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EC number: 605-092-1 | CAS number: 157248-25-4
- 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
- Study period:
- Apr 14 - Dec 09, 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test (Carbon and Ammonium Oxidation))
- Version / remarks:
- July, 2010
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Purity: 99.93%
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- The test substance was insufficiently soluble to permit addition via aqueous solution. Individually weighed quantities of test substance were added directly to the appropriate test vessels.
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- The activated sludge inoculum was collected from the sludge return line at Pool or Burley Menston sewage treatment works (West Yorkshire, UK), which has a predominantly domestic catchment. The point of collection was to ensure that the activated sludge sample was relatively free of exogenous material.
Preparation and Maintenance
The sludge was transported to the test facility in a closed container with an adequate headspace to prevent the sample becoming anoxic. On arrival at the test facility, the sludge was aerated with a compressed air supply delivered through a suitable distribution device.
The suspended solids concentration was determined gravimetrically following homogenisation and adjusted using dechlorinated tap water to 3 g/L (± 0.3 g/L). The sludge was maintained at 20 ± 2°C with aeration. During storage it was maintained at 20 ± 2°C and fed with synthetic sewage concentrate at a rate of 50 mL/L. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Test temperature:
- 20 ± 2°C
- pH:
- 7.08 - 7.14
- Dissolved oxygen:
- saturated
- Nominal and measured concentrations:
- 0, 1, 10, 100 and 1000 mg/L
highest concentration was conducted in triplicate - Details on test conditions:
- TEST SYSTEM
- Test vessel: ca 250 mL glass conical flask
- Type (delete if not applicable): open
- Aeration:compressed air supply
- No. of vessels per concentration (replicates): 2, except highest cooncentration: 3
- No. of vessels per vehicle control (replicates): range finder: 6
- Sludge concentration (weight of dry solids per volume): 3 g/L
- Weight of dry solids per volume of reaction mixture per unit of time:
- Nutrients provided for bacteria: no
- Nitrification inhibitor used (delete if not applicable): N-allylthiourea
- Biomass loading rate:
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: dechlorinated tap water
- Particulate matter:
OTHER TEST CONDITIONS
- Adjustment of pH: yes
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 10
- Justification for using fewer concentrations than requested by guideline: n.a.
- Test concentrations: 1, 10, 100, 1000 mg/L - Reference substance (positive control):
- yes
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of heterotrophic respiration
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of respiration due to nitrification
- Results with reference substance (positive control):
- 3,5-DCP:
Total Respiration: 4.6 mg/L
Nitrification Respiration: 1.1 mg/L - Validity criteria fulfilled:
- yes
- Conclusions:
- There were no statistically significant effects on respiration observed during the test. The EC50 for 4-Ethyl-2',3'-difluor-4''-propyl-1,1':4',1''-terphenyl was greater than 1000 mg/L under the test conditions.
- Executive summary:
Purpose
The aim of this study was to determine the no observable effect concentration (NOEC) and estimate the effect concentration for an x% effect (ECx) for activated sludge exposed to the test substance, where possible.
Study Design
The study was undertaken according to OECD Guideline 209, Activated Sludge, Respiration and Inhibition Test (Carbon and Ammonium Oxidation), adopted July, 2010.
Methods
The activated sludge inoculum for the limit test was collected from the sludge return line at Pool Sewage Treatment Works (West Yorkshire, U.K.), which has a predominantly domestic catchment. The point of collection was to ensure that the activated sludge sample was relatively free of exogenous material.
Results
A range-finder/limit test, employing nominal concentrations of 1, 10, 100 and 1000 mg/L, was undertaken to determine the appropriate concentration levels for a definitive test. The range-finder/limit test showed no inhibition of total, nitrification or heterotrophic respiration. As there were sufficient control replicates at the start and end of each exposure period and the highest concentration (1000 mg/L) was conducted in triplicate, as per the OECD 209 guideline, it was not therefore necessary to carry out any further testing.
Determination of EC50 was not possible and is therefore reported to be greater than 1000 mg/L (the highest concentration tested under these conditions). As there were slight enhancement effects noted (observed as negative inhibition), the endpoint for this is reported as No Observed Adverse Effect Concentration (NOEAC). The NOAEC is therefore reported to be 1000 mg/L.
The validity criteria applied to this study type were met and therefore the data are considered valid.
Conclusion
There were no statistically significant effects on respiration observed during the test. The EC50 was greater than 1000 mg/L under the test conditions.
Reference
Description of key information
OECD 209 study (Reliability 1): NOEC = 1000 mg/L
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 000 mg/L
- EC10 or NOEC for microorganisms:
- 1 000 mg/L
Additional information
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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