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EC number: 233-162-8 | CAS number: 10049-04-4
- 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
- Reliability:
- 1 (reliable without restriction)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Version / remarks:
- OECD-GLP compliance 1996-09-09
- Deviations:
- no
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 1996-09-09
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
no data - Analytical monitoring:
- no
- Details on sampling:
- After 3 h aeration, the first sample was taken for oxygen measurement over a period of up to 10 minutes. Thereafter, in 15 minute intervals, the rest of the samples were submitted to measurement of oxygen concentration. Sampling was started with control 1, continued with the reference substance samples, the positive controls and the test article samples. Finally the oxygen consumption of control 2 was determined.
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Test solutions of shlorine dioxide were prepared by dissolving volumes of test article stock solution directly to the study beakers in order to obtain the requested concentrations taking into account the strength of the stock solution that was checked weekly, following the analytical method supplied by the sponsor.
- Eluate:
- Differential loading:
- Controls:
- Chemical name of vehicle (organic solvent, emulsifier or dispersant):
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)):
- Evidence of undissolved material (e.g. precipitate, surface film, etc): - Test organisms (species):
- activated sludge
- Details on inoculum:
- A synthetic sewage feed was made by dissolving the following in 1 L of water:
16 g peptone
11 g meat extract
3 g urea
0.7 g NaCl
0.4 g CaCl2.2H2O2O
0.2 g MgSO4.7H2O
2.8 g K2HPO4 - Test type:
- not specified
- Water media type:
- not specified
- Limit test:
- no
- Total exposure duration:
- 3 h
- Post exposure observation period:
- no data
- Hardness:
- no data
- Test temperature:
- 20 °C
- pH:
- 6.24 - 7.13
- Dissolved oxygen:
- no data
- Salinity:
- not applicable
- Nominal and measured concentrations:
- Nominal concentrations: 100, 32, 10, 3.2, 1 mg/L
Actual test concentrations were not measured. - Details on test conditions:
- TEST SYSTEM
- Test vessel: beakers
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: 500 ml of final volume
- Aeration: yes until use, with an air-flow using compressed air
- Type of flow-through (e.g. peristaltic or proportional diluter): not applicable
- Renewal rate of test solution (frequency/flow rate): not applicable
- No. of organisms per vessel: 200 ml of activated sludge
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- No. of vessels per vehicle control (replicates): not applicable
- Biomass loading rate: no data
OTHER TEST CONDITIONS
- Adjustment of pH: no data
- Photoperiod: no data
- Light intensity: no data - Reference substance (positive control):
- yes
- Remarks:
- 3,5-Dichlorophenol (batch 6300410, 99% purity)
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- 10.7 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Remarks:
- 100 %
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Remarks on result:
- other: The EC50 was a calculated value. 95 % confidence limit: 10.5 – 10.9 mg/L
- Details on results:
- The study was performed taking into account the actual content of the stock solution of chlorine dioxide. The toxicity values can therefore be expressed as referring to 100% ClO2 and to the solution at the nominal concentration of 0.2%. The calculated EC50 value of 100% ClO2 was 10.7 mg/L corresponding to 5.35 g/L of 0.2% solution being 1 g/L its density. The EC50 of the reference compound 3,5-dichlorophenol tested under the same conditions was 10.2 mg/L which is in the guideline accepted range.
- Results with reference substance (positive control):
- Nominal concentrations of the reference substance: 50, 32, 10 3.2, 1.0 mg/L
The EC50 of the reference substance compound 3,5-dichlorophenol was 10.2 mg/L which is in the guideline accepted range. - Reported statistics and error estimates:
- No data
- Validity criteria fulfilled:
- yes
- Remarks:
- 2 contro respiration rates within 15% of each other, and EC50 (3h) of reference substance is in the accepted range of 5-30 mg/L
- Conclusions:
- The calculated E50 value of 100% ClO2 was 10.7 mg/L with 95 % confidence limit of 10.5 – 10.9 mg/L.
- Executive summary:
Inhibitory effect of chlorine dioxide on activated sludge was realized in a respiration inhibition test. Test article was tested with 5 different concentrations: 1, 3.2, 10, 32, and 100 mg/L of chlorine dioxide. Calculated EC50 = 10.7 mg/L (for 100% of ClO2), i.e. to 5.35 g/L of 0.2% solution being 1 g/L its density. All criteria were fulfilled.
Reference
Table 1: Effect data of chlorine dioxide
Concentration of Chlorine Dioxide (mg/L) |
Oxygen Consumption (mgO2/Lmin) |
Inhibition (%) |
Starting pH |
100 |
0 |
100 |
6.24 |
32 |
0.27 |
55.4 |
6.81 |
10 |
0.44 |
27.3 |
7.02 |
3.2 |
0.53 |
12.4 |
7.10 |
1 |
0.57 |
5.8 |
7.13 |
Table 2: Effect data of the reference substance
Concentration of Reference (mg/L) |
Oxygen Consumption (mgO2/Lmin) |
Inhibition (%) |
Starting pH |
50 |
0.10 |
83.5 |
7.19 |
32 |
0.15 |
75.2 |
7.18 |
10 |
0.19 |
68.6 |
7.13 |
3.2 |
0.51 |
15.7 |
7.13 |
1.0 |
0.59 |
2.5 |
7.13 |
Description of key information
Based on results from Gnemi (1996), EC50(3h) was 10.7 mg/L of chlorine dioxide on activated sludge. Chlorine dioxide reacts rapidly degrading to chlorite (which also degrades rapidly) and chlorate as dominant species. For chlorite the 3h EC50 for activated sludge was >75 mg/L, the highest concentration tested (as the sodium salt). For chlorate the 3h EC50 was >1000 mg/L, the highest concentration tested (as sodium salt).
Key value for chemical safety assessment
- EC50 for microorganisms:
- 10.7 mg/L
Additional information
Three toxicity studies valid were found in chlorine dioxide, sodium chlorite, and sodium chlorate for activated sludge, according to OECD guideline 209 (Gnemi 1996; L'Haridon 2002; L'Haridon 2003).
Based on results from Gnemi (1996), EC50(3h) = 10.7 mg/L of 100% chlorine dioxide on activated sludge. Chlorine dioxide react easily and rapidly generating chlorite and chlorate as dominant species. In the absence of oxidisable substances, and in the presence of pH > 9, chlorine dioxide dissolves in water and decomposes with the slow formation of chlorite and chlorate ions.
Valid studies on both transformation products demonstrated an EC50(3h) > 75 mg/L for sodium chlorite (L'Haridon 2002), and an EC50(3h) >1000 mg/L for sodium chlorate (L'Haridon 2003), which corresponds to levels 7 to 90 times higher than that of chlorine dioxide.
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