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Environmental fate & pathways

Biodegradation in water: screening tests

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Reference
Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Study period:
From 2017-03-23 to 2017-05-23
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Remarks:
All validity criteria was successful
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
Principles of method if other than guideline:
Not applicable.
GLP compliance:
yes (incl. QA statement)
Remarks:
2017-03-13
Specific details on test material used for the study:
Not applicable
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic (adaptation not specified)
Details on inoculum:
- Test Species: Aerobic activated sludge (microorganisms from a domestic waste¬water treatment plant) was supplied by the sewage treatment plant of Rossdorf, Germany.

- Conditioning: The aerobic activated sludge used for this study was washed by centrifugation and the supernatant liquid phase was decanted. The solid material was re-suspended in test water and centrifuged again. This procedure was done three times. An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge to its dry weight was determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 3.5 g dry material per litre were mixed with test water (see 6.5) and aerated overnight. This suspension was used for the experiment.
Duration of test (contact time):
28 d
Initial conc.:
102.9 mg/L
Based on:
other: Test Item Loading Rate (initial concentration in medium C0)
Initial conc.:
279.7 mg/L
Based on:
ThOD
Remarks:
NH4
Parameter followed for biodegradation estimation:
O2 consumption
Details on study design:
TEST CONDITIONS
- Composition of medium: Aliquots of washed sludge suspension were mixed with reconstitued test water.
- Reconstitued pure water: Analytical grade salts were added to pure water to prepare the following stock solutions:
a) 8.5 g KH2PO4, 21.75 g K2HPO4, 33.4 g Na2HPO4 x 2 H2O, 0.5 g NH4Cl filled up with pure water to 1000 mL volume; The pH-value was 7.4.
b) 11.25 g MgSO4 x 7 H2O filled up with pure water to 500 mL volume
c) 18.2 g CaCl2 x 2 H2O filled up with pure water to 500 mL volume
d) 0.125 g FeCl3 x 6 H2O filled up with pure water to 500 mL volume
In order to avoid precipitation of iron hydroxide in the stock solution d), one drop of concentrated HCl per litre was added before storage. 50 mL of stock solution a) and 5 mL of the stock solutions b) to d) were combined and filled up to a final volume of 5000 mL with pure water.
- Solubilising agent: Silicone oil AR20 was used as an emulsifying agent. (1%)
- Test temperature: 22°C ± 1°C
- pH: 7.4 to 8.1
- Continuous darkness: yes


TEST SYSTEM
- Culturing apparatus: The closed test flasks were incubated in a climatised chamber under continuous stirring.
- Number of culture flasks/concentration: 2
The test flasks were closed gas-tight by a measuring head. Potassium hydroxide solution (45%) was used for trapping the produced carbon dioxide. The amount of O2 consumed by the activated sludge was calculated from the decrease of pressure in the reaction vessel.
- Measuring equipment: BSB/BOD-Sensor- System, Aqualytic Dortmund, Germany
- Test performed in closed vessels due to significant volatility of test substance:

SAMPLING
O2 consumed daily by the activated sludge was calculated from the decrease of pressure in the reaction vessel.

CONTROL AND BLANK SYSTEM
- Inoculum blank: 2 (activated sludge + silicone oil + test water)
- Abiotic sterile control: 1
- Toxicity control: 1
- Other: Procedure control : (Ref. Item + activated sludge + silicone oil + test water)
Reference substance:
benzoic acid, sodium salt
Remarks:
Sodium Benzoate
Preliminary study:
No data.
Test performance:
No data.
Parameter:
% degradation (O2 consumption)
Remarks:
ThODNH4
Value:
72
Sampling time:
28 d
Details on results:
The 10-day windows began on day 4 after applica-tion, the mean value was calculated to be 13% bio-degradation. Therefore, the end of the 10-day win-dow was day 14. After correction for the mean bio-chemical oxygen demand of the inoculum controls the mean biodegradation percentage based on ThODNH4 at the end of the 10-day window was 56%; the criterion of the 10 day window was not passed. The mean biodegradation percentage at the end of the 28-day exposure period was 72%.
Results with reference substance:
The reference item sodium benzoate was sufficient-ly degraded to 77% after 14 days and to 77% after 28 days of incubation.
The percentage biodegradation of the reference item confirms the suitability of the used aerobic activated sludge inoculum.

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

45

0

55

 

2

0

0

5

5

85

0

85

 

3

15

15

5

5

105

0

100

 

4

45

45

5

10

115

0

120

 

5

60

60

10

10

125

0

125

 

6

80

80

10

10

135

0

135

 

7

95

100

10

15

140

0

140

 

8

115

120

10

15

145

0

150

 

9

130

135

15

20

150

0

160

 

10

145

145

15

20

150

0

165

 

11

155

160

15

20

150

0

170

 

12

165

170

15

20

155

0

180

 

13

170

180

15

20

155

0

185

 

14

175

180

20

25

155

0

195

 

15

180

185

20

25

155

0

205

 

16

185

185

20

25

160

0

215

 

17

195

190

20

25

160

0

220

 

18

205

190

20

25

160

0

225

 

19

210

195

25

25

160

0

235

 

20

215

200

25

25

160

0

240

 

21

220

205

25

25

160

0

245

 

22

220

205

25

25

160

0

255

 

23

225

210

25

25

160

0

260

 

24

225

215

25

30

160

0

265

 

25

230

220

25

30

160

0

270

 

26

230

220

25

30

160

0

275

 

27

235

225

25

30

160

0

280

 

28

235

225

25

30

160

0

285

 

Flasks 1 and 2: Artemisia herba-alba oil (thuyone type)

Flasks 3 and 4: inoculum control

Flask 5:reference (procedure control)

Flask 6: abiotic control

Flask 7: toxicity control

Percentage Biodegradation of Test Item, of Sodium Benzoate and of the Toxicity Control based on ThODNH4:

Time

Percentage Biodegradation1

(Days)

Artemisia herba-alba oil (thuyone type)1

Sodium Benzoate2

Toxicity
control1, 2

 

Flask 1 [%]

Flask 2 [%]

Flask 5 [%]

Flask 7 [%]

1

0

0

26

12

2

0

0

46

18

3

4

4

58

21

4

13

13

62

25

5

18

18

67

25

6

25

25

73

28

7

30

31

74

28

8

37

38

77

30

9

40

42

77

32

10

46

45

77

33

11

49

51

77

34

12

53

54

80

36

13

55

58

80

37

14

55

56

77

38

15

57

58

77

40

16

58

58

80

43

17

62

60

80

44

18

66

60

80

45

19

66

61

78

47

20

68

62

78

48

21

70

64

78

49

22

70

64

78

51

23

72

66

78

52

24

71

67

77

53

25

73

69

77

54

26

73

69

77

55

27

74

70

77

56

28

74

70

77

57

            1ThODNH4of Artemisia herba-alba oil (thuyone type): 2.719 mg O2/mg test item
            2ThODNH4of sodium benzoate: 1.666 mg O2/mg reference item

Biodegradation in the Toxicity Control

In the toxicity control containing both, the test item and the reference item sodium benzoate, 38% biodegradation was noted within 14 days and 57% biodegradation after 28 days of incubation. According to the test guidelines, the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms because degradation was >25% within 14 days.

According to the test guidelines the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms because degradation was >25% within 14 days.

Validity Criteria of the Study

- Inoculum Control: The oxygen demand of the inoculum control (medium and inoculum) was 27.5 mg O2/L and thus not greater than 60 mg O2/L within 28 days as required by the test guideline.

- pH-Value: The pH-value of the test item flasks at day 32 of the test was 7.4 and therefore within the range of pH 6.0 to 8.5 as required by the test guideline.

- Reference Item: The percentage degradation of the reference item should reach the level for ready biodegradability (>60%) within 14 days as required by the test guideline. The reference item sodium benzoate was degraded to more than 60% after 4 days of incubation.

- Test Item: The difference of duplicate values for the degradation of the test item at the plateau, at the end of the test and at the end of the 10-day window was less than 20%. The difference of duplicate values at day 28 differed by 4%. The validity criterion was fulfilled.

- Toxicity Control: If in a toxicity test, containing both the test substance and a reference compound less than 25% biodegradation (based on total ThOD) occurred within 14 days, the test substance can be assumed to be inhibitory. The biodegradation was 38% at day 14; the test item was not inhibitory.

All validity criteria are fulfilled.

Validity criteria fulfilled:
yes
Interpretation of results:
readily biodegradable
Conclusions:
Artemisia herba-alba oil (thuyone type) is considered to be readily biodegradable.
Executive summary:

The test item Artemisia herba-alba oil (thuyone type) was investigated for its ready biodegradability in a manometric respirometry test over a period of 28 days, according to the OECD 301F guideline. The biodegradation was followed by the oxygen uptake of the microorganisms 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.

The degradation rate of Artemisia herba-alba oil (thuyone type) reached 72% at 28 days and was therefore greater than 60% after 28 days.

Due to the fact that the substance is identified as an UVCB or as a complex, multi-constituent substance with structurally similar constituents, the 10-day window condition may be waived and the pass level applied at 28 days according to section 4.1.2.9.5 of CLP COMMISSION REGULATION (EU) No 286/2011 of 10 March 2011.

Therefore, Artemisia herba-alba oil (thuyone type) is considered to be readily biodegradable.

The reference item sodium benzoate was sufficiently degraded, thus confirming the suitability of the aerobic activated sludge inoculum used.

According to the test guidelines, the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms because degradation was >25% within 14 days in the toxicity control.

The oxygen demand of the inoculum control (medium and inoculum) was not greater than 60 mg O2/L within 28 days as required by the test guideline.

pH values were in the range required in the guideline. Therefore, all validity criteria of the study were fulfilled.

Therefore, this study is considered valid for that endpoint.

Results synopsys:

Test item: Artemisia herba-alba oil (thuyone type)

Biodegradation endpoint:Readily biodegradable based on the results at 28 days

Description of key information

Artemisia herba-alba oil (thuyone type) is considered to be readily biodegradable.

Key value for chemical safety assessment

Biodegradation in water:
readily biodegradable

Additional information

A reliable experimental study was available for that endpoint.

The test item Artemisia herba-alba oil (thuyone type) was investigated for its ready biodegradability in a manometric respirometry test over a period of 28 days, according to the OECD 301F guideline.

The degradation rate of Artemisia herba-alba oil (thuyone type) reached 72% at 28 days and was therefore greater than 60% after 28 days.

Due to the fact that the substance is identified as an UVCB or as a complex, multi-constituent substance with structurally similar constituents, the 10-day window condition may be waived and the pass level applied at 28 days according to section 4.1.2.9.5 of CLP COMMISSION REGULATION (EU) No 286/2011 of 10 March 2011.

All validity criteria were fulfilled. Moreover, the reference item sodium benzoate was sufficiently degraded, thus confirming the suitability of the aerobic activated sludge inoculum used.

In addition, the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms because degradation was >25% within 14 days in the toxicity control.

Therefore, this study was compliant with the guideline requirements. The study is considered valid for that endpoint.