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EC number: 249-323-0 | CAS number: 28950-61-0
- 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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Experiment start date -13 May 1992; Experiment end date-03 June 1992; Study completion date - 14 September 1992.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- Read-across based on grouping of substances (category approach). A detailed category justification is included in chapter 13 of this dossier.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: internal company procedure.
- Derived solution: 1500 mg/l - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea, parthenogenetic females.
- Colony: clone strain from Bundesgesundheitsamt Berlin.
- Source: Bayer AG Leverkusen Laboratories.
- Age: 6 - 24 hours.
- Feeding during test: 0.2 mg/adult daphnia (day 0-3); 0.4 mg/adult daphnia (day 4-7); 0.6 mg/adult daphnia (day 8-21)
- Food type: Scenedesmus subspicatus from fermenter culture. The concentrated algal suspension is prepared fresh weekly and stored maximum of 7 days in the refrigerator. When the algae tend, when fed to the formation of precipitates, a 5-minute ultrasound treatment is recommended. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 21 d
- Test temperature:
- 20 ± 2 °C (maximum in individual test: ± 1 °C).
- pH:
- 7.6 - 8.8
- Dissolved oxygen:
- 87.3 - 128.5 %
- Nominal and measured concentrations:
- 10, 31.6, 100, 316 and 1000 mg/l
- Details on test conditions:
- TEST SYSTEM
- Test vessel: beakers (diameter 5.5 cm, high 9.5 cm), with a coverage of 6 cm of diameter.
- Fill volume: 100 ml/beaker.
- Aeration: not aerated.
- Renewal rate of test solution: thrice a week (on Monday, Wednesday and Friday).
- No. of organisms per concentration: 10 (both tested and control groups).
- Replicates: 10 per concentration.
TEST MEDIUM
- Intervals of water quality measurement: once a week.
OTHER TEST CONDITIONS
- Photoperiod: 16 h light / 8 h darkness
- Light intensity: ca. 1700 lux
- Irradiation: 25 µE/m^2 x s
EFFECT PARAMETERS MEASURED: reproduction, mobility. - Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 6.59 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 31.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- Immoobilization EC50 (21d): 31.6 -100 mg/l (nominal)
Reproductive EC50 (21d): 30.2 mg/l (probit-analysis based on nominal concentrations). - Validity criteria fulfilled:
- yes
- Remarks:
- The mortality of the parent animals does not exceed 20 % at the end of the test, in the control; nevertheless there are no information about the mean number of live offspring produced per parent animal surviving at the end of the test
- Conclusions:
- The reproductive NOEC (21 d) was found to be 6.59 mg/l (geom. mean).
- Executive summary:
Method
The test substance chronic toxicity on aquatic invertebrates (Daphnia Magna) was evaluated according to the OECD guideline 211.
The nominal concentrations used were: 10, 31.6, 100, 316 and 1000 mg/l.
Results
Reproductive NOEC (21 d): 6.59 mg/l (geom. mean)
Mortality/immobilization NOEC (21 d): 31.6 mg/l (nominal)
Reference
Conc (mg/l) | Immobilization/mortality of parents at 21 day | Reproduction rate (R21) | ||
Pup/parent | % | |||
Control | 0 | 0 | 92.0 | 100 |
10 | 0 | 0 | 91.6 | 99.6 |
31.6 | 0 | 0 | 42.1 | 45.8 |
100 | 10 | 100 | 0.0 | 0.0 |
316 | 10 | 100 | 0.0 | 0.0 |
1000 | 10 | 100 | 0.0 | 0.0 |
Concentration (mg/l) | Reproduction rate at the 21th day | Standard Deviation | Variation coefficient (%) |
Control | 92.0 | 11.9 | 12.9 |
10 | 91.6 | 10.2 | 11.1 |
31.6 | 42.1 | 22.0 | 52.3 |
100 | 0.0 | 0.0 | 0.0 |
316 | 0.0 | 0.0 | 0.0 |
1000 | 0.0 | 0.0 | 0.0 |
Control
Day |
Puppies | Stillbirths | ||||||||||||
1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | 3 | 5 | 6 | 7 | |
0 | ||||||||||||||
1 | ||||||||||||||
2 | ||||||||||||||
3 | ||||||||||||||
4 | ||||||||||||||
5 | ||||||||||||||
6 | # | # | # | # | ||||||||||
7 | # | # | # | # | # | # | ||||||||
8 | ||||||||||||||
9 | 10 | 15 | 10 | 15 | ||||||||||
10 | ||||||||||||||
11 | ||||||||||||||
12 | 5 | 16 | 15 | 10 | 11 | 16 | 17 | 15 | 18 | 13 | ||||
13 | ||||||||||||||
14 | 15 | 22 | 17 | 16 | 25 | 16 | 10 | 1 | 2 | 2T | 1T | 1T | 1T | |
15 | ||||||||||||||
16 | 16 | 30 | 18 | 10 | 33 | 7 | 11 | 8 | 30 | 30 | ||||
17 | ||||||||||||||
18 | ||||||||||||||
19 | 20 | 20 | 18 | 21 | 13 | 22 | 16 | 11 | 33 | 8 | ||||
20 | ||||||||||||||
21 | 26 | 21 | 26 | 23 | 15 | 32 | 24 | 28 | 40 | |||||
Reproduction rate at the 21th day |
92 | 109 | 94 | 80 | 72 | 102 | 84 | 87 | 92 | 108 | 2T | 1T | 1T | 1T |
T: dead pup
Concentration of 10 mg/l
Day |
Puppies | Stillbirths | ||||||||||||
1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | 4 | 8 | 9 | 10 | |
0 | ||||||||||||||
1 | ||||||||||||||
2 | ||||||||||||||
3 | ||||||||||||||
4 | ||||||||||||||
5 | ||||||||||||||
6 | # | # | # | # | # | # | # | # | # | |||||
7 | # | |||||||||||||
8 | ||||||||||||||
9 | 13 | 20 | 14 | 20 | 22 | 18 | 23 | 15 | 12 | |||||
10 | ||||||||||||||
11 | ||||||||||||||
12 | 14 | 23 | 8 | 18 | 16 | 20 | 10 | 10T | ||||||
13 | ||||||||||||||
14 | 4 | 2 | 20 | 23 | 21 | 23 | 20 | 1T | ||||||
15 | ||||||||||||||
16 | 25 | 28 | 8 | 33 | 26 | 20 | 7T | |||||||
17 | ||||||||||||||
18 | ||||||||||||||
19 | 31 | 23 | 20 | 21 | 15 | 16 | 28 | 24 | 30 | 1T | 3T | |||
20 | ||||||||||||||
21 | 28 | 15 | 33 | 24 | 26 | 26 | 27 | 10 | ||||||
Reproduction rate at the 21th day |
115 | 88 | 98 | 87 | 90 | 82 | 89 | 100 | 85 | 92 | 1T | 1T | 3T | 17T |
T: dead pup
Concentration of 31.6 mg/l
Day |
Puppies | |||||||||
1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | |
0 | ||||||||||
1 | ||||||||||
2 | ||||||||||
3 | ||||||||||
4 | ||||||||||
5 | ||||||||||
6 | # | # | # | # | # | |||||
7 | # | |||||||||
8 | ||||||||||
9 | # | # | # | # | ||||||
10 | ||||||||||
11 | ||||||||||
12 | 6 | 6 | 15 | 18 | 5 | 11 | 10 | 10 | 2 | |
13 | ||||||||||
14 | 23 | 28 | 31 | 5 | ||||||
15 | ||||||||||
16 | 6 | 10 | 10 | 20 | 10 | 8 | 11 | |||
17 | ||||||||||
18 | ||||||||||
19 | 8 | 16 | 5 | 16 | 4 | 22 | 7 | 15 | ||
20 | ||||||||||
21 | 25 | 16 | 15 | 6 | 6 | 10 | 5 | |||
Reproduction rate at the 21th day |
68 | 32 | 64 | 80 | 25 | 53 | 26 | 28 | 19 | 26 |
T: dead pup
Concentration of 100 mg/l
Day |
Puppies | |||||||||
1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | |
0 | ||||||||||
1 | ||||||||||
2 | ||||||||||
3 | ||||||||||
4 | ||||||||||
5 | + | + | + | + | + | + | + | |||
6 | ||||||||||
7 | + | |||||||||
8 | ||||||||||
9 | + | + | ||||||||
10 | ||||||||||
11 | ||||||||||
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15 | ||||||||||
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17 | ||||||||||
18 | ||||||||||
19 | ||||||||||
20 | ||||||||||
21 | ||||||||||
Reproduction rate at the 21th day |
+: dead in the mother's brood chamber
Concentration of 316 mg/l
Day |
Puppies | |||||||||
1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | |
0 | ||||||||||
1 | ||||||||||
2 | ||||||||||
3 | ||||||||||
4 | ||||||||||
5 | + | + | + | + | + | + | + | + | + | + |
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19 | ||||||||||
20 | ||||||||||
21 | ||||||||||
Reproduction rate at the 21th day |
+: dead in the mother's brood chamber
Concentration of 1000 mg/l
Day |
Puppies | |||||||||
1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | |
0 | ||||||||||
1 | ||||||||||
2 | ||||||||||
3 | ||||||||||
4 | ||||||||||
5 | + | + | + | + | + | + | + | + | + | + |
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21 | ||||||||||
Reproduction rate at the 21th day |
+: dead in the mother's brood chamber
MEASURED CONCENTRATIONS
Sampling time | Concentration | ||
Nominal | Measured (mg/l) | % | |
Initial condition | Control | < 0.2 | - |
10 | 6.4 | 64 | |
100 | 804.7 | 80.5 | |
48 hrs | Control | < 0.2 | - |
10 | 7.2 | 72 | |
100 | 632.6 | 63.3 | |
Renewal | Control | < 0.2 | - |
10 | 6.5 | 65 | |
100 | 727.4 | 72.7 | |
72 hrs | Control | < 0.2 | - |
10 | 6.3 | 63 | |
100 | 667.7 | 66.8 |
Description of key information
NOEC 21d daphnids = 6.59 mg/l
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 6.59 mg/L
Additional information
A Daphnia magna reproductive study is available on the analogous substance CAS 16470-24-9 with NOEC reported as geometric mean because the difference between nominal and measured values is often greater than ± 20 %. The test was performed on a similar substance within the category of Stilbene Fluorescent Whitening Agents, the analogous dihydroxyethyl derivative tetrasulphonated sodium salt. The diethylamino substituent is less polar, less reactive and makes the molecule slightly less soluble compared to the dihydroxyethylamino derivative. The latter can therefore considered as a representative conservative analogous for the aquatic toxicity because of the higher bioavailability and higher reactivity with organic substrates. The Category Justification Report is attached to the section 13.
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.
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