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EC number: 228-408-6 | CAS number: 6259-76-3
- 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:
- 11/04/1995 - 11/05/1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Principles of method if other than guideline:
- Not relevant
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not relevant - 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 (City of Geneva, Aire) was used. The sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000 g for 10 mins, discarding the supernatant and resuspending in mineral medium) and kept aerobic until being used on the same day.
- 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
Stock solutions (a)-(d) were prepared by dissolving the following salts in 1 litre of deionised water:
(a) 8.5 g KH2PO4, 21.75 g K2HPO4, 33.40 g Na2HPO4.2H2O, 0.5 g NH4Cl
(b) 27.5 g CaCl2
(c) 22.50 g MgSO4.7H2O
(d) 0.25 g FeCl3.6H2O, one drop of HCl Conc.
The water used during this study is deionised water containing less than 10 mg/L dissolved organic carbon.
The mineral medium was 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 L with deionised water.
TEST SYSTEM
A respirometer was used (Sapromat D 12).
The dry weight of suspended solids is 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.
A volume of suspended sludge corresponding to 7.5 mg dry weight (as determined from 3.6) is placed in a 250 mL volumetric flask and made up with mineral medium. This is poured into each test flask of the Sapromat. The test and reference substances are weighed in small aluminium boats which are added to the test flasks contents. The pH of each flask is measured and, if necessary, adjusted to 7.4 ± 0.2 with phosphoric acid or potassium hydroxide. About 2 g of soda lime is placed in an attachment of the stopper, the flasks are closed and placed in the water bath of the Sapromat. After temperature and pressure equilibration, the oxygen meters of the instrument are set to zero (time zero of the experiment).
CONTROL AND BLANK SYSTEM
A pair of volumetirc flasks of the volumetric respirometer (Sapromat) are filled with:
mineral medium + test chemical (100 mg/L) + aniline (100 mg/L) + inoculum
and their respirations are recorded as for the other flasks. If they are lower than those of the flasks containing:
mineral medium + aniline (100 mg/L) + inoculum
the test chemical can be used assumed to be inhibitory to the inoculum used. - Reference substance:
- aniline
- Remarks:
- 100 mg/L; min purity = 99.5 %
- Preliminary study:
- No details supplied
- Test performance:
- 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.
- Parameter:
- % degradation (O2 consumption)
- Value:
- 91
- Sampling time:
- 28 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 82
- Sampling time:
- 10 d
- Details on results:
- Oxygen uptakes, as read on the Sapromat meters are corrected:
-by deducing the basic oxygen uptake of sludge (the average of flasks 1/1 and 2/1)
- 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 graph of BOD vs. time, % of biodegradation vs. time and the biodegradation rates.
Hexyl salicylate undergoes 91 % biodegradation after 28 days in the test conditions. Biodegradation reaches 82 % at the end of the 10-day window (days 2 to 12).
Therefore, Hexyl salicylate should be regarded as readily biodegradable according to this test. - 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
- Remarks:
- 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.
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The ready biodegradability of Hexyl salicylate has been determined according to the OECD guideline 301F. In the conditions of the test, Hexyl salicylate undergoes 91 % biodegradation after 28 days. Biodegradation reaches 82 % at the end of the 10-day window (days 2 to 12).
Thus, Hexyl salicylate should be regarded as readily biodegradable according to this test.
At the concentration used in the test (100 mg/L), it is not inhibitory to the micro-organisms - Executive summary:
The ready biodegradability of Hexyl salicylate has been determined according to the OECD guideline 301F. In the conditions of the test, Hexyl salicylate undergoes 91 % biodegradation after 28 days. Biodegradation reaches 82 % at the end of the 10-day window (days 2 to 12).
Thus, Hexyl salicylate should be regarded as readily biodegradable according to this test.
At the concentration used in the test (100 mg/L), it is not inhibitory to the micro-organisms
Reference
The curve obtained with aniline alone and with Hexyl salicylate + aniline show no toxic effect of Hexyl salicylate on the micro-organisms at the test concentration.
Table 2: BOD for Hexyl salicylate
|
Days: |
2 |
7 |
12 |
14 |
21 |
28 |
|
BOD Sludge |
1st flask |
B1 |
13.0 |
19.0 |
21.0 |
21.0 |
21.0 |
24.0 |
2nd flask |
B2 |
13.0 |
19.0 |
22.0 |
23.0 |
25.0 |
32.0 |
|
mean |
B |
13.0 |
19.0 |
21.5 |
22.0 |
23.0 |
28.0 |
|
BOD test substance |
1st flask |
C1 |
57.0 |
162.0 |
208.0 |
215.0 |
230.0 |
240.0 |
2nd flask |
C2 |
104.6 |
182.5 |
213.1 |
217.0 |
225.9 |
233.9 |
|
1stfl. Corr. |
C1-B |
44.0 |
143.0 |
186.5 |
193.0 |
207.0 |
212.0 |
|
2ndfl. Corr. |
C2-B |
91.6 |
163.5 |
191.6 |
195.0 |
202.9 |
205.9 |
|
% degradation |
1 st flask |
D1 |
19 |
62 |
81 |
84 |
90 |
92 |
2 nd flask |
D2 |
40 |
71 |
83 |
85 |
88 |
90 |
|
mean |
D |
29 |
67 |
82 |
84 |
89 |
91 |
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
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
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