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EC number: 682-818-3 | CAS number: 95306-64-2
- 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2018 - 02 - 23 - 2018 - 05 - 18
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 4-amino-5-methyl-1,2-dihydropyridin-2-one
- EC Number:
- 682-818-3
- Cas Number:
- 95306-64-2
- Molecular formula:
- C6 H8 N2 O
- IUPAC Name:
- 4-amino-5-methyl-1,2-dihydropyridin-2-one
- Test material form:
- solid
Constituent 1
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Species/Origin: Aerobic activated sludge, microorganisms from a domestic waste water treatment plant was supplied by the sewage treatment plant Bensheim, Germany.
Conditioning: The aerobic activated sludge used for this study was washed by centrifugation and the supernatant liquid phase was decanted after 15 minutes of deposition. 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 for 2 days. This suspension was used for the experiment. - Duration of test (contact time):
- 28 d
Initial test substance concentration
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- Test Design:
The test item 4-Amino-5-methylpyridinon 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 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.
Endpoints:
Degradation rate of test item calculated by the oxygen consumption of the aerobic activated sludge microorganisms after 28 days of incubation.
Test Item Loading Rate (initial concentration in medium C0):
101.4 mg/L corresponding to an oxygen demand of about 156.9 mg/L (ThODNH4) and 261.6 mg/L
(ThODNO3)
Reference Item:
Sodium Benzoate
Reference Item Loading Rate:
103.7 mg/L corresponding to an oxygen demand of about 172.7 mg/L (ThODNH4)
Test Conditions:
22°C ± 1°C, darkness
Test Units
Type and Size:
Manometric Test System with test flasks containing a volume of approximately 500 mL.
Apparatus: BSB/BOD-Sensor-System, Aqualytic Dortmund, Germany
Principle:
The test flasks prepared according paragraph 6.6 were incubated at 22°C * 1°C. The pressure decrease in the reaction vessels was measured over complete experimental phase of 28 days using the BSB/BOD-Sensor-System, Aqualytic Dortmund, Germany. 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.
Identification: Each test unit was uniquely identified with the study number, treatment and replicate number.
Preparation of Test Flasks:
The amounts of test item and reference item were directly weighed into the test flasks. No emulsifiers or solvents were used, but the solutions were dispersed by stirring to achieve a homogeneous solution of the test item.
The expiry date of the reference item refers to the storage in the container. At test start (weighing of test item and reference item), the reference item was durable. The reference item expired not until it was in test solution.
Incubation:
The closed test flasks were incubated in a climatised chamber under continuous stirring. The consumption of oxygen was determined by measuring the change of pressure in the flasks. Evolved carbon dioxide was absorbed in an aqueous solution (45%) of potassium hydroxide.
Test Duration:
28 days
Reference substance
- Reference substance:
- benzoic acid, sodium salt
Results and discussion
- Test performance:
- The mean biodegradation of 4-Amino-5-methylpyridinon never reached 10%. The mean biodegradation at test end after 28 days was 0% (ThODNH4, ThODNO3).
Therefore, 4-Amino-5-methylpyridinon is considered to be not readily biodegradable based on ThODNH4 and ThODNO3.
% Degradation
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 0
- Sampling time:
- 28 d
- Remarks on result:
- not readily biodegradable based on QSAR/QSPR prediction
- Details on results:
- Biodegradation of Test Item
Percentage Biodegradation:
Nitrogen is part of the molecular structure of the test item; therefore nitrification (ThODNO3) was considered for the evaluation of the results. The criterion for ready biodegradability under the conditions of a manometric respirometry test is the degradation of the test item of at least 60%, reached within a 10-day window; the 10-day window starts when the degradation of the test item reaches at least 10% degradation.
The mean biodegradation of 4-Amino-5-methylpyridinon never reached 10%. The mean biodegradation at test end after 28 days was 0% (ThODNH4, ThODNO3).
Therefore, 4-Amino-5-methylpyridinon is considered to be not readily biodegradable based on ThODNH4 and ThODNO3.
Conclusion:
The degradation rate of 4-Amino-5-methylpyridinon never reached 10%.
Therefore, 4-Amino-5-methylpyridinon is considered to be not readily biodegradable.
Biodegradation in the Toxicity Control
Percentage Biodegradation:
In the toxicity control containing both, the test item and the reference item sodium benzoate, 44% (ThODNH4) biodegradation was noted within 14 days and 46% (ThODNH4) biodegradation after 28 days of incubation (34% and 35% based on ThODNO3).
Conclusion:
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.
Abiotic Control
Oxygen Demand:
The oxygen demand in the abiotic control was 0 mg/L during the test duration
BOD5 / COD results
- Results with reference substance:
- Biodegradation of Reference Item Sodium Benzoate
Percentage Biodegradation:
The reference item sodium benzoate was sufficiently degraded to 81% after 14 days and to 87% after 28 days of incubation.
Conclusion: The percentage biodegradation of the reference item confirms the suitability of the used aerobic activated sludge inoculum.
Any other information on results incl. tables
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 |
5 |
5 |
5 |
5 |
65 |
0 |
70 |
|
2 |
5 |
5 |
5 |
5 |
90 |
0 |
90 |
|
3 |
10 |
10 |
10 |
10 |
120 |
0 |
120 |
|
4 |
10 |
10 |
10 |
10 |
130 |
0 |
130 |
|
5 |
10 |
10 |
10 |
10 |
140 |
0 |
140 |
|
6 |
15 |
15 |
15 |
15 |
145 |
0 |
145 |
|
7 |
15 |
15 |
15 |
15 |
150 |
0 |
150 |
|
8 |
15 |
15 |
15 |
15 |
150 |
0 |
155 |
|
9 |
15 |
15 |
15 |
15 |
155 |
0 |
160 |
|
10 |
15 |
15 |
15 |
15 |
155 |
0 |
160 |
|
11 |
20 |
20 |
20 |
20 |
160 |
0 |
165 |
|
12 |
20 |
20 |
20 |
20 |
160 |
0 |
165 |
|
13 |
20 |
20 |
20 |
20 |
160 |
0 |
165 |
|
14 |
20 |
20 |
20 |
20 |
160 |
0 |
165 |
|
15 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
16 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
17 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
18 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
19 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
20 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
21 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
22 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
23 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
24 |
20 |
20 |
20 |
20 |
165 |
0 |
170 |
|
25 |
20 |
20 |
20 |
20 |
170 |
0 |
170 |
|
26 |
20 |
20 |
20 |
20 |
170 |
0 |
170 |
|
27 |
20 |
20 |
20 |
20 |
170 |
0 |
170 |
|
28 |
20 |
20 |
20 |
20 |
170 |
0 |
170 |
|
Flasks 1 and 2: 4-Amino-5-methylpyridinon
Flasks 3 and 4: inoculum control
Flask5: reference(procedure control)
Flask 6: abiotic control
Flask 7: toxicity control
Percentage Biodegradation of the Test Item, of Sodium Benzoate and of the Toxicity Control based on ThODNH4
Time |
Percentage Biodegradation1 |
|||
(Days) |
4-Amino-5-methylpyridinon1 |
Sodium Benzoate2 |
Toxicity |
|
|
Flask 1 [%] |
Flask 2 [%] |
Flask 5 [%] |
Flask 7 [%] |
1 |
0 |
0 |
35 |
20 |
2 |
0 |
0 |
49 |
26 |
3 |
0 |
0 |
64 |
34 |
4 |
0 |
0 |
69 |
37 |
5 |
0 |
0 |
75 |
40 |
6 |
0 |
0 |
75 |
40 |
7 |
0 |
0 |
78 |
41 |
8 |
0 |
0 |
78 |
43 |
9 |
0 |
0 |
81 |
44 |
10 |
0 |
0 |
81 |
44 |
11 |
0 |
0 |
81 |
44 |
12 |
0 |
0 |
81 |
44 |
13 |
0 |
0 |
81 |
44 |
14 |
0 |
0 |
81 |
44 |
15 |
0 |
0 |
84 |
46 |
16 |
0 |
0 |
84 |
46 |
17 |
0 |
0 |
84 |
46 |
18 |
0 |
0 |
84 |
46 |
19 |
0 |
0 |
84 |
46 |
20 |
0 |
0 |
84 |
46 |
21 |
0 |
0 |
84 |
46 |
22 |
0 |
0 |
84 |
46 |
23 |
0 |
0 |
84 |
46 |
24 |
0 |
0 |
84 |
46 |
25 |
0 |
0 |
87 |
46 |
26 |
0 |
0 |
87 |
46 |
27 |
0 |
0 |
87 |
46 |
28 |
0 |
0 |
87 |
46 |
1ThODNH4of
4-Amino-5-methylpyridinon: 1.547 mg O2/mg test item
2ThODNH4of
sodium benzoate: 1.666 mg O2/mg reference item
Percentage Biodegradation of Test Item and of the Toxicity Control based on ThODNO3 and of Sodium Benzoate based on ThODNH4
Time |
Percentage Biodegradation1 |
|||
(Days) |
4-Amino-5-methylpyridinon1 |
Sodium Benzoate2 |
Toxicity |
|
|
Flask 1 [%] |
Flask 2 [%] |
Flask 5 [%] |
Flask 7 [%] |
1 |
0 |
0 |
35 |
15 |
2 |
0 |
0 |
49 |
20 |
3 |
0 |
0 |
64 |
26 |
4 |
0 |
0 |
69 |
28 |
5 |
0 |
0 |
75 |
30 |
6 |
0 |
0 |
75 |
30 |
7 |
0 |
0 |
78 |
31 |
8 |
0 |
0 |
78 |
33 |
9 |
0 |
0 |
81 |
34 |
10 |
0 |
0 |
81 |
34 |
11 |
0 |
0 |
81 |
34 |
12 |
0 |
0 |
81 |
34 |
13 |
0 |
0 |
81 |
34 |
14 |
0 |
0 |
81 |
34 |
15 |
0 |
0 |
84 |
35 |
16 |
0 |
0 |
84 |
35 |
17 |
0 |
0 |
84 |
35 |
18 |
0 |
0 |
84 |
35 |
19 |
0 |
0 |
84 |
35 |
20 |
0 |
0 |
84 |
35 |
21 |
0 |
0 |
84 |
35 |
22 |
0 |
0 |
84 |
35 |
23 |
0 |
0 |
84 |
35 |
24 |
0 |
0 |
84 |
35 |
25 |
0 |
0 |
87 |
35 |
26 |
0 |
0 |
87 |
35 |
27 |
0 |
0 |
87 |
35 |
28 |
0 |
0 |
87 |
35 |
1ThODNO3of
4-Amino-5-methylpyridinon: 2.579 mg O2/mg test item
2 ThODNH4of
sodium benzoate: 1.666 mg O2/mg reference item
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The degradation rate of 4-Amino-5-methylpyridinon never reached 10%.
Therefore, 4-Amino-5-methylpyridinon is considered to be not readily biodegradable. - Executive summary:
Summary
Title:
4-Amino-5-methylpyridinon: Ready Biodegradability in a Manometric Respirometry Test
Guidelines:
This study was designed to comply with the following methods:
- Commission Regulation 440/2008/EC, Method C.4-D of: Manometric Respirometry Test (EEC Publication No. L 142/496, May 2008)
- OECD Guideline for Testing of Chemicals No. 301 F: "Ready Biodegradability: Manometric Respirometry Test", adopted
Material and Methods:
Test Item:
4-Amino-5-methylpyridinon; Batch No.: BXR7SWA
Test Species:
Aerobic activated sludge (microorganisms from a domestic wastewater treatment plant) was supplied by the sewage treatment plant of Bensheim,.
Test Design:
The test item 4-Amino-5-methylpyridinon 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 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.
Endpoints:
Degradation rate of test item calculated by the oxygen consumption of the aerobic activated sludge microorganisms after 28 days of incubation.
Test Item Loading Rate (initial concentration in medium C0):
101.4 mg/L corresponding to an oxygen demand of about 156.9 mg/L (ThODNH4) and 261.6 mg/L
(ThODNO3)Reference Item:
Sodium Benzoate
Reference Item Loading Rate:
103.7 mg/L corresponding to an oxygen demand of about 172.7 mg/L (ThODNH4)
Test Conditions:
22°C ± 1°C, darkness
Results:
Biodegradation of 4-Amino-5-methylpyridinon:
Nitrogen is part of the molecular structure of the test item; therefore the evaluation of biodegradation has to be based on ThODNH4and ThODNO3. The criterion for ready biodegradability under the conditions of a manometric respirometry test is the degradation of the test item of at least 60%, reached within a 10-day window; the 10-day window starts when the degradation of the test item reaches at least 10% degradation.
The mean biodegradation of 4-Amino-5-methylpyridinon never reached 10%. The mean biodegradation at test end after 28 days was 0% (ThODNH4, ThODNO3).
Therefore, 4-Amino-5-methylpyridinon is considered to be not readily biodegradable based on ThODNH4and
ThODNO3.Biodegradation of Sodium Benzoate:
The reference item sodium benzoate was sufficiently degraded to 81% after 14 days and to 87% after 28 days of incubation, thus confirming the suitability of the aerobic activated sludge inoculum used.
Biodegradation of the Toxicity Control:
In the toxicity control containing both, the test item and the reference item sodium benzoate, 44% (ThODNH4) biodegradation was noted within 14 days and 46% (ThODNH4) biodegradation after 28 days of incubation (34% and 35% based on ThODNO3). 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.
.
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