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Diss Factsheets
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EC number: 202-924-1 | CAS number: 101-20-2
- 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:
- supporting study
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- secondary literature
- Justification for type of information:
- Data is from secondary literature
- Qualifier:
- according to guideline
- Guideline:
- other: Refer below principle
- Principles of method if other than guideline:
- To evaluate the effect of test chemical on the domestic sewage by providing the exposure period of 16 days.
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- not specified
- Test organisms (species):
- other: domestic sewage
- Details on inoculum:
- Sludge source: Ocean County South Treatment Plant Test
- Test type:
- other: Anaerobic Digester Inhibition Test
- Water media type:
- not specified
- Total exposure duration:
- 16 d
- Test temperature:
- 32 degree C
- pH:
- 7.4
- Details on test conditions:
- Total alkalinity: 2,600 mg/l CaCO3
- Reference substance (positive control):
- not specified
- Key result
- Duration:
- 16 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of anaerobic gas production
- Remarks on result:
- other: Other details not known
- Validity criteria fulfilled:
- not specified
- Conclusions:
- After the exposure period of 16 days, effect of test chemical on the domestic sewage were determine. The NOEC was determine to be at 100 mg/l.
- Executive summary:
To evaluate the effect of test chemical on the domestic sewage by providing the exposure period of 16 days. Domestic sewage was obtain ocean County South Treatment Plant Test. Anaerobic Digester Inhibition test was performed. After the exposure period of 16 days, effect of test chemical on the domestic sewage were determine. The NOEC was determine to be at 100 mg/l.
Reference
Description of key information
Toxicity to microorganisms:
The MIC values were determined by the microbroth dilution assay according to the National Committee for Clinical Laboratory Standards methods for antimicrobial susceptibility tests for aerobically growing bacteria (Approved Standard M7-A2, NCCLS, Villanova, PA, 1990).
Approximately 6.5 3 108 cells of strain RN4220 (25) were plated on to brain-heart infusion agar medium (Becton-Dickinson) containing 0.5 mg/ml test material. The plates were incubated at 37 °C with periodic monitoring. After 48 h, resistant clones were picked and their phenotype confirmed by regrowth on the original selective concentration of test material.
Three strains of Staphylococcus aureus namely RN4220 (wild-type) , RN4220/pTri-1 , GR664 (fabIG23S) and three starins of E.coli
W3110 (wild-type) , W3110/pFabI , RJH108 (fabIG93V) . The wild-type FabI proteins from either S. aureus or E. coli were expressed using plasmids pTri-1 or pFabI, respectively, to determine if resistance was conferred by the presence of multiple copies of the fabI genes.
The minimum ihhibition concentration (MIC) was observed in the range of 0.25 to 2 mg/l in case of Staphylococcus aureus and for E.Coli MIC was observed in concentration range of 0.5 - 35 mg/l.
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 100 mg/L
Additional information
Toxicity to microorganisms:
The MIC values were determined by the microbroth dilution assay according to the National Committee for Clinical Laboratory Standards methods for antimicrobial susceptibility tests for aerobically growing bacteria (Approved Standard M7-A2, NCCLS, Villanova, PA, 1990).
Approximately 6.5 3 108 cells of strain RN4220 (25) were plated on to brain-heart infusion agar medium (Becton-Dickinson) containing 0.5 mg/ml test material. The plates were incubated at 37 °C with periodic monitoring. After 48 h, resistant clones were picked and their phenotype confirmed by regrowth on the original selective concentration of test material.
Three strains of Staphylococcus aureus namely RN4220 (wild-type) , RN4220/pTri-1 , GR664 (fabIG23S) and three starins of E.coli
W3110 (wild-type) , W3110/pFabI , RJH108 (fabIG93V) . The wild-type FabI proteins from either S. aureus or E. coli were expressed using plasmids pTri-1 or pFabI, respectively, to determine if resistance was conferred by the presence of multiple copies of the fabI genes.
The minimum ihhibition concentration (MIC) was observed in the range of 0.25 to 2 mg/l in case of Staphylococcus aureus and for E.Coli MIC was observed in concentration range of 0.5 - 35 mg/l.
In another secondary data for test chemical the effect of test chemical on the domestic sewage by providing the exposure period of 16 days. Domestic sewage was obtain ocean County South Treatment Plant Test. Anaerobic Digester Inhibition test was performed. After the exposure period of 16 days, effect of test chemical on the domestic sewage were determine. The NOEC was determine to be at 100 mg/l.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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