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EC number: 242-745-6 | CAS number: 19009-56-4
- 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:
- 27 February 2012 to 04 May 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- The study was conducted in accordance with international guidelines and in accordance with GLP. All relevant validity criteria were met.
- 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
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.3110 (Ready Biodegradability)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- 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 (Bois-de-Bay, Satigny, Switzerland) was used. The sludge is collected in the morning, washed three times in the mineral medium (by centrigugation at 1000 g for 10 minutes, discarding the supernatant and resuspending in mineral medium) and kept aerobic until being used on the same day.
The dry weight of suspended solids was determined by taking two 50 mL samples of the homogenised sludge, evaporating water on a steam bath, drying in an oven at 105 - 110 °C for two hours and weighing the residue.
Dry weight of suspended solids: 6.36 g/L, diluted to 1.53 g/L.
To obtain a concentration of 30 mg/L (dry weight) in 103 mL total volume. 2 mL of sludge was added (inoculum).
To obtain a concentration of 30 mg/L (dry weight) in 255 mL total volume, 5 mL of sludge was added (inoculum). - Initial conc.:
- 30 mg/L
- Based on:
- ThOD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: According to OECD 301 Guideline
- Additional substrate: Not applicable
- Solubilising agent (type and concentration if used): Not applicable
- Test temperature: 21.8 - 22.9 °C
- pH: 7.4 - 8.0
- pH adjusted: no
- CEC (meq/100 g): Not applicable
- Aeration of dilution water: Yes
- Suspended solids concentration: 30 mg/L
- Continuous darkness: Yes
- Other:
TEST SYSTEM
- Culturing apparatus: Closed flask
- Number of culture flasks/concentration: Control x 2, Reference x 2, Test x 2
- Method used to create aerobic conditions: aeration
- Method used to create anaerobic conditions: Not applicable
- Measuring equipment: Oxitop system
- Test performed in closed vessels due to significant volatility of test substance: Yes
- Test performed in open system: No
- Details of trap for CO2 and volatile organics if used: Not applicable
- Other:
SAMPLING
- Sampling frequency: Daily
- Sampling method: In-situ oxitop measurement
- Sterility check if applicable: Not applicable
- Sample storage before analysis: No
- Other:
CONTROL AND BLANK SYSTEM
- Inoculum blank: Yes
- Abiotic sterile control: No
- Toxicity control: No
- Other:
STATISTICAL METHODS:
Not applicable - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- (Fluka, Buchs, Switzerland, Art. No. 71300), purity = 99 %
- Preliminary study:
- Not applicable
- Parameter:
- % degradation (O2 consumption)
- Value:
- 5
- Sampling time:
- 1 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 16
- Sampling time:
- 2 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 44
- Sampling time:
- 7 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 58
- Sampling time:
- 12 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 74
- Sampling time:
- 21 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 77
- Sampling time:
- 28 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 80
- Sampling time:
- 36 d
- Details on results:
- Oxygen uptakes, as read on the Oxitop controller, are corrected to account for the small differences between actual and nominal concentrations of test and reference substances.
The substance undergoes 77 % biodegradation after 28 days (80 % after 36 days) under the test conditions. The 10-day window criterion is not fulfilled (16 % biodegradation on day 2 and 58 % on day 12). The substance did not inhibit the intrinsic respiration of the inoculum the the test concentration and was therefore considered to be non-toxic to the inculum at the test concentration.
The repeatability validity criterion (not more than 20 % difference between replicates) is fulfilled for the flasks containing test substance, confirming validity of the study. - Results with reference substance:
- Degradation of the reference substance exceeded 40 % after 7-days and 65 % after 14 days, meeting the relevant validity criterion.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable, but failing 10-day window
- Conclusions:
- The substance undergoes 77 % biodegradation after 28 days (80 % after 36 days) under the test conditions. The 10-day window criterion is not fulfilled (16 % biodegradation on day 2 and 58 % on day 12). The test item can not be considered as readily biodegradable, however the results indicate that the substance may be regarded as inherently and ultimately biodegradable.
- Executive summary:
The ready biodegradability of the test item was determined in accordance with OECD 301F (Manometric Respirometry Test). The substance underwent 77 % biodegradation after 28 -days (80 % after 36 days) under test conditions. The 10 -day window criterion was not fulfilled (16 % biodegradation on day 2 and 58 % on day 12). The test item did not inhibit the intrinsic respiration of the inoculum at the test concentration and was therefore considered to be non-toxic to the inoculum at the test concentration.
The test item should be regarded as not readily biodegradable according to the study. However, based on the results the test item may be regarded as inherently and ultimately biodegradable.
Reference
Theoretical Oxygen Demand
Formula: C11H22N0O1
Molecular Weight: 170.3 g/mol
Theoretical Oxygen Demand (ThOD): 3.01 mg O2/mg
Biodegradation of the Test Item
|
Days: |
1 |
2 |
7 |
12 |
21 |
28 |
36 |
|
O2 Uptake of Sludge (Inoculum Blank) |
1a |
B1 |
8.1 |
16.2 |
28.3 |
35.0 |
41.7 |
47.1 |
51.2 |
2a |
B2 |
8.1 |
16.2 |
28.3 |
35.0 |
41.7 |
45.8 |
48.5 |
|
Mean |
B |
8.1 |
16.2 |
28.3 |
35.0 |
41.7 |
46.5 |
49.9 |
|
O2 Uptake of Test Substance + Sludge |
19a |
C1 |
13.5 |
31.1 |
68.9 |
87.7 |
110.3 |
118.3 |
123.3 |
20a |
C2 |
12.1 |
31.0 |
67.4 |
87.6 |
106.2 |
114.2 |
120.2 |
|
O2 Uptake of Test Substance |
|
C1-B |
5.4 |
14.9 |
40.6 |
52.7 |
68.6 |
71.8 |
73.4 |
|
C2-B |
4.0 |
14.8 |
39.1 |
52.6 |
64.5 |
67.7 |
70.3 |
|
% Biodegradation of Test Substance |
|
D1 |
6 |
16 |
45 |
58 |
76 |
80 |
81 |
|
D2 |
4 |
16 |
43 |
58 |
71 |
75 |
78 |
|
mean |
D |
5 |
16 |
44 |
58 |
74 |
77 |
80 |
Calculations:
B1, B2, C1, C2, A1, A2, E1: Experimental O2 uptake values
B = (B1 + B2) / 2
D1 = 100 * (C1 - B) / ThOD * [S]
D2 = 100 * (C2 - B) / ThOD * [S] D = (D1 + D2) / 2
[S]: Initial test substance concentration (mg/L)
Biodegradation of the Reference Item
|
Days: |
5 |
7 |
14 |
21 |
28 |
|
O2 Uptake of Sludge (Inoculum Blank) |
1a |
B1 |
24.2 |
28.3 |
37.7 |
41.7 |
47.1 |
2a |
B2 |
24.2 |
28.3 |
36.3 |
41.7 |
45.8 |
|
Mean |
B |
24.2 |
28.3 |
37.0 |
41.7 |
46.5 |
|
O2 Uptake of Test Substance + Sludge |
17a |
A1 |
146.2 |
162.3 |
188.5 |
198.5 |
204.5 |
18a |
A2 |
146.2 |
162.3 |
183.4 |
198.5 |
204.5 |
|
O2 Uptake of Test Substance |
|
A1-B |
122.0 |
134.0 |
151.5 |
156.8 |
158.1 |
|
A2-B |
122.0 |
134.0 |
146.4 |
156.8 |
158.1 |
|
% Biodegradation of Test Substance |
|
D1 |
73 |
80 |
91 |
94 |
95 |
|
D2 |
73 |
80 |
88 |
94 |
95 |
|
mean |
D |
73 |
80 |
89 |
94 |
95 |
Calculations:
B1, B2, C1, C2, A1, A2, E1: Experimental O2 uptake values
B = (B1 + B2) / 2
D1 = 100 * (C1 - B) / ThOD * [S]
D2 = 100 * (C2 - B) / ThOD * [S] D = (D1 + D2) / 2
[S]: Initial test substance concentration (mg/L)
Description of key information
28d Biodegradation: 77 %, readily biodegradable but failing the 10-day window; OECD 301F; Anon, 2012
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable but failing 10-day window
Additional information
In a single key study, the ready biodegradability of the test item was determined in accordance with OECD 301F (Manometric Respirometry Test). The substance underwent 77 % biodegradation after 28 -days (80 % after 36 days) under test conditions. The 10 -day window criterion was not fulfilled (16 % biodegradation on day 2 and 58 % on day 12). The test item did not inhibit the intrinsic respiration of the inoculum at the test concentration and was therefore considered to be non-toxic to the inoculum at the test concentration.
The test item should be regarded as not readily biodegradable according to the study. However, based on the results the test item may be regarded as inherently and ultimately biodegradable.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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