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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:
2018
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:
no
Qualifier:
equivalent or similar to guideline
Guideline:
EU Method C.3 (Algal Inhibition test)
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Specific details on test material used for the study:
Name: Poly(oxy-1,2-ethanediyl), .alpha.,.alpha.'-(iminodi-2,1-ethanediyl)bis[.omega.-hydroxy-, N-[3-(C10-16-alkyloxy)propyl] derivs., di-Et sulfate-quaternized
Product Description: C10-16-alkyletherpropylamine, ethoxylated, DES Quat
CAS No.: 70983-58-3
Physical state: yellowish to amber viscous liquid at 20 °C
Batch No.: PFS-755-173
Re-certification date of batch: 19 April 2018
Purity: 100 % (UVCB)
Color, Gardner 8.8
pH, 5% in water 5.76
Acid Value , mg KOH/g 20.1
Moisture, % 0.127
Total Amine, mg/g 11.18
Viscosity,cps, #4@60,25C 3280
Appearance @25C pass
Stability: stable under test conditions
Storage condition of test material: Room temperature, protected from light
Analytical monitoring:
yes
Details on sampling:
Chemical analysis of the test item concentrations in the test solutions was performed to determine exposure concentration and stability of the test item during exposure. Substance specific analysis was performed at the test site menal GmbH. The samples were filled into 10 mL glass vials and stored in the freezer (≤ -18 °C). The sampling was conducted according to the following specification:

- After 0 h, 24 h and 48 h exposure, both additional vessels of NC (0 g/l), A (0.5 µg/l), B (1.5 µg/l), C (4.5 µg/l), D (13.5 µg/l) and E (40.5 µg/l) were sampled; one sample per replicate: 4 samples of 6 mL per treatment group.

- At the end of the test (72 h), both additional vessels and 2 replicates of the test vessels from NC, A, B, C, D and E were sampled; one sample per replicate: 4 samples of 6 mL per treatment group.

Of each sampled treatment, one of the analytic samples from 0 h, 24 h, 48 h and 72 h was sent to the analytical laboratory at the test site menal GmbH. The remaining samples were stored as retain samples in the freezer (≤ -18 °C) until finalization of the study.
Vehicle:
no
Details on test solutions:
The stock solution was prepared by adding 4.7 mg test item (including a factor of 1.11 to take into account the dilution caused by addition of the algal inoculum) to 1000 mL test medium and shaking for ca. 1 h using an overhead shaker at 20.5 – 21.1 °C (planned nominal concentration of the stock solution: 4.5 mg/L).
Into each test vessel, 50 mL test solution (including algal inoculum) was transferred. The negative control (NC; test medium) and the test item concentrations were prepared by diluting the stock solution with test medium according to the following scheme (dilution factor of 3). Test item concentration and treatment groups: NC (0 g/l), A (0.5 µg/l), B (1.5 µg/l), C (4.5 µg/l), D (13.5 µg/l) and E (40.5 µg/l). (E)
Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Details on test organisms:
The test organism Raphidocelis subcapitata (Strain No. 61.81 SAG) originates from the Culture Collection of Algae at the University of Goettingen and was cultivated in suspension culture. The strain used for this study has been cultured at Hydrotox GmbH since July 2017. Twice a week, the stock suspension is inoculated into fresh Holm-Hansen medium (composition: 496 mg/L NaNO3, 39 mg/L K2HPO4, 75 mg/L MgSO4×7H2O, 36 mg/L CaCl2×2H2O, 58 mg/L Na2CO3, 10 mg/L Na2EDTA×2H2O, 3 mg/L citric acid, 3 mg/L iron citrate, 0.1144 mg/L H3BO3, 0.0724 mg/L MnCl2× 4H2O, 0.0088 mg/L ZnSO4×7H2O, 0.0032 mg/L CuSO4×5H2O, 0.0010 mg/L Na2MoO4×2H2O, 0.0016 mg/L CoCl2×6H2O) under axenic conditions to keep it in exponential growth.
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Hardness:
The test was performed with OECD TG 201 medium according to OECD 201 (2006).
Test temperature:
The temperature during the exposure was 22.3 – 23.2 °C.
pH:
The pH was 7.65 – 7.96 in the control and 7.71 – 8.14 in the test item treatment.
Dissolved oxygen:
not specified
Salinity:
The test was performed with OECD TG 201 medium according to OECD 201 (2006).
Conductivity:
The test was performed with OECD TG 201 medium according to OECD 201 (2006).
Nominal and measured concentrations:
As all measured test item concentrations are within ± 20 % of the nominal concentration, according to OECD 201 (2006), all results are given in relation to the nominal test item concentrations.
Reference substance (positive control):
yes
Remarks:
potassium dichromate
Key result
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
4.5 µg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
cell number
Key result
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
10.47 µg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
cell number
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
18.21 µg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
cell number
Key result
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
13.5 µg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Key result
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
15.49 µg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
28.56 µg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Results with reference substance (positive control):
Quality assurance takes place at regular intervals by testing the sensitivity of the test organisms to the reference item potassium dichromate. The recent quality testing was performed in December 2017 which resulted in an ErC50 (72 h) of 1.18 mg/L (CL 95 %: 0.97 - 1.42 mg/L; interlaboratory test result for ErC50: mean of 1.19 mg/L with SD of 0.27 mg/L) and an EyC50 (72 h) of 0.61 mg/L (CL 95 %: 0.42 – 0.91 mg/L).
Reported statistics and error estimates:
With the statistical software ToxRat 3.2.1 (ToxRat Solutions GmbH, Alsdorf), ECx and LOEC/NOEC for yield and growth rate were determined.

Results

Criteria of validity

- The biomass (cell concentration) in the control has increased by a factor of 71.5 and therefore ≥ 16 during the test period.  

- The mean coefficient of variation for section-by-section growth rate (day 0 - 1, 1 - 2 and 2 - 3) in the control is 16.5 % and therefore ≤ 35 %.

- The coefficient of variation of average specific growth rate during the test period in the control replicates is 5.6 % and therefore ≤ 7 %.

The test is valid according to OECD Test Guideline 201 (23 March 2006).

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

 Nominal test item concentration [µg/l] Inhibition of growth rate [%]
 24 h  48 h  72 h
 NC  -  -  -
 0.5  20.2  1.0  3.4
 1.5  68.5  10.6  6.4
 4.5  58.2  5.7  2.6
 13.5  12.5  20.7  8.2
 40.5  95.2  85.6  77.3

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

 Nominal test item concentration [µg/l] Inhibition of yield [%]
 24 h  48 h  72 h
 NC  -  -  -
 0.5  26.0  1.7  11.8
 1.5  60.7  23.5  25.0
 4.5  50.4  11.9  6.5
 13.5  18.1  44.3

 31.0

 40.5

 97.4

 96.3

 97.0

Validity criteria fulfilled:
yes
Conclusions:
An algae, growth inhibition test with Raphidocelis subcapitata was performed with five concentrations between 0.5 µg/L and 40.5 µg/L of the test item. The growth rate EC50 was determined at 28.56 µg/L (CI: 18.63 – 44.56 µg/L).
Executive summary:

An algae, growth inhibition test with Raphidocelis subcapitata was performed with five concentrations between 0.5 µg/L and 40.5 µg/L of the test item. As all measured test item concentrations are within ± 20 % of the nominal concentration, according to OECD 201 (2006) and OECD 23 (2000), all results are given in relation to the nominal test item concentrations. All validity criteria were fulfilled. The test is valid according to OECD Test Guideline 201 (23 March 2006).

The following results were obtained:

Growth rate:

EC50 = 28.56 µg/L (CI: 18.63 – 44.56 µg/L)

Yield:

EC50 = 18.21 µg/L (CI: 6.04 – 51.62 µg/L)

Description of key information

An algae, growth inhibition test with Raphidocelis subcapitata was performed with five concentrations between 0.5 µg/L and 40.5 µg/L of the test item. The  growth rate EC50 was determined at 28.56 µg/L (CI: 18.63 – 44.56 µg/L)

Key value for chemical safety assessment

EC50 for freshwater algae:
28.56 µg/L

Additional information