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EC number: 947-403-6 | 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Remarks:
- of read aross substance
- Justification for type of information:
- Data for the target chemical is summarized based on the structurally similar read across chemicals
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- WoE report is based on two short term toxicity study of aquatic invertebrate for the test chemical :1.This study was designed to assess the toxic effects of the test compound on the test Daphnids.2.To evalaute the toxicity on test material on aquatic invertebrate Daphnia magna
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material: Reaction mass of 3H-Indolium, 2-[2-[4-[(2-cyanoethyl)methylamino]phenyl]ethenyl]-1,3,3-trimethyl- & acetate- Molecular formula: C23H26N3.C2H3O2- Molecular weight: 403.5231g/mole- Smiles : CC(=O)[O-].CC1(C2=CC=CC=C2[N+](=C1C=CC3=CC=C(C=C3)N(C)CCC#N)C)C- Inchl: 1S/C23H26N3.C2H4O2/c1-23(2)20-8-5-6-9-21(20)26(4)22(23)15-12-18-10-13-19(14-11-18)25(3)17-7-16-24;1-2(3)4/h5-6,8-15H,7,17H2,1-4H3;1H3,(H,3,4)/q+1;/p-1- Substance type: Organic- Physical state: Greenish lustourous liquid
- Analytical monitoring:
- not specified
- Details on sampling:
- 1.PREPARATION AND APPLICATION OF TEST SOLUTIONThe test substance was soluble in water. Therefore, the test solution was prepared by dissolving 10 mg of the test substance in 100 ml of ADaM’s media. Achieving test concentrations of 100 mg/L, respectively.2.The stock solution (100 g/L) was prepared by dissolving white powder in acetone. The test solutions of required concentrationas were prepared by mixing the stock solution of the test sample with reconstituted test water. The test solution were kept 10 min in ultrasonic bath.
- Vehicle:
- not specified
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- 1 . TEST ORGANISM - Common name: Water flea - Strain/clone: No data - Source: Own breeding of Daphnia magna - Age: No data - Feeding during test : No feeding after hatching ACCLIMATION - Acclimation period: No data - Acclimation conditions (same as test or not): No data - Type and amount of food: No data - Feeding frequency: No data - Health during acclimation (any mortality observed): No data QUARANTINE (wild caught) - Duration: No data - Health/mortality: No data 2.TEST ORGANISM- Common name: Water flea- Strain: Straus- Source: Own breeding at University of Chemistry and Technology, Prague- Age at study initiation (mean and range, SD): The animals used for the test shall be less than 24 h old and should not be first brood progeny- Feeding during test: No feedingACCLIMATION - No data available- Acclimation period:- Acclimation conditions (same as test or not):- Type and amount of food:- Feeding frequency:- Health during acclimation (any mortality observed):
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Hardness:
- 1) 145.5 mg of CaCO3
- Test temperature:
- 1) and 2) 20 °C ± 2 °C
- pH:
- 1) 7.12)Sample at concentration 100 mg/l: pH= 7.8 (changed to 7.7 during test)Control 1: pH= 7.6 (did not change during test)Control 1 + aceotone: pH=8 (changed to 8.1 during test)Control 2: pH=7.8 (changed to 7.7 during test)Control 2 + aceotone: pH=7.7 (did not changed during test)
- Nominal and measured concentrations:
- 1) 100 mg/L2)6, 10, 17, 29, 50 and 100 mg/L
- Details on test conditions:
- 1 . TEST SYSTEM- Test vessel: The test vessels used were all glass beaker having the water capacity of 25ml.- Material, size, headspace, fill volume: 20 ml - Aeration: No aeration during experiment- No. of organisms per vessel: 10 Daphnids- No. of vessels per concentration (replicates): No data - No. of vessels per control (replicates): No data - No. of vessels per vehicle control (replicates): No data - Biomass loading rate: No data TEST MEDIUM / WATER PARAMETERS - Source/preparation of dilution water: No data - Total organic carbon: No data - Particulate matter: No data - Metals: No data - Pesticides: No data - Chlorine: No data - Alkalinity: No data - Ca/mg ratio: No data - Conductivity: No data - Salinity: No data - Culture medium different from test medium: No data - Intervals of water quality measurement: No data OTHER TEST CONDITIONS - Adjustment of pH: No data - Photoperiod: 16 hours light and 8 hours dark EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Determination or calculation of the median effective concen trations (EC 50) and observations ((immobility, pH, Temperature, dissolved oxygen content) ) of the symptoms were done after 24 and 48 hours.VALIDITY OF THE TEST:1. In the control, including the control containing the solubilising agent, not more that 10 percent of the daphnids should have been immobiliz ed. 2. The dissolved oxygen concentration at the end of the test should be 3 mg/l in control and test vessels.2.TEST SYSTEM- Test vessel: 50 ml glass vessel- fill volume: 25 ml- No. of organisms per vessel: 5- No. of vessels per concentration (replicates): 4TEST MEDIUM / WATER PARAMETERS- Source/preparation of dilution water: Natural water (surface or ground water), reconstituted water or dechlorinated tap water are acceptable as culturing and dilution water if D. magna survives in it for the duration of the culturing, acclimation and testing without showing signs of stress. Waters in the range pH 6 to pH 9, with hardness between 140 mg/l and 275 mg/l (as CaCO3) are recommended.As an example, the preparation of dilution water meeting the requirements is described below.Dissolve known quantities of reagents in water. The dilution water prepared shall have a pH of 7.8 ± 0.5, a hardness of (225 ± 50) mg/l (expressed as CaCO3), a molar Ca + Mg ratio close to 4 + 1 and a dissolved oxygen concentration above 7 mg/l.Prepare the solutions specified below:- Calcium chloride solution: Dissolve 117.6 g of calcium chloride dihydrate (CaCl2.2H2O) in water (4.2) and make up to 1 l with water (4.2).- Magnesium sulfate solution: Dissolve 49.3 g of magnesium sulfate heptahydrate (MgSO4.7H2O) in water (4.2) and make up to 1 l with water (4.2).- Sodium bicarbonate solution: Dissolve 25.9 g of sodium bicarbonate (NaHCO3) in water (4.2) and make up to 1 l with water (4.2).- Potassium chloride solution: Dissolve 2.3 g of potassium chloride (KCI) in water (4.2) and make up to 1 l with water (4.2).MixingMix 2.5 ml of each of the four solutions and make up to 1 l with water.The dilution water shall be aerated until the dissolved oxygen concentration has reached saturation and the pH has stabilized. If necessary, adjust the pH to 7.8 ± 0.5 by adding sodium hydroxide (NaOH) solution or hydrochloric acid (HCI). The dilution water prepared in this way shall not be further aerated before use.- Sodium hydroxide solution, e.g. [NaOH] : 1 mol/l.- Hydrochloric acid, e.g. [HCl] : 1 mol/l.Reference substance: Dissolve 600 mg of potassium dichromate (K2Cr2O7) in water and make up to 1 l with water (4.2).OTHER TEST CONDITIONS- Adjustment of pH: no adjustment done- Photoperiod: No - Darkness- Light intensity:CALCULATION:EC50 was calculated using non linear regression by the software Prism 4.0
- Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate (K2Cr2O7) for Read across 2
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: Read across 1
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 29.8 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: Read across 2
- Details on results:
- 2) - Results with reference substance valid- EC50: 0.79 mg/L (24 hours)
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The test chemical 2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetate is likely to be toxic to Daphnia magna in the dose range of 29.8 to 100 mg/l
- Executive summary:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of aquatic invertebrate of the test chemical Reaction mass of 3H-Indolium, 2-[2-[4-[(2-cyanoethyl)methylamino]phenyl]ethenyl]-1,3,3-trimethyl- & acetate.The studies are as mentioned below:
1.Daphnia sp., Acute Immobilization Test according to OECD Guideline 202 was conducted for test material. The nominal concent ration selected for the experiment was 100 mg/L and test Daphnids were exposed to this concentration for 48hours. The Effective concentrations EC50 was found to be 100 mg/L. Also the substance was found to be not rapidly degradable.Thus according to CLP Criteria for aquatic classification of the substance, it is concluded that test material exhibits toxicity to aquatic invertebrate (Daphnia magna) in the chronic 3 classification category.
EC50 (48 hours) Experimental = 100 mg/L
2.Determination of the inhibition of the mobility of daphnids was carried out with the substance,according to OECD Guideline 202.
The test substance was tested at the concentrations 0, 6, 10, 17, 29, 50 and 100 mg/L. Effects on immobilisation were observed for 48 hours. The median effective concentration (EC50) for the test substance,1-(3-chloropropyl)-1,3-dihydro-2H-benzimidazol-2-one, in Daphnia magna was determined to be 29.8 mg/L for immobilisation effects.
This value indicates that the substance is likely to be hazardous to aquatic invertebrates and can be classified as Aquatic Chronic category 3 as per the CLP criteria.
Thus, based on the above summarised studies, Reaction mass of 3H-Indolium, 2-[2-[4-[(2-cyanoethyl)methylamino]phenyl]ethenyl]-1,3,3-trimethyl- & acetate and it’s functionally similar read across substance, it can be concluded that effect concetration value is in the range of 29 to 100 mg/
L. Thus, comparing this value with the criteria of CLP regulation, Reaction mass of 3H-Indolium, 2-[2-[4-[(2-cyanoethyl)methylamino]phenyl]ethenyl]-1,3,3-trimethyl- & acetate can be classified for short term toxicity for aquatic invertebrate .Hence,based on the data available for functionally similar read across, test chemical Reaction mass of 3H-Indolium, 2-[2-[4-[(2-cyanoethyl)methylamino]phenyl]ethenyl]-1,3,3-trimethyl- & acetate can be classified as Aquatic Chronic category 3 as per the CLP criteria.
.
Reference
Description of key information
Short-term toxicity to aquatic invertebrate:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of aquatic invertebrate of the test chemical2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetate(65122 -06 -7).The studies are as mentioned below:
1.Daphnia sp., Acute Immobilization Test according to OECD Guideline 202 was conducted for test material. The nominal concent ration selected for the experiment was 100 mg/L and test Daphnids were exposed to this concentration for 48hours. The Effective concentrations EC50 was found to be 100 mg/L. Also the substance was found to be not rapidly degradable.Thus according to CLP Criteria for aquatic classification of the substance, it is concluded that test material exhibits toxicity to aquatic invertebrate (Daphnia magna) in the chronic 3 classification category.
EC50 (48 hours) Experimental = 100 mg/L
2.Determination of the inhibition of the mobility of daphnids was carried out with the substance,according to OECD Guideline 202.
The test substance was tested at the concentrations 0, 6, 10, 17, 29, 50 and 100 mg/L. Effects on immobilisation were observed for 48 hours. The median effective concentration (EC50) for the test substance,1-(3-chloropropyl)-1,3-dihydro-2H-benzimidazol-2-one, in Daphnia magna was determined to be 29.8 mg/L for immobilisation effects.
This value indicates that the substance is likely to be hazardous to aquatic invertebrates and can be classified as Aquatic Chronic category 3 as per the CLP criteria.
Thus, based on the above summarised studies,2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetateand it’s functionally similar read across substance, it can be concluded that effect concetration value is in the range of 29 to 100 mg/
L. Thus, comparing this value with the criteria of CLP regulation,2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetatecan be classified for short term toxicity for aquatic invertebrate .Hence,based on the data available for functionally similar read across, test chemical2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetatecan be classified as Aquatic Chronic category 3 as per the CLP criteria.
.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 29.8 mg/L
Additional information
Short-term toxicity to aquatic invertebrate:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of aquatic invertebrate of the test chemical2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetate(65122 -06 -7).The studies are as mentioned below:
1.Daphnia sp., Acute Immobilization Test according to OECD Guideline 202 was conducted for test material. The nominal concent ration selected for the experiment was 100 mg/L and test Daphnids were exposed to this concentration for 48hours. The Effective concentrations EC50 was found to be 100 mg/L. Also the substance was found to be not rapidly degradable.Thus according to CLP Criteria for aquatic classification of the substance, it is concluded that test material exhibits toxicity to aquatic invertebrate (Daphnia magna) in the chronic 3 classification category.
EC50 (48 hours) Experimental = 100 mg/L
2.Determination of the inhibition of the mobility of daphnids was carried out with the substance,according to OECD Guideline 202.
The test substance was tested at the concentrations 0, 6, 10, 17, 29, 50 and 100 mg/L. Effects on immobilisation were observed for 48 hours. The median effective concentration (EC50) for the test substance,1-(3-chloropropyl)-1,3-dihydro-2H-benzimidazol-2-one, in Daphnia magna was determined to be 29.8 mg/L for immobilisation effects.
This value indicates that the substance is likely to be hazardous to aquatic invertebrates and can be classified as Aquatic Chronic category 3 as per the CLP criteria.
Thus, based on the above summarised studies,2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetateand it’s functionally similar read across substance, it can be concluded that effect concetration value is in the range of 29 to 100 mg/
L. Thus, comparing this value with the criteria of CLP regulation,2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetatecan be classified for short term toxicity for aquatic invertebrate .Hence,based on the data available for functionally similar read across, test chemical2-(2-{4-[(2-cyanoethyl)(methyl)amino]phenyl}vinyl)-1,3,3-trimethyl-3H-indolium acetatecan be classified as Aquatic Chronic category 3 as per the CLP criteria.
.
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