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EC number: 202-288-5 | CAS number: 93-92-5
- 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:
- 9th July 1996 to 7th August 1996
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- no
- GLP compliance:
- yes
- Specific details on test material used for the study:
- - Name of test material: 1-phenylethyl acetate
- Physical state: colourless liquid
- Name of test material (as cited in study report): Gardenol
- Lot/batch No.: 260657 - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (City of Geneva, Aïre) was used.- Preparation of inoculum for exposure: the sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000 g for 10 minutes, discarding the supernatant and resuspending in mineral medium) and kept aerobic until being used on the same day.- Concentration of sludge: the dry weight of suspended solids is determined by taking to 50 mL samples of the homogenised sludge, evaporating water on a steam bath, drying in an oven at 105 - 110 ºC for two hours and weighing the residue. Dry weight of suspended solids: 4.346 g/L. To obtain a concentration of 30 mg/L (dry weight) in a 250 mL flask, 1.73 mL of sludge is needed (inoculum).- Water filtered: the water used during this study is deionised water containing less than 10 mg/L dissolved organic carbon.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS- Composition of medium: prepared by mixing 50 mL of solution A and 2000 mL deionised water, adding 5 mL of each of the solutions B, C and D and making up to 5 litres with deionised water.- Test temperature: 22 ºC- pH: 7.4- pH adjusted: yes (with phosphoric acid or potassium hydroxide as necessary)TEST SYSTEM- Culturing apparatus: 250 mL volumetric flasks- Number of culture flasks/concentration: flasks were prepared in duplicate- Measuring equipment: SAPROMAT D 12, made by J. M. VOITH GmbH, D-7920 HeidenheimSTATISTICAL METHODS:Oxygen uptakes as read on the SAPROMAT meters are corrected:- by deducting the basic oxygen uptake of sludge (flasks 2/7 and 2/8)- proportionally to account for the differences between actual and nominal concentrations of test and reference substances. Averages of identical flasks have been used to obtain the graphs of BOD versus time (Figure 1) and percentage of biodegradation versus time (Figure 2).
- Reference substance:
- aniline
- Preliminary study:
- No preliminary study was performed.
- Test performance:
- No unusual observations were noted in the study.
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 89
- Sampling time:
- 28 d
- Remarks on result:
- other: Mean % degradation
- Parameter:
- % degradation (O2 consumption)
- Value:
- 68
- Sampling time:
- 12 d
- Remarks on result:
- other: Mean % degradation; 10-day window
- Details on results:
- 1-phenylethyl acetate undergoes an average of 89% biodegradation after 28 days in the test conditions (figure 2). Biodegradation starts on day 2 and reaches 68% at the end of the 10-day window (days 2 to 12).The curve (figure 1) obtained with aniline alone and with 1-phenylethyl acetate and aniline show no toxic effect of 1-phenylethyl acetate on the micro-organisms at the test concentration.
- Results with reference substance:
- Degradation of aniline exceeds 40% after 7 days and 65% after 14 days: the activity of the inoculum is thus verified and the test is considered as valid.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Under the conditions of the test, 1-phenylethyl acetate undergoes an average 89% biodegradation after 28 days and meets the 10-day widow criterion. Thus the substance is considered to be readily biodegradable.
- Executive summary:
The ready biodegradability of 1-phenylethyl acetate has been determined by the Manometric Respirometry Test according to the OECD Guidelines for Testing of Chemicals, Method No. 301 F.
1-phenylethyl acetate undergoes on average 89% biodegradation after 28 days in the test conditions. Biodegradation starts on day 2 and reaches 68% at the end of the 10-day window (days 2 to 12).
Thus 1 -phenylethyl acetate should be regarded as readily biodegradable according to this test.
At the concentration used in the test (100 mg/L), 1-phenylethyl acetate is not inhibitory to the micro-organisms.
Reference
Table 1: Actual concentrations and pH measurements
Concentrations (mg/L) | pH | |||
Flask number | Test substance | Reference substance | initial | final |
2/5 | 0 | 100.0 | 7.42 | 7.99 |
2/6 | 0 | 100.0 | 7.40 | 7.91 |
2/7 | 0 | 0 | 7.37 | 7.48 |
2/8 | 0 | 0 | 7.34 | 7.40 |
1/11 | 102.1 | 0 | 7.45 | 7.54 |
1/12 | 100.8 | 0 | 7.43 | 7.46 |
1/9 | 100.2 | 100.0 | 7.47 | 8.29 |
7/10 | 99.4 | 100.0 | 7.47 | 8.46 |
Nominal concentrations
Test substance: 100 mg/L
Reference substance: 100 mg/L
Table 2: Biodegradation of test substance
Days: | 2 | 7 | 12 | 14 | 21 | 28 | ||
BOD sludge | 1st flask | B1 | 5.0 | 10.0 | 10.0 | 12.0 | 23.0 | 23.0 |
(figure 1) | 2nd flask | B2 | 5.0 | 7.0 | 7.0 | 8.0 | 17.0 | 17.0 |
mean | B | 3.5 | 8.5 | 8.5 | 10.0 | 20.0 | 20.0 | |
BOD test substance | 1st flask | C1 | 33.4 | 105.9 | 166.6 | 178.4 | 197.2 | 203.1 |
(figure 1) | 2nd flask | C2 | 30.8 | 110.2 | 170.7 | 181.6 | 236.3 | 253.1 |
1st fl. corr. | C1-B | 29.9 | 97.4 | 158.1 | 168.4 | 177.2 | 183.1 | |
2nd fl. corr. | C2-B | 27.3 | 101.7 | 162.2 | 171.6 | 216.3 | 233.1 | |
% degradation | 1st flask | D1 | 13 | 42 | 68 | 72 | 76 | 78 |
(figure 2) | 2nd flask | D2 | 12 | 43 | 69 | 73 | 92 | 100 |
mean | D | 12 | 43 | 68 | 73 | 84 | 89 |
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)
Table 3: Biodegradation of reference substance
Days: | 5 | 7 | 10 | 14 | 21 | 28 | ||
BOD sludge | 1st flask | B1 | 9.0 | 10. | 10. | 12.0 | 23.0 | 23.0 |
(figure 1) | 2nd flask | B2 | 6.0 | 7.0 | 7.0 | 8.0 | 17.0 | 17.0 |
mean | B | 7.5 | 8.5 | 8.5 | 10.0 | 20.0 | 20.0 | |
BOD reference substance | 1st flask | A1 | 186.9 | 198.9 | 206.9 | 214.9 | 227.9 | 232.9 |
(figure 1) | 2nd flask | A2 | 158.9 | 192.9 | 202.9 | 210.9 | 222.9 | 226.9 |
1st fl. corr. | A1-B | 179.4 | 190.4 | 198.4 | 204.9 | 207.9 | 212.9 | |
2nd fl. corr. | A2-B | 151.4 | 184.4 | 194.4 | 200.9 | 202.9 | 206.9 | |
% degradation | 1st flask | D1 | 74 | 79 | 82 | 85 | 86 | 88 |
2nd flask | D2 | 63 | 77 | 81 | 83 | 84 | 86 | |
mean | D | 69 | 78 | 82 | 84 | 85 | 87 |
B = (B1 + B2) / 2
D1 = 100 * (A1 - B) / ThOD * [S]
D2 = 100 * (A2 - B0 / ThOD * [S]
D = (D1 + D2) /2
[S] = initial test substance concentration (mg/L)
Description of key information
1-phenylethyl acetate has been tested for ready biodegradability. It achieved >60 % biodegradation after 28 days and passed the 10 day window criterion in two standardised biodegradation tests. Therefore it is regarded as readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
In the key study, the ready biodegradability of 1-phenylethyl acetate was determined by the Manometric Respirometry Test (OECD 301F) and the study determined that 1-phenylethyl acetate undergoes on average 89% biodegradation after 28 days under test conditions. Biodegradation starts on day 2 and reaches 68% at the end of the 10-day window (days 2 to 12). 1-phenylethyl acetate should therefore be regarded as readily biodegradable according to this test. 1-phenylethyl acetate was also determined to be readily biodegradable in the supporting test (>100% after 28 days in sealed CO2 test, 10 day window criterion met).
A biodegradation study for the structurally closely related analogue, benzyl acetate, is also included in the dossier as relevant supporting information to strengthen the rationale for the use of read-across to benzyl acetate (source substance) in order to address short-term toxicity to aquatic invertebrates and toxicity to aquatic algae for 1-phenylethyl acetate (target substance). In an OECD Guideline 301C study, benzyl acetate was determined to be readily biodegradable. The result has been included in the data matrix of the target records for the two read-across endpoints (acute daphnia and algal inhibition).
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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