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EC number: - | CAS number: 56388-48-8
- 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Remarks:
- test on C12 naphthalene
- Adequacy of study:
- key study
- Study period:
- Start : 05 December 2012 Completion : 03 January 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP OECD guideline study without deficiencies that affected study validity
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Test material form:
- liquid: viscous
- Details on test material:
- Description: Clear amber slightly viscous liquid
Batch: 18515
Purity/Composition: UVCB (tested as 100% pure)
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- The source of test organisms was activated sludge freshly obtained from a municipal sewage treatment plant: 'Waterschap Aa en Maas', Heeswijk-Dinther, The Netherlands, receiving predominantly domestic sewage.
The freshly obtained sludge was used immediately. The concentration of suspended solids, determined on sludge taken 2 days later from the same sewage treatment plant was 4 g/l in the concentrated sludge. The amount of suspended solids is representative for the sludge used in this study. Before use, the sludge was allowed to settle (78 minutes) and the supernatant liquid was used as inoculum at the amount of 10 ml/l of mineral medium. - Duration of test (contact time):
- >= 28 d
Initial test substance concentration
- Initial conc.:
- >= 12 mg/L
- Based on:
- ThIC
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- The study consisted of six bottles:
- 2 inoculum blanks (no test substance),
- 2 test bottles (alkylated naphthalene),
- 1 positive control (sodium acetate) and
- 1 toxicity control (alkylated naphthalene) plus sodium acetate).
Results and discussion
- Preliminary study:
- No preliminary test was conducted.
- Test performance:
- 1. The positive control substance was biodegraded by at least 60% (68%) within 14 days.
2. The difference of duplicate values for %-degradation of the test substance was always less than 20.
3. The total CO2 release in the blank at the end of the test did not exceed 40 mg/l (56 mg CO2 per 2 litres of medium, corresponding to 28 mg CO2/l).
4. The Inorganic Carbon content (IC) of the test substance (suspension) in the mineral medium at the beginning of the test was less than 5% of the Total Carbon content (TC). Since the test medium was prepared in tap-water purified by reverse osmosis (Milli-RO water (Millipore Corp., Bedford, Mass., USA, carbon levels < 500 ppb)), IC was less than 5% of TC (mainly coming from the test substance, 12 mg TOC/l).
Since all criteria for acceptability of the test were met, this study was considered to be valid.
4. The Inorganic Carbon content (IC) of the test substance (suspension) in the mineral medium at the beginning of the test was less than 5% of the Total Carbon content (TC). Since the test medium was prepared in tap-water purified by reverse osmosis (Milli-RO water (Millipore Corp., Bedford, Mass., USA, carbon levels < 500 ppb)), IC was less than 5% of TC (mainly coming from the test substance, 13 mg TOC/l).
Since all criteria for acceptability of the test were met, this study was considered to be valid.
% Degradation
- Parameter:
- % degradation (CO2 evolution)
- Value:
- >= 1 - <= 2
- Sampling time:
- 29 d
- Details on results:
- See results table
BOD5 / COD results
- Results with reference substance:
- The reference substance biodegraded by 68% within 14 days.
Any other information on results incl. tables
Table 1 CO2production and percentage biodegradation of the test substance (bottle A). |
|
||||||||
|
Day |
HCl (0.05 N) titrated (ml) |
Produced CO2 (ml HCl) |
Produced CO2 (mg) |
Cumulative CO2 (mg) |
Biodegradation1) (%) |
|||
|
Blank (mean) |
bottle A |
|||||||
|
2 |
46.27 |
45.45 |
0.82 |
0.9 |
0.9 |
1 |
||
|
5 |
44.69 |
44.70 |
0.00 |
0.0 |
0.9 |
1 |
||
|
7 |
44.92 |
46.30 |
0.00 |
0.0 |
0.9 |
1 |
||
|
9 |
45.85 |
46.38 |
0.00 |
0.0 |
0.9 |
1 |
||
|
14 |
45.04 |
45.59 |
0.00 |
0.0 |
0.9 |
1 |
||
|
19 |
43.74 |
44.76 |
0.00 |
0.0 |
0.9 |
1 |
||
|
23 |
44.08 |
44.91 |
0.00 |
0.0 |
0.9 |
1 |
||
|
26 |
44.98 |
44.67 |
0.31 |
0.3 |
1.2 |
1 |
||
|
29 |
43.36 |
43.41 |
0.00 |
0.0 |
1.2 |
1 |
||
|
29 |
46.23 |
46.64 |
0.00 |
0.0 |
1.2 |
1 |
||
|
29 |
47.85 |
47.55 |
0.30 |
0.3 |
1.6 |
2 |
||
|
1): Calculated as the ratio between CO2produced (cumulative) and the ThCO2of the test substance: 84.2 mg CO2/2l |
|
Table 2 CO2production and percentage biodegradation of the test substance (bottle B). |
|
||||||||
|
Day |
HCl (0.05 N) titrated (ml) |
Produced CO2 (ml HCl) |
Produced CO2 (mg) |
Cumulative CO2 (mg) |
Biodegradation1) (%) |
|||
|
Blank (mean) |
bottle B |
|||||||
|
2 |
46.27 |
45.49 |
0.78 |
0.9 |
0.9 |
1 |
||
|
5 |
44.69 |
44.89 |
0.00 |
0.0 |
0.9 |
1 |
||
|
7 |
44.92 |
45.11 |
0.00 |
0.0 |
0.9 |
1 |
||
|
9 |
45.85 |
46.85 |
0.00 |
0.0 |
0.9 |
1 |
||
|
14 |
45.04 |
46.28 |
0.00 |
0.0 |
0.9 |
1 |
||
|
19 |
43.74 |
45.19 |
0.00 |
0.0 |
0.9 |
1 |
||
|
23 |
44.08 |
45.48 |
0.00 |
0.0 |
0.9 |
1 |
||
|
26 |
44.98 |
45.66 |
0.00 |
0.0 |
0.9 |
1 |
||
|
29 |
43.36 |
43.66 |
0.00 |
0.0 |
0.9 |
1 |
||
|
29 |
46.23 |
46.69 |
0.00 |
0.0 |
0.9 |
1 |
||
|
29 |
47.85 |
47.66 |
0.19 |
0.2 |
1.1 |
1 |
||
|
1): Calculated as the ratio between CO2produced (cumulative) and the ThCO2of the test substance: 87.9 mg CO2/2l |
|
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- other: not readily biodegradable
- Conclusions:
- Alkylated naphthalene was not readily biodegradable under the conditions of the modified Sturm test presently performed.
- Executive summary:
A Ready Biodegradation Test was conducted with alkyalted naphthalene. The study procedures described in this report were based on the OECD guideline No. 301 B, 1992. In addition, the procedures were designed to meet the test methods of the Commission Regulation (EC) No. 440/2008 of 30 May 2008, Publication No. L142, Part C.4-C, ISO International Standard 9439, 1999 and ISO Standard 10634, 1995.
Alkylated naphthalene, a UVCB, was a clear amber slightly viscous liquid and was not sufficiently soluble to allow preparation of an aqueous solution at a concentration of 1 g/l.
The Total Organic Carbon (TOC) content of alkyalted naphthalene was determined to be 91%. The test substance was tested in duplicate at approximately 13 mg/l, corresponding to 12 mg TOC/l. The Theoretical CO2 production (ThCO2) was calculated to be 3.33 mg CO2/mg.
The study consisted of six bottles:
- 2 inoculum blanks (no test substance),
- 2 test bottles (Alkylated naphthalene),
- 1 positive control (sodium acetate) and
- 1 toxicity control (Alkylated naphthalene plus sodium acetate).
Weighed amounts were added to the 2-litres test bottles containing medium with microbial organisms and mineral components. To this end, approximately 20 ml of Milli-RO water was added to each weighing bottle containing the test substance. After vigorous mixing (vortex) the resulting suspension was added quantitatively to the test medium. The test solutions were continuously stirred during the test, to ensure optimal contact between the test substance and the test organisms. Test duration was 28 days (last CO2-measurement on the 29th day).
The relative biodegradation values calculated from the measurements performed during the test period revealed no significant biodegradation of Alkylated naphthalene..In the toxicity control, Alkyalted naphthalene was found not to inhibit microbial activity. Since all criteria for acceptability of the test were met, this study was considered to be valid.
In conclusion, Alkylated naphthalene was designated as not readily biodegradable.
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