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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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: No purity provided in the CoA and no batch number provided. The method would have been better run under flow-through conditions considering the potential for loss of chlorine dioxide due to its volatility.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.1 (Acute Toxicity for Fish)
- Deviations:
- no
- GLP compliance:
- yes
- Remarks:
- but no certificate is joined
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
no data - Analytical monitoring:
- yes
- Details on sampling:
- Oxygen, pH, temperature and the test substance concentration were measured daily.
- Concentrations:
- nominal concentrations: 0.009, 0.021, 0.045, and 0.1 mg/L
- measured concentrations: 0.01, 0.02, 0.05, 0.08 mg/L
- Sampling method: samples were analyzed for chlorine dioxide by RBM, with the spectrophotometer HACH and the method supplied by the Sponsor.
- Sample storage conditions before analysis: no data - Vehicle:
- no
- Details on test solutions:
- Some volatility of chlorine dioxide may be expected. Although the test systems were not treated as such, analysis of the fresh test solutions showed that there was low loss during preparation.
- Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- TEST ORGANISM
- Common name: Zebrafish
- Strain: no data
- Source: AQUA, Turin, IT
- Age at study initiation (mean and range, SD): no data
- Length at study initiation (length definition, mean, range and SD): 3 cm
- Weight at study initiation (mean and range, SD): 0.4 g
- Method of breeding: no data
- Feeding during test: NO
- Food type:
- Amount:
- Frequency:
ACCLIMATION
- Acclimation period: 2 wks before start of test. All fish were exposed (in a glass aquarium) to water.
- Acclimation conditions (same as test or not): in water , from municipal water main system, at 22°C, pH: 7.2, Hardeness: 21 mg/L of CaCO3, [O2]: 8.1 mg/L
- Type and amount of food: Mangine SERA (Aquaristik GmbH, batch CH 09-3)
- Feeding frequency: daily
- Health during acclimation (any mortality observed): no mortality was recorded after 7 days of acclimation - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Post exposure observation period:
- no data
- Hardness:
- no data
- Test temperature:
- 21 - 22 °C
- pH:
- 6.6 - 7.1
- Dissolved oxygen:
- 7.7 - 9.0
- Salinity:
- not applicable
- Nominal and measured concentrations:
- Nominal concentrations: 0.009, 0.021, 0.045 and 0.1 mg/L
Measured concentrations at t = 0 h: 0.01, 0.02, 0.05 and 0.08 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: glass beakers
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: 5 L
- Aeration:no data
- Type of flow-through (e.g. peristaltic or proportional diluter): no data
- Renewal rate of test solution (frequency/flow rate): no data
- No. of organisms per vessel: 7
- 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:
- Photoperiod: 16:8
- Light intensity: no data
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2.2
- Range finding study
- Test concentrations:
- nominal concentrations: 0.009, 0.021, 0.045, and 0.01 mg/L
- measured concentrations: 0.01, 0.02, 0.05, and 0.08 mg/L - Reference substance (positive control):
- no
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.049 mg/L
- Nominal / measured:
- meas. (TWA)
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95 % confidence limits 0.04 – 0.061 mg/L
- Duration:
- 72 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.049 mg/L
- Nominal / measured:
- meas. (TWA)
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95 % confidence limits 0.04 – 0.061 mg/L
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.021 mg/L
- Nominal / measured:
- meas. (TWA)
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95 % confidence limits 0.01 – 0.04 mg/L
- Duration:
- 96 h
- Dose descriptor:
- LC0
- Effect conc.:
- 0.009 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Duration:
- 96 h
- Dose descriptor:
- LC100
- Effect conc.:
- 0.072 mg/L
- Nominal / measured:
- meas. (TWA)
- Basis for effect:
- mortality (fish)
- Details on results:
- The concentration causing no mortality was lower than 0.009 mg/L. The lowest concentration causing 100% mortality was 0.100 mg/L. In the fish treated at 0.045 and 1.00 mg/L the only sign of abnormality observed was decreased escape reflex that appeared at the 24 h observation until the 72 observation in the fish (in fish treated with 0.045 mg/L. In animals treated at 0.009 and 0.021 mg/L the only sign of abnormality observed was decreased escape reflex that appeared at the 72 h observation in those treated at 0.009 mg/L. In both the treated groups this sign lasted until the end of the study. 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 the 100% ClO2 and to the solution at the nominal concentration of 0.2%. The LC50 at 24 h was not calculable.
- Results with reference substance (positive control):
- Not applicable
- Reported statistics and error estimates:
- no data
- Sublethal observations / clinical signs:
Table A7_4_1_1(1)-5: Mortality data
Test-Substance
Concentration
nominal [mg/l]Mortality
Number
24 h 48 h 72 h 96 h
Percentage
24 h 48 h 72 h 96 h
0.0
0/7
0/7
0/7
0/7
0
0
0
0
0.009
0/7
0/7
0/7
1/7
0
0
0
14
0.021
0/7
0/7
0/7
3/7
0
0
0
43
0.045
0/7
1/7
1/7
4/7
0
14
14
57
0.100
4/7
7/7
7/7
7/7
57
100
100
100
Table A7_4_1_1(1)-6: Effect data
48 h [mg/l]1
95 % c.l.
96 h [mg/l]1
95 % c.l.
LC0
Not stated
Not stated
0.009 (n)
Not stated
LC50
0.054 (n)
Not stated
0.030 (n)
Not stated
LC100
Not stated
Not stated
0.100 (n)
Not stated
1 effect data are based on nominal (n) concentrations
- Validity criteria fulfilled:
- no
- Remarks:
- no reference substance was tested
- Conclusions:
- 96 h LC50 = 0.021 mg/L (based on the TWA)
- Executive summary:
Acute toxicity test was conducted on zebrafish, Danio rerio, to assess effects of chlorine dioxide. The experiment was realized under GLP conditions, and following C.1 EEC Guideline. 4 measured concentrations were tested, with 7 fish exposed to each ones: 0.01, 0.02, 0.05, and 0.08 mg/L of chlorine dioxide. LC50(96h) = 0.030 mg/L of 100 % ClO2; i.e. 0.015 g/L of 0.2% ClO2
Reference
Description of key information
Based on results from Gnemi (1996), an LC50(96h) of 0.021 mg/L was determined for chlorine dioxide on the zebrafish, Danio rerio. Chlorine dioxide is highly acutely toxic to fish, it has a short half-life in the environment following use, and there is no direct release of the active substance to aquatic systems. Chlorine dioxide in aqueous solution reacts rapidly, abiotically with organic matter and oxidisable metals, generating chlorite, chlorate and ultimately chloride as dominant species. Under the conditions of use, no chlorine dioxide is expected to be found in the environment, however the principal decomposition products, chlorite, chlorate and chloride will be. Therefore, supporting studies concerning these substances (except chloride) have also been included in this section such that their toxicity and ultimately risk can be characterised in the CSR.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 0.021 mg/L
Additional information
One acute toxicity study valid was found in Chlorine dioxide for zebrafish Danio rerio (Gnemi 1996, according to C.1 EEC Guideline). Two acute toxicity studies valid were used in Sodium chlorite for sheepshead minnow Cyprinodon variegates (Ward and Boeri 1991, according to EPA OPP 72 -1; Yurk 1994, according to EPA-FIFRA 72 -3). Finally, two acute toxicity studies valid from the same authors (Ward and Boeri 1991, according to EPA OPP 72 -1 and Ward and Boeri 1991, EPA-FIFRA 72 -3 severally) were used in Sodium chlorate for rainbow trout Oncorhynchus mykiss and sheepshead minnow, respectively.
Based on results from Gnemi (1996), LC50(96h) = 0.021 mg/L of chlorine dioxide on zebrafish. Chlorine dioxide is highly acutely toxic to fish. It has a short half-life (seconds to minutes) in the environment, and there is no direct release of the active substance to aquatic systems. Chlorine dioxide in aqueous solution reacts rapidly, abiotically with organic matter and oxidisable metals, generating chlorite, chlorate and ultimately chloride as dominant species. Under the conditions of use, no chlorine dioxide is expected to be found in the environment, however the principal decomposition products, chlorite, chlorate and chloride will be.
For sodium chlorite the two lowest 96 h LC50s for fish were found at 78 mg/L of chlorite and 55.9 mg/L of chlorite (Ward 1991 and Yurk 1994 respectively). For sodium chlorate 96 h LC50s for fish > 1000 mg/L were observed.
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