Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 203-149-1 | CAS number: 103-83-3
- 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: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-GLP guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 302 B (Inherent biodegradability: Zahn-Wellens/EMPA Test)
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, industrial, non-adapted
- Details on inoculum:
- - Initial cell/biomass concentration: 1 g/l
- Initial conc.:
- 400 mg/L
- Based on:
- other: DOC (calculated)
- Initial conc.:
- 425 mg/L
- Based on:
- other: DOC (measured)
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- pH: 6.7 - 7.4
- pH adjusted: yes - Parameter:
- % degradation (DOC removal)
- Value:
- 90 - 100
- Sampling time:
- 13 d
- Interpretation of results:
- inherently biodegradable
- Conclusions:
- Benzyldimethylamine was shown to be 100% inherently biodegradable after 13 days.
- Executive summary:
The inherent biodegradability of benzyldimethylamine was tested in a study equivalent or similar to a 13-d- Zahn-Wellens test (OECD Guideline 302B). With an initial test substance concentration of 425 mg/L and an activated sludge (industrial, non-adadapted) with an initial cell/biomass concentration of 1 g/L 100% degradability of benzyldimethylamine was determined by DOC-removal.
Benzyldimethylamine was shown to be 100% inherently biodegradable after 13 days and fulfilled the criterion for inherent, ultimative biodegradability (70% degradability within 7 days).
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Qualifier:
- according to guideline
- Guideline:
- other: "Biodegradation test of chemical substance by mircoorganisms etc." stipulated in the order Prescribing the Items of the test relating to the new chemical substance (1974)
- Principles of method if other than guideline:
- This guideline corresponds to 301C, ready biodegradability: modified MITI Test (I) or 302C, inherent biodegradability: modified MITI Test (II) stipulated in the OECD Guidelines for testing of chemicals (May 12, 1981)
- GLP compliance:
- not specified
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- mixture of sewage, soil and natural water
- Details on inoculum:
- Sludge concentration: 30 mg/L related to BOD
Preparation of acitvated sludge:
Sludge sampling sites and time
Sampling were made four times in every year at ten places in Japan. Details are reread in bibliographic source mentioned above
Mixing of fresh and old activated sludge
5L of the filtrate of the supernatant of an activated sludge in the present use was mixed with 500 mL of the filtrate of the supernatant of a newly collected sludge respectively and the mixture was cultured at 7.0 +- 1.0 under the sufficient aeration (prefiltered open air was used for aeration)
Culture
About 30 minutes after ceasing the aeration to the sludge mixture, supernatant corresponding to about 1/3 of the whole volume was removed. Then the equal volume of dechlorination water was added to the remaining portion and aerated again, followed by addition of synthetic sewage*, concentration of that portion was to be 0.1 (W/V)%. This procedure was repeated once every day. The culturing was carried out at 25+-2°C.
*synthetic sewage: glucose, peptone and monopotassium phosphate were dissolved in dechlorination water respectively. Each concentration of them was to be 5(W/V)% and the solution was adjusted to pH 7.0 +- 1.0 with sodium hydroxide.
Control
During the cultivation, appearance of the supernatant, precipitabiltiy, formation of flock, pH, dissolved oxygen concentration in the solution and temperature were checked and necessary adjustments were made. microflora in the activated sludge was microscopically observed and sludge with no abnormal symptom was used for the test.
Inspection of activity
Activity of the sludge was inspected to use reference substance. And the relation between new and old activated sludge was taken account. - Duration of test (contact time):
- 4 wk
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Reference substance:
- aniline
- Remarks:
- guaranteed reagent, Showa Chemicals Inc.
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0 - 2
- Sampling time:
- 4 wk
- Interpretation of results:
- not readily biodegradable
- Executive summary:
The ready biodegradability of benzyldimethylamine was tested according to "Biodegradation test of chemical substance by mircoorganisms etc." stipulated in the order Prescribing the Items of the test relating to the new chemical substance (1974). (This guideline corresponds to 301C, ready biodegradability: modified MITI Test (I) or 302C, inherent biodegradability: modified MITI Test (II) stipulated in the OECD Guidelines for testing of chemicals (May 12, 1981)).
The biodegradation rate is 0 to 2 % after 4 weeks.
(MITI, 1992)
Referenceopen allclose all
Results:
Time [d] |
Blank value [mg/L]* |
Test item DOC [mg/L] |
DOC elimination |
pH |
0 |
17 |
425 |
-6 |
7.0 |
3 hours |
17 |
409 |
2 |
7.0 |
1 |
17 |
418 |
0 |
7.0 |
4 |
17 |
223 |
48 |
6.7 |
7 |
17 |
23 |
98 |
7.0 |
13 |
17 |
21 |
99 |
7.8 |
* = Blank value was statistically determined (from blank controls with the same inoculum)
Description of key information
Benzyldimethylamine was shown to be not ready biodegradable in different ready biodegradability tests using non-adapted sludge (MITI, 1992). In addition, Benzyldimethylamine was shown to be 100% inherently biodegradable after 13 days and fulfilled the criterion for inherent, ultimative biodegradability (BASF, 1987).
Key value for chemical safety assessment
- Biodegradation in water:
- inherently biodegradable
Additional information
READY BIODEGRADABILITY
Key study:
The ready biodegradability of benzyldimethylamine was tested according to "Biodegradation test of chemical substance by mircoorganisms etc." stipulated in the order prescribing the items of the test relating to the new chemical substance (1974). This guideline corresponds to 301C, ready biodegradability: modified MITI Test (I) or 302C, inherent biodegradability: modified MITI Test (II) stipulated in the OECD Guidelines for testing of chemicals (May 12, 1981). The biodegradation rate (measured as O2 consumption) is 0 to 2 % after 4 weeks. The substance is thus, not regarded ready biodegradable (MITI, 1992).
Supporting studies:
- A 4-wk Modified MITI Test (I) was performed on the basis of the OECD guideline 301C with activated sludge. 1% degradation was observed within 4 weeks on the basis of O2 consumption. Benzyldimethylamine is not readily biodegradable (MITI-Online, 2002)
- A 20-d ready biodegradability test was performed on the basis of the OECD guideline 301D with activated, non-adapted sludge under aerobic conditions. 0% degradation was observed within 20 days on the basis of O2 consumption. Benzyldimethylamine is not readily biodegradable (Bayer AG, 1979).
- A 20-d ready biodegradability test was performed on the basis of the OECD guideline 301D with activated, adapted sludge under aerobic conditions. 100% degradation was observed within 20 days on the basis of O2 consumption. Benzyldimethylamine is readily biodegradable with adapted sludge (Bayer AG, 1979).
INHERENT BIODEGRADABILITY
Key study:
The inherent biodegradability of benzyldimethylamine was tested in a study equivalent or similar to a 13-d- Zahn-Wellens test (OECD Guideline 302B). With an initial test substance concentration of 425 mg/L and an activated sludge (industrial, non-adadapted) with an initial cell/biomass concentration of 1 g/L 100% degradability of benzyldimethylamine was determined by DOC-removal.
Benzyldimethylamine was shown to be 100% inherently biodegradable after 13 days and fulfilled the criterion for inherent, ultimative biodegradability (70% degradability within 7 days).
A new inherent biodegradation test is currently on-going (2023), the dossier will be updated as soon as study report has been reviewed and agreed (Q4, 2023).
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.