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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:
3-6 April 2020
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
Deviations:
yes
Remarks:
The vessel temperature in the range-finding test was outwith the 21 – 24 °C (±2 °C) range.
GLP compliance:
yes (incl. QA statement)
Specific details on test material used for the study:
66% purity
Aqueous solution
Analytical monitoring:
no
Vehicle:
no
Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Details on test organisms:
TEST ORGANISM
- Common name: Pseudokirchneriella subcapitata
- Strain: 278/4
- Source: stock laboratory cultures
- Method of cultivation: autoclaved freshwater at 120 °C for 15 minutes with nutrient medium (3N-BBM+V) 7 days before test commencement. They were then incubated at approximately 21 2 °C under constant illumination to be used as the inoculum source for subsequent toxicity tests. The initial inoculum was checked microscopically using a haemocytometer.

ACCLIMATION
- Acclimation period: 7 days
- Culturing media and conditions same as test
- Any deformed or abnormal cells observed: no
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Hardness:
Not specified
Test temperature:
21 to 24 °C controlled at 2 °C
pH:
7.5 ±0.1. Not increased during the test by more than 1.5 relative to the pH of the growth medium
Dissolved oxygen:
Not specified
Salinity:
Not specified
Conductivity:
Not specified
Nominal and measured concentrations:
1, 3.2, 10, 32, 100 mg/L
Details on test conditions:
TEST SYSTEM
- Test vessel: glass conical flasks
- Material, size, headspace, fill volume: borosilicate, 100ml
- Aeration: flasks were loosely covered with aluminium foil caps and mounted on an orbital shaker
- Initial cells density: approximately 5 x 10^3 – 10^4 cells per millilitre
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6

GROWTH MEDIUM
- Standard medium used: yes, US EPA culture medium

TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: The purified water used in this test was treated by reverse osmosis followed by electro-deionisation. This process produces water of an equivalent grade to deionised water. The purified water was held in two 75 litre header tanks until use.

OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: pH of the culture medium was adjusted if required, by adding 1M HCl, or NaOH to give a pH of 7.5 ±0.1.
- Light intensity and quality: Between 4440 to 8880 lx. The illumination consisted of 40 W cool white LED light which was mounted at a distance of approximately 40 cm directly above the test area.

TEST CONCENTRATIONS
- Spacing factor for test concentrations:
- Justification for using less concentrations than requested by guideline:
- Range finding study: The range-finding test employed four concentrations 1000, 100, 10 and 1 mg/l with one replicate per concentration; plus, four controls
- Test concentrations: The definitive test employed five concentrations (1, 3.2, 10, 32, 100 mg/l) with three replicates per concentration; plus, six controls.
- Results used to determine the conditions for the definitive study: Calculated 72h EC(r)50 in the range-finding test was 5.33 mg/l
Reference substance (positive control):
yes
Remarks:
potassium dichromate
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
ca. 5.11 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
EC90
Effect conc.:
ca. 9.02 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
ca. 3.43 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
24 h
Dose descriptor:
EC50
Effect conc.:
ca. 1.42 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
ca. 1 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Details on results:
- Exponential growth in the control (for algal test): yes
Results with reference substance (positive control):
- Results with reference substance valid? Yes
- EC50: 1.16 mg/L
Reported statistics and error estimates:
Results for both range-finding and definitive tests were calculated by linear regression within the CETIS suite of statistical analysis.
Validity criteria fulfilled:
yes
Conclusions:
The 72-hour EC50 was ca. 5.11 mg/L and the 72-hour NOEC was ca. 1 mg/L.
Executive summary:

The aquatic phase toxicity of 2-propen-1-amine, N-2-propen-1-yl, hydrochloride to the freshwater unicellular algae Pseudokirchneriella subcapitata was determined during a GLPcompliant study performed according to the OECD Testing Guideline 201.


A range-finding test was conducted over 72h to determine the approximate concentrations at which growth rate effects were observed.


The range-finding test employed four concentrations 1000, 100, 10 and 1 mg/L with one replicate per concentration; plus, four controls.


As a result of this range-finding test, concentrations of 1, 3.2, 10, 32, 100 mg/L were used during the definitive test.


The 72-hour EC50 was ca. 5.11 mg/L and the 72-hour NOEC was ca. 1 mg/L. 

Description of key information

The aquatic phase toxicity of 2-propen-1-amine, N-2-propen-1-yl, hydrochloride to the freshwater unicellular algae Pseudokirchneriella subcapitata was determined during a GLPcompliant study performed according to the OECD Testing Guideline 201.


A range-finding test was conducted over 72h to determine the approximate concentrations at which growth rate effects were observed.


The range-finding test employed four concentrations 1000, 100, 10 and 1 mg/L with one replicate per concentration; plus, four controls.


As a result of this range-finding test, concentrations of 1, 3.2, 10, 32, 100 mg/L were used during the definitive test.


The 72-hour EC50 was ca. 5.11 mg/L and the 72-hour NOEC was ca. 1 mg/L.


The EC50 for the substance was 5.11 mg/L and the substance is not readily biodegradable.  Therefore, the substance is classifield as aquatic toxicity category 2.

Key value for chemical safety assessment

EC50 for freshwater algae:
5.11 mg/L
EC10 or NOEC for freshwater algae:
1 mg/L

Additional information