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Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Reference
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
31 March 2020 to 29 June 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)
Version / remarks:
23 March 2006
Deviations:
no
GLP compliance:
yes
Analytical monitoring:
yes
Details on sampling:
- Concentrations: 1.23 mg/L, 3.70 mg/L, 11.11 mg/L, 33.33 mg/L, 100 mg/L
- Sampling method: after 0h, 24h, 48h and 72h 200 µl test solution were transferred into a 96-well microplate
Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: stock solution was prepared by adding 111.1 mg test item to 1000 mL test medium and stirring for 5 min.:
- Controls: negative control
Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Details on test organisms:
TEST ORGANISM
- Strain: 61.81 SAG
- Source (laboratory, culture collection): Culture Collection of Algae at the University of Goettingen
- Method of cultivation: twice a week the stock suspension is inoculated into fresh Holm-Hansen medium under axenic conditions to keep it in exponential growth.
ACCLIMATION
- Culturing media and conditions: Holm-Hansen medium for culturing, OECD 201 medium for testing
- Any deformed or abnormal cells observed: none by microscopy
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Test temperature:
21-24 °C
pH:
7.7-8.2
Nominal and measured concentrations:
Nominal concetrations: 1.23 mg/L, 3.70 mg/L, 11.11 mg/L, 33.33 mg/L, 100 mg/L
Measured concentrations are within 20% deviation from the nominal concentrations.
Details on test conditions:
TEST SYSTEM
- Test vessel: Erlenmeyer glass flasks 100 ml, Schott, Mainz
- Initial cells density: 7 x 10^4 cells/ml
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates):6


GROWTH MEDIUM
- Standard medium used: yes

OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 24h
- Light intensity and quality: 80.5 µE m/s +/- 9.8%


EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: cell counter
- Chlorophyll measurement: with fluorescence microplate reader (excitation at 465 nm and emission at 670 nm)

TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3
- Test concentrations: 1.23 mg/L, 3.70 mg/L, 11.11 mg/L, 33.33 mg/L, 100 mg/L
- Results used to determine the conditions for the definitive study: range finding study
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
33.66 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
6 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
3.7 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
10.38 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
3.79 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
3.7 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Details on results:
- Exponential growth in the control: yes
- Observation of abnormalities: no
- Any stimulation of growth found in any treatment: yes, up to 11.11 mg/L after 24h, up tp 3.70 mg/L after 48h and at 1.23 mg/L after 72h
Results with reference substance (positive control):
- Results with reference substance valid? yes (potassium dichromate)
- EC50: 1.19 mg/L
Reported statistics and error estimates:
ECx and LOEC/NOEC for yield and growth rate were determined with the statistical software ToxRat 3.3.0 (ToxRat Solutions GmbH, Alsdorf).

Table 1: Inhibition of yield after 24h, 48h and 72h exposure

Nominal test item concentration (mg/L)

Inhibition of yield (%)

24h

48h

72h

NC

--

--

--

1.23

1.3

-17.9

-20.0

3.70

-30.7

-10.8

4.2

11.11

-6.9

15.7

50.9

33.33

38.5

83.4

91.6

100

56.8

89.6

97.2

Table 2: Inhibition of growth rate after 24h, 48h and 72h exposure

Nominal test item concentration (mg/L)

Inhibition of growth rate (%)

24h

48h

72h

NC

--

--

--

1.23

3.1

-4.7

-3.6

3.70

-17.9

-3.4

1.0

11.11

-5.2

6.2

16.2

33.33

25.7

55.8

54.4

100

40.1

65.5

74.1

Table 3: Effect concentrations for yield and growth rate at the end of the test

(Lowest/No Observed) Effect Concentration

Nominal test item concentration (mg/L)

95 % Confidence Limits (CL)

Yield (72h)

Growth rate (72h)

EC50

10.38

33.66

CL

4.53 – 23.32

16.69-66.69

EC20

5.36

10.84

CL

2.75 – 10.50

3.3 – 10.90

EC10

3.79

6.00

CL

1.87 – 7.70

3.30-10.90

LOEC

33.33

11.11

NOEC

11.11

3.70

Validity criteria fulfilled:
yes
Conclusions:
N1,N3-diallylpropane-1,3-diamine dihydrochloride has inhibitory effects on the growth rate of freshwater algae above concentrations of 3.70 mg/L (=NOEC). The 72-hr ErC50 is 33.66 mg/L.
Executive summary:

In a 72 hour acute toxicity study, the cultures of Raphidocelis subcapitata strain 61.81 SAG were exposed to N1,N3-diallylpropane-1,3-diamine dihydrochloride at nominal concentrations of 0, 1.23, 3.70, 11.11, 33.33 and 100 mg/L under static conditions in accordance with the OECD 201 guideline (23 March 2006).  The NOEC and EC50 values based on growth rate were 3.70 and 33.66 mg/L, respectively.  The % growth inhibition in the treated algal culture as compared to the control ranged from 1 to 74 .

 

Abnormalities were not observed.

 

This toxicity study is classified as acceptable and satisfies the guideline requirements for algae growth inhihition test toxicity study.

 

Results Synopsis

Test Organism: Raphidocelis subcapitata strain 61.81 SAG

Test Type: static

 

72 hr EC10:  6.00 mg /L                       95% C.I.:  3.59 to 9.96 mg/L

72 hr EC50:  33.66 mg/L                95% C.I.:  26.25 to 43.18 mg/L

72 hr NOEC:  3.70 mg/L                   

Endpoint(s) Effected:  growth rate

Description of key information

In a single key study on the acute toxicity of N1,N3-diallylpropane-1,3-diamine dihydrochloride to Raphidocelis subcapitata according to OECD guideline 202, an 72-hr EC50 of 33.66 mg/L based on growth rate was reported. The test was conducted under static conditions and fulfilled all criteria for a valid test.

Key value for chemical safety assessment

EC50 for freshwater algae:
33.66 mg/L
EC10 or NOEC for freshwater algae:
3.7 mg/L

Additional information

Cultures of Raphidocelis subcapitata strain 61.81 SAG were exposed to N1,N3-diallylpropane-1,3-diamine dihydrochloride at nominal concentrations of 0, 1.23, 3.70, 11.11, 33.33 and 100 mg/L under static conditions in accordance with the OECD 201 guideline (23 March 2006).  The NOEC and EC50 values based on growth rate were 3.70 and 33.66 mg/L, respectively. The % growth inhibition in the treated algal culture as compared to the control ranged from 1 to 74.

Abnormalities were not observed.