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Diss Factsheets

Ecotoxicological information

Short-term toxicity to aquatic invertebrates

Administrative data

Endpoint:
short-term toxicity to aquatic invertebrates
Type of information:
experimental study
Adequacy of study:
key study
Study period:
06 - 13 August 2019
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2019
Report date:
2019

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
Version / remarks:
13 April 2004
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.2 (Acute Toxicity for Daphnia)
Version / remarks:
30 May 2008
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Chemical structure
Reference substance name:
3-(aminocarbonyl)-1-ß-D-ribofuranosyl-pyridinium bromide
Cas Number:
78687-39-5
Molecular formula:
C11H15BrN2O5
IUPAC Name:
3-(aminocarbonyl)-1-ß-D-ribofuranosyl-pyridinium bromide
impurity 1
Chemical structure
Reference substance name:
Nicotinamide
EC Number:
202-713-4
EC Name:
Nicotinamide
Cas Number:
98-92-0
Molecular formula:
C6H6N2O
IUPAC Name:
nicotinamide
impurity 2
Chemical structure
Reference substance name:
Methanol
EC Number:
200-659-6
EC Name:
Methanol
Cas Number:
67-56-1
Molecular formula:
CH4O
IUPAC Name:
methanol
impurity 3
Chemical structure
Reference substance name:
Ethyl acetate
EC Number:
205-500-4
EC Name:
Ethyl acetate
Cas Number:
141-78-6
Molecular formula:
C4H8O2
IUPAC Name:
ethyl acetate
impurity 4
Chemical structure
Reference substance name:
Water
EC Number:
231-791-2
EC Name:
Water
Cas Number:
7732-18-5
Molecular formula:
H2O
IUPAC Name:
Oxidane
impurity 5
Reference substance name:
inorganic salts by sulphated ash
IUPAC Name:
inorganic salts by sulphated ash
impurity 6
Chemical structure
Reference substance name:
Bromic acid
EC Number:
232-158-3
EC Name:
Bromic acid
Cas Number:
7789-31-3
Molecular formula:
BrHO3
IUPAC Name:
bromic acid
impurity 7
Reference substance name:
Unknown impurities.
Molecular formula:
Not available as unknown impurities.
IUPAC Name:
Unknown impurities.
Test material form:
solid
Details on test material:
Batch / Lot No. 1000146/01
Specific details on test material used for the study:
Lot no.: 1000146/01
Storage conditions: At approximately -15 °C

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
Samples were taken from all test media at the start of the test as well as after 24 and 48 hours of exposure. At the start of the test, the samples were taken from the freshly prepared test solutions as well as from the pure test water serving as control. For all subsequent sampling time points, aliquots from the respective replicates of the test media were pooled before sampling.

Immediately after sampling, acetonitrile containing 0.2% acetic acid was added to each sample to obtain a composition of sample:acetonitrile (1:1; v:v) containing 0.1% acetic acid. Thereafter, all samples were stored deep-frozen (at about -20 °C). In pre-experiments for investigation of the storage stability of the samples (non-GLP), 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 vessels were set up:
- Test solution: containing test water with test item (four replicates per concentration with five daphnids each)
- Control: containing pure test water (four replicates with five daphnids each)
Since the test item is soluble, the test solution was prepared by adding 100 mg/l of test item to test water in glassware. Pure test water served as control.
The test vessels were filled with 50 ml of the respective test medium. Daphnia, aged less than 24 hours and already acclimatized to the test water, were introduced into the test media and the vessels were covered with a glass plate. The Daphnia were not fed during the test and the test vessels were not aerated.

Test organisms

Test organisms (species):
Daphnia magna
Details on test organisms:
TEST ORGANISMS
- Test organism: Daphnia magna Straus, supplied by IES Ltd., 4108 Witterswil, Switzerland
- Breeding: The daphnids are cultivated in Elendt M4 medium at 18–22 °C, controlled at ±1 °C
- Illumination: 16 h per day, about 550-1100 lux, source: overhead white fluorescent tubes
- Medium: Reconstituted water (Elendt M4 medium)
- Feed: Suspension of Desmodesmus subspicatus in Elendt M4 medium with an optical density OD680 of about 12 units. This results in a final concentration of about 0.1 units from Monday to Thursday and 0.4 units on Fridays in the culture vessel.

Study design

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

Test conditions

Hardness:
2.5 mM (based on the sum of Ca2+ and Mg2+), Carbonate Alkalinity: 0.8 mM
Test temperature:
18–22°C, controlled at ±1 °C
pH:
7.5 - 7.6
Dissolved oxygen:
>=3 mg O2/l (required >=3 mg O2/l)
Salinity:
not reported
Conductivity:
638 µS cm-1
Nominal and measured concentrations:
NOMINAL CONCENTRATIONS
The definitive test was performed as a static limit-test at a nominal concentration of 100 mg/l.

MEASURED CONCENTRATIONS
The concentration of Nicotinamide-beta-D-riboside bromide (CAS no. 78687-39-5) in the test media at 0, 24 and 48 hours of exposure was determined by HPLC with UV detection. These analyses showed that the test item was correctly dosed and that the concentration remained stable within 80-120% of the nominal concentration over the duration of the test. Therefore, the effective concentrations ECx were assessed based on the nominal concentration of the test item, which was 100 mg/l.
Details on test conditions:
TEST SYSTEM
- Test vessel: 100 ml glass beaker containing 50 ml of test medium, covered with a glass plate to avoid evaporation and contamination of the test solutions with dust.
- Test medium: Elendt M4 medium
- Number of Daphnia: 20 individuals per test concentration and for the control divided in four groups of five individuals.
- Age: Less than 24 hours
- Light: 16 hours photoperiod per day, about 550–1100 lux, source: overhead white fluorescent tubes.
- Temperature: 18–22 °C, controlled at ±1 °C
- pH: The pH should not vary by more than 1.5 units during the exposure.
- Feed: The daphnids are not fed during the test
- Test design: Static exposure conditions
- Test duration: 48 hours

RANGE-FINDING STUDY
Prior to the definitive test a non-GLP range finding test with nominal concentrations of 1, 10 and 100 mg/l of Nicotinamide-beta-D-riboside bromide was performed (two replicates for each of the test concentration and the control; five daphnids per replicate).

EFFECT PARAMETERS MEASURED
Observations of immobilised daphnids were made after 24 and 48 hours of exposure. Any abnormal behaviour or appearance was reported.
Reference substance (positive control):
yes
Remarks:
Acute reference test with potassium dichromate conducted twice a year

Results and discussion

Effect concentrationsopen allclose all
Key result
Duration:
48 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Key result
Duration:
48 h
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
24 h
Dose descriptor:
EC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Duration:
24 h
Dose descriptor:
NOEC
Effect conc.:
100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mobility
Details on results:
During the first 24 hours of the test, no immobilised test organism was determined in the control and in the single test concentration of 100 mg/l. Thus, the 24-hour EC50 was greater than 100 mg/l. The no observed effect concentration (NOEC) after 24 hours was determined to be 100 mg/l.

After 48 hours of exposure, no immobilised test organism was determined in the control and in the single test concentration of 100 mg/l. Thus, the 48-hour EC50 was greater than 100 mg/l. The no observed effect concentration (NOEC) after 48 hours was determined to be 100 mg/l.
Results with reference substance (positive control):
The result of the latest positive control test performed in March 2019 showed that the sensitivity of the test system (24-hour EC50 = 0.88 mg/l) lies within the recommended range of 0.6–2.1 mg/l according to ISO 6341:2012: Water quality – determination of the inhibition of the mobility of Daphnia magna Straus (Cladocera, Crustacea) – Acute toxicity test.
Reported statistics and error estimates:
The effective concentration EC50 for 24 and 48 hours was estimated based on the concentration tested and immobilisation observed.

The no observed effect concentration (NOEC) is the highest test concentration for which the test item is observed to have an immobilisation rate not exceeding 10%. Thus, immobilisation rates >10% are considered to be significant.

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Remarks:
All validity criteria i.e. immobilization in the controls <=10% and O2 concentrations at the end of the test >=3 mg/L were fulfilled.
Conclusions:
In conclusion, Nicotinamide-beta-D-riboside bromide (CAS no. 78687-39-5) had no acute toxic effects on Daphnia magna up to the nominal concentration of 100 mg/l under the conditions of the test.
Executive summary:

The acute toxicity of Nicotinamide-beta-D-riboside bromide (CAS no. 78687-39-5) to Daphnia magna was investigated according to the OECD guideline 202 under static exposure conditions over a period of 48 hours.

The test item Nicotinamide-beta-D-riboside bromide is solid, 96.2% pure and soluble in test water up to at least 100 mg/l. Consequently, the single test solution was prepared by adding 100 mg/l of the test item to test water and stirring it until dissolution. The single nominal concentration tested was 100 mg/l.

The concentration of Nicotinamide-beta-D-riboside bromide in the test media at 0, 24 and 48 hours of exposure was determined by HPLC with UV detection. These analyses showed that the test item was correctly dosed and that the concentration remained stable within 80-120% of the nominal concentration over the duration of the test. Therefore, the effective concentrations ECx were assessed based on the nominal concentration of the test item.

In the control and at the test concentration of 100 mg/l, no immobilised test organism was observed during the test period of 48 hours.

The biological test results of Nicotinamide-beta-D-riboside bromide to Daphnia magna after 24 and 48 hours of exposure are summarized in the following table based on the nominal concentration of the test item:

Parameter

Immobilisation (0-24 h) [mg/l]

Immobilisation (0-48 h) [mg/l]

EC50

>100

>100

NOEC

100

100

In conclusion, Nicotinamide-beta-D-riboside bromide (CAS no. 78687-39-5) had no acute toxic effects on Daphnia magna up to the nominal concentration of 100 mg/l under the conditions of the test.

All validity criteria were fulfilled.