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EC number: 203-232-2 | CAS number: 104-74-5
- 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
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Data is from peer reviewed journal
- Justification for type of information:
- Data is from peer reviewed journal
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- The aim of this study was to investigate the antibacterial effect of test material against the model P-( phosphate) accumulating bacterium Acinetobacter junii.
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Details on sampling:
- not specified
- Vehicle:
- not specified
- Details on test solutions:
- 1 mL of mixed suspension was distributed in series of bottles containing different concentration of per 100 mL of simulative wastewater. The concentrations were 10-4, 10-5, 10-6, 10-7 mol L-1 for each surfactant.
- Test organisms (species):
- other: Acinetobacter junii DSM1532
- Details on inoculum:
- - Laboratory culture: Deutsch Sammlung von Mikroorganismen und Zellkulturen, Braunschweig, Germany
- Method of cultivation: nutrient agar
- Preparation of inoculum for exposure: The bacteria were pregrown on nutrient agar for 20 h at 30±0.1°C to obtain log phase cell culture. The biomass was then resuspended in 10 mL of 0.3% NaCl.
- Pretreatment: not specified
- Initial biomass concentration: not specified - Test type:
- semi-static
- Water media type:
- other: Simulative wastewater
- Limit test:
- no
- Total exposure duration:
- 24 h
- Hardness:
- not specified
- Test temperature:
- 30±0.1°C
- pH:
- 7.00 ± 0.02
- Dissolved oxygen:
- not specified
- Salinity:
- not specified
- Conductivity:
- not specified
- Nominal and measured concentrations:
- 10-4, 10-5, 10-6, 10-7 mol L-1
- Details on test conditions:
- Simulative wastewater:
The composition of the simulative wastewater (prepared in 1L of distilled water) was as follows:
Na-propionate, 300 mg;
peptone, 100 mg;
MgSO4, 10 mg;
CaCl2, 6 mg;
KCl, 30 mg;
yeast extract, 20 mg;
KH2PO4, 88 mg.
The pH of the synthetic wastewater was adjusted to 7.00 ± 0.02 with 1 M HCl or 1 M NaOH before autoclaving (15 min at 121°C).
The average characteristics of simulative wastewater were: chemical oxygen demand (KPK), 680 mg/L; biological oxygen demand in 5 days (BOD5), 310 mg O2/l; total organic carbon (TOC), 189 mg/l; P, 20 mg/l
Control: The control contained no test chemical.
Other: The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. - Reference substance (positive control):
- yes
- Remarks:
- The broth bottle syringe method of YTT (Yeast toxicity test) was used to compare the toxicity obtained against A. junii with the standardized toxicity test. Yeast used was S. cerevisiae.
- Key result
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0 mol/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Details on results:
- The inhibition of the P-uptake rates was determined to be 7.3± 2.6 x 10-5 mol L-1.
- Results with reference substance (positive control):
- not specified
- Reported statistics and error estimates:
- not specified
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The estimated EC50 values of the test material for growth inhibition of phosphate (P)-accumulating bacteriumAcinetobacter junii was 1.4±0.5 x 10-6 mol/ L (0.3974 mg/L).
- Executive summary:
The antibacterial effect of cationic surfactant against the pure culture of phosphate (P)-accumulating bacteriumAcinetobacter junii was investigated. The bacteria were pregrown on nutrient agar for 20 h at 30±0.1°C to obtain log phase cell culture. The biomass was then resuspended in 10 mL of 0.3% NaCl and 1 mL of mixed suspension was distributed in series of bottles containing different concentration of test material per 100 mL of simulative wastewater. The concentrations used were 10e-4, 10e-5, 10e-6, 10e-7 mol/L. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. The broth bottle syringe method of YTT (Yeast toxicity test) was used to compare the toxicity obtained against A. junii with the standardized toxicity test. Yeast used was S. cerevisiae. The control contained no test chemical. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. The EC50 values of the test material (D for growth inhibition of phosphate (P)-accumulating bacterium Acinetobacter junii was 1.4±0.5 x 10-6 mol/ L (0.3974 mg/L). Thus based on the above data, it can be considered that the substance test material is toxic to microorganisms.
Reference
Description of key information
The antibacterial effect of cationic surfactant against the pure culture of phosphate (P)-accumulating bacteriumAcinetobacter juniiwas investigated. The bacteria were pregrown on nutrient agar for 20 h at 30±0.1°C to obtain log phase cell culture. The biomass was then resuspended in 10 mL of 0.3% NaCl and 1 mL of mixed suspension was distributed in series of bottles containing different concentration of test material per 100 mL of simulative wastewater. The concentrations used were 10e-4, 10e-5, 10e-6, 10e-7 mol/L. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. The broth bottle syringe method of YTT (Yeast toxicity test) was used to compare the toxicity obtained againstA. juniiwith the standardized toxicity test. Yeast used wasS. cerevisiae.The control contained no test chemical. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm.The EC50 values of the test material (D for growth inhibition of phosphate (P)-accumulating bacteriumAcinetobacter juniiwas 1.4±0.5 x 10-6 mol/ L (0.3974 mg/L). Thus based on the above data, it can be considered that the substance test material is toxic to microorganisms.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 0.397 mg/L
Additional information
Experimental study of the test chemical and supporting study for its read across chemical were reviewed for toxicity to microorganisms end point which are summarized as below:
The antibacterial effect of cationic surfactant against the pure culture of phosphate (P)-accumulating bacterium Acinetobacter junii was investigated. The bacteria were pregrown on nutrient agar for 20 h at 30±0.1°C to obtain log phase cell culture. The biomass was then resuspended in 10 mL of 0.3% NaCl and 1 mL of mixed suspension was distributed in series of bottles containing different concentration of test material per 100 mL of simulative wastewater. The concentrations used were 10e-4, 10e-5, 10e-6, 10e-7 mol/L. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. The broth bottle syringe method of YTT (Yeast toxicity test) was used to compare the toxicity obtained against A. junii with the standardized toxicity test. Yeast used was S. cerevisiae. The control contained no test chemical. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. The EC50 values of the test material (D for growth inhibition of phosphate (P)-accumulating bacterium Acinetobacter junii was 1.4±0.5 x 10-6 mol/ L (0.3974 mg/L). Thus based on the above data, it can be considered that the substance test material is toxic to microorganisms.
The above data was further supported by data from peer reviewed journal for read across substance, the antibacterial effect of cationic surfactant against the pure culture of phosphate (P)-accumulating bacterium Acinetobacter juniiwas investigated. The bacteria were pregrown on nutrient agar for 20 h at 30±0.1°C to obtain log phase cell culture. The biomass was then resuspended in 10 mL of 0.3% NaCl and 1 mL of mixed suspension was distributed in series of bottles containing different concentration of Test material per 100 mL of simulative wastewater. The concentrations used were 10-4, 10-5, 10-6, 10-7mol L-1. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. The broth bottle syringe method of YTT (Yeast toxicity test) was used to compare the toxicity obtained against A. Junii with the standardized toxicity test. Yeast used was S. cerevisiae. The control contained no test chemical. The bottles were sealed with a sterile gum cap and thereafter purged with filtered air during a 24-hour incubation in a temperature-controlled water bath shaker at 30±0.1°C and 70 rpm. The estimated EC50 values of the test material for growth inhibition of phosphate (P)-accumulating bacterium Acinetobacter junii was 4.9±1.3 x 10-7 mol L-1. Thus based on the above data, it can be considered that the test substance is toxic to microorganisms.
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