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EC number: - | CAS number: -
- 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:
- 26 August 2010- 24 September 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Fully documented study run under GLP and according to international guidelines.
- Qualifier:
- according to guideline
- Guideline:
- other: ISO 14593:2005 adopted 2005 “Water quality - Evaluation of ultimate aerobic biodegradability of organic compounds in aqueous medium – Method by analysis of inorganic carbon in sealed vessels (CO2 headspace test)”
- Deviations:
- yes
- Remarks:
- Uncritical deviations: The temperature was slightly lower than demanded in the study plan (18.4 – 21.6 °C). Only five points of measurement were performed instead of eight. The content of OC and IC was determined on day 5 though not required.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 310 (Ready Biodegradability - CO2 in Sealed Vessels (Headspace Test)
- Deviations:
- yes
- Remarks:
- Uncritical deviations: The temperature was slightly lower than demanded in the study plan (18.4 – 21.6 °C). Only five points of measurement were performed instead of eight. The content of OC and IC was determined on day 5 though not required.
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- The sludge was taken from the activation basin of the ESN (Stadtentsorgung Neustadt) sewage treatment plant, Im Altenschemel, NW-Lachen-Speyerdorf.
Date of collection: 26. Aug. 2010.
The sludge was washed with tap water twice, then filtrated through a cloth and resuspended in test medium. It was then aerated. The dry matter was determined with 4000 mg suspended solids /L. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 26.32 mg/L
- Based on:
- other: nominal
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to OECD 310
TEST SYSTEM
- Number of culture flasks/concentration:
Blank: 1 flask
Control: 2 flasks
Positive control: 2 flasks
Test substance: 2 flasks
Abiotic control: 1 flask
Toxicity control:1 flask
SAMPLING
The test was performed at room temperature (18.4 – 21.6 °C) without direct lighting.
Duration of the test was 28 days. During this time, the created CO2 in the vessels was determined on days 0, 5, 13, 21, and, 28.
Sampling dates were derived from the degradation behaviour of the test item. - Reference substance:
- aniline
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 4.3
- Sampling time:
- 0 d
- Remarks on result:
- other: Based on 2 replicates
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 3.6
- Sampling time:
- 5 d
- Remarks on result:
- other: Based on 2 replicates
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 10.7
- Sampling time:
- 13 d
- Remarks on result:
- other: Based on 2 replicates
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 3.6
- Sampling time:
- 21 d
- Remarks on result:
- other: Based on 2 replicates
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 14.1
- Sampling time:
- 28 d
- Remarks on result:
- other: Based on 2 replicates
- Results with reference substance:
- Degradation of the positive control was 69% after thirteen days.
- Validity criteria fulfilled:
- yes
- Remarks:
- Degradation of positive control > 60% at day 14; Mean IC content of controls at the end of the test < 3 mg/L
- Interpretation of results:
- other: not readily biodegradable
- Conclusions:
- During the whole test an equilibrium between solution and head space was present and bioavailability of the test item was given. A degradation of the test item of 14% only was observed after 28 days. Therefore, the test item 2-propanol and 2-butanol production, distn. residues consisting mainly of di-isobutylether, di-isopropylether, C3- and C4-alcohols and C6-hydrocarbons is not readily biodegradable following ISO 14593:2005.
- Executive summary:
The test item was tested for ready biodegradability using a concentration of 26.32 mg 2-propanol and 2-butanol production, distn. residues /L (consisting mainly of di-isobutylether, di-isopropylether, C3- and C4-alcohols and C6-hydrocarbons) in test medium following ISO 14593:2005. Aniline was chosen as positive control.
Activated sludge from a sewage treating plant was used as inoculum (concentration 4 mg suspended solids/L) and the test was left running for 28 days.
All validity criteria were met and the test item concentration remained stable over the whole test. Degradation of the positive control was 69% after thirteen days.
The following data were determined for the test item:
- 10-day-window: not detectable
- degradation at the end of 10-day-window: none
- degradation at the end of the test: 14 %
Therefore, regardless of the 10-day-window, the test item 2-propanol and 2-butanol production, distn. residues is not readily biodegradable following ISO14593:2005.
Reference
For verification of bioavailability of the volatile test item, the content of organic carbon and inorganic carbon in all vessels was determined at the end of the test and on day 5. They were measured at least 3 times.
IC-values in ppm
Day |
Blank |
Control 1 |
Control 2 |
Pos. Control 1 |
Pos. Control 2 |
Test 1 |
Test 2 |
Abiotic Control |
Toxicity Control |
0 |
7.20 |
7.29 |
6.09 |
7.10 |
8.20 |
5.32 |
9.77 |
6.22 |
5.42 |
5 |
1.63 |
1.67 |
2.24 |
2.73 |
3.38 |
2.53 |
2.83 |
2.20 |
13.34 |
13 |
4.09 |
4.28 |
2.60 |
18.38 |
16.18 |
5.55 |
5.62 |
3.70 |
20.77 |
21 |
3.23 |
4.29 |
4.39 |
18.21 |
19.23 |
5.48 |
4.62 |
3.47 |
21.18 |
28 |
1.75 |
3.09 |
2.35 |
20.02 |
18.67 |
5.31 |
5.44 |
2.99 |
19.72 |
28 |
2.73 |
2.48 |
3.53 |
20.16 |
18.63 |
6.33 |
6.10 |
3.13 |
23.40 |
28 |
2.07 |
2.99 |
3.41 |
18.84 |
19.04 |
6.14 |
5.40 |
2.90 |
19.80 |
DOC-values in ppm
Day |
Blank |
Control 1 |
Control 2 |
Pos. Control 1 |
Pos. Control 2 |
Test 1 |
Test 2 |
Abiotic Control |
Toxicity Control |
5 |
2.15 |
1.54 |
1.02 |
17.95 |
17.2 |
14.58 |
14.72 |
14.5 |
14.9 |
28 |
0 |
0 |
0 |
0 |
0 |
10.76 |
10.99 |
12.48 |
0 |
28 |
0 |
0 |
0 |
0 |
0 |
9.07 |
8.21 |
12.95 |
6.69 |
28 |
0 |
0 |
0 |
0 |
0 |
9.44 |
10.37 |
11.84 |
0 |
For verification of bioavailability of the volatile test item, the content of organic carbon and inorganic carbon in all vessels was determined on day 5 and at the end of the test. A well detectable content of organic carbon was found in. all test vessels, abiotic control vessels and in one toxicity control vessel on day 5 and at the end of the test. That means that equilibrium between solution and head space was present during the test and bioavailability of the test item was given.
Net Inorganic Carbon
The net inorganic carbon was calculated from the measured IC values by subtraction of the blank (medium only without inoculum).
The net IC values are presented in the following table:
Table 1 Net IC-values in ppm
Day |
Control 1 |
Control 2 |
Pos. Control 1 |
Pos. Control 2 |
Test 1 |
Test 2 |
Abiotic Control |
Toxicity Control |
0 |
0.09 |
-1.11 |
-0.10 |
1.00 |
-1.88 |
2.57 |
-0.98 |
-1.78 |
5 |
0.04 |
0.61 |
1.10 |
1.75 |
0.90 |
1.20 |
0.57 |
11.71 |
13 |
0.19 |
-1.49 |
14.29 |
12.09 |
1.46 |
1.53 |
-0.39 |
16.68 |
21 |
1.06 |
1.16 |
14.98 |
16.00 |
2.25 |
1.39 |
0.24 |
17.95 |
28 |
0.91 |
0.17 |
17.84 |
16.49 |
3.13 |
3.26 |
0.81 |
17.54 |
28 |
0.30 |
1.35 |
17.98 |
16.45 |
4.15 |
3.92 |
0.95 |
21.22 |
28 |
0.81 |
1.23 |
16.66 |
16.86 |
3.96 |
3.22 |
0.72 |
17.62 |
Negative values are attributed to measurement uncertainties and variation within the test flasks. In these low concentrations, this is considered as typical.
Table 2 Degradation values in %
Day |
Pos. Control 1 |
Pos. Control 2 |
Pos. Control Mean |
Test 1 |
Test 2 |
Test Mean |
Abiotic Control |
Toxicity Control |
0 |
2.0 |
7.5 |
4.8 |
-6.9 |
15.4 |
4.3 |
-4.9 |
-3.2 |
5 |
3.9 |
7.1 |
5.5 |
2.9 |
4.4 |
3.6 |
2.9 |
28.7 |
13 |
74.6 |
63.6 |
69.1 |
10.6 |
10.9 |
10.7 |
-2.0 |
43.6 |
21 |
69.2 |
74.3 |
71.8 |
5.7 |
1.4 |
3.6 |
1.2 |
42.4 |
28 |
83.4 |
78.9 |
81.1 |
14.8 |
13.4 |
14.1 |
4.1 |
45.3 |
Biological Results
The results are presented in the following table.
Table 3 Results
Parameter |
Value |
Lag phase |
not detected |
10-day-window |
not detected |
Degradation at the end of 10-day-window |
not detected |
Degradation at the end of the test |
14 % |
Description of key information
No degradation of the test item was observed after 28 days. The test item “2-propanol and 2-butanol production, distn. residues” (consisting mainly of di-isobutyl ether, di-isopropyl ether, C3- and C4-alcohols and C6-hydrocarbons) is not readily biodegradable following ISO 14593:2005.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
The ready biodegradation of "2-propanol and 2-butanol production, distn. residues" (consisting mainly of di-isobutyl ether, di-isopropyl ether, C3- and C4-alcohols and C6-hydrocarbons) was tested according to ISO 14593:2005 under GLP. No significant degradation (14%) of the test item was observed after 28 days. As a result, "2-propanol and 2-butanol production, distn. residue" is not considered readily 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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