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EC number: 248-948-6 | CAS number: 28299-41-4
- 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:
- 1984-01-16
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- ISO 8192 (Water quality - Test for inhibition of oxygen consumption by activated sludge for carbonaceous and ammonium oxidation)
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- no
- Principles of method if other than guideline:
- The purpose of this test method was to provide a rapid screening method whereby substances which may adversely affect aerobic microbial treatment plants can be identified, and to indicate suitable non-inhibitory concentrations of test items to be used in biodegradability tests.
Two controls without test item were included in the test design, one at the start and the other at the end of the test series. Each batch of activated sludge was checked using 3.5-Dichlorophenol as a reference compound.
The chemical oxygen consumption control was carried out, since some substances may consume oxygen by chemical reactivity. In order to be able to differentiate between chemical oxygen consumption and biological oxygen consumption (respiration), at least the maximum concentration of the test item was additionally tested without activated sludge.
To measure the oxygen consumption, 250 mL of sludge with test item (or control or reference compound) was incubated for 3 h in 300 mL closed Erlenmeyer flasks (with air inlet and outlet) and aerated through a glass tube at 50-100 L/h with clean oil-free air. For measurement, the content of the Erlenmeyer flasks was completely transferred to 250 mL BOD bottles and 02-content was measured with an 02-meter (redox electrode) with writer. - GLP compliance:
- no
- Analytical monitoring:
- no
- Details on sampling:
- Test item concentrations: 6.25, 12.5, 25, 50 and 100 mg/L
Test item concentration in chemical oxygen consumption control
Concentration of reference compound (3,5-Dichlorophenol): 1 and 100 mg/L - Vehicle:
- no
- Details on test solutions:
- Before use the pH of the activated sludge was measured and adjusted to pH 6-8. 8 mL of the synthetic medium and 25 mL of activated sludge were added to the dissolved test item. The mixture was filled up to 250 mL with deionised water and aerated at 20 °C +/-2 °C.
The exposure medium with the reference substance was prepared by adding 8 mL of the sythetic medium, 25 mL of activated sludge and a defined amount of the stock solution to achieve the test concentrations and was filled up to 250 mL with deionised water. - Test organisms (species):
- activated sludge of a predominantly industrial sewage
- Details on inoculum:
- Type : mixed population of aquatic microorganisms (activated sludge)
Origin: laboratory scale sewage treatment unit (3L), treating prdominantly industrial sewage. (Location: Bürrig / Germany)
Microbial inoculum:
- First, the sludge was settled and the supernatent was decanted.
- After centrifuging (20 min at 4000 rpm and 20 °C) the supernatent was decanted.
- Approx. 1 g of the wet sludge was dried in order to calculate the amount of wet sludge to achieve a concentration of activated sludge of 6 g/L (dry weight) suspended solids.
- The calculated amount of sludge was first dissolved in synthetic medium and than filled up to a defined end volume with deionised water.
Storage of sludge: Aeration of the activated sludge at 20 °C +/- 2°C daily fed with synthetic medium.
Synthetic medium: A synthetic waste water feed was made by dissolving the following amounts of substance in 1 litre of water:
16.0 g peptone
11.0 g meat extract
3.0 g urea
0.7 g NaCl
0.4 g CaCl2 x 2 H2O
0.2 g MgSO4 x 7 H2O
2.8 g K2HPO4 - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Remarks on exposure duration:
- with permanent aeration
- Post exposure observation period:
- not reported
- Hardness:
- not reported
- Test temperature:
- 20 °C +/- 2 °C
- pH:
- 7.1 - 7.6
- Dissolved oxygen:
- not reported
- Salinity:
- not reported
- Nominal and measured concentrations:
- Nominal concentrations of test item: 6.25, 12.5, 25, 50, and 100 mg/L
Nominal concentration in chemical oxygen consumption control: 100 mg/L
Nominal concentration of reference compound (3,5-Dichlorophenol): 1 and 100 mg/L - Details on test conditions:
- Test vessels: 300 mL glass Erlenmeyer flasks
Test concentration of the activated sludge: 0.38 g/L dry weight - Reference substance (positive control):
- yes
- Remarks:
- 3,5-Dichlorophenol
- Duration:
- 3 h
- Dose descriptor:
- IC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- The substance showed no significant respiration inhibition of activated sludge at the highest test item concentration of 100 mg/L.
- Results with reference substance (positive control):
- The EC50 of 3,5-Dichlorophenol is in the range 5-30 mg/L.
- Reported statistics and error estimates:
- not reported
- Validity criteria fulfilled:
- yes
- Remarks:
- (- respiratory rates of the 2 controls differ less than 15 % form each other; - EC50 of 3,5-Dichlorophenol is in the range 5-30 mg/L)
- Conclusions:
- The substance showed no significant respiration inhibition of activated sludge at the highest test item concentration of 100 mg/L.
- Executive summary:
The toxicity of the substance to microorganisms was assessed in a study according to ISO 8192 "Test for Inhibition of Oxygen Consumption of Activated Sludge". This test method is in accordance with the OECD Guideline 209 (1983). The respiration rate of each mixture was determined after aeration periods of 3 hours. The substance showed no significant respiration inhibition of activated sludge at the highest concentration tested, and hence: IC50 > 100 mg/L (based on nominal concentrations).
Reference
In the following table the respirationrate, the percentage of inhibition as well as the pH values at the different test concentrations were presented:
|
Test item concentration [mg/L] |
Respirationrate
[mg/(L*min)] |
Inhibition
% |
pH |
Test item |
6.25 |
0.33 |
- |
7.5 |
12.5 |
0.32 |
- |
7.5 |
|
25 |
0.30 |
- |
7.5 |
|
50 |
0.29 |
- |
7.6 |
|
100 |
0.26 |
10.34 |
7.6 |
|
Control 1 |
|
0.25 |
|
7.5 |
Control 2 |
|
0.33 |
|
7.6 |
Chemical oxygen consumption control |
100 |
0.07 |
|
7.1 |
Description of key information
The substance showed no significant respiration inhibition of activated sludge at the highest concentration tested, and hence the IC50 is > 100 mg/L (based on nominal concentrations).
Key value for chemical safety assessment
Additional information
The toxicity of the substance to bacteria was assessed in a study according to ISO 8192 "Test for Inhibition of Oxygen Consumption of Activated Sludge". The substance showed no significant respiration inhibition of activated sludge at the highest concentration tested, and hence the IC50 is > 100 mg/L (based on nominal concentrations).
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