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EC number: 266-840-7 | CAS number: 67656-24-0
- 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:
- 19 Oct - 16 Nov 2004
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Version / remarks:
- 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Version / remarks:
- 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Regulation (EC) No 648/2004 01 the Eurapean Parliament and 01 the Couneil
- Version / remarks:
- 31 March 2004 on detergents (OJ L 104, 804.2004)
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Activated sludge from the aeration tank of a municipal biological waste water treatment plant: ARA Werdhölzli, Zürich, Switzerland (18 Oct 2004; 2.00 p.m)
- Storage length: activated sludge was used immediately after sampling from the treatment plant
- Preparation of inoculum for exposure: Prior to the test the sludge was washed twice with tap water. To prepare the stock solution the test material was dissolved in a double concentration in the test medium. An appropriate amount of this stock solution was diluted with test medium to give a final test concentration of 100 mg/L.
- Pretreatment: no feed, test item and funtional control as sole organic carbon source
- Initial cell/biomass concentration: 30 mg/L dry matter in the final mixture - Duration of test (contact time):
- 28 d
- Initial conc.:
- 93 mg/L
- Based on:
- act. ingr.
- Remarks:
- 100 mg/l of test material with 93% active ingredient
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Aerobic mineral salts medium according to the guideline, prepared with deionised water
- Test temperature: 22 ± 0.5 °C
- pH: inoculum blanks 7.5; procedure control 8.1, test suspension: 7.2
- pH adjusted: yes to 7.4
- Conductivity: <1.5 µS/cm
- DOC: <0.3 mg/L (test medium)
- Suspended solids concentration: 30 mg/L dry matter
- Continuous darkness: yes (thermostat cabinet in the dark)
TEST SYSTEM
- Culturing apparatus: 500 mL glass bottles (tightly closed with manometrie BOD measuring devices); containing 200 mL total volume; bottles are equipped with stirring rods and butyl rubber quivers which contain 2 pellets of sodium hydroxide each to absorb the produced CO2 from the head space
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: test vessels were stirred by an inductive stirring system for a maximum test period of 28 days.
- Measuring equipment: During the test the O2 uptake was continuously measured with a manometrie BOD measuring device (OxiTop®-C measuring head (WTW Wissenschaftlich-Technische Werkstätten GmbH & Co. KG, Weilheim, Germany). Ultimate biodegradation was determined by analysis of dissolved organic carbon (DOC) concentrations at the beginning and at the end of the test (Shimadzu 5050 TOC-Analyzer using the NPOC-mode)
SAMPLING
- Sampling frequency: continously
CONTROL AND BLANK SYSTEM
- Inoculum blank: 2 replicates
- Abiotic sterile control: not determined
- Toxicity control: not determined
- Other: Functional control (reference) 1 replicate - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Value:
- 62
- Sampling time:
- 28 d
- Details on results:
- The lag-phase last until day 17 (7.0% degradation). At day 18 13.1% degradation was achieved and 60% after day 26 so the 10-day window was fulfilled (see table 1 in section "Any other information on results incl. tables").
- Results with reference substance:
- The procedure control sodium benzoate reaehed 80% biodegradation after 14 days, thus confirming suitability of inoculum and test conditions.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Readily biodegradable according to the OECD criteria (62% degradation after 28 d, OECD 301 F).
Reference
The ThOD value of the test substance was calculated from the molecular formula. The ThOD value was 1.235 mg O2/mg of test material.
The ThOD of the reference eompound sodium benzoate was calculated to be 1.665 mg O2/mg substance.
Table 1: O2 uptake of the test units, the inoculum blank and the corresponding degradation data
|
Inoculum blank * |
Test unit no. 1 containing test material |
Test unit no. 2 containing test material |
|
||
Time (days) |
BOD (mg O2/L) |
BOD (mg O2/L) |
Degradation (%) ** |
BOD (mg O2/L) |
Degradation (%) ** |
Mean Degradation of no. 1+2 (%) |
0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
1 |
5.0 |
8.0 |
2.6 |
8.0 |
2.6 |
2.6 |
2 |
9.0 |
8.0 |
-0.9 |
10.0 |
0.9 |
0.0 |
3 |
11.0 |
12.0 |
0.9 |
14.0 |
2.6 |
1.7 |
4 |
13.0 |
14.0 |
0.9 |
16.0 |
2.6 |
1.7 |
5 |
15.0 |
16.0 |
0.9 |
18.0 |
2.6 |
1.7 |
6 |
16.0 |
18.0 |
1.7 |
18.0 |
1.7 |
1.7 |
7 |
18.0 |
20.0 |
1.7 |
20.0 |
1.7 |
1.7 |
8 |
18.0 |
22.0 |
3.5 |
22.0 |
3.5 |
3.5 |
9 |
20.0 |
22.0 |
1.7 |
22.0 |
1.7 |
1.7 |
10 |
20.0 |
24.0 |
3.5 |
22.0 |
1.7 |
2.6 |
11 |
22.0 |
24.0 |
1.7 |
24.0 |
1.7 |
1.7 |
12 |
22.0 |
24.0 |
1.7 |
26.0 |
3.5 |
2.6 |
13 |
22.0 |
24.0 |
1.7 |
26.0 |
3.5 |
2.6 |
14 |
22.0 |
26.0 |
3.5 |
28.0 |
5.2 |
4.4 |
15 |
24.0 |
26.0 |
1.7 |
28.0 |
3.5 |
2.6 |
16 |
24.0 |
28.0 |
3.5 |
34.0 |
8.7 |
6.1 |
17 |
25.0 |
28.0 |
2.6 |
38.0 |
11.3 |
7.0 |
18 |
25.0 |
30.0 |
4.4 |
50.0 |
21.8 |
13.1 |
19 |
26.0 |
30.0 |
3.5 |
67.9 |
36.5 |
20.0 |
20 |
26.0 |
32.0 |
5.2 |
87.9 |
53.9 |
29.6 |
21 |
27.0 |
34.0 |
6.1 |
91.9 |
56.5 |
31.3 |
22 |
28.0 |
38.0 |
8.7 |
95.9 |
59.1 |
33.9 |
23 |
27.0 |
48.0 |
18.3 |
97.9 |
61.7 |
40.0 |
24 |
28.0 |
57.9 |
26.0 |
99.9 |
62.6 |
44.3 |
25 |
28.0 |
77.9 |
43.4 |
102.0 |
64.4 |
53.9 |
26 |
28.0 |
91.9 |
55.6 |
102.0 |
64.4 |
60.0 |
27 |
30.0 |
93.9 |
55.6 |
106.0 |
66.2 |
60.9 |
28 |
30.0 |
95.9 |
57.4 |
106.0 |
66.2 |
61.8 |
* Mean of two replicates
** The calculation is based on the nominal concentration of the test substance of 93 mg/L and a theoretical O2 demand (ThOD) in mg O2/mg test substance of 1.235
Table 2: O2 uptake of the procedure and toxicity control, the inoculum blank, the abiotic sterile control and the corresponding degradation data
|
Inoculum blank |
Procedure control containing sodium benzoate |
Toxicity control containing test material+sodium benzoate |
Abiotic sterile control |
||
Time (days) |
BOD (mg O2/L) |
BOD (mg O2/L) |
Degradation (%)** |
BOD (mg O2/L) |
Degradation (%)** |
BOD (mg O2/L) |
0 |
0.0 |
0.0 |
0.0 |
n.d. |
|
n.d. |
1 |
5.0 |
44.0 |
23.4 |
n.d. |
|
n.d. |
2 |
9.0 |
76.9 |
40.8 |
n.d. |
|
n.d. |
3 |
11.0 |
102.0 |
54.6 |
n.d. |
|
n.d. |
4 |
13.0 |
114.0 |
60.7 |
n.d. |
|
n.d. |
5 |
15.0 |
123.0 |
64.9 |
n.d. |
|
n.d. |
6 |
16.0 |
130.0 |
68.5 |
n.d. |
|
n.d. |
7 |
18.0 |
135.0 |
70.3 |
n.d. |
|
n.d. |
8 |
18.0 |
139.0 |
72.7 |
n.d. |
|
n.d. |
9 |
20.0 |
143.0 |
73.9 |
n.d. |
|
n.d. |
10 |
20.0 |
147.0 |
76.3 |
n.d. |
|
n.d. |
11 |
22.0 |
150.0 |
76.9 |
n.d. |
|
n.d. |
12 |
22.0 |
151.0 |
77.5 |
n.d, |
|
n.d. |
13 |
22.0 |
154.0 |
79.3 |
n.d. |
|
n.d. |
14 |
22.0 |
156.0 |
80.5 |
n.d. |
|
n.d. |
15 |
24.0 |
157.0 |
79.9 |
n.d. |
|
n.d. |
16 |
24.0 |
159.0 |
81.1 |
n.d. |
|
n.d. |
17 |
25.0 |
160.0 |
81.1 |
n.d. |
|
n.d. |
18 |
25.0 |
162.0 |
82.3 |
n.d. |
|
n.d. |
19 |
26.0 |
163.0 |
82.3 |
n.d. |
|
n.d. |
20 |
26.0 |
166.0 |
84.1 |
n.d. |
|
n.d. |
21 |
27.0 |
166.0 |
83.5 |
n.d. |
|
n.d. |
22 |
28.0 |
167.0 |
83.5 |
n.d. |
|
n.d. |
23 |
27.0 |
170.0 |
85.9 |
n.d. |
|
n.d. |
24 |
28.0 |
169.0 |
84.7 |
n.d. |
|
n.d. |
25 |
28.0 |
170.0 |
85.3 |
n.d. |
|
n.d. |
26 |
28.0 |
171.0 |
85.9 |
n.d. |
|
n.d. |
27 |
30.0 |
171.0 |
84.7 |
n.d. |
|
n.d. |
28 |
30.0 |
173.0 |
85.9 |
n.d. |
|
n.d. |
*Mean of two replicates
**The calculation is based on the nominal concentration of sodium benzoate of 100 mg/L and a theoretical O2 demand (ThOD) in mg O2/mg test substance of 1.665
n.d. not determined
Description of key information
Readily biodegradable according to the OECD criteria (62% degradation after 28 d, OECD 301 F).
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
One biodegradation screening study according to OECD 301 F (GLP) is available for the substance (BMG Engineering, 2005). Non-adapted, domestic activated sludge from a sewage treatment plant was used as inoculum. At the end of the 28 -day exposure period 62% degradation based on O2 measurement was determined and the 10 -day window criterion was fulfilled. Thus the substance can be considered as readily biodegradable.
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