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EC number: 283-905-5 | CAS number: 84775-75-7 Extractives and their physically modified derivatives such as tinctures, concretes, absolutes, essential oils, oleoresins, terpenes, terpene-free fractions, distillates, residues, etc., obtained from Artemisia herba-alba, Compositae.
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- 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. - 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
Reference
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 |
|
|
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.
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.
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