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EC number: 231-836-6 | CAS number: 7758-19-2
- 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 aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The test substance could not be monitored in the test solutions due to background interference. However, the method allowed accurate determination of the stock solution concentrations in deionised water. As a flow-through system was used, the nominals are considered acceptable estimates of the actual concentration.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 72-3 (Estuarine/Marine Fish, Mollusk, or Shrimp Acute Toxicity Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Test organisms (species):
- other aquatic crustacea: Eastern Oyster (Crassostrea virginica)
- Test type:
- flow-through
- Water media type:
- saltwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Test temperature:
- 20.4 - 21.2 °C
- pH:
- 7.5 - 9.2
- Dissolved oxygen:
- 7.0 - 8.3 mg/L
- Nominal and measured concentrations:
- Nominal concentrations of the active substance were 0 (control), 70.6, 121, 252, 504 and 1008 mg sodium chlorite/L(Doses are equivalent to 0, 53, 90, 188, 376 and 752 mg chlorite/L)
- Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC0
- Remarks:
- and NOEC
- Effect conc.:
- 70.6 other: mg sodium chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: shell deposition
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC0
- Remarks:
- and NOEC
- Effect conc.:
- 53 other: mg chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: shell deposition
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 129 other: mg sodium chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: shell deposition
- Remarks on result:
- other: 95% confidence interval of 121 – 138 mg/L
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 96 other: mg chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: shell deposition
- Details on results:
- No sub-lethal effects were noted during the exposure period however, after 72 h large and approximately equal amounts of faecal material were present in the control and at 70.6 and 121 mg/L sodium chlorite. The volume of fecal material at concentrations above 121 mg/L appeared to decrease with increasing toxicant concentration.
Shell deposition by oysters was related to the concentration of test substance.
Exposure of the oysters to sodium chlorite resulted in a 96 h EC50 of 129 mg/L sodium chlorite with a 95% confidence interval of 121 – 138 mg/L (equivalent to 96 mg chlorite/L).
The 96 h NOEC was 70.6 mg/L sodium chlorite (equivalent to 53 mg chlorite/L). - Conclusions:
- Exposure of the oysters to sodium chlorite resulted in a 96 h EC50 of 129 mg/L sodium chlorite with a 95% confidence interval of 121 – 138 mg/L (equivalent to 96 mg chlorite/L). The 96 h NOEC was 70.6 mg/L sodium chlorite (equivalent to 53 mg chlorite/L).
- Executive summary:
The aim of this study was to investigate the shell deposition of the Eastern Oyster crustacea produced by the test material.
The test procedure used was the EPA OPP 72-3 (Estuarine/Marine Fish, Mollusk, or Shrimp Acute Toxicity Test)
Nominal concentrations of the active substance were 0 (control), 70.6, 121, 252, 504 and 1008 mg sodium chlorite/L (Doses are equivalent to 0, 53, 90, 188, 376 and 752 mg chlorite/L)
The result was as follows:
Exposure of the oysters to sodium chlorite resulted in a 96 h EC50 of 129 mg/L sodium chlorite with a 95% confidence interval of 121 – 138 mg/L (equivalent to 96 mg chlorite/L). The 96 h NOEC was 70.6 mg/L sodium chlorite (equivalent to 53 mg chlorite/L).
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The test substance could not be monitored in the test solutions due to background interference. However, the method allowed accurate determination of the stock solution concentrations in deionised water. As a flow-through system was used, the nominals are considered acceptable estimates of the actual concentration.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 72-3 (Estuarine/Marine Fish, Mollusk, or Shrimp Acute Toxicity Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Dissolved oxygen, pH, salinity and temperature were recorded for each test chamber. The temperature in one test vessel was recorded continuously during the test.
- Test organisms (species):
- Americamysis bahia (previous name: Mysidopsis bahia)
- Test type:
- flow-through
- Water media type:
- saltwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Test temperature:
- 22 ± 1 °C
- pH:
- 7.8 - 8.2
- Dissolved oxygen:
- 7.3 - 8.0 mg/L
- Nominal and measured concentrations:
- Nominal concentrations:Nominal concentrations were 0, 0.15, 0.25, 0.40, 0.60, 1.00 mg sodium chlorite/L(Doses are equivalent to 0, 0.11, 0.19, 0.30, 0.45 and 0.75 mg chlorite/L)
- Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC0
- Remarks:
- and NOEC
- Effect conc.:
- 0.25 other: mg sodium chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC0
- Remarks:
- and NOEC
- Effect conc.:
- 0.19 other: mg chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.65 other: mg sodium chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% confidence interval of 0.40 – 1.00 mg/L
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.49 other: mg chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- Lethargy was noted in the 1.00 mg/L treatment group between 48 and 72 h.
- Validity criteria fulfilled:
- yes
- Remarks:
- (immobilisation in the control was 0%; the dissolved oxygen concentration at the end of the test was greater than 3 mg/l in control and test vessels).
- Conclusions:
- Exposure of mysids to the test substance resulted in a 96 h LC50 of 0.65 mg/L of sodium chlorite, with a 95% confidence interval of 0.40 – 1.00 mg/L (equivalent to 0.49 mg chlorite/L). The 96 h NOEC was 0.25 mg/L sodium chlorite (equivalent to 0.19 mg chlorite/L).
- Executive summary:
The aim of this study was to investigate the degree of inhibition of the Mysidopsis bahia mobility produced by the test material.
The test procedure used was the EPA OPP 72-3 (Estuarine/Marine Fish, Mollusk, or Shrimp Acute Toxicity Test)
Nominal concentrations were 0, 0.15, 0.25, 0.40, 0.60, 1.00 mg sodium chlorite/L (Doses are equivalent to 0, 0.11, 0.19, 0.30, 0.45 and 0.75 mg chlorite/L)
The result was as follows:
Exposure of mysids to the test substance resulted in a 96 h LC50 of 0.65 mg/L of sodium chlorite, with a 95% confidence interval of 0.40 – 1.00 mg/L (equivalent to 0.49 mg chlorite/L)
The 96 h NOEC was 0.25 mg/L sodium chlorite (equivalent to 0.19 mg chlorite/L).
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- No GLP statement or analysis
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- Principles of method if other than guideline:
- The acute toxicity of sodium chlorite to Daphnia magna in a 48 hr static test was assessed.
- GLP compliance:
- no
- Analytical monitoring:
- no
- Details on sampling:
- Water quality parameters were tested, namely temperature, hardness, dissolved oxygen and pH at 0 hr and 48 hr for the control and highest concentration.
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 19.6 °C
- pH:
- 7.91 - 8.45
- Dissolved oxygen:
- 6.7 - 9.3 mg/L
- Nominal and measured concentrations:
- Nominal concentrations:1, 10 and 100 mg/L (expressed as active component)(Doses are equivalent to 0.75, 7.5 and 75 mg chlorite/L)
- Reference substance (positive control):
- no
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- < 1 other: mg sodium chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- < 0.75 other: mg chlorite/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Validity criteria fulfilled:
- yes
- Remarks:
- (immobilisation in the control was 0%; the dissolved oxygen concentration at the end of the test was greater than 3 mg/l in control and test vessels).
- Conclusions:
- The 48 hr EC50 < 1 mg sodium chlorite/L (equivalent to 0.75 mg chlorite/L).
- Executive summary:
The aim of this study was to investigate the degree of inhibition of the Daphnia magna´s mobility produced by the test material.
The test procedure used was the OECD Guideline 202
Nominal concentrations: 1, 10 and 100 mg/L (expressed as active component) (Doses are equivalent to 0.75, 7.5 and 75 mg chlorite/L)
The result was as follows:
The 48 hr EC50 < 1 mg sodium chlorite/L (equivalent to 0.75 mg chlorite/L).
Referenceopen allclose all
Table A7_4_1_2(5)-5: Immobilisation data: Number of live oysters
Test-Substance Concentration [mg sodium chlorite/L] |
0 h |
24 h |
48 h |
72 h |
96 h |
0 (control) |
20 |
20 |
20 |
20 |
20 |
70.6 |
20 |
20 |
20 |
20 |
20 |
121 |
20 |
20 |
20 |
20 |
20 |
252 |
20 |
20 |
20 |
20 |
19 |
504 |
20 |
20 |
20 |
20 |
13 |
1008 |
20 |
20 |
20 |
20 |
2 |
Table A7_4_1_2(5)-6: Shell growth at longest finger (mm)
Oyster Number |
0.0 mg/l |
70.6 mg/l |
121 mg/l |
252 mg/l |
504 mg/l |
1008 mg/l |
1 |
2.2 |
1.9 |
1.3 |
0.0 |
0.0 |
0.0 |
2 |
2.1 |
1.7 |
1.0 |
0.0 |
0.0 |
0.0 |
3 |
1.9 |
2.2 |
1.2 |
0.0 |
0.0 |
- |
4 |
2.4 |
2.4 |
1.6 |
0.2 |
0.0 |
- |
5 |
2.1 |
2.3 |
1.4 |
0.0 |
0.0 |
- |
6 |
2.1 |
2.0 |
1.3 |
0.0 |
0.0 |
- |
7 |
2.3 |
2.1 |
1.0 |
0.1 |
0.0 |
- |
8 |
1.9 |
2.2 |
0.9 |
0.0 |
0.0 |
- |
9 |
2.3 |
1.9 |
1.4 |
0.0 |
0.0 |
- |
10 |
2.2 |
2.2 |
1.5 |
0.0 |
0.0 |
- |
11 |
2.0 |
2.4 |
1.3 |
0.0 |
0.0 |
- |
12 |
2.4 |
2.0 |
1.6 |
0.0 |
0.0 |
- |
13 |
2.0 |
2.1 |
1.0 |
0.1 |
- |
- |
14 |
2.1 |
2.1 |
0.7 |
0.1 |
- |
- |
15 |
2.1 |
1.7 |
0.8 |
0.0 |
- |
- |
16 |
1.8 |
2.3 |
1.1 |
0.0 |
- |
- |
17 |
1.7 |
2.4 |
0.9 |
00 |
- |
- |
18 |
2.2 |
1.8 |
1.3 |
0.0 |
- |
- |
19 |
2.4 |
2.1 |
1.2 |
0.0 |
- |
- |
20 |
2.1 |
2.0 |
1.0 |
0.0 |
- |
- |
Mean |
2.1 |
2.1 |
1.2 |
0.1 |
0.0 |
0.0 |
Std. dev. |
0.2 |
0.2 |
0.3 |
0.1 |
- |
- |
% of control |
100 |
100 |
57.1 |
1.4 |
0.0 |
0.0 |
Table A7_4_1_2(5)-7: Effect data
EC50 |
95 % c.l. |
EC0 |
|
96 h [mg sodium chlorite/L] |
129 mg/L (n1) |
121 – 138 mg/l |
70.6 mg/l |
1 Effect data are based on nominal (n) concentrations
Table A7_4_1_2(4)-6: Immobilisation data: mysids living
Test Substance Concentration [mg sodium chlorite/L] |
Replicate |
0 h |
24 h |
48 h |
72 h |
96 h |
0 (Control) |
1 |
10 |
10 |
10 |
10 |
9 |
2 |
10 |
10 |
10 |
10 |
9 |
|
0.15 |
1 |
10 |
10 |
10 |
10 |
10 |
2 |
10 |
10 |
10 |
10 |
9 |
|
0.25 |
1 |
10 |
10 |
10 |
10 |
10 |
2 |
10 |
10 |
10 |
10 |
10 |
|
0.40 |
1 |
10 |
10 |
10 |
8 |
8 |
2 |
10 |
10 |
10 |
9 |
7 |
|
0.60 |
1 |
10 |
10 |
7 |
5 |
5 |
2 |
10 |
10 |
9 |
7 |
7 |
|
1.00 |
1 |
10 |
8 |
3 |
1 |
0 |
2 |
10 |
8 |
3 |
1 |
1 |
Table A7_4_1_2(1)-7: Immobilisation data: lethargic mysids
Test Substance Concentration [mg sodium chlorite/L] |
Replicate |
0 h |
24 h |
48 h |
72 h |
96 h |
0 (Control) |
1 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
|
0.15 |
1 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
|
0.25 |
1 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
|
0.40 |
1 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
|
0.60 |
1 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
|
1.00 |
1 |
0 |
0 |
3 |
1 |
- |
2 |
0 |
0 |
3 |
1 |
0 |
Table A7_4_1_2(4)-8: Effect data
Exposure Period |
Median LC50 |
95 % c.l. |
LC50 Calculation Method |
24 h [mg sodium chlorite/L] |
>1.00 mg/L (n) |
- |
- |
48 h [mg sodium chlorite/L] |
0.83 mg/L (n) |
0.72 – 1.00 mg/L |
Probit |
72 h [mg sodium chlorite/L] |
0.66 mg/L (n) |
0.40 – 1.00 mg/L |
Binomial / nonlinear interpolation |
96 h [mg sodium chlorite/L] |
0.65 mg/L (n) |
0.40 – 1.00 mg/L |
Binomial / nonlinear interpolation |
Table A7_4_1_2 (3)-6: Cumulative immobilisation data
Test Substance Concentration [mg sodium chlorite/L] | ||||
Immobile Daphnia | ||||
Number 24 h 48 h | Percentage 24 h 48 h | |||
0 | 0/5 | 0/5 | 0 | 0 |
0/5 | 0/5 | 0 | 0 | |
0/5 | 0/5 | 0 | 0 | |
0/5/ | 0/5 | 0 | 0 | |
1 | 4/5 | 5/5 | 80 | 100 |
4/5 | 5/5 | 80 | 100 | |
1/5 | 5/5 | 20 | 100 | |
3/5 | 5/5 | 60 | 100 | |
10 | 2/5 | 5/5 | 40 | 100 |
4/5 | 5/5 | 80 | 100 | |
3/5 | 5/5 | 60 | 100 | |
3/5 | 5/5 | 60 | 100 | |
100 | 5/5 | 5/5 | 100 | 100 |
5/5 | 5/5 | 100 | 100 | |
5/5 | 5/5 | 100 | 100 | |
5/5 | 5/5 | 100 | 100 |
1 Concentrations were nominal
Table A7_4_1_2 (3)-7: Effect data
EC501 | 95 % c.l. | EC01 | EC1001 | |
24 h [mg sodium chlorite/L] | Not specified | Not specified | Not specified | Not specified |
48 h [mg sodium chlorite/L] | 1 mg/L (n) | Not specified | Not specified | 7 mg/L |
1 effect data are based on nominal (n) concentrations
Description of key information
Key study. Test method OECD 202. The 48 hr-EC50 in Daphnia magna was < 1 mg sodium chlorite/L (equivalent to 0.75 mg chlorite/L).
Key study. Test method EPA OPP 72-3. The 96 h-LC50 in mysids was 0.65 mg/L of sodium chlorite (equivalent to 0.49 mg chlorite/L). The 96 h NOEC was 0.25 mg/L sodium chlorite (equivalent to 0.19 mg chlorite/L).
Key study. Test method EPA OPP 72-3. The 96 h-EC50 in oysters was 129 mg/L sodium chlorite with a 95% (equivalent to 96 mg chlorite/L). The 96 h NOEC was 70.6 mg/L sodium chlorite (equivalent to 53 mg chlorite/L).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- EC50
- Effect concentration:
- 0.65 mg/L
Additional information
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