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EC number: 203-412-0 | CAS number: 106-58-1
- 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:
- toxicity to microorganisms, other
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1996-02-12 - 1996-02-13
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- DIN 38412-8 (Pseudomonas Zellvermehrungshemmtest)
- GLP compliance:
- yes
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 1,4-Dimethylpiperazin
- Analytical purity: > 99 %
- Lot/batch No.: Abl.-Nr. 32-1659 - Analytical monitoring:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The test solutions were prepared by diluting a stock solution (12500 mg/l) with demineralised 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:
- 21 ± 1°C
- pH:
- Uninoculated t = 0h: 6.9 - 10.1
Uninoculated t = 16h: 7.1 - 9.5
Inoculated t =16h: 6.8 - 9.6 - Nominal and measured concentrations:
- Nominal concentrations: control, 4.88, 9.77, 19.53, 39.06, 78.13, 156.25, 312.5, 625, 1250, 2500, 5000, 10000 mg/L
HCl-neutralised stock solution was used to test the nominal concentrations 156.25, 1250 and 10000 mg/L in parallel (neutralised to pH 6.8 - 7.2). - Details on test conditions:
- TEST SYSTEM
- Test vessel: tubes of glass with flat bottom, nominal volume 50 mL, plugged with gas permeable siliconesponge caps
- Fill volume: 10 mL
- No. of vessels per concentration (replicates): 4 inoculated replicates, 1 uninoculated replicate
- No. of vessels per control (replicates): 4 inoculated replicates, 1 uninoculated replicate
- Biomass loading rate: 5 FNU (optical density)
TEST MEDIUM / WATER PARAMETERS
- Test medium: AK-Medium according to DIN 38412, Part 8
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
Optical density: at a wavelength of 436 nm. Measurements are made at t=16h in all inoculated replicates, whereby the uninoculated replicate of each concentration is used as background measurement. - Duration:
- 16 h
- Dose descriptor:
- EC10
- Effect conc.:
- 651 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth inhibition
- Remarks on result:
- other: not neutralised
- Key result
- Duration:
- 16 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1 380 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth inhibition
- Remarks on result:
- other: not neutralised
- Duration:
- 16 h
- Dose descriptor:
- other: EC90
- Effect conc.:
- 2 240 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth inhibition
- Remarks on result:
- other: not neutralised
- Duration:
- 16 h
- Dose descriptor:
- EC10
- Effect conc.:
- > 1 250 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth inhibition
- Remarks on result:
- other: neutralised
- Details on results:
- The inhibition of bacterial cell multiplication at test substance concentrations of >= 1250 mg/L is most likely due to pH effects. In the corresponding neutralised samples no or lower inhibitory effects were observed.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The inhibitory effect of the test substance on the celI multiplication of the bacterium Pseudomonas putida was investigated in a 16-hour static test according to DIN 38412 part 8 (March 1991). The test substance was tested in the concentration range between 4.88 and 10,000 mg/l (nominal).
The reference substance result was within required range, and control variability was valid. The 16-hr EC50 of dimethylpiperazine to activated sludge was found to be > 1000 mg/L. The 16-hr EC10 was 651 mg/L.
Reference
The neutralised samples caused no toxic effect up to a concentration of 1250 mg/L.
Optical densities of the bacteria cultures at t =16h (mean of 4 replicates)
Concentration (mg/L) |
Optical density (corrected) |
(% of control) |
Control |
0.349 |
100 |
4.88 |
0.353 |
101.1 |
9.77 |
0.373 |
107.0 |
19.53 |
0.367 |
105.1 |
39.06 |
0.356 |
102.0 |
78.13 |
0.360 |
103.1 |
156.25 |
0.367 |
105.1 |
312.5 |
0.354 |
101.4 |
625 |
0.321 |
92.0 |
1250 |
0.203 |
58.2 |
2500 |
0.003 |
0.9 |
5000 |
0.003 |
0.9 |
10000 |
0.003 |
0.9 |
156.25 * |
0.371 |
106.3 |
1250 * |
0.360 |
103.2 |
1000* |
0.079 |
22.7 |
* neutralised
pH values
Nominal conc. (mg/l) |
pH values |
|||
Rep. 1 |
Rep. 2 |
Rep. 3 |
Rep. 4 |
|
control |
7.2 |
7.2 |
7.1 |
7.2 |
4.88 |
7.1 |
7.2 |
7.3 |
7.3 |
9.77 |
7.1 |
7.2 |
7.3 |
7.3 |
19.53 |
7.2 |
7.3 |
7.3 |
7.2 |
39.06 |
7.2 |
7.3 |
7.3 |
7.3 |
78.13 |
7.2 |
7.2 |
7.3 |
7.4 |
156.25 |
7.3 |
7.3 |
7.2 |
7.3 |
312.5 |
7.3 |
7.3 |
7.3 |
7.4 |
625 |
7.5 |
7.5 |
7.5 |
7.5 |
1250 |
7.8 |
7.7 |
7.8 |
7.7 |
2500 |
9.0 |
9.1 |
9.1 |
9.1 |
5000 |
9.3 |
9.3 |
9.3 |
9.3 |
10000 |
9.5 |
9.6 |
9.6 |
9.6 |
156.25 * |
7.2 |
7.3 |
7.2 |
7.2 |
1250 * |
7.1 |
7.1 |
7.0 |
7.1 |
1000* |
6.8 |
6.8 |
6.8 |
6.8 |
Description of key information
The 16-h EC50 of the test substance for the organism Pseudomonas putida was found to be > 1000 mg/L. The EC10 (for the not neutralised sample) was 651 mg/L. The EC10 for the neutralised sample was > 1250 mg/L. The worst-case EC10 of 651 mg/L was used for derivation of the PNEC. An assessment factor of 1 was used as specified in the ECHA guidance (2008) for growth inhibition tests with Pseudomonas putida EC10 values.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 380 mg/L
- EC10 or NOEC for microorganisms:
- 651 mg/L
Additional information
A 16-h Pseudomonas putida growth inhibition study was conducted according to DIN 38412 part 8. Concentrations tested were: a control treatment and concentrations between 4.88 and 10,000 mg/L. Above a concentration of about 2000 mg/L the pH-values of the test samples rise over pH 9,9 at the beginning of the test. In these samples a strong inhibition of the bacterial cell multiplication occurs (at 10000 mg/L = 99,1% inhibition, at 1250 mg/L = 41.8% inhibition). The testing of the neutralized samples showed an evidently lower inhibitory effect (at 10000 mg/L neutralized sample = 77.3% inhibition and at 1250 mg/L = 3.2% stimulation). The reference substance result was within the required range, and control variability was within the validity requirements. The 16-h EC50 and 16-h EC10 of 1,4-dimethylpiperazine was found to be 1380 mg/L and 651 mg/L for the not neutralised sample. As no other study was available, the results of the Pseudomonas putida growth inhibition study were used for PNEC derivation.
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