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Diss Factsheets

Ecotoxicological information

Short-term toxicity to aquatic invertebrates

Administrative data

Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
other information
Study period:
From December 5, 1991 to January 13, 1992
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Study design appears to follow EU method C.2 with deviations.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1992
Report date:
1992

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
EU Method C.2 (Acute Toxicity for Daphnia)
Deviations:
yes
Remarks:
No evidence that test concentrations were maintained during exposure.
GLP compliance:
no

Test material

Reference
Name:
Unnamed
Type:
Constituent
Details on test material:
- Name of test material (as cited in study report): TK 13110 (Generic/Trade name: CG 21-1201)
- Batch No.: 1197
- Expiration date of the lot/batch: 09/93
- Storage condition of test material: room temperature
- Purity: 98.3%
- Physical state: white solid

Sampling and analysis

Analytical monitoring:
no

Test solutions

Vehicle:
yes
Details on test solutions:
Stock solutions:
3 g test substance were mixed with 18 g from an aqueous solution containing 0.4% Arkopal (alkylphenol-polyglycol-ether) by means of a marble-mill during about 24 hours. 1 mL from this mixture was mixed with and made up to 100 mL with water making dilution 1:100.

Test concentrations:
- Nominal: 1,8, 3.2, 5.8, 10 and 18 mg test substance/L.
- Controls: Blank: water
Vehicle: 0.643 mg Arkopal/L.
Calculated amounts of the dilution 1:100 to produce the desired test concentrations were given into the water and were homogeneously distributed.

Test organisms

Test organisms (species):
Daphnia magna
Details on test organisms:
- Common name: Daphnia magna
- Strain: Straus 1820
- Source: CIBA-GEIGY Ltd., testing facility
- Feeding during test: none
- Age at study initiation (mean and range, SD): 6-24 h at the start of the test

Study design

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
48 h

Test conditions

Hardness:
240 mg CaCO3/l
Test temperature:
20+/-1°C
pH:
7.7 - 7.8
Dissolved oxygen:
98 - 100%
Salinity:
Freshwater
Nominal and measured concentrations:
1.8, 3.2, 5.8, 10, 18 mg/l (nominal)
Details on test conditions:
TEST SYSTEM
- Test vessel: beakers covered with watch glasses (100 mL solution per beaker)
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): 4

TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reconstituted water
- Intervals of water quality measurement: 0 and 48 hours
- Reconstituted water containing: 65 mg NaHCO3, 294 mg CaCl2.2H2O, 123 mg MgSO4.7H2O, 6 mg KCl in 1000 mL bidistilled water.
The water was aerated with clean air for at least 24 hours before use.

OTHER TEST CONDITIONS
- Photoperiod: 16 hours fluorescent light daily
- Light intensity: approximately 1500 lux
Reference substance (positive control):
no

Results and discussion

Effect concentrationsopen allclose all
Duration:
48 h
Dose descriptor:
EC0
Effect conc.:
10 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Remarks on result:
other: Observed values
Duration:
48 h
Dose descriptor:
EC50
Remarks:
calculated
Effect conc.:
14 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Remarks on result:
other: 95% confidence limit: 12 - 16 mg/l
Duration:
48 h
Dose descriptor:
EC100
Effect conc.:
18 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Remarks on result:
other: Observed values
Duration:
24 h
Dose descriptor:
EC50
Effect conc.:
> 18 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Details on results:
- Immobilization in controls: no immoblization in blank and vehicle controls
Results with reference substance (positive control):
No reference substance control
Reported statistics and error estimates:
The EC50 values were calculated according to BERKSON, JASA 48 (1953), 569-599.
EC values were graphically determined on gausso-logarithmic probability paper.

Any other information on results incl. tables

Values are based only on nominal concentrations.

Applicant's summary and conclusion