Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

Administrative data

Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Comparable to guideline study; well documented study report; test material measured analytically

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2011
Report date:
2011

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.3 (Algal Inhibition test)
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Details on test material:
- Physical state: colorless colourless viscous liquid

Sampling and analysis

Analytical monitoring:
yes

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method:
1) OECD 2000. Guidance Document on Aquatic Toxicity Testing of Difficult Substances and Mixtures

A determination of the General PhysicoChemical Properties on the test material gave a water solubility value of less than or equal to 0.138 mg/L at 20 degrees C. Pre-study solubility work conducted indicated that it was not possible to obtain a testable solution of the test material using traditional methods of preparation (e.g., ultrasonication and high shear mixing). Therefore a media preparation trial was conducted in order to determine the solubility of the test material under test conditions. A saturated solution was prepared from an initial test material dispersion at a concentration of 500 mg/L.

- Evidence of undissolved material (e.g. precipitate, surface film, etc):
At the start of the test all control and test cultures were observed to be clear colourless solutions. After the 72-hour test period all control and test cultures were observed to be pale green dispersions.

Test organisms

Test organisms (species):
Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
Details on test organisms:
TEST ORGANISM
- Common name: Green alga
- Strain: Desmodesmus subspicatus, strain CCAP 276/20
- Source (laboratory, culture collection): Liquid cultures were obtained from the Culture Collection of Algae and Protozoa (CCAP), Dunstaffnage Marine Laboratory, Oban, Argyll, Scotland.
- Age of inoculum (at test initiation):
- Method of cultivation: Cultures were maintained in the laboratory at a temperature of 21 degrees C under constant aeration and constant illumination.

Study design

Test type:
static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
72 h
Remarks on exposure duration:
This experimental design conforms to a limit test to confirm that at the highest attainable test concentration no effect on growth was observed.

Test conditions

Test temperature:
Temperature was maintained at 24C throughout the test
pH:
The pH values of the control cultures were observed to increase from 7.3 at 0 hours to 7.6 at 72 hours. The pH deviation in the control cultures was less than 1.5 pH units after 72 hours and therefore was within the limits given in the test guidelines. The pH values of the saturated test material concentration were 7.2 at 0 hours and 7.6 and 72 hours.
Salinity:
not applicable.
Nominal and measured concentrations:
Control
Mean Measured 0.45 mg/L
Details on test conditions:
TEST SYSTEM
- Test vessel:
As in the range finding test 250 mL glass conical flasks were used. Six flasks each containing 100 mL of solution were used for the control and 0.45 mg/L treatment group. The control group was maintained under identical conditions but not exposed to the test material. Preculture conditions gave an algal suspension in log phase growth characterized by a cell density of 3.61x105 cells per mL. Inoculation of 2 litres of test medium with this algal suspension gave an initial nominal cell density of 4x103 cells per mL. The flasks were plugged with polyurethane foam bungs and incubated at 24 degrees C under continuous illumination (intensity approximately 7000 lux) provided by warm white lighting (380 to 730 nm) and constantly shaken at approximately 150 rpm for 72 hours. Samples were taken at 0, 24, 48, and 72 hours and the cell densities determined using a Coulter Multisizer Particle Counter.


GROWTH MEDIUM
The culture medium used for the range finding and definitive tests was the same as that used to maintain the stock culture. Stock solutions of the culture medium was prepared using reverse osmosis purified deionized water and the pH adjusted to 7.5.

- Standard medium used: yes
Reference substance (positive control):
yes
Remarks:
A positive control used potassium dichromate as the reference material. Exposure conditions and data evaluation for the positive control were similar to those in the definitive test. The results from the positive control with potassium dichromate were wit

Results and discussion

Effect concentrationsopen allclose all
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
> 0.35 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
other: Growth rate and biomass
Remarks on result:
other: The EC50 values based on the geometric mean measured test concentration were greater than 0.35 mg/L and there were no toxic effects at saturation.
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
ca. 0.45 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
test mat.
Basis for effect:
other: Growth rate and biomass
Remarks on result:
other: The EC50 value based on the 0 hour mean measured test concentration gave EC50 values of greater than 0.45 mg/L.
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
0.35 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
other: Growth rate and biomass
Remarks on result:
other: The No Observed Effect Concentration was 0.35 mg/L the highest test concentration possible and demonstrated that there were no toxic effects at saturation.
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
0.45 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
test mat.
Basis for effect:
other: Growth rate and biomass
Remarks on result:
other: The No Observed Effect Concentration was 0.45 mg/L and no toxic effects at saturation were observed.
Details on results:
- Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test):
All test and control cultures were inspected microscopically at 72 hours. There were no abnormalities detected in any of the control of test cultures at 72 hours.

Any other information on results incl. tables

Table. Inhibition of Growth Rate and Yield in the Definitive Test

0-Hour Mean Measured Test Concentration (mg/L)

Growth Rate (cells/ml/hour)

 

 

  0 to 72 hours              % Inhibition

Yield (cells/mL)

 

 

0 to 72 hours                % Inhibition

Control

R1

R2

R3

R4

R5

R6

Mean

SD

 

0.06

0.056

0.058

0.060

0.061

0.059

0.059

0.002

 

 

 

 

--

 

3.03E5

2.17E5

2.51E5

2.96E5

3.1E5

2.72E5

2.75E5

3.57E4

 

 

 

 

--

0.45 Saturated Solution

R1

R2

R3

R4

R5

R6

Mean

SD

 

 

0.065

0.059

0.064

0.059

0.066

0.070

0.064

0.004

 

 

[10]

0

[8]

0

[12]

[19]

[8]

 

 

4.40E5

2.68E5

3.97E5

2.77E5

4.72E5

6.25E5

4.13E5

1.33E5

 

 

 

 

 

 

 

 

[50]

[Increase in growth as compared to controls]

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
Exposure of Desmodesmus subspicatus to the test material resulted in no toxic effects at saturation. The EC50 values were greater than the level of saturation, which at 0 hours was measured at 0.45 mg/L and using the geometric mean measured test concentrations over the 72 hour period was greater than 0.35 mg/L. The No Observed Effect Concentration was greater than the level of saturation, which was measured at 0.45 mg/L at time 0 hours.
Executive summary:

Introduction. A study was performed to assess the effect of the test material on the growth of the green algaDesmodesmus subspicatus. The method followed that described in the OECD Guidelines for Testing of Chemicals (2006) No. 201, “Freshwater Alga and Cyanobacteria, Growth Inhibition Test” referenced as Method C.3 of Commission Regulation (EC) No 440/2008.

 

Methods:

A determination of the General Physico-Chemical Properties study conducted on the test material gave a water solubility value for the test material of less than or equal to 0.138 mg/L at 20 degrees C. A pre-study media preparation trial indicated that a dissolved test material concentration of approximately 0.1 mg/L was obtained from a saturated solution method of preparation indicating this to be the limit of water solubility of this material under test conditions.

 

Following a preliminary range-finding test,Desmodesmus subspicatuswas exposed to a solution of the test material at a 0 hour mean measured test concentration of 0.45 mg/L for 72 hours, under constant illumination and shaking at a temperature of 24 degrees C. The test material solution was prepared by shaking an excess (500 mg/L) of test material in culture medium in sealed vessels at approximately 300 rpm for 24 hours. Potential undissolved material was removed by centrifugation at 10000 g for 30 minutes. Samples of the algal populations were removed daily and cell concentrations determined for each control and treatment group, using a Coulter Multisizer Particle Counter.

 

Results:

Exposure ofDesmodesmus subspicatusto the test material, based on the 0 hour mean measured test concentration gave EC50 values of greater than 0.45 mg/L which is greater than the level of saturation. This study showed that there were no toxic effects at saturation, and the No Observed Effect Concentration was 0.45 mg/L the level of saturation.