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EC number: 203-058-7 | CAS number: 102-82-9
- 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
Endpoint summary
Administrative data
Description of key information
Key values for acute aquatic toxicity
Algae: 72h-ErC50 (Pseudokirchneriella subcapitata; growth rate; geometric mean measured) 10.1 (95% CI: 9.38 -10.9) mg/L;
Daphnia: 48h-EC50 (Daphnia magna, immobilisation; measured) 8 mg/L (95% CI: 6.1-10.8 mg/L);
Fish: 28-days LC50 (Danio rerio, mortality; analytically verified) > 10 mg/L;
Key value for chronic aquatic toxicity
Algae: 72h-EC10 (Pseudokirchneriella subcapitata; growth rate; geometric mean measured) 4.64 (95% CI: 3.97 – 5.53) mg/L;
Toxicity to microorganisms
STP microorganisms: 2h-NOEC (Nitrosomonas sp., Nitrobacter sp., inhibition of nitrification rate) 100 mg/L;
Additional information
Short-term and long-term toxicity
Fish:
According to the key study for acute toxicity to fish, the 28-d LC50 for acute fish toxicity is greater than 10 mg/L (OECD 204; Danio rerio; analyt. verified; Hoechst 1991).
The supporting study delivered a 96-h LC50 of 16.3 mg/L (OECD 203; Oryzias latipes; nominal; NITE, 2002).
There are no valid long-term toxicity results for fish available. Fish are not the most sensitive organisms. Therefore and for reasons of animal welfare, a long-term toxicity study in fish is not provided.
Aquatic invertebrates:
In the reliable key study, the 48-h EC50 for acute effects of tributylamine on aquatic invertebrates was experimentally determined to be 8 mg/L (OECD 202; measured; Daphnia magna; Pedersen, 2003).
There are no valid long-term toxicity results for aquatic invertebrates available. As the chemical safety assessment does not indicate the need for further testing, no long-tern toxicity tests on aquatic invertebrates is provided.
Algae:
A valid OECD 201 (GLP; RL 1) study with Pseudokirchneriella subcapitata over 72 hours was performed (Herrmann, 2018) with analytical verification of test item concentrations.
The following ECx -values with 95% confidence intervals were determined (based on geometric mean measured test item concentrations):
ErC50: 10.1 (9.38 -10.9) mg/L
EyC50: 5.13 (4.14 -7.26) mg/L
ErC10: 4.64 (3.97 – 5.53) mg/L
The NOEC-values for inhibition of growth rate and yield after 72 hours were 1.65 mg/L and 0.154 mg/L, respectively.
Microorganisms:
The results from the nitrification inhibition study were selected as key value for the derivation of the PNEC stp. Tributylamine does not disturb nitrification: 2-h NOEC: 100 mg/L (Nitrosomonas sp., Nitrobacter sp.; nominal; no guideline followed; Hockenbury and Grady, 1977).
The second reliable study (key study) was a respiration inhibition test conducted with activated sludge (predominantly domestic). No guideline was followed. The substrate was glucose. The 7-d EC05 was 100 mg/L (read across from tributylammonium chloride; Yoshimura et al., 1980).
Overview on key and supporting ecotoxicity studies
Endpoint |
Species |
Value [mg/L] |
Reliability |
Remarks |
Source |
Fish |
|||||
28-d LC50 |
Danio rerio |
> 10 |
1 key study |
nominal, analyt. verified |
Hoechst AG (1991) |
96-h LC50 |
Oryzias latipes |
16.3 |
2 supp. study |
nominal |
NITE (2002) |
96-h LC50 |
Leuciscus idus |
> 100 - < 500 |
2 supp. study |
pH-adjusted; nominal |
BASF AG (1987)/ (BASF SE (2011) |
Aquatic invertebrates |
|||||
48-h EC50 |
Daphnia magna |
8 |
2 key study |
analytically verified concentrations; |
Pedersen (2003) |
Aquatic algae |
|||||
72-h ErC10 (95% C.I.) |
Pseudokirchneriella subcapitata |
4.64 (3.97 – 5.53) |
1 key study |
geometric mean measured; growth rate |
Herrmann (2018) |
72-h ErC50 (95% C.I.) |
Pseudokirchneriella subcapitata |
10.1 (9.38 -10.9) |
1 key study |
geometric mean measured; growth rate |
|
72-h EbC10 |
Desmodesmus subspicatus (reported as Scenedesmus subspicatus) |
1.4 |
2 supp. study |
test solutions neutralised; nominal; presumably biomass |
Nusch (1987), cited in Amann et al. (1987/1988) |
72-h EbC50 |
Desmodesmus subspicatus (reported as Scenedesmus subspicatus) |
8.2 |
2 supp. study |
test solutions neutralised; nominal; presumably biomass |
|
Microorganisms |
|||||
7-d EC05 |
Activated sludge, domestic |
100 |
2 key study |
Read-across to HCl salt of tributylamine used as test item; nominal |
Yoshimura et al. (1980) |
2-h NOEC |
Nitrosomonas sp. and Nitrobacter sp. |
100 |
2 key study |
nominal |
Hockenbury & Grady (1977) |
It can be concluded that tributylamine is acutely toxic to aquatic organisms. TBA has been found to be stable in test solutions, based on TOC measurements in screening tests (without organisms) according to OECD 201 (>80% for 96 h) and OECD 202 (>80% for 48 h).
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