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EC number: 213-156-1 | CAS number: 927-62-8
- 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 respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- DIN 38412-8 (Pseudomonas Zellvermehrungshemmtest)
- GLP compliance:
- no
- Remarks:
- non-animal study which was already available, pre-REACH
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution of 1250 mg/L was prepared in deionised water. - Test organisms (species):
- Pseudomonas putida
- Details on inoculum:
- - Laboratory culture: The used test strain of Pseudomonas putida DSM 50026 is purchased on regular times from DSM (Deutsche Sammlung von Mikroorganismen in Göttingen (German collection of microorganisms in Göttingen)) and cultured further on slant agar in the Laboratory of Ecotoxicology of BASF AG in Ludwigshafen, Germany.
- Method of cultivation: The stock cultures are kept in slant agar culturing tubes of 50 mL. The inoculation density is one smear from an inoculating loop. The culture is transferred weekly.
- Pretreatment: The pre-cultures are kept in Erlenmeyer flasks with a nominal volume of 250 mL. The vessels are filled with 100 mL pre-culture medium and inoculated with a smear from an inoculation loop with 10 TE/F bacteria suspension at 21 ± 1 °C and incubated for 7h while shaking. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 16 h
- Test temperature:
- 20 ± 1 °C
- pH:
- Uninoculated t = 0 h: 6.92 - 10.05
Uninoculated t = 17 h: 6.92 - 8.32
Inoculated t =17 h: 6.71 - 7.78 - Nominal and measured concentrations:
- Nominal concentrations: control, 3.9, 7.8, 15.6, 31.3, 62.5, 125, 250, 500, 1000 mg/L
HCl-neutralised stock solution was used to test the nominal concentrations 125 and 1000 mg/L in parallel (neutralised to pH 6.92 - 7.78). - Details on test conditions:
- TEST SYSTEM
- Test vessel: Penicillin vessels with flattened bottom, nominal volume 50 mL and air permeable silicon-foam caps
- Fill volume: 10 mL
- No. of vessels per concentration (replicates): 4 inoculated replicates
- No. of vessels per control (replicates): 1 uninoculated replicate
- Biomass loading rate: 5 TE/F (optical density)
TEST MEDIUM / WATER PARAMETERS
- Test medium: AK-Medium according to DIN 38412, Part 8
OTHER TEST CONDITIONS
- Photoperiod: continuous light
- Adjustment of pH: no
- Light intensity: 120 µEinstein/m²s
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
Optical density: With a Zeiss PM 2 DL, 1 cm cuvette at a wavelength of 436 nm. Measurements are made at t = 16 h in all inoculated replicates, whereby the uninoculated replicate of each concentration is used as background measurement.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Test concentrations: control, 3.9, 7.8, 15.6, 31.3, 62.5, 125, 250, 500, 1000 mg/L
- Application method: liquid-dosing from the stock solution - Duration:
- 16 h
- Dose descriptor:
- EC10
- Effect conc.:
- 292 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Key result
- Duration:
- 16 h
- Dose descriptor:
- EC50
- Effect conc.:
- 480 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Duration:
- 16 h
- Dose descriptor:
- other: EC90
- Effect conc.:
- 930 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Conclusions:
- The 16-hour EC50, based on biomass, was 480 mg/L with the free base.
- Executive summary:
The inhibitory effect of N,N-Dimethylbutylamine on cell proliferation of Pseudomonas putida was determined according to an acknowledged national test method, DIN 38412 Part 8. The EC50 (16 h) based on biomass was 480 mg/L with the free base (BASF AG, 1991).
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- ISO 8192 (Water quality - Test for inhibition of oxygen consumption by activated sludge for carbonaceous and ammonium oxidation)
- Version / remarks:
- (draft, 1984)
- GLP compliance:
- no
- Remarks:
- non-animal study which was already available, pre-REACH
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Stock solution: 2000 mg test substance in 1000 mL; DOC = 1256 mg/L - Test organisms (species):
- activated sludge, industrial
- Details on inoculum:
- - Laboratory culture: activated sludge from a wastewater plant treating industrial wastewater (BASF AG)
- Concentration of dry substance: 1 g/L - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 30 min
- Test temperature:
- ambient (20 ± 2 °C)
- Nominal and measured concentrations:
- nominal: 400 and 800 mg/L
- Details on test conditions:
- A mean reference value of 41 mg/L*h was used instead of running a blank.
- Reference substance (positive control):
- no
- Duration:
- 30 min
- Dose descriptor:
- other: EC20
- Effect conc.:
- > 800 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Conclusions:
- Respiration of microorganisms contained in activated industrial sludge was not affected at concentrations up to 800 mg/L.
- Executive summary:
The inhibitory effect of N,N-Dimethylbutylamine on cell respiration of activated industrial sludge was determined according to an acknowledged national test method, ISO 8192 (Draft, 1984). At concentrations of 400 and 800 mg/L the respiration rate (45 and 43 mg O2/L*h) was slightly increased compared to the blank (mean: 41 mg O2/L*h). Thus, respiration of microorganisms contained in activated industrial sludge was not affected at concentrations up to 800 mg/L (BASF AG, 1986).
Referenceopen allclose all
Remark
The neutralised sample (1000 mg/L, pH 6.94) caused no toxic effect compared to the not neutralised sample (1000 mg/L, pH 10.05).
Optical densities of the bacteria cultures at t = 16 h
Concentration (mg/L) |
E 436 nm Inoculated |
E 436 nm Uninoculated |
Difference |
(% of controls) |
Control |
0.908 |
--- |
|
|
3.9 |
0.949 |
0.001 |
0.948 |
104.46 |
7.8 |
0.963 |
-0.001 |
0.964 |
106.14 |
15.6 |
0.949 |
0.000 |
0.949 |
104.57 |
31.3 |
0.962 |
-0.001 |
0.963 |
106.11 |
62.5 |
0.998 |
-0.002 |
1.000 |
110.16 |
125 |
0.996 |
0.003 |
0.993 |
109.39 |
250 |
0.901 |
0.003 |
0.898 |
98.93 |
500 |
0.412 |
-0.003 |
0.415 |
45.69 |
1000 |
0.036 |
-0.002 |
0.038 |
4.19 |
Optical densities of the bacteria cultures exposed to test solutions prepared with a neutralized stock solution at t = 16 h
Concentration (mg/L) |
E 436 nm Inoculated |
E 436 nm Uninoculated |
Difference |
(% of controls) |
Control |
0.913 |
--- |
|
|
125 neutr. |
0.957 |
0.000 |
0.957 |
104.82 |
1000 neutr. |
0.937 |
0.001 |
0.936 |
102.49 |
pH values
Concentration (mg/L) |
Uninoculated 0 h |
Uninoculated 17 h |
Inoculated 17 h |
Control |
6.92 |
6.94 |
7.42 |
100 |
10.05 |
8.32 |
6.94 |
500 |
9.69 |
7.99 |
6.71 |
250 |
9.41 |
7.74 |
7.34 |
125 |
8.25 |
7.46 |
7.54 |
62.5 |
7.36 |
7.20 |
7.50 |
31.3 |
7.13 |
7.08 |
7.49 |
15.6 |
7.01 |
7.01 |
7.48 |
7.8 |
6.96 |
6.97 |
7.66 |
3.9 |
6.95 |
6.95 |
7.77 |
|
|
|
|
1000 neutr. |
6.94 |
6.92 |
7.37 |
125 neutr. |
6.92 |
6.92 |
7.78 |
Concentration (mg/L) |
Conc DOC-Test substance (mg/L) |
Respiration rate (mg O2/L*h) |
Change of respiration rate (%) |
400 |
251 |
45 |
11 |
800 |
502 |
43 |
5 |
- blank (mean value): 41 mg O2/L*h
- Increase in respiration rate at 400 and 800 mg/L
- The inhibition of the degradation activity of activated sludge is not anticipated when introduced in appropriate low concentrations
Description of key information
DIN 38412-8 (Pseudomonas Zellvermehrungshemmtest)
The EC50 (16 hrs), based on biomass, was 480 mg/L with the free base (BASF AG, 1991).
ISO 8192 (Water quality - Test for inhibition of oxygen consumption by activated sludge for carbonaceous and ammonium oxidation)
Respiration of microorganisms contained in activated industrial sludge was not affected at concentrations up to 800 mg/L (BASF AG, 1986).
Key value for chemical safety assessment
- EC50 for microorganisms:
- 480 mg/L
Additional information
DIN 38412-8 (Pseudomonas Zellvermehrungshemmtest)
In the key study, the inhibitory effect of N,N-Dimethylbutylamine on cell proliferation of Pseudomonas putida was determined according to an acknowledged national test method, DIN 38412 Part 8. The EC50 (16 hrs), based on biomass, was 480 mg/L with the free base (BASF AG, 1991).
ISO 8192 (Water quality - Test for inhibition of oxygen consumption by activated sludge for carbonaceous and ammonium oxidation)
In the supporting study, the inhibitory effect of N,N-Dimethylbutylamine on cell respiration of activated industrial sludge was determined according to an acknowledged national test method, ISO 8192 (Draft, 1984). At concentrations of 400 and 800 mg/L the respiration rate (45 and 43 mg O2/L*h) was slightly increased compared to the blank (mean: 41 mg O2/L*h). Thus, respiration of microorganisms contained in activated industrial sludge was not affected at concentrations up to 800 mg/L (BASF AG, 1986).
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