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Diss Factsheets

Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

Administrative data

Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
14 July - 21 July 2020
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2020
Report date:
2020

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
Version / remarks:
23 March 2006, Annex 5 corrected 28 July 2011
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.3 (Algal Inhibition test)
Version / remarks:
20 May 2008, amended 7 December 2015, for the purpose of its adaptation to technical progress, by Commission Regulation (EU) 2016/266
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Chemical structure
Reference substance name:
N-glycylglycine
EC Number:
209-127-8
EC Name:
N-glycylglycine
Cas Number:
556-50-3
Molecular formula:
C4H8N2O3
IUPAC Name:
N-glycylglycine
Test material form:
solid: crystalline
Details on test material:
Batch Number: S119 0711
Storage conditions: room temperature
Specific details on test material used for the study:
Batch no.: S119 0711
Test item storage: At room temperature, protected from light

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
Samples were taken from all test media including the control at the start of the test (without algae), after 24, 48 and 72 hours of exposure (containing algae). For sampling at the start of the test the samples were taken from the freshly prepared test solutions as well as from the control. For sampling at 24, 48 and 72 hours, the replicates per treatment were pooled prior to sampling. These samples were centrifuged at 4500 g for 10 min to separate the algae.

All samples were diluted with acetonitrile containing 1% conc. ammonia solution to obtain a composition of sample:acetonitrile (9:1; v:v) containing 0.1% conc. ammonia solution. Subsequently, the samples were stored deep-frozen (at about -20 °C) until analysis. In non-GLP preliminary experiments, the test item proved to be stable under these storage conditions.

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
The following test flasks will be set up:
- Test solution: containing test water, test item and algae (six replicates in a limit test and three replicates per test concentration in a full test)
- Control: containing test water and algae (six replicates)
Since the test item is soluble, the single test solution was prepared by adding 100 mg/l of test item to test water in sterile glassware and stirring it for five minutes. 100 ml of the resulting test solution and of the test water without test item used for the control was added to sterile test flasks and inoculated with an exponentially growing preculture of algae.
For the exposure, the test flasks were then placed on an orbital shaker at a nominal shaking speed of about 130 revolutions per minute. The test flasks were repositioned daily during the exposure.

Test organisms

Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Details on test organisms:
TEST ORGANISM
- Test organism: Raphidocelis subcapitata (SAG Nr. 61.81), supplied by the SAG Culture Collection of Algae at Göttingen University, 37073 Göttingen, Germany.
- Culture: 250 ml flask containing 100 ml of OECD medium inoculated with an exponentially growing preculture of Raphidocelis subcapitata.
- Illumination: Continuous, 4440 – 8880 lux ± max. 15% variation, source: Osram Fluora L 18W77 and Osram Daywhite L 18W840 (Osram AG, Winterthur, Switzerland).
- Temperature: 21–24 °C maintained at ±2 °C in a thermo-controlled room.
- Control of sensitivity: For evaluation of the algal quality and the test procedure, potassium dichromate is tested as a positive control twice a year.

Study design

Test type:
static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
72 h

Test conditions

Hardness:
The calculated water hardness of the test water is 24.2 mg/l as CaCO3.
Test temperature:
21–24 °C maintained at ±2 °C in a thermo-controlled room.
pH:
7.8 - 8.8 (the pH of the control should not increase by more than 1.5 units during the test)
Dissolved oxygen:
not reported
Salinity:
not reported
Conductivity:
not reported
Nominal and measured concentrations:
NOMINAL CONCENTRATIONS
Since no relevant inhibitory effects were observed in the non-GLP range-finding test, the definitive test was performed as a limit test at a nominal concentration of 100 mg/l.

MEASURED CONCENTRATIONS
The concentrations of Glycyl-glycine in the test media were determined by HPLC with UV detection in the samples from the test start as well as in the samples after 24, 48 and 72 hours of exposure. These analyses showed that the test item was correctly dosed and remained stable within 80–120% of the nominal concentration. Therefore, the effective concentrations ECx were assessed based on the nominal concentration of the test item.
Details on test conditions:
TEST SYSTEM
- Test vessel: 250 ml flask, all-glass, with 100 ml of test medium, shaken (130 rpm), capped with air permeable stoppers
- Test medium: Reconstituted water (OECD medium) prepared according to the test guidelines was used for algal cultivation and testing.
- Preculture: Exponentially growing liquid culture of Raphidocelis subcapitata kept under the same environmental conditions as in the test.
- Illumination: Source: Osram Fluora L 18W77 and Osram Daywhite L 18W840 (Osram AG, Winterthur, Switzerland).
- Light intensity and homogeneity: Continuous, 4440 – 8880 lux ± max. 15% variation. The test flasks were repositioned daily during the exposure.
- Temperature: 21 to 24°C, maintained at ± 2°C in a thermo-controlled room
- pH: Initially adjusted to 8.0±0.2; the pH of the control medium should not increase by more than 1.5 units during the test
- Test design: Static exposure conditions over a period of 72 h
- Initial cell density: Nominal density of 5,000 cells/ml in all test vessels.

RANGE FINDING STUDY
Prior to the definitive test a non-GLP range finding test (three replicates for the control and two replicates per test concentration) with nominal concentrations of 10 and 100 mg/l of Glycyl-glycine was performed. No relevant inhibitory effects were observed in the non-GLP range-finding test.

EFFECT PARAMETERS MEASURED
- Biomass: Algal biomass is determined at 24, 48 and 72 hours of exposure using a spectrophotometer at 680 nm wavelength (Shimadzu UV 1800, Shimadzu Schweiz GmbH, Römerstr. 3, CH-4153 Reinach). Sample aliquots of 5 ml are taken from each test flask. At test start (0 hours) the nominal value is applied.
Reference substance (positive control):
yes
Remarks:
Control of sensitivity: Potassium dichromate is tested as a positive control twice a year.

Results and discussion

Effect concentrationsopen allclose all
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Key result
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
biomass
Details on results:
AVERAGE SPECIFIC GROWTH RATE
With respect to the endpoint average specific growth rate no significant effects (Student T-test, one-sided smaller, a = 0.05) were observed at a nominal concentration of 100 mg/l compared to the control. The 72-hour EC50 based on average specific growth rate of Glycyl-glycine to Raphidocelis subcapitata was therefore estimated to be >100 mg/l, while the NOEC was determined to be 100 mg/l.

YIELD
With respect to the endpoint yield no significant effects (Student T-test, one-sided smaller, a = 0.05) were observed at a nominal concentration of 100 mg/l compared to the control. The 72-hour EC50 based on yield of Glycyl-glycine to Raphidocelis subcapitata was therefore estimated to be >100 mg/l, while the NOEC was determined to be 100 mg/l.

OBSERVATIONS AND ENVIRONMENTAL CONDITIONS
The microscopic examination of the algal cells at the end of the test showed no abnormal appearance of the algae growing at the nominal test concentration of 100 mg/l. The appearance of the algal cells was not affected by the test item up to at least this concentration. No remarkable observations were made concerning the appearance of the test media. The pH value in the control replicates changed by 1.0 units. The light intensity was maintained at 5273 lux ± 6.1%. The temperature ranged from 23 to 24 °C. All values were within the guideline ranges.
Results with reference substance (positive control):
The result of the positive control test performed in July 2020 showed that the sensitivity of the test system based on average specific growth rate (72-h EC50 = 1.25 mg/l) was in line with a ring test yielding 1.19 mg/l, SD = 0.27 (ISO 8692:2012: Water quality - Fresh water algal growth inhibition test with unicellular green algae).
Reported statistics and error estimates:
Statistical analysis was performed with respect to the no observed effect concentrations. The statistical analysis was conducted with the software ToxRat® Pro.

Any other information on results incl. tables

Validity of the test:

Validity criterion
(applies to control cultures)

Required value

Achieved value

Average specific growth rate [d-1]

>=0.92

1.97

CV of average specific growth rate

over 3 days [%]

<=7

0.4

CV of section-by-section specific

growth rates [%]

<=35

13.5

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Remarks:
See table in section "any other information on results incl. tables".
Conclusions:
Glycyl-glycine had no significant inhibitory effects on the green algae Raphidocelis subcapitata up to the nominal concentration of 100 mg/l under the conditions of the test.
Executive summary:

The growth inhibitory effects of Glycyl-glycine (CAS no. 556-50-3) to the green alga Raphidocelis subcapitata were investigated according to the OECD guideline 201 over a period of 72 hours.

The test item is solid, 99.97% pure and soluble in test water up to at least 100 mg/l. The single nominal concentration tested was 100 mg/l.

The concentrations of Glycyl-glycine in the test media were determined by HPLC with UV detection in the samples from the test start as well as in the samples after 24, 48 and 72 hours of exposure. These analyses showed that the test item was correctly dosed and remained stable within 80–120% of the nominal concentration. Therefore, the effective concentrations ECx were assessed based on the nominal concentration of the test item.

With respect to the endpoint average specific growth rate no significant effects were observed at a nominal concentration of 100 mg/l compared to the control.

With respect to the endpoint yield no significant effects were observed at a nominal concentration of 100 mg/l compared to the control.

The results of the average specific growth rate and yield inhibition of Glycyl-glycine to the green alga Raphidocelis subcapitata are summarised in the following table based on the nominal concentration:

Parameter
(0-72 h)

Growth rate [mg/l]

Yield [mg/l]

EC50

>100

>100

NOEC

100

100

In conclusion, Glycyl-glycine had no significant inhibitory effects on the green algae Raphidocelis subcapitata up to the nominal concentration of 100 mg/l under the conditions of the test.

All validity criteria were fulfilled.