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EC number: 911-819-6 | 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
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 08 JAN 2010 to 09 FEB 2010
- 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
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Details on sampling:
- Not applicable
- Vehicle:
- no
- Details on test solutions:
- A 5 g Polyol PX/L stock solution was prepared by adding Polyol PX (4.99986 g) to a 1000 mL volumetric flask and bringing to volume with deionised water. The solution was ultrasonicated for ca 5 min to aid dissolution.
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- A sample of activated sewage sludge was obtained from Haddington Municipal Sewage Works (a local sewage processing plant, which handles predominantly domestic sewage) on 06 April 2010. On arrival at the laboratory, the sludge was aerated. The solid content of the sludge was determined by shaking the bottle of sludge by hand to homogenise thoroughly. Duplicate sub-samples (5mL) of the homogenised sludge were dried in an oven at
approximately 105°C and the suspended solids content determined as 3.1 g/L. Synthetic sewage feed was then added at a rate of 50 mL/L sludge and the sludge left aerating overnight. To concentrate the solid sewage flocculent to the required level, the sludge was allowed to settle before 2 L of the overlying supernant was siphoned off. The solid content of the sludge was then re-determined and found to be 4.2 g/L, which was acceptable for use.
The pH of the sludge was measured as 7.84 upon receipt. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Post exposure observation period:
- Not applicable
- Hardness:
- Not applicable
- Test temperature:
- 18.9 to 19.5°C
- pH:
- The pH of the sludge was measured as 7.84 upon receipt.
- Dissolved oxygen:
- Measured during the study.
- Salinity:
- Not applicable
- Nominal and measured concentrations:
- Nominal exposure concentrations were 10, 31.6, 100, 316 and 1000 mg/L.
- Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Key result
- 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
- 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):
- The 3 h EC50 for 3,5-dichlorophenol to activated sludge was estimated to be 12.14 mg/L with 95 % confidence limits of 10.54 and 13.98 mg/L, under the conditions of this test.
- Reported statistics and error estimates:
- The respiration rate for each vessel was calculated from the recorded oxygen concentrations and expressed as mg O2/L/h for the period between approximately 6.5 and 2.5 mg O2/L. Where respiration was low the calculation was conducted over the full linear range.
The EC50 and associated 95% confidence interval was estimated using the non-parametric Trimmed Spearman-Karber Method (Hamilton et al, 1977), where appropriate. - Validity criteria fulfilled:
- yes
- Conclusions:
- As there was no inhibition of respiration at any Polyol PX concentration, the 3 h EC50 for Polyol PX to activated sludge was estimated as >1000 mg/L, under the conditions of this test.
- Executive summary:
The toxicity of Polyol PX to activated sewage sludge was investigated in a respiration inhibition test according to OECD test guideline 209. Following three hours exposure to Polyol PX the EC50 was observed to be > 1000 mg/L (based on nominal exposure concentrations), the corresponding NOEC was observed to 1000 mg/L.
Reference
Respiration rates and percentage inhibition
Treatment |
Nominal concentration (mg/L) |
Respiration rate |
% inhibition |
Control 1 |
0 |
77.4 |
- |
Control 2 |
0 |
68.80 |
- |
Mean of controls |
- |
73.10 |
- |
% difference in controls |
- |
11.1 |
- |
|
5 |
69.60 |
4.79 |
15 |
26.02 |
64.40 |
|
30 |
12.76 |
82.54 |
|
|
10 |
81.00 |
0 |
31.6 |
78.90 |
0 |
|
100 |
80.00 |
0 |
|
316 |
80.40 |
0 |
|
1000 |
82.20 |
0 |
Description of key information
A reliable study (Klimisch 1) is available. The toxicity of Polyol PX to activated sewage sludge was investigated in a respiration inhibition test according to OECD test guideline 209. Following three hours exposure to Polyol PX the EC50 was observed to be > 1000 mg/L (based on nominal exposure concentrations), the corresponding NOEC was observed to 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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