Registration Dossier
Registration Dossier
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: 252-744-2 | CAS number: 35836-73-8
- 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:
- 10-19 January 2012
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- This study was performed according to OECD Guideline 209 with GLP statement: average oxygen uptake rate for the control replicates was slightly lower than the guideline
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- yes
- Remarks:
- average oxygen uptake rate for the control replicates was slightly lower than the guideline
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 18 March 2010
- Analytical monitoring:
- no
- Details on sampling:
- Not applicable
- Vehicle:
- no
- Details on test solutions:
- Nopol was weighed directly in the incubation vessels.
- Test organisms (species):
- other: Unadapted secondary activated sludge
- Details on inoculum:
- Unadapted secondary activated sludge was obtained (17-01-2012) from the WWTP Nieuwgraaf in Duiven. The WWTP Duiven is an activated sludge plant treating predominantly domestic wastewater. Prior to use the activated sludge was homogenized with a syringe. The dry weight of the homogenized activated sludge was determined and subsequently concentrated by settlement to the required dry weight concentration. The dry weight of the activated sludge in the incubation vessels was 1.5 g/L.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Post exposure observation period:
- None
- Hardness:
- No data
- Test temperature:
- 20.0-20.6 °C
- pH:
- 6.9-7.3
- Dissolved oxygen:
- Average oxygen uptake rate for the control replicates of 19 mg O2/g dry weight/hour on the first day and 23 mg O2/g dry weight/hour on the second day.
- Salinity:
- No data
- Conductivity:
- No data
- Nominal and measured concentrations:
- 19.3, 38.7, 77.4, 154.7, 309.4 and 618.9 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Test was performed in 250 mL Erlenmeyer flasks closed with Teflon coated lids, with a working volume of 50 mL.
- Type: closed
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Synthetic Sewage: 16 g peptone; 11 g meat extract; 3 g urea; 0.7 g NaCl; 0.3 g CaCl2; 0.2 g MgSO4 · 7H2O; 2.8 g K2HPO4 - filled up to 1 litre with deionised water.
- In the incubation vessels 1.6 mL of the synthetic sewage feed is added in a total volume of 50 mL.
TEST PROCEDURE
- Activated sludge with test substances was incubated in a shaking bath (100 rpm/min) for 3 hours.
EFFECT PARAMETERS MEASURED
Determination of respiration rates, pH, dry weight and temperature: The respiration rates of the activated sludge were measured in a Biological Oxygen Monitor YSI 5300. The BOM consisted of a thermostated vessel with a magnetic stirrer and an oxygen electrode. The electrode to measure the oxygen depletion tightly closed the vessel. The volume of the vessel was 10 mL and the temperature in the vessel was 20 °C. The pH was measured using an EUTECH pH meter. The temperature was measured with a Keithley 871A digital thermometer. The dry weight of the inoculum was determined by filtrating 30 mL of the activated sludge over a preweighed 12 µm cellulose nitrate filter. This filter was dried for minimal 1.5 hours at 104 ± 5 °C and weighed after cooling. Dry weight was calculated by subtracting the weight of the filters and dividing the difference by the filtered volume. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-Dichlorophenol
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- 106 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% confidence limits of 44 and 247 mg/L
- Duration:
- 3 h
- Dose descriptor:
- EC10
- Effect conc.:
- 32 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:
- other: EC20
- Effect conc.:
- 48 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:
- other: EC80
- Effect conc.:
- 234 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- The inhibition percentage of test substance was 3, 18, 28, 64, 94 and 96 at 19.3, 38.7, 77.4, 154.7, 309.4 and 618.9 mg/L, respectively.
- Results with reference substance (positive control):
- The inhibition percentage of positive control was 8, 26, 39, 80 and 88% at 2.5, 5.1, 10.2, 20.3 and 40.6 mg/L, respectively. Test is valid as shown by the EC50 of the reference compound, 3,5-dichlorophenol is 11 mg/L.
- Reported statistics and error estimates:
- The EC values were computed from the best-fitted line (least square method) through the points given by the probit of the percentage inhibition and the logarithm of the nominal concentration of the substance. All computations were performed with the program TOXCALCTM(Tidepool Scientific Software 1994-1999).
- Validity criteria fulfilled:
- yes
- Conclusions:
- The EC50 of the test substance for activated sludge after 3 hours contact time is 106 mg/L with 95% confidence limits of 44 and 247 mg/L. The EC10, EC20 and EC80 are 32, 48 and 234 mg/L, respectively. The test substance is therefore considered not harmful to activated sludge.
- Executive summary:
An activated sludge respiration inhibition test was performed according to Guideline OECD 209 with GLP compliance.
Unadapted secondary activated sludge was obtained from activated sludge plant treating predominantly domestic wastewater (WWTP Nieuwgraaf in Duiven). The respiration rate (oxygen consumption) of an aerobic activated sludge fed with a standard amount of synthetic sewage was measured in the presence of various concentrations of the test substance after an incubation period of 3 h.
Test Concentrations: 19.3, 38.7, 77.4, 154.7, 309.4 and 618.9 mg/L
The test is valid as shown by the EC50 of the reference compound, 3,5-dichlorophenol (11 mg/L), the coefficient of variation of the replicates of the control oxygen uptake rates (7% on first day and 4% on second day) and the average oxygen uptake rate for the control replicates of 19 mg O2/g dry weight/hour on the first day and 23 mg O2/g dry weight/hour on the second day.
The inhibition percentage of test substance was 3, 18, 28, 64, 94 and 96 at 19.3, 38.7, 77.4, 154.7, 309.4 and 618.9 mg/L, respectively.
Therefore, the EC50 of the test substance for activated sludge after 3 hours contact time is 106 mg/L with 95% confidence limits of 44 and 247 mg/L. The EC10, EC20 and EC80 are 32, 48 and 234 mg/L, respectively. The test substance is therefore considered not harmful to activated sludge.
Reference
Table 6.1.7/1: Respiration rates of the activated sludge, inhibition percentages and pH at various concentrations of test substance after 3 hours contact time
Concentration (mg/L) |
Activity (mg O2/g/min) |
Inhibition (%) |
pH at start test |
pH at end test |
Temperature end test (°C) |
Control |
0.4083 |
- |
7.0 |
7.2 |
20.0 |
Control |
0.4000 |
- |
7.0 |
7.3 |
20.4 |
Control* |
0.3833 |
- |
7.0 |
7.3 |
20.5 |
Control* |
0.3833 |
- |
7.0 |
7.3 |
20.5 |
19.3* |
0.3704 |
3 |
n.d |
7.2 |
20.1 |
38.7 |
0.3333 |
18 |
n.d |
7.2 |
20.1 |
77.4 |
0.2917 |
28 |
n.d |
7.2 |
20.6 |
154.7 |
0.1458 |
64 |
n.d |
7.2 |
20.5 |
309.4 |
0.0250 |
94 |
n.d |
7.2 |
20.5 |
618.9 |
0.0167 |
96 |
n.d |
7.2 |
20.2 |
* = corresponding control and reference concentration
n.d. = not determined, the pH was not measured at the start to prevent evaporation of the test substance.
Validity of the test
The reference substance and test substance were measured on two subsequent days. The validity of the test is demonstrated by three criteria.
First, the coefficient of variation of the replicates of the control oxygen uptake rates was 7% on the first day and 4% on the second day, which fulfils the maximum prescribed variation of <30%. Secondly, the EC50 of the reference compound was 11 mg/L which is within the prescribed range of 2 to 25 mg/L.
The third criterion, an oxygen uptake rate of >20 mg O2/g dry weight/hour for the control measurements, was not achieved on the first day (19 mg O2/g dry weight/hour) and was met on the second day (23 mg O2/g dry weight/hour).
The inoculum used was obtained from a treatment plant which is operated at a low organic sludge load and therefore has a natural lower oxygen uptake rate.
According the guideline activated sludge used should be fed with synthetic sewage feed, for a maximum of two additional days, when used after the day of collection. Adding synthetic sewage feed leads to an increase of the oxygen uptake rate of the activated sludge, but does not affect the sensitivity of the activated sludge significantly (AkzoNobel, 2012). Accurate oxygen uptake rate measurements were very well possible, with the slightly lower oxygen uptake rate on the first day, as shown by the very low coefficient of variation. Therefore this is a minor deviation which does not invalidate the test.
Description of key information
The EC50 of the test substance for activated sludge after 3 hours contact time is 106 mg/L. The EC10, EC20 and EC80 are 32, 48 and 234 mg/L, respectively. The test substance is therefore considered not harmful to activated sludge.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 106 mg/L
- EC10 or NOEC for microorganisms:
- 32 mg/L
Additional information
An activated sludge respiration inhibition test was available and it was performed according to Guideline OECD 209 under GLP, at the following test concentrations: 19.3, 38.7, 77.4, 154.7, 309.4 and 618.9 mg/L.
The test was valid and the inhibition percentage of the test substance was 3, 18, 28, 64, 94 and 96 at 19.3, 38.7, 77.4, 154.7, 309.4 and 618.9 mg/L, respectively.
The EC50 of the test substance for activated sludge after 3 hours contact time is 106 mg/L with 95% confidence limits of 44 and 247 mg/L. The EC10, EC20 and EC80 are 32, 48 and 234 mg/L, respectively. The test substance is therefore considered not harmful to activated sludge.
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.