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Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Administrative data

Link to relevant study record(s)

Reference
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
18.10.2016-21.10.2016
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Justification for type of information:
Experiment test result performed using standard test guidelines.
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Principles of method if other than guideline:
Short term toxicity to algae was performed according to the OECD guideline 201 in a static system.
GLP compliance:
not specified
Specific details on test material used for the study:
Name of test material (as cited in study report): Amaranth dye
Molecular formula (if other than submission substance): C20H11N2Na3O10S3
Molecular weight (if other than submission substance): 604.47
Smiles notation (if other than submission substance): c1ccc2c(c1)c(ccc2S(=O)(=O)[O-])N=Nc3c4ccc(cc4cc(c3O)S(=O)(=O)[O-])S(=O)(=O)[O-].[Na+].[Na+].[Na+]
InChl (if other than submission substance): 1S/C20H14N2O10S3.3Na/c23-20-18(35(30,31)32)10-11-9-12(33(24,25)26)5-6-13(11)19(20)22-21-16-7-8-17(34(27,28)29)15-4-2-1-3-14(15)16;;;/h1-10,23H,
(H,24,25,26)(H,27,28,29)(H,30,31,32);;;/q;3*+1/p-3
Substance type: Organic
Physical state: Solid
Analytical monitoring:
not specified
Details on sampling:
No data available
Vehicle:
yes
Details on test solutions:
The stock solution (200 g/L) was prepared by dissolving brown powder in OECD growth medium. Test solutions of required concentration were prepared by mixing the stock solution of the test sample with OECD growth medium and inoculum culture.
Test organisms (species):
Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
Details on test organisms:
TEST ORGANISM
- Common name:
- Strain: 86.81 SAG
- Source (laboratory, culture collection): Institute of botany of the ASCR
- Initial biomass concentration: 5x10(3) cells /ml
- Method of cultivation: No data available

ACCLIMATION - No data available
- Acclimation period:
- Culturing media and conditions (same as test or not):
- Any deformed or abnormal cells observed:
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Remarks on exposure duration:
±1 hour
Post exposure observation period:
No data available
Hardness:
No data available
Test temperature:
23±2°C
pH:
Test at highest concentration: 8 changed to 7.9 during tests
Control: 8.0 (changed to 8.1 during test)
Dissolved oxygen:
No data available
Salinity:
No data available
Conductivity:
No data available
Nominal and measured concentrations:
0,12.5, 25, 50, 100, 200 mg/l
Details on test conditions:
TEST SYSTEM
- Test vessel: 50 ml Glass vessel
- Type (delete if not applicable): closed (with air permeable stopper)
- Sample volume: 7.5/ 50 ml
- Initial cells density: 5x10(3) cells/ml
- No. of vessels per concentration (replicates): 3

GROWTH MEDIUM
- Standard medium used: yes

OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: Continuous
- Light intensity and quality: 6000-8000 lx

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: microscope with counting chamber Cyrus I or electronic particle counter.
- Other: ErC50 was calculated using non-linear regression by the software Prism 4.0
Reference substance (positive control):
yes
Remarks:
Potassium dichromate (K2Cr2O7)
Key result
Duration:
72 h
Dose descriptor:
other: ErC50
Effect conc.:
356.2 mg/L
Nominal / measured:
meas. (not specified)
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: 95% CL: 266.8 - 475.7
Details on results:
No data available
Results with reference substance (positive control):
Results with reference substance valid
- ErC50: 0.69 mg/L
Reported statistics and error estimates:
ErC50 was calculated using non-linear regression by the software Prism 4.0
Validity criteria fulfilled:
yes
Conclusions:
The median effective concentration (ECr50) for the test substance 2,7-Naphthalenedisulfonic acid, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl), sodium salt (Amaranth dye) in Desmodesmus subspicatus was determined to be 356.2 mg/L on the basis of effects on growth rate in a 72 hour study.
Executive summary:

Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance 2,7-Naphthalenedi- sulfonic acid, 3-hydroxy-4-[(4-sulfo- 1-naphthal - enyl), sodium salt (Amaranth dye) according to OECD Guideline 201.

The test substance was dissolved in OECD growth medium and tested at the concentrations 0, 12.5, 25, 50, 100, 200 mg/L. Effects on the growth rate of the organism were studied.

The median effective concentration (ErC50) for the test substance, 2,7-Naphthalenedisulfonic acid, 3-hydroxy-4-[(4-sulfo-1- -naphthalenyl), sodium salt, in Desmodesmus subspicatus was determined to be 356.2 mg/L.

This value indicates that the substance is likely to be non-hazardous to aquatic algae and can not be classified as toxic as per the CLP criteria.

Description of key information

Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance 2,7-Naphthalenedi- sulfonic acid, 3-hydroxy-4-[(4-sulfo- 1-naphthal - enyl), sodium salt (Amaranth dye) according to OECD Guideline 201. The test substance was dissolved in OECD growth medium and tested at the concentrations 0, 12.5, 25, 50, 100, 200 mg/L. Effects on the growth rate of the organism were studied. The effective concentration (ErC50) for the test substance, 2,7-Naphthalen -edisulfonic acid, 3-hydroxy-4-[(4-sulfo-1- -naphthalenyl), sodium salt, in Desmodesmus subspicatus was determined to be 356.2 mg/L. This value indicates that the substance is likely to be non-hazardous to aquatic algae and cannot be classified as toxic as per the CLP criteria.

 

Key value for chemical safety assessment

EC50 for freshwater algae:
356.2 mg/L

Additional information

Based on the various data for the read across chemical (915-67-3), and (4548-53-2) which was structually and chemically more similar to the target chemical (7-Hydroxy-8- (4-sulpho-1-naphthyl) azo) naphtha- alene-1,3-disulphonato(3-))aluminium (15876-47-8)l various studies has been reviewed to check the toxic nature of the target chemical on the growth and other activity of the aquatic life:

 

In the first weight of evidence study for RA chemical 2,7-Naphthalenedisulfonic acid, 3-hydroxy- 4-[(4-sulfo-1-naphthalenyl), sodium salt (Amaranth dye) (915-67-3), ABITEC lab report, 2016. Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance 2,7-Naphthalenedi- sulfonic acid, 3-hydroxy-4-[(4-sulfo- 1-naphthal - enyl), sodium salt (Amaranth dye) according to OECD Guideline 201. The test substance was dissolved in OECD growth medium and tested at the concentrations 0, 12.5, 25, 50, 100, 200 mg/L. Effects on the growth rate of the organism were studied. The effective concentration (ErC50) for the test substance, 2,7-Naphthalen -edisulfonic acid, 3-hydroxy-4-[(4-sulfo-1- -naphthalenyl), sodium salt, in Desmodesmus subspicatus was determined to be 356.2 mg/L. This value indicates that the substance is likely to be non-hazardous to aquatic algae and cannot be classified as toxic as per the CLP criteria.

 

Similarly in the second experimental weight of evidence study for RA chemical Disodium 3-[(2,4-dimethyl-5-sulphonatophenyl) azo]-4-hydroxy naphthalene-1-sulphonate (4548-53-2) ABITEC report, 2016. Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance Disodium 3-[(2,4-dimethyl -5-sulphonatophenyl) azo]-4-hydroxynaphthalene-1-sulphonate according to OECD Guideline 201. The test substance was dissolved in OECD growth medium and tested at the concentrations 0, 0, 12.5, 25, 50, 100 and 200 mg/L. Effects on the growth rate of the organism were studied. The median effective concentration (ErC50) for the test substance, Disodium 3-[(2,4-dimethyl-5-sulphonatophenyl)azo]-4-hydroxynaphthalene-1-sulphonate, in Desmodesmus subspicatus was determined to be 276.1 mg/L. Based on this ErC50 value and after comparing with CLP criteria for aquatic classification of the substance it is concluded that the substance Disodium 3-[(2,4-dimethyl-5-sulphonatophenyl)azo]-4-hydroxynaphthalene-1-sulphonate does not exhibit toxicity to aquatic algae (Desmodesmus subspicatus).

Based on the above RA cas which was structually and chemically more similar to the target chemical data obtain from various databases, from the sources it was concluded that the (7-Hydroxy-8-((4-sulpho-1-naphthyl) azo) naphtha- alene-1,3-disulphonato(3-)) aluminium does not exhibit toxicity to aquatic algae and cyanobacteria. Hence the test chemical is not likely to classify as a toxic as per the criteria mentioned in CLP regulation.