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Diss Factsheets

Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Administrative data

Link to relevant study record(s)

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Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
weight of evidence
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study with acceptable restrictions
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Version / remarks:
1980
GLP compliance:
not specified
Specific details on test material used for the study:
a 40% solution of dimethylamine in water was used for the test
supplied by Fluka, 99% purity
Analytical monitoring:
not specified
Vehicle:
not specified
Details on test solutions:
no further information given
Test organisms (species):
Chlorella pyrenoidosa
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
96 h
Hardness:
culture medium used
hardness as CaCO3 = 90
Test temperature:
20+-1°C
pH:
8.7+-0.2 of culture medium
Dissolved oxygen:
no information
Nominal and measured concentrations:
nominal: 10, 18, 32, 56, 100, 180 mg/l
control
Details on test conditions:
test solutions with an initial cell density of 10E-8 cells/litre (100ml) where added to 200 ml Erlenmeyer flask stoppered with a cotton plug and placed on a mechanical shaker under fluorescent light (7.5 W x m E-2). the cells were counted in a model ZbI Coulter Counter using a 70µm aperture. The test were carried out in triplicate
Reference substance (positive control):
not specified
Duration:
96 h
Dose descriptor:
EC50
Effect conc.:
30 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
96 h
Dose descriptor:
EC50
Effect conc.:
22 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
cell number
Reported statistics and error estimates:
The EC50 values and their 95% confidence intervals were calculated according to Lichtfield and Wilkoxon (1949) method
Population growth curve were analysed according to Kooyman et al. 1983
Validity criteria fulfilled:
not specified
Executive summary:

For dimethylamine an EC50 value of 30 mg/l (growth rate) were determined in a 96 h algae test equivalent or similar to OECD guideline 201.

Endpoint:
toxicity to aquatic algae and cyanobacteria
Data waiving:
study technically not feasible
Justification for data waiving:
other:
Justification for type of information:
Titanium tetrakic(dimethylammonium) is an organometalic compound. It can only be handled air-free. It is a flammable liquid and very unstable (see also chapter 1.2 or 5.1.2 or 13). Within seconds it reacts violently in contact with moisture or water. Aquatic toxicity studies are technically not feasible. The decomposition products are dimethylamine and titanium oxide. Dimethylamine is a highly flammable gas. But dimethylamine is a well water soluble substance and was tested for acute aquatic toxicity.
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
weight of evidence
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study without detailed documentation
Qualifier:
according to guideline
Guideline:
other: EPA guideline no further information was given
GLP compliance:
not specified
Specific details on test material used for the study:
dimethylamine as 40% aqueous solution
Analytical monitoring:
yes
Details on sampling:
at the beginning of the test
frequently checking during the test
at the end of the test
Vehicle:
no
Test organisms (species):
Selenastrum sp.
Details on test organisms:
Selenastrum capricornutum
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
96 h
Remarks on exposure duration:
96 h was in accordance with the EPA guideline
Post exposure observation period:
yes until 7 days after
Hardness:
no information
Test temperature:
no information
pH:
no information
Dissolved oxygen:
no information
Nominal and measured concentrations:
nominal: 0; 1; 2, 5; 10; 20; 40; 80 mg/l
Details on test conditions:
Algae growth was evaluated by measuring in vivo the fluorimetric units at 48h; 72h; 96h and dafter 7 days
Reference substance (positive control):
not specified
Duration:
96 h
Dose descriptor:
EC50
Effect conc.:
9 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
96 h
Dose descriptor:
EC0
Effect conc.:
2 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
96 h
Dose descriptor:
EC100
Effect conc.:
40 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Reported statistics and error estimates:
The 96h EC50 was extrapolated from the eye fitted empirical curve on log-probability paper with percentages of growth inhibition and the logarithm of concentrations
Validity criteria fulfilled:
not specified
Executive summary:

An EC50 after 96h exposure of 8mg/l was determined for dimethylamine. The test was carried out according to an EPA guideline.

Description of key information

Titanium tetrakic(dimethylammonium) is an organometalic compound. It can only be handled air-free. It is a flammable liquid and very unstable (see also chapter 1.2 or 5.2.1 or 13). Within seconds it reacts violently in contact with moisture or water. Aquatic toxicity studies are technically not feasible. The decomposition products are dimethylamine and titanium oxide. Dimethylamine is a highly flammable gas. But dimethylamine is a well water soluble substance and was tested for acute aquatic toxicity. For dimethylamine an EC50 value of 30 mg/l (growth rate) were determined in a 96 h algae test equivalent or similar to OECD guideline 201 (van Leeuwen, 1985). In a second test (Calamari, 1980) an EC50 of 8mg/l after 96h exposure duration was determined for dimethylamine. The test was carried out according to an EPA guideline.

Key value for chemical safety assessment

Additional information