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EC number: 233-109-9 | CAS number: 10034-85-2
- 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
- Study period:
- 11.06.2019 - 30.09.2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- April 13, 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Version / remarks:
- May 30, 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Remarks:
- ion chromatography with conductivity detection
- Details on sampling:
- One replicate of the stock solution and duplicate samples from the freshly prepared test media of all test concentrations and the control were taken at the start of the test.
For the determination of the stability of the test item under the test conditions and of the maintenance of the test item concentrations during the test period, duplicate samples from the test media of all test concentrations and the control were collected at the end of the test (after 48 hours) by pouring together the contents of the test beakers of each treatment. - Vehicle:
- no
- Details on test solutions:
- A stock solution of 16.95 mg test item/L corresponding to 10 mg hydroiodic acid/L was prepared by dissolving 18.12 mg test item into 1069.03 mL test water by intense stirring for 15 minutes. Adequate volumes of this stock solution were diluted with test water to prepare the test media of the desired test concentrations.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: water flea
- Strain/clone: Straus, clone 5
- Age at study initiation: 1.75 to 19.15 hours old.
- Source: in-house laboratory culture
- Method of breeding: The daphnids were bred in the laboratories of the testing facility under similar temperature and light conditions as used in the test. The cultivation of the parental daphnids was performed in Elendt M4 medium.
- Feeding during test : none
ACCLIMATION
- Acclimation period: Was not necessary, since the test was performed in the same medium as the culturing. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 2.5 mmol/L (= 250 mg/L) as CaCO3
- Test temperature:
- 20.7 - 21.1 °C
- pH:
- 7.8 - 8.0
- Dissolved oxygen:
- 8.6 - 8.7 mg/L
- Nominal and measured concentrations:
- Nominal concentrations: control, 2.0, 0.91, 0.41, 0.19, 0.09 mg Hydroiodic acid/L, corresponding to 3.39, 1.54, 0.69, 0.32 and 0.153 mg test item/L
Measured concentration: 97 % of the nominal at the start and 95 % of the nominal at the end of the study - Details on test conditions:
- TEST SYSTEM
- Test vessel: beakers
- Type: covered with a lid to reduce the loss of water due to evaporation and to avoid the entry of dust into the solutions
- Material, size: glass, 100 mL
- Volume of solution: 60 mL
- Aeration: none
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Elendt M4, prepared according to OECD 202
- Alkalinity: 0.9 mmol/L
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 h light : 8 h dark
- Light intensity: 530 - 840 lux - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 1.01 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- other: EC20
- Effect conc.:
- 0.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC10
- Effect conc.:
- 0.685 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.41 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 0.91 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Details on results:
- After 48 hours of exposure no immobilisation of the test animals was observed in the control and up to and including the test item concentration of 0.41 mg hydroiodic acid/L. At the concentration of 0.91 mg hydroiodic acid/L, 7 animals were immobile and 20 animals were immobile at the concentration of 2.0 mg hydroiodic acid/L.
- Results with reference substance (positive control):
- The most recent test with the reference item resulted in 24-h EC50 of 0.932 mg/L and 48-h EC50 of 0.672 mg/L (95 % CI: 0.598 - 0.757 mg/L), respectively. The results indicate that the sensitivity of the daphnids was consistent with the level proposed by the OECD 202 guideline (24-h EC50 between 0.6 and 2.1 mg potassium dichromate/L).
- Validity criteria fulfilled:
- yes
- Conclusions:
- The 48-hour NOEC was determined to be 0.41 mg hydroiodic acid/L and the 48-hour EC50 value was calculated to be 1.01 mg hydroiodic acid/L.
- Executive summary:
The toxic effect of the test item to Daphnia magna was assessed in a static concentration-response test performed according to OECD 202 under GLP. Daphnids were exposed to test item concentrations of control, 2.0, 0.91, 0.41, 0.19, 0.09 mg Hydroiodic acid/L, corresponding to 3.39, 1.54, 0.69, 0.32 and 0.153 mg test item/L for 48 hours under static conditions. After 48 hours of exposure no immobilisation of the test animals was observed in the control and up to and including the test item concentration of 0.41 mg hydroiodic acid/L. At the concentration of 0.91 mg hydroiodic acid/L, 7 animals were immobile and 20 animals were immobile at the concentration of 2.0 mg hydroiodic acid/L. The 48-hour NOEC was determined to be 0.41 mg hydroiodic acid/L. The 48-hour LOEC was determined to be 0.91 mg hydroiodic acid/L and the 48-hour EC50 value was calculated to be 1.01 mg hydroiodic acid/L. The initial concentrations and the maintenance of the exposure concentrations during the test were verified in the analytical part. All reported results refer to nominal values since the concentrations of the test item were within ± 20 % of the nominal concentrations during the test.
Reference
Biological results
Table 1. Summary of Biological Results
Nominal Concentration |
% of immobilised daphnids after |
|
[mg hydroiodic acid/L] |
24 hours |
48 hours |
Control |
0 |
0 |
0.09 |
0 |
0 |
0.19 |
0 |
0 |
0.41 |
0 |
0 |
0.91 |
0 |
35 |
2.0 |
30 |
100 |
EC50 [mg hydroiodic acid/L]: |
>2.0 |
1.01 |
95 % CI [mg hydroiodic acid/L]: |
n.d. |
0.848 - 1.21 |
EC20 [mg hydroiodic acid/L]: |
1.94 |
0.800 |
95 % CI [mg hydroiodic acid/L]: |
0.595 - >2.0 |
0.675 - 0.949 |
EC10 [mg hydroiodic acid/L]: |
0.547 |
0.685 |
95 % CI [mg hydroiodic acid/L]: |
0.257 - 1.16 |
0.542 - 0.868 |
NOEC [mg hydroiodic acid/L]: |
0.91 |
0.41 |
LOEC [mg hydroiodic acid/L]: |
2.0 |
0.91 |
Values refer
to nominal test concentrations
CI: Confidence interval
n.d.: not determinable
NOEC and LOEC were determined directly from the raw data.
Analytical results
The quantification of the active ingredient iodide of the test item in the test samples was performed using ion chromatography with conductivity detection. At the start of the test 97 % of the nominal test concentrations were found (average of all test concentrations). After 48 hours test duration, 95 % of the nominal value was determined (average of all test concentrations). During the test the daphnids were exposed to a mean of 96 % of nominal.
Table 2. Summary of Analytical Results
Sample Description [mg hydroiodic acid/L] |
% of nominal* |
RSD [%] |
n |
Control |
n.a. |
n.a. |
4 |
0.09 |
94 |
3 |
4 |
0.19 |
96 |
3 |
4 |
0.41 |
100 |
3 |
4 |
0.91 |
96 |
2 |
4 |
2.0 |
95 |
2 |
4 |
* mean value of all measured samples per
treatment group
RSD: relative standard deviation per treatment group
n: number of analysed samples
n.a.: not applicable
Description of key information
The 48-hour NOEC was determined to be 0.41 mg hydroiodic acid/L and the 48-hour EC50 value was calculated to be 1.01 mg hydroiodic acid/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 1.01 mg/L
Additional information
The toxic effect of the test item to Daphnia magna was assessed in a static concentration-response test performed according to OECD 202 under GLP. Daphnids were exposed to test item concentrations of control, 2.0, 0.91, 0.41, 0.19, 0.09 mg Hydroiodic acid/L, corresponding to 3.39, 1.54, 0.69, 0.32 and 0.153 mg test item/L for 48 hours under static conditions. After 48 hours of exposure no immobilisation of the test animals was observed in the control and up to and including the test item concentration of 0.41 mg hydroiodic acid/L. At the concentration of 0.91 mg hydroiodic acid/L, 7 animals were immobile and 20 animals were immobile at the concentration of 2.0 mg hydroiodic acid/L. The 48-hour NOEC was determined to be 0.41 mg hydroiodic acid/L. The 48-hour LOEC was determined to be 0.91 mg hydroiodic acid/L and the 48-hour EC50 value was calculated to be 1.01 mg hydroiodic acid/L. The initial concentrations and the maintenance of the exposure concentrations during the test were verified in the analytical part. All reported results refer to nominal values since the concentrations of the test item were within ± 20 % of the nominal concentrations during the test (reference 6.1.3-1).
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