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Reaction mass of Amines, C10-14-branched and linear alkyl, bis[2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)] chromate(1-) (1:1) and Amines,C10-14-branched and linear alkyl, bis[2,4-dihydro-4-[(2-hydroxy-4-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)] chromate(1-)
EC number: 943-145-3 | CAS number: -
- 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
![](https://www.echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_ecotoxicological-information.png)
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
- Study period:
- 14 Feb 2017 to 27 Feb 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 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:
- Reaction mass of Amines, C10-14-branched and linear alkyl, bis[2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)] chromate(1-) (1:1) and Amines,C10-14-branched and linear alkyl, bis[2,4-dihydro-4-[(2-hydroxy-4-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)] chromate(1-)
- EC Number:
- 943-145-3
- IUPAC Name:
- Reaction mass of Amines, C10-14-branched and linear alkyl, bis[2,4-dihydro-4-[(2-hydroxy-5-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)] chromate(1-) (1:1) and Amines,C10-14-branched and linear alkyl, bis[2,4-dihydro-4-[(2-hydroxy-4-nitrophenyl)azo]-5-methyl-2-phenyl-3H-pyrazol-3-onato(2-)] chromate(1-)
- Test material form:
- solid
Constituent 1
- Specific details on test material used for the study:
- STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage conditions: The sample of the test item was stored at ambient temperature without exposure to light in a tightly sealed container.
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- From each filtrate and the control, two samples were collected for chemical determinations (100 mL each). One was transferred to chemical analyses at exposure initiation, the others were stored under test conditions.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
The test item is a complex mixture. Every constituent contributes to a different degree to overall solubility, depending on its own individual solubility and its mass fraction in the test item. For this reason, the loading rates were prepared by using the water accommodated fraction (WAF) approach followed by filtration. Appropriate amounts of the test item were weighed separately in glass flasks with 20X AAP medium and mixed with appropriate volume of the 20X AAP medium. The mixtures of the loadings were visually heterogeneous (with undissolved particles) and colored. The mixtures and the control (20X AAP medium) were left for mechanical shaking for 48 hours (30ºC, 90 rpm, darkness). After 48 hours of mechanical shaking, the mixtures (visually heterogeneous) and the control were left at room temperature for a settling phase (no shaking). After 24 hours of settling, the mixtures were still visually heterogeneous. All mixtures and the control were filtrated, first through a conditioned paper filter (qualitative cellulose filter) and next through a conditioned nitrocellulose membrane filter (HAWG filter, 0.22 µm, Millipore). Each filtrate was visually homogeneous (without any visible undissolved particles.
Test organisms
- Test organisms (species):
- Lemna gibba
- Details on test organisms:
- TEST ORGANISM
- Common name: Duckweed
- Strain: CPCC 310
- Source: The culture of Lemna gibba CPCC 310 on agar bevels was received from Canadian Phycological Culture Centre (CPCC), Department of Biology, University of Waterloo, Ontario, Canada.
- Method of cultivation: Cultivated in a standard laboratory culture at the Institute of Industrial Organic Chemistry, Branch Pszczyna, Department of Ecotoxicology, Laboratory of Aquatic Toxicology, according to the OECD Guideline No. 221 (2006) recommendations.
CULTURING
Duckweed Lemna gibba was transferred from agar bevels to the fresh 20X AAP medium in glass beakers with a capacity of 600 mL with transparent lids and incubated at room temperature with constant illumination (pre-culturing). The duckweed culture was inoculated to fresh medium once a week. A pre-culture was started nine days before exposure. Only organisms in good physiological condition without any discolouration were used for the inoculation of the test item concentrations and the control.
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 7 d
Test conditions
- Hardness:
- 304.1 mg/L as CaCO3
- Test temperature:
- 24.2 - 25.2 °C
- pH:
- - Fresh samples: 7.24 - 7.74
- Spent samples: 7.99 - 8.78 - Nominal and measured concentrations:
- - Nominal loading rates: 0 (control), 2.56, 6.4, 16, 40 and 100 mg/L.
- Details on test conditions:
- TEST SYSTEM
- Incubation chamber: yes / thermostatic chamber (incubator with shaker, ILW400STD Pol-Eko-Aparatura, Poland)
- Test vessel: Glass crystallisers with a depth of 4 cm and a diameter of 7 cm were used.
- Type: Closed; transparent lids were used to minimise evaporation and accidental contamination, allowing necessary air exchange.
- Fill volume: 150 mL
- Renewal rate of test solution: Daily
- No. of colonies per vessel: 3
- No. of fronds per colony: 3
- No. of vessels per concentration: 3
- No. of vessels per control: 6
GROWTH MEDIUM
- Standard medium used: The 20X AAP medium recommended by the OECD Guideline No. 221 (2006) was the culturing medium for test organism and the diluent/solvent for the test item.
TEST MEDIUM / WATER PARAMETERS
- Alkalinity: 304.9 mg/L as CaCO3 in the culture medium
- Culture medium different from test medium: No
- Intervals of water quality measurement: Daily, before and after renewals
OTHER TEST CONDITIONS
- Photoperiod: Constant illumination;
- Light intensity: 7713 - 7863 lux; The light intensity was measured at exposure initiation, twice during exposure and at exposure termination with a 2π receptor lux-meter (Sonopan L-100, Poland)
- Light type: fluorescent
EFFECT PARAMETERS MEASURED: number of fronds, plant development (frond size, shape and apperance) and growth rate.
The total number of fronds in each test vessel was counted on days 3, 5 and at exposure termination. Only visibly distinct fronds were counted. At the same time, observations of plant development were performed: frond size, shape and appearance (necrosis, chlorosis, gibbosity or bending of fronds), colony breakup or loss of buoyancy, root length and appearance. The dry weight of the representative sample of the duckweed culture used as the inoculum was measured after exposure initiation. The dry weight of all plants from each test vessel was measured after exposure termination. All colonies (with roots) were transferred onto previously weighed microscopic slides and dried at approximately 60°C in a laboratory oven until constant weight.
PRELIMINARY NON-GLP TEST
- Test item loading rates: 0 (control), 0.1 (diluted), 1 (diluted), 10 and 100 mg/L
- Results used to determine the conditions for the definitive study: 42.1% and 53.6% growth rate inhibition at 10 and 100 mg/L, respectively. See 'Any other information on materials and methods incl. tables'. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EL50
- Effect conc.:
- 74.77 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% CL: 68.62 - 82.04 mg/L
- Key result
- Duration:
- 7 d
- Dose descriptor:
- EL10
- Effect conc.:
- 2.23 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% CL: 68.62 - 82.04 mg/L
- Duration:
- 7 d
- Dose descriptor:
- EL50
- Effect conc.:
- 8.32 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Remarks on result:
- other: 95% CL: 7.91 - 8.75 mg/L
- Duration:
- 7 d
- Dose descriptor:
- EL20
- Remarks:
- EL10 not determined
- Effect conc.:
- 1.73 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: yield
- Remarks on result:
- other: 95% CL: 1.56 - 1.90 mg/L
- Details on results:
- At exposure termination, in the filtrates of a loading of 2.56 mg/L, no distinctive changes from the development of plants in the control were observed. In the filtrate of a loading of 6.4 mg/L, shortened roots were observed. In the filtrates of a loading of 100, 40 and 16 mg/L, separated roots were observed. Inhibition of growth rate was 9.4% at 2.56 mg/L and increased in a dose-dependent manner up to 43% inhibition at 100 mg/L. In 'Any other information on results incl. tables' the results are tabulated and additional effect values are presented.
VALIDITY CRITERIA
In the definitive test, the following validity criteria specified in the OECD Guideline No. 221 (2006) were met:
- The doubling time of frond number in the control was 1.5 days, criterion: less than 2.5 days (the factor of frond number in the control between 0 and 7 day was 28.1).
- The average specific growth rate in the control between day 0 and day 7 was 0.476 d-1 (minimum requirement: higher than 0.275 d-1). - Results with reference substance (positive control):
- EFFECT LEVELS BASED ON FROND NUMBER:
- 7-d ErC50: 9.94 mg/L (95% CL: 8.14 - 12.12 mg/L)
- 7-d ErC10: 4.71 mg/L (95% CL: 1.10 - 6.48 mg/L)
- 7-d EyC50: 6.60 mg/L (95% CL: 3.77 - 9.77 mg/L)
- 7-d EyC10: 3.05 mg/L (95% CL: 0.48 - 4.77 mg/L)
- Results with reference substance valid? Yes - Reported statistics and error estimates:
- Probit method calculations and analysis by Shapiro-Wilk’s Test on Normal Distribution, Levene’s Test on Variance Homogeneity (with Residuals), Step-down Jonckheere -Terpstra test procedure, Williams multiple sequential and t-test procedure.
Any other information on results incl. tables
Table: Inhibition of growth rate and yield, definitive test
Filtrate of a loading of |
Based on frond number |
Based on dry weight |
||
% Inhibition at exposure termination (day 7) (growth rate) |
% Inhibition at exposure termination (day 7) (yield) |
% Inhibition at exposure termination (day 7) (growth rate) |
% Inhibition at exposure termination (day 7) (yield) |
|
Control |
0 |
0 |
0 |
0 |
2.56 mg/L |
7.1 |
22.2 |
9.4 |
31 |
6.4 mg/L |
17.3 |
45.6 |
17.4 |
49.6 |
16 mg/L |
33.2 |
69.4 |
28.8 |
67.7 |
40 mg/L |
42.9 |
79 |
33.7 |
73.9 |
100 mg/L |
51.1 |
84.9 |
43 |
82.3 |
Table: Frond number and dry weight
Filtrate of a loading of |
Frond number |
Dry weight [mg] |
||
day 3 |
day 5 |
day 7 |
day 7 |
|
Control mean |
38.8 |
103.3 |
253.3 |
44.4 |
standard deviation |
2.04 |
5.65 |
27.78 |
5.62 |
2.56 mg/L mean |
31 |
79 |
199 |
30.9 |
standard deviation |
3 |
3.61 |
9.17 |
0.97 |
6.4 mg/L mean |
33.3 |
71 |
142 |
22.9 |
standard deviation |
3.51 |
4.36 |
10.82 |
2.06 |
16 mg/L mean |
29 |
54.3 |
83.7 |
15 |
standard deviation |
3.61 |
5.69 |
6.66 |
2.7 |
40 mg/L mean |
26.7 |
46 |
60.3 |
12.3 |
standard deviation |
1.53 |
1.73 |
3.21 |
0.71 |
100 mg/L mean |
25.7 |
39 |
46 |
8.7 |
standard deviation |
0.58 |
2 |
2.65 |
0.47 |
Table: Section-by-section growth rate and growth rate, based on frond number
Filtrate of a loading of |
Section-by-section growth rate* |
Growth rate |
||
0-3 d |
3-5 d |
5-7 d |
0-7 d |
|
Control mean |
0.487 |
0.489 |
0.446 |
0.476 |
standard deviation |
0.0181 |
0.0166 |
0.0319 |
0.0166 |
2.56 mg/L mean |
0.411 |
0.469 |
0.462 |
0.442 |
standard deviation |
0.0324 |
0.0357 |
0.0098 |
0.0065 |
6.4 mg/L mean |
0.435 |
0.379 |
0.346 |
0.394 |
standard deviation |
0.035 |
0.0283 |
0.0092 |
0.0111 |
16 mg/L mean |
0.388 |
0.315 |
0.217 |
0.318 |
standard deviation |
0.0407 |
0.0607 |
0.0153 |
0.0116 |
40 mg/L mean |
0.362 |
0.273 |
0.135 |
0.272 |
standard deviation |
0.0193 |
0.0311 |
0.0407 |
0.0075 |
100 mg/L mean |
0.349 |
0.209 |
0.082 |
0.233 |
standard deviation |
0.0075 |
0.0167 |
0.0096 |
0.0083 |
EFFECT VALUES
7-d ErL20 based on frond number: 7.45 mg/L (95% CL: 6.69 - 8.23 mg/L)
7-d LOErLR based on frond number: < 2.56 mg/L
7-d NOErLR based on frond number: < 2.56 mg/L
7-d EyL20 based on frond number: 1.73 mg/L (95% CL: 1.56 - 1.90 mg/L)
7-d LOEyLR based on frond number: < 2.56 mg/L
7-d NOEyLR based on frond number: < 2.56 mg/L
7-d ErL50 based on dry weight: 169.56 mg/L (95% CL: 136.46 - 220.29 mg/L)
7-d ErL20 based on dry weight: 8.68 mg/L (95% CL: 7.12 – 10.27 mg/L)
7-d ErL10 based on dry weight: 1.83 mg/L (95% CL: 1.28 - 2.47 mg/L)
7-d LOErLR based on dry weight: < 2.56 mg/L
7-d NOErLR based on dry weight: < 2.56 mg/L
7-d EyL50 based on dry weight: 7.08 mg/L (95% CL: 6.53 - 7.65 mg/L)
7-d EyL20 based on dry weight: n.d.
7-d EyL10 based on dry weight: n.d.
7-d LOEyLR based on dry weight: < 2.56 mg/L
7-d NOEyLR based on dry weight: < 2.56 mg/L
n.d. - not determined
Table: Concentration and stability of TOC, definitive test
Day |
Mean TOC concentration in filtrate [mg/L] |
|||||
Control |
2.56 mg/L |
6.4 mg/L |
16 mg/L |
40 mg/L |
100 mg/L |
|
Day 0 fresh |
1.36 |
2.49 |
2.74 |
2.97 |
3.49 |
6 |
Day 1 old |
1.02 |
2.41 |
2.92 |
3.07 |
3.51 |
4.96 |
Day 1 fresh |
1.06 |
2.65 |
-- |
-- |
-- |
4.36 |
Day 2 old |
< LoQ |
3.06 |
-- |
-- |
-- |
4.85 |
Day 2 fresh |
< LoQ |
3.1 |
-- |
-- |
-- |
5.02 |
Day 3 old |
1.22 |
2.21 |
-- |
-- |
-- |
4.46 |
Day 3 fresh |
< LoQ |
2.51 |
-- |
-- |
-- |
4.77 |
Day 4 old |
< LoQ |
2.83 |
-- |
-- |
-- |
6.95 |
Day 4 fresh |
< LoQ |
2.57 |
-- |
-- |
-- |
6.96 |
Day 5 old |
< LoQ |
2.76 |
-- |
-- |
-- |
4.92 |
Day 5 fresh |
< LoQ |
2.99 |
-- |
-- |
-- |
5.47 |
Day 6 old |
< LoQ |
2.82 |
-- |
-- |
-- |
6.57 |
Day 6 fresh |
< LoQ |
2.98 |
-- |
-- |
-- |
6.79 |
Day 7 old |
1.25 |
2.61 |
-- |
-- |
-- |
6.17 |
LoQ = 1.0 mg C/L
The results were corrected by the value determined for the control sample in a series and presented as the concentrations of total
organic carbon (TOC)
TOC - total organic carbon
-- no value/not determined
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- See 'Any other information on materials and methods incl. tables'
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