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EC number: 476-280-7 | CAS number: 109113-72-6
- 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:
- 2007-01-29 to 2007-03-01
- 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:
- 1988
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Version / remarks:
- 1984
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 850.6800 (Modified Activated Sludge, Respiration Inhibition Test for Sparingly Soluble Chemicals)
- Version / remarks:
- 1996
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- -Preparation of Test Flask: One test solution with a final volume of 330 mL was tested per treatment in a glass flask. 10.56 mL synthetic sewage and an adequate amount of the stock solution of the test item or an adequate volume of the stock solution of the reference item were added to a flask and then the flask was filled up with deionised water to 198 mL before the start of the test. At the start of the test 132 mL activated sludge inoculum with a sludge concentration of 4 g/L (dry weight) was added, first to the first control, then in time intervals of approximately 15 minutes (an optional but convenient interval) to the test solutions of the reference item and the test item and finally to a second control.
- Test organisms (species):
- activated sludge, domestic
- Details on inoculum:
- - Source: sewage plant for domestic sewage in Veszprém, Hungary
- Pretreatment: activated sludge was washed and centrifuged and the supernatant liquid phase was decanted. The solid material was re-suspended in isotonic saline solution and again centrifuged. This procedure was repeated twice. Based on dry weight determinations, calculated amounts of wet sludge were suspended in isotonic saline solution to yield a concentration equivalent to 4 g per litre (on dry weight basis). The activated sludge inoculum was determined to have a pH of 7.51. The activated sludge was used directly after conditioning.
- Initial biomass concentration: 1.6 g/L - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Hardness:
- no data
- Test temperature:
- 18.4 – 20.9 °C (during the incubation) and
18.6 – 20.5 °C (during oxygen measurement) - pH:
- 7.05 - 7.78
- Dissolved oxygen:
- 6.7 - 9.0
- Salinity:
- not applicable
- Nominal and measured concentrations:
- - Nominal: 3, 10, 31, 98, 313 and 1000 mg test item/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer bottles of approximately 350 ml volume, and BOD bottles with special neck of 300 ml volume
- Material, fill volume: 330 mL test media
- Aeration: yes, compressed air (approximately 1 litre per minute)
- No. of organisms per vessel: 132 mL activated sludge (with 4 g dw/L)
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 2
- Biomass loading rate: 132 mL activated sludge inoculum with a sludge concentration of 4 g/L (dry weight) (start of the test)
OTHER TEST CONDITIONS
- Other: Climate chamber (during the incubation) and controlled environment room (during the formulation and oxygen measuring)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : respiration rate and pH, Dissolved Oxygen, Water Temperature - Reference substance (positive control):
- yes
- Remarks:
- 3,5-Dichlorophenol (nominal test concentrations of 5, 16 and 32 mg/L)
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- 316.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: 95% CL = 245.4 - 408.9 mg/L
- Duration:
- 3 h
- Dose descriptor:
- other: EC20
- Effect conc.:
- 71.3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: 95% CL = 54.6 - 92.9 mg/L
- Duration:
- 3 h
- Dose descriptor:
- other: EC80
- Effect conc.:
- 1 408.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: 95% CL = 939.2 - 2111.5 mg/L
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 31 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: EC50 (3 h, 3,5-Dichlorophenol) = 7.3 mg/L (95% CL 5.2 - 10.4 mg/L). - Reported statistics and error estimates:
- Based on measured inhibition rates, the 3-h EC20, EC50 and EC80 and their 95%-confidence limits were calculated by Probit analysis using TOXSTAT software.
- Validity criteria fulfilled:
- yes
- Conclusions:
- A 3-h EC50 value of 316.8 mg/L and a NOEC of 31 mg/L were determined for the test item under the conditions of the test.
- Executive summary:
In comparison to the inoculum controls the respiration rate of the activated sludge was inhibited between –8.8 % (the negative value was interpreted biologically as zero inhibition (slight stimulation)) and 77.2 % up to the highest nominal test concentration of 1000 mg/L. Concentrations exceeding 1000 mg/L nominal were not tested.
Based on measured inhibition rates, the 3-hour EC20, EC50 and EC80 and their 95 %-confidence limits were calculated by
Probit analysis using TOXSTAT software: EC20: 71.3 mg/L (54.6–92.9); EC50: 316.8 mg/L (245.4–408.9); EC80: 1408.2 mg/L (939.2–2111.5). The EC50 value is in the range of 100 to 1000 mg/L.
The NOEC was determined to be 31 mg/L The NOEC for respiration rates was not based on the results of a statistical analysis, but it is biologically justified. At the lower concentration values the respiration inhibition was not influenced dose dependently and additionally the respiration rates at 3.1, 10 and 31 mg/L concentrations were in/above the historical control data range (0.490 ± 0.090).
Reference
Toxicity of test item:
In comparison to the inoculum controls the respiration rate of the activated sludge was inhibited by 5.3 % at the lowest nominal concentration of 3 mg/L. At the nominal concentrations of 10, 31 and 98 mg/L, the respiration rate was inhibited by -8.8 %*, -1.8 %* and 29.8 %, respectively. At the nominal concentrations of 313 and 1000 mg test item/L, the respiration rate was inhibited by 50.9 % and 77.2 %, respectively.
Toxicity of 3,5 -Dichlorophenol
In comparison to the controls the respiration rate of the activated sludge was inhibited by 42.1 % at the lowest nominal concentration of 5 mg/L. At the nominal concentrations of 16 and 32 mg/L, the respiration rate was inhibited by 66.7 % and 78.9 %, respectively. The 3-hour EC50 of 3,5-Dichlorophenol was calculated to be 7.3 mg/L with 95 % confidence limits of 5.2 to 10.4 mg/L.
* the negative value was interpreted biologically as zero inhibition (slight stimulation)
Description of key information
A 3 -h EC50 of 316.8 mg/L and a NOEC of 31 mg/L for activated sludge were determined for the substance according to OECD 209.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 316.8 mg/L
- EC10 or NOEC for microorganisms:
- 31 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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