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EC number: 606-948-7 | CAS number: 2217-02-9
- 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:
- 17 March 2017 - 14 April 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Test method according to OECD 301F. GLP study.
- 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)
- 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): A sample of activated sludge was taken from the aeration tank of Sewage Treatment Plant ”Czajka” , Warsaw, receiving predominantly domestic sewage.
- Preparation of inoculum: The coarse particles were removed by settling and the supernatant was discarded. The sludge was washed in the mineral medium. The concentrated sludge was suspended in mineral medium to yield a concentration of 3-5 g suspended solids/l and it was aerated, at the test temperature of 22 °C, until application next day. A sample was withdrawn just before use for the determination of the dry weight of the suspended solids. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Remarks:
- (77.8 mg/l of organic carbon)
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: 10ml of solution (A) in 800 ml water, plus 1 ml solutions (B), (C), (D) and 11ml water. The following stock solutions were used, prepared with analytical grade reagents: Solution (A) contains: 8.50 g monopotassium dihydrogen orthophosphate (KH2PO4), 21.75 g dipotassium monohydrogen orthophosphate (K2HPO4), 33.40 g disodium monohydrogen orthophosphate dihydrate (Na2HPO4·2H2O), 0.50 g ammonium chloride (NH4Cl), in 1 L water. Solution (B) contains: 27.50 g calcium chloride, anhidrous (CaCl2) in 1L water. Solution (C) contains: 22.50 g magnesium sulphate heptahydrate (MgSO4·7H2O) in 1L water. Solution (D) contains: 0.25 g iron(III) chloride hexahydrate (FeCl3·6H2O) in 1L water.
- The water used is double-distilled, containing 3.5 mg/L of organic carbon (< 10% of the organic carbon content introduced by the test item), checked by DOC analysis using spectrophotometer Hach DR 3900 and Hach-Lange reagents.
- Test temperature: 22 ± 2ºC
- pH: 7.4 ± 0.2
- pH adjusted: no
- Suspended solids concentration: 30 mg/L
- Continuous darkness: yes
- Volume of test solution in flask, V: 0.164 L
TEST SYSTEM
- Number of culture flasks/concentration: triplicates were used, flasks #7, 8, 9 containing test item (100 mg/l) and inoculum (30mg/L SS).
- Measuring equipment: O2 uptake was measured by a closed WTW OxiTop OC 110 repirometer.
- Details of trap for CO2 and volatile organics if used: potassium hydroxide solution.
SAMPLING
- Sampling frequency: O2 uptake data were read out every 112 min during the 28 day test (40 320 min that is 360 readings) and were recorded and stored in the measuring heads of the sample bottles.
- Sampling method: Readings from apparatus (closed WTW OxiTop OC 110 repirometer).
CONTROL AND BLANK SYSTEM
- Inoculum blank: flasks #1, 2, 3, containing only inoculum 30mg/L SS.
- Procedure control: flasks #4, 5, 6, containing reference item (sodium acetate 100 mg/l) and inoculum 30mg/L SS.
- Toxicity control: flasks #10, 11, 12, containing test item, reference item and inoculum 30mg/L SS.
STATISTICAL METHODS: The calculations and the graphs were performed using SigmaPlot 9.0 software of SYSTAT Software, Inc., USA purchased from GAMBIT CoiS Ltd, Poland. - Reference substance:
- acetic acid, sodium salt
- Remarks:
- CAS No: 127-09-3, purity ≥ 99.7%, source: CHEMPUR, Piekary Śląskie, Polska.
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 74.5
- Sampling time:
- 28 d
- Details on results:
- - The test item attained 74.5% of biodegradation (>60% reached in a 10-day window within the 28-day period of the test)
- The reference item reached 83.6 % of biodegradation and the level for ready biodegradability by 5 days (>60% reached before day 14)
- In the toxicity test the biodegradation was equal to 55.3% in 14 days (>25% in 14 days). Therefore, the test item is not inhibitory.
- The oxygen uptake of the inoculum blank was equal to 38.9 mg/l in 28 days (<60 mg/l in 28 days)
- The pH values ( 7.43-8.78) of almost all flasks were inside the range (6-8.5, minimal overruns took place in 3 flasks without any influence in the test result) - Results with reference substance:
- The reference item reached 83.6% of biodegradation and the level for ready biodegradability by 5 days (>60% reached before day 14).
- Validity criteria fulfilled:
- yes
- Remarks:
- See "overall remarks".
- Interpretation of results:
- readily biodegradable
- Conclusions:
- At the 28th day of the test the measured aerobic biodegradation of the test item attained 74.5%. Thus, the test item can be deemed to be readily biodegradable.
- Executive summary:
A 28-day ready aerobic biodegradability test in an aerobic aqueous medium with manometric respirometry method was performed on the test item, according to OECD 301F / EC C.4 – D manometric respirometry methods, in accordance with GLP principles. 100 mg/l of test item was inoculated with activated sludge (30 mg/L SS) and incubated under aerobic conditions in a closed respirometer flask at constant temperature (22 ± 2ºC) for 28 days. A blank test, a procedure test with reference substance (sodium acetate) and a toxicity test were run in parallel. In the toxicity test, containing both the test item and a reference item, on the 14th test day the biodegradation (based on ThOD) attained 55.3%. Thus, the test item is not inhibitory. At the 28th day of the test the measured aerobic biodegradation of the test item attained 74.5%. Thus, the test item can be deemed to be readily biodegradable.
Reference
Table 2. Sample oxygen uptake: biodegradability.
|
time, days |
|||||||||||||
1 |
3 |
5 |
7 |
9 |
12 |
14 |
16 |
18 |
21 |
23 |
25 |
28 |
||
Test item O2uptake, mg/l |
a1 |
13.4 |
17.4 |
21.2 |
23.8 |
89.6 |
149.9 |
178.9 |
200.0 |
211.8 |
230.2 |
236.5 |
243.4 |
250.2 |
a2 |
12.9 |
18.7 |
22.1 |
25.3 |
32.1 |
136.3 |
165.2 |
186.6 |
207.8 |
232.3 |
240.1 |
249.1 |
257.5 |
|
a3 |
11.0 |
17.4 |
19.2 |
25.7 |
121.0 |
166.2 |
187.2 |
206.4 |
222.4 |
239.7 |
247.1 |
250.5 |
257.4 |
|
am. avg |
12.4 |
17.9 |
20.8 |
24.9 |
80.9 |
150.8 |
177.1 |
197.7 |
214.0 |
234.1 |
241.2 |
247.6 |
255.0 |
|
Blank test O2uptake mg/l |
b1 |
7.4 |
14.7 |
19.1 |
24.1 |
26.8 |
29.8 |
31.6 |
33.4 |
33.7 |
36.8 |
35.1 |
37.9 |
40.3 |
b2 |
10.8 |
16.1 |
18.4 |
19.1 |
22.3 |
23.7 |
24.9 |
25.9 |
27.2 |
28.8 |
31.2 |
32.1 |
34.5 |
|
b3 |
16.8 |
21.1 |
23.8 |
26.2 |
27.2 |
31.2 |
34.4 |
34.0 |
34.7 |
38.9 |
37.3 |
39.6 |
42.0 |
|
bm. avg |
11.7 |
17.3 |
20.4 |
23.2 |
25.4 |
28.2 |
30.3 |
31.1 |
31.9 |
34.8 |
34.5 |
36.5 |
38.9 |
|
Reference item O2uptake. mg/l |
w1 |
27.8 |
53.7 |
68.8 |
75.8 |
78.1 |
83.4 |
85.4 |
87.7 |
88.2 |
92.6 |
92.5 |
93.1 |
95.5 |
w2 |
29.3 |
56.5 |
70.7 |
77.5 |
83.0 |
88.4 |
90.9 |
94.3 |
96.8 |
99.1 |
101.2 |
104.3 |
106.0 |
|
w3 |
24.5 |
54.0 |
68.1 |
76.9 |
80.7 |
87.1 |
90.5 |
94.0 |
96.0 |
100.6 |
103.1 |
105.2 |
110.9 |
|
wm. avg |
27.2 |
54.7 |
69.2 |
76.8 |
80.6 |
86.3 |
88.9 |
92.0 |
93.7 |
97.5 |
98.9 |
100.9 |
104.1 |
|
Toxicity control O2uptake. mg/l |
tox1 |
22.4 |
59.6 |
74.8 |
82.2 |
101.6 |
211.1 |
233.2 |
248.5 |
259.3 |
273.9 |
281.3 |
290.4 |
300.0 |
tox2 |
21.7 |
56.7 |
71.7 |
82.1 |
145.1 |
221.5 |
249.3 |
266.6 |
282.1 |
300.3 |
308.5 |
315.4 |
326.5 |
|
tox3 |
20.8 |
56.3 |
70.7 |
78.7 |
117.2 |
196.8 |
219.3 |
235.4 |
249.7 |
264.5 |
273.5 |
279.6 |
288.9 |
|
toxm.avg |
21.6 |
57.5 |
72.4 |
81.0 |
121.3 |
209.8 |
233.9 |
250.2 |
263.7 |
279.6 |
287.8 |
295.2 |
305.1 |
|
Corrected test item O2uptake, mg/l |
(a1-bm) |
1.8 |
0.2 |
0.8 |
0.6 |
64.2 |
121.7 |
148.6 |
168.9 |
179.9 |
195.4 |
202.0 |
206.9 |
211.2 |
(a2-bm) |
1.2 |
1.4 |
1.6 |
2.2 |
6.6 |
108.1 |
134.9 |
155.5 |
175.9 |
197.4 |
205.6 |
212.5 |
218.6 |
|
(a3-bm) |
-0.6 |
0.2 |
-1.2 |
2.6 |
95.6 |
138.0 |
156.9 |
175.3 |
190.5 |
204.9 |
212.6 |
213.9 |
218.5 |
|
Reference item % degradation ThOD = 0.78 mgO2/mg C = 100 mg/l |
R1(w1) |
20.6 |
46.7 |
62.1 |
67.5 |
67.6 |
70.8 |
70.7 |
72.6 |
72.2 |
74.1 |
74.4 |
72.5 |
72.5 |
R2(w2) |
22.6 |
50.2 |
64.4 |
69.7 |
73.9 |
77.1 |
77.7 |
81.0 |
83.2 |
82.4 |
85.4 |
86.9 |
86.0 |
|
R3(w3) |
16.5 |
47.0 |
61.1 |
68.9 |
70.8 |
75.5 |
77.1 |
80.6 |
82.2 |
84.3 |
87.9 |
88.1 |
92.2 |
|
Rwavg |
19.9 |
48.0 |
62.6 |
68.7 |
70.8 |
74.5 |
75.2 |
78.1 |
79.2 |
80.3 |
82.6 |
82.5 |
83.6 |
|
Test item% degradation ThOD = 2.90 mgO2/mg C = 100 mg/l |
R1(a1) |
0.6 |
0.1 |
0.3 |
0.2 |
22.1 |
42.0 |
51.2 |
58.2 |
62.0 |
67.4 |
69.6 |
71.3 |
72.8 |
R2(a2) |
0.4 |
0.5 |
0.6 |
0.7 |
2.3 |
37.3 |
46.5 |
53.6 |
60.7 |
68.1 |
70.9 |
73.3 |
75.4 |
|
R3(a3) |
0.0 |
0.1 |
0.0 |
0.9 |
33.0 |
47.6 |
54.1 |
60.4 |
65.7 |
70.6 |
73.3 |
73.8 |
75.3 |
|
Raavg |
0.3 |
0.2 |
0.3 |
0.6 |
19.1 |
42.3 |
50.6 |
57.4 |
62.8 |
68.7 |
71.3 |
72.8 |
74.5 |
|
Toxicity test % degradation
|
R1(tox1) |
2.9 |
11.5 |
14.8 |
16.0 |
20.7 |
49.7 |
55.2 |
59.1 |
61.8 |
64.9 |
67.1 |
69.0 |
70.9 |
R2(tox2) |
2.7 |
10.7 |
13.9 |
16.0 |
32.5 |
52.5 |
59.5 |
64.0 |
68.0 |
72.1 |
74.4 |
75.8 |
78.1 |
|
R3(tox3) |
2.5 |
10.6 |
13.7 |
15.1 |
25.0 |
45.8 |
51.4 |
55.5 |
59.2 |
62.4 |
64.9 |
66.1 |
67.9 |
|
Rtoxavg |
2.7 |
10.9 |
14.1 |
15.7 |
26.1 |
49.3 |
55.3 |
59.5 |
63.0 |
66.5 |
68.8 |
70.3 |
72.3 |
Table 3. The pH values of test flasks (no adjustment of pH was conducted).
flask # |
7 |
8 |
9 |
1 |
2 |
3 |
4 |
5 |
6 |
10 |
11 |
12 |
Test item |
Inoculum blank |
Reference item |
Toxicity test |
|||||||||
initial |
7.43 |
7.45 |
7.46 |
7.38 |
7.44 |
7.44 |
7.42 |
7.43 |
7.45 |
7.47 |
7.47 |
7.48 |
final |
7.84 |
7.64 |
7.85 |
7.43 |
7.44 |
7.44 |
8.71 |
8.78 |
8.69 |
7.85 |
7.66 |
8.13 |
Description of key information
Key study: Test method according to OECD 301F / EU C.4 (Manometric respirometry methods), GLP study. At the 28th day of the test the measured aerobic biodegradation of the test item attained 74.5%. Thus, the test item is readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
Key study. A 28-day ready aerobic biodegradability test in an aerobic aqueous medium with manometric respirometry method was performed on the test substance D-alpha fenchol, according to OECD 301F / EC C.4-D manometric respirometry methods (GLP study). 100 mg/l of test item was inoculated with activated sludge (30 mg/L SS) and incubated under aerobic conditions in a closed respirometer flask at constant temperature (22 ± 2ºC) for 28 days. A blank test, a procedure test with reference substance (sodium acetate) and a toxicity test were run in parallel. In the toxicity test, containing both the test item and a reference item, on the 14th test day the biodegradation (based on ThOD) attained 55.3%. Thus, the test substance is not inhibitory. At the 28th day of the test the measured aerobic biodegradation of the test item attained 74.5%. Thus, the test item is readily biodegradable.
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