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Ecotoxicological information

Toxicity to microorganisms

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Administrative data

Endpoint:
activated sludge respiration inhibition testing
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2015-03-04 to 2015-03-05
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP study, no deficiencies

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2014
Report date:
2015

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
Deviations:
no
GLP compliance:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
D-Glucitol, 1-deoxy-1-(methylamino)-, N-[C8-16 (even numbered) and C18 unsaturated acyl] derivs.
EC Number:
940-422-0
Cas Number:
1591783-13-9
Molecular formula:
C15H31NO6 (C8 derivative) C17H35NO6 (C10 derivative) C19H39NO6 (C12 derivative) C21H43NO6 (C14 derivative) C23H47NO6 (C16 derivative) C25H51NO6 (C18 derivative) C25H49NO6 (C18 unsatd. derivative)
IUPAC Name:
D-Glucitol, 1-deoxy-1-(methylamino)-, N-[C8-16 (even numbered) and C18 unsaturated acyl] derivs.
Test material form:
other: waxy solid
Details on test material:
- Molecular formula: C19H39NO6 (C12-Glucamide) and C21H43NO6 (C14-Glucamide)
- Molecular weight: 377.52 – 405.57 g/mol for C12- and C14-Glucamide
- Substance type: UVCB
- Physical state: waxy solid
- Stability under test conditions: Stable (in water and light at room temperature)
- Storage condition of test material: Room temperature, protected from light, in the tightly closed original container

- Other:
- Solubility (in water at RT): Slightly soluble
- pH value (in aqueous solution): Ca. 8-10 at concentration of 10.000 [mg/L]
- Melting point: 70 – 71 °C
- Boiling point: No boiling point, substance decomposes before boiling
- Vapour pressure: < 0.1 Pa

Sampling and analysis

Analytical monitoring:
no

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: 10 - 32 - 100 - 320 - 1000 mg/L were weighed out on object slides and placed into Erlenmeyer flasks and stirred over night
- Eluate: Synthetic waste water acc. to OECD 209
- Differential loadings: 10 - 32 - 100 - 320 - 1000 mg/L
- Controls: Test medium without test or reference item. Triplicates at the beginning of the test + triplicates at the end of the test

Test organisms

Test organisms (species):
activated sludge
Details on inoculum:
- Preparation of inoculum for exposure: Non-adapted activated sludge from the sewage plant at Hildesheim (Municipal sewage treatment plant of 31137 Hildesheim, Germany)
- Pretreatment: The sludge was washed twice with chlorine free tap water and adjusted to a dry sludge concentration of 3.0 g/L ± 10 %. The sludge was used within 24 h after sampling.
- Dry sludge concentration: 3.02 g/L, corresponding to 1.51 g/L in the test vessel

Study design

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
3 h

Test conditions

Hardness:
Not determined
Test temperature:
21.1 °C
pH:
pH-value of the activated sludge 7.84
pH-value of the synthetic waste water 7.54
Salinity:
Not determined
Details on test conditions:
TEST SYSTEM
- Test vessel: 500 mL Erlenmeyer flask, DIN 12380
- Aeration: Shaking of flasks at 150 rpm to keep the dissolved oxygen concentration above 60 - 70 % saturation and to maintain the sludge flakes in suspension.


- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6 (Triplicates at the beginning of the test + triplicates at the end of the test.)
- Composition of test medium:

Table for the Test Item Concentrations
Test Item Test concentration [mg/L]
10 32 100 320 1000
Test item [mg] 5 16 50 160 500
Inoculum [mL] 250
Synthetic waste water [mL] 16
Demineralised water [mL] filled up to 250 mL




EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
After 3 h incubation, the oxygen concentration of each control, reference item and test item replicate was determined by means of oximeter immediately after transferring the solution to the measuring cell and the oxygen depletion was recorded for at least 3 minutes on a flat bed recorder.

TEST CONCENTRATIONS
Inhibition of Respiration (Preliminary Tests)

Inhibitions in the Preliminary Tests

Nominal Test Item Concentration [mg/L] pH(test item in demin. water) pH (adjusted to) pH (test item in medium) Inhibition [%]
Preliminary test – stirred overnight, shaker
10 5.85 - 7.59 4
6.14 - 7.46 -2
100 6.64 - 7.35 20
6.79 - 7.35 25
1000 9.00 7.90* 7.43 79
9.12 - 7.52 79

*)adjusted with 0.5 mol/L HCl


Additional replicates were prepared to determine the inhibition of nitrification. Two replicates with 1000 mg/L were measured with addition of Allylthiourea ATU (Final concentration: 11.6 mg/L). No indication for the requirement to measure the inhibition of nitrification in the definitive study was observed.

Inhibitions in the Preliminary Test (with / without ATU)

Nominal Test Item Concentration Inhibition of total respiration Inhibition of heterotrophic respiration Inhibition of nitrification
[mg/L] [%] [%] [%]
1000 80 54 98
80 57 95








Reference substance (positive control):
yes
Remarks:
Copper (II) sulphate pentahydrate p.a.

Results and discussion

Effect concentrationsopen allclose all
Duration:
3 h
Dose descriptor:
NOEC
Effect conc.:
8.1 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
inhibition of total respiration
Remarks:
respiration rate
Duration:
3 h
Dose descriptor:
EC10
Effect conc.:
34.4 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
inhibition of total respiration
Remarks:
respiration rate
Remarks on result:
other: 22.5-43.3 mg/L
Duration:
3 h
Dose descriptor:
EC50
Effect conc.:
171 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
inhibition of total respiration
Remarks:
respiration rate
Remarks on result:
other: 157 - 189 mg/L
Results with reference substance (positive control):
- Results with reference substance valid? Yes
- Relevant effect levels: EC50: 104 mg/L
Reported statistics and error estimates:
The NOEC was determined by calculation of statistical significance of the inhibition of respiration in comparison to the control. One Way Analysis of Variance (ANOVA) and DUNNETT’s test was used for NOEC calculations. When running a One Way Analysis of Variance a Normality test and an Equal Variance test were done first. P-values for both Normality and Equal Variance test are 0.05. The -value (acceptable probability of incorrectly concluding that there is a difference) is =0.05.

The EC-values of the test item and the reference item were calculated by sigmoidal dose-response regression and linear regression, respectively, using software GraphPadPrism. Calculations of the confidence intervals for the EC-values were carried out using standard procedures.


Any other information on results incl. tables

From the oxygen depletion the oxygen uptake rates were calculated in mg O2/L×h, additionally the specific respiration rates based on the dry sludge concentration were calculated in mg O2/g×h.

The inhibition of the oxygen uptake rates of the test and reference item concentrations in % was calculated in comparison with the oxygen uptake rates of the control.

Oxygen Uptake Rates, Specific Respiration Rates and Inhibition of the Respiration of the Control and Test Item Concentrations

 

Test
Concentration
[mg/L]

Repl.

Oxygen Uptake Rate R
[mg O2/L
×h]

Inhibition

[%]

Mean Inhibition
[%]

 

Control

1

32.8

2

33.2

3

31.2

4

30.8

5

30.8

6

30.0

Test Item

10

1

29.2

7

4

2

29.2

7

3

31.2

1

4

29.6

6

5

31.2

1

32

1

27.6

12

11

2

26.8

15

3

26.8

15

4

30.0

5

5

29.2

7

100

1

24.8

21

27

2

21.6

31

3

22.8

28

4

24.0

24

5

22.4

29

320

1

8.4

73

72

2

9.2

71

3

8.8

72

4

8.0

75

5

9.6

70

1000

1

6.0

81

82

2

5.6

82

3

5.6

82

4

5.6

82

5

5.6

82

Repl. = Replicate

Coefficient of variation of oxygen uptake rates of the control: 4%

Suspended solids in the test vessel: 1.51 g/L

Specific Respiration Rates of the Control Replicates

 

 

Repl.

Specific Respiration Rate Rs
[mg O2/g
×h]

 

Control

1

21.7

2

22.0

3

20.7

4

20.4

5

20.4

6

19.9

Mean value

20.8

Repl. = Replicate

Suspended solids in the test vessel: 1.51 g/L

 

Oxygen Uptake Rates and Inhibition of the Respiration of the Reference Item Concentrations

 

Test Concentration
[mg/L]

Repl.

Oxygen Uptake

Rate R
[mg O2/L
×h]

Inhibition

 

[%]

Mean Inhibition

[%]

Reference Item

58

1

24.8

21

22

2

24.4

23

3

24.4

23

100

1

16.8

47

48

2

16.0

49

3

16.8

47

180

1

7.6

76

77

2

7.2

77

3

7.2

77

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
The NOEC of Glucamide CC is 10 mg/L. The test item is not toxic at the concentration of 10 mg/L to activated sludge of a municipal sewage treatment plant. The EC10 is 42.5 mg/L, the EC20 is 79.4 mg/L the EC50 is 171 mg/L and EC80 is 590 mg/L of the test item.


Executive summary:

A Respiration Inhibition Test with activated sludge according to OECD Guideline No. 209 was carried out with the test itemGlucamide CC(batch number:EK13/177) from 2015-03-04 to 2015-03-05 inDr.U.Noack-Laboratorien, 31157 Sarstedt, Germany. The test system was activated sludge of the municipal treatment plant of 31137 Hildesheim, Germany. The test was carried out under static conditions with the test item concentrations10 - 32 - 100 - 320 - 1000 mg/L. The respiration rates of the control, reference and test item replicates were measured after a contact time of three hours, and the inhibitory effects of the test and reference item were determined in comparison to the control respiration rates. The mean inhibition of respiration for the test item replicates ranged from 4 % to 82 %.

 

In a pre-test additional replicates were prepared to determine the inhibition of nitrification. Two replicates with 1000 mg/L were measured with addition of Allylthiourea ATU (Final concentration: 11.6 mg/L). No indication for the requirement to measure the inhibition of nitrification in the definitive study was observed.

 

In order to check the activity of the test system and the test conditions a reference test was carried out with copper (II) sulphate pentahydrate as reference item and the reference toxicity was determined. The EC50-value for the reference item was 104 mg/L.

NOEC and EC-Values with Confidence Interval ofGlucamide CC
after 3 h exposure time, Inhibition of Total Respiration

 

EC-values

[mg/L]

Confidence interval
P = 95 [%]
[mg/L]

NOEC*

10

EC10

42.5

27.8 – 53.4

EC20

79.4

70.7 – 88.5

EC50

171

157 – 189

EC80

590

451 – > 1000

*) No statistically significant inhibition (P < 0.05), ANOVA, Dunnett`s Method

 

 

 

The NOEC ofGlucamide CCis10mg/L.

The test item is not toxic at the concentration of 10 mg/L to activated sludge of a municipal sewage treatment plant.

The EC10is 42.5 mg/L, the EC20is 79.4 mg/L the EC50is 171 mg/L and EC80is 590 mg/L of the test item.