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Diss Factsheets

Environmental fate & pathways

Biodegradation in water: screening tests

Administrative data

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2009-09-02 to 2010-03-09
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Monitored GLP study, following international guidelines

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2010
Report date:
2010

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Chemical structure
Reference substance name:
N-(3-{1,1,1,5,5,5-hexamethyl-3-[(trimethylsilyl)oxy]trisiloxan-3-yl}propyl)prop-2-enamide
EC Number:
700-253-3
Cas Number:
115258-10-1
Molecular formula:
C15H37NO4Si4
IUPAC Name:
N-(3-{1,1,1,5,5,5-hexamethyl-3-[(trimethylsilyl)oxy]trisiloxan-3-yl}propyl)prop-2-enamide

Study design

Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic, non-adapted
Details on inoculum:
- Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): supplied by the sewage works of Rossdorf, Germany
- Storage conditions: after inital washing aeration overnight
- Storage length: overnight
- Preparation of inoculum for exposure:dilution to stock concentration in test water
- Pretreatment: 3x wash in tap water, centrifugation and resuspension, finally in test water
- Concentration of sludge: stock suspension: 1.5 g/L (on dry matter base)
- Initial cell/biomass concentration: final concentration in test vessel: 31 mg/L
- Test water: reconstituted by adding analytical grade salt solutions
Duration of test (contact time):
28 d
Initial test substance concentration
Initial conc.:
25 mg/L
Based on:
test mat.
Parameter followed for biodegradation estimation
Parameter followed for biodegradation estimation:
O2 consumption
Details on study design:
TEST CONDITIONS
- Composition of medium: see block "Any other informations on matgerial and methods, incl. tables"
- Additional substrate: no
- Solubilising agent (type and concentration if used): not applicable
- Test temperature: 22 +-1 °C
- pH: Start of test: 7.6; end of test: 6.6 - 7.5
- Aeration of dilution water: yes (before dilution)
- Suspended solids concentration: final concentration in test vessel: 31 mg/L
- Continuous darkness: yes
- Other:

TEST SYSTEM
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: no data
- Method used to create anaerobic conditions: not applicable
- Measuring equipment: BSB Sensomat system, Aqualytic Dortmund
- Test performed in closed vessels due to significant volatility of test substance: no
- Test performed in open system: no
- Details of trap for CO2 and volatile organics if used: Potassium hydroxide solution (45%)

SAMPLING
- Sampling frequency: daily
- Sampling method: not applicable
- Sterility check if applicable: not applicable
- Sample storage before analysis: not applicable

CONTROL AND BLANK SYSTEM
- Inoculum blank: 2 x
- Abiotic sterile control: no
- Toxicity control:1 x (HgCl2)
Reference substance
Reference substance:
benzoic acid, sodium salt

Results and discussion

% Degradation
Parameter:
% degradation (O2 consumption)
Value:
0
Sampling time:
28 d
Details on results:
Over the whole test period 0% consumtion/degradation could be observed. Results calculated with THOD (NO3) and ThOD (NH4) were identical.

BOD5 / COD results

Results with reference substance:
Results with reference substance bencoic acid, sodium salt and the toxic control with HgCl2 were vaild.

Any other information on results incl. tables

I. Cumulative Biochemical Oxygen Demand (mg O2/L) in Test Flasks During the Test Period of 28 Days

Time

Flask No.

(days)

1

2

3

4

5

6

7

 

1

0

0

0

0

55

0

50

 

2

0

0

0

0

85

0

85

 

3

0

5

0

5

115

0

110

 

4

5

5

5

5

120

0

115

 

5

5

5

5

10

125

0

125

 

6

5

5

5

10

130

0

130

 

7

10

10

10

10

135

0

135

 

8

10

10

10

10

140

0

140

 

9

10

10

10

10

145

0

145

 

10

10

10

10

10

145

0

145

 

11

10

10

10

10

150

0

150

 

12

10

10

10

10

150

0

150

 

13

10

10

10

10

155

0

155

 

14

10

10

10

10

155

0

160

 

15

15

10

15

15

160

0

165

 

16

15

15

15

15

165

0

170

 

17

15

15

15

15

165

0

180

 

18

15

15

15

15

170

0

190

 

19

15

15

15

15

175

0

200

 

20

15

15

15

15

175

0

200

 

21

15

15

15

15

175

0

200

 

22

15

15

15

15

180

0

200

 

23

15

15

15

15

180

0

200

 

24

15

15

15

15

180

0

200

 

25

15

15

15

20

180

0

200

 

26

15

15

15

20

180

0

205

 

27

15

15

20

20

185

0

205

 

28

15

15

20

20

185

0

205

 

where

            Flasks 1 and 2: 2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl]

            Flasks 3 and 4: inoculum control

Flask 5: reference (procedure control)

            Flask 6: abiotic control

            Flask 7: toxicity control

II. pH Values of the test solutions after the test period (28 d)

Flask No.

Treatment

pH-value

1

2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl]

7.5

2

2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl]

7.5

3

Inoculum control

7.5

4

Inoculum control

7.5

5

Procedure control

7.5

6

Abiotic control

6.6

7

Toxicity control

7.5

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Interpretation of results:
under test conditions no biodegradation observed
Conclusions:
The substance 2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl] is considered not to be readily biodegradable.
Executive summary:

The test item 2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl] was investigated for its ready biodegradability in a manometric respirometry test over a period of 28 days. The biodegradation was followed by the oxygen uptake of the micro-organisms during exposure. As a reference item sodium benzoate was tested simultaneously under the same conditions as the test item, and functioned as a procedure control.

 

Degradation rate of test item calculated by the oxygen consumption of the aerobic activated sludge microorganisms after 28 days of incubation.

The test item 2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl] contains nitrogen, therefore the evaluation of biodegradation has to be based on ThODNH4andThODNO3. The criterion for ready biodegradability under the conditions of a manometric respirometry test is the 10-day window, describing the period between reaching at least 10% degradation and 60% degradation. This period should not exceed 10 days.

The mean biodegradation after 28 days of 2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl] was -2% (ThODNH4+ThODNO3); the 10 day window criterion was not passed.

Therefore, 2-Propenamide, N-[3-[3,3,3-trimethyl-1,1-bis[(trimethylsilyl)oxy]-1-disiloxanyl]propyl] is considered not to be readily biodegradable.