Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 931-745-8 | CAS number: 1335203-21-8
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- The study was performed according to accepted scientifical standards. However there minor deviation from the guideline, but this does not invalidate the study.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1981
- GLP compliance:
- not specified
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- Oncorhynchus mykiss (previous name: Salmo gairdneri)
- Details on test organisms:
- TEST ORGANISM
- Common name: Salmo-Gardia, Shasta
- Source: Fischzucht Jochen Müller, 30966 (formerly 3005) Harkenbleck, Germany
- Age at study initiation (mean and range, SD):
- Length at study initiation (length definition, mean, range and SD): 5 - 6 cm ("Setzlinge")
- Method of breeding: Fish were kept for 14 days in a 360 L basin prior acclimation, water removal at a flow rate of 80L/hour, aeration, advection of the water, removal of suspendend matter, O2-content was > 90% saturation.
- Feeding during test: no
ACCLIMATION
- Acclimation period: An appropriate number of fish were kept for two days in a 240 L basin
- Acclimation conditions (same as test or not): yes
- Test type:
- not specified
- Water media type:
- freshwater
- Test temperature:
- 16 +/- 1 degreeC
- pH:
- 7.3 +/- 0.13
- Dissolved oxygen:
- 7.8 - 8.0
- Nominal and measured concentrations:
- 10.0, 13.3, 17.6, 23.3, 30.8 mg test mat. /L (nominal), no control was perfomed
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 30 L glass aquaria
- Aeration: yes
- Renewal rate of test solution: no data
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 2
-No controls were performed
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: dechlorinated tap water for human use, Stadtwerke Hannover
- Metals: Ca2+: 1.140 mmol/L +/- 5%, Mg2+: 0.610 mmol/L +/- 5 %
- Acid capacity up to pH 4.3: 1.65 - 1.45 mval/L
-Base capacity up to pH 8.2: 1.8 mg/L
- Ca/mg ratio:1.14:0.61
- Culture medium different from test medium: No
- Intervals of water quality measurement: O2-monitoring daily
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: No data
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : mortality
TEST CONCENTRATIONS
- Range finding study
- Test concentrations: Yes
- Results used to determine the conditions for the definitive study: No data - Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 9.84 - <= 10.24 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Confidence interval: 2.7 - 11.73 mg a.i./L
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 11.4 - <= 11.86 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Confidence interval: 9.38 - 13.40 mg a.i./L
- Duration:
- 24 h
- Dose descriptor:
- LC50
- Effect conc.:
- 13.91 - 14.48 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: Confidence interval: 12.00 - 17.39 mg a.i./L
- Details on results:
- Effect concentrations:
96 h LC50 = 13.3 mg test mat./L (nominal, Confidence interval: 3.69 - 15.24 mg/L )
48 h LC50 = 15.4 mg test mat./L (nominal, Confidence interval: 12.67 - 17.40 mg/L)
24 h LC50 = 18.8 mg test mat./L (nominal, Confidence interval: 16.22 - 22.59 mg/L)
96 h LC50 = 9.84 – 10.24 mg act. ingr./L (nominal, Confidence interval: 2.7 - 11.73 mg/L)
48 h LC50 = 11.40 – 11.86 mg act. ingr./L (nominal, Confidence interval: 9.38 - 13.40 mg/L)
24 h LC50 = 13.91 – 14.48 mg act. ingr./L (nominal, Confidence interval: 12.00 - 17.39 mg/L)
- Behavioural abnormalities: At test start fisch showed enhanced activity and prospecting the new surrounding, however no adverse effects were observed.
- Observations on body length and weight: No
- Other biological observations: The dead animals showed apparently no alternation in appearence, pigmentation, mucosa and eyes .
- Mortality of control: No control
- Abnormal responses:
- Any observations that might cause a difference between measured and nominal values: In a seperate test analytical monitoring (UV spectrometric measurement) of the a.i. in aqueous solution showed depletion of the a.i. ( 0.0504 mg/L at time 0, 0.0468 mg/L afetr 48 hours, and 445 mg/L after 96 hours).
No control was performed. - Reported statistics and error estimates:
- LC50 was calculated according to Probit analysis after Finney (1971)
Since no control was performed, it is assumed that the lowest test concentration without any adverse affects on fish was taken as control for statistical analysis. This is acceptable, since the concentration/response curve is very steep. - Sublethal observations / clinical signs:
Mortality of Rainbow trout (Onchorhynchus mykiss) during a 96-Hour Exposure to test substance under Static Test Conditions
Concentrations (nominal)
[ppm]
Concentrations (nominal)
[mg test mat. /L]
Cumulative number
Mortality
[%]
Cumulative number
Mortality
[%]
Cumulative number
Mortality
[%]
24 hours
24 hours
48 hours
48 hours
96 hours
96 hours
10.0
300
0
0
0
0
0
0
13.3
399
1
10
3
30
5
50
17.6
528
6
60
8
80
10
100
23.3
699
7
70
9
90
10
100
30.8
924
9
90
10
100
10
100
The test substance forms stable suspensions in water. All test concentrations were below the suspensibility of the test material.
No control was performed.
- Validity criteria fulfilled:
- no
- Remarks:
- no control was performed
- Conclusions:
- There is minor deviation from the OECD-Test Guideline 203 ( no control was performed). For statistical analysis the lowest concentration with no adverse effects to fish was presumably used, however this is acceptable, since the concentration/response curve is very steep.
The test material partially unsaturated IQAC, DMS quaternised contains considerable amounts of isopropanol. The toxicity of isopropanol against fish is about 100 to 1000 times lower than the toxicity of the test material. Therefore it can be concluded in a first approach, neglecting additive effects, that the observed effect values can be attributed to the active ingredient itself.
Despite of this the study is performed according to acceptable scientifical standards and regarded as reliable with restrictions - Executive summary:
In a 96-h acute toxicity study, Rainbow trouts (Salmo-Gardia, Shasta, Oncorhynchus mykiss) were exposed to partially unsaturated IQAC, DMS quaternised at nominal concentrations of 10.0, 13.3, 17.6, 23.3, 30.8 mg test mat. /L. The 96-h LC50 was 9.84 – 10.24 mg act. ingr./L (nominal, Confidence interval: 2.7 - 11.73 mg a.i./L) . Sublethal effects were not observed. The observed concentration/response curve is very steep. The test material contains considerable amounts of isopropanol. The toxicity of isopropanol against fish is about 100 to 1000 times lower than the toxicity of the test material. Therefore it can be concluded in a first approach, neglecting additive effects, that the observed effect values can be attributed to the active ingredient itself.
This toxicity study is classified as acceptable with restrictions and satisfies the guideline requirement for acute toxicity to fish despite of some deviations that do not invalidate the study.Results Synopsis
Test organism size/age: juvenile rainbow trout (Onchorhynchus mykiss)
Test Type: no data, OECD 203
LC50: 9.84 – 10.24 mg a.i./L 95% C.I.: 2.7 to 11.73 mg a.i./L- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 96 h
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- No data on analytical purity of the test substance is available. No analytical monitoring was conducted.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Leuciscus idus
- Details on test organisms:
- TEST ORGANISM
- Length at study initiation (length definition, mean, range and SD): 47 - 65 mm (average 54.8 mm)
- Weight at study initiation (mean and range, SD): 1.45 - 3.84 g (average 2.32 g)
ACCLIMATION
- Acclimation period: 2 weeks, then held at test temperature for 5 days
- No mortalities during the 5 day period. - Test type:
- semi-static
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- mean: 54 mg/l CaCO3 (49 - 60 mg /l CaCO3)
- Test temperature:
- 22°C (+-1°C)
- pH:
- 7.2 - 8.5
- Dissolved oxygen:
- 6.6 - 8.4 mg/l
- Nominal and measured concentrations:
- 0.32; 1.0; 1.8; 3.2; 5.6 mg/l + freshwater control (nominal concentrations)
0.24, 0.75, 1.35, 2.4, 4.2 mg/l based on a. i. (mean 75%) - Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Aeration: continously
- glas aquaria (39 x 28 x 28 cm), 28 l volume
- test volume: 20 l
- Renewal rate of test solution: 24h interval
- No. of organisms per vessel: 10 fish per concentration and control
- continuous aeration
TEST MEDIUM / WATER PARAMETERS
- Intervals of water quality measurement: 24h interval
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- mortality was recorded in test solutions and control
- Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 1.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 2.4 mg/L (nominal); 99.8% CL: 1.8 - 3.2
- Duration:
- 72 h
- Dose descriptor:
- LC50
- Effect conc.:
- 1.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 2.4 mg/L (nominal); 99.8% CL: 1.8 - 3.2
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 1.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 2.4 mg/L (nominal); 99.8% CL: 1.8 - 3.2
- Duration:
- 24 h
- Dose descriptor:
- LC50
- Effect conc.:
- 2.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 2.4 mg/L (nominal); 95% CI: 2.9 - 4.4
- Details on results:
- - 96h-LC50 = 1.8 mg/l (based on a.i. content of 75%)
- Mortality of control: 0% - Sublethal observations / clinical signs:
Percent mortality observed:
Nominal concentration of test substance [mg/l] 24 h 48 h 72 h 96 h 5.6 100 100 100 100 3.2 30 100 100 100 1.8 0 0 0 0 1.0 0 0 0 0 0.32 0 0 0 0 control 0 0 0 0 - Validity criteria fulfilled:
- yes
- Remarks:
- Valid with restriction. No data on analytical purity of the test substance is available. No analytical monitoring was conducted. Therefore the test concentrations can only be based on nominal concentrations of the test material.
- Conclusions:
- In a 96-h acute toxicity study, Leuciscus idus were exposed to oleic acid-based IQAC, DMS quaternised at nominal concentrations of 0 (control), 0.32; 1.0; 1.8; 3.2; 5.6 mg/l under semi-static conditions. The 96-h LC50was 1.8 mg a.i. /L (2.4 mg/l, nominal).
- Executive summary:
In a 96-h acute toxicity study, Leuciscus idus were exposed to oleic-acid based IQAC, DMS quaternised at nominal concentrations of 0 (control), 0.32; 1.0; 1.8; 3.2; 5.6 mg/l under semi-static conditions. The 96-h LC50was 1.8 mg a.i. /L (2.4 mg/l, nominal).
This study is classified as reliable with restriction and satisfies the guideline requirements for an acute toxicity study with fish.
Results Synopsis
Test organism size: 47 - 65 mm (average 54.8 mm)
Test organism size: 1.45 - 3.84 g (average 2.32 g)
Test Type: Static Renewal
LC50: 2.4 mg/l (nominal, 99.8% C.I.: 1.8 to 3.2 mg/l)LC50 = 1.8 mg a.i. /l (based on a.i. content of 75%)
Endpoint(s) Effected: mortality
Referenceopen allclose all
Description of key information
The 96-h LC50 was 1.8 mg/l (based on a.i. content of 75%; 2.4 mg/L nominal)
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 1.8 mg/L
Additional information
In a 96-h acute toxicity study, Leuciscus idus were exposed to Oleic-acid based IQAC, DMS quaternised under semi-static conditions. The 96-h LC50was 1.8 mg/l (based on a. i. content of 75%; 2.4 mg/l (nominal)).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
