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Environmental fate & pathways

Biodegradation in water: screening tests

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Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
1994
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
No details on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 mg/L
Duration of test (contact time):
28 d
Initial conc.:
100 mg/L
Based on:
test mat.
Details on study design:
No data
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
94
Sampling time:
28 d
Details on results:
- Indirect analysis (BOD): 94%
- Direct analysis (GC): 100%
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
readily biodegradable
Conclusions:
Under the test conditions, the chemical substance was determined to be ready biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, (D,L)-camphor was tested at concentrations of 100 mg/L and the inoculum was activated sludge (30 mg/L). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 mg/L test concentration, 94% degradation (biochemical oxygen demand) was reached in 28 days.

 

Under the test conditions, the substance was determined to be ready biodegradable.

 

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
1996
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
no detail on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
Details on properties of test surrogate or analogue material (migrated information):
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 mg/L
Duration of test (contact time):
28 d
Initial conc.:
100 mg/L
Based on:
test mat.
Details on study design:
No data
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
>= 90 - <= 99
Sampling time:
28 d
Details on results:
- Indirect analysis (BOD): 90%
- Direct analysis (TOC) & (GC): 99% and 100% respectively.
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
readily biodegradable
Conclusions:
Under the test conditions, linalool was readily biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, linalool was tested at concentrations of 100 mg/L and the inoculum was activated sludge (30 mg/L). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 mg/L test concentration, 90 -99% degradation (biochemical oxygen demand) was reached in 28 days.

 

Under the test conditions, linalool was readily biodegradable.

 

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
2007
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
no detail on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 mg/L
Duration of test (contact time):
28 d
Initial conc.:
100 mg/L
Based on:
test mat.
Details on study design:
No data
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
>= 90 - <= 95
Sampling time:
28 d
Details on results:
- Indirect analysis (BOD): 91, 90 and 95%
- Direct analysis (GC): 100, 100 and 100%
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
readily biodegradable
Conclusions:
Under the test conditions, alpha-pinene was readily biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, alpha-pinene was tested at concentrations of 100 mg/L and the inoculum was activated sludge (30 mg/L). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 mg/L test concentration, 90 -95% degradation (biochemical oxygen demand) was reached in 28 days.

 

Under the test conditions, alpha-pinene was readily biodegradable.

 

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
1988
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
no detail on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 mg/L
Duration of test (contact time):
4 wk
Initial conc.:
100 mg/L
Based on:
test mat.
Details on study design:
Improved type for a volatile substance
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
>= 2 - <= 16
Sampling time:
4 wk
Details on results:
- Indirect analysis (BOD): 2%
- Direct analysis (GC): 16%
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
not readily biodegradable
Conclusions:
Under the test conditions, camphene was not found to be readily biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, camphene was tested at concentrations of 100 mg/L and the inoculum was activated sludge (30 mg/L). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 mg/L test concentration, 2 - 16 % degradation was reached in 28 days.

 

Under the test conditions, camphene was not found to be readily biodegradable.

 

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
1980
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
no detail on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 ppm
Duration of test (contact time):
14 d
Initial conc.:
100 other: ppm
Based on:
test mat.
Details on study design:
No data
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
>= 41 - <= 98
Sampling time:
14 d
Details on results:
- Indirect analysis (BOD): 41, 81 and 98%
- Direct analysis (GC): 100%
- Direct analysis (TOC): 50, 73 and 81%
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
readily biodegradable
Conclusions:
Under the test conditions, Limonene was readily biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, Limonene was tested at concentrations of 100 ppm and the inoculum was activated sludge (30 ppm). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 ppm test concentration, 41-98% degradation by biochemical oxygen demand was reached in 14 days.

 

Under the test conditions, Limonene was readily biodegradable.

 

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
1987
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
no detail on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 ppm
Duration of test (contact time):
2 wk
Initial conc.:
100 other: ppm
Based on:
test mat.
Details on study design:
No data
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
86
Sampling time:
2 wk
Details on results:
- Indirect analysis (BOD): 86%
- Direct analysis (GC): 99%
- Direct analysis (TOC): 87%
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
readily biodegradable
Conclusions:
Under the test conditions, myrcene beta was readily biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, myrcene beta was tested at concentrations of 100 ppm and the inoculum was activated sludge (30 ppm). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 ppm test concentration, 86% degradation by biochemical oxygen demand was reached in 2 weeks.

 

Under the test conditions, myrcene beta was readily biodegradable.

 

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
1978
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
no detail on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 ppm
Duration of test (contact time):
2 wk
Initial conc.:
100 other: ppm
Based on:
test mat.
Details on study design:
No data
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
84.6
Sampling time:
2 wk
Details on results:
- Indirect analysis (BOD): 84.6%
- Direct analysis (GC): 100%
- Direct analysis (TOC): 93%
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
readily biodegradable
Conclusions:
Under the test conditions, alpha-terpineol was readily biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, alpha-terpineol was tested at concentrations of 100 ppm and the inoculum was activated sludge (30 ppm). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 ppm test concentration, 84.6% degradation by biochemical oxygen demand was reached in 2 weeks.

 

Under the test conditions, alpha-terpineol was readily biodegradable.

 

Endpoint:
biodegradation in water: screening tests
Type of information:
(Q)SAR
Adequacy of study:
weight of evidence
Study period:
2017-08-04 to 2017-08-04
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
Remarks:
The value is not an experimental result, however the QSAR model is recommended by the ECHA guidance document on information requirements, is well documented with regard to validation parameters according to OECD principles. Moreover, the substance is fully characterised towards the applicability domain.
Justification for type of information:
QSAR prediction
Qualifier:
according to guideline
Guideline:
other: Reach Guidance on QSAR - R.6
Deviations:
no
Principles of method if other than guideline:
QSAR, Biowin v4.10. More details are given in QMRF/QPRF attached to the dossier.
GLP compliance:
no
Specific details on test material used for the study:
- SMILES: C(=CCCC(C(C(C1(C)C)C2)C1)=C)(C2)C
- CHEM: Bicyclo 7.2.0 undec-4-ene, 4,11,11-trimethyl-8-methylene-, 1R-(1R*,4E,9S*) -
- MOL FOR: C15 H24
- MOL WT: 204.36
Oxygen conditions:
not specified
Inoculum or test system:
not specified
Details on inoculum:
not applicable
Details on study design:
not applicable
Preliminary study:
not applicable
Test performance:
not applicable
Parameter:
probability of ready biodegradability (QSAR/QSPR)
Remarks on result:
not readily biodegradable based on QSAR/QSPR prediction
Details on results:
Biowin 1 (linear model prediction) = Does not Biodegrade Fast
Biowin 2 (non-linear model prediction) = Does not Biodegrade Fast
Biowin 3 (ultimate biodegradation timeframe) = Weeks-Months
Biowin 4 (Primary biodegradation timeframe) = Days-Weeks
Biowin 5 (MITI linear model prediction) = Not Readily Degradable
Biowin 6 (MITI non-linear model prediction) = Not Readily Degradable
Biowin 7 (Anaerobic model prediction) = Does not Biodegrade Fast
Ready Biodegradability Prediction: NO
Results with reference substance:
not applicable

Please see the attached documents.

Validity criteria fulfilled:
not applicable
Interpretation of results:
not readily biodegradable
Conclusions:
It is expected that the substance is not readily biodegradable.
Executive summary:

The ready biodegradation property of the substance was investigated using QSAR approach with Biowin v4.10 plug-in from EPISUITE v4.1 from US EPA.

It's expected that the test item is not readily biodegradable.

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
1987
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
other: Study conducted according to OECD Guideline 301 C but with deviations: no detail on material and methods
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
Deviations:
yes
Remarks:
no detail on material and methods
Principles of method if other than guideline:
Not applicable
GLP compliance:
not specified
Specific details on test material used for the study:
No data
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Concentration of sludge: 30 mg/L
Duration of test (contact time):
4 wk
Initial conc.:
100 mg/L
Based on:
test mat.
Details on study design:
Improved type for a volatile substance
Preliminary study:
No data
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
97
Sampling time:
4 wk
Details on results:
- Indirect analysis (BOD): 97%
- Direct analysis (TOC and GC): 90% and 100% respectively
Results with reference substance:
No data

None

Validity criteria fulfilled:
not specified
Interpretation of results:
not readily biodegradable
Conclusions:
Under the test conditions, the test item was found to be readily biodegradable.
Executive summary:

In a ready biodegradation study performed according to OECD Guideline 301 C, the substance was tested at concentrations of 100 mg/L and the inoculum was activated sludge (30 mg/L). The degradation of the test material was assessed by the determination of the oxygen consumption.

At 100 mg/L test concentration, 97% degradation (BOD) was reached in 4 weeks.

 

Under the test conditions, the test item was found to be readily biodegradable.

 

Endpoint:
biodegradation in water: screening tests
Type of information:
(Q)SAR
Adequacy of study:
weight of evidence
Study period:
2017-08-04 to 2017-08-04
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
Remarks:
The value is not an experimental result, however the QSAR model is recommended by the ECHA guidance document on information requirements, is well documented with regard to validation parameters according to OECD principles. Moreover, the substance is fully characterised towards the applicability domain.
Justification for type of information:
QSAR prediction
Qualifier:
according to guideline
Guideline:
other: Reach Guidance on QSAR - R.6
Deviations:
no
Principles of method if other than guideline:
QSAR, Biowin v4.10. More details are given in QMRF/QPRF attached to the dossier.
GLP compliance:
no
Specific details on test material used for the study:
- SMILES: CC1=CCC(CC1)C(=CCC=C(C)C)C
- MOL FOR: C15 H24
- MOL WT: 204.36
Oxygen conditions:
not specified
Inoculum or test system:
not specified
Details on inoculum:
not applicable
Details on study design:
not applicable
Preliminary study:
not applicable
Test performance:
not applicable
Parameter:
probability of ready biodegradability (QSAR/QSPR)
Remarks on result:
not readily biodegradable based on QSAR/QSPR prediction
Details on results:
Biowin 1 (linear model prediction) = Biodegrades Fast
Biowin 2 (non-linear model prediction) = Biodegrades Fast
Biowin 3 (ultimate biodegradation timeframe) = Weeks-Months
Biowin 4 (Primary biodegradation timeframe) = Days-Weeks
Biowin 5 (MITI linear model prediction) = Not Readily Degradable
Biowin 6 (MITI non-linear model prediction) = Not Readily Degradable
Biowin 7 (Anaerobic model prediction) = Does not Biodegrade Fast
Ready Biodegradability Prediction: NO
Results with reference substance:
not applicable

Please see the attached documents.

Validity criteria fulfilled:
not applicable
Interpretation of results:
not readily biodegradable
Conclusions:
It is expected that the substance is not readily biodegradable.
Executive summary:

The ready biodegradation property of the substance was investigated using QSAR approach with Biowin v4.10 plug-in from EPISUITE v4.1 from US EPA.

It's expected that the test item is not readily biodegradable.

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
weight of evidence
Study period:
From 1997.09.25 to 1997.11.11
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Remarks:
This study was performed according to OECD Guideline 301F with GLP statement. All validity criteria were fulfilled and no deviations were observed.
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
Deviations:
no
Principles of method if other than guideline:
Not applicable
GLP compliance:
yes (incl. QA statement)
Specific details on test material used for the study:
None
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic, non-adapted
Details on inoculum:
Fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (City of Geneva, Aïre) was used. The sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000 g for 10 minutes, discarding the supernatant and resuspending in mineral medium) and kept aerobic until being used on the same day.

Dry weight of suspended solids: 2.342 g/L.
To obtain a concentration of 30 mg/L (dry weight) in a 250 mL flask, 3.20 mL of sludge is needed (inoculum).
Duration of test (contact time):
38 d
Initial conc.:
100 mg/L
Based on:
test mat.
Parameter followed for biodegradation estimation:
O2 consumption
Details on study design:
TEST CONDITIONS
- Composition of medium: The mineral medium was prepared by mixing 50 mL of solution A (8.5g of KH2PO4 + 21.75g of K2HPO4 + 33.4g of Na2HPO4.2H2O + 0.5g of NH4Cl, dissolved in water and made up to 1L) and 2L deionised water, adding 5 mL of each of the solutions B (27.5g of CaCl2, dissolved in water and made up to 1L), C (22.5g of MgSO4.7H2O, dissolved in water and made up to 1L) and D (0.25g of FeCl3.6H2O + one drop of HCl Conc., dissolved in water and made up to 1L) and making up to 5L with deionised water.
- Solubilising agent (type and concentration if used): not applicable
- Test temperature: 22°C
- pH adjusted: the pH of the mineral medium is measured and if necessary adjusted to 7.4 +/- 0.2 with phosphoric acid or potassium hydroxide. At the start of the test, the pH of each flask is not measured but assumed to be the same as the mineral medium (7.31), in order not to remove any floating undissolved test substance from the test medium by dipping a glass electrode in it. Neutral test substances, even sodium benzoate, were shown not to affect the pH of the medium by more than 0.1 pH unit.
- Suspended solids concentration: 30 mg/L

TEST SYSTEM
- Culturing apparatus: 250 mL flasks
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: no data
- Method used to create anaerobic conditions: not applicable
- Measuring equipment: The respirometer used during this study is a SAPROMAT D 12, made by J. M. VOITH GmbH, D-7920 Heidenheim.
- Test performed in closed vessels: yes
- Test performed in open system: no

CONTROL AND BLANK SYSTEM
- Inoculum blank: yes (mineral medium + inoculum)
- Positive control: yes (mineral medium + 100 mg/L reference substance + inoculum)
- Toxicity control: yes (mineral medium + 100 mg/L test chemical + 100 mg/L reference substance + inoculum)
Reference substance:
benzoic acid, sodium salt
Preliminary study:
Not applicable
Test performance:
No data
Parameter:
% degradation (O2 consumption)
Value:
82
Sampling time:
28 d
Parameter:
% degradation (O2 consumption)
Value:
82
Sampling time:
38 d
Details on results:
See tables in "Any other information on results incl. tables" and graph in "Attached background material".
Results with reference substance:
94% biodegradation after 14 days and 97% biodegradation after 28 days. See table 5.2.1/3 in "Any other information on results incl. tables"

Table 5.2.1/2: Biological Oxygen Demand and percentage of biodegradation of the test substance

Days :

3

7

13

21

28

38

BOD Sludge

1rst flask

B1

14.0

19.0

21.0

23.0

26.0

27.0

2ndflask

B2

11.0

15.0

18.0

21.0

23.0

24.0

Mean

B

12.5

17.0

19.5

22.0

24.5

25.5

BOD Test subs.

1rst flask

C1

72.7

150.1

219.7

249.1

258.9

259.0

2ndflask

C2

90.7

171.4

238.3

263.0

267.9

267.9

1rst fl. corr.

C1-B

60.2

133.1

200.2

227.1

234.4

233.5

2ndfl. Corr.

C2-B

78.2

154.4

218.8

241.0

243.4

242.4

% degr.

1rst flask

D1

21

46

69

78

81

81

2ndflask

D2

27

53

75

83

84

84

mean

D

24

50

72

81

82

82

B = (B1 + B2) / 2

D1 = 100 * (C1 - B) / ThOD * [S]

D2 = 100 * (C2 - B) / ThOD * [S]

D = (D1 + D2) / 2

ThOD = 2.90 mg O2/mg

[S] = Initial test substance concentration (mg/L)

Table 5.2.1/3: Biological Oxygen Demand and percentage of biodegradation of the reference substance

Days :

5

7

10

14

21

28

BOD Sludge

1rst flask

B1

17.0

19.0

20.0

22.0

23.0

26.0

2ndflask

B2

14.0

15.0

16.0

19.0

21.0

23.0

Mean

B

15.0

17.0

18.0

20.5

22.0

24.5

BOD Ref subs.

1rst flask

A1

141.0

158.0

168.0

176.0

180.0

185.0

2ndflask

A2

145.0

162.0

172.0

178.0

182.0

186.0

1rst fl. corr.

A1-B

125.5

141.0

150.0

155.5

158.0

160.5

2ndfl. Corr.

A2-B

129.5

145.0

154.0

157.5

160.0

161.5

% degr.

1rst flask

D1

75

85

90

93

95

96

2ndflask

D2

78

87

92

95

96

97

mean

D

77

86

91

94

95

97

B = (B1 + B2) / 2

D1 = 100 * (A1 - B) / ThOD * [S]

D2 = 100 * (A2 - B) / ThOD * [S]

D = (D1 + D2) / 2

ThOD = 1.67 mg O2/mg

[S] = Initial reference substance concentration (mg/L)

Validity criteria fulfilled:
yes
Interpretation of results:
readily biodegradable
Conclusions:
Eucalyptol undergoes 82% biodegradation after 28 days in the test conditions. Biodegradation starts on day 3 and reaches 72% at the end of the 10 -day window (days 3 to 13). The curves obtained with the reference substance alone and with Eucalyptol + reference substance show no toxic effect of Eucalyptol on the micro-organisms at the test concentration.
Executive summary:

This study was performed according to OECD Guideline 301F with GLP statement.

A measured volume of inoculated mineral medium, containing a known concentration of test substance (100 mg/L) as the nominal sole source of organic carbon, is stirred in a closed flask at a constant temperature (22 +/-1°C) for up to 38 days. The consumption of oxygen is determined by measuring the quantity of oxygen (produced electrolytically) required to maintain constant the gas volume in the respirometer flask. Evolved carbon dioxide is absorbed in soda lime pellets. The amount of oxygen taken up by the microbial population during biodegradation of the test chemical (corrected for uptake by blank inoculum, run in parallel) is expressed as a percentage of ThOD (Theoretical Oxygen Demand, calculated from the elemental composition, assuming that carbon is oxidized to carbon dioxide and hydrogen to water).

As suggested in the guideline, the toxicity of the test chemical for the inoculum is checked. Therefore, a pair of flasks of the volumetric respirometer (SAPROMAT) are filled with mineral medium + test chemical (100 mg/L) + reference substance (sodium benzoate, 100 mg/L) + inoculum and their respirations are recorded as for the other flasks. If they are lower than those of the flasks containing mineral medium + reference substance (100 mg/L) + inoculum, the test chemical can be assumed to be inhibitory to the inoculum used.

Eucalyptol undergoes 82% biodegradation after 28 days (also after 38 days) in the test conditions. Biodegradation starts on day 3 and reaches 72% at the end of the 10 -day window (days 3 to 13). The curves obtained with the reference substance alone and with Eucalyptol + reference substance show no toxic effect of Eucalyptol on the micro-organisms at the test concentration.

In conclusion, Eucalyptol should be regarded as readily biodegradable according to this test.

Description of key information

Based on a Weight of Evidence approach with individual data on constituents, the registered substance can be regarded as readily biodegradable.

Key value for chemical safety assessment

Biodegradation in water:
readily biodegradable

Additional information

Based on typical composition, 96.1% of the substance is known. Major constituents (above 1%) represent 95.0% of the whole substance.

Individual data about ready biodegradability of major constituents can be found in the table below:

Constituents

CAS No

Typical %*

Biodegradation results

Reference

Linalool

78-70-6

42.00

Readily biodegradable

MITI, 1996

Camphor

76-22-2

13.00

Readily biodegradable

MITI, 1994

1,8-cineol

470-82-6

25.00

Readily biodegradable

Rudio, 1997

 α/β -pinene 80-56-8 and 127 -91-3  6.00  Readily biodegradable MITI, 2007; and ECHA disseminated dossier of b-pinene
 limonene  138-86-3 2.00  Readily biodegradable MITI, 1980
 trans-a-bisabolene 25532-79-0  1.80 Not Readily biodegradable  QSAR, BioWin v4.10 
 b-caryophyllene  87 -44 -5 1.00 Not Readily biodegradable  QSAR, BioWin v4.10 
 a-terpineol 98 -55 -5  1.20  Readily biodegradable MITI, 1978
 borneol laevo  464 -45 -9 1.00  Readily biodegradable MITI, 1987 
 b-myrcene  123 -35 -3 1.00  Readily biodegradable MITI, 1987
 camphene  79 -92 -5 1.00 Not readily biodegradable  MITI, 1988

* Typical composition taking into account constituents above 1%

In total, ca. 90% of the substance is composed by readily biodegradable constituents.

Based on a Weight of Evidence approach, it can therefore be possible to consider that the substance is readily biodegradable.