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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:
key study
Study period:
March 2018 - May 2018
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Version / remarks:
23 march 2006
Deviations:
yes
Remarks:
The breeding of the organisms is carried out according to method APAT IRSA CNR 8020 appendix 1 . It is believed that these modifications have not had an effect on the quality and integrity of the study and the data produced
GLP compliance:
yes
Analytical monitoring:
yes
Details on sampling:
- Concentrations: 46, 15 e 10 mg/l
- Sampling method: aliquot were taken
- Sample storage conditions before analysis: refrigerated storage 4±2°C
Vehicle:
no
Details on test solutions:
- Separation method : GC
- Conditions (column, mobile phase, etc.): solvent detection column (capillary column DB1, lenght: 60 m, int. diam. 0.53 mm)
- Detection method: FID
- Reproducibility in % (indicate method of evaluation; should be given for stated concentration levels): 20%
- Linearity range: 1-50 mg/l
- Extraction recovery (indicate if results are corrected or not for recoveries): not corrected
- Method of confirmation of identity of measured compound: standard (conc. 46 mg/l)
Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Details on test organisms:
- Strain: PSEUDOKIRCHNERIELLA SUBCAPITATA (KORSHIKOV) F.HINDAK (1990)
- Source (laboratory, culture collection): Breeding of a certified Algaltox F kit
- Age of inoculum (at test initiation): 4/5 days
- Method of cultivation: APAT IRSA CNR 8020 appendix 1 .


ACCLIMATION

- Acclimation period: continuos breeding
- Culturing media and conditions (same as test or not): same as test excluding photoperiod (16 h light/ 8 h dark) and culturing media (see APAT IRSA CNR 8020 appendix 1)
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Test temperature:
20-24°C ( tmin 21.4°C; tmax 22.1°C);
pH:
8.02÷8.43
Nominal and measured concentrations:
1.5, 4.6, 6.8, 10 (measured 7.3 mg/l), 15 (measured 13.3 mg/l), 22, 46 mg/L (measured 47.8 mg/l)
Details on test conditions:
TEST SYSTEM

- Test vessel: flask
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: glass, 50 ml, sample 20 ml
- Aeration: no
- Initial cells density: 104 cell/ml
- Control end cells density: 1.64 x 106 cell/ml
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6


GROWTH MEDIUM

- Standard medium used: OECD TG 201 medium


TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: iso stock solution


OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: CONTINUOUS
- Light intensity and quality: 4400÷8800 lux


EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: [counting chamber )

TEST CONCENTRATIONS
- Spacing factor for test concentrations: Annex 4 OECD 215 (excluding end concentrations)
- Range finding study: yes (1- 10- 100 mg/l)
- Test concentrations: 1.5 – 4.6 – 6.8 – 10 – 15 – 22 - 46 mg/l (definitive test)
- Results used to determine the conditions for the definitive study: yes
Reference substance (positive control):
yes
Remarks:
zinc heptahydrate suplhate
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
19.7 mg/L
Nominal / measured:
meas. (initial)
Conc. based on:
test mat.
Basis for effect:
growth rate
Details on results:
- Exponential growth in the control (for algal test): yes
- Flocculation: no
- Aggregation of algal cells: no
- Any stimulation of growth found in any treatment: no
Reported statistics and error estimates:
The growth rates and the percentages of inhibition were calculated.
The curve dose /effect was done using tese values.
The value of the ErC50 was calculated from the curev dose / effect (calculation made using the Excel software and confirmed with the software R)
Validity criteria fulfilled:
yes
Conclusions:
In a 72h acute toxicty study, the cultures of Pseudokirchneriella subcapitata were exposed to Mercaptamine HCl at measure concentrations of 1.5, 4.6, 6.8, 10, 15, 22, 46 mg/L under static conditions in accordance to OECD guideline 201
The 72h EC50 (calculated form initial measured concentrations) was 19.8 mg/L
This study is classified as reliability 1 and satisfies the guideline requirements for an algal growth inhibition study

Description of key information

Key value for chemical safety assessment

EC50 for freshwater algae:
19.7 mg/L

Additional information