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EC number: 483-940-8 | 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:
- From January 23, 2008 to April 15, 2008
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
- Version / remarks:
- Modified Sturm Test
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- - Source of inoculum/activated sludge: Waterschap de Maaskant, ‘s-Hertogenbosch, The Netherlands
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 12 mg/L
- Based on:
- TOC
- Reference substance:
- acetic acid, sodium salt
- Remarks:
- Sodium acetate
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 24
- Sampling time:
- 28 d
- Remarks on result:
- other: The percentage biodegradation of Everzol Red CDN Crude was not achieve 60 % with following 10 days.
- Results with reference substance:
- At Day 14 during the study, the biodegradation was 72 %.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- According to OECD 301B test method and EC Method C.4-C, Everzol Red CDN Crude was not readily biodegradable.
- Executive summary:
This test using the procedures outlined in the NOTOX Study Plan for 487481, OECD 301B (OECD, 1992) and EC Method C.4-C (1992). The results of this test for Everzol Red CDN Crude show that all validity criteria were met. Everzol Red CDN Crude was not be considered readily biodegradable under the test conditions.
Reference
Positive control: reference substance and inoculum.
Toxicity control: test substance, reference substance and inoculum.
The total CO2 release in the blank at the end of the test was 22.8 mg/l.
Table 1. The percentage biodegradation of Positive control, Toxicity control and Test substance
Day |
Biodegradation (%) |
|||||
Positive control |
Toxicity control |
Test substance |
||||
Bottle A |
Bottle B |
Mean A and B |
ΔA and B1 |
|||
2 |
16 |
9 |
3 |
3 |
3 |
1 |
5 |
41 |
24 |
12 |
12 |
12 |
0 |
7 |
55 |
29 |
12 |
15 |
14 |
2 |
9 |
62 |
31 |
14 |
16 |
15 |
2 |
14 |
72 |
37 |
17 |
18 |
17 |
2 |
19 |
78 |
40 |
19 |
20 |
19 |
1 |
23 |
80 |
42 |
20 |
21 |
20 |
1 |
27 |
81 |
43 |
22 |
22 |
22 |
0 |
29 |
82 |
44 |
22 |
24 |
23 |
1 |
29 |
82 |
44 |
22 |
25 |
23 |
2 |
29 |
82 |
44 |
22 |
26 |
24 |
3 |
1Absolute difference in biodegradation between bottles A and B
Description of key information
Not readily biodegradable (OECD TG 301B and EC Method C.4-C).
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable, not fulfilling specific criteria
Additional information
The total CO2 release in the blank at the end of the test did not exceed 40 mg/l. The positive control was degraded by 72 % within 14 days and the difference of duplicate values for %-degradation of Everzol Red CDN Crude was always less than 20. All test validity criteria were met. Toxicity control was 37% degradation occurred within 14 days. Therefore, the test substance was assumed not to inhibit microbial activity. The percentage biodegradation of Everzol Red CDN Crude was not achieve 60 % with following 10 days. Therefore, Everzol Red CDN Crude was not the readily biodegradable.
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