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EC number: 941-684-9 | CAS number: 1689527-25-0
- 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:
- other: read across from analogue substance
- Adequacy of study:
- key study
- Study period:
- From November 25 to December 05, 2016
- 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 guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 221 (Lemna sp. Growth Inhibition Test)
- Version / remarks:
- 2006
- Deviations:
- yes
- Remarks:
- The light homogeneity variation was between 15.1 and 15.8 % therefore not in the 15% range. The temperature ranged from 20.6 to 23.5 °C (i.e. 2.9 °C variation), which is out of the required range of 24± 2 °C
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Analogue Substance #1
- IUPAC Name:
- Analogue Substance #1
- Test material form:
- solid: particulate/powder
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 230, 72.8, 23.0, 7.28 and 2.30 mg/l nominal concentration - Sampling method: Since the test item is soluble in SIS medium, the test solutions were prepared by respective dilutions of a stock solution (test item dissolved in SIS Medium) with SIS Medium. - Sample storage conditions before analysis:
Test organisms
- Test organisms (species):
- Lemna minor
- Details on test organisms:
- TEST ORGANISM - Common name: Lemna minor - Source (laboratory, culture collection): Umweltbundesamt, FGIII 2.5, berwachungsverfahren Abwasserentsorgung, Schichauweg 58, D-12307 Berlin)
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 7 d
Test conditions
- Test temperature:
- from 20.6 to 23.5 °C
- pH:
- 6.5 at the beginning of the test
- Nominal and measured concentrations:
- 230, 72.8, 23.0, 7.28 and 2.30 mg/l nominal concentration, corresponding to 150, 47.4, 15.0, 4.74 and 1.50 mg/l of the active ingredient.
- Details on test conditions:
- TEST SYSTEM - Incubation chamber used: yes - Test vessel: beakers - Type (delete if not applicable): open / closed - Material, size, headspace, fill volume: 400 ml beakers, all-glass - Type of cover: black paper up until the 200 ml - Agitation: yes/no - No. of colonies per vessel: 9-12 fronds - No. of fronds per colony: 2-4 fronds - No. of vessels per concentration (replicates): 3 - No. of vessels per control (replicates): 6 GROWTH MEDIUM - Standard medium used: yes OTHER TEST CONDITIONS - Sterile test conditions: yes - Adjustment of pH: adjusted to 6.5 ± 0.2 with either 0.1 or 1 M HCl or NaOH - Light intensity and quality: continuous (6500–10000 lux) from Osram Fluora L18W77 (Osram AG, Winterthur, Switzerland) and CH Lighting F18T8/6500K EUP (CH Lighting CO., Ltd., China). Homogeneity: ± 15 % (target; see section 1.10.2 Deviations) EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : - Determination of frond number: [manual counting / computerized image analysis] - Determination of biomass: dry weight RANGE-FINDING STUDY - Test concentrations: 1, 10 and 100 mg/l - Results used to determine the conditions for the definitive study: at 1 mg/l 6 % of immobilisation based on growth rate, at 10 mg/l 19 % of immobilisation, at 100 mg/l 27 % of immobilisation.
- Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 192 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth rate
- Remarks on result:
- other: based on frond number
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 192 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth rate
- Remarks on result:
- other: based on dry weight
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 78.6 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- act. ingr.
- Basis for effect:
- other: yield
- Remarks on result:
- other: based on frond number
- Duration:
- 7 d
- Dose descriptor:
- EC50
- Effect conc.:
- ca. 63.4 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- act. ingr.
- Basis for effect:
- other: yield
- Remarks on result:
- other: based on dry weight
Any other information on results incl. tables
Test concentrations
The test concentrations of the test substance during the 7 day test period were determined by photometry at the beginning of the test, as well as after 3, 5 and 7 days of exposure.
These analyses confirmed the right dosage of the test item, and showed that the concentrations of the test item remained stable over the whole 7 day test period. The measured concentrations of the active ingredient at the beginning of the test were 150, 46.0, 15.2, 4.50 and 1.12 mg/l and 136, 44.0, 13.7, 3.77 and 0.943 mg/l after 7 days (i.e. 90, 96, 90, 84 and 85%, respectively, of the initial value). However, the lowest concentrations did not remain in the 80-120 % range of the nominal concentration. Therefore, the effective concentrations (ErCx and EyCx) were assessed based on the geometric mean (GM) of the measured concentrations of the active ingredient, which were 144, 43.7, 14.4, 4.15 and 1.00 mg/l .
Environmental conditions
The pH value in the control drifted by 0.4 units during the whole test period, which is therefore in the range allowed by the guideline (required: not more than 1.5).
The light intensity was 6930-8550 lux (mean 7382 lux; max. variation ± 15.8 %) at the start of the test and 7000-8500 lux (mean 7388 lux, max. variation ± 15.1 %) at the end of the exposure period.
The light homogeneity was therefore not in the 15 % range.
The temperature ranged from 20.6 to 23.5 °C (i.e. 2.9 °C variation), which is out of the required range of 24 ± 2 °C.
Since the test vessels were randomly re-placed and since the growth criterion in the control was fulfilled, these deviations are not expected to have had any significant impact on the outcome of the study.
Appearance of the plants at the end of the test
In the blank control the plants were very healthy with dark green fronds and roots reaching the
bottom of the test vessel.
At 1.50 and 4.74 mg/l, the plants looked like the blanks.
At 15.0 mg/l, the plants looked like the blanks but were slightly smaller.
At 47.4 mg/l, the plants looked like the blanks but were only half as big as the blanks.
At 150 mg/l, the plants had very small dark green fronds and very short roots
Validity of the test and remarks
The validity criterion was met.
At the nominal concentration of 1.5 mg/l an inhibitory effect was always detected while at the next upper concentration, i.e. 4.74 (and sometimes also for 15 mg/l) a stimulating effect was observed.
Moreover, the inhibitory effects observed at 1.5 mg/l are higher than those recorded for 15 mg/l.
While this seems like a discrepancy, it is not more than natural biological variation, which is observed when plants are exposed to concentrations below the NOEC.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- ECr50 = 192 mg/l based on frond numberECr50 = 192 mg/l based on dry weight
- Executive summary:
Method
The inhibitory effects of the test substance to the duckweed Lemna minor were investigated over a period of 7 days, based on the frond number and biomass (dry weight), following the guideline OECD 221.
The test solutions were prepared by respective dilutions of a stock solution in SIS Medium. The test was performed at 230, 72.8, 23.0, 7.28 and 2.30 mg/l nominal concentration, corresponding to 150, 47.4, 15.0, 4.74, 1.50, and 0.474 mg/l of the active ingredient.
Three parallel test vessels were used for each test concentration of the test item and six vessels for the blank controls.
The test concentrations during the 7 day test period were determined by photometry at the beginning of the test, as well as after 3, 5 and 7 days of exposure. These analyses confirmed the right dosage of the test item, and showed that the concentrations of the test item remained stable over the whole 7 day test period. However, the lowest concentrations did not remain in the 80-120 % range of the nominal concentration. Therefore, the effective concentrations (ErCx and EyCx) were assessed based on the geometric mean (GM) of the measured
concentrations of the active ingredient.
The two endpoints frond number and biomass (dry weight) were investigated at days 3, 5 and 7, and each of them were assessed as growth rate and yield.
Results
ECr50 = 192 mg/l based on frond number
ECr50 = 192 mg/l based on dry weight
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