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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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge nitrification inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1977
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable, well-documented publication, which meets basic scientific principles
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Screening test on inhibition of ammonia-/nitrite-oxidation
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- other: Nitrosomonas sp. and Nitrobacter sp. (mixed nitrifying culture)
- Details on inoculum:
- - Laboratory culture: autrophic nitrifying bacteria maintained in 12-L fiber-wall reactor with continuous feeding (solids retention time: 24 d); aeration (12.5 L/min) through submersed diffusers; buffered at pH 8 (Na carbonate/Na bicarbonate)
- Preparation of inoculum for exposure: mixed liquor removed from stock culture, centrifuged (18400 x g, 15 min), supernatant discarded, cells dispersed in feed solution; 90-mL aliquots added to each test flask
- Pretreatment: no
- Initial biomass concentration: no data - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 2 h
- pH:
- 8.1 (buffered with Na carbonate/bicarbonate)
- Nominal and measured concentrations:
- nominal: 0 (control) and 100 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: reaction flasks, fill volume: 100 mL
- No. of vessels per concentration (replicates): 2
- No. of vessels per control (replicates): 2
- agitation: shaker with 80 rpm
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: de-ionized water
- Nitrogen concentration: 200 mg/L NH3-N
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH: yes (pH 8.1)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- determination of NO3-N and NO2-N after 25 min, 1 h and 2 h - Duration:
- 2 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of nitrification rate
- Validity criteria fulfilled:
- yes
- Conclusions:
- Tributylamine does not inhibit nitirifcation (NOEC: 100 mg/L).
- Executive summary:
The inhibiting effect of tributylamine was tested on a mixed autotrophic culture of nitrifying bacteria (Nitrosomonas sp. and Nitrobacter sp.; laboratory culture). The test was a limit test with a control and a test concentration of 100 mg/L tributylamine, both run in duplicate. The pH was buffered at pH 8.1. The NH3-N concentration was 200 mg/L. The nitrite and nitrate concentration were determined after 25 min, 1 h and 2 h. Tributylamine did not inhibit the nitrification. The NOEC was determined to be 100 mg/L.
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Basic data given: comparable to guideline study
- Justification for type of information:
- For details on endpoint specific justification please see read-across report in section 13 or find a link in cross-reference “assessment report”.
- Reason / purpose for cross-reference:
- assessment report
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Respiration inhibition test with activated sludge using glucose as substrate
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- activated sludge, domestic
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): municipal sewage treatment plant treating domestic sewage from Tokyo
- Concentration of sludge: 30 mg/L - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 7 d
- Test temperature:
- 25 °C
- Duration:
- 7 d
- Dose descriptor:
- other: EC5
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The 7-d EC5 is 100 mg/L in the respiration inhibition test.
- Executive summary:
The effect of tributylamine on the respiration rate of microorganisms was tested in a non-guideline study. The HCl salt of tributylamine was used as test item (100 mg/L). The test method was a respiration inhibition test with domestic activated sludge (30 mg/L) using glucose (40 mg/L) as substrate. The observation period was 7 d. The oxygen consumption was monitored continuously. Tributylammonium cloride inhibited the respiration slightly. The relative oxygen consumption was 0.95 compared to a control without the test item. Therefore the 7-d EC5 is 100 mg/L.
Referenceopen allclose all
Relative oxygen consumption after 7 d:
control (activated sludge and glucose): 1.0
tributylammonium chloride (act. sludge + glucose + test item): 0.95
Description of key information
The 7-d EC5 for respiration inhibition of activated sludge is 100 mg/L (tributylammonium chloride; non-guideline study; Yoshimura et al., 1980).
The 2-h NOEC for inhibtion of nitrification is 100 mg/L (non-guideline study; Hockenbury & Grady, 1977).
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 100 mg/L
Additional information
There is one relevant study available regarding the assessment of effects on the functioning of wastewater treatment processes (Yoshimura et al., 1980). There is another relevant study available dealing with the effect of tributylamine on the nitrification process (Hockenbury & Grady, 1977).
Endpoint |
Organism group |
Test system |
Value [mg/L] |
Reliability |
Remarks |
Source |
7-d EC5 |
Microorganisms |
Activated sludge, domestic |
100 |
2 key study |
HCl salt of tributylamine used as test item |
Yoshimura et al. (1980) |
2-h NOEC |
Microorganisms |
Nitrosomonas sp. and Nitrobacter sp. |
100 |
2 key study |
Hockenbury & Grady (1977) |
The effect of tributylamine on the respiration rate of microorganisms was tested in a non-guideline study (Yoshimura et al., 1980). The HCl salt of tributylamine was used as test item (100 mg/L). The test method was a respiration inhibition test with domestic activated sludge (30 mg/L) using glucose (40 mg/L) as substrate. The observation period was 7 d. The oxygen consumption was monitored continuously. Tributylammonium cloride inhibited the respiration slightly. The relative oxygen consumption was 0.95 compared to a control without the test item. Therefore the 7-d EC5 is 100 mg/L.
The study from Hockenbury and Grady (1977) showed that tributylamine did not disturb the nitrifying abilities of a mixed culture of Nitrosomonas sp. and Nitrobacter sp. The 2-h NOEC was determined to be 100 mg/L.
Based on these results, it was concluded that disturbances of wastewater treatment processes are not to be expected when tributylamine is released in appropriate amounts.
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