: 13223-03-5
- 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 plants other than algae
Administrative data
- Endpoint:
- toxicity to aquatic plants other than algae
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 221 (Lemna sp. Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Ethyldimethyl[2-[(2-methyl-1-oxoallyl)oxy]ethyl]ammonium ethyl sulphate
- EC Number:
- 236-195-6
- EC Name:
- Ethyldimethyl[2-[(2-methyl-1-oxoallyl)oxy]ethyl]ammonium ethyl sulphate
- Cas Number:
- 13223-03-5
- Molecular formula:
- C10H20NO2.C2H5O4S
- IUPAC Name:
- ethyldimethyl{2-[(2-methylprop-2-enoyl)oxy]ethyl}azanium ethyl sulfate
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- All test item concentrations and the control were analytically verified via LC-MS/MS at the start (0 day) and at the end of the exposure (7 days) and on every renewal day. Freshly prepared and old media were analyzed. At the start samples were taken from the freshly prepared dilution levels. At the end samples were taken from pooled replicates and analyzed immediately. Details of the analytical method are given in section 13. The samples were analyzed with an LC-MS/MS method. The method was implemented under non-GLP but documented in the raw data and validated according to Annex 1. The method validation was not part of this GLP study.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- A stock solution with a nominal test item concentration of 500 mg/L was freshly prepared with dilution water (see Table 3) and agitated until the solution was visually clear. The stock solution was freshly prepared on each renewal day. 5 concentrations were tested in a geometrical series with a dilution factor of 3.2: 4.77 - 15.3 - 48.8 - 156 - 500 mg Quat 311/L, corresponding to the following corrected nominal concentrations of the test item (concentration of the main component): 4.67 - 15.0 - 47. 7 - 153 - 489 mg/L.
The concentrations are based on the results of a preliminary range finding test
Test organisms
- Test organisms (species):
- Lemna gibba
- Details on test organisms:
- TEST ORGANISM
- Common name: Duckweed
- Strain: not indicated
- Source (laboratory, culture collection): EUROFINS-GAB GMBH, Eutinger Str. 24, D-75223 Niefernöschelbronn, Germany
- Age of inoculum (at test initiation): not applicable
- Method of cultivation: in house culture
ACCLIMATION
- Acclimation period: not applicable
- Culturing media and conditions (same as test or not): yes
- Any deformed or abnormal cells observed: no
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 7 d
Test conditions
- Test temperature:
- 23.7 - 25.7
- pH:
- 7.53 - 8.59
- Nominal and measured concentrations:
- Nominal: control, 4.67, 15, 47.7, 153, 489 mg/L
TWA: < LOQ, 2.23, 6.38, 23.0, 126, 439 mg/L
As the analytical determined test concentrations were above +/-20 % of the nominal test concentrations, all biological results were referred to the time weightes average (TWA) concentrations. - Details on test conditions:
- TEST SYSTEM
- Incubation chamber used: not indicated
- Test vessel: crystalizing glass dishes
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: glass, 900 ml (nominal), filled with 500 ml medium
- Aeration: no
- Agitation: no
- Renewal rate of test solution (frequency/flow rate): daily
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates):6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: 20> AAP-medium; according to OECD 221
- Culture medium different from test medium: no
- Intervals of water quality measurement: daily
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: continuous
- Light intensity and quality: 1100 - 4440 lux (fluorescent)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : frond number (after 3 5 and 7 days), dry weight at test end.
- Determination of frond number: yes
- Determination of biomass: yes
- Determination of frond area:
- Other:
RANGE-FINDING STUDY
- Test concentrations:
- Results used to determine the conditions for the definitive study: - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- 320 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- frond number
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- 478 mg/L
- Nominal / measured:
- meas. (TWA)
- Conc. based on:
- test mat.
- Basis for effect:
- other: dry weight
- Results with reference substance (positive control):
- ErC50: 7.68 mg/L (frond number)
ErC50: > 8 mg/L (dry weight) - Reported statistics and error estimates:
- EC10-, EC20- and ECso-values (0 - 7 d) of the growth rate and yield (frond number and dry weight) inhibition were calculated by third order polynomial regression. Calculations of the confidence intervals of EC10-, EC20- and ECso-values were carried out from the best fit values, the standard error and the t-distribution with the software GraphPad Prism.
The data for the tables in this report were computer-generated and rounded for presentation from the fully derived data. Consequently, if calculated manually based on the given data, minor deviations
may occur from these figures. Calculations were carried out using the following software:
- Excel, MICROSOFT CORPORATION
- SigmaPlot, SPSS INC.
- GraphPad Prism, GRAPHPAD SOFTWARE, INC.
Applicant's summary and conclusion
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.
