Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 700-792-4 | CAS number: -
- 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
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 23 July 2012 - 24 July 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to internationally accepted guidelines and to GLP.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2012
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Reaction mass of 1,2,2,6,6-pentamethylpiperidin-4-yl hexadecanoate and 1,2,2,6,6-pentamethylpiperidin-4-yl octadecanoate
- EC Number:
- 700-792-4
- Molecular formula:
- C26H51NO2, C28H55NO2
- IUPAC Name:
- Reaction mass of 1,2,2,6,6-pentamethylpiperidin-4-yl hexadecanoate and 1,2,2,6,6-pentamethylpiperidin-4-yl octadecanoate
- Details on test material:
- - Name of test material (as cited in study report): T-1640L
- Physical state: White to pale yellow solid
- Analytical purity: 98.74%
- Purity test date: 20 May 2011
- Lot/batch No.: 10121
- Expiration date of the lot/batch: 12 April 2013
- Storage condition of test material: Refrigerated in the dark
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Weigh compound directly to required test bottles
-- Evidence of undissolved material (e.g. precipitate, surface film, etc):
Test organisms
- Test organisms (species):
- activated sludge, domestic
- Details on inoculum:
- - Laboratory culture: sample was maintained under aerobic conditions until required
- Method of cultivation:
- Preparation of inoculum for exposure:
On the day of collection, an aliquot (10 mL) of the activated sludge was filtered through a dried and preweighed Whatman GF/C filter paper, which was then dried again at approximately 105°C for at least one hour, allowed to cool in a desiccator and reweighed.
The mixed liquor suspended solids (MLSS) content of the activated sludge was then calculated. Synthetic sewage (50 mL/L) was added to the stock of activated sludge and this was aerated overnight.
- Pretreatment:
On the day of the test, the MLSS content of the sludge was determined (in triplicate) and adjusted to 4 g/L by the addition of tap water. The pH and temperature of the sludge were also measured. Aliquots (200 mL) were then added to each mixture to give a final MLSS
concentration of 1.6 g/L.
- Initial biomass concentration:
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
Test conditions
- Test temperature:
- 20 ± 2°C
- pH:
- 7.0
- Dissolved oxygen:
- 6.38 - 8.00 (initial mgO2/L)
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Bottle
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: glass, 500 mL
- Aeration: aerator connected to lab supply of oil-free compressed air (one L/min.)
- Renewal rate of test solution (frequency/flow rate):
- No. of organisms per vessel:
- No. of vessels per concentration (replicates): 5
- No. of vessels per control (replicates): 5
- No. of vessels per vehicle control (replicates):
- Biomass loading rate:
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: reverse osmosis water
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod:
- Light intensity:
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
Oxygen consumption measured at one minute intervals for 15 minutes post-exposure
TEST CONCENTRATIONS
- Spacing factor for test concentrations: x10
- Range finding study: no
- Test concentrations: 10, 100, 1000 mg/L - Reference substance (positive control):
- yes
- Remarks:
- 3,5-Dichlorophenol
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: Could not be calculated so must be > highest conc. tested
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Relevant effect levels: The three-hour EC50 for 3,5-DCP was 11.9 mg/L
- Other: Validity criteria relating to controls was satisfied (specific respiration rate ≥20 mgO2/gh) and CV≤30%
Any other information on results incl. tables
Measurements of the pH of the aqueous stock solutions of the synthetic sewage, the test and reference substances and of the sample of activated sludge (4 g/L) before the start of the test are given below.
Preparation pH
Synthetic Sewage 7.47
3,5 -DCP stock 7.24
Activated sludge 7.05
Sludge respiration rates were progressively reduced in the presence of increasing concentrations of 3,5-DCP. The three-hour 50% effect concentration (EC50) for 3,5-DCP was calculated to be 11.9 mg/L (95% confidence). The mean specific respiration rate of the control cultures established was 23.4 mgO2/gh with a coefficient of variation of 20.3%.
Applicant's summary and conclusion
- Conclusions:
- T-1640L did not significantly inhibit the respiration rates of the samples of activated sludge.
Consequently the EC50 for inhibition could not be calculated but must be >1000 mg/L, the
highest concentration tested in this study. The no observed effect concentration (NOEC) for T-1640L was 1000 mg/L.
The three-hour EC50 for 3,5-DCP (11.9 mg/L) fulfilled the validity criterion relating to sensitivity to inhibition (acceptable EC50 range 2 to 25 mg/L). The validity criterion relating to the respiration rates in the control (specific respiration rate ≥20 mgO2/gh and a coefficient
of variation of ≤30%) was also satisfied.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.