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EC number: 235-468-7 | CAS number: 12237-62-6 This substance is identified in the Colour Index by Colour Index Constitution Number, C.I. 42535:3.
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- Data is from experimental source
- Qualifier:
- according to guideline
- Guideline:
- other: EEC Directive 93/32/EEC (December 1992)
- GLP compliance:
- yes
- Analytical monitoring:
- not specified
- Vehicle:
- no
- Details on test solutions:
- Preparation of the stock solution and dilution: The test substance was stirred in M4-medium for about 20 hours. Undisolved test substance was recoved by centrifugation (approx. 20 min about 17700 G). The result is a clear solution.
The study was performed with an aqueous extract (eluate) of the test substance.
Test concentrations :100 mg/L; 10 mg/L; 1 mg/L ; 0.1 mg/L; 0.01 mg/L - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Daphnia magna STRAUS
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Nominal and measured concentrations:
- Test concentrations: 100 mg/L; 10 mg/L; 1 mg/L ; 0.1 mg/L; 0.01 mg/L
- Details on test conditions:
- Measured test parameter: Swimming ability of the daphina after 24 and 48 h; O2-content and pH-values at the begin and end of the exposure period
- Reference substance (positive control):
- not specified
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks:
- inhibition of the swimming ability
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 6.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks:
- inhibition of the swimming ability
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks:
- inhibition of the swimming ability
- Remarks on result:
- other: * highest test concentration with an effect of ≤ 10%
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The EL-values of test chemical in Daphnia magna, which cause after 48 h no (EC0) or 50% (EC50) and 100% (EC100) inhibition of the swimming ability compared to an untreated control are:
EC0 = 1 mg/l (nominal)
EC50 = 6.5 mg/l (nominal)
EC100 = 100 mg/l (nominal) - Executive summary:
An acute immobilisation test was carried out for assessing the effect of test chemical on aquatic invertebrates. The study was performed following the principles of the EEC Directive 93/32/EEC (December 1992) method. Daphnia magna Straus (Water flea) was used as a test organism. The test substance was stirred in M4-medium for about 20 hours. Undisolved test substance was recoved by centrifugation (approx. 20 min about 17700 G). The result is a clear solution. The study was performed with an aqueous extract (eluate) of the test substance. Daphnids were exposed to different test chemical conc. (0, 0.01, 0.1, 1, 10 and 100 mg/l) for 48 hrs. Swimming ability of the daphina after 24 and 48 h; O2-content and pH-values at the begin and end of the exposure period were measured. Based on the effect of test chemical on mobility of the test organism, the 48 hr EC0, EC50 and EC100 value was determined to be 1, 6.5 and 100 mg/l, respectively. Thus, test chemical was considered as toxic and hence, considered to be classified in 'aquatic chronic category 2' as per the CLP classification criteria.
Reference
Concentration Effect Relationship after 48 h:
Nominal concentration [mg/L] |
Number of daphnia without Inhibition (from 20) |
Inhibition (%) |
0 (Control) | 20 | 0 |
100 | 0 | 100 |
10 | 4 | 20 |
1 | 20 | 0 |
0.1 | 20 | 0 |
0.01 | 20 | 0 |
Description of key information
An acute immobilisation test was carried out for assessing the effect of test chemical on aquatic invertebrates (Experimental study report. 2002). The study was performed following the principles of the EEC Directive 93/32/EEC (December 1992) method. Daphnia magna Straus (Water flea) was used as a test organism. The test substance was stirred in M4-medium for about 20 hours. Undisolved test substance was recoved by centrifugation (approx. 20 min about 17700 G). The result is a clear solution. The study was performed with an aqueous extract (eluate) of the test substance. Daphnids were exposed to different test chemical conc. (0, 0.01, 0.1, 1, 10 and 100 mg/l) for 48 hrs. Swimming ability of the daphina after 24 and 48 h; O2-content and pH-values at the begin and end of the exposure period were measured. Based on the effect of test chemical on mobility of the test organism, the 48 hr EC0, EC50 and EC100 value was determined to be 1, 6.5 and 100 mg/l, respectively. Thus, test chemical was considered as toxic and hence, considered to be classified in 'aquatic chronic category 2' as per the CLP classification criteria.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 6.5 mg/L
Additional information
Various experimental studies of the test chemical were reviewed for short term toxicity to aquatic invertebrate end point which are summarized as below:
In an experimental study from study report (2002), an acute immobilisation test was carried out for assessing the effect of test chemical on aquatic invertebrates. The study was performed following the principles of the EEC Directive 93/32/EEC (December 1992) method. Daphnia magna Straus (Water flea) was used as a test organism. The test substance was stirred in M4-medium for about 20 hours. Undisolved test substance was removed by centrifugation (approx. 20 min about 17700 G). The result is a clear solution. The study was performed with an aqueous extract (eluate) of the test substance. Daphnids were exposed to different test chemical conc. (0, 0.01, 0.1, 1, 10 and 100 mg/l) for 48 hrs. Swimming ability of the daphina after 24 and 48 h; O2-content and pH-values at the beginning and end of the exposure period were measured. Based on the effect of test chemical on mobility of the test organism, the 48 hr EC0, EC50 and EC100 value was determined to be 1, 6.5 and 100 mg/l, respectively. Thus, test chemical was considered as toxic and hence, considered to be classified in 'aquatic chronic category 2' as per the CLP classification criteria.
Another short term toxicity to aquatic invertebrate study was carried out for assessing the effect of test chemical (2002). The study was performed following the principles of the EEC Directive 93/32/EEC (December 1992) method. Daphnia magna Straus (Water flea) was used as a test organism. The test substance was stirred in M4-medium for about 20 hours. Undisolved test substance was removed by centrifugation (approx. 20 min about 17700 G). The result is a clear solution. The study was performed with an aqueous extract (eluate) of the test substance. Daphnids were exposed to different test chemical conc. (0, 0.01, 0.1, 1, 10 and 100 mg/l) for 48 hrs. Swimming ability of the daphina after 24 and 48 h; O2-content and pH-values at the beginning and end of the exposure period were measured. Based on the effect of test chemical on mobility of the test organism, the 48 hr EC0, EC50 and EC100 value was determined to be 1, 10.8 and 100 mg/l, respectively. Thus, test chemical was considered as toxic to aquatic invertebrates at environmental relevant concentrations and hence, considered to be classified in 'aquatic chronic category 3' as per the CLP classification criteria.
In a supporting study, short term toxicity of test chemical was studied on invertebrates. No stock solution was prepared (Experimental study report, 1989). The test substance was added directly to the water in the tanks. Test conducted on Daphnia magna Straus 1820 obtained from CIBA-GEIGY Ltd., Facilities, Basel. Cultures of daphnia are maintained in glass vessels containing approx. 2.5 L of reconstituted water at 20 ± 1°C (water is renewed partially thrice weekly). At each renewal the daphnia are fed a suspension of green algae (Scenedesmus subspicatus) supplemented by a suspension of TETRAMIN-extract in such quantities that the food is consumed after 24h. ≤24h before the start of the test, reproductive daphnia are separated from the young by sieving all individuals through a 800 um seive. This operation is repeated 6h before the start of the test and the young (6-≤24h of age) are retained for the test. Total 20 daphnia per concentration and control 4 replicates of 5 daphnia each were exposed with the test chemical conc. (0.0010, 0.0018, 0.0032, 0.0058, 0.010 0.018, 0.032, 0.058, 0.010 mg/l) in a test beakers covered with watch glasses. The study was performed under static conditions at hardness of 240 mg CaC03/L., temperature of 20 ± 1°C under fluorescent light of approx. 1500 lux, 16 hours daily for 24 hrs. The EC-50 values were calculated according to the maximum likelihood method, probit model (Mc Cullagh, P., Nelder, J.A., 1983: Generalized linear models, Chapman & Hall, London) EC-values were graphically determined on gausso-logarithmic probability paper. The 24 hour EC50 value of test chemical in Daphnia magna based on the effect of immobilisation was determined graphically as 0.088 mg/l and calculated as 0.15 mg/l (95% confidence limits 0.085-0.52 mg/l). The 24 hr EC0 and EC100 was evaluated to be 0.018 mg/l and >0.10 mg/l, respectively.
On the basis of the above results, it can be concluded that the test chemical was considered as toxic to aquatic invertebratesat environmental relevant concentrations and hence, considered to be classified in 'aquatic chronic category 2' as per the CLP classification criteria.
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