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EC number: 941-360-7 | 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)
Description of key information
Key information for Acetophenone:
Information on aerobic and anaerobic degradation of acetophenone are available. In the study conducted according to OECD Guideline 301C, acetophenone proved to be readily biodegradable and fulfilling the 14 d window criterion (64.7% biodegradation after 14 d). A number of supportive studies confirm this result obtained at the well-known stringent conditions of the MITI Test (very high ratio substance/inoculum).
Under anaerobic conditions, acetophenone was biodegraded neither in the standard test nor in the low concentration test in appreciable amounts (general: 30% biodegradation after 28 d; in the low concentration test: 15% degradation after 28 d, value taken from a figure). Benzoic acid (reference substance) was biodegraded by more than 78% after 14 d.
Key information regarding the Reaction mass of acetophenone and hydratropaldehyde and (E)-1,4-diphenyl-2-butene-1,4-dione:
Based on the available data for a high percentage of the constituents, the multi constituent substance is regarded as at least inherently biodegradable. No further testing regarding the Ready biodegradability (9.2.1.1 of Annex VII, REACH) is considered appropriate. This procedure is in compliance with the general rules contained in Annex XI, REACH (see detailed discussion below).
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Discussion regarding Acetophenone:
The aerobic biodegradation was investigated in a study conducted according to OECD Guideline 301C ' Ready biodegradability: Modified MITI Test (I)' and judged as valid with restrictions due to some missing information. The study on the anaerobic biodegradation of acetophenone was judged as reliable with restrictions as the study is documented in sufficient detail and the methods applied meet generally accepted scientific principles.
Discussion regarding the Reaction mass of acetophenone and hydratropaldehyde and (E)-1,4-diphenyl-2-butene-1,4-dione
No tests regarding biodegradability are available with the registered substance. The procedure laid down in the CLP regulation (1272/2008/EG) to base the classification and labelling on the available data and classification of the known main and relevant constituents was used.
Table Main constituents of the registered substance and other relevant substances that were analytically determined and respective data on biodegradability
Substance (other names), main constituents marked in bold letters |
CAS |
LL (%) |
UL (%) |
typical concentration (%) |
biodegradability data |
(E)-1,4-diphenyl-2-butene-1,4-dione (trans-1,2-Dibenzoylethylene) |
959-28-4 |
3 |
10 |
5.5 |
no data |
1,1'-(1,1-dimethyl-3-methylene-1,3-propanediyl)bisbenzene (dim. A-MS) |
6362-80-7 |
1 |
2.2 |
1.9 |
not readily biodegradable; inherently biodegradable (OECD 302 C: mean of 64% degradation, after 28 days) (ECHA-Information on registered substance) |
2-phenylpropan-2-ol (DMPC) |
617-94-7 |
0.5 |
5 |
1.6 |
no data |
acetophenone (Acvph) |
98-86-2 |
40 |
80 |
69 |
64,7%/14d (OECD 301 C). --> readily biodegradable |
cresol |
1319-77-3 |
2 |
4 |
0.71 |
p-cresol: 80 to 95% were degraded within 40 days, OECD 301 C, activated sludge (Desai et al., 1990) o-cresol: 80 to 95 % were degraded within 40 days, OECD 301 C, activated sludge (Desai et al., 1990) m-cresol: 90 % after 28 d, OECD 302 D, closed bottle test, sewage (study report, 2002) (based onECHA-Information on registered substance) |
hydratropaldehyde (Phenylpropionaldehyd-2) |
93-53-8 |
5 |
20 |
8.5 |
no data |
phenol |
108-95-2 |
0.1 |
0,5 |
0.11 |
activated sludge 62 %/100 h, readily biodegradable (OECD 301C); activated sludge (anaerob): 80,1 %/50 d, readily biodegradable under anaerob conditions(ECETOC-Method). Water: 86–96 %/20 d, readily biodegradable (BOD-Test APHA) |
β,β-dimethylstyrene |
768-49-0 |
0.2 |
5 |
1.2 |
no data |
unknown constituents |
|
1 |
15 |
11.5 |
no data |
Data on Biodegradability is available for the main constituent Acetophenon (with up to 80% concentration) and the impurities1,1'-(1,1-dimethyl-3-methylene-1,3-propanediyl)bisbenzene and Phenol. For the impurity isomeric mixture cresol (CAS1319-77-3) results for the isomerso-, m-, p-cresol were extrapolated to cresol by the REACH registrants (based on available disseminated information by ECHA).
Based on the available data for a high percentage of the constituents, the multi constituent substance is regarded as at least inherently biodegradable. No further testing regarding the Ready biodegradability (9.2.1.1 of Annex VII, REACH) is considered appropriate. This procedure is in compliance with the general rules contained in Annex XI, REACH.
However it needs to be pointed out that there is no data available with regard to biodegradability for a minor part of the substance composition.
References
Desai S, Govind R, Tabak H, ACS Symp. Ser. 422: 142-156, 1990
ECHA: http://echa.europa.eu/information-on-chemicals
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