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EC number: 939-685-4 | CAS number: 1474044-71-7
- 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:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
- Version / remarks:
- 31 May 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- - Name of test material: 1-Propanaminium, 2-hydroxy-N-(2-hydroxypropyl)-N,N-dimethyl-, esters with fatty acids, C18 unsatd., Me-sulfates (salts)
- Physical state: liquid
- Analytical purity: 100% - Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
The relevant amounts of test substance and reference substance were directly weighed into beakers and 170 mL demineralised water were added. For the final
preparations, 9.6 mL synthetic sewage and 120 mL inoculum suspension were added to each mixture. - Test organisms (species):
- activated sludge, domestic
- Details on inoculum:
- - Laboratory culture: a fresh sample from the aeration basin of a municipal sewage treatment plant (Moers, Germany) was collected one day before carrying out the test
- Preparation of inoculum for exposure: filtration by means of a water jet pump through a filter paper, sludge was washed twice with mineral medium; 50 mL synthetic sewage were added and the whole mixture was stirred and aerated (0.5 - 1.0 litre per minute) overnight at 20 ± 2°C
- Initial biomass concentration: 4 g/L - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Test temperature:
- 20±2°C
- pH:
- 7.39
- Nominal and measured concentrations:
- nominal 0, 10, 32, 100, 320 and 1000 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 1 L beaker
- Aeration: compressed synthetic air (0.5 -1.0 litre per minute) under permanent stirring with a magnetic stirrer
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 2
OTHER TEST CONDITIONS
- Adjustment of pH: not necessary; with a measured pH value of 7.39, it was within the required range of 6.0 to 8.0
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- pH at start and end of incubation
- oxygen consumption at end of incubation - Reference substance (positive control):
- yes
- Remarks:
- 3,5- dichlorophenol: 3.2, 10 and 32 mg/L
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 3 h
- Dose descriptor:
- EC10
- Effect conc.:
- 323.4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Validity criteria fulfilled:
- yes
- Conclusions:
- The 3 h EC50 of MDIPA Esterquat C18 unsatd. towards activated sludge microorganisms was >1000 mg/L, the 3 h EC10 was 323.4 mg/L.
- Executive summary:
In a 3 h respiration inhibition study, activated sludge from the aeration basin of a municipal sewage treatment plant fed with synthetic sewage was exposed to MDIPA Esterquat C18 unsatd. at nominal concentrations of 0 (control), 10, 32, 100, 320 and 1000 mg/L in accordance with EU method C.11 (31 May 2008). 3,5- dichlorophenol at concentrations of 3.2, 10 and 32 mg/L was used as reference substance.
The 3 h EC50 of MDIPA Esterquat C18 unsatd. was determined to be >1000 mg/L, the 3 h EC10 was 323.4 mg/L.
Reference
The respiration rates of the controls showed a coefficient of variation of 8.3%. The EC50 for the reference substance was calculated to be 10.0 mg/L, thus fulfilling the validation criteria mentioned in the test guidelines.
Description of key information
EC10 =323.4 mg/L, EC50 > 1000 mg/L (EU method C.11 (respiration inhibition test) with activated sludge; GLP)
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 000 mg/L
- EC10 or NOEC for microorganisms:
- 323.4 mg/L
Additional information
In a 3 h respiration inhibition study, activated sludge from the aeration basin of a municipal sewage treatment plant fed with synthetic sewage was exposed to MDIPA Esterquat C18 unsatd. at nominal concentrations of 0 (control), 10, 32, 100, 320 and 1000 mg/L in accordance with EU method C.11 (31 May 2008). 3,5- dichlorophenol at concentrations of 3.2, 10 and 32 mg/L was used as reference substance.
The 3 h EC50 of MDIPA Esterquat C18 unsatd. was determined to be >1000 mg/L, the 3 h EC10 was 323.4 mg/L.
Similar results were obtained with the closely related read-across substance MDEA-EsterquatC16-18 and C18 unsatd.:
In a 3-hour toxicity study, activated sludge fed with synthetic sewage was exposed to MDEA-EsterquatC16-18 and C18 unsatd.at nominal concentrations of 0 and 47.4 mg a.i./L in accordance with OECD 209 (Activated Sludge Respiration Inhibition). The NOEC based on respiration rate was >47.4 mg a.i./L.
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